303 Second Street, Suite 300 South San Francisco, California 94107 415-243-2150 FAX: 415-896-0999 Human Health Risk Assessment Report 31 March 2011 Prepared for West Valley Water District and the City of Rialto 855 West Base Line Road Rialto, California 92377 K/J Project No. 1089040*00 Table of Contents List of Tables ................................................................................................................................ iii List of Figures............................................................................................................................... iii List of Appendices ........................................................................................................................ iii List of Acronyms........................................................................................................................... iv Executive Summary ............................................................................................................... ES - I Section 1: Introduction .................................................................................. 1 1.1 1.2 1.3 1.4 Section 2: Background and Description of Area ........................................... 5 2.1 2.2 Section 3: Description of Area ................................................................................. 5 Water Supply in the Rialto Area ............................................................. 5 2.2.1 Rialto Well No. 6 ......................................................................... 5 2.2.2 District Well No. 11...................................................................... 6 Identification of Chemicals of Potential Concern ....................... 7 3.1 3.2 3.3 Section 4: Background and Regulatory Context ..................................................... 1 HHRA Objectives ................................................................................... 2 HHRA Approach ..................................................................................... 2 Report Organization ............................................................................... 3 Available Data and Data Reduction ....................................................... 7 Identification and Selection of Chemicals of Potential Concern ............. 7 3.2.1 Carcinogenic Classification ......................................................... 8 3.2.2 Frequency of Detection ............................................................... 8 3.2.3 Comparison with Risk-Based Levels........................................... 8 Chemicals of Potential Concern ............................................................. 8 Exposure Assessment ................................................................ 10 4.1 4.2 4.3 4.4 Identification of Potentially Exposed Populations ................................. 10 Identification of Relevant Exposure Pathways ..................................... 10 Process to Estimate Exposure Point Concentrations ........................... 11 Process to Estimate Chronic Daily Intakes .......................................... 12 4.4.1 Route-Specific Assumptions ..................................................... 12 4.4.1.1 Ingestion of Groundwater ....................................... 13 4.4.1.2 Inhalation of Vapors ................................................ 13 4.4.1.3 Dermal Contact with Groundwater .......................... 13 4.4.2 Chronic Daily Intake Equations ................................................. 13 4.4.2.1 Ingestion of Chemicals in Groundwater .................. 13 4.4.2.2 Inhalation of Chemicals in Groundwater ................. 14 Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc i Table of Contents (cont’d) 4.4.2.3 Section 5: Toxicity Assessment .................................................................. 15 5.1 5.2 5.3 5.4 Section 6: Noncancer Hazard Estimates............................................................... 21 Cancer Risk Estimates ......................................................................... 21 Risk Characterization Results .............................................................. 22 6.3.1 Adult Resident Risk Characterization Results........................... 22 6.3.2 Child Resident Risk Characterization Results........................... 22 6.3.3 Combined Adult and Child Resident ......................................... 23 Uncertainty Assessment ............................................................ 24 7.1 7.2 7.3 7.4 Section 8: Sources of Toxicity Values ................................................................... 15 Chemicals of Potential Concern with Noncarcinogenic Effects ............ 15 5.2.1 1,2-Dibromo-3-chloropropane ................................................... 16 5.2.2 Arsenic ...................................................................................... 16 5.2.3 Chloroform ................................................................................ 16 5.2.4 Fluoride ..................................................................................... 16 5.2.5 Hexavalent Chromium............................................................... 16 5.2.6 Nitrate and Nitrite ...................................................................... 17 5.2.7 Perchlorate ................................................................................ 17 5.2.8 Trichloroethene ......................................................................... 18 Chemicals of Potential Concern with Carcinogenic Effects.................. 18 5.3.1 Lines of Evidence for Carcinogenic Potential............................ 18 5.3.2 Cancer Slope Factors ............................................................... 19 Dermal Toxicity Assessment ................................................................ 19 Risk Characterization ................................................................. 21 6.1 6.2 6.3 Section 7: Dermal Contact with Chemicals in Groundwater ........................................................... 14 Uncertainties in Data and EPCs ........................................................... 24 Uncertainties in Exposure Factors ....................................................... 25 Uncertainties in Toxicological Data ...................................................... 25 Impact of Uncertainties......................................................................... 25 Summary and Conclusions ......................................................... 26 References ........................................................................................................................... Ref - 1 ii Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc List of Tables 1 2 3 4 5 6 7 8 9 10 11 12 Occurrence, Distribution, and Selection of Chemicals of Potential Concern in Groundwater Exposure Point Concentrations for Chemicals of Potential Concern Values for Chronic Daily Intake Calculations Chemical-Specific Parameters for Dermal Exposure to Domestic Water Toxicity Information for Noncarcinogenic Chemicals of Potential Concern Toxicity Information for Carcinogenic Chemicals of Potential Concern Calculation of Noncancer Hazards - Adult Resident, Domestic Water Use Calculation of Cancer Risks - Adult Resident, Domestic Water Use Calculation of Noncancer Hazards - Child Resident, Domestic Water Use Calculation of Cancer Risks - Child Resident, Domestic Water Use Combined Adult and Child Resident Cancer Risk Estimates Summary of Human Health Risks List of Figures 1 2 3 4 Location Map Human Health Risk Assessment Process District and City Service Areas Human Health Conceptual Site Model List of Appendices A Human Health Risk Assessment Data Sets (Provided on CD) B Results of Trend Analyses for Chemicals of Potential Concern (Provided on CD) C ProUCL Version 4.00.05 Files (Provided on CD) Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc iii List of Acronyms AFY AT BMD BMDL CDI CDPH CDPR CFR cm CERCLA COPCs City CSF DBCP District DLR DTSC EC EPC GI HI HQ HHRA gpm Kennedy/Jenks IRIS LADI L/day L/m3 MCL mgd mg/m3 µg/L µg/m3 NCP NIS NOAEL NO3 NO3-N OEHHA PHG RfC iv acre-feet per year averaging time benchmark dose limit of the benchmark dose chronic daily intake California Department of Public Health California Department of Pesticide Regulation Code of Federal Regulations centimeter Comprehensive Environmental Response, Compensation and Liability Act chemicals of potential concern City of Rialto cancer slope factor 1,2-dibromo-3-chloropropane West Valley Water District detection limit for reporting California Department of Toxic Substances Control exposure concentration exposure point concentration gastrointestinal hazard index hazard quotient human health risk assessment gallons per minute Kennedy/Jenks Consultants Integrated Risk Information System lifetime average daily intake liters per day liters per cubic meter maximum contaminant level millions gallons per day milligrams per cubic meter micrograms per liter micrograms per cubic meter National Contingency Plan sodium-iodide symporter no-observable-adverse-effect nitrate nitrate as nitrogen California Office of Environmental Health Hazard Assessment public health goal reference concentration Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc List of Acronyms (cont’d) RfD RCB RME RSL RL TCE USEPA VFw VOC reference dose Rialto Colton Basin reasonable maximum exposure Regional Screening Level reporting limit trichloroethene United States Environmental Protection Agency volatilization factor volatile organic compound Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc v Executive Summary Together, the West Valley Water District (the District) and the City of Rialto (the City) provide water for residential and commercial/industrial uses in the City of Rialto. In recent years, perchlorate has been detected in several of the District’s and City’s production wells at concentrations exceeding the notification level and maximum contaminant level (MCL) of six micrograms per liter (µg/L) established by the California Department of Public Health (CDPH). The District and City have removed these production wells from service, pending installation of appropriate treatment systems. Treatment systems are being developed for two of the production wells, Rialto Well No. 6 and District Well No. 11. This human health risk assessment (HHRA) was performed to estimate the potential human health risks associated with domestic use of untreated groundwater from the Rialto Well No. 6 and District Well No. 11, assuming that no reduction in the concentrations of contaminants occurs through treatment or response actions. The objective of the HHRA is to provide an analysis of baseline risks, which are defined as the “risks that might exist if no remediation or institutional controls were applied at a site” (United States Environmental Protection Agency [USEPA] 1989). This HHRA has assumed that no treatment has been conducted, consistent with the appropriate state and Federal guidance, and although risk values have been calculated as a result of several COPCs, many of these COPCs are present in groundwater at levels less than State and Federal drinking water standards. The chemicals of potential concern (COPCs) for quantitative risk assessment were selected in accordance with USEPA risk assessment guidelines (USEPA 1989). The chemicals identified as COPCs for further evaluation in the HHRA were: Inorganic anions: perchlorate, nitrate as nitrogen (NO3-N), and fluoride. Metals: arsenic and hexavalent chromium. VOCs: 1,2-dibromo-3-chloropropane (DBCP), chloroform, and trichloroethene (TCE). Of these COPCs, only perchlorate, NO3-N, and TCE were detected at concentrations above the respective California primary maximum contaminant level (MCL). Potentially exposed populations for evaluation in the HHRA were identified based on consideration of the current and future use category and USEPA (1989) guidance. Because Rialto Well No. 6 is not currently used for domestic supply and District Well No. 11 is provided with treatment, the only potentially exposed populations are under future use conditions if the production wells were restored to service without treatment. The HHRA considered potential future exposures for adult and child water consumers (Adult and Child Residents) via ingestion of, inhalation of, and dermal contact with COPCs in groundwater used as a domestic water source. The groundwater data used in this HHRA were obtained from the historical water quality database maintained by CDPH, which requires all certified drinking water analytical laboratories to submit water quality data directly to CDPH in electronic form. Studies not requiring reporting to CDPH were not included in the HHRA data set. Groundwater data collected from Rialto Well Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc ES - I No. 6 and District Well No. 11 were used to develop exposure point concentrations (EPCs) for use in this HHRA. Trend analysis was used to determine the appropriate data set for use in HHRA so that the EPCs represented a stable trend in concentrations. Both noncarcinogenic and carcinogenic health effects were evaluated in this HHRA. For noncarcinogenic effects, hazard quotients (HQs) were calculated by comparing the estimated average daily intakes of COPCs to toxicity value benchmarks that represent exposures that would not cause adverse health effects, even if the exposure occurred continuously over a lifetime. Estimated HQs were compared to the point of departure of 1 established by the California Department of Toxic Substances Control (DTSC). For carcinogenic effects, incremental cancer risks were calculated by combining the estimated lifetime average daily intakes of COPCs with chemical-specific dose-response data. Incremental cancer risks were compared to the DTSC point of departure of 1 x 10-6. The results of the risk characterization for the production wells Rialto Well No. 6 and District Well No. 11 are summarized as follows: Rialto Well No. 6. TCE, chloroform, and perchlorate are the chemicals found to exceed the DTSC point of departure for carcinogenic or noncarcinogenic effects for Rialto Well No. 6. TCE and chloroform resulted in cancer risk estimates exceeding the DTSC point of departure of 1 x 10-6. For the combined adult and child resident exposure scenario the cancer risk estimates for TCE and chloroform were 3 x10-6 and 2 x 10-6, respectively. Perchlorate was the only COPC that resulted in a HQ greater than the point of departure of 1. District Well No. 11. DBCP and arsenic are the chemicals found to exceed the DTSC point of departure for carcinogenic effects for District Well No. 11. DBCP and arsenic are the chemicals associated with cancer risks greater than the DTSC point of departure of 1 x 10-6. For the combined adult and child resident exposure scenario, the cancer risk estimates for DBCP and arsenic were 2 x10-5 and 3 x 10-5, respectively. No COPCs resulted in a HQ greater than the point of departure of 1. Of the chemicals found to exceed the DTSC points of departure for carcinogenic and noncarcinogenic effects, only the TCE and perchlorate EPCs were above the California MCLs. DBCP is a halogenated volatile organic compound (VOC) that was historically used as a soil fumigant for agricultural purposes, although it has not been approved for use in agriculture in California since 1977 (California Office of Environmental Health Hazard Assessment [OEHHA] 1999). The California Department of Pesticide Regulation (CDPR) reported detections of DBCP in all of the 261 wells that were tested for DBCP (2009). The concentrations of DBCP detected in groundwater collected from District Well No. 11 are similar to concentrations commonly detected in groundwater as reported by CDPR (2009). The DBCP EPC for District Well No. 11 (0.032 µg/L) was based on the maximum detected concentration, which is almost one order of magnitude less than the California MCL for DBCP of 0.2 µg/L. CDPH (2008) states that arsenic is ubiquitous in nature and is commonly found in drinking water sources in California. The arsenic EPC for District Well No. 11 (1.2 µg/L) was based on the maximum detected concentration and is less than the California MCL for arsenic of 10 µg/L. ES - II Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc The District has taken the lead in constructing and operating a groundwater wellhead treatment system that will remove perchlorate and nitrate, and reduce VOC concentrations in groundwater. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc ES - III Section 1: Introduction Kennedy/Jenks Consultants (Kennedy/Jenks) has prepared this Human Health Risk Assessment Report (HHRA report) on behalf of the West Valley Water District (the District) and the City of Rialto (the City). This HHRA report presents the evaluation of potential human health risks associated with domestic use of groundwater from two production wells (Rialto Well No. 6 and District Well No. 11), assuming that the wells were restored to service and no reduction in the concentrations of contaminants occurs through treatment or response actions. The goal of the HHRA is to provide an analysis of baseline risks, which are defined as the “risks that might exist if no remediation or institutional controls were applied at a site” (United States Environmental Protection Agency [USEPA] 1989). Therefore, this HHRA evaluated baseline risks for the two production wells as the risks that might exist if the groundwater was used without any pretreatment or reduction in contaminants through response actions. 1.1 Background and Regulatory Context Together, the District and the City provide water for residential and commercial/industrial uses in the City of Rialto. The District and the City obtain water from several different sources, including groundwater wells, surface water sources and the State Water Project; however, groundwater accounts for more than two thirds of these supplies (ERSC 2006, Egan 2006). In recent years, perchlorate has been detected in several of the District’s and City’s production wells at concentrations exceeding the maximum contaminant level (MCL) of six micrograms per liter (µg/L) established by the California Department of Public Health (CDPH). The District and City have removed these production wells from service, pending installation of appropriate treatment systems. The loss of these wells has made it challenging for the District and the City to maintain operational flexibility and to meet seasonal peak water demands. Accordingly, the City and the District have established a cooperative agreement to restore two of the production wells to service. Under this agreement, the District has taken the lead for the planned construction and operation of a groundwater wellhead treatment system that will remove perchlorate and nitrate from groundwater, and reduce volatile organic compound (VOC) concentrations in groundwater. Groundwater pumped from Rialto Well No. 6 (located off Etiwanda Avenue in Rialto) and District Well No. 11 (located off Willow Avenue in Rialto) will be conveyed approximately 6,300 linear feet via existing and new underground pipelines to a treatment facility to be constructed at the District’s headquarters, located at 855 West Base Line Road, Rialto, California. The wellhead treatment system and associated piping will be referred to herein as the Project. Upon successful completion of a required initial startup demonstration period (of up to one year) to be overseen by CDPH, approximately 2,000 gallons per minute (gpm) of treated groundwater will be restored to the District’s drinking water supply for distribution. Figure 1 provides a map of the general area. The Project will be implemented at the same time as other perchlorate cleanup projects in the vicinity. In particular, a 160-acre parcel located on the corner of West Casa Grande Drive and Locust Avenue in Rialto was previously identified by the USEPA as a Superfund site under the federal Comprehensive Environmental Response, Compensation and Liability Act (CERCLA) (USEPA 2009a). Cleanup activities at and near the 160-acre site are focusing on remediating the source of contamination. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Page 1 The wells to be used by the District and the City for the Project are not part of the Superfund site; however, they are located immediately downgradient of the 160-acre parcel. Therefore, the District and the City plan to implement the Project in accordance with applicable requirements of Superfund, and regulations set forth in the National Contingency Plan (NCP) (40 Code of Federal Regulations [CFR], Part 300). Typically, when a cleanup project is implemented in accordance with the NCP, an environmental regulatory agency (such as the USEPA or the California Department of Toxic Substances Control [DTSC]) assumes responsibility for overseeing the investigation and cleanup activities. In this case, however, none of the agencies with a potential interest in the Project has requested an oversight agreement. Therefore the City will serve as the primary Project reviewer, and will accept comments from the agencies if provided. Concurrent with the NCP process, the District and the City will pursue from CDPH the required permit for restoring an impaired water source for use as public water supply, as directed in CDPH Policy Memo 97-005, Policy Guidance for Direct Domestic Use of Extremely Impaired Sources (CDPH 1997). 1.2 HHRA Objectives The general objective of a HHRA is to characterize the risks to human health that may be posed by chemicals present in or entering into environmental media (e.g., groundwater, surface water, air, or soil). The objective of the HHRA is to provide an analysis of baseline risks, which are defined as the “risks that might exist if no remediation or institutional controls were applied at a site” (USEPA 1989). The results of a HHRA help to establish acceptable exposure levels for use in developing appropriate response actions. The specific objective of this HHRA was to estimate the potential human health risks associated with domestic use of groundwater from two production wells (Rialto Well No. 6 and District Well No. 11), assuming that the wells were restored to service and no reduction in the concentrations of contaminants occurs through treatment or response actions. The objectives of the HHRA were to: ● ● ● ● ● Identify and select chemicals of potential concern (COPCs). Identify and estimate potential exposure pathways to individuals who may come in contact with COPCs in groundwater from the two production wells. Characterize potentially exposed populations and estimate the extent of their exposure to COPCs in groundwater from the two production wells. Identify the potential cancer risk and health hazards associated with the COPCs. Quantitatively characterize the noncarcinogenic and carcinogenic risks to the potentially exposed human populations posed by the COPCs in groundwater from the two production wells. Figure 2 provides a general schematic that outlines the process that was followed in this HHRA to estimate the potential human health risks associated with domestic use of groundwater from the two production wells. 1.3 HHRA Approach The approach and methods that were used to perform this HHRA were consistent with risk assessment guidance published by the DTSC, and with similar guidance from the USEPA for Page 2 Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc issues not addressed by the State of California. The HHRA incorporated health-protective assumptions in estimating the potential health risk associated with domestic use of water from the two production wells (Rialto Well No. 6 and District Well No. 11). Current regulations and applicable HHRA guidance that were used in this HHRA included the following: ● Supplemental Guidance for Human Health Multimedia Risk Assessments of Hazardous Waste Sites and Permitted Facilities (DTSC 1996) ● Preliminary Endangerment Assessment Guidance Manual (DTSC 1994) ● Risk Assessment Guidance for Superfund, Volume 1: Human Health Evaluation Manual (Part A) (USEPA 1989) ● Risk Assessment Guidance for Superfund Volume 1: Human Health Evaluation Manual (Part D, Standardized Planning, Reporting and Review of Superfund Risk Assessments) (USEPA 2001) ● Risk Assessment Guidance for Superfund Volume 1: Human Health Evaluation Manual (Part E, Supplemental Guidance for Dermal Risk Assessment) (USEPA 2004) ● Risk Assessment Guidance for Superfund Volume 1: Human Health Evaluation Manual (Part F, Supplemental Guidance for Inhalation Risk Assessment) (USEPA 2009b) 1.4 Report Organization The organization of this HHRA report is as follows: Section 2.0 Background and Description of Area – This section presents a description of the project area, water supply sources, and background information on the two production wells. Section 3.0 Identification of Chemicals of Potential Concern – This section summarizes the data used in the assessment and identifies the COPCs. Section 4.0 Exposure Assessment – This section identifies potentially complete routes of exposure and potential receptor populations, as well as the exposure assumptions to estimate doses of COPCs. Section 5.0 COPCs. Toxicity Assessment – This section presents the toxicological data for the Section 6.0 Risk Characterization – This section presents the noncarcinogenic and carcinogenic risk estimates. Section 7.0 Uncertainty Assessment – This section discusses the uncertainties inherent in performing an HHRA. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Page 3 Section 8.0 Summary and Conclusion – This section summarizes and presents the conclusions of this HHRA. References – This section provides the references used in the development of this HHRA. Page 4 Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Section 2: Background and Description of Area This section presents a description of the project area, water supply sources, and background information on the two production wells. 2.1 Description of Area The Project site is located in the City of Rialto, San Bernardino County, California, approximately 60 miles east of Los Angeles (Figure 1). The City is situated in the San Bernardino Valley, within the Santa Ana River Basin Watershed (ERSC 2006). The population of the City as of 2008 was approximately 100,000. Land use in the area during the first half of the 20th century was mostly agricultural, but is now dominantly residential, industrial, and commercial. The land surface slopes gently to the southeast from a high of approximately 2,000 feet above sea level at the base of the San Gabriel Mountains, to a low of approximately 950 feet near the Santa Ana River. The elevation at the Project site is approximately 1,300 feet above sea level. 2.2 Water Supply in the Rialto Area The Project site is located in the central part of the Rialto Colton Basin (RCB), one of several groundwater basins associated with the San Bernardino sedimentary basin (Figure 1). Groundwater has been a primary water source in the region for decades, and the RCB has provided a substantial portion of the overall groundwater supply. In addition to the District and the City, the City of Colton and Fontana Water Company also produce significant amounts of groundwater from the RCB. The District service area is split into northern and southern portions by the City’s service area (Figure 3). Approximately one-half of the City residents are served by the District (ERSC 2006, Egan 2006). The three primary sources of water for the District are local surface water, groundwater, and water imported from the State Water Project. The District’s total water demand for the period 2000-2004 ranged from 19,698 to 22,374 acre-feet per year (AFY), with groundwater supplying between 56 and 72 percent of the total demand (ERSC 2006). The City uses the same three water sources as the District, plus additional water from the San Bernardino Valley Municipal Water District. The City’s total water demand for the period 2000-2004 ranged from 13,927 to 14,281 AFY, with groundwater supplying between 64 and 73 percent of the total demand. The City also supplied approximately 2,500 AFY to the Marygold Mutual Water Company (Egan 2006). 2.2.1 Rialto Well No. 6 Rialto Well No. 6 (1S/5W-2G1) is located approximately 300 feet north of W. Etiwanda Avenue and 670 feet west of N. Riverside Avenue in Rialto. Drilling for Rialto Well No. 6 was completed on 15 March 1989. The total depth of the borehole for Rialto Well No. 6 is 1,000 feet, and the well casing has two perforated, or screened, intervals. The depths of these screened intervals below land surface are 440-830 feet and 930-970 feet. The reported pumping capacity of Rialto Well No. 6 is 2,510 gpm with production and permitted capacities of 3.61 million gallons per day (mgd) (Egan 2006). Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Page 5 2.2.2 District Well No. 11 District Well No. 11 (1S/5W-2K1) is located approximately 1,800 feet north of W. Foothill Boulevard and 200 feet east of N. Willow Ave in Rialto. Drilling for District Well No. 11 was completed on 2 July 1929. The total depth of the borehole for District Well No. 11 is 828 feet, and the well casing has twelve perforated, or screened, intervals. The depths of these screened intervals below land surface are: 310-370 feet 388-402 feet 414-436 feet 436-502 feet 506-534 feet 586-592 feet 618-622 feet 622-632 feet 684-694 feet 700-748 feet 766–776 feet 782-787 feet The reported pumping capacity of District Well No. 11 is 1,650 gpm with production and permitted capacities of 1.6 mgd (ESRC 2006). Page 6 Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Section 3: Identification of Chemicals of Potential Concern Water quality data for the Rialto Well No. 6 and District Well No. 11 were obtained from the historical water quality database maintained by CDPH, which requires all certified drinking water analytical laboratories to submit water quality data directly to CDPH in electronic form. Studies not requiring reporting to CDPH were not included in the HHRA data set. The water quality data are included in Appendix A. 3.1 Available Data and Data Reduction Water quality monitoring data for Rialto Well No. 6 and District Well No. 11 were evaluated in this HHRA. Water quality monitoring data include analytes required by Title 22 of the California Code of Regulations for community water systems. To focus the HHRA on more current conditions, the HHRA only evaluated data collected during the period of 1999 through 2010. Samples in the data set collected on the same day were assumed to be duplicates. Field duplicate samples were reduced as follows: If analytical results for both samples were detected values, the maximum detected concentration was used in the exposure point concentration (EPC) calculations If the analytical result for one sample was a detected value and the other sample was a non-detect, the detected value was used in the EPC calculations If analytical results for both samples were non-detects, the lower reporting limit (RL) was used as a non-detect in the EPC calculations. For cases in which a non-detected result was reported, but the method detection limit was not listed in the database, the detection limit for reporting (DLR) for drinking water analysis under the CDPH was assumed to be the detection limit (CDPH 2010). Finally, the different nitrogen species reported in the data set were revised for evaluation purposes. Specifically, the detected concentrations for samples analyzed for nitrate (NO3) as nitrate were converted to results reported as nitrate as nitrogen (NO3-N) using a conversion factor of 4.4, in order to compile these results with other data based on methods analyzing for NO3-N. Uncertainties associated with this conversion are discussed in Section 7.1. Both dissolved nitrate and unfiltered nitrate results were assessed as the same constituent without adjustments to either result. The uncertainties associated with this assumption are also discussed in Section 7.1. The results reported as a combination of both nitrate and nitrite (as nitrogen) were not used in this HHRA due to uncertainties with the toxicity of the mixture of nitrogen species. 3.2 Identification and Selection of Chemicals of Potential Concern The COPCs for quantitative risk assessment were selected in accordance with USEPA risk assessment guidelines (USEPA 1989). The COPCs are a subset of the chemicals detected in Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Page 7 groundwater samples collected from the two production wells. An iterative, multi-step process was used to review all detected chemicals to focus on those chemicals that may contribute appreciably to potential health risks associated with domestic use of groundwater from the two production wells, assuming that no reduction in the concentration of contaminants occurs through treatment or response actions. 3.2.1 Carcinogenic Classification Following USEPA (1989) guidelines, detected chemicals with a USEPA carcinogenic classification of A or classified as carcinogenic using USEPA’s Guidelines for Carcinogen Risk Assessment (2005), were retained as COPCs based on the carcinogenic screen. 3.2.2 Frequency of Detection The frequency of detection was used as a criterion for identifying chemicals that present a greater potential for exposure to the potential receptor population. Chemicals detected in more than 5 percent of the samples (with a sample population of at least 20) were initially selected as COPCs, or eliminated if detected in less than 5 percent of the samples at low concentrations (USEPA 1989) (with the exception of Group A carcinogens). 3.2.3 Comparison with Risk-Based Levels To further screen the candidate chemicals that were not eliminated as COPCs during evaluation of the screening criteria listed above, a risk-based benchmark value screen was performed. The objective of the risk-based benchmark value screen is to identify chemicals in a particular medium (e.g., groundwater) that (based on concentration and toxicity) are most likely to contribute significantly to risks calculated for exposure scenarios involving that medium. Thus, the preliminary HHRA focuses on the “most significant” chemicals (USEPA 1989). The maximum concentrations of the remaining candidate COPCs were compared to the screening benchmark. If the maximum detected concentration was less than the benchmark, the chemical was eliminated as a COPC under current and future exposure scenarios for purposes of this HHRA. The health-based screening criteria were selected according to a hierarchy. If available, public health goals (PHGs) established by the California Office of Environmental Health Hazard Assessment (OEHHA) were used as the screening benchmark. PHGs represent concentrations of drinking water contaminants that pose no significant health risk if consumed for a lifetime, based on current risk assessment principles, practices, and methods. If a PHG has not been established, then the USEPA (2010a) Regional Screening Level (RSL) for tap water was used. RSLs are generic risk-based concentrations derived from standardized risk equations and USEPA toxicity data. 3.3 Chemicals of Potential Concern The results of the COPC screening evaluation are summarized in Table 1. The chemicals identified as COPCs for further evaluation in the HHRA were: Inorganic anions: perchlorate, NO3-N, and fluoride Page 8 Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Metals: arsenic and hexavalent chromium Volatile organic compounds (VOCs): 1,2-dibromo-3-chloropropane (DBCP), chloroform, and trichloroethene (TCE). Of these COPCs, only perchlorate, NO3-N, and TCE were detected at concentrations above the respective California primary MCL. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Page 9 Section 4: Exposure Assessment The objective of the exposure assessment was to evaluate the ways people might be exposed to COPCs (exposure pathway) and at what levels they could be exposed (dose). The exposure assessment outline followed USEPA guidelines and used the reasonable maximum exposure (RME) methods recommended by USEPA. The USEPA (1989) guidance has identified four primary tasks for an exposure assessment: ● First, identify potentially exposed human populations that may come in contact with the COPC. This requires knowledge of (and/or making reasonable assumptions regarding) both current and future populations. ● Second, identify relevant exposure pathways for human populations by which potentially exposed populations may contact COPCs originating from groundwater. ● Third, estimate EPCs at the points of potential human contact for all identified COPCs. EPCs for chemicals detected in groundwater were derived directly from detected concentrations. ● Fourth, estimate chronic daily intakes (CDI) for exposure routes and potentially exposed populations. The CDIs were derived using the EPCs and RME assumptions regarding such variables as exposure duration, skin absorption factors, and various parameters that describe human activities. The HHRA characterized the risk to human health associated with potential use of untreated groundwater pumped from District Well No.11 and Rialto Well No. 6. The HHRA is not designed to consider all of the potential sources of exposure to perchlorate and nitrate (such as other beverages or food). 4.1 Identification of Potentially Exposed Populations Potentially exposed populations for evaluation in the HHRA were identified based on consideration of the current and future use category and USEPA (1989) guidance. Because Rialto Well No. 6 is not currently used for domestic supply and District Well No. 11 is provided with treatment, the only potentially exposed populations are under future use conditions if the production wells were restored to service without treatment. The scenarios for future use conditions consider the following potential receptors: ● ● Adult Water Consumer (Adult Resident) Child Water Consumer (Child Resident) 4.2 Identification of Relevant Exposure Pathways USEPA guidance documents were used to identify relevant exposure pathways for evaluation in the HHRA. USEPA (1989) describes exposure pathways consisting of four necessary elements: ● Source and mechanism of chemical release Page 10 Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc ● ● ● Retention or transport medium (or media in cases involving media transfer) Point of potential human contact with the COPC-containing medium (referred to as an exposure point) Exposure route (e.g., ingestion) at the exposure point The currently known and identified affected medium is groundwater from the two production wells. The exposure points are the locations where potentially exposed populations may come in direct contact with the detected chemicals. The exposure routes are defined as the physical pathways through which chemicals may enter the human body (e.g., ingestion, inhalation, dermal absorption). This HHRA followed USEPA guidance by identifying exposure points and potential exposure routes for both current and reasonably foreseeable future land use conditions. The potential exposure pathways that were evaluated in the HHRA included: ● ● ● Ingestion of COPCs in groundwater Inhalation of COPCs from groundwater Dermal contact with COPCs in groundwater A pathway is considered “complete” if there is a source or chemical release from a source, an exposure point where contact can occur, and an exposure route by which contact can occur. Because the depth to groundwater in the Basin is greater than 15 feet below ground surface, the only potential exposure points would be when the groundwater is pumped to the surface for domestic use. The conceptual site model representing all potentially exposed populations and complete exposure pathways is shown on Figure 4. 4.3 Process to Estimate Exposure Point Concentrations The EPC represents the chemical concentration in the exposure medium (e.g., groundwater) that the receptor will potentially come into contact with during the exposure duration (e.g., 30 years for an adult resident). A trend analysis was performed on COPCs at each well to determine the appropriate data set for each EPC calculation. When a COPC was detected at least five times since 1999, and showed an upward or downward trend over time, historic data were removed from the dataset so that only the most recent, stable results were used in the EPC calculations. The exception is for TCE at the District Well No.11 exposure point, for which a trend extends to the most recent sampling event. For TCE at the District Well No.11 exposure point, the maximum detected concentration was conservatively used as the EPC. The results of the trend analysis are provided in Appendix B. The date ranges for the data sets used for each EPC calculation and the resulting EPCs are shown in Table 2. DTSC (1996) defines the EPC as the lesser of the maximum-detected concentration and the 95 percent upper confidence limit of the arithmetic mean (95% UCL) of sample data. The 95% UCL values were calculated using the USEPA software ProUCL (Version 4.00.05). USEPA (2010b) recommends not using substitution methods (e.g., one-half the detection limit substitution method) for managing non-detect values in the data set. ProUCL (Version 4.00.05) performs EPC calculations incorporating data reported as non-detects by using estimation Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Page 11 methods (e.g., regression on order statistics and Kaplan-Meier methods) instead of using substitution methods (USEPA 2010b). Data reported as non-detect concentrations were managed in accordance with ProUCL User’s Guide (USEPA 2010b). The ProUCL output files are included in Appendix C. Environmental media concentrations often show lognormal or other non-normal distributions. The groundwater data were tested for normal, gamma, and lognormal distributions using the current version of ProUCL. Data were tested first for normality, then for gamma distributions, and finally for lognormal distributions, as recommended by ProUCL guidance (USEPA 2010b). The 95% UCL was then determined and used as the EPC based on the recommendations from ProUCL guidance (USEPA 2010b). If the data set did not contain enough detected concentrations to calculate a 95% UCL using ProUCL, then the maximum detected concentration was used as the EPC. 4.4 Process to Estimate Chronic Daily Intakes For oral and dermal exposure pathways, intakes of COPCs by potentially exposed receptors were quantified in the HHRA by estimating the mass of substance taken into the body per unit body weight per unit time (milligrams per kilogram per day [mg/kg-day]). For the inhalation exposure pathway, intakes of COPCs by potentially exposed receptors were quantified in the HHRA by estimating a time-weighted exposure concentration (EC) that takes into consideration the exposure time, frequency, and duration for each receptor being evaluated as well as the period over which the exposure is averaged (i.e., the averaging time [AT]). The CDI (i.e., dose) for each exposure medium was calculated using media-specific equations based on exposure parameters that represent the duration of exposure, frequency of exposure, and other factors that affect overall intake. The methodology for incorporating the averaging time term in the dose equations was consistent with USEPA (1989) HHRA guidelines. For noncarcinogenic COPCs, the CDI is averaged over the duration of the exposure to the COPC. For evaluation of carcinogenic COPCs, the CDI is expressed as a lifetime average daily intake (LADI) because dose is averaged over the entire lifetime. The USEPA (1989) states that the approach for carcinogens is based on the assumption that a high dose received over a short period of time is equivalent to a corresponding low dose spread over a lifetime. The calculated LADI for the adult resident is greater than the LADI for the child resident because the length of exposure is greater for the adult resident compared to the child resident while the averaging time term is the same (see Table 3). As presented in Section 5, the cancer risk estimates are greater for the adult resident relative to the child resident due to the methodology in calculating the LADI. In contrast, for noncarcinogenic exposures, the CDI for the child resident is greater than the CDI for the adult resident because the averaging time terms are based on the exposure duration. As a result, the noncancer hazards are greater for the child resident relative to the adult resident. 4.4.1 Route-Specific Assumptions Ingestion, inhalation, and dermal contact are complete exposure pathways for future use of groundwater as a domestic supply. The route-specific assumptions are presented in Tables 3 and 4 and discussed below. Page 12 Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc 4.4.1.1 Ingestion of Groundwater Ingestion of groundwater occurs through daily water consumption, including beverages made using drinking water. USEPA recommendations were used in calculating the chemical intake from ingestion of groundwater. Contaminated groundwater was assumed to be the only source of water for potentially exposed populations. The daily water consumption rates were 2 liters per day (L/day) for adults and 1.5 L/day for children (USEPA 1997). 4.4.1.2 Inhalation of Vapors Exposure to COPCs in water via inhalation of vapors occurs during uses of domestic water (e.g., showering) and is dependent on the volatilization of the COPC, the inhalation rate, and the exposure duration. As was assumed in establishing RSLs for tap water, inhalation of vapors from groundwater was only considered a complete exposure pathway for COPCs with a Henry’s Law constant of 1 x 10-5 atm-m3/mole or greater and with a molecular weight less than 200 grams/mole (USEPA 2010a). For this HHRA, the COPCs that are classified as volatile and for which inhalation of vapors is considered a potentially complete exposure pathway are DBCP, chloroform, and TCE. A volatilization factor (VFw) of 0.5 liters per cubic meter (0.5 L/m3) was used to derive a COPC concentration in indoor air based on the COPC concentration in the domestic water. The VFw of 0.5 L/m3 is based on USEPA (1991) guidance and is used by USEPA (2010a) in the derivation of the RSLs. It was assumed that inhalation of vapors from domestic uses of groundwater occurs 24 hours per day. 4.4.1.3 Dermal Contact with Groundwater Exposure to COPCs in water via dermal contact occurs during bathing and showering and is dependent on the dermal permeability of the COPC, the body area exposed, and the exposure duration. USEPA recommendations were used in calculating chemical intake through dermal contact. The exposed body area for bathing and showering was assumed to be 23,000 square centimeters (cm2) for adults and 10,000 cm2 for children. One of the parameters in the intake equations for dermal contact with groundwater is the absorbed dose per event (DAevent). This parameter was derived per EPA guidance (2004) using chemical-specific factors, which are presented in Table 4. The chemical specific factors used in the calculation of DAevent were obtained from Appendix B (Screening Tables and Reference Values for the Water Pathway) of USEPA’s Supplemental Guidance for Dermal Risk Assessment (2004). 4.4.2 Chronic Daily Intake Equations The equations and exposure parameters used to calculate the CDI or LADI for complete exposure pathways for potentially exposed receptor populations under current and future landuse scenarios are presented in Tables 3 and 4 discussed below. The human intake equations were derived from USEPA guidance (USEPA 1989, 1991). For inhalation exposures, a concentration-based approach is used to assess risks for consistency with the inhalation dosimetry methodology (USEPA 2009). 4.4.2.1 Ingestion of Chemicals in Groundwater The CDI or LADI of chemicals in groundwater via ingestion is estimated by: Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Page 13 Intake (mg/kg-day) = EPCxWIRxEFxED BWxAT Where: EPC = chemical concentration in water (mg/L) WIR = water ingestion rate (L/day) EF = exposure frequency (days/year) ED = exposure duration (years) BW = body weight (kg) AT = averaging time (days) 4.4.2.2 Inhalation of Chemicals in Groundwater The concentration for exposure to chemicals in groundwater via inhalation is estimated by: Exposure Concentration (mg/m3) = EPCxVFwx( ET / 24hours / day ) xEFxED AT Where: EPC = chemical concentration in water (mg/L) VFw = volatilization factor for water (L/m3) ET = exposure time (hours/day) EF = exposure frequency (days/year) ED = exposure duration (years) AT = averaging time (days) 4.4.2.3 Dermal Contact with Chemicals in Groundwater The CDI or LADI of chemicals in groundwater via dermal contact is estimated by: Intake (mg/kg-day) = EPCxSAxDAw xEVxEFxED BWxAT Where: EPC = chemical concentration in water (mg/L) SA = skin surface area exposed to water (cm2) DAw = dermal absorbed dose for water (L/cm2-ev) EV = event frequency (events/day) EF = exposure frequency (days/year) ED = exposure duration (years) BW = body weight (kg) AT = averaging time (days) Page 14 Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Section 5: Toxicity Assessment The purpose of the toxicity assessment is to evaluate the potential for each COPC to cause adverse effects in those individuals who potentially could be exposed over an extended period of time. Adverse chronic health effects in humans include both noncarcinogenic and carcinogenic health effects. This section presents the approach that was used to evaluate both noncarcinogenic and carcinogenic health effects of the COPCs selected for quantitative evaluation in the HHRA. Noncarcinogenic and carcinogenic toxicity values are presented in Tables 5 and 6, respectively. Toxicity values for the inhalation pathway are only presented for volatile COPCs. 5.1 Sources of Toxicity Values Toxicity values that describe the relationship between exposure to a chemical and the associated increased likelihood of adverse effects were compiled. Toxicity values provided by Cal EPA (OEHHA 2010) were used as the primary source of toxicity values for the HHRA. If Cal EPA did not provide toxicity values for a COPC, then toxicity values were obtained from USEPA’s Integrated Risk Information System (IRIS) database, which is USEPA’s preferred source of information because IRIS represents the official agency scientific position regarding the toxicity of the chemicals based on the data available at the time of the review (USEPA 2003). 5.2 Chemicals of Potential Concern with Noncarcinogenic Effects Oral reference doses (RfDs) and reference concentrations for inhalation (RfCs) are toxicity values developed for chemicals exhibiting noncarcinogenic effects. RfDs and RfCs are usually derived from no-observable-adverse-effect levels (NOAELs) taken either from human studies, often involving workplace exposures, or from animal studies, and are adjusted downward using uncertainty or modifying factors. For example, a modifying factor of 2 to 10 may be applied if the database on a particular COPC lacks information on possible reproductive or developmental toxicity. Uncertainty factors are generally applied to adjust for the possibility that humans are more sensitive than experimental animals and that there may be sensitive subpopulations (e.g., children, pregnant women, individuals with hay fever, or asthma). Depending upon the information available, other factors may also be applied. RfDs and RfCs are intended as conservative estimates of the daily exposure to a COPC that would not cause adverse effects even if exposure occurs continuously over a lifetime. Table 5 presents the toxicity values used in this HHRA to evaluate noncarcinogenic health effects. The following sections provide additional detail on noncarcinogenic health effects for the COPCs. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Page 15 5.2.1 1,2-Dibromo-3-chloropropane OEHHA developed a public health protective water concentration for DBCP (0.2 µg/L) based on a noncarcinogenic toxic endpoint (OEHHA 1999). OEHHA (1999) identified testicular effects as the most sensitive noncarcinogenic toxic endpoint, based on toxicity studies of test animals. The NOAEL derived from this test animal study was 0.025 mg/kg-day. OEHHA applied an uncertainty factor of 1,000 to the NOAEL (10 for interspecies variability, 10 for intraspecies variability, and 10 for the use of a subchronic NOAEL) in the development of the public health protective water concentration for DBCP based on a noncarcinogenic toxic endpoint. The oral RfD for DBCP (0.000025 mg/kg-day) used in this HHRA is derived from the NOAEL (0.025 mg/kg-day) divided by an uncertainty factor of 1,000. The inhalation RfC used in this HHRA for DBCP (2.0 x 10-4 milligrams per cubic meter [mg/m3]) was obtained from the IRIS database (USEPA 2010c). 5.2.2 Arsenic OEHHA (2004a) developed a noncarcinogenic health protective value for arsenic of 0.9 μg/L based on vascular effects in a human epidemiological study of cerebrovascular disease. OEHHA (2004a) used a benchmark dose approach to derive this value based on the lower bound of the lowest effective dose of 3.0 milligrams per liter (mg/L)-year with an uncertainty factor of 10 and a relative source contribution of 0.2. The studies cited in OEHHA (2004a) do not provide sufficient information to calculate an oral RfD. The oral RfD (0.0003 mg/kg-day) from the IRIS database (USEPA 2010c) is based on a NOAEL of 0.009 mg/L, which is equivalent to the lowest effective dose of 3.0 (mg/L)-year with a relative source contribution of 0.2. As a result, the oral RfD from IRIS was used in this HHRA. 5.2.3 Chloroform OEHHA has not developed a PHG for chloroform. The oral RfD (0.01 mg/kg-day) used for chloroform in this HHRA was obtained from the IRIS database (USEPA 2010c). The inhalation RfC used for chloroform in this HHRA (1.5 x10-5 mg/m3) is the chronic REL listed for chloroform by OEHHA (2008). 5.2.4 Fluoride OEHHA (1997a) developed a PHG for fluoride of 1 mg/L based on a NOAEL of 1 mg/L for dental fluorosis in children. The NOAEL of 1 mg/L is also used by the USEPA (2010c) to derive the oral RfD listed in the IRIS database. The oral RfD of 0.06 mg/kg-day listed by the USEPA (2010c) in the IRIS database was used as the oral RfD in this HHRA. The USEPA (2010c) did not apply uncertainty factors since the NOAEL is that of the critical effect (i.e., dental fluorosis) in a sensitive population of humans (i.e., children) for a length of exposure that encompasses both the critical effect and the sensitive population. 5.2.5 Hexavalent Chromium OEHHA has not developed a PHG for hexavalent chromium. The oral RfD (3 x10-3 mg/kg-day) used for hexavalent chromium in this HHRA was obtained from the IRIS database (USEPA 2010c). Page 16 Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc 5.2.6 Nitrate and Nitrite The primary adverse health effect associated with human exposure to nitrate or nitrite is methemoglobinemia (OEHHA 1997). Methemoglobinemia is the oxidation of normal hemoglobin to methemoglobin, which is unable to transport oxygen from the lungs to tissues. Nitrate must be converted to nitrite to cause methemoglobinemia. The conversion of nitrate to nitrite is mediated by bacteria in the gastrointestinal system. OEHHA (1997) identified infants as the subpopulation that is most susceptible to nitrate-induced methemoglobinemia based on several factors: “1) infants have a greater total fluid intake per unit body weight than adults, 2) the gastrointestinal system in infants normally has a high pH that allows bacterial proliferation and nitrate catalysis to nitrite, 3) frequent occurrences of infant gastroenteritis may favor the development of methemoglobin when the upper gastrointestinal tract becomes colonized with bacteria, 4) fetal hemoglobin is more readily oxidized than adult hemoglobin and 5) infants have half the methemoglobin reductase activity of older children and adults and are therefore less capable of metabolizing excess methemoglobin”. OEHHA (1997) has adopted the following PHGs for nitrogen species: Nitrate = 10 mg NO3-N/L = 45 mg nitrate/L, Nitrite = 1 mg nitrite-nitrogen/L; and Joint nitrate/nitrite = 10 mg/L, expressed on a nitrogen basis. The PHGs are based on USEPA’s previous analysis on nitrate and nitrite, which considered “the conversion of nitrate to nitrite, nitrite-induced formation of methomoglobin, and the general absence of methemoglobinemia occurring at nitrate-nitrogen levels below 10 mg/L based on worldwide epidemiological evidence”. The USEPA (2010c) lists an oral RfD for NO3-N of 1.6 mg/kg-day based on a NOAEL of 10 mg/L1. The NOAEL of 10 mg/L is based on human studies using the most sensitive population (infants); therefore, no additional adjustment using modifying and uncertainty factors was applied by the USEPA. The oral RfD of 1.6 mg/kg-day was used in this HHRA to evaluate noncancer hazards for NO3-N. 5.2.7 Perchlorate Adverse health effects observed in both test animals and humans exposed to perchlorate are related to the disruption of thyroid hormone regulation. Animal and human studies have demonstrated that perchlorate inhibits the “sodium-iodide symporter” (NIS), disrupts thyroidpituitary homeostatis, and causes pathological changes of the thyroid and sometimes even thyroid tumors. OEHHA (2004b) identifies the inhibitory effect of perchlorate on the uptake of iodide (i.e., inhibit the NIS) as the critical event for assessing perchlorate risk. The nature and severity of the effects are related to the extent and duration of perchlorate exposure as well as the iodine status of the individual. OEHHA (2004b) identified four sensitive subpopulations for perchlorate toxicity: (i) pregnant women and their fetuses, especially those who are getting less 1 Expressed as the amount of nitrogen within the nitrite molecule commonly shown as mg NO3-N/L (1 mg NO3-N = 4.4 mg nitrate). Doses based on ingestion of drinking water used to prepare infants' formula: 0.64 L/day by a 4 kg infant (0.16 L/kg/day). 10 mg/L x 0.64 L/day divided by 4 kg = 1.6 mg/kg/day (USEPA 2010c). Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Page 17 than a sufficient amount of iodine; (ii) lactating women, especially those who are getting less than a sufficient amount of iodine, (iii) infants; and (iv) individuals with thyroid problems. OEHHA (2004b) defines the benchmark dose for perchlorate as the dose that reduces mean thyroidal iodide uptake by five percent based on the study by Geer et al. (2002) (as cited by OEHHA 2004b). The lower limit of the benchmark dose (BMDL) is defined as the lower limit of a one-sided 95 percent confidence interval of the benchmark dose (BMD). The estimated BMD and BMDL are 0.0068 mg/kg-day and 0.0037 mg/kg-day, respectively. The oral RfD (0.00037 mg/kg-day) used in this HHRA for assessing perchlorate toxicity is equal to the BMDL of 0.0037 mg/kg-day divided by an uncertainty factor of 10. OEHHA (2004b) applied an uncertainty factor of 10 for inter-individual variability to the BMDL to account for exposures by sensitive subpopulations (pregnant or lactating women, infants, and individuals with thyroid problems). 5.2.8 Trichloroethene The primary adverse health effect associated with human exposure to TCE in drinking water is kidney nephropathy. OEHHA (2009) presented a benchmark dose of 50 mg/kg-day, for kidney nephropathy, as the most appropriate endpoint for derivation of a non-cancer health-protective value. OEHHA (2009) applied an uncertainty factor of 10 for inter-species extrapolation and 10 for intraspecies variation, including potential susceptible subpopulations. The oral RfD for TCE (0.5 mg/kg-day) used in this HHRA is equal to the benchmark dose of 50 mg/kg-day divided by the uncertainty factor of 10 for inter-species extrapolation and 10 for intraspecies variation. The inhalation RfC used for trichloroethene in this HHRA (0.6 mg/m3) is the chronic REL listed for TCE by OEHHA (2008). 5.3 Chemicals of Potential Concern with Carcinogenic Effects For carcinogenic health effects, the evaluation of a chemical involves two components: 1) a qualitative determination of the likelihood of it being a human carcinogen and 2) a quantitative assessment of the relationship between exposure dose and response. 5.3.1 Lines of Evidence for Carcinogenic Potential The 1986 USEPA classification system for the characterization of the overall weight of carcinogenicity has the following categories: Group A: "Human Carcinogen" Group B (1 and 2): "Probable Human Carcinogen" Group C: "Possible Human Carcinogen" Group D: "Not Classifiable as to Human Carcinogenicity" Group E: “Evidence of Non-Carcinogenicity for Humans” USEPA’s Guidelines for Carcinogen Risk Assessment (2005) emphasizes the importance of weighing individual lines of evidence in assessing the human carcinogenic potential of COPCs. Page 18 Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Various types of evidence are considered in the assessment. The 2005 USEPA classification system for the characterization of the overall weight of carcinogenicity has the following five categories: Carcinogenic to Humans. This category indicates strong evidence of human carcinogenicity. Likely to be Carcinogenic to Humans. This category indicates that there is adequate evidence to demonstrate carcinogenic potential but does not reach the weight of evidence for “Carcinogenic to Humans”. Suggestive Evidence of Carcinogenic Potential. This category indicates that there is evidence of carcinogenicity, but the data are not sufficient for a stronger conclusion. Inadequate Information to Assess Carcinogenic Potential. This category indicates that the available data are inadequate for applying a different category. Not Likely to be Carcinogenic to Humans. This category indicates that the available data are considered robust for deciding there is no basis for human hazard concern. Table 6 presents lines of evidence for carcinogenic potential for each of the COPCs where available. 5.3.2 Cancer Slope Factors A COPC that exhibits carcinogenicity is generally considered by USEPA to have no threshold (i.e., there is no dose below which a carcinogenic response, no matter how slight, might be expressed) (USEPA 1989). USEPA uses a linear-multistage low-dose extrapolation model for estimating cancer risk at low doses based primarily on animal data and on available epidemiological studies. This is recognized as a conservative approach to prevent underestimation of risk. These conservative cancer slope factors (CSFs) are commonly used in conducting health risk assessments. The CSF describes the increase in an individual's risk of developing cancer over a 70-year lifetime per unit of exposure. For inhalation, USEPA (2009b) uses unit risk to describe the increase in cancer risk. CSFs and unit risks are calculated using methods intended to be protective of human health and are based on the assumption that cancer risks decrease linearly with decreasing dose. The 95% UCL estimate for the slope is used in most cases to compensate for animal to human extrapolation and other uncertainties and generally is considered to be upper range estimates (worst case) of potential carcinogenic effects in humans. The unit risk is the upper-bound excess cancer risk from continuous exposure to a chemical at a concentration of 1 microgram per cubic meters (µg/m3) in air. Table 6 presents the toxicity values used to assess carcinogenic toxicity in this HHRA. 5.4 Dermal Toxicity Assessment Most toxicity values are based on oral, not dermal, exposures. For oral exposures, toxicity values are often expressed as the amount of substance administered, whereas dermal Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Page 19 exposures are expressed as absorbed dose. USEPA has developed a simplified method for oral-to-dermal extrapolations (USEPA 2004). These extrapolations involve an adjustment to the oral toxicity value based on the gastrointestinal (GI) absorption factor of the specific chemical in the same administration vehicle (e.g., corn oil, food) as used in the critical toxicity study to derive an estimated dermal dose. As recommended by USEPA guidance (USEPA 2004), an adjustment to the oral toxicity factor to account for the estimated absorbed dose was applied in the HHRA when the following conditions were met: The toxicity value derived from the critical study is based on an administered dose (e.g., through diet or by delivery by forced feeding through a tube) A scientifically defensible database demonstrates that the GI absorption of the chemical is less than 50% in a medium similar to the one used in the critical study. If both of these conditions were met, the oral toxicity factor was adjusted to reflect the absorbed dose in the HHRA. For carcinogenic effects, the oral CSF was divided by the GI absorption factor to estimate the dermal SF. For noncarcinogenic effects, the oral RfD was multiplied by the GI absorption factor to estimate the dermal RfD. If both conditions for adjustment were not met, the oral toxicity value was used as a surrogate for the dermal toxicity value in the HHRA. Hexavalent chromium was the only COPC for which both conditions were met and the oral RfD was adjusted using the GI absorption factor (0.025) for hexavalent chromium listed by USEPA (2004). Page 20 Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Section 6: Risk Characterization Risk characterization integrates the information from the exposure assessment and toxicity assessment using a combination of qualitative and quantitative information. With this information, risk characterization estimates the potential health risk based on the dose of a chemical that a person may receive under certain site-specific exposure conditions and the toxicity of that chemical. To characterize potential noncarcinogenic effects, comparisons were made between projected intakes of substances and toxicity values. To characterize potential carcinogenic effects, projected intakes and chemical-specific dose-response data were used to estimate the incremental probability that an individual will develop cancer over a lifetime of exposure. Tables 7 through 12 present the results of the risk characterization. The following sections discuss the methodology to calculate noncancer hazard and cancer risk estimates and the results of the risk characterization. 6.1 Noncancer Hazard Estimates The potential for adverse effects resulting from exposure to chemicals with noncarcinogenic effects is generally addressed by comparing the COPC-specific average daily intake (i.e., dose) to its RfD. This comparison was made by calculating the ratio of the estimated CDI to the corresponding RfD to yield a hazard quotient (HQ): HQ CDI RfD Tables 7 and 9 present the HQs separately for adult and child residents. Estimated HQs were compared to the DTSC point of departure of 1 for noncarcinogenic effects. HQs are typically summed across chemicals to calculate a hazard index (HI); however, the HI is only toxicologically relevant for chemicals which have the same toxic manifestation or affect the same target organ. Because none of the chemicals have the same toxicity endpoint for noncarcinogenic effects, HIs were not calculated. 6.2 Cancer Risk Estimates Potential cancer risks were assessed by multiplying the estimated LADI (i.e., lifetime dose) of a carcinogen by its CSF. This calculated risk is expressed as the probability of an individual developing cancer over a lifetime as a result of exposure to the potential carcinogen, and is an estimated upper-bound incremental probability of excess individual lifetime cancer risk. Risk LADI * CSF Tables 8 and 10 present the cancer risks separately for adult and child residents. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Page 21 Initially, potential cancer risks for exposure to each chemical for each exposure pathway were estimated separately. The separate potential cancer risk estimates were summed across chemicals and across all exposure pathways to obtain the total potential excess lifetime cancer risk for the potentially exposed population. Estimated cancer risks for individual COPCs were compared to the DTSC point of departure of 1 x 10-6 for carcinogenic effects. Because cancer risks are assessed over a lifetime, the cancer risks for a combined adult and child resident exposure scenario were calculated as using an adjustment factor of 24 years exposure as adult/30 years exposure total: Combined Adult and Child Resident cancer risk = Adult Resident cancer risk * (24 Years/30 Years) + Child Resident cancer risk Table 11 presents the cancer risk for a combined adult and child resident exposure scenario. 6.3 Risk Characterization Results The results of the risk characterization are presented in Tables 7 through 11. Table 12 presents a summary of the maximum and cumulative cancer risk and noncancer hazard risk estimates for the adult and child resident exposure scenarios. 6.3.1 Adult Resident Risk Characterization Results Tables 7 and 8 present the noncancer hazards and cancer risk estimates for the adult resident exposure scenario for the two production wells used as a future domestic water source: Rialto Well No. 6 and District Well No. 11. Rialto Well No. 6. The HQ estimate for perchlorate (20) is the only HQ estimate that exceeds the DTSC point of departure of 1 for noncarcinogenic effects (Table 7). The cancer risk estimate for TCE (3 x 10-6) was the only individual cancer risk estimate that exceeded the DTSC point of departure of 1 x 10-6 for carcinogenic effects (Table 8). The cumulative cancer risk estimate was 5 x 10-6, due to cancer risks from TCE and chloroform. District Well No. 11. The HQ estimates did not exceed the DTSC point of departure of 1 for noncarcinogenic effects (Table 7).The cancer risk estimates for DBCP (2 x 10-5) and arsenic (2 x 10-5) exceeded the DTSC point of departure of 1 x 10-6 for carcinogenic effects (Table 8). The cumulative cancer risk estimate was 4 x 10-5, primarily associated with DBCP and arsenic. 6.3.2 Child Resident Risk Characterization Results Tables 9 and 10 present the noncancer hazards and cancer risk estimates for the child resident exposure scenario for the two production wells used as a future domestic water source: Rialto Well No. 6 and District Well No. 11. Rialto Well No. 6. The HQ estimate for perchlorate (60) was the only HQ estimate that exceeds the DTSC point of departure of 1 for noncarcinogenic effects (Table 9). None of the individual cancer risk estimates exceeded the DTSC point of departure of 1 x 10-6 for carcinogenic effects (Table 10). The cumulative cancer risk estimate was 1 x 10-6. Page 22 Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc District Well No. 11. The HQ estimates did not exceed the DTSC point of departure of 1 for noncarcinogenic effects (Table 9). The cancer risk estimates for DBCP (5 x 10-6) and arsenic (1 x 10-5) exceeded the DTSC point of departure of 1 x 10-6 for carcinogenic effects (Table 10). The cumulative cancer risk estimate was 2 x 10-5, primarily associated with arsenic. 6.3.3 Combined Adult and Child Resident Table 11 presents the cancer risk estimates for the combined adult and child resident exposure scenario for the two production wells used as a future domestic water source: Rialto Well No. 6 and District Well No. 11. Rialto Well No. 6. The cancer risk estimates for TCE (3 x 10-6) and chloroform (2 x 10-6) exceeded the DTSC point of departure of 1 x 10-6 for carcinogenic effects (Table 11). The cumulative cancer risk estimate was 5 x 10-6. District Well No. 11. The cancer risk estimates for DBCP (2 x 10-5) and arsenic (3 x 10-5) exceed the DTSC point of departure of 1 x 10-6 for carcinogenic effects (Table 11). The cumulative cancer risk estimate was 5 x 10-5. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Page 23 Section 7: Uncertainty Assessment Uncertainty arises at every stage in the risk assessment, from the sampling and analysis of concentrations in environmental media to the characterization of health hazard and risk. In general, the risk assessment approach and methodology are designed to err on the side of conservatism, i.e., protection of health. This section includes a discussion of the uncertainties with some of the conservative assumptions, procedures, and parameters used in this HHRA. This section identifies issues of variability and uncertainty associated with the parameters used in the risk estimates: ● Variability arises from true heterogeneity in characteristics such as dose-response differences within a population, or differences in chemical concentrations in the environment. The values of some variables used in an assessment change with time and space, or across the population whose exposure is being estimated. ● Uncertainty, on the other hand, represents lack of knowledge about factors such as adverse effects or chemical concentrations. A substantial amount of uncertainty is often inherent in environmental sampling as well as in the scientific models used in risk assessment. Potentially significant sources of uncertainty and variability in this HHRA that may impact the risk estimates are discussed in the following subsections. 7.1 Uncertainties in Data and EPCs According to USEPA guidance (USEPA 1989), the EPC should represent the arithmetic average of the concentration that will be contacted over the exposure period. Due to uncertainty associated with estimating an EPC, the 95 percent upper confidence limit on the arithmetic average, which depending on the data distribution and presence of outliers can be much higher than the arithmetic average, was used in the HHRA as the EPC. In cases when the number of results was not sufficient to calculate an EPC, the maximum concentration was used in the HHRA. Use of upper confidence limits or maximum concentrations provides a protective approach and likely resulted in overestimates of the actual risks, especially for long-term exposures. The calculation of EPCs assumed that groundwater concentrations would remain constant over the duration of the exposure. Trend analyses (provided in Appendix B) were performed to determine groundwater data sets representative of stable concentrations, thereby minimizing the uncertainty associated with future trends in groundwater concentrations. However, the production wells are downgradient of higher groundwater concentrations, so in the absence of treatment, it is possible that concentrations, and associated risks, could increase. The handling of NO3-N concentrations in the data assessment also resulted in uncertainty in the EPCs. Treating NO3-N results from unfiltered and dissolved analysis as the same constituent caused these results to be treated as duplicates, since every dissolved nitrate analysis had an unfiltered analysis performed on the same sample. The conversion of nitrate analytical results to Page 24 Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc NO3-N concentrations also introduced uncertainty into the NO3-N EPCs, since these results rely on different analytical methods to measure nitrogen content than methods that measure NO3-N directly. 7.2 Uncertainties in Exposure Factors Numerous conservative assumptions were made in selecting the exposure factors used in each of the exposure scenarios to provide a protective estimate of risk, due to uncertainties in some of the data used. By using conservative exposure factors (i.e., RME factors), the risk estimates are inherently biased towards more health protective, conservative values. Actual exposures may be lower than those assumed in this assessment. A volatilization factor of 0.5 L/m3 was used to estimate indoor air concentrations of volatile COPCs using groundwater concentrations. While there is a great deal of uncertainty associated with this factor, this uncertainty is not anticipated to have a significant influence on the HHRA results given that inhalation exposures are low relative to oral and dermal exposures. 7.3 Uncertainties in Toxicological Data The toxicity factors used in this HHRA, which are established by state and federal policy, are conservative estimates of the potential dose-response. In addition, the results of animal studies are often used to predict the potential human health effects of a chemical. Extrapolation of toxicological data from animal studies is one of the largest sources of uncertainty. Because of these uncertainties, toxicity values are usually very conservative to be more protective of human health due to methodologies and safety factors used by OEHHA and USEPA. The safety factors used by OEHHA and USEPA typically range from two to three orders of magnitude (100 to 1,000 times), depending on various aspects of the animal study. As a result, actual risks are likely to be lower than the potential risk estimates calculated in this HHRA. Uncertainty factors are also used by OEHHA and USEPA to account for exposures by sensitive subpopulations (e.g., infants or pregnant women). To assess noncarcinogenic toxicity of perchlorate, OEHHA (2004b) applied an uncertainty factor of 10 for inter-individual variability to the BMDL to account for exposures by sensitive subpopulations (pregnant or lactating women, infants, and individuals with thyroid problems). For NO3-N, the toxicity studies used the most sensitive population (infants); therefore, no additional adjustment using modifying and uncertainty factors was applied by the USEPA to assess noncarcinogenic toxicity of NO3-N. 7.4 Impact of Uncertainties When summed and used in the risk equations, these uncertainties generally provide overestimates of risk. Resulting risk estimates are thus intentionally conservative to provide a margin of safety in the protection of human health at a site. This must always be factored in to the interpretation of risk estimates, as HHRAs are designed to provide guidance for understanding the levels of COPCs that would be protective of potentially exposed human receptor populations. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Page 25 Section 8: Summary and Conclusions This HHRA was performed to estimate the potential human health risks associated with the future domestic use of groundwater from Rialto Well No. 6 and District Well No. 11, assuming that no reduction in concentration of contaminants through treatment or response actions occurs. The estimated risks in this HHRA are based on available groundwater data for Rialto Well No. 6 and District Well No. 11 from the historical water quality database maintained by CDPH, and DBS&A. The chemicals identified as COPCs for further evaluation in the HHRA included: Inorganic anions: perchlorate, NO3-N, and fluoride Metals: arsenic and hexavalent chromium VOCs: DBCP, chloroform, and TCE. Of these COPCs, only perchlorate, NO3-N, and TCE were detected at concentrations above the respective California primary MCL. Potentially exposed populations for evaluation in the HHRA were identified based on consideration of the current and future uses of groundwater and USEPA (1989) guidance. The exposure scenarios evaluated in this HHRA were: ● ● Adult Water Consumer (Adult Resident) Child Water Consumer (Child Resident) The potential exposure pathways that were evaluated in this HHRA included: ● ● ● Ingestion of COPCs in groundwater Inhalation of COPCs from groundwater Dermal contact with COPCs in groundwater Noncancer hazards and cancer risk estimates were calculated for the adult and child residents, and compared to the DTSC point of departure of 1 for noncancer hazards and 1 x 10-6 for cancer risk estimates. Noncancer hazards and cancer risk estimates were calculated separately for the two production wells. The results of the risk characterization for the production wells Rialto Well No. 6 and District Well No. 11 are summarized as follows: Rialto Well No. 6. TCE and chloroform resulted in cancer risk estimates exceeding the DTSC point of departure of 1 x 10-6. For the combined adult and child resident exposure scenario, the cancer risk estimates for TCE and chloroform were 3 x10-6 and 2 x 10-6, respectively. Perchlorate was the only COPC that resulted in a HQ greater than the DTSC point of departure HQ of 1. District Well No. 11. DBCP and arsenic resulted in cancer risks greater than the DTSC point of departure for cancer risk of 1 x 10-6. For the combined adult and child resident exposure Page 26 Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc scenario the cancer risk estimates for DBCP and arsenic were 2 x10-5 and 3 x 10-5, respectively. DBCP was the only COPC that resulted in a HQ greater than the DTSC point of departure HQ of 1. Of the chemicals found to exceed the DTSC points of departure for carcinogenic and noncarcinogenic effects, only the TCE and perchlorate EPCs were above the California MCLs. DBCP is a halogenated VOC that was historically used as a soil fumigant for agricultural purposes though has not been approved for use in agriculture in California since 1977 (OEHHA 1999). DBCP can be persistent in groundwater and is associated with widespread groundwater detections (OEHHA 1999). The California Department of Pesticide Regulation (CDPR) reported that the PHG (0.0017 µg/L) for DBCP was exceeded in all of the 261 wells tested for DBCP (CDPR 2009). The concentrations of DBCP detected in groundwater collected from District Well No. 11 are similar to concentrations commonly detected in groundwater as reported by CDPR (2009). The DBCP EPC for District Well No. 11 (0.032 µg/L) was based on the maximum detected concentration, which is below the California MCL for DBCP of 0.2 µg/L. CDPH (2008) states that arsenic is ubiquitous in nature and is commonly found in drinking water sources in California. The arsenic EPC for District Well No. 11 (1.2 µg/L) was based on the maximum detected concentration and is less than the California MCL for arsenic of 10 µg/L. As discussed in Section 1, the District has taken the lead on constructing and operating a groundwater wellhead treatment system that will remove perchlorate and nitrate, and reduce VOC concentrations in groundwater. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Page 27 References California Department of Public Health, 1997. Policy Memo 97-005 Policy Guidance for Direct Domestic Use of Extremely Impaired Sources. November 1997. California Department of Public Health (DPH) 2008. Arsenic in Drinking Water: MCL Status. Updated 1 December 2008. www.cdph.ca.gov/certlic/drinkingwater/Pages/Arsenic.aspx. California Department of Public Health, 2010. Detection Limits for Purposes of Reporting. Microsoft Excel document retrieved online October 2010. California Environmental Protection Agency, Department of Toxic Substances Control (DTSC), 1994. Preliminary Endangerment Assessment Guidance Manual. January 1994. California Environmental Protection Agency, Department of Toxic Substances Control (DTSC), 1996. Supplemental Guidance for Human Health Multimedia Risk Assessments of Hazardous Waste Sites and Permitted Facilities. August 1996. California Environmental Protection Agency, Department of Pesticide Regulation (CDPR). 2009. Sampling for Pesticide Residues in California Well Water. 2008 Update of the Well Inventory Database for Sampling Results Reported from January 2007 through June 2008. August 2009. Egan 2006. City of Rialto Urban Water Management Plan. John Egan and Associates, Inc., February 2006. ERSC 2006. West Valley Water District Urban Water Management Plan. Engineering Resources of Southern California, January 2006. OEHHA, 1997a. Public Health Goals for Chemicals in Drinking Water, Flouride. December 1997. OEHHA, 1997b. Public Health Goals for Nitrate and Nitrite in Drinking Water. December 1997. OEHHA, 1999. Public Health Goals for Chemicals in Drinking Water, 1,2-Dibromochloropropane. February 1999. OEHHA, 2004a. Public Health Goals for Chemicals in Drinking Water, Arsenic. April 2004. OEHHA, 2004b. Public Health Goal for Perchlorate in Drinking Water. March 2004. OEHHA, 2008. Acute, 8-hour and Chronic Reference Exposure Levels (chRELs). Last updated 18 December 2008. OEHHA, 2009. Public Health Goals for Chemicals in Drinking Water, Trichloroethene. July 2009. Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Ref - 1 OEHHA, 2010. Toxicity Criteria Database. URL: http://www.oehha.ca.gov/risk/ChemicalDB/index.asp. URL Site accessed 25 October 2010. USEPA, 1986. Guidelines for Carcinogen Risk Assessment. EPA/630/R-00/004. September 1986. USEPA, 1989. Risk Assessment Guidance for Superfund, Volume 1, Human Health Evaluation Manual (Part A), Interim Final. U.S. Environmental Protection Agency, Office of Solid Waste and Emergency Response, Washington D.C. EPA/540/1 89/002. December 1989. USEPA, 1991. Risk Assessment Guidance for Superfund, Volume I. Human Health Evaluation Manual, Supplemental Guidance, Standard Default Exposure Factors, Interim Final. Office of Emergency and Remedial Response: OSWER Directive: 9285.6-03. USEPA, 2001. Risk Assessment Guidance for Superfund Volume 1: Human Health Evaluation Manual. Part D: Standardized Planning, Reporting and Review of Superfund Risk Assessments, Final. U.S. Environmental Protection Agency, Office of Solid Waste and Emergency Response, Washington D.C. Publication 9285.7-47. December 2001. USEPA, 2003. Memorandum: Human Health Toxicity Values in Superfund Risk Assessments (Human Health Toxicity Value Hierarchy). OSWER Directive 9285.7-53. U.S. Environmental Protection Agency. USEPA, 2004. Risk Assessment Guidance for Superfund Volume 1: Human Health Evaluation Manual. Part E: Supplemental Guidance for Dermal Risk Assessment, Interim Guidance. EPA/540/R-99/005. U.S. Environmental Protection Agency, Office of Solid Waste and Emergency Response, Washington D.C. PB99-963312. July 2004. USEPA, 2005. Guidelines for Carcinogen Risk Assessment. Risk Assessment Forum. Washington, D.C. EPA/630/P-03/001F. March 2005. USEPA, 2009a. National Priorities List, Final Rule No. 47. 40 Code of Federal Regulations (CFR), Part 300. USEPA, 2009b. Risk Assessment Guidance for Superfund Volume 1: Human Health Evaluation Manual. Part E: Supplemental Guidance for Inhalation Risk Assessment, Final Guidance. U.S. Environmental Protection Agency, Office of Solid Waste and Emergency Response, Washington D.C. EPA-540-R-070-002. January 2009. USEPA, 2010a. Regional Screening Levels for Chemical Contaminants at Superfund Sites. May 2010. USEPA, 2010b. ProUCL Version 4.00.05 User Guide (Draft). EPA/600/R-07/038. May 2010. USEPA, 2010c. Integrated Risk Information System (IRIS) Database. URL: http://www.epa.gov/ncea/iris/. URL Site accessed 25 October 2010. Ref - 2 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto g:\is-group\admin\job\10\1089040.00_wvwd\09-reports\hhra rpt\text.doc Tables Table 1: Occurrence, Distribution, and Selection of Chemicals of Potential Concern in Groundwater Number of Samples(a) Number of Detected Concentrations Percent Detected Maximum Detect Units Screening (b) Value c/nc(c) Screening Value Source COPC? Reason for Selection/Exclusion California MCL(e) Maximum Detect Exceeds MCL Carcinogenicity Classificiation(d) 1,2‐Dibromo‐3‐Chloropropane (DBCP) 18 2 11% 0.032 µg/L 0.0017 c PHG, Oct 2010 Y Max detect exceeds screening level 0.2 N NA Arsenic 24 3 13% 1.2 µg/L 0.004 c PHG, Oct 2010 Y Max detect exceeds screening level 10 N A Barium 11 2 18% 42 µg/L 200 nc PHG, Oct 2010 N Max detect does not exceed screening level 1000 N D Chloroform 12 1 8% 1 µg/L 0.19 c RSL, May 2010 Y Max detect exceeds screening level 80 (total trihalomethanes) N B2 A (Inhalation route), D (oral route) Analyte Chromium, Hexavalent 10 9 90% 20 µg/L 0.043 c RSL, May 2010 Y Max detect exceeds screening level NA ‐‐ Chromium, Total(e) Copper 11 3 27% 2.4 µg/L 5500 nc RSL, May 2010 N Max detect does not exceed screening level 50 N D 13 2 15% 2.9 µg/L 30 nc PHG, Oct 2010 N Max detect does not exceed screening level 1000 (secondary) N D Dichloromethane 12 1 8% 1.1 µg/L 4 c PHG, Oct 2010 N Max detect does not exceed screening level 5 N B2 Fluoride (natural‐source) 12 11 92% 400 µg/L 100 nc PHG, Oct 2010 Y Max detect exceeds screening level 2,000 N NA Iron 14 2 14% 61 µg/L 2600 nc RSL, May 2010 N Max detect does not exceed screening level 300 (secondary) Y NA Manganese 13 2 15% 2.1 µg/L 88 nc RSL, May 2010 N Max detect does not exceed screening level 50 (Secondary) N D Nitrate‐N Perchlorate 57 57 100% 12,341 µg/L 1000 nc PHG, Oct 2010 Y Max detect exceeds screening level 10,000 Y NA 175 139 79% 320 µg/L 0.6 nc PHG, Oct 2010 Y Max detect exceeds screening level 6 Y Not likely to be carcinogenic Trichloroethene 15 7 47% 6.3 µg/L 1.7 c PHG, Oct 2010 Y Max detect exceeds screening level 5 Y Withdrawn Vanadium 9 7 78% 5.7 µg/L 18 nc RSL, May 2010 N Max detect does not exceed screening level NA N NA (f) Abbreviations: c = carcinogen COPC = Chemical of Potential Concern IRIS = Integrated Risk Information System MCL = Maximum Contaminant Level N = Nitrogen NA = not assessed under the IRIS program nc = noncarcinogen PHG = Public Health Goals for water developed as of October 2010. California Office of Environmental Health Hazard Assessment RSL = Regional Screening Levels for tapwater, published May 2010. United States Environmental Protection Agency (USEPA) µg/L = micrograms per liter USEPA = United States Environmental Protection Agency Notes: a) Data set includes all data from the California Department of Public Health database for Rialto Well #6 and District Well #11 from 1999‐2010, with duplicates reduced as described in the text. b) Noncarcinogenic screening levels were divided by ten for the purposes of this screening. c) c/nc classification listed by USEPA RSL table (May 2010). d) Carcinogenicity classification obtained from USEPA Integrated Risk Information System (IRIS), 2010. Classifications are as follows: A: Human carcinogen B2: Probable human carcinogen ‐ based on sufficient evidence of carcinogenicity in animals D: Not classifiable as to human carcinogenicity e) Screening level for Chromium III was used for Total Chromium. f) Unfiltered Nitrate and dissolved Nitrate results were combined and converted to Nitrate as Nitrogen (NO3‐N) using a factor of 4.4. Human Health Risk Assessment Report, Wellhead Treatment Project, West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\Table1_COPC_Screen.xlsx Page 1 of 1 Table 2: Exposure Point Concentrations for Chemicals of Potential Concern Domestic Water Source (Exposure Point) Rialto Well No. 6 District Well No. 11 Chemical of Potential Concern Units Exposure Max Value Date range of EPC dataset(a) Number of Samples(a) Distribution UCL Method 95% UCL EPC DBCP Arsenic Chloroform Chromium, Hexavalent Fluoride Nitrate-Nitrogen (NO3-N) Perchlorate Trichloroethene µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L ND ND 1 1.7 400 2,955 320 6.3 1999-2010 1999-2010 1999-2010 1999-2010 1999-2010 3/22/05-2010 9/11/07-2010 1999-2010 9 6 7 6 6 5 33 9 ------non-parametric -- ------95% Student's-t UCL -- ------244 -- ND ND 1 1.7 400 2955 244 6.3 µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L 0.032 1.2 ND 20 320 10,909 13 1 1999-2010 1999-2010 1999-2010 1999-2010 6/28/02-2010 08/08/03-2010 1999-2010 1999-2010 9 19 5 4 4 33 47 6 -----normal non-parametric -- -----95% Student's-t UCL 95% KM (t) UCL -- -----8,748 4.7 -- 0.032 1.2 ND 20 320 8,748 4.7 1 (b) DBCP Arsenic Chloroform Chromium, Hexavalent Fluoride Nitrate-Nitrogen (NO3-N) Perchlorate Trichloroethene Notes: (a) Data set included all well data from 1999 to 2010 (October). Date range for individual analytes and wells reflects data reduction resulting from trend analyses, as discussed in the text. (b) Dissolved nitrate was combined with unfiltered nitrate and converted to nitrate as nitrogen (NO3-N), using a factor of 4.4, for use in the data set. Abbreviations: DBCP = 1,2-Dibromo-3-chloropropane ND = Analyte not detected in data set used to calculate EPCs. µg/L = Micrograms per liter. EPC = Exposure point concentration 95% UCL = 95 percent upper confidence limit on the mean. NA = Analyte not analyzed in data set used to calculate EPCs. "-- = not applicable. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\Tables2-12_withFormulas.xlsx Page 1 of 1 General and Chemical-Specific Exposure Parameters Domestic Water - Ingestion EPC x WIR x EF x ED x 1/BW x 1/AT Domestic Water - Dermal Contact DA x SA x EF x ED x EV x 1/BW x 1/AT Domestic Water - Inhalation EPCx VFw x (ET/24 hr/day) x EF x ED x 1/AT Notes: (a) (b) (c) (d) (e) (f) (g) (h) (i) (j) Parameter Code Parameter Definition Units EPC BW EF ED ATc ATnc Exposure Point Concentration Body weight Exposure frequency Exposure duration Averaging time, cancer Averaging time, noncancer mg/L kg days/yr years days days WIR Water ingestion rate L/day Event duration hr/ev Skin surface area Event frequency Absorbed dose per event Volatilization factor for water Exposure Time cm2 event/day mg/cm 2-ev L/m3 hours/day tev SA EV DAj VFw ET Recommended value (USEPA 1989). Recommended value for children (USEPA 1991). USEPA 1991. National upper-bound time (90th percentile) at one residence (USEPA 1989). National median time (50th percentile) at one residence (USEPA 1989). Recommended for residential ingestion of drinking water (USEPA 1997). Recommended for adults while showering/bathing (USEPA 2004). Recommended value for children while showering/bathing (USEPA 2004). BPJ. DA = dermal absorbed dose for water (DAw, L/cm 2-ev) multiplied by the EPC (mg/L). DAw calculations are shown in Table 4. (k) Andelman Volatilization Factor for volatilization from water during household (indoor) uses (USEPA 1991). 3 (l) Inhalation is assessed as an exposure concentration (mg/m ) Adult Resident Value CS, see Table 2 70 350 30 25,550 9,125 a c d a a 2 f 0.58 18,000 1 CS 0.5 24 Child Resident Value CS, see Table 2 15 350 6 25,550 2,190 Source Daily Intake Equation (mg/kg-day)(l) Exposure Route Source Table 3: Values for Chronic Daily Intake Calculations b c b a a 1.5 f g 1 h g i 6,600 1 CS 0.5 24 h i k i k i Abbreviations: BPJ = Best Professional Judgement. cm2 = squared centimeter. CS = chemical-specific value. DAw = Dermal absorbed dose for water. ev = event. hr = hour. kg = kilogram. L = liter. m3 = cubic meter. mg = milligram. yr = year. USEPA = United States Environmental Protection Agency. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\Tables2-12_withFormulas.xlsx Page 1 of 1 Table 4: Chemical-Specific Parameters for Dermal Exposure to Domestic Water Adult Resident Chemical of Potential Concern Domestic Water(a) DBCP Arsenic Chloroform Chromium, Hexavalent Fluoride Nitrate (as N) Perchlorate Trichloroethene Child Resident (b) Kp (cm/hr) B (unitless) FA (unitless) τ (hr) t* (hr) Tevent (hr/event) DAw (L/cm2-event) Tevent (hr/event) DAw (L/cm2-event) 6.9E-03 1.0E-03 6.8E-03 1.0E-03 1.0E-03 1.0E-03 1.0E-03 1.2E-02 0.0 -0.0 ----0.1 1.0 -1.0 ----1.0 2.26 -0.5 ----0.58 5.41 -1.19 ----1.39 0.58 0.58 0.58 0.58 0.58 0.58 0.58 0.58 2.17E-05 5.80E-07 1.01E-05 5.80E-07 5.80E-07 5.80E-07 5.80E-07 1.92E-05 1 1 1 1 1 1 1 1 2.85E-05 1.00E-06 1.33E-05 1.00E-06 1.00E-06 1.00E-06 1.00E-06 2.53E-05 Notes: (a) Values for Kp, B, τ, and t* from Exhibit 3-3, Exhibit B-3 of USEPA RAGS PART E (USEPA 2004), or calculated using equations from USEPA RAGS PART E (USEPA 2004). (b) DAw calculated as follows (USEPA 2004): For organics, where Tevent ≤ t*: DAw = 2 x FA x Kp x [(6 x τ x Tevent)/π]^0.5 x 10-3 L/cm3 For organics, where Tevent > t*: DAw = FA x Kp x [(Tevent/(1 + B)) + 2 x τ x ((1 + 3B + 3B2)/(1 + B)2)] x 10-3 L/cm3 For inorganics: DAw = Kp x Tevent x 10-3 l/cm3 Abbreviations: -- = Not applicable. B = Relative contribution of permeability coefficients. cm = Centimeters. DAw = Dermal absorbed dose for water. DBCP = 1,2-Dibromo-3-chloropropane. FA = Fraction absorbed water. hr = Hours. Kp = Dermal permeability constant. L = Liters. N = Nitrogen. RAGS = Risk Assessment Guidance for Superfund. t* = Time to reach steady state. Tevent = Event time. τ = Lag time. USEPA = United States Environmental Protection Agency. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\Tables2-12_withFormulas.xlsx Page 1 of 1 Reference Dose (Dermal) (mg/kg-day) Reference Concentration (Inhalation) (mg/m 3) Source Reference Dose (Oral) Primary Target Organ (mg/kg-day) (Oral Exposure) GIABS(a) b d 1.0E+00 1.0E+00 2.5E-05 3.0E-04 2.0E-04 1.5E-05 1.0E-02 Testicular effects Development; cardiovascular system; nervous system; lung; skin Liver c 1.0E+00 1.0E-02 Chromium, Hexavalent 3.0E-03 None reported c 2.5E-02 Fluoride 6.0E-02 e Nitrate (as N) 1.6E+00 Perchlorate Trichloroethene 3.7E-04 5.0E-01 Objectionable dental fluorosis, a cosmetic effect Early clinical signs of methemoglobinemia in excess of 10% (03 months old infants formula) Inhibit “sodium-iodide symporter” Kidney nephropathy Chemical of Potential Concern DBCP Arsenic 2.5E-05 3.0E-04 Chloroform Primary Target Organ (Inhalation Exposure) Source Table 5: Toxicity Information for Noncarcinogenic Chemicals of Potential Concern 3.0E-01 Testicular effects Development; cardiovascular system; nervous system; lung; skin Alimentary system; kidney; teratogenicity d 7.5E-05 2.0E-04 Respiratory system d 1.0E+00 6.0E-02 NA NA c f 1.0E+00 1.6E+00 NA NA c g h 1.0E+00 1.0E+00 3.7E-04 5.0E-01 NA 6.0E-01 NA Nervous system; eyes c d Notes: (a) GIABS listed by USEPA (2004). (b) Public Health Goals for Chemicals in Drinking Water, 1,2-Dibromochloropropane (OEHHA 1999). (c) IRIS Database (USEPA 2010c). (d) OEHHA Acute, 8-hour and Chronic Reference Exposure Levels (chRELs) (OEHHA 2008). (e) Public Health Goals for Chemicals in Drinking Water, Flouride (OEHHA 1997a). (f) Public Health Goals for Chemicals in Nitrate and Nitrite in Drinking Water (OEHHA 1997b). (g) Public Health Goal for Perchlorate in Drinking Water (OEHHA 2004b). (h) Public Health Goals for Chemicals in Drinking Water, Trichloroethene (OEHHA 2009). c d Abbreviations: DBCP = 1,2-Dibromo-3-chloropropane. GIABS = Gastrointestinal absorption factor. kg = kilograms. IRIS = Integrated Risk Information System. mg/m 3 = milligrams per cubic meter. mg = milligrams. N = Nitrogen. NA = Not available. NV = Chemical not assessed for inhalation pathway because non-volatile. OEHHA = Office of Environmental Health Hazard Assessment. USEPA = United States Environmental Protection Agency. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\Tables2-12_withFormulas.xlsx Page 1 of 1 DBCP Arsenic Chloroform Chromium, Hexavalent Fluoride Nitrate (as N) Perchlorate Trichloroethene Slope Factor (Oral) (mg/kg-day)-1 Not assessed A, Carcinogenic to Humans B2 (Probable human carcinogen ), Likely to be Carcinogenic to Humans A, Carcinogenic to Humans (Inhalation); D, Inadequate Information to Assess Carcinogenic Potential (Oral) 7.0E+00 1.5E+00 3.1E-02 Not assessed Not assessed Not likely to be carcinogenic to humans Not assessed Weight of Evidence(a) Notes: (a) Weight of evidence listed in IRIS database (USEPA 2010c). (b) GIABS listed by USEPA (2004). (c) OEHHA Toxicity Database (OEHHA 2010). (d) IRIS Database (USEPA 2010c) GIABS(b) Slope Factor (Dermal) (mg/kg-day)-1 Unit Risk Factor (Inhalation) (µg/m3)-1 Source Chemical of Potential Concern Source Table 6: Toxicity Information for Carcinogenic Chemicals of Potential Concern c c c 1.0E+00 1.0E+00 1.0E+00 7.0E+00 1.5E+00 3.1E-02 2.0E-03 NV 5.3E-06 c NA c,d 2.5E-02 NA NV NA NA NA 5.9E-03 c,d c,d c,d c 1.0E+00 1.0E+00 1.0E+00 1.0E+00 NA NA NA 5.9E-03 NV NV NV 2.0E-06 c c Abbreviations: DBCP = 1,2-Dibromo-3-chloropropane. GIABS = Gastrointestinal absorption factor. kg = kilograms. IRIS = Integrated Risk Information System. µg/m3 = micrograms per cubic meter. mg = milligrams. N = Nitrogen. NA = Not applicable because chemical is a non-carcinogen. NV = Chemical not assessed for inhalation pathway because non-volatile. OEHHA = Office of Environmental Health Hazard Assessment. USEPA = United States Environmental Protection Agency. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\Tables2-12_withFormulas.xlsx Page 1 of 1 Table 7: Calculation of Noncancer Hazards - Adult Resident, Domestic Water Use EPC Domestic Water Source (Exposure Point) Rialto Well No. 6 Noncancer Hazard Calculations a Units Dermal RfD (mg/kg-day) Oral RfD (mg/kg-day) Inhalation RfC (mg/m3) Dermal CDI (mg/kg-day) Oral CDI (mg/kg-day) Inhalation EC (mg/m3) Noncancer HQ from Dermal Contact Noncancer HQ from Ingestion Noncancer HQ from Inhalation Total Noncancer HQ ND ND 1.0E+00 1.7E+00 4.0E+02 3.0E+03 2.4E+02 6.3E+00 µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L 2.5E-05 3.0E-04 1.0E-02 7.5E-05 6.0E-02 1.6E+00 3.7E-04 5.0E-01 2.5E-05 3.0E-04 1.0E-02 3.0E-03 6.0E-02 1.6E+00 3.7E-04 5.0E-01 2.0E-04 1.5E-05 3.0E-01 2.0E-04 NA NA NA 6.0E-01 ND ND 3.0E-06 2.9E-07 6.9E-05 5.1E-04 4.2E-05 3.6E-05 ND ND 3.3E-05 5.6E-05 1.3E-02 9.7E-02 8.0E-03 2.1E-04 ND ND 5.8E-04 ----3.6E-03 ND ND 3.0E-04 3.9E-03 1.1E-03 3.2E-04 1.1E-01 7.2E-05 ND ND 3.3E-03 1.9E-02 2.2E-01 6.1E-02 2.2E+01 4.1E-04 ND ND 1.9E-03 ----6.0E-03 --6E-03 2E-02 2E-01 6E-02 2E+01 7E-03 3.2E-02 1.2E+00 ND 2.0E+01 3.2E+02 8.7E+03 4.7E+00 1.0E+00 µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L 2.5E-05 3.0E-04 1.0E-02 7.5E-05 6.0E-02 1.6E+00 3.7E-04 5.0E-01 2.5E-05 3.0E-04 1.0E-02 3.0E-03 6.0E-02 1.6E+00 3.7E-04 5.0E-01 2.0E-04 1.5E-05 3.0E-01 2.0E-04 NA NA NA 6.0E-01 2.1E-07 2.1E-07 ND 3.4E-06 5.5E-05 1.5E-03 8.1E-07 5.7E-06 1.1E-06 3.9E-05 ND 6.6E-04 1.1E-02 2.9E-01 1.5E-04 3.3E-05 1.8E-05 -ND ----5.8E-04 8.2E-03 6.9E-04 ND 4.6E-02 9.2E-04 9.4E-04 2.2E-03 1.1E-05 4.2E-02 1.3E-01 ND 2.2E-01 1.8E-01 1.8E-01 4.2E-01 6.6E-05 9.2E-02 -ND ----9.6E-04 1E-01 1E-01 -3E-01 2E-01 2E-01 4E-01 1E-03 Chemical of Potential Concern Value DBCP Arsenic Chloroform Chromium, Hexavalent Fluoride Nitrate (as N) Perchlorate Trichloroethene DBCP Arsenic Chloroform Chromium, Hexavalent Fluoride Nitrate (as N) Perchlorate Trichloroethene District Well No. 11 Note: (a) Inhalation EC is calculated only for volatile COPCs. Abbreviations: -- = Not Applicable. µg = microgram. CDI = Chronic Daily Intake. COPC = Chemical of Potential Concern. DBCP = 1, 2-Dibromo-3-chloropropane. EC = Inhalation Exposure Concentration. EPC = Exposure Point Concentration. HQ = Hazard Quotient. kg = kilogram. L = liter. mg = milligram. N = Nitrogen. NA = Not available. ND = Not detected. RfD = Reference Dose. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\Tables2-12_withFormulas.xlsx Page 1 of 1 Table 8: Calculation of Cancer Risks - Adult Resident, Domestic Water Use EPC Domestic Water Source (Exposure Point) Cancer Risk Calculations Oral Cancer Slope Factor -1 (mg/kg-day) Inhalation Unit Risk Factor Units Dermal Cancer Slope Factor -1 (mg/kg-day) ND ND 1.0E+00 1.7E+00 4.0E+02 3.0E+03 2.4E+02 6.3E+00 µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L 7.0E+00 1.5E+00 3.1E-02 NA NA NA NA 5.9E-03 3.2E-02 1.2E+00 ND 2.0E+01 3.2E+02 8.7E+03 4.7E+00 1.0E+00 µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L 7.0E+00 1.5E+00 3.1E-02 NA NA NA NA 5.9E-03 Chemical of Potential Concern Value DBCP Arsenic Chloroform Chromium, Hexavalent Fluoride Nitrate (as N) Perchlorate Trichloroethene DBCP Arsenic Chloroform Chromium, Hexavalent Fluoride Nitrate (as N) Perchlorate Trichloroethene a (µg/m3)-1 Dermal LADI (mg/kg-day) Oral LADI (mg/kg-day) Inhalation EC (µg/m3) Cancer Risk from Dermal Contact Cancer Risk from Oral Contact Cancer Risk fron Inhalation 7.0E+00 1.5E+00 3.1E-02 NA NA NA NA 5.9E-03 2.0E-03 NV 5.3E-06 NV NV NV NV 2.0E-06 ND ND 1.1E-06 1.0E-07 2.5E-05 1.8E-04 1.5E-05 1.3E-05 ND ND 1.2E-05 2.0E-05 4.7E-03 3.5E-02 2.9E-03 7.4E-05 ND ND 2.1E-01 ----1.3E+00 ND ND 3.3E-08 ----7.6E-08 ND ND 3.6E-07 ----4.4E-07 ND ND 1.1E-06 ----2.6E-06 ND ND 1E-06 ----3E-06 5E-06 7.0E+00 1.5E+00 3.1E-02 NA NA NA NA 5.9E-03 2.0E-03 NV 5.3E-06 NV NV NV NV 2.0E-06 7.3E-08 7.4E-08 ND 1.2E-06 2.0E-05 5.4E-04 2.9E-07 2.0E-06 3.8E-07 1.4E-05 ND 2.3E-04 3.8E-03 1.0E-01 5.5E-05 1.2E-05 6.6E-03 -ND ----2.1E-01 5.1E-07 1.1E-07 ND ----1.2E-08 2.6E-06 2.1E-05 ND ----6.9E-08 1.3E-05 -ND ----4.1E-07 2E-05 2E-05 ND ----5E-07 4E-05 a Total Cancer Risk Rialto Well No. 6 Exposure Point Total District Well No. 11 Exposure Point Total Note: (a) Inhalation EC is calculated only for volatile COPCs (i.e., DBCP, chloroform, and trichloroethene). Abbreviations: -- = Not Applicable. µg = microgram. COPC = Chemical of Potential Concern. DBCP = 1, 2-Dibromo-3-chloropropane. EC = Inhalation Exposure Concentration. EPC = Exposure Point Concentration. kg = kilogram. L = liter. LADI = Lifetime Average Daily Intake. m3 = cubic meter. mg = milligram. N = Nitrogen. NA = Not available. ND = Not detected. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\Tables2-12_withFormulas.xlsx Page 1 of 1 Table 9: Calculation of Noncancer Hazards - Child Resident, Domestic Water Use EPC Domestic Water Source (Exposure Point) Rialto Well No. 6 Noncancer Hazard Calculations a Units Dermal RfD (mg/kg-day) Oral RfD (mg/kg-day) Inhalation RfC (mg/m3) Dermal CDI (mg/kg-day) Oral CDI (mg/kg-day) Inhalation EC (mg/m3) Noncancer HQ from Dermal Contact Noncancer HQ from Ingestion Noncancer HQ from Inhalation Total Noncancer HQ ND ND 1.0E+00 1.7E+00 4.0E+02 3.0E+03 2.4E+02 6.3E+00 µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L 2.5E-05 3.0E-04 1.0E-02 7.5E-05 6.0E-02 1.6E+00 3.7E-04 5.0E-01 2.5E-05 3.0E-04 1.0E-02 3.0E-03 6.0E-02 1.6E+00 3.7E-04 5.0E-01 2.0E-04 1.5E-05 3.0E-01 2.0E-04 NA NA NA 6.0E-01 ND ND 5.6E-06 7.2E-07 1.7E-04 1.2E-03 1.0E-04 6.7E-05 ND ND 9.6E-05 1.6E-04 3.8E-02 2.8E-01 2.3E-02 6.0E-04 ND ND 4.8E-04 ----3.0E-03 ND ND 5.6E-04 9.6E-03 2.8E-03 7.8E-04 2.8E-01 1.3E-04 ND ND 9.6E-03 5.4E-02 6.4E-01 1.8E-01 6.3E+01 1.2E-03 ND ND 1.6E-03 ----5.0E-03 --1E-02 6E-02 6E-01 2E-01 6E+01 6E-03 3.2E-02 1.2E+00 ND 2.0E+01 3.2E+02 8.7E+03 4.7E+00 1.0E+00 µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L 2.5E-05 3.0E-04 1.0E-02 7.5E-05 6.0E-02 1.6E+00 3.7E-04 5.0E-01 2.5E-05 3.0E-04 1.0E-02 3.0E-03 6.0E-02 1.6E+00 3.7E-04 5.0E-01 2.0E-04 1.5E-05 3.0E-01 2.0E-04 NA NA NA 6.0E-01 3.8E-07 5.1E-07 ND 8.4E-06 1.4E-04 3.7E-03 2.0E-06 1.1E-05 3.1E-06 1.2E-04 ND 1.9E-03 3.1E-02 8.4E-01 4.5E-04 9.6E-05 1.5E-05 -ND ----4.8E-04 1.5E-02 1.7E-03 ND 1.1E-01 2.3E-03 2.3E-03 5.4E-03 2.1E-05 1.2E-01 3.8E-01 ND 6.4E-01 5.1E-01 5.2E-01 1.2E+00 1.9E-04 7.7E-02 -ND ----8.0E-04 2E-01 4E-01 -8E-01 5E-01 5E-01 1E+00 1E-03 Chemical of Potential Concern Value DBCP Arsenic Chloroform Chromium, Hexavalent Fluoride Nitrate (as N) Perchlorate Trichloroethene DBCP Arsenic Chloroform Chromium, Hexavalent Fluoride Nitrate (as N) Perchlorate Trichloroethene District Well No. 11 Note: (a) Inhalation EC is calculated only for volatile COPCs. Abbreviations: -- = Not Applicable. µg = microgram. CDI = Chronic Daily Intake. COPC = Chemical of Potential Concern. DBCP = 1, 2-Dibromo-3-chloropropane. EC = Inhalation Exposure Concentration. EPC = Exposure Point Concentration. HQ = Hazard Quotient. kg = kilogram. L = liter. mg = milligram. N = Nitrogen. NA = Not available. ND = Not detected. RfD = Reference Dose. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\Tables2-12_withFormulas.xlsx Page 1 of 1 Table 10: Calculation of Cancer Risks - Child Resident, Domestic Water Use EPC Domestic Water Source (Exposure Point) Cancer Risk Calculations Oral Cancer Slope Factor -1 (mg/kg-day) Inhalation Unit Risk Factor Units Dermal Cancer Slope Factor -1 (mg/kg-day) ND ND 1.0E+00 1.7E+00 4.0E+02 3.0E+03 2.4E+02 6.3E+00 µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L 7.0E+00 1.5E+00 3.1E-02 NA NA NA NA 5.9E-03 3.2E-02 1.2E+00 ND 2.0E+01 3.2E+02 8.7E+03 4.7E+00 1.0E+00 µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L 7.0E+00 1.5E+00 3.1E-02 NA NA NA NA 5.9E-03 Chemical of Potential Concern Value DBCP Arsenic Chloroform Chromium, Hexavalent Fluoride Nitrate (as N) Perchlorate Trichloroethene DBCP Arsenic Chloroform Chromium, Hexavalent Fluoride Nitrate (as N) Perchlorate Trichloroethene a (µg/m3)-1 Dermal LADI (mg/kg-day) Oral LADI (mg/kg-day) Inhalation EC (µg/m3) Cancer Risk from Dermal Contact Cancer Risk from Oral Contact Cancer Risk fron Inhalation 7.0E+00 1.5E+00 3.1E-02 NA NA NA NA 5.9E-03 2.0E-03 NV 5.3E-06 NV NV NV NV 2.0E-06 ND ND 4.8E-07 6.1E-08 1.4E-05 1.1E-04 8.8E-06 5.8E-06 ND ND 8.2E-06 1.4E-05 3.3E-03 2.4E-02 2.0E-03 5.2E-05 ND ND 4.1E-02 ----2.6E-01 ND ND 1.5E-08 ----3.4E-08 ND ND 2.5E-07 ----3.1E-07 ND ND 2.2E-07 ----5.2E-07 ND ND 5E-07 ----9E-07 1E-06 7.0E+00 1.5E+00 3.1E-02 NA NA NA NA 5.9E-03 2.0E-03 NV 5.3E-06 NV NV NV NV 2.0E-06 3.3E-08 4.3E-08 ND 7.2E-07 1.2E-05 3.2E-04 1.7E-07 9.1E-07 2.6E-07 9.9E-06 ND 1.6E-04 2.6E-03 7.2E-02 3.9E-05 8.2E-06 1.3E-03 -ND ----4.1E-02 2.3E-07 6.5E-08 ND ----5.4E-09 1.8E-06 1.5E-05 ND ----4.8E-08 2.6E-06 -ND ----8.2E-08 5E-06 1E-05 ND ----1E-07 2E-05 a Total Cancer Risk Rialto Well No. 6 Exposure Point Total District Well No. 11 Exposure Point Total Note: (a) Inhalation EC is calculated only for volatile COPCs (i.e., DBCP, chloroform, and trichloroethene). Abbreviations: -- = Not Applicable. µg = microgram. COPC = Chemical of Potential Concern. DBCP = 1, 2-Dibromo-3-chloropropane. EC = Inhalation Exposure Concentration. EPC = Exposure Point Concentration. kg = kilogram. L = liter. LADI = Lifetime Average Daily Intake. m3 = cubic meter. mg = milligram. N = Nitrogen. NA = Not available. ND = Not detected. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\Tables2-12_withFormulas.xlsx Page 1 of 1 Table 11: Combined Adult and Child Resident Cancer Risk Estimates Domestic Water Source (Exposure Point) Rialto Well No. 6 Chemical of Potential Concern Adult Resident Cancer Risk Child Resident Cancer Risk Combined Adult and Child Resident Cancer Risk DBCP Arsenic Chloroform Chromium, Hexavalent Fluoride Nitrate (as N) Perchlorate Trichloroethene ND ND 1E-06 ----3E-06 5E-06 ND ND 5E-07 ----9E-07 1E-06 ND ND 2E-06 ----3E-06 5E-06 DBCP Arsenic Chloroform Chromium, Hexavalent Fluoride Nitrate (as N) Perchlorate Trichloroethene 2E-05 2E-05 ND ----5E-07 4E-05 5E-06 1E-05 ND ----1E-07 2E-05 2E-05 3E-05 ND ----5E-07 5E-05 Exposure Point Total District Well No. 11 Exposure Point Total Note: Bolded values represent noncancer hazards or cancer risks that exceed Department of Toxic Substances Control point of departure levels. Abbreviations: -- = Not Applicable. DBCP = 1, 2-Dibromochloro-3-propane. N = Nitrogen. NA = Not available. ND = Not detected. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\Tables2-12_withFormulas.xlsx Page 1 of 1 Table 12: Summary of Human Health Risks Maximum Cancer Risks for Individual COPCs Cumulative Cancer Risk for COPCs Maximum Noncancer Hazards for Individual COPCs Domestic Water Source (Exposure Point) Exposure Scenario Rialto Well No. 6 Adult Resident 3E-06 Trichloroethene 5E-06 2E+01 Perchlorate Child Resident 9E-07 Trichloroethene 1E-06 6E+01 Perchlorate Combined Adult and Child Resident 3E-06 Trichloroethene 5E-06 Adult Resident 2E-05 Arsenic, DBCP 4E-05 4E-01 Perchlorate Child Resident 1E-05 Arsenic 2E-05 1E+00 Perchlorate Combined Adult and Child Resident 3E-05 Arsenic 5E-05 District Well No. 11 Notes: Bolded values represent noncancer hazards or cancer risks that exceed Department of Toxic Substances Control point of departure levels. The individual COPC associated with the maximum cancer risk or noncancer hazard is listed. Abbreviations: DBCP = 1,2-Dibromo-3-chloropropane. COPC = Chemical of Potential Concern. Human Health Risk Assessment Report, Wellhead Treatment System Project, West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\Tables2-12_withFormulas.xlsx Page 1 of 1 Figures Gabriel Mountains Sa n Cr n jo Ca Ly tle San Bernardino County An dr ea Cr k ee sF au ee lt Map Area _ ^ h as kW Ba rr ie r Fa ul t ul t ( ' & % 210 Rialto Well No. 6 Cactus Basin A A District Well No. 11 Creek n Fa h as W ol to BA SI N o k ee -C OL TO N ci nt 215 Cr Ri al to -C Ja ( ' & % Cactus Wash 15 % ( ' & Sa n tle Ly RI AL TO E Path: Z:\Projects\West Valley\Events\20100921_NCP_Compliance\MXD\Fig3-1.mxd ar W m nta Sa An aR 10 ( ' & % Sa nT im ote o San Bernardino County Riverside County ( ' & % na Ri ve r 215 þ } | · Sa nt aA 60 Image Source: ESRI Legend A A Rialto Well No. 6 Fault Rialto-Colton Basin Fault (Concealed) District Well No. 11 Fault (Approximate) 0 ³ 1 Miles Kennedy/Jenks Consultants West Valley Water District and City of Rialto Rialto, California Location Map 2 K/J 1089040*00 November 2010 Figure 1 W Process for Evaluating Potential Risk from Domestic Use of Wells E Exposure Assessment A t COPC Selection Screen detected d d chemicals in two wells to identify the subset of chemicals to evaluate further in HHRA in HHRA Evaluate how people will be exposed to COPCs through domestic use of the two wells and at what levels (i e dose)1 what levels (i.e., dose) Toxicity Assessment Evaluate potential Evaluate potential cancer and non‐cancer health effects (i.e., toxicity) associated with exposure to COPCs Notes: 1 Exposure Assessment will assume that no reduction in concentration of contaminants through treatment or response actions occurs. Risk Characterization Risk Characterization Risk = Dose x Toxicity Calculate and summarize risk estimates associated with domestic use of the two wells Kennedy/Jenks Consultants West Valley Water District and City of Rialto Rialto, California Human Health Risk Assessment Process K/J 1089040.00 Figure 2 eR vor De Rd Ri ve rs i de Av Bohnert Ave e Foothill Blvd Rialto Well No. 6 A A District Well No. 11 Av e Bl oo m in gt on Alder Ave Sierra Ave Merrill Ave San Bernardino Ave Rialto Ave San Bernardino Ave Valley Blvd § ¨ ¦ 10 Riverside Ave Slover Ave Citrus Ave Foothill Blvd RIALTO Rialto Ave Jurupa Ave COLTON 7th St SAN BERNARDINO COUNTY str on g Rd RIVERSIDE COUNTY Ar m Z:\Projects\West Valley\Events\20100921_NCP_Compliance\MXD\Fig3-3_Service_Area.mxd Base Line Rd Pepper Ave FONTANA Miro Way Cedar Ave Baseline Rd Cactus Ave Highland Ave Ayala Dr Citrus Ave Sierra Ave 15 Linden Ave § ¨ ¦ ek Locust Ave tle Ly e Cr d Note: All locations and boundaries are approximate. Legend A A Rialto Well No. 6 District Well No. 11 West Valley Water District Service Area City of Rialto Service Area 0 ³ 5,000 Scale: Feet Kennedy/Jenks Consultants West Valley Water District and City of Rialto Rialto, California District and City Service Areas 10,000 K/J 1089040*00 November 2010 Figure 3 PRIMARY SOURCE PRIMARY RELEASE MECHANISM SECONDARY SOURCE SECONDARY RELEASE MECHANISM PATHWAY EXPOSURE ROUTE RECEPTOR Future Groundwater Historic Sources Infiltration and Percolation Child Resident Ingestion Dermal absorption Inhalation Groundwater Volatilization during domestic uses Adult Resident Air Potentially complete pathway; quantitative evaluation Complete Pathway Kennedy/Jenks Consultants West Valley Water District and City of Rialto Rialto, California Human Health Conceptual Site Model K/J 1089040.00 Figure 4 Appendix A Human Health Risk Assessment Data Sets PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 SAMP_DATE CHEMICAL_( 26‐Feb‐04 ARSENIC 26‐Feb‐04 DIBROMOCHLOROPROPANE (DBCP) 26‐Feb‐04 ETHYLENE DIBROMIDE (EDB) 26‐Feb‐04 NITRATE (AS NO3) 26‐Feb‐04 PERCHLORATE 20‐May‐04 NITRATE (AS NO3) 20‐May‐04 PERCHLORATE 28‐Jun‐04 FLUORIDE (TREATMENT RELATED‐DISTRIBUTION) 28‐Jun‐04 NITRATE (AS NO3) 28‐Jun‐04 PERCHLORATE 21‐Jul‐04 DIBROMOCHLOROPROPANE (DBCP) 21‐Jul‐04 ETHYLENE DIBROMIDE (EDB) 21‐Jul‐04 NITRATE (AS NO3) 21‐Jul‐04 NITRATE + NITRITE (AS N) 21‐Jul‐04 NITRITE (AS N) 21‐Jul‐04 PERCHLORATE 13‐Aug‐04 NITRATE NITROGEN (NO3‐N) 13‐Aug‐04 PERCHLORATE 30‐Sep‐04 NITRATE (AS NO3) 30‐Sep‐04 PERCHLORATE 27‐Oct‐04 NITRATE (AS NO3) 27‐Oct‐04 PERCHLORATE 18‐Nov‐04 CHLORINE DIOXIDE 18‐Nov‐04 NITRATE NITROGEN (NO3‐N) 18‐Nov‐04 NITRITE (AS N) 29‐Dec‐04 ARSENIC 29‐Dec‐04 NITRATE (AS NO3) 29‐Dec‐04 PERCHLORATE 07‐Jan‐05 ARSENIC 07‐Jan‐05 NITRATE (AS NO3) 07‐Jan‐05 PERCHLORATE 18‐Feb‐05 ARSENIC 21‐Mar‐05 NITRATE (AS NO3) 21‐Mar‐05 PERCHLORATE 30‐Mar‐05 ARSENIC 26‐Apr‐05 PERCHLORATE 25‐May‐05 PERCHLORATE 15‐Jun‐05 ALUMINUM 15‐Jun‐05 ANTIMONY 15‐Jun‐05 ARSENIC 15‐Jun‐05 BARIUM 15‐Jun‐05 BERYLLIUM 15‐Jun‐05 CADMIUM 15‐Jun‐05 CHROMIUM (TOTAL) 15‐Jun‐05 COPPER 15‐Jun‐05 CYANIDE 15‐Jun‐05 FLUORIDE (F) (NATURAL‐SOURCE) Det_Flag ug/l_Result Units 0 2 ug/l 0 0.01 ug/l 0 0.02 ug/l 1 48000 ug/l 0 4 ug/l 1 32000 ug/l 1 2.8 ug/l 0 100 ug/l 1 34000 ug/l 1 3.8 ug/l 0 0.01 ug/l 0 0.02 ug/l 1 29000 ug/l 1 6600 ug/l 0 150 ug/l 1 4 ug/l 1 7400 ug/l 1 4.6 ug/l 1 40000 ug/l 1 4.5 ug/l 1 35000 ug/l 1 3.8 ug/l 0 100 ug/l 1 7700 ug/l 0 150 ug/l 0 1 ug/l 1 39000 ug/l 1 4.7 ug/l 1 1 ug/l 1 40000 ug/l 1 4.3 ug/l 0 1 ug/l 1 27000 ug/l 0 1 ug/l 1 1.1 ug/l 1 4.7 ug/l 1 5.3 ug/l 0 10 ug/l 0 2 ug/l 0 1 ug/l 1 42 ug/l 0 0.5 ug/l 0 1 ug/l 1 2.4 ug/l 1 2.9 ug/l 0 25 ug/l 1 290 ug/l Page 1 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 SAMP_DATE 15‐Jun‐05 15‐Jun‐05 15‐Jun‐05 15‐Jun‐05 15‐Jun‐05 15‐Jun‐05 15‐Jun‐05 15‐Jun‐05 15‐Jun‐05 15‐Jun‐05 15‐Jun‐05 15‐Jun‐05 15‐Jun‐05 15‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 16‐Jun‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 CHEMICAL_( FLUORIDE (TREATMENT RELATED‐DISTRIBUTION) IRON LEAD MANGANESE MERCURY NICKEL NITRATE (AS NO3) NITRATE NITROGEN (NO3‐N) NITRITE (AS N) PERCHLORATE SELENIUM SILVER THALLIUM ZINC ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CHROMIUM (TOTAL) COPPER CYANIDE FLUORIDE (F) (NATURAL‐SOURCE) IRON LEAD MANGANESE MERCURY NICKEL NITRATE (AS NO3) NITRATE NITROGEN (NO3‐N) NITRITE (AS N) PERCHLORATE SELENIUM SILVER THALLIUM ZINC 1,1,1‐TRICHLOROETHANE 1,1,2,2‐TETRACHLOROETHANE 1,1,2‐TRICHLORO‐1,2,2‐TRIFLUOROETHANE 1,1,2‐TRICHLOROETHANE 1,1‐DICHLOROETHANE 1,1‐DICHLOROETHYLENE 1,2,4‐TRICHLOROBENZENE 1,2‐DICHLOROBENZENE 1,2‐DICHLOROETHANE 1,2‐DICHLOROPROPANE Det_Flag ug/l_Result Units 0 100 ug/l 1 61 ug/l 0 1 ug/l 1 2.1 ug/l 0 0.2 ug/l 0 2 ug/l 1 43000 ug/l 1 9700 ug/l 0 150 ug/l 1 4.8 ug/l 0 2 ug/l 0 1 ug/l 0 1 ug/l 0 20 ug/l 0 10 ug/l 0 2 ug/l 0 1 ug/l 1 42 ug/l 0 0.5 ug/l 0 1 ug/l 1 2.4 ug/l 1 2.9 ug/l 0 25 ug/l 1 290 ug/l 1 61 ug/l 0 1 ug/l 1 2.1 ug/l 0 0.2 ug/l 0 2 ug/l 1 43000 ug/l 1 9700 ug/l 0 150 ug/l 1 4.8 ug/l 0 2 ug/l 0 1 ug/l 0 1 ug/l 0 20 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 10 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l Page 2 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 SAMP_DATE 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 21‐Jul‐05 CHEMICAL_( 1,3‐DICHLOROPROPENE (TOTAL) 1,4‐DICHLOROBENZENE 2,3,7,8‐TCDD (DIOXIN) 2,4,5‐TP (SILVEX) 2,4‐D 3‐HYDROXYCARBOFURAN 4‐NITROPHENOL ALACHLOR ALDICARB ALDICARB SULFONE ALDICARB SULFOXIDE ATRAZINE BENTAZON BENZENE BENZO (A) PYRENE BROMODICHLORMETHANE (THM) BROMOFORM (THM) CARBARYL CARBOFURAN CARBON TETRACHLORIDE CHLORDANE CHLOROFORM (THM) CIS‐1,2‐DICHLOROETHYLENE CIS‐1,3‐DICHLOROPROPENE DALAPON DCPA (TOTAL DI & MONO ACID DEGRADATES) DI(2‐ETHYLHEXYL)ADIPATE DI(2‐ETHYLHEXYL)PHTHALATE DIBROMOCHLOROMETHANE (THM) DIBROMOCHLOROPROPANE (DBCP) DICAMBA DICHLOROMETHANE DINOSEB DIQUAT ENDOTHALL ENDRIN ETHYLBENZENE ETHYLENE DIBROMIDE (EDB) GLYPHOSATE HEPTACHLOR HEPTACHLOR EPOXIDE HEXACHLOROBENZENE HEXACHLOROCYCLOPENTADIENE LINDANE M,P‐XYLENE METHOMYL METHOXYCHLOR Det_Flag ug/l_Result Units 0 0.5 ug/l 0 0.5 ug/l 0 0.000005 ug/l 0 1 ug/l 0 10 ug/l 0 3 ug/l 0 5 ug/l 0 1 ug/l 0 3 ug/l 0 2 ug/l 0 3 ug/l 0 0.5 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 5 ug/l 0 0.5 ug/l 0 0.1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 10 ug/l 0 1 ug/l 0 5 ug/l 0 3 ug/l 0 0.5 ug/l 1 0.012 ug/l 0 1.5 ug/l 0 0.5 ug/l 0 2 ug/l 0 4 ug/l 0 45 ug/l 0 0.1 ug/l 0 0.5 ug/l 0 0.02 ug/l 0 25 ug/l 0 0.01 ug/l 0 0.01 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.2 ug/l 0 0.5 ug/l 0 2 ug/l 0 10 ug/l Page 3 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 SAMP_DATE CHEMICAL_( 21‐Jul‐05 METHYL‐TERT‐BUTYL‐ETHER (MTBE) 21‐Jul‐05 MOLINATE 21‐Jul‐05 MONOCHLOROBENZENE 21‐Jul‐05 OXAMYL 21‐Jul‐05 O‐XYLENE 21‐Jul‐05 PARAQUAT 21‐Jul‐05 PCB‐1016 (AS DECACHLOROBIPHENYL (DCB)) 21‐Jul‐05 PCB‐1221 (AS DCB) 21‐Jul‐05 PCB‐1232 (AS DCB) 21‐Jul‐05 PCB‐1242 (AS DCB) 21‐Jul‐05 PCB‐1248 (AS DCB) 21‐Jul‐05 PCB‐1254 (AS DCB) 21‐Jul‐05 PCB‐1260 (AS DCB) 21‐Jul‐05 PENTACHLOROPHENOL 21‐Jul‐05 PERCHLORATE 21‐Jul‐05 PICLORAM 21‐Jul‐05 POLYCHLORINATED BIPHENYLS, TOTAL, AS DCB 21‐Jul‐05 SIMAZINE 21‐Jul‐05 STYRENE 21‐Jul‐05 TETRACHLOROETHYLENE 21‐Jul‐05 THIOBENCARB 21‐Jul‐05 TOLUENE 21‐Jul‐05 TOXAPHENE 21‐Jul‐05 TRANS‐1,2‐DICHLOROETHYLENE 21‐Jul‐05 TRANS‐1,3‐DICHLOROPROPENE 21‐Jul‐05 TRICHLOROETHYLENE 21‐Jul‐05 TRICHLOROFLUOROMETHANE 21‐Jul‐05 VINYL CHLORIDE 21‐Jul‐05 XYLENES (TOTAL) 29‐Sep‐05 ARSENIC 29‐Sep‐05 NITRATE (AS NO3) 29‐Sep‐05 PERCHLORATE 14‐Oct‐05 NITRATE NITROGEN (NO3‐N) 14‐Oct‐05 PERCHLORATE 30‐Nov‐05 NITRATE (AS NO3) 30‐Nov‐05 PERCHLORATE 29‐Dec‐05 ARSENIC 20‐Jan‐06 NITRATE (AS NO3) 20‐Jan‐06 PERCHLORATE 22‐Mar‐06 ARSENIC 22‐Mar‐06 METHYL‐TERT‐BUTYL‐ETHER (MTBE) 22‐Mar‐06 PERCHLORATE 18‐May‐06 PERCHLORATE 29‐Jun‐06 ARSENIC 29‐Jun‐06 NITRATE (AS NO3) 29‐Jun‐06 NITRITE (AS N) 29‐Jun‐06 PERCHLORATE Det_Flag ug/l_Result Units 0 3 ug/l 0 2 ug/l 0 0.5 ug/l 0 20 ug/l 0 0.5 ug/l 0 20 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.2 ug/l 1 6.5 ug/l 0 1 ug/l 0 0.1 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 0.5 ug/l 0 1 ug/l 1 1.2 ug/l 1 43000 ug/l 1 4.9 ug/l 1 9200 ug/l 1 4.3 ug/l 1 37000 ug/l 1 3.9 ug/l 0 1 ug/l 1 34000 ug/l 1 3.7 ug/l 0 1 ug/l 0 3 ug/l 1 4.1 ug/l 1 3.5 ug/l 0 1 ug/l 1 38000 ug/l 0 150 ug/l 1 3.9 ug/l Page 4 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 WELL 11 ‐ RAW WELL 11 ‐ RAW SAMP_DATE CHEMICAL_( 19‐Jul‐06 PERCHLORATE 15‐Sep‐06 ARSENIC 15‐Sep‐06 NITRATE (AS NO3) 15‐Sep‐06 PERCHLORATE 20‐Oct‐06 PERCHLORATE 03‐Nov‐06 PERCHLORATE 27‐Dec‐06 METHYL‐TERT‐BUTYL‐ETHER (MTBE) 28‐Feb‐07 PERCHLORATE 20‐Mar‐07 PERCHLORATE 24‐Apr‐07 PERCHLORATE 15‐Jun‐07 ARSENIC 15‐Jun‐07 DIBROMOCHLOROPROPANE (DBCP) 15‐Jun‐07 ETHYLENE DIBROMIDE (EDB) 15‐Jun‐07 METHYL‐TERT‐BUTYL‐ETHER (MTBE) 15‐Jun‐07 NITRATE (AS NO3) 15‐Jun‐07 NITRATE NITROGEN (NO3‐N) 15‐Jun‐07 PERCHLORATE 27‐Sep‐07 NITRATE (AS NO3) 27‐Sep‐07 PERCHLORATE 30‐Nov‐07 PERCHLORATE 12‐Sep‐08 ALUMINUM 12‐Sep‐08 ANTIMONY 12‐Sep‐08 ARSENIC 12‐Sep‐08 BARIUM 12‐Sep‐08 BERYLLIUM 12‐Sep‐08 CADMIUM 12‐Sep‐08 CHROMIUM (TOTAL) 12‐Sep‐08 COPPER 12‐Sep‐08 CYANIDE 12‐Sep‐08 FLUORIDE (F) (NATURAL‐SOURCE) 12‐Sep‐08 IRON 12‐Sep‐08 LEAD 12‐Sep‐08 MANGANESE 12‐Sep‐08 MERCURY 12‐Sep‐08 NICKEL 12‐Sep‐08 NITRATE (AS NO3) 12‐Sep‐08 NITRATE + NITRITE (AS N) 12‐Sep‐08 NITRITE (AS N) 12‐Sep‐08 SELENIUM 12‐Sep‐08 SILVER 12‐Sep‐08 THALLIUM 12‐Sep‐08 ZINC 26‐Sep‐08 IRON 26‐Sep‐08 NITRATE (AS NO3) 26‐Sep‐08 PERCHLORATE 26‐Mar‐99 PERCHLORATE 19‐May‐99 PERCHLORATE Det_Flag ug/l_Result Units 1 3.9 ug/l 0 1 ug/l 1 39000 ug/l 1 3.6 ug/l 1 2.9 ug/l 1 3.7 ug/l 0 0.5 ug/l 1 2.4 ug/l 0 4 ug/l 0 4 ug/l 0 1 ug/l 1 0.032 ug/l 0 0.02 ug/l 0 0.5 ug/l 1 41000 ug/l 1 9200 ug/l 0 4 ug/l 1 38000 ug/l 0 4 ug/l 0 4 ug/l 0 10 ug/l 0 2 ug/l 0 1 ug/l 0 36 ug/l 0 0.5 ug/l 0 1 ug/l 0 2.3 ug/l 0 2.7 ug/l 0 25 ug/l 1 320 ug/l 0 1500 ug/l 0 1 ug/l 0 3.6 ug/l 0 0.2 ug/l 0 2 ug/l 1 39000 ug/l 0 8700 ug/l 0 150 ug/l 0 2 ug/l 0 1 ug/l 0 1 ug/l 0 20 ug/l 0 380 ug/l 1 35000 ug/l 0 4 ug/l 0 5 ug/l 0 5 ug/l Page 5 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW SAMP_DATE 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 CHEMICAL_( 1,1,1,2‐TETRACHLORETHANE 1,1,1‐TRICHLOROETHANE 1,1,2,2‐TETRACHLOROETHANE 1,1,2‐TRICHLORO‐1,2,2‐TRIFLUOROETHANE 1,1,2‐TRICHLOROETHANE 1,1‐DICHLOROETHANE 1,1‐DICHLOROETHYLENE 1,1‐DICHLOROPROPENE 1,2,3‐TRICHLOROBENZENE 1,2,3‐TRICHLOROPROPANE 1,2,4‐TRICHLOROBENZENE 1,2,4‐TRIMETHYLBENZENE 1,2‐DICHLOROBENZENE 1,2‐DICHLOROETHANE 1,2‐DICHLOROPROPANE 1,3,5‐TRIMETHYLBENZENE 1,3‐DICHLOROBENZENE 1,3‐DICHLOROPROPANE 1,3‐DICHLOROPROPENE (TOTAL) 1,4‐DICHLOROBENZENE 1‐PHENYLPROPANE (N‐PROPYLBENZENE) 2,2‐DICHLOROPROPANE 2,3,7,8‐TCDD (DIOXIN) 2,4,5‐TP (SILVEX) 2,4‐D 2‐CHLOROETHYLVINYL ETHER 2‐CHLOROTOLUENE 3‐HYDROXYCARBOFURAN 4‐CHLOROTOLUENE ALACHLOR ALDICARB ALDICARB SULFONE ALDICARB SULFOXIDE ALDRIN ALUMINUM ANTIMONY ARSENIC ATRAZINE BARIUM BENTAZON BENZENE BENZO (A) PYRENE BERYLLIUM BROMACIL BROMOBENZENE BROMOCHLOROMETHANE BROMODICHLORMETHANE (THM) Det_Flag ug/l_Result Units 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 10 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.005 ug/l 0 0.5 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.000005 ug/l 0 1 ug/l 0 10 ug/l 0 0 ug/l 0 0.5 ug/l 0 3 ug/l 0 0.5 ug/l 0 1 ug/l 0 3 ug/l 0 4 ug/l 0 3 ug/l 0 0.075 ug/l 0 50 ug/l 0 6 ug/l 0 2 ug/l 0 0.5 ug/l 0 100 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.1 ug/l 0 1 ug/l 0 10 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l Page 6 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW SAMP_DATE 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 CHEMICAL_( BROMOFORM (THM) BROMOMETHANE BUTACHLOR CADMIUM CARBARYL CARBOFURAN CARBON TETRACHLORIDE CHLORDANE CHLOROETHANE CHLOROFORM (THM) CHLOROMETHANE CHLOROTHALONIL CHROMIUM (TOTAL) CIS‐1,2‐DICHLOROETHYLENE COPPER CYANIDE DALAPON DI(2‐ETHYLHEXYL)ADIPATE DI(2‐ETHYLHEXYL)PHTHALATE DIAZINON DIBROMOCHLOROMETHANE (THM) DIBROMOCHLOROPROPANE (DBCP) DIBROMOMETHANE DICAMBA DICHLORODIFLUOROMETHANE (FREON 12) DICHLOROMETHANE DIELDRIN DIMETHOATE DINOSEB DIQUAT DIURON ENDOTHALL ENDRIN ETHYLBENZENE ETHYLENE DIBROMIDE (EDB) ETHYL‐TERT‐BUTYL ETHER FLUORIDE (F) (NATURAL‐SOURCE) GLYPHOSATE HEPTACHLOR HEPTACHLOR EPOXIDE HEXACHLOROBENZENE HEXACHLOROBUTADIENE HEXACHLOROCYCLOPENTADIENE IRON ISOPROPYLBENZENE LEAD LINDANE Det_Flag ug/l_Result Units 0 1 ug/l 0 0.5 ug/l 0 0.38 ug/l 0 1 ug/l 0 5 ug/l 0 5 ug/l 0 0.5 ug/l 0 0.1 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 0 5 ug/l 0 10 ug/l 0 0.5 ug/l 0 50 ug/l 0 100 ug/l 0 10 ug/l 0 5 ug/l 0 3 ug/l 0 0 ug/l 0 1 ug/l 0 0.01 ug/l 0 0.5 ug/l 0 1.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.02 ug/l 0 0 ug/l 0 2 ug/l 0 4 ug/l 0 0 ug/l 0 45 ug/l 0 0.1 ug/l 0 0.5 ug/l 0 0.02 ug/l 0 3 ug/l 1 137 ug/l 0 25 ug/l 0 0.01 ug/l 0 0.01 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 100 ug/l 0 0.5 ug/l 0 5 ug/l 0 0.2 ug/l Page 7 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW SAMP_DATE 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 28‐Jul‐99 02‐Aug‐99 02‐Aug‐99 24‐Sep‐99 24‐Sep‐99 09‐Mar‐00 CHEMICAL_( M,P‐XYLENE MANGANESE MERCURY METHOMYL METHOXYCHLOR METHYL‐TERT‐BUTYL‐ETHER (MTBE) METOLACHLOR METRIBUZIN MOLINATE MONOCHLOROBENZENE NAPHTHALENE N‐BUTYLBENZENE NICKEL NITRATE (AS NO3) NITRATE + NITRITE (AS N) NITRITE (AS N) OXAMYL O‐XYLENE PENTACHLOROPHENOL PICLORAM P‐ISOPROPYLTOLUENE POLYCHLORINATED BIPHENYLS, TOTAL, AS DCB PROMETRYN PROPACHLOR SEC‐BUTYLBENZENE SELENIUM SILVER SIMAZINE STYRENE TERT‐AMYL‐METHYL ETHER TERT‐BUTYLBENZENE TETRACHLOROETHYLENE THALLIUM THIOBENCARB TOLUENE TOXAPHENE TRANS‐1,2‐DICHLOROETHYLENE TRICHLOROETHYLENE TRICHLOROFLUOROMETHANE VINYL CHLORIDE XYLENES (TOTAL) ZINC NITRATE (AS NO3) PERCHLORATE NITRATE (AS NO3) PERCHLORATE 1,1,1,2‐TETRACHLORETHANE Det_Flag ug/l_Result Units 0 0.5 ug/l 0 20 ug/l 0 1 ug/l 0 2 ug/l 0 10 ug/l 0 3 ug/l 0 0 ug/l 0 0 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 10 ug/l 1 52200 ug/l 1 11800 ug/l 0 400 ug/l 0 20 ug/l 0 0.5 ug/l 0 0.2 ug/l 0 1 ug/l 0 0 ug/l 0 0.5 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 10 ug/l 0 1 ug/l 0 0.5 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 1 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 0.5 ug/l 0 0 ug/l 0 50 ug/l 1 48700 ug/l 0 5 ug/l 1 54300 ug/l 0 4 ug/l 0 0.5 ug/l Page 8 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW SAMP_DATE 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 CHEMICAL_( 1,1,1‐TRICHLOROETHANE 1,1,2,2‐TETRACHLOROETHANE 1,1,2‐TRICHLORO‐1,2,2‐TRIFLUOROETHANE 1,1,2‐TRICHLOROETHANE 1,1‐DICHLOROETHANE 1,1‐DICHLOROETHYLENE 1,1‐DICHLOROPROPENE 1,2,3‐TRICHLOROBENZENE 1,2,3‐TRICHLOROPROPANE 1,2,4‐TRICHLOROBENZENE 1,2,4‐TRIMETHYLBENZENE 1,2‐DICHLOROBENZENE 1,2‐DICHLOROETHANE 1,2‐DICHLOROPROPANE 1,3,5‐TRIMETHYLBENZENE 1,3‐DICHLOROBENZENE 1,3‐DICHLOROPROPANE 1,3‐DICHLOROPROPENE (TOTAL) 1,4‐DICHLOROBENZENE 1‐PHENYLPROPANE (N‐PROPYLBENZENE) 2,2‐DICHLOROPROPANE 2,3,7,8‐TCDD (DIOXIN) 2,4,5‐TP (SILVEX) 2,4‐D 2‐CHLOROETHYLVINYL ETHER 2‐CHLOROTOLUENE 3‐HYDROXYCARBOFURAN 4‐CHLOROTOLUENE ALACHLOR ALDICARB ALDICARB SULFONE ALDICARB SULFOXIDE ALDRIN ALUMINUM ANTIMONY ARSENIC ATRAZINE BARIUM BENTAZON BENZENE BENZO (A) PYRENE BERYLLIUM BROMACIL BROMOBENZENE BROMOCHLOROMETHANE BROMODICHLORMETHANE (THM) BROMOFORM (THM) Det_Flag ug/l_Result Units 0 0.5 ug/l 0 0.5 ug/l 0 10 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.005 ug/l 0 0.5 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.000005 ug/l 0 1 ug/l 0 10 ug/l 0 0 ug/l 0 0.5 ug/l 0 3 ug/l 0 0.5 ug/l 0 1 ug/l 0 3 ug/l 0 4 ug/l 0 3 ug/l 0 0.075 ug/l 0 50 ug/l 0 6 ug/l 0 2 ug/l 0 0.5 ug/l 0 100 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.1 ug/l 0 1 ug/l 0 10 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 1 ug/l Page 9 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW SAMP_DATE 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 CHEMICAL_( BROMOMETHANE BUTACHLOR CADMIUM CARBARYL CARBOFURAN CARBON TETRACHLORIDE CHLORDANE CHLOROETHANE CHLOROFORM (THM) CHLOROMETHANE CHLOROTHALONIL CHROMIUM (TOTAL) CIS‐1,2‐DICHLOROETHYLENE COPPER CYANIDE DALAPON DI(2‐ETHYLHEXYL)ADIPATE DI(2‐ETHYLHEXYL)PHTHALATE DIAZINON DIBROMOCHLOROMETHANE (THM) DIBROMOCHLOROPROPANE (DBCP) DIBROMOMETHANE DICAMBA DICHLORODIFLUOROMETHANE (FREON 12) DICHLOROMETHANE DIELDRIN DIMETHOATE DINOSEB DIQUAT DIURON ENDOTHALL ENDRIN ETHYLBENZENE ETHYLENE DIBROMIDE (EDB) ETHYL‐TERT‐BUTYL ETHER FLUORIDE (F) (NATURAL‐SOURCE) GLYPHOSATE HEPTACHLOR HEPTACHLOR EPOXIDE HEXACHLOROBENZENE HEXACHLOROBUTADIENE HEXACHLOROCYCLOPENTADIENE IRON ISOPROPYLBENZENE LEAD LINDANE M,P‐XYLENE Det_Flag ug/l_Result Units 0 0.5 ug/l 0 0.38 ug/l 0 1 ug/l 0 5 ug/l 0 5 ug/l 0 0.5 ug/l 0 0.1 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 0 5 ug/l 0 10 ug/l 0 0.5 ug/l 0 50 ug/l 0 100 ug/l 0 10 ug/l 0 5 ug/l 0 3 ug/l 0 0 ug/l 0 1 ug/l 0 0.01 ug/l 0 0.5 ug/l 0 1.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.02 ug/l 0 0 ug/l 0 2 ug/l 0 4 ug/l 0 0 ug/l 0 45 ug/l 0 0.1 ug/l 0 0.5 ug/l 0 0.02 ug/l 0 3 ug/l 0 100 ug/l 0 25 ug/l 0 0.01 ug/l 0 0.01 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 100 ug/l 0 0.5 ug/l 0 5 ug/l 0 0.2 ug/l 0 0.5 ug/l Page 10 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW SAMP_DATE 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 09‐Mar‐00 16‐Mar‐01 16‐Mar‐01 16‐Mar‐01 28‐Jul‐01 28‐Jul‐01 CHEMICAL_( MANGANESE MERCURY METHOMYL METHOXYCHLOR METHYL‐TERT‐BUTYL‐ETHER (MTBE) METOLACHLOR METRIBUZIN MOLINATE MONOCHLOROBENZENE NAPHTHALENE N‐BUTYLBENZENE NICKEL NITRATE (AS NO3) NITRATE + NITRITE (AS N) NITRITE (AS N) OXAMYL O‐XYLENE PENTACHLOROPHENOL PERCHLORATE PICLORAM P‐ISOPROPYLTOLUENE POLYCHLORINATED BIPHENYLS, TOTAL, AS DCB PROMETRYN PROPACHLOR SEC‐BUTYLBENZENE SELENIUM SILVER SIMAZINE STYRENE TERT‐AMYL‐METHYL ETHER TERT‐BUTYLBENZENE TETRACHLOROETHYLENE THALLIUM THIOBENCARB TOLUENE TOXAPHENE TRANS‐1,2‐DICHLOROETHYLENE TRICHLOROETHYLENE TRICHLOROFLUOROMETHANE VINYL CHLORIDE XYLENES (TOTAL) ZINC METHYL‐TERT‐BUTYL‐ETHER (MTBE) NITRATE (AS NO3) PERCHLORATE 1,1,1,2‐TETRACHLORETHANE 1,1,1‐TRICHLOROETHANE Det_Flag ug/l_Result Units 0 20 ug/l 0 1 ug/l 0 2 ug/l 0 10 ug/l 0 3 ug/l 0 0 ug/l 0 0 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 10 ug/l 1 52000 ug/l 1 10400 ug/l 0 400 ug/l 0 20 ug/l 0 0.5 ug/l 0 0.2 ug/l 0 5 ug/l 0 1 ug/l 0 0 ug/l 0 0.5 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 10 ug/l 0 1 ug/l 0 0.5 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 1 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 1 1 ug/l 0 5 ug/l 0 0.5 ug/l 0 0 ug/l 0 50 ug/l 0 3 ug/l 1 49000 ug/l 0 4 ug/l 0 0.5 ug/l 0 0.5 ug/l Page 11 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW SAMP_DATE 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 CHEMICAL_( 1,1,2,2‐TETRACHLOROETHANE 1,1,2‐TRICHLORO‐1,2,2‐TRIFLUOROETHANE 1,1,2‐TRICHLOROETHANE 1,1‐DICHLOROETHANE 1,1‐DICHLOROETHYLENE 1,1‐DICHLOROPROPENE 1,2,3‐TRICHLOROBENZENE 1,2,4‐TRICHLOROBENZENE 1,2,4‐TRIMETHYLBENZENE 1,2‐DICHLOROBENZENE 1,2‐DICHLOROETHANE 1,2‐DICHLOROPROPANE 1,3,5‐TRIMETHYLBENZENE 1,3‐DICHLOROBENZENE 1,3‐DICHLOROPROPANE 1,3‐DICHLOROPROPENE (TOTAL) 1,4‐DICHLOROBENZENE 1‐PHENYLPROPANE (N‐PROPYLBENZENE) 2,2‐DICHLOROPROPANE 2‐CHLOROETHYLVINYL ETHER 2‐CHLOROTOLUENE 4‐CHLOROTOLUENE BENZENE BROMOBENZENE BROMOCHLOROMETHANE BROMODICHLORMETHANE (THM) BROMOFORM (THM) BROMOMETHANE CARBON TETRACHLORIDE CHLOROETHANE CHLOROFORM (THM) CHLOROMETHANE CIS‐1,2‐DICHLOROETHYLENE DIBROMOCHLOROMETHANE (THM) DIBROMOCHLOROPROPANE (DBCP) DIBROMOMETHANE DICHLORODIFLUOROMETHANE (FREON 12) DICHLOROMETHANE ETHYLBENZENE ETHYLENE DIBROMIDE (EDB) ETHYL‐TERT‐BUTYL ETHER HEXACHLOROBUTADIENE ISOPROPYLBENZENE M,P‐XYLENE METHYL‐TERT‐BUTYL‐ETHER (MTBE) MONOCHLOROBENZENE NAPHTHALENE Det_Flag ug/l_Result Units 0 0.5 ug/l 0 10 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.01 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.02 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l Page 12 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW SAMP_DATE 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 28‐Jul‐01 27‐Feb‐02 27‐Feb‐02 27‐Feb‐02 27‐Mar‐02 27‐Mar‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 CHEMICAL_( N‐BUTYLBENZENE NITRATE (AS NO3) O‐XYLENE PERCHLORATE P‐ISOPROPYLTOLUENE SEC‐BUTYLBENZENE STYRENE TERT‐AMYL‐METHYL ETHER TERT‐BUTYL ALCOHOL TERT‐BUTYLBENZENE TETRACHLOROETHYLENE TOLUENE TRANS‐1,2‐DICHLOROETHYLENE TRICHLOROETHYLENE TRICHLOROFLUOROMETHANE VINYL CHLORIDE XYLENES (TOTAL) CHROMIUM, HEXAVALENT METHYL‐TERT‐BUTYL‐ETHER (MTBE) NITRATE (AS NO3) ARSENIC NITRATE (AS NO3) 1,1,1,2‐TETRACHLORETHANE 1,1,1‐TRICHLOROETHANE 1,1,2,2‐TETRACHLOROETHANE 1,1,2‐TRICHLORO‐1,2,2‐TRIFLUOROETHANE 1,1,2‐TRICHLOROETHANE 1,1‐DICHLOROETHANE 1,1‐DICHLOROETHYLENE 1,1‐DICHLOROPROPENE 1,2,3‐TRICHLOROBENZENE 1,2,4‐TRICHLOROBENZENE 1,2,4‐TRIMETHYLBENZENE 1,2‐DICHLOROBENZENE 1,2‐DICHLOROETHANE 1,2‐DICHLOROPROPANE 1,3,5‐TRIMETHYLBENZENE 1,3‐DICHLOROBENZENE 1,3‐DICHLOROPROPANE 1,3‐DICHLOROPROPENE (TOTAL) 1,4‐DICHLOROBENZENE 1‐PHENYLPROPANE (N‐PROPYLBENZENE) 2,2‐DICHLOROPROPANE 2,3,7,8‐TCDD (DIOXIN) 2,4,5‐TP (SILVEX) 2,4‐D 2‐CHLOROTOLUENE Det_Flag ug/l_Result Units 0 0.5 ug/l 1 49000 ug/l 0 0.5 ug/l 0 4 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 3 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 0.5 ug/l 0 0 ug/l 1 2 ug/l 0 3 ug/l 1 53000 ug/l 0 2 ug/l 1 42000 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 10 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.000005 ug/l 0 1 ug/l 0 10 ug/l 0 0.5 ug/l Page 13 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW SAMP_DATE 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 CHEMICAL_( 3‐HYDROXYCARBOFURAN 4‐CHLOROTOLUENE ALACHLOR ALDICARB ALDICARB SULFONE ALDICARB SULFOXIDE ALDRIN ALUMINUM ANTIMONY ARSENIC ATRAZINE BARIUM BENTAZON BENZENE BENZO (A) PYRENE BERYLLIUM BORON BROMACIL BROMOBENZENE BROMOCHLOROMETHANE BROMODICHLORMETHANE (THM) BROMOFORM (THM) BROMOMETHANE BUTACHLOR CADMIUM CARBARYL CARBOFURAN CARBON TETRACHLORIDE CHLORDANE CHLOROETHANE CHLOROFORM (THM) CHLOROMETHANE CHLOROTHALONIL CHROMIUM (TOTAL) CHROMIUM, HEXAVALENT CIS‐1,2‐DICHLOROETHYLENE COPPER CYANIDE DALAPON DI(2‐ETHYLHEXYL)ADIPATE DI(2‐ETHYLHEXYL)PHTHALATE DIAZINON DIBROMOCHLOROMETHANE (THM) DIBROMOCHLOROPROPANE (DBCP) DIBROMOMETHANE DICAMBA DICHLORODIFLUOROMETHANE (FREON 12) Det_Flag ug/l_Result Units 0 3 ug/l 0 0.5 ug/l 0 1 ug/l 0 3 ug/l 0 4 ug/l 0 3 ug/l 0 0.075 ug/l 0 50 ug/l 0 6 ug/l 0 2 ug/l 0 0.5 ug/l 0 100 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.1 ug/l 0 1 ug/l 0 100 ug/l 0 10 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.38 ug/l 0 1 ug/l 0 5 ug/l 0 5 ug/l 0 0.5 ug/l 0 0.1 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 0 5 ug/l 0 10 ug/l 1 1.8 ug/l 0 0.5 ug/l 0 50 ug/l 0 100 ug/l 0 10 ug/l 0 5 ug/l 0 3 ug/l 0 0 ug/l 0 1 ug/l 0 0.01 ug/l 0 0.5 ug/l 0 1.5 ug/l 0 0.5 ug/l Page 14 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW SAMP_DATE 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 CHEMICAL_( DICHLOROMETHANE DIELDRIN DIMETHOATE DINOSEB DIQUAT ENDOTHALL ENDRIN ETHYLBENZENE ETHYLENE DIBROMIDE (EDB) ETHYL‐TERT‐BUTYL ETHER FLUORIDE (F) (NATURAL‐SOURCE) GLYPHOSATE HEPTACHLOR HEPTACHLOR EPOXIDE HEXACHLOROBENZENE HEXACHLOROBUTADIENE HEXACHLOROCYCLOPENTADIENE IRON ISOPROPYLBENZENE LEAD LINDANE M,P‐XYLENE MANGANESE MERCURY METHOMYL METHOXYCHLOR METHYL‐TERT‐BUTYL‐ETHER (MTBE) METOLACHLOR METRIBUZIN MOLINATE MONOCHLOROBENZENE NAPHTHALENE N‐BUTYLBENZENE NICKEL NITRATE (AS NO3) NITRATE + NITRITE (AS N) NITRITE (AS N) OXAMYL O‐XYLENE PENTACHLOROPHENOL PERCHLORATE PICLORAM P‐ISOPROPYLTOLUENE POLYCHLORINATED BIPHENYLS, TOTAL, AS DCB PROMETRYN PROPACHLOR SEC‐BUTYLBENZENE Det_Flag ug/l_Result Units 0 0.5 ug/l 0 0.02 ug/l 0 0 ug/l 0 2 ug/l 0 4 ug/l 0 45 ug/l 0 0.1 ug/l 0 0.5 ug/l 0 0.02 ug/l 0 3 ug/l 1 230 ug/l 0 25 ug/l 0 0.01 ug/l 0 0.01 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 100 ug/l 0 0.5 ug/l 0 5 ug/l 0 0.2 ug/l 0 0.5 ug/l 0 20 ug/l 0 1 ug/l 0 2 ug/l 0 10 ug/l 0 3 ug/l 0 0 ug/l 0 0 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 10 ug/l 1 45000 ug/l 1 8800 ug/l 0 0 ug/l 0 20 ug/l 0 0.5 ug/l 0 0.2 ug/l 0 4 ug/l 0 1 ug/l 0 0 ug/l 0 0.5 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.5 ug/l Page 15 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT SOURCE_NAM WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW SAMP_DATE 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 28‐Jun‐02 27‐Sep‐02 20‐Dec‐02 20‐Dec‐02 20‐Dec‐02 20‐Dec‐02 20‐Dec‐02 20‐Dec‐02 20‐Dec‐02 20‐Dec‐02 20‐Dec‐02 08‐Aug‐03 08‐Aug‐03 08‐Aug‐03 08‐Aug‐03 08‐Aug‐03 08‐Aug‐03 08‐Aug‐03 08‐Aug‐03 08‐Aug‐03 08‐Aug‐03 08‐Aug‐03 08‐Aug‐03 08‐Aug‐03 08‐Aug‐03 08‐Aug‐03 06‐Mar‐09 06‐Mar‐09 22‐Apr‐09 CHEMICAL_( SELENIUM SILVER SIMAZINE STYRENE TERT‐AMYL‐METHYL ETHER TERT‐BUTYL ALCOHOL TERT‐BUTYLBENZENE TETRACHLOROETHYLENE THALLIUM THIOBENCARB TOLUENE TOXAPHENE TRANS‐1,2‐DICHLOROETHYLENE TRICHLOROETHYLENE TRICHLOROFLUOROMETHANE VANADIUM VINYL CHLORIDE XYLENES (TOTAL) ZINC METHYL‐TERT‐BUTYL‐ETHER (MTBE) ARSENIC BORON CHROMIUM, HEXAVALENT METHYL‐TERT‐BUTYL‐ETHER (MTBE) MOLINATE NITRATE (AS NO3) NITRITE (AS N) PERCHLORATE VANADIUM 1,2,3‐TRICHLOROPROPANE BORON CHROMIUM, HEXAVALENT DIBROMOCHLOROPROPANE (DBCP) DICHLORODIFLUOROMETHANE (FREON 12) ETHYLENE DIBROMIDE (EDB) ETHYL‐TERT‐BUTYL ETHER METHYL‐TERT‐BUTYL‐ETHER (MTBE) MOLINATE NITRATE (AS NO3) NITRATE + NITRITE (AS N) PERCHLORATE TERT‐AMYL‐METHYL ETHER TERT‐BUTYL ALCOHOL VANADIUM NITRATE (AS NO3) PERCHLORATE IRON Det_Flag ug/l_Result Units 0 5 ug/l 0 10 ug/l 0 1 ug/l 0 0.5 ug/l 0 3 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 1 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 1 4.6 ug/l 0 0.5 ug/l 0 0 ug/l 0 50 ug/l 0 3 ug/l 0 2 ug/l 0 100 ug/l 1 1 ug/l 0 5 ug/l 0 2 ug/l 1 48000 ug/l 0 0 ug/l 0 4 ug/l 1 4.1 ug/l 0 0.005 ug/l 0 100 ug/l 1 20 ug/l 0 0.01 ug/l 0 0.5 ug/l 0 0.02 ug/l 0 3 ug/l 0 3 ug/l 0 2 ug/l 1 42000 ug/l 1 8600 ug/l 0 4 ug/l 0 3 ug/l 0 2 ug/l 0 3 ug/l 1 38000 ug/l 0 4 ug/l 0 40 ug/l Page 16 PRIM_STA_C 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610004‐008 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610004 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT WEST VALLEY WATER DISTRICT RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW WELL 11 ‐ RAW ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE 22‐Apr‐09 22‐Apr‐09 22‐Apr‐09 22‐Apr‐09 09‐Jun‐09 09‐Jun‐09 09‐Jun‐09 09‐Jun‐09 09‐Jun‐09 09‐Jun‐09 10‐Sep‐09 10‐Sep‐09 10‐Sep‐09 29‐Jun‐10 29‐Jun‐10 07‐Jul‐10 07‐Jul‐10 03‐Feb‐99 03‐Feb‐99 03‐Mar‐99 03‐Mar‐99 03‐Mar‐99 03‐Mar‐99 03‐Mar‐99 03‐Mar‐99 31‐Mar‐99 31‐Mar‐99 31‐Mar‐99 31‐Mar‐99 31‐Mar‐99 31‐Mar‐99 31‐Mar‐99 31‐Mar‐99 31‐Mar‐99 31‐Mar‐99 31‐Mar‐99 31‐Mar‐99 31‐Mar‐99 31‐Mar‐99 31‐Mar‐99 31‐Mar‐99 13‐Apr‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 CHEMICAL_( NITRATE (AS NO3) PERCHLORATE PHOSPHATE (AS PO4) SILICA ETHYLENE DIBROMIDE (EDB) METHYL‐TERT‐BUTYL‐ETHER (MTBE) NITRATE (AS NO3) TETRACHLOROETHYLENE TRICHLOROETHYLENE URANIUM (UG/L) NITRATE (AS NO3) TETRACHLOROETHYLENE URANIUM (UG/L) NITRATE (AS NO3) PERCHLORATE NITRATE (AS NO3) PERCHLORATE NITRATE (AS NO3) PERCHLORATE COPPER IRON MANGANESE NITRATE (AS NO3) PERCHLORATE ZINC 2,3,7,8‐TCDD (DIOXIN) ALACHLOR ATRAZINE BROMACIL BUTACHLOR DIAZINON DIBROMOCHLOROPROPANE (DBCP) DIMETHOATE DIURON ETHYLENE DIBROMIDE (EDB) METOLACHLOR METRIBUZIN MOLINATE PROMETRYN SIMAZINE THIOBENCARB PERCHLORATE 2,3,7,8‐TCDD (DIOXIN) 2,4,5‐TP (SILVEX) 2,4‐D 3‐HYDROXYCARBOFURAN ALACHLOR Det_Flag ug/l_Result Units 1 27000 ug/l 1 4.4 ug/l 0 150 ug/l 1 21000 ug/l 0 0.02 ug/l 0 3 ug/l 1 35000 ug/l 0 0.5 ug/l 0 0.5 ug/l 1 4.6 ug/l 1 37000 ug/l 0 0.5 ug/l 1 4.1 ug/l 1 24000 ug/l 1 12 ug/l 1 24000 ug/l 1 13 ug/l 1 9180 ug/l 0 5 ug/l 0 50 ug/l 0 100 ug/l 0 20 ug/l 1 9000 ug/l 0 4 ug/l 0 50 ug/l 0 0.000005 ug/l 0 1 ug/l 0 0.5 ug/l 0 10 ug/l 0 0.38 ug/l 0 0 ug/l 0 0.01 ug/l 0 0 ug/l 0 0 ug/l 0 0.02 ug/l 0 0 ug/l 0 0 ug/l 0 2 ug/l 0 2 ug/l 0 1 ug/l 0 1 ug/l 0 4 ug/l 0 0.000005 ug/l 0 1 ug/l 0 10 ug/l 0 3 ug/l 0 1 ug/l Page 17 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 23‐Jun‐99 CHEMICAL_( ALDICARB ALDICARB SULFONE ALDICARB SULFOXIDE ALDRIN ATRAZINE BENTAZON BENZO (A) PYRENE BROMACIL BUTACHLOR CARBARYL CARBOFURAN CHLORDANE CHLOROTHALONIL DALAPON DI(2‐ETHYLHEXYL)ADIPATE DI(2‐ETHYLHEXYL)PHTHALATE DIAZINON DIBROMOCHLOROPROPANE (DBCP) DICAMBA DIELDRIN DIMETHOATE DINOSEB DIQUAT DIURON ENDOTHALL ENDRIN ETHYLENE DIBROMIDE (EDB) GLYPHOSATE HEPTACHLOR HEPTACHLOR EPOXIDE HEXACHLOROBENZENE HEXACHLOROCYCLOPENTADIENE LINDANE METHOMYL METHOXYCHLOR METOLACHLOR METRIBUZIN MOLINATE NITRATE (AS NO3) OXAMYL PENTACHLOROPHENOL PERCHLORATE PICLORAM POLYCHLORINATED BIPHENYLS, TOTAL, AS DCB PROMETRYN PROPACHLOR SIMAZINE Det_Flag ug/l_Result Units 0 3 ug/l 0 4 ug/l 0 3 ug/l 0 0.075 ug/l 0 0.5 ug/l 0 2 ug/l 0 0.1 ug/l 0 10 ug/l 0 0.38 ug/l 0 5 ug/l 0 5 ug/l 0 0.1 ug/l 0 5 ug/l 0 10 ug/l 0 5 ug/l 0 3 ug/l 0 0 ug/l 0 0.01 ug/l 0 1.5 ug/l 0 0.02 ug/l 0 0 ug/l 0 2 ug/l 0 4 ug/l 0 0 ug/l 0 45 ug/l 0 0.1 ug/l 0 0.02 ug/l 0 25 ug/l 0 0.01 ug/l 0 0.01 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.2 ug/l 0 2 ug/l 0 10 ug/l 0 0 ug/l 0 0 ug/l 0 2 ug/l 1 7000 ug/l 0 20 ug/l 0 0.2 ug/l 0 4 ug/l 0 1 ug/l 0 0.5 ug/l 0 2 ug/l 0 0.5 ug/l 0 1 ug/l Page 18 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE CHEMICAL_( 23‐Jun‐99 THIOBENCARB 23‐Jun‐99 TOXAPHENE 07‐Jul‐99 PERCHLORATE 04‐Aug‐99 ALUMINUM 04‐Aug‐99 ANTIMONY 04‐Aug‐99 ARSENIC 04‐Aug‐99 BARIUM 04‐Aug‐99 BERYLLIUM 04‐Aug‐99 CADMIUM 04‐Aug‐99 CHROMIUM (TOTAL) 04‐Aug‐99 CYANIDE 04‐Aug‐99 FLUORIDE (F) (NATURAL‐SOURCE) 04‐Aug‐99 LEAD 04‐Aug‐99 MERCURY 04‐Aug‐99 NICKEL 04‐Aug‐99 NITRATE (AS NO3) 04‐Aug‐99 NITRITE (AS N) 04‐Aug‐99 PERCHLORATE 04‐Aug‐99 SELENIUM 04‐Aug‐99 SILVER 04‐Aug‐99 THALLIUM 14‐Sep‐99 PERCHLORATE 06‐Oct‐99 PERCHLORATE 02‐Nov‐99 PERCHLORATE 07‐Dec‐99 PERCHLORATE 11‐Jan‐00 PERCHLORATE 01‐Feb‐00 COPPER 01‐Feb‐00 IRON 01‐Feb‐00 MANGANESE 01‐Feb‐00 NITRATE (AS NO3) 01‐Feb‐00 PERCHLORATE 01‐Feb‐00 ZINC 02‐Mar‐00 1,1,1,2‐TETRACHLORETHANE 02‐Mar‐00 1,1,1‐TRICHLOROETHANE 02‐Mar‐00 1,1,2,2‐TETRACHLOROETHANE 02‐Mar‐00 1,1,2‐TRICHLORO‐1,2,2‐TRIFLUOROETHANE 02‐Mar‐00 1,1,2‐TRICHLOROETHANE 02‐Mar‐00 1,1‐DICHLOROETHANE 02‐Mar‐00 1,1‐DICHLOROETHYLENE 02‐Mar‐00 1,1‐DICHLOROPROPENE 02‐Mar‐00 1,2,3‐TRICHLOROBENZENE 02‐Mar‐00 1,2,3‐TRICHLOROPROPANE 02‐Mar‐00 1,2,4‐TRICHLOROBENZENE 02‐Mar‐00 1,2,4‐TRIMETHYLBENZENE 02‐Mar‐00 1,2‐DICHLOROBENZENE 02‐Mar‐00 1,2‐DICHLOROETHANE 02‐Mar‐00 1,2‐DICHLOROPROPANE Det_Flag ug/l_Result Units 0 1 ug/l 0 1 ug/l 0 4 ug/l 0 50 ug/l 0 6 ug/l 0 2 ug/l 0 100 ug/l 0 1 ug/l 0 1 ug/l 0 10 ug/l 0 100 ug/l 1 400 ug/l 0 5 ug/l 0 1 ug/l 0 10 ug/l 1 8000 ug/l 0 0 ug/l 0 4 ug/l 0 5 ug/l 0 10 ug/l 0 1 ug/l 0 4 ug/l 0 4 ug/l 0 4 ug/l 0 4 ug/l 0 4 ug/l 0 50 ug/l 0 100 ug/l 0 20 ug/l 1 8000 ug/l 0 4 ug/l 0 50 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 10 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.005 ug/l 0 0.5 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l Page 19 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 02‐Mar‐00 CHEMICAL_( 1,3,5‐TRIMETHYLBENZENE 1,3‐DICHLOROBENZENE 1,3‐DICHLOROPROPANE 1,3‐DICHLOROPROPENE (TOTAL) 1,4‐DICHLOROBENZENE 1‐PHENYLPROPANE (N‐PROPYLBENZENE) 2,2‐DICHLOROPROPANE 2‐CHLOROETHYLVINYL ETHER 2‐CHLOROTOLUENE 4‐CHLOROTOLUENE BENZENE BIS (2‐CHLOROETHYL) ETHER BROMOBENZENE BROMOCHLOROMETHANE BROMODICHLORMETHANE (THM) BROMOFORM (THM) BROMOMETHANE CARBON TETRACHLORIDE CHLOROETHANE CHLOROFORM (THM) CHLOROMETHANE CIS‐1,2‐DICHLOROETHYLENE DIBROMOCHLOROMETHANE (THM) DIBROMOMETHANE DICHLORODIFLUOROMETHANE (FREON 12) DICHLOROMETHANE ETHYLBENZENE ETHYL‐TERT‐BUTYL ETHER HEXACHLOROBUTADIENE ISOPROPYLBENZENE M,P‐XYLENE METHYL ETHYL KETONE METHYL ISOBUTYL KETONE METHYL‐TERT‐BUTYL‐ETHER (MTBE) MONOCHLOROBENZENE NAPHTHALENE N‐BUTYLBENZENE O‐XYLENE PERCHLORATE P‐ISOPROPYLTOLUENE SEC‐BUTYLBENZENE STYRENE TERT‐AMYL‐METHYL ETHER TERT‐BUTYLBENZENE TETRACHLOROETHYLENE TOLUENE TRANS‐1,2‐DICHLOROETHYLENE Det_Flag ug/l_Result Units 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 1 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 5 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 4 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l Page 20 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE CHEMICAL_( 02‐Mar‐00 TRICHLOROETHYLENE 02‐Mar‐00 TRICHLOROFLUOROMETHANE 02‐Mar‐00 VINYL CHLORIDE 02‐Mar‐00 XYLENES (TOTAL) 05‐Apr‐00 PERCHLORATE 26‐Apr‐00 PERCHLORATE 02‐May‐00 DIBROMOCHLOROPROPANE (DBCP) 02‐May‐00 ETHYLENE DIBROMIDE (EDB) 02‐May‐00 PERCHLORATE 07‐Jun‐00 PERCHLORATE 11‐Jul‐00 PERCHLORATE 02‐Aug‐00 PERCHLORATE 06‐Sep‐00 PERCHLORATE 19‐Sep‐00 PERCHLORATE 03‐Oct‐00 PERCHLORATE 14‐Nov‐00 PERCHLORATE 06‐Dec‐00 PERCHLORATE 23‐Jan‐01 PERCHLORATE 21‐Feb‐01 COPPER 21‐Feb‐01 IRON 21‐Feb‐01 MANGANESE 21‐Feb‐01 METHYL‐TERT‐BUTYL‐ETHER (MTBE) 21‐Feb‐01 NITRATE (AS NO3) 21‐Feb‐01 PERCHLORATE 21‐Feb‐01 ZINC 14‐Mar‐01 PERCHLORATE 04‐Apr‐01 PERCHLORATE 01‐May‐01 1,2,3‐TRICHLOROPROPANE 01‐May‐01 DIBROMOCHLOROPROPANE (DBCP) 01‐May‐01 ETHYLENE DIBROMIDE (EDB) 01‐May‐01 METHYL‐TERT‐BUTYL‐ETHER (MTBE) 01‐May‐01 PERCHLORATE 10‐Jul‐01 1,1,1,2‐TETRACHLORETHANE 10‐Jul‐01 1,1,1‐TRICHLOROETHANE 10‐Jul‐01 1,1,2,2‐TETRACHLOROETHANE 10‐Jul‐01 1,1,2‐TRICHLORO‐1,2,2‐TRIFLUOROETHANE 10‐Jul‐01 1,1,2‐TRICHLOROETHANE 10‐Jul‐01 1,1‐DICHLOROETHANE 10‐Jul‐01 1,1‐DICHLOROETHYLENE 10‐Jul‐01 1,1‐DICHLOROPROPANE 10‐Jul‐01 1,1‐DICHLOROPROPENE 10‐Jul‐01 1,2,3‐TRICHLOROBENZENE 10‐Jul‐01 1,2,3‐TRICHLOROPROPANE 10‐Jul‐01 1,2,4‐TRICHLOROBENZENE 10‐Jul‐01 1,2,4‐TRIMETHYLBENZENE 10‐Jul‐01 1,2‐DICHLOROBENZENE 10‐Jul‐01 1,2‐DICHLOROETHANE Det_Flag ug/l_Result Units 0 0.5 ug/l 0 5 ug/l 0 0.5 ug/l 0 0 ug/l 1 5 ug/l 0 4 ug/l 0 0.01 ug/l 0 0.02 ug/l 0 4 ug/l 1 6 ug/l 1 6 ug/l 1 5 ug/l 1 9 ug/l 1 6 ug/l 1 7 ug/l 1 7 ug/l 1 9 ug/l 1 10 ug/l 0 50 ug/l 0 100 ug/l 0 20 ug/l 0 3 ug/l 1 11000 ug/l 1 9 ug/l 0 50 ug/l 1 9.7 ug/l 1 9 ug/l 0 0.02 ug/l 0 0.01 ug/l 0 0.02 ug/l 0 3 ug/l 1 13 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 10 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.02 ug/l 0 0.5 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l Page 21 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 CHEMICAL_( 1,2‐DICHLOROPROPANE 1,3,5‐TRIMETHYLBENZENE 1,3‐DICHLOROBENZENE 1,3‐DICHLOROPROPANE 1,3‐DICHLOROPROPENE (TOTAL) 1,4‐DICHLOROBENZENE 1‐PHENYLPROPANE (N‐PROPYLBENZENE) 2,2‐DICHLOROPROPANE 2‐CHLOROETHYLVINYL ETHER 2‐CHLOROTOLUENE 4‐CHLOROTOLUENE BENZENE BIS (2‐CHLOROETHYL) ETHER BORON BROMOBENZENE BROMOCHLOROMETHANE BROMODICHLORMETHANE (THM) BROMOFORM (THM) BROMOMETHANE CARBON TETRACHLORIDE CHLOROETHANE CHLOROFORM (THM) CHLOROMETHANE CIS‐1,2‐DICHLOROETHYLENE DIBROMOCHLOROMETHANE (THM) DIBROMOCHLOROPROPANE (DBCP) DIBROMOMETHANE DICHLORODIFLUOROMETHANE (FREON 12) DICHLOROMETHANE ETHYLBENZENE ETHYLENE DIBROMIDE (EDB) ETHYL‐TERT‐BUTYL ETHER HEXACHLOROBUTADIENE ISOPROPYLBENZENE M,P‐XYLENE METHYL ETHYL KETONE METHYL ISOBUTYL KETONE METHYL‐TERT‐BUTYL‐ETHER (MTBE) MONOCHLOROBENZENE NAPHTHALENE N‐BUTYLBENZENE N‐NITROSODIMETHYLAMINE (NDMA) O‐XYLENE PERCHLORATE P‐ISOPROPYLTOLUENE SEC‐BUTYLBENZENE STYRENE Det_Flag ug/l_Result Units 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 100 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.01 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.02 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 5 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.02 ug/l 0 0.5 ug/l 0 4 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l Page 22 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 10‐Jul‐01 17‐Jul‐01 08‐Aug‐01 08‐Aug‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 18‐Sep‐01 CHEMICAL_( TERT‐AMYL‐METHYL ETHER TERT‐BUTYL ALCOHOL TERT‐BUTYLBENZENE TETRACHLOROETHYLENE TOLUENE TRANS‐1,2‐DICHLOROETHYLENE TRICHLOROETHYLENE TRICHLOROFLUOROMETHANE VANADIUM VINYL CHLORIDE XYLENES (TOTAL) CHROMIUM, HEXAVALENT METHYL‐TERT‐BUTYL‐ETHER (MTBE) PERCHLORATE 1,1,1,2‐TETRACHLORETHANE 1,1,1‐TRICHLOROETHANE 1,1,2,2‐TETRACHLOROETHANE 1,1,2‐TRICHLORO‐1,2,2‐TRIFLUOROETHANE 1,1,2‐TRICHLOROETHANE 1,1‐DICHLOROETHANE 1,1‐DICHLOROETHYLENE 1,1‐DICHLOROPROPENE 1,2,3‐TRICHLOROBENZENE 1,2,3‐TRICHLOROPROPANE 1,2,4‐TRICHLOROBENZENE 1,2,4‐TRIMETHYLBENZENE 1,2‐DICHLOROBENZENE 1,2‐DICHLOROETHANE 1,2‐DICHLOROPROPANE 1,3,5‐TRIMETHYLBENZENE 1,3‐DICHLOROBENZENE 1,3‐DICHLOROPROPANE 1,3‐DICHLOROPROPENE (TOTAL) 1,4‐DICHLOROBENZENE 1‐PHENYLPROPANE (N‐PROPYLBENZENE) 2,2‐DICHLOROPROPANE 2‐CHLOROETHYLVINYL ETHER 2‐CHLOROTOLUENE 4‐CHLOROTOLUENE BENZENE BIS (2‐CHLOROETHYL) ETHER BROMOBENZENE BROMOCHLOROMETHANE BROMODICHLORMETHANE (THM) BROMOFORM (THM) BROMOMETHANE CARBON TETRACHLORIDE Det_Flag ug/l_Result Units 0 3 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 1 5.6 ug/l 0 0.5 ug/l 0 0 ug/l 1 1.4 ug/l 0 3 ug/l 1 8 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 10 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.005 ug/l 0 0.5 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l Page 23 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE CHEMICAL_( 18‐Sep‐01 CHLOROETHANE 18‐Sep‐01 CHLOROFORM (THM) 18‐Sep‐01 CHLOROMETHANE 18‐Sep‐01 CIS‐1,2‐DICHLOROETHYLENE 18‐Sep‐01 DIBROMOCHLOROMETHANE (THM) 18‐Sep‐01 DIBROMOMETHANE 18‐Sep‐01 DICHLORODIFLUOROMETHANE (FREON 12) 18‐Sep‐01 DICHLOROMETHANE 18‐Sep‐01 ETHYLBENZENE 18‐Sep‐01 ETHYL‐TERT‐BUTYL ETHER 18‐Sep‐01 HEXACHLOROBUTADIENE 18‐Sep‐01 ISOPROPYLBENZENE 18‐Sep‐01 M,P‐XYLENE 18‐Sep‐01 METHYL ETHYL KETONE 18‐Sep‐01 METHYL ISOBUTYL KETONE 18‐Sep‐01 METHYL‐TERT‐BUTYL‐ETHER (MTBE) 18‐Sep‐01 MONOCHLOROBENZENE 18‐Sep‐01 NAPHTHALENE 18‐Sep‐01 N‐BUTYLBENZENE 18‐Sep‐01 O‐XYLENE 18‐Sep‐01 PERCHLORATE 18‐Sep‐01 P‐ISOPROPYLTOLUENE 18‐Sep‐01 SEC‐BUTYLBENZENE 18‐Sep‐01 STYRENE 18‐Sep‐01 TERT‐AMYL‐METHYL ETHER 18‐Sep‐01 TERT‐BUTYL ALCOHOL 18‐Sep‐01 TERT‐BUTYLBENZENE 18‐Sep‐01 TETRACHLOROETHYLENE 18‐Sep‐01 TOLUENE 18‐Sep‐01 TRANS‐1,2‐DICHLOROETHYLENE 18‐Sep‐01 TRICHLOROETHYLENE 18‐Sep‐01 TRICHLOROFLUOROMETHANE 18‐Sep‐01 VINYL CHLORIDE 18‐Sep‐01 XYLENES (TOTAL) 02‐Oct‐01 PERCHLORATE 20‐Nov‐01 METHYL‐TERT‐BUTYL‐ETHER (MTBE) 20‐Nov‐01 PERCHLORATE 11‐Dec‐01 1,1,1,2‐TETRACHLORETHANE 11‐Dec‐01 1,1,1‐TRICHLOROETHANE 11‐Dec‐01 1,1,2,2‐TETRACHLOROETHANE 11‐Dec‐01 1,1,2‐TRICHLORO‐1,2,2‐TRIFLUOROETHANE 11‐Dec‐01 1,1,2‐TRICHLOROETHANE 11‐Dec‐01 1,1‐DICHLOROETHANE 11‐Dec‐01 1,1‐DICHLOROETHYLENE 11‐Dec‐01 1,1‐DICHLOROPROPENE 11‐Dec‐01 1,2,3‐TRICHLOROBENZENE 11‐Dec‐01 1,2,3‐TRICHLOROPROPANE Det_Flag ug/l_Result Units 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 5 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 1 8 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 3 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 0.5 ug/l 0 0 ug/l 1 14 ug/l 0 3 ug/l 1 15 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 10 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.02 ug/l Page 24 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 11‐Dec‐01 CHEMICAL_( 1,2,4‐TRICHLOROBENZENE 1,2,4‐TRIMETHYLBENZENE 1,2‐DICHLOROBENZENE 1,2‐DICHLOROETHANE 1,2‐DICHLOROPROPANE 1,3,5‐TRIMETHYLBENZENE 1,3‐DICHLOROBENZENE 1,3‐DICHLOROPROPANE 1,3‐DICHLOROPROPENE (TOTAL) 1,4‐DICHLOROBENZENE 1‐PHENYLPROPANE (N‐PROPYLBENZENE) 2,2‐DICHLOROPROPANE 2‐CHLOROETHYLVINYL ETHER 2‐CHLOROTOLUENE 4‐CHLOROTOLUENE BENZENE BIS (2‐CHLOROETHYL) ETHER BORON BROMOBENZENE BROMOCHLOROMETHANE BROMODICHLORMETHANE (THM) BROMOFORM (THM) BROMOMETHANE CARBON TETRACHLORIDE CHLOROETHANE CHLOROFORM (THM) CHLOROMETHANE CHROMIUM, HEXAVALENT CIS‐1,2‐DICHLOROETHYLENE DIBROMOCHLOROMETHANE (THM) DIBROMOCHLOROPROPANE (DBCP) DIBROMOMETHANE DICHLORODIFLUOROMETHANE (FREON 12) DICHLOROMETHANE ETHYLBENZENE ETHYLENE DIBROMIDE (EDB) ETHYL‐TERT‐BUTYL ETHER HEXACHLOROBUTADIENE ISOPROPYLBENZENE M,P‐XYLENE METHYL ETHYL KETONE METHYL ISOBUTYL KETONE METHYL‐TERT‐BUTYL‐ETHER (MTBE) MONOCHLOROBENZENE NAPHTHALENE N‐BUTYLBENZENE O‐XYLENE Det_Flag ug/l_Result Units 0 0.5 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 100 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 1 1.2 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.01 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.02 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 5 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l Page 25 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE CHEMICAL_( 11‐Dec‐01 PERCHLORATE 11‐Dec‐01 P‐ISOPROPYLTOLUENE 11‐Dec‐01 SEC‐BUTYLBENZENE 11‐Dec‐01 STYRENE 11‐Dec‐01 TERT‐AMYL‐METHYL ETHER 11‐Dec‐01 TERT‐BUTYL ALCOHOL 11‐Dec‐01 TERT‐BUTYLBENZENE 11‐Dec‐01 TETRACHLOROETHYLENE 11‐Dec‐01 TOLUENE 11‐Dec‐01 TRANS‐1,2‐DICHLOROETHYLENE 11‐Dec‐01 TRICHLOROETHYLENE 11‐Dec‐01 TRICHLOROFLUOROMETHANE 11‐Dec‐01 VANADIUM 11‐Dec‐01 VINYL CHLORIDE 11‐Dec‐01 XYLENES (TOTAL) 31‐Jan‐02 METHYL‐TERT‐BUTYL‐ETHER (MTBE) 31‐Jan‐02 PERCHLORATE 21‐Feb‐02 NITRATE (AS NO3) 21‐Feb‐02 PERCHLORATE 12‐Mar‐02 ALUMINUM 12‐Mar‐02 ANTIMONY 12‐Mar‐02 ARSENIC 12‐Mar‐02 BARIUM 12‐Mar‐02 BERYLLIUM 12‐Mar‐02 CADMIUM 12‐Mar‐02 CHROMIUM (TOTAL CR‐CRVI SCREEN) 12‐Mar‐02 CHROMIUM (TOTAL) 12‐Mar‐02 COPPER 12‐Mar‐02 CYANIDE 12‐Mar‐02 FLUORIDE (F) (NATURAL‐SOURCE) 12‐Mar‐02 MANGANESE 12‐Mar‐02 MERCURY 12‐Mar‐02 NICKEL 12‐Mar‐02 NITRATE (AS NO3) 12‐Mar‐02 NITRITE (AS N) 12‐Mar‐02 SELENIUM 12‐Mar‐02 SILVER 12‐Mar‐02 THALLIUM 12‐Mar‐02 ZINC 16‐Apr‐02 PERCHLORATE 14‐May‐02 PERCHLORATE 15‐Aug‐02 PERCHLORATE 12‐Sep‐02 PERCHLORATE 01‐Oct‐02 PERCHLORATE 13‐Nov‐02 PERCHLORATE 09‐Dec‐02 PERCHLORATE 22‐Jan‐03 PERCHLORATE Det_Flag ug/l_Result Units 1 16 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 3 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 1 1 ug/l 0 5 ug/l 1 5 ug/l 0 0.5 ug/l 0 0 ug/l 0 3 ug/l 1 20 ug/l 1 10000 ug/l 1 21 ug/l 0 50 ug/l 0 6 ug/l 0 2 ug/l 0 100 ug/l 0 1 ug/l 0 1 ug/l 1 1.1 ug/l 0 10 ug/l 0 50 ug/l 0 100 ug/l 1 300 ug/l 0 20 ug/l 0 1 ug/l 0 10 ug/l 1 11000 ug/l 0 0 ug/l 0 5 ug/l 0 10 ug/l 0 1 ug/l 0 50 ug/l 1 19 ug/l 1 19 ug/l 1 23 ug/l 1 38 ug/l 1 26 ug/l 1 24 ug/l 1 27 ug/l 1 30 ug/l Page 26 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE CHEMICAL_( 24‐Feb‐03 PERCHLORATE 12‐Mar‐03 NITRATE (AS NO3) 12‐Mar‐03 NITRITE (AS N) 12‐Mar‐03 PERCHLORATE 22‐Apr‐03 PERCHLORATE 21‐May‐03 PERCHLORATE 05‐Jun‐03 PERCHLORATE 23‐Jul‐03 PERCHLORATE 19‐Aug‐03 PERCHLORATE 11‐Sep‐03 PERCHLORATE 22‐Oct‐03 PERCHLORATE 05‐Nov‐03 PERCHLORATE 09‐Dec‐03 PERCHLORATE 13‐Jan‐04 PERCHLORATE 26‐Feb‐04 PERCHLORATE 16‐Mar‐04 PERCHLORATE 20‐Apr‐04 PERCHLORATE 18‐May‐04 PERCHLORATE 16‐Jun‐04 PERCHLORATE 27‐Jul‐04 PERCHLORATE 24‐Aug‐04 PERCHLORATE 22‐Sep‐04 PERCHLORATE 13‐Oct‐04 PERCHLORATE 22‐Nov‐04 PERCHLORATE 14‐Dec‐04 PERCHLORATE 25‐Jan‐05 PERCHLORATE 24‐Feb‐05 1,1,1,2‐TETRACHLORETHANE 24‐Feb‐05 1,1,1‐TRICHLOROETHANE 24‐Feb‐05 1,1,2,2‐TETRACHLOROETHANE 24‐Feb‐05 1,1,2‐TRICHLORO‐1,2,2‐TRIFLUOROETHANE 24‐Feb‐05 1,1,2‐TRICHLOROETHANE 24‐Feb‐05 1,1‐DICHLOROETHANE 24‐Feb‐05 1,1‐DICHLOROETHYLENE 24‐Feb‐05 1,1‐DICHLOROPROPENE 24‐Feb‐05 1,2,3‐TRICHLOROBENZENE 24‐Feb‐05 1,2,4‐TRICHLOROBENZENE 24‐Feb‐05 1,2,4‐TRIMETHYLBENZENE 24‐Feb‐05 1,2‐DICHLOROBENZENE 24‐Feb‐05 1,2‐DICHLOROETHANE 24‐Feb‐05 1,2‐DICHLOROPROPANE 24‐Feb‐05 1,3,5‐TRIMETHYLBENZENE 24‐Feb‐05 1,3‐DICHLOROBENZENE 24‐Feb‐05 1,3‐DICHLOROPROPANE 24‐Feb‐05 1,3‐DICHLOROPROPENE (TOTAL) 24‐Feb‐05 1,4‐DICHLOROBENZENE 24‐Feb‐05 1‐PHENYLPROPANE (N‐PROPYLBENZENE) 24‐Feb‐05 2,2‐DICHLOROPROPANE Det_Flag ug/l_Result Units 1 31 ug/l 1 10000 ug/l 0 0 ug/l 1 32 ug/l 1 34 ug/l 1 32 ug/l 1 35 ug/l 1 41 ug/l 1 46 ug/l 1 36 ug/l 1 40 ug/l 1 42 ug/l 1 45 ug/l 1 45 ug/l 0 4 ug/l 1 45 ug/l 1 45 ug/l 1 52 ug/l 1 53 ug/l 1 56 ug/l 1 57 ug/l 1 57 ug/l 1 57 ug/l 1 62 ug/l 1 68 ug/l 1 71 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 10 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l Page 27 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 24‐Feb‐05 CHEMICAL_( 2‐CHLOROETHYLVINYL ETHER 2‐CHLOROTOLUENE 4‐CHLOROTOLUENE BENZENE BORON BROMOBENZENE BROMOCHLOROMETHANE BROMODICHLORMETHANE (THM) BROMOFORM (THM) BROMOMETHANE CARBON TETRACHLORIDE CHLOROETHANE CHLOROFORM (THM) CHLOROMETHANE CHROMIUM, HEXAVALENT CIS‐1,2‐DICHLOROETHYLENE DIBROMOCHLOROMETHANE (THM) DIBROMOMETHANE DICHLORODIFLUOROMETHANE (FREON 12) DICHLOROMETHANE DIISOPROPYL ETHER ETHYLBENZENE ETHYL‐TERT‐BUTYL ETHER HALOACETIC ACIDS (5) (HAA5) HEXACHLOROBUTADIENE ISOPROPYLBENZENE METHYL ETHYL KETONE METHYL ISOBUTYL KETONE METHYL‐TERT‐BUTYL‐ETHER (MTBE) MONOCHLOROBENZENE NAPHTHALENE N‐BUTYLBENZENE O‐XYLENE PERCHLORATE P‐ISOPROPYLTOLUENE P‐XYLENE SEC‐BUTYLBENZENE STYRENE TERT‐AMYL‐METHYL ETHER TERT‐BUTYL ALCOHOL TERT‐BUTYLBENZENE TETRACHLOROETHYLENE TOLUENE TRANS‐1,2‐DICHLOROETHYLENE TRICHLOROETHYLENE TRICHLOROFLUOROMETHANE VANADIUM Det_Flag ug/l_Result Units 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 100 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 1 1.5 ug/l 0 0.5 ug/l 0 1 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 3 ug/l 0 0.5 ug/l 0 3 ug/l 0 0 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 5 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 1 65 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 3 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 1 1.6 ug/l 0 5 ug/l 1 4.4 ug/l Page 28 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE 24‐Feb‐05 24‐Feb‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 22‐Mar‐05 20‐Apr‐05 20‐Apr‐05 31‐May‐05 31‐May‐05 31‐May‐05 29‐Jun‐05 29‐Jun‐05 29‐Jun‐05 29‐Jun‐05 29‐Jun‐05 29‐Jun‐05 29‐Jun‐05 29‐Jun‐05 29‐Jun‐05 29‐Jun‐05 29‐Jun‐05 29‐Jun‐05 29‐Jun‐05 29‐Jun‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 CHEMICAL_( VINYL CHLORIDE XYLENES (TOTAL) ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CHROMIUM (TOTAL) CYANIDE FLUORIDE (F) (NATURAL‐SOURCE) LEAD MERCURY NICKEL NITRATE (AS NO3) NITRITE (AS N) PERCHLORATE SELENIUM SILVER THALLIUM METHYL‐TERT‐BUTYL‐ETHER (MTBE) PERCHLORATE DIBROMOCHLOROPROPANE (DBCP) ETHYLENE DIBROMIDE (EDB) PERCHLORATE ALACHLOR ATRAZINE BROMACIL BUTACHLOR DIAZINON DIMETHOATE DIURON METOLACHLOR METRIBUZIN MOLINATE PERCHLORATE PROMETRYN SIMAZINE THIOBENCARB 2,3,7,8‐TCDD (DIOXIN) 2,4,5‐TP (SILVEX) 2,4‐D 3‐HYDROXYCARBOFURAN ALACHLOR ALDICARB ALDICARB SULFONE ALDICARB SULFOXIDE Det_Flag ug/l_Result Units 0 0.5 ug/l 0 0 ug/l 0 50 ug/l 0 6 ug/l 0 2 ug/l 0 100 ug/l 0 1 ug/l 0 1 ug/l 0 10 ug/l 0 100 ug/l 1 300 ug/l 0 5 ug/l 0 1 ug/l 0 10 ug/l 1 11000 ug/l 0 0 ug/l 1 62 ug/l 0 5 ug/l 0 10 ug/l 0 1 ug/l 0 3 ug/l 1 65 ug/l 0 0.01 ug/l 0 0.02 ug/l 1 76 ug/l 0 1 ug/l 0 0.5 ug/l 0 10 ug/l 0 0.38 ug/l 0 0.25 ug/l 0 10 ug/l 0 1 ug/l 0 1 ug/l 0 1 ug/l 0 0.9 ug/l 1 69 ug/l 0 2 ug/l 0 1 ug/l 0 1 ug/l 0 0.000005 ug/l 0 1 ug/l 0 10 ug/l 0 3 ug/l 0 1 ug/l 0 3 ug/l 0 4 ug/l 0 3 ug/l Page 29 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 12‐Jul‐05 CHEMICAL_( ALDRIN ALUMINUM ANTIMONY ARSENIC ATRAZINE BARIUM BENTAZON BENZO (A) PYRENE BERYLLIUM BROMACIL BUTACHLOR CADMIUM CARBARYL CARBOFURAN CHLORDANE CHLOROTHALONIL CHROMIUM (TOTAL) COPPER CYANIDE DALAPON DI(2‐ETHYLHEXYL)ADIPATE DI(2‐ETHYLHEXYL)PHTHALATE DIAZINON DIBROMOCHLOROPROPANE (DBCP) DICAMBA DIELDRIN DIMETHOATE DINOSEB DIQUAT DIURON ENDOTHALL ENDRIN ETHYLENE DIBROMIDE (EDB) FLUORIDE (F) (NATURAL‐SOURCE) GLYPHOSATE HEPTACHLOR HEPTACHLOR EPOXIDE HEXACHLOROBENZENE HEXACHLOROCYCLOPENTADIENE IRON LEAD LINDANE MANGANESE MERCURY METHOMYL METHOXYCHLOR METOLACHLOR Det_Flag ug/l_Result Units 0 0.075 ug/l 0 50 ug/l 0 6 ug/l 0 2 ug/l 0 0.5 ug/l 0 100 ug/l 0 2 ug/l 0 0.1 ug/l 0 1 ug/l 0 10 ug/l 0 0.38 ug/l 0 1 ug/l 0 5 ug/l 0 5 ug/l 0 0.1 ug/l 0 5 ug/l 1 1.3 ug/l 0 50 ug/l 0 100 ug/l 0 10 ug/l 0 5 ug/l 0 3 ug/l 0 0.25 ug/l 0 0.01 ug/l 0 1.5 ug/l 0 0.02 ug/l 0 10 ug/l 0 2 ug/l 0 4 ug/l 0 1 ug/l 0 45 ug/l 0 0.1 ug/l 0 0.02 ug/l 1 300 ug/l 0 20 ug/l 0 0.01 ug/l 0 0.01 ug/l 0 0.5 ug/l 0 1 ug/l 0 100 ug/l 0 5 ug/l 0 0.2 ug/l 0 20 ug/l 0 1 ug/l 0 2 ug/l 0 10 ug/l 0 1 ug/l Page 30 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE CHEMICAL_( 12‐Jul‐05 METRIBUZIN 12‐Jul‐05 MOLINATE 12‐Jul‐05 NICKEL 12‐Jul‐05 NITRATE (AS NO3) 12‐Jul‐05 NITRITE (AS N) 12‐Jul‐05 OXAMYL 12‐Jul‐05 PENTACHLOROPHENOL 12‐Jul‐05 PICLORAM 12‐Jul‐05 POLYCHLORINATED BIPHENYLS, TOTAL, AS DCB 12‐Jul‐05 PROMETRYN 12‐Jul‐05 PROPACHLOR 12‐Jul‐05 SELENIUM 12‐Jul‐05 SILVER 12‐Jul‐05 SIMAZINE 12‐Jul‐05 THALLIUM 12‐Jul‐05 THIOBENCARB 12‐Jul‐05 TOXAPHENE 12‐Jul‐05 ZINC 20‐Jul‐05 PERCHLORATE 02‐Aug‐05 PERCHLORATE 22‐Sep‐05 PERCHLORATE 19‐Oct‐05 METHYL‐TERT‐BUTYL‐ETHER (MTBE) 19‐Oct‐05 PERCHLORATE 23‐Nov‐05 PERCHLORATE 15‐Dec‐05 PERCHLORATE 19‐Jan‐06 PERCHLORATE 21‐Feb‐06 1,1,1,2‐TETRACHLORETHANE 21‐Feb‐06 1,1,1‐TRICHLOROETHANE 21‐Feb‐06 1,1,2,2‐TETRACHLOROETHANE 21‐Feb‐06 1,1,2‐TRICHLORO‐1,2,2‐TRIFLUOROETHANE 21‐Feb‐06 1,1,2‐TRICHLOROETHANE 21‐Feb‐06 1,1‐DICHLOROETHANE 21‐Feb‐06 1,1‐DICHLOROETHYLENE 21‐Feb‐06 1,1‐DICHLOROPROPENE 21‐Feb‐06 1,2,3‐TRICHLOROBENZENE 21‐Feb‐06 1,2,3‐TRICHLOROPROPANE 21‐Feb‐06 1,2,4‐TRICHLOROBENZENE 21‐Feb‐06 1,2,4‐TRIMETHYLBENZENE 21‐Feb‐06 1,2‐DICHLOROBENZENE 21‐Feb‐06 1,2‐DICHLOROETHANE 21‐Feb‐06 1,2‐DICHLOROPROPANE 21‐Feb‐06 1,3,5‐TRIMETHYLBENZENE 21‐Feb‐06 1,3‐DICHLOROBENZENE 21‐Feb‐06 1,3‐DICHLOROPROPANE 21‐Feb‐06 1,3‐DICHLOROPROPENE (TOTAL) 21‐Feb‐06 1,4‐DICHLOROBENZENE 21‐Feb‐06 1‐PHENYLPROPANE (N‐PROPYLBENZENE) Det_Flag ug/l_Result Units 0 1 ug/l 0 0.9 ug/l 0 10 ug/l 1 12000 ug/l 0 100 ug/l 0 5 ug/l 0 0.2 ug/l 0 1 ug/l 0 0.5 ug/l 0 2 ug/l 0 0.5 ug/l 0 5 ug/l 0 10 ug/l 0 1 ug/l 0 1 ug/l 0 1 ug/l 0 1 ug/l 0 50 ug/l 1 73 ug/l 1 80 ug/l 1 82 ug/l 0 3 ug/l 1 88 ug/l 1 94 ug/l 1 92 ug/l 1 86 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 10 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.005 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l Page 31 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 21‐Feb‐06 CHEMICAL_( 2,2‐DICHLOROPROPANE 2‐CHLOROTOLUENE 4‐CHLOROTOLUENE BENZENE BIS (2‐CHLOROETHYL) ETHER BORON BROMOBENZENE BROMOCHLOROMETHANE BROMODICHLORMETHANE (THM) BROMOFORM (THM) BROMOMETHANE CARBON TETRACHLORIDE CHLOROETHANE CHLOROFORM (THM) CHLOROMETHANE CHROMIUM, HEXAVALENT CIS‐1,2‐DICHLOROETHYLENE DIBROMOCHLOROMETHANE (THM) DIBROMOMETHANE DICHLORODIFLUOROMETHANE (FREON 12) DICHLOROMETHANE DIISOPROPYL ETHER ETHYLBENZENE ETHYL‐TERT‐BUTYL ETHER HEXACHLOROBUTADIENE ISOPROPYLBENZENE M,P‐XYLENE METHYL ETHYL KETONE METHYL ISOBUTYL KETONE METHYL‐TERT‐BUTYL‐ETHER (MTBE) MONOCHLOROBENZENE NAPHTHALENE N‐BUTYLBENZENE O‐XYLENE PERCHLORATE P‐ISOPROPYLTOLUENE SEC‐BUTYLBENZENE STYRENE TERT‐AMYL‐METHYL ETHER TERT‐BUTYL ALCOHOL TERT‐BUTYLBENZENE TETRACHLOROETHYLENE TOLUENE TRANS‐1,2‐DICHLOROETHYLENE TRICHLOROETHYLENE TRICHLOROFLUOROMETHANE VANADIUM Det_Flag ug/l_Result Units 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 100 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 1 1.4 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 3 ug/l 0 0.5 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 5 ug/l 0 5 ug/l 0 3 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 1 89 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 3 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 1 2.5 ug/l 0 5 ug/l 1 4.8 ug/l Page 32 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE CHEMICAL_( 21‐Feb‐06 VINYL CHLORIDE 21‐Feb‐06 XYLENES (TOTAL) 22‐Mar‐06 NITRATE (AS NO3) 22‐Mar‐06 PERCHLORATE 11‐Apr‐06 PERCHLORATE 12‐Sep‐06 PERCHLORATE 23‐Oct‐06 PERCHLORATE 16‐Nov‐06 PERCHLORATE 12‐Dec‐06 PERCHLORATE 03‐Jan‐07 PERCHLORATE 15‐Feb‐07 PERCHLORATE 05‐Apr‐07 PERCHLORATE 02‐May‐07 PERCHLORATE 12‐Jun‐07 PERCHLORATE 17‐Jul‐07 PERCHLORATE 07‐Aug‐07 PERCHLORATE 11‐Sep‐07 PERCHLORATE 24‐Oct‐07 PERCHLORATE 06‐Nov‐07 PERCHLORATE 04‐Dec‐07 PERCHLORATE 09‐Jan‐08 PERCHLORATE 21‐Feb‐08 1,2,3‐TRICHLOROPROPANE 21‐Feb‐08 BORON 21‐Feb‐08 CHROMIUM, HEXAVALENT 21‐Feb‐08 COPPER 21‐Feb‐08 DICHLORODIFLUOROMETHANE (FREON 12) 21‐Feb‐08 ETHYL‐TERT‐BUTYL ETHER 21‐Feb‐08 FLUORIDE (F) (NATURAL‐SOURCE) 21‐Feb‐08 IRON 21‐Feb‐08 MANGANESE 21‐Feb‐08 NITRATE (AS NO3) 21‐Feb‐08 PERCHLORATE 21‐Feb‐08 TERT‐AMYL‐METHYL ETHER 21‐Feb‐08 TERT‐BUTYL ALCOHOL 21‐Feb‐08 VANADIUM 21‐Feb‐08 ZINC 11‐Mar‐08 PERCHLORATE 09‐Apr‐08 METHYL‐TERT‐BUTYL‐ETHER (MTBE) 09‐Apr‐08 PERCHLORATE 13‐May‐08 PERCHLORATE 17‐Jun‐08 PERCHLORATE 12‐Aug‐08 PERCHLORATE 12‐Aug‐08 TRICHLOROETHYLENE 28‐Oct‐08 METHYL‐TERT‐BUTYL‐ETHER (MTBE) 28‐Oct‐08 PERCHLORATE 12‐Nov‐08 PERCHLORATE 12‐Nov‐08 TRICHLOROETHYLENE Det_Flag ug/l_Result Units 0 0.5 ug/l 0 0.5 ug/l 1 12000 ug/l 1 110 ug/l 1 94 ug/l 1 130 ug/l 1 130 ug/l 1 130 ug/l 1 140 ug/l 1 140 ug/l 1 150 ug/l 1 180 ug/l 1 170 ug/l 1 180 ug/l 1 180 ug/l 1 190 ug/l 1 180 ug/l 1 230 ug/l 1 210 ug/l 1 180 ug/l 1 270 ug/l 0 0.005 ug/l 0 100 ug/l 0 1 ug/l 0 50 ug/l 0 0.5 ug/l 0 3 ug/l 1 340 ug/l 0 100 ug/l 0 20 ug/l 1 12000 ug/l 1 190 ug/l 0 3 ug/l 0 2 ug/l 1 5.7 ug/l 0 50 ug/l 1 190 ug/l 0 3 ug/l 1 210 ug/l 1 210 ug/l 1 300 ug/l 1 230 ug/l 1 4 ug/l 0 3 ug/l 1 280 ug/l 1 320 ug/l 1 5.3 ug/l Page 33 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE 23‐Dec‐08 06‐Jan‐09 18‐Feb‐09 11‐Mar‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 CHEMICAL_( PERCHLORATE PERCHLORATE PERCHLORATE PERCHLORATE 1,1,1‐TRICHLOROETHANE 1,1,2,2‐TETRACHLOROETHANE 1,1,2‐TRICHLORO‐1,2,2‐TRIFLUOROETHANE 1,1,2‐TRICHLOROETHANE 1,1‐DICHLOROETHANE 1,1‐DICHLOROETHYLENE 1,2,3‐TRICHLOROPROPANE 1,2,4‐TRICHLOROBENZENE 1,2‐DICHLOROBENZENE 1,2‐DICHLOROETHANE 1,2‐DICHLOROPROPANE 1,3‐DICHLOROPROPENE (TOTAL) 1,4‐DICHLOROBENZENE 2,3,7,8‐TCDD (DIOXIN) 2,4,5‐TP (SILVEX) 2,4‐D ALACHLOR ALUMINUM ANTIMONY ARSENIC ATRAZINE BARIUM BENTAZON BENZENE BENZO (A) PYRENE BERYLLIUM BORON BROMODICHLORMETHANE (THM) BROMOFORM (THM) CADMIUM CARBOFURAN CARBON TETRACHLORIDE CHLORDANE CHLOROFORM (THM) CHROMIUM (TOTAL) CHROMIUM, HEXAVALENT CIS‐1,2‐DICHLOROETHYLENE COPPER CYANIDE DALAPON DI(2‐ETHYLHEXYL)ADIPATE DI(2‐ETHYLHEXYL)PHTHALATE DIBROMOCHLOROMETHANE (THM) Det_Flag ug/l_Result Units 1 200 ug/l 1 210 ug/l 1 210 ug/l 1 280 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 10 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.005 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.5 ug/l 0 0.000005 ug/l 0 1 ug/l 0 10 ug/l 0 1 ug/l 0 50 ug/l 0 6 ug/l 0 2 ug/l 0 0.5 ug/l 0 100 ug/l 0 2 ug/l 0 0.5 ug/l 0 0.1 ug/l 0 1 ug/l 0 100 ug/l 0 1 ug/l 0 1 ug/l 0 1 ug/l 0 5 ug/l 0 0.5 ug/l 0 0.1 ug/l 0 1 ug/l 0 10 ug/l 1 1.7 ug/l 0 0.5 ug/l 0 50 ug/l 0 100 ug/l 0 10 ug/l 0 5 ug/l 0 3 ug/l 0 1 ug/l Page 34 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 08‐Apr‐09 CHEMICAL_( DIBROMOCHLOROPROPANE (DBCP) DICHLORODIFLUOROMETHANE (FREON 12) DICHLOROMETHANE DINOSEB DIQUAT ENDOTHALL ENDRIN ETHYLBENZENE ETHYLENE DIBROMIDE (EDB) ETHYL‐TERT‐BUTYL ETHER FLUORIDE (F) (NATURAL‐SOURCE) GLYPHOSATE HEPTACHLOR HEPTACHLOR EPOXIDE HEXACHLOROBENZENE HEXACHLOROCYCLOPENTADIENE IRON LEAD LINDANE M,P‐XYLENE MANGANESE MERCURY METHOXYCHLOR METHYL‐TERT‐BUTYL‐ETHER (MTBE) MOLINATE MONOCHLOROBENZENE NICKEL NITRATE (AS NO3) NITRATE + NITRITE (AS N) NITRITE (AS N) OXAMYL O‐XYLENE PENTACHLOROPHENOL PERCHLORATE PICLORAM POLYCHLORINATED BIPHENYLS, TOTAL, AS DCB SELENIUM SILVER SIMAZINE STYRENE TERT‐AMYL‐METHYL ETHER TERT‐BUTYL ALCOHOL TETRACHLOROETHYLENE THALLIUM THIOBENCARB TOLUENE TOXAPHENE Det_Flag ug/l_Result Units 0 0.01 ug/l 0 0.5 ug/l 1 1.1 ug/l 0 2 ug/l 0 4 ug/l 0 45 ug/l 0 0.1 ug/l 0 0.5 ug/l 0 0.02 ug/l 0 3 ug/l 1 300 ug/l 0 25 ug/l 0 0.01 ug/l 0 0.01 ug/l 0 0.5 ug/l 0 1 ug/l 0 100 ug/l 0 5 ug/l 0 0.2 ug/l 0 0.5 ug/l 0 20 ug/l 0 1 ug/l 0 10 ug/l 0 3 ug/l 0 2 ug/l 0 0.5 ug/l 0 10 ug/l 1 13000 ug/l 1 3000 ug/l 0 0 ug/l 0 20 ug/l 0 0.5 ug/l 0 0.2 ug/l 1 220 ug/l 0 1 ug/l 0 0.5 ug/l 0 5 ug/l 0 10 ug/l 0 1 ug/l 0 0.5 ug/l 0 3 ug/l 0 2 ug/l 0 0.5 ug/l 0 1 ug/l 0 1 ug/l 0 0.5 ug/l 0 1 ug/l Page 35 PRIM_STA_C 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 3610038‐010 SYSTEM_NO 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 3610038 SYSTEM_NAM RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY RIALTO‐CITY SOURCE_NAM ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE ETIWANDA WELL (RIALTO 06) ‐ INACTIVE SAMP_DATE CHEMICAL_( 08‐Apr‐09 TRANS‐1,2‐DICHLOROETHYLENE 08‐Apr‐09 TRICHLOROETHYLENE 08‐Apr‐09 TRICHLOROFLUOROMETHANE 08‐Apr‐09 VANADIUM 08‐Apr‐09 VINYL CHLORIDE 08‐Apr‐09 XYLENES (TOTAL) 08‐Apr‐09 ZINC 06‐May‐09 PERCHLORATE 09‐Jun‐09 PERCHLORATE 13‐Jul‐09 PERCHLORATE 19‐Aug‐09 PERCHLORATE 15‐Sep‐09 PERCHLORATE 15‐Oct‐09 PERCHLORATE 10‐Nov‐09 PERCHLORATE 06‐Jan‐10 PERCHLORATE 18‐Feb‐10 PERCHLORATE 24‐Mar‐10 PERCHLORATE 27‐Apr‐10 PERCHLORATE 25‐May‐10 PERCHLORATE 22‐Jun‐10 PERCHLORATE 28‐Jul‐10 PERCHLORATE 18‐Aug‐10 PERCHLORATE Det_Flag ug/l_Result Units 0 0.5 ug/l 1 6.3 ug/l 0 5 ug/l 0 3 ug/l 0 0.5 ug/l 0 0 ug/l 0 50 ug/l 1 210 ug/l 1 250 ug/l 1 200 ug/l 1 310 ug/l 1 300 ug/l 1 230 ug/l 1 200 ug/l 1 220 ug/l 1 250 ug/l 1 210 ug/l 1 230 ug/l 1 230 ug/l 1 260 ug/l 1 280 ug/l 1 33 ug/l Page 36 Appendix B Results of Trend Analyses for Chemicals of Potential Concern Appendix B: B.1 Results of Trend Analyses for Chemicals of Potential Concern Hexavalent Chromium, Rialto Well 6 Time-series plot of all hexavalent chromium data from Rialto Well 6 that are part of the human health risk assessment database: ChemStat software output of Mann-Kendall upward trend analysis for the same dataset: Mann-Kendall Trend Analysis Parameter: Chromium, Hexavalent Location: Rialto-o6 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 1 Original Data (Not Transformed) Non-Detects Replaced with Detection Limit 95% Confidence Level ============================================ Xj Xk Xj - Xk Positives 1.2 1.4 -0.2 0 1 1.5 1.4 0.1 1 1 1.4 1.4 0 1 1 ND<1 1.4 -0.4 1 2 1.7 1.4 0.3 2 2 1.5 1.2 0.3 3 2 1.4 1.2 0.2 4 2 ND<1 1.2 -0.2 4 3 1.7 1.2 0.5 5 3 1.4 1.5 -0.1 5 4 ND<1 1.5 -0.5 5 5 1.7 0.2 6 5 ND<1 1.4 -0.4 6 6 1.7 1.4 0.3 7 6 1.7 ND<1 0.7 8 6 1.5 Negatives Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 2 S Statistic = 8 - 6 = 2 Comparing at 95% confidence level (upward trend) Probability of obtaining S >= 2 is 0.43 S < 0 or 0.43 >= 0.05 indicating no evidence of an upward trend ChemStat software output of Mann-Kendall downward trend analysis for the same dataset: Mann-Kendall Trend Analysis Parameter: Chromium, Hexavalent Location: Rialto-o6 Original Data (Not Transformed) Non-Detects Replaced with Detection Limit 95% Confidence Level ============================================ Xj Xk Xj - Xk Positives 1.2 1.4 -0.2 0 1 1.5 1.4 0.1 1 1 1.4 1.4 0 1 1 ND<1 1.4 -0.4 1 2 1.7 1.4 0.3 2 2 1.5 1.2 0.3 3 2 Negatives Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 3 1.4 1.2 0.2 4 2 ND<1 1.2 -0.2 4 3 1.7 1.2 0.5 5 3 1.4 1.5 -0.1 5 4 ND<1 1.5 -0.5 5 5 1.7 0.2 6 5 ND<1 1.4 -0.4 6 6 1.7 1.4 0.3 7 6 1.7 ND<1 0.7 8 6 1.5 S Statistic = 8 - 6 = 2 Comparing at 95% confidence level (downward trend) Probability of obtaining S >= 2 is 0.43 S > 0 or 0.43 > 0.05 indicating no evidence of a downward trend Summary: No significant trending was observed in the dataset; all results from the HHRA database for this well and analyte were used in the determination of the exposure point concentration. Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 4 B.2 Nitrate-Nitrogen, Rialto Well 6 Time-series plot of all nitrate-nitrogen data from Rialto Well 6 that are part of the human health risk assessment database: ChemStat software output of Mann-Kendall upward trend analysis for the same dataset: Mann-Kendall Trend Analysis Parameter: NO3-N Location: RIALTO-CITY Original Data (Not Transformed) Non-Detects Replaced with Detection Limit Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 5 95% Confidence Level ============================================ Xj Xk Xj - Xk Positives Negatives 2045.5 2086.4 -40.9 0 1 1590.9 2086.4 -495.5 0 2 1818.2 2086.4 -268.2 0 3 1818.2 2086.4 -268.2 0 4 2500 2086.4 413.6 1 4 2272.7 2086.4 186.3 2 4 2500 2086.4 413.6 3 4 2272.7 2086.4 186.3 4 4 2500 2086.4 413.6 5 4 2727.3 2086.4 640.9 6 4 2727.3 2086.4 640.9 7 4 2727.3 2086.4 640.9 8 4 2954.5 2086.4 868.1 9 4 1590.9 2045.5 -454.6 9 5 1818.2 2045.5 -227.3 9 6 1818.2 2045.5 -227.3 9 7 2500 2045.5 454.5 10 7 2272.7 2045.5 227.2 11 7 2500 2045.5 454.5 12 7 2272.7 2045.5 227.2 13 7 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 6 2500 2045.5 454.5 14 7 2727.3 2045.5 681.8 15 7 2727.3 2045.5 681.8 16 7 2727.3 2045.5 681.8 17 7 2954.5 2045.5 909 18 7 1818.2 1590.9 227.3 19 7 1818.2 1590.9 227.3 20 7 2500 1590.9 909.1 21 7 2272.7 1590.9 681.8 22 7 2500 1590.9 909.1 23 7 2272.7 1590.9 681.8 24 7 2500 1590.9 909.1 25 7 2727.3 1590.9 1136.4 26 7 2727.3 1590.9 1136.4 27 7 2727.3 1590.9 1136.4 28 7 2954.5 1590.9 1363.6 29 7 1818.2 1818.2 0 29 7 2500 1818.2 681.8 30 7 2272.7 1818.2 454.5 31 7 2500 1818.2 681.8 32 7 2272.7 1818.2 454.5 33 7 2500 1818.2 681.8 34 7 2727.3 1818.2 909.1 35 7 2727.3 1818.2 909.1 36 7 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 7 2727.3 1818.2 909.1 37 7 2954.5 1818.2 1136.3 38 7 2500 1818.2 681.8 39 7 2272.7 1818.2 454.5 40 7 2500 1818.2 681.8 41 7 2272.7 1818.2 454.5 42 7 2500 1818.2 681.8 43 7 2727.3 1818.2 909.1 44 7 2727.3 1818.2 909.1 45 7 2727.3 1818.2 909.1 46 7 2954.5 1818.2 1136.3 47 7 2272.7 2500 -227.3 47 8 2500 2500 0 47 8 2272.7 2500 -227.3 47 9 2500 2500 0 47 9 2727.3 2500 227.3 48 9 2727.3 2500 227.3 49 9 2727.3 2500 227.3 50 9 2954.5 2500 454.5 51 9 2500 2272.7 227.3 52 9 2272.7 2272.7 0 52 9 2500 2272.7 227.3 53 9 2727.3 2272.7 454.6 54 9 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 8 2727.3 2272.7 454.6 55 9 2727.3 2272.7 454.6 56 9 2954.5 2272.7 681.8 57 9 2272.7 2500 -227.3 57 10 2500 2500 0 57 10 2727.3 2500 227.3 58 10 2727.3 2500 227.3 59 10 2727.3 2500 227.3 60 10 2954.5 2500 454.5 61 10 2500 2272.7 227.3 62 10 2727.3 2272.7 454.6 63 10 2727.3 2272.7 454.6 64 10 2727.3 2272.7 454.6 65 10 2954.5 2272.7 681.8 66 10 2727.3 2500 227.3 67 10 2727.3 2500 227.3 68 10 2727.3 2500 227.3 69 10 2954.5 2500 454.5 70 10 2727.3 2727.3 0 70 10 2727.3 2727.3 0 70 10 2954.5 2727.3 227.2 71 10 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 9 2727.3 2727.3 0 71 10 2954.5 2727.3 227.2 72 10 2954.5 2727.3 227.2 73 10 S Statistic = 73 - 10 = 63 ============================================ Tied Group Value Members 1 1818.2 2 2 2500 3 2272.7 2 4 2727.3 3 3 ============================================ Time Period Observations 2/3/1999 1 3/3/1999 1 6/23/1999 1 8/4/1999 1 2/1/2000 1 2/21/2001 1 2/21/2002 1 3/12/2002 1 3/12/2003 1 3/22/2005 1 7/12/2005 1 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 10 3/22/2006 1 2/21/2008 1 4/8/2009 1 There are 0 time periods with multiple data ============================================ A = 168 B=0 C = 12 D=0 E = 16 F=0 a = 6006 b = 19656 c = 364 Group Variance = 324.333 Z-Score = 3.44267 Comparison Level at 95% confidence level = 1.65463 (upward trend) 3.44267 > 1.65463 indicating an upward trend ChemStat software output of Mann-Kendall upward trend analysis for most recent data indicating no trend for the same well and analyte: Mann-Kendall Trend Analysis Parameter: NO3-N Location: RIALTO-CITY Original Data (Not Transformed) Non-Detects Replaced with Detection Limit Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 11 95% Confidence Level ============================================ Xj Xk Xj - Xk Positives Negatives 2727.3 2500 227.3 1 0 2727.3 2500 227.3 2 0 2727.3 2500 227.3 3 0 2954.5 2500 454.5 4 0 2727.3 2727.3 0 4 0 2727.3 2727.3 0 4 0 2954.5 2727.3 227.2 5 0 2727.3 2727.3 0 5 0 2954.5 2727.3 227.2 6 0 2954.5 2727.3 227.2 7 0 S Statistic = 7 - 0 = 7 Comparing at 95% confidence level (upward trend) Probability of obtaining S >= 7 is 0.0795 S < 0 or 0.0795 >= 0.05 indicating no evidence of an upward trend Summary: An upward trend was observed in the nitrate-nitrogen data for Rialto Well 6. Thus, only the most recent results were used in the HHRA to determine the exposure point concentration, in order to not include results from years in which the nitrate-nitrogen concentration in this well was increasing, and to better represent current and future well concentrations for this analyte. Based on the trend analysis results, the range of sample dates used in the HHRA for this analyte and well were from 22 March 2005 to October 2010, which includes five sample results. Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 12 B.3 Nitrate-Nitrogen, District Well 11 Time-series plot of all nitrate-nitrogen data from District Well 11 that are part of the human health risk assessment database: ChemStat software output of Mann-Kendall downward trend analysis for the same dataset: Mann-Kendall Trend Analysis Parameter: NO3-N Location: WEST VALLEY WATER DISTRICT Original Data (Not Transformed) Non-Detects Replaced with Detection Limit 95% Confidence Level ============================================ Xj Xk Xj - Xk Positives Negatives Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 13 11068.2 12340.9 11818.2 11136.4 11136.4 12045.5 9545.5 10227.3 10909.1 9545.5 10909.1 7272.7 7727.3 6590.9 7400 9090.9 7954.5 7700 8863.6 9090.9 6136.4 9772.7 9700 9772.7 9700 9772.7 9200 8409.1 7727.3 8636.4 8863.6 9318.2 9200 8636.4 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 11863.6 -795.4 477.3 -45.4 -727.2 -727.2 181.9 -2318.1 -1636.3 -954.5 -2318.1 -954.5 -4590.9 -4136.3 -5272.7 -4463.6 -2772.7 -3909.1 -4163.6 -3000 -2772.7 -5727.2 -2090.9 -2163.6 -2090.9 -2163.6 -2090.9 -2663.6 -3454.5 -4136.3 -3227.2 -3000 -2545.4 -2663.6 -3227.2 -3000 -3909.1 -3227.2 -5727.2 -3909.1 -3454.5 -6409.1 -6409.1 0 1 1 1 1 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 1 1 2 3 4 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 12340.9 11818.2 11136.4 11136.4 12045.5 9545.5 10227.3 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 1272.7 750 68.2 68.2 977.3 -1522.7 -840.9 3 4 5 6 7 7 7 40 40 40 40 40 41 42 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 14 10909.1 9545.5 10909.1 7272.7 7727.3 6590.9 7400 9090.9 7954.5 7700 8863.6 9090.9 6136.4 9772.7 9700 9772.7 9700 9772.7 9200 8409.1 7727.3 8636.4 8863.6 9318.2 9200 8636.4 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 11068.2 -159.1 -1522.7 -159.1 -3795.5 -3340.9 -4477.3 -3668.2 -1977.3 -3113.7 -3368.2 -2204.6 -1977.3 -4931.8 -1295.5 -1368.2 -1295.5 -1368.2 -1295.5 -1868.2 -2659.1 -3340.9 -2431.8 -2204.6 -1750 -1868.2 -2431.8 -2204.6 -3113.7 -2431.8 -4931.8 -3113.7 -2659.1 -5613.7 -5613.7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60 61 62 63 64 65 66 67 68 69 70 71 72 73 74 75 76 11818.2 11136.4 11136.4 12045.5 9545.5 10227.3 10909.1 9545.5 10909.1 7272.7 7727.3 6590.9 7400 9090.9 7954.5 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 -522.7 -1204.5 -1204.5 -295.4 -2795.4 -2113.6 -1431.8 -2795.4 -1431.8 -5068.2 -4613.6 -5750 -4940.9 -3250 -4386.4 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 77 78 79 80 81 82 83 84 85 86 87 88 89 90 91 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 15 7700 8863.6 9090.9 6136.4 9772.7 9700 9772.7 9700 9772.7 9200 8409.1 7727.3 8636.4 8863.6 9318.2 9200 8636.4 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 12340.9 -4640.9 -3477.3 -3250 -6204.5 -2568.2 -2640.9 -2568.2 -2640.9 -2568.2 -3140.9 -3931.8 -4613.6 -3704.5 -3477.3 -3022.7 -3140.9 -3704.5 -3477.3 -4386.4 -3704.5 -6204.5 -4386.4 -3931.8 -6886.4 -6886.4 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 92 93 94 95 96 97 98 99 100 101 102 103 104 105 106 107 108 109 110 111 112 113 114 115 116 11136.4 11136.4 12045.5 9545.5 10227.3 10909.1 9545.5 10909.1 7272.7 7727.3 6590.9 7400 9090.9 7954.5 7700 8863.6 9090.9 6136.4 9772.7 9700 9772.7 9700 9772.7 9200 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 -681.8 -681.8 227.3 -2272.7 -1590.9 -909.1 -2272.7 -909.1 -4545.5 -4090.9 -5227.3 -4418.2 -2727.3 -3863.7 -4118.2 -2954.6 -2727.3 -5681.8 -2045.5 -2118.2 -2045.5 -2118.2 -2045.5 -2618.2 7 7 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 117 118 118 119 120 121 122 123 124 125 126 127 128 129 130 131 132 133 134 135 136 137 138 139 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 16 8409.1 7727.3 8636.4 8863.6 9318.2 9200 8636.4 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 11818.2 -3409.1 -4090.9 -3181.8 -2954.6 -2500 -2618.2 -3181.8 -2954.6 -3863.7 -3181.8 -5681.8 -3863.7 -3409.1 -6363.7 -6363.7 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 140 141 142 143 144 145 146 147 148 149 150 151 152 153 154 11136.4 12045.5 9545.5 10227.3 10909.1 9545.5 10909.1 7272.7 7727.3 6590.9 7400 9090.9 7954.5 7700 8863.6 9090.9 6136.4 9772.7 9700 9772.7 9700 9772.7 9200 8409.1 7727.3 8636.4 8863.6 9318.2 9200 8636.4 8863.6 7954.5 8636.4 6136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 0 909.1 -1590.9 -909.1 -227.3 -1590.9 -227.3 -3863.7 -3409.1 -4545.5 -3736.4 -2045.5 -3181.9 -3436.4 -2272.8 -2045.5 -5000 -1363.7 -1436.4 -1363.7 -1436.4 -1363.7 -1936.4 -2727.3 -3409.1 -2500 -2272.8 -1818.2 -1936.4 -2500 -2272.8 -3181.9 -2500 -5000 8 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 154 154 155 156 157 158 159 160 161 162 163 164 165 166 167 168 169 170 171 172 173 174 175 176 177 178 179 180 181 182 183 184 185 186 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 17 7954.5 8409.1 5454.5 5454.5 11136.4 11136.4 11136.4 11136.4 -3181.9 -2727.3 -5681.9 -5681.9 9 9 9 9 187 188 189 190 12045.5 9545.5 10227.3 10909.1 9545.5 10909.1 7272.7 7727.3 6590.9 7400 9090.9 7954.5 7700 8863.6 9090.9 6136.4 9772.7 9700 9772.7 9700 9772.7 9200 8409.1 7727.3 8636.4 8863.6 9318.2 9200 8636.4 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 11136.4 909.1 -1590.9 -909.1 -227.3 1 -1590.9 -227.3 -3863.7 -3409.1 -4545.5 -3736.4 -2045.5 -3181.9 -3436.4 -2272.8 -2045.5 -5000 -1363.7 -1436.4 -1363.7 -1436.4 -1363.7 -1936.4 -2727.3 -3409.1 -2500 -2272.8 -1818.2 -1936.4 -2500 -2272.8 -3181.9 -2500 -5000 -3181.9 -2727.3 -5681.9 -5681.9 10 10 10 0 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 190 191 192 193 194 195 196 197 198 199 200 201 202 203 204 205 206 207 208 209 210 211 212 213 214 215 216 217 218 219 220 221 222 223 224 225 226 9545.5 10227.3 10909.1 9545.5 10909.1 7272.7 7727.3 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 -2500 -1818.2 -1136.4 -2500 -1136.4 -4772.8 -4318.2 10 10 10 10 10 10 10 227 228 229 230 231 232 233 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 18 6590.9 7400 9090.9 7954.5 7700 8863.6 9090.9 6136.4 9772.7 9700 9772.7 9700 9772.7 9200 8409.1 7727.3 8636.4 8863.6 9318.2 9200 8636.4 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 12045.5 -5454.6 -4645.5 -2954.6 -4091 -4345.5 -3181.9 -2954.6 -5909.1 -2272.8 -2345.5 -2272.8 -2345.5 -2272.8 -2845.5 -3636.4 -4318.2 -3409.1 -3181.9 -2727.3 -2845.5 -3409.1 -3181.9 -4091 -3409.1 -5909.1 -4091 -3636.4 -6591 -6591 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 234 235 236 237 238 239 240 241 242 243 244 245 246 247 248 249 250 251 252 253 254 255 256 257 258 259 260 261 262 10227.3 10909.1 9545.5 10909.1 7272.7 7727.3 6590.9 7400 9090.9 7954.5 7700 8863.6 9090.9 6136.4 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-72.7 0 -572.7 -1363.6 -2045.4 -1136.3 -909.1 -454.5 -572.7 -1136.3 -909.1 -1818.2 -1136.3 -3636.3 -1818.2 -1363.6 -4318.2 -4318.2 1994 199 199 199 199 199 199 199 199 199 199 199 199 199 199 199 199 199 199 199 84 484 485 485 486 487 488 489 490 491 492 493 494 495 496 497 498 499 500 501 9772.7 9700 9772.7 9200 8409.1 7727.3 8636.4 8863.6 9318.2 9200 8636.4 8863.6 7954.5 8636.4 6136.4 9700 9700 9700 9700 9700 9700 9700 9700 9700 9700 9700 9700 9700 9700 9700 72.7 0 72.7 -500 -1290.9 -1972.7 -1063.6 -836.4 -381.8 -500 -1063.6 -836.4 -1745.5 -1063.6 -3563.6 200 200 201 201 201 201 201 201 201 201 201 201 201 201 201 501 501 501 502 503 504 505 506 507 508 509 510 511 512 513 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 28 7954.5 8409.1 5454.5 5454.5 9700 9700 9700 9700 -1745.5 -1290.9 -4245.5 -4245.5 201 201 201 201 514 515 516 517 9700 9772.7 9200 8409.1 7727.3 8636.4 8863.6 9318.2 9200 8636.4 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 Same Date 0 -572.7 -1363.6 -2045.4 -1136.3 -909.1 -454.5 -572.7 -1136.3 -909.1 -1818.2 -1136.3 -3636.3 -1818.2 -1363.6 -4318.2 -4318.2 201 201 201 201 201 201 201 201 201 201 201 201 201 201 201 201 201 201 517 517 518 519 520 521 522 523 524 525 526 527 528 529 530 531 532 533 9772.7 9200 8409.1 7727.3 8636.4 8863.6 9318.2 9200 8636.4 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 9700 9700 9700 9700 9700 9700 9700 9700 9700 9700 9700 9700 9700 9700 9700 9700 9700 72.7 -500 -1290.9 -1972.7 -1063.6 -836.4 -381.8 -500 -1063.6 -836.4 -1745.5 -1063.6 -3563.6 -1745.5 -1290.9 -4245.5 -4245.5 202 202 202 202 202 202 202 202 202 202 202 202 202 202 202 202 202 533 534 535 536 537 538 539 540 541 542 543 544 545 546 547 548 549 9200 8409.1 7727.3 8636.4 8863.6 9318.2 9200 8636.4 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 -572.7 -1363.6 -2045.4 -1136.3 -909.1 -454.5 -572.7 -1136.3 202 202 202 202 202 202 202 202 550 551 552 553 554 555 556 557 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 29 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 9772.7 -909.1 -1818.2 -1136.3 -3636.3 -1818.2 -1363.6 -4318.2 -4318.2 202 202 202 202 202 202 202 202 558 559 560 561 562 563 564 565 8409.1 7727.3 8636.4 8863.6 9318.2 9200 8636.4 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 9200 9200 9200 9200 9200 9200 9200 9200 9200 9200 9200 9200 9200 9200 9200 -790.9 -1472.7 -563.6 -336.4 118.2 0 -563.6 -336.4 -1245.5 -563.6 -3063.6 -1245.5 -790.9 -3745.5 -3745.5 202 202 202 202 203 203 203 203 203 203 203 203 203 203 203 566 567 568 569 569 569 570 571 572 573 574 575 576 577 578 7727.3 8636.4 8863.6 9318.2 9200 8636.4 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 8409.1 8409.1 8409.1 8409.1 8409.1 8409.1 8409.1 8409.1 8409.1 8409.1 8409.1 8409.1 8409.1 8409.1 -681.8 227.3 454.5 909.1 790.9 227.3 454.5 -454.6 227.3 -2272.7 -454.6 0 -2954.6 -2954.6 203 204 205 206 207 208 209 209 210 210 210 210 210 210 579 579 579 579 579 579 579 580 580 581 582 582 583 584 8636.4 8863.6 9318.2 9200 8636.4 8863.6 7954.5 8636.4 6136.4 7954.5 7727.3 7727.3 7727.3 7727.3 7727.3 7727.3 7727.3 7727.3 7727.3 7727.3 909.1 1136.3 1590.9 1472.7 909.1 1136.3 227.2 909.1 -1590.9 227.2 211 212 213 214 215 216 217 218 218 219 584 584 584 584 584 584 584 584 585 585 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 30 8409.1 5454.5 5454.5 7727.3 7727.3 7727.3 681.8 -2272.8 -2272.8 220 220 220 585 586 587 8863.6 9318.2 9200 8636.4 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 8636.4 8636.4 8636.4 8636.4 8636.4 8636.4 8636.4 8636.4 8636.4 8636.4 8636.4 8636.4 227.2 681.8 563.6 0 227.2 -681.9 0 -2500 -681.9 -227.3 -3181.9 -3181.9 221 222 223 223 224 224 224 224 224 224 224 224 587 587 587 587 587 588 588 589 590 591 592 593 9318.2 9200 8636.4 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 8863.6 8863.6 8863.6 8863.6 8863.6 8863.6 8863.6 8863.6 8863.6 8863.6 8863.6 454.6 336.4 -227.2 0 -909.1 -227.2 -2727.2 -909.1 -454.5 -3409.1 -3409.1 225 226 226 226 226 226 226 226 226 226 226 593 593 594 594 595 596 597 598 599 600 601 9200 8636.4 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 318.2 9318.2 9318.2 9318.2 9318.2 9318.2 9318.2 9318.2 9318.2 9318.2 Same Date -681.8 -454.6 -1363.7 -681.8 -3181.8 -1363.7 -909.1 -3863.7 -3863.7 226 226 226 226 226 226 226 226 226 226 601 602 603 604 605 606 607 608 609 610 8636.4 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 9200 9200 9200 9200 9200 9200 9200 9200 9200 -563.6 -336.4 -1245.5 -563.6 -3063.6 -1245.5 -790.9 -3745.5 -3745.5 226 226 226 226 226 226 226 226 226 611 612 613 614 615 616 617 618 619 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 31 8863.6 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 8636.4 8636.4 8636.4 8636.4 8636.4 8636.4 8636.4 8636.4 227.2 -681.9 0 -2500 -681.9 -227.3 -3181.9 -3181.9 227 227 227 227 227 227 227 227 619 620 620 621 622 623 624 625 7954.5 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 8863.6 8863.6 8863.6 8863.6 8863.6 8863.6 8863.6 -909.1 -227.2 -2727.2 -909.1 -454.5 -3409.1 -3409.1 227 227 227 227 227 227 227 626 627 628 629 630 631 632 8636.4 6136.4 7954.5 8409.1 5454.5 5454.5 7954.5 7954.5 7954.5 7954.5 7954.5 7954.5 681.9 -1818.1 0 454.6 -2500 -2500 228 228 228 229 229 229 632 633 633 633 634 635 6136.4 7954.5 8409.1 5454.5 5454.5 8636.4 8636.4 8636.4 8636.4 8636.4 -2500 -681.9 -227.3 -3181.9 -3181.9 229 229 229 229 229 636 637 638 639 640 7954.5 8409.1 5454.5 5454.5 6136.4 6136.4 6136.4 6136.4 1818.1 2272.7 -681.9 -681.9 230 231 231 231 640 640 641 642 8409.1 5454.5 5454.5 7954.5 7954.5 7954.5 454.6 -2500 -2500 232 232 232 642 643 644 5454.5 5454.5 8409.1 8409.1 -2954.6 -2954.6 232 232 645 646 5454.5 5454.5 0 232 646 S Statistic = 232 - 646 = -414 ============================================ Tied Group Value Members 1 11136.4 2 2 9545.5 2 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 32 3 10909.1 2 4 7727.3 2 5 9090.9 2 6 7954.5 3 7 8863.6 3 8 6136.4 2 9 9772.7 3 10 9700 2 11 9200 2 12 8409.1 2 13 8636.4 3 14 5454.5 2 ============================================ Time Period Observations 7/28/1999 1 8/2/1999 1 9/24/1999 1 3/9/2000 1 3/16/2001 1 7/28/2001 1 2/27/2002 1 3/27/2002 1 6/28/2002 1 12/20/2002 1 8/8/2003 1 2/26/2004 1 5/20/2004 1 6/28/2004 1 7/21/2004 1 8/13/2004 1 9/30/2004 1 10/27/2004 1 11/18/2004 1 12/29/2004 1 1/7/2005 1 3/21/2005 1 6/15/2005 2 6/16/2005 2 9/29/2005 1 10/14/2005 1 11/30/2005 1 1/20/2006 1 6/29/2006 1 9/15/2006 1 6/15/2007 2 9/27/2007 1 9/12/2008 1 9/26/2008 1 3/6/2009 1 4/22/2009 1 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 33 6/9/2009 1 9/10/2009 1 6/29/2010 1 7/7/2010 1 There are 3 time periods with multiple data ============================================ A = 444 B = 54 C = 24 D=0 E = 44 F=6 a = 164346 b = 666414 c = 3612 Group Variance = 9102.74 Z-Score = -4.32876 Comparison Level at 95% confidence level = -1.65463 (downward trend) -4.32876 < -1.65463 indicating a downward trend ChemStat software output of Mann-Kendall downward trend analysis for most recent data indicating no trend for the same well and analyte: Mann-Kendall Trend Analysis Parameter: NO3-N Location: WEST VALLEY WATER DISTRICT Original Data (Not Transformed) Non-Detects Replaced with Detection Limit 95% Confidence Level ============================================ Xj Xk Xj - Xk Positives Negatives 10909.1 9545.5 1363.6 1 0 7272.7 9545.5 -2272.8 1 1 7727.3 9545.5 -1818.2 1 2 6590.9 9545.5 -2954.6 1 3 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 34 7400 9545.5 -2145.5 1 4 9090.9 9545.5 -454.6 1 5 7954.5 9545.5 -1591 1 6 7700 9545.5 -1845.5 1 7 8863.6 9545.5 -681.9 1 8 9090.9 9545.5 -454.6 1 9 6136.4 9545.5 -3409.1 1 10 9772.7 9545.5 227.2 2 10 9700 9545.5 154.5 3 10 9772.7 9545.5 227.2 4 10 9700 9545.5 154.5 5 10 9772.7 9545.5 227.2 6 10 9200 9545.5 -345.5 6 11 8409.1 9545.5 -1136.4 6 12 7727.3 9545.5 -1818.2 6 13 8636.4 9545.5 -909.1 6 14 8863.6 9545.5 -681.9 6 15 9318.2 9545.5 -227.3 6 16 9200 9545.5 -345.5 6 17 8636.4 9545.5 -909.1 6 18 8863.6 9545.5 -681.9 6 19 7954.5 9545.5 -1591 6 20 8636.4 9545.5 -909.1 6 21 6136.4 9545.5 -3409.1 6 22 7954.5 9545.5 -1591 6 23 8409.1 9545.5 -1136.4 6 24 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 35 5454.5 9545.5 -4091 6 25 5454.5 9545.5 -4091 6 26 7272.7 10909.1 -3636.4 6 27 7727.3 10909.1 -3181.8 6 28 6590.9 10909.1 -4318.2 6 29 7400 10909.1 -3509.1 6 30 9090.9 10909.1 -1818.2 6 31 7954.5 10909.1 -2954.6 6 32 7700 10909.1 -3209.1 6 33 8863.6 10909.1 -2045.5 6 34 9090.9 10909.1 -1818.2 6 35 6136.4 10909.1 -4772.7 6 36 9772.7 10909.1 -1136.4 6 37 9700 10909.1 -1209.1 6 38 9772.7 10909.1 -1136.4 6 39 9700 10909.1 -1209.1 6 40 9772.7 10909.1 -1136.4 6 41 9200 10909.1 -1709.1 6 42 8409.1 10909.1 -2500 6 43 7727.3 10909.1 -3181.8 6 44 8636.4 10909.1 -2272.7 6 45 8863.6 10909.1 -2045.5 6 46 9318.2 10909.1 -1590.9 6 47 9200 10909.1 -1709.1 6 48 8636.4 10909.1 -2272.7 6 49 8863.6 10909.1 -2045.5 6 50 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 36 7954.5 10909.1 -2954.6 6 51 8636.4 10909.1 -2272.7 6 52 6136.4 10909.1 -4772.7 6 53 7954.5 10909.1 -2954.6 6 54 8409.1 10909.1 -2500 6 55 5454.5 10909.1 -5454.6 6 56 5454.5 10909.1 -5454.6 6 57 7727.3 7272.7 454.6 7 57 6590.9 7272.7 -681.8 7 58 7400 7272.7 127.3 8 58 9090.9 7272.7 1818.2 9 58 7954.5 7272.7 681.8 10 58 7700 7272.7 427.3 11 58 8863.6 7272.7 1590.9 12 58 9090.9 7272.7 1818.2 13 58 6136.4 7272.7 -1136.3 13 59 9772.7 7272.7 2500 14 59 9700 7272.7 2427.3 15 59 9772.7 7272.7 2500 16 59 9700 7272.7 2427.3 17 59 9772.7 7272.7 2500 18 59 9200 7272.7 1927.3 19 59 8409.1 7272.7 1136.4 20 59 7727.3 7272.7 454.6 21 59 8636.4 7272.7 1363.7 22 59 8863.6 7272.7 1590.9 23 59 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 37 9318.2 7272.7 2045.5 24 59 9200 7272.7 1927.3 25 59 8636.4 7272.7 1363.7 26 59 8863.6 7272.7 1590.9 27 59 7954.5 7272.7 681.8 28 59 8636.4 7272.7 1363.7 29 59 6136.4 7272.7 -1136.3 29 60 7954.5 7272.7 681.8 30 60 8409.1 7272.7 1136.4 31 60 5454.5 7272.7 -1818.2 31 61 5454.5 7272.7 -1818.2 31 62 6590.9 7727.3 -1136.4 31 63 7400 7727.3 -327.3 31 64 9090.9 7727.3 1363.6 32 64 7954.5 7727.3 227.2 33 64 7700 7727.3 -27.3 33 65 8863.6 7727.3 1136.3 34 65 9090.9 7727.3 1363.6 35 65 6136.4 7727.3 -1590.9 35 66 9772.7 7727.3 2045.4 36 66 9700 7727.3 1972.7 37 66 9772.7 7727.3 2045.4 38 66 9700 7727.3 1972.7 39 66 9772.7 7727.3 2045.4 40 66 9200 7727.3 1472.7 41 66 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 38 8409.1 7727.3 681.8 42 66 7727.3 7727.3 0 42 66 8636.4 7727.3 909.1 43 66 8863.6 7727.3 1136.3 44 66 9318.2 7727.3 1590.9 45 66 9200 7727.3 1472.7 46 66 8636.4 7727.3 909.1 47 66 8863.6 7727.3 1136.3 48 66 7954.5 7727.3 227.2 49 66 8636.4 7727.3 909.1 50 66 6136.4 7727.3 -1590.9 50 67 7954.5 7727.3 227.2 51 67 8409.1 7727.3 681.8 52 67 5454.5 7727.3 -2272.8 52 68 5454.5 7727.3 -2272.8 52 69 7400 6590.9 809.1 53 69 9090.9 6590.9 2500 54 69 7954.5 6590.9 1363.6 55 69 7700 6590.9 1109.1 56 69 8863.6 6590.9 2272.7 57 69 9090.9 6590.9 2500 58 69 6136.4 6590.9 -454.5 58 70 9772.7 6590.9 3181.8 59 70 9700 6590.9 3109.1 60 70 9772.7 6590.9 3181.8 61 70 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 39 9700 6590.9 3109.1 62 70 9772.7 6590.9 3181.8 63 70 9200 6590.9 2609.1 64 70 8409.1 6590.9 1818.2 65 70 7727.3 6590.9 1136.4 66 70 8636.4 6590.9 2045.5 67 70 8863.6 6590.9 2272.7 68 70 9318.2 6590.9 2727.3 69 70 9200 6590.9 2609.1 70 70 8636.4 6590.9 2045.5 71 70 8863.6 6590.9 2272.7 72 70 7954.5 6590.9 1363.6 73 70 8636.4 6590.9 2045.5 74 70 6136.4 6590.9 -454.5 74 71 7954.5 6590.9 1363.6 75 71 8409.1 6590.9 1818.2 76 71 5454.5 6590.9 -1136.4 76 72 5454.5 6590.9 -1136.4 76 73 9090.9 7400 1690.9 77 73 7954.5 7400 554.5 78 73 7700 7400 300 79 73 8863.6 7400 1463.6 80 73 9090.9 7400 1690.9 81 73 6136.4 7400 -1263.6 81 74 9772.7 7400 2372.7 82 74 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 40 9700 7400 2300 83 74 9772.7 7400 2372.7 84 74 9700 7400 2300 85 74 9772.7 7400 2372. 7 86 74 9200 7400 1800 87 74 8409.1 7400 1009.1 88 74 7727.3 7400 327.3 89 74 8636.4 7400 1236.4 90 74 8863.6 7400 1463.6 91 74 9318.2 7400 1918.2 92 74 9200 7400 1800 93 74 8636.4 7400 1236.4 94 74 8863.6 7400 1463.6 95 74 7954.5 7400 554.5 96 74 8636.4 7400 1236.4 97 74 6136.4 7400 -1263.6 97 75 7954.5 7400 554.5 98 75 8409.1 7400 1009.1 99 75 5454.5 7400 -1945.5 99 76 5454.5 7400 -1945.5 99 77 7954.5 9090.9 -1136.4 99 78 7700 9090.9 -1390.9 99 79 8863.6 9090.9 -227.3 99 80 9090.9 9090.9 0 99 80 6136.4 9090.9 -2954.5 99 81 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 41 9772.7 9090.9 681.8 100 81 9700 9090.9 609.1 101 81 9772.7 9090.9 681.8 102 81 9700 9090.9 609.1 103 81 9772.7 9090.9 681.8 104 81 9200 9090.9 109.1 105 81 8409.1 9090.9 -681.8 105 82 7727.3 9090.9 -1363.6 105 83 8636.4 9090.9 -454.5 105 84 8863.6 9090.9 -227.3 105 85 9318.2 9090.9 227.3 106 85 9200 9090.9 109.1 107 85 8636.4 9090.9 -454.5 107 86 8863.6 9090.9 -227.3 107 87 7954.5 9090.9 -1136.4 107 88 8636.4 9090.9 -454.5 107 89 6136.4 9090.9 -2954.5 107 90 7954.5 9090.9 -1136.4 107 91 8409.1 9090.9 -681.8 107 92 5454.5 9090.9 -3636.4 107 93 5454.5 9090.9 -3636.4 107 94 7700 7954.5 -254.5 107 95 8863.6 7954.5 909.1 108 95 9090.9 7954.5 1136.4 109 95 6136.4 7954.5 -1818.1 109 96 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 42 9772.7 7954.5 1818.2 110 96 9700 7954.5 1745.5 111 96 9772.7 7954.5 1818.2 112 96 954.5 1745.5 113 96 9772.7 7954.5 1818.2 114 96 9200 7954.5 1245.5 115 96 8409.1 7954.5 454.6 116 96 7727.3 7954.5 -227.2 116 97 8636.4 7954.5 681.9 117 97 8863.6 7954.5 909.1 118 97 9318.2 7954.5 1363.7 119 97 9200 7954.5 1245.5 120 97 8636.4 7954.5 681.9 121 97 8863.6 7954.5 909.1 122 97 7954.5 7954.5 0 122 97 8636.4 7954.5 681.9 123 97 6136.4 7954.5 -1818.1 123 98 7954.5 7954.5 0 123 98 8409.1 7954.5 454.6 124 98 5454.5 7954.5 -2500 124 99 5454.5 7954.5 -2500 124 100 8863.6 7700 1163.6 125 100 9090.9 7700 1390.9 126 100 6136.4 7700 -1563.6 126 101 9772.7 7700 2072.7 127 101 9700 7 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 43 9700 7700 2000 128 101 9772.7 7700 2072.7 129 101 9700 7700 2000 130 101 9772.7 7700 2072.7 131 101 9200 7700 1500 132 101 8409.1 7700 709.1 133 101 7727.3 7700 27.3 134 101 8636.4 7700 936.4 135 101 8863.6 7700 1163.6 136 101 9318.2 7700 1618.2 137 101 9200 7700 1500 138 101 8636.4 7700 936.4 139 101 8863.6 7700 1163.6 140 101 7954.5 7700 254.5 141 101 8636.4 7700 936.4 142 101 6136.4 7700 -1563.6 142 102 7954.5 7700 254.5 143 102 8409.1 7700 709.1 144 102 5454.5 7700 -2245.5 144 103 5454.5 7700 -2245.5 144 104 9090.9 8863.6 227.3 145 104 6136.4 8863.6 -2727.2 145 105 9772.7 8863.6 909.1 146 105 9700 8863.6 836.4 147 105 9772.7 8863.6 909.1 148 105 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 44 9700 8863.6 836.4 149 105 9772.7 8863.6 909.1 150 105 9200 8863.6 336.4 151 105 8409.1 8863.6 -454.5 151 106 7727.3 8863.6 -1136.3 151 107 8636.4 8863.6 -227.2 151 108 8863.6 8863.6 0 151 108 9318.2 8863.6 454.6 152 108 9200 8863.6 336.4 153 108 8636.4 8863.6 -227.2 153 109 8863.6 8863.6 0 153 109 7954.5 8863.6 -909.1 153 110 8636.4 8863.6 -227.2 153 111 6136.4 8863.6 -2727.2 153 112 7954.5 8863.6 -909.1 153 113 8409.1 8863.6 -454.5 153 114 5454.5 8863.6 -3409.1 153 115 5454.5 8863.6 -3409.1 153 116 6136.4 9090.9 -2954.5 153 117 9772.7 9090.9 681.8 154 117 9700 9090.9 609.1 155 117 9772.7 9090.9 681.8 156 117 9700 9090.9 609.1 157 117 9772.7 9090.9 681.8 158 117 9200 9090.9 109.1 159 117 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 45 8409.1 9090.9 -681.8 159 118 7727.3 9090.9 -1363.6 159 119 8636.4 9090.9 -454.5 159 120 8863.6 9090.9 -227.3 159 121 9318.2 9090.9 227.3 160 121 9200 9090.9 109.1 161 121 8636.4 9090.9 -454.5 161 122 8863.6 9090.9 -227.3 161 123 7954.5 9090.9 -1136.4 161 124 8636.4 9090.9 -454.5 161 125 6136.4 9090.9 -2954.5 161 126 7954.5 9090.9 -1136.4 161 127 8409.1 9090.9 -681.8 161 128 5454.5 9090.9 -3636.4 161 129 5454.5 9090.9 -3636.4 161 130 9772.7 6136.4 3636.3 162 130 9700 6136.4 3563.6 163 130 9772.7 6136.4 3636.3 164 130 9700 6136.4 3563.6 165 130 9772.7 6136.4 3636.3 166 130 9200 6136.4 3063.6 167 130 8409.1 6136.4 2272.7 168 130 7727.3 6136.4 1590.9 169 130 8636.4 6136.4 2500 170 130 8863.6 6136.4 2727.2 171 130 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 46 9318.2 6136.4 3181.8 172 130 9200 6136.4 3063.6 173 130 8636.4 6136.4 2500 174 130 8863.6 6136.4 2727.2 175 130 7954.5 6136.4 1818.1 176 130 8636.4 6136.4 2500 177 130 6136.4 6136.4 0 177 130 7954.5 6136.4 1818.1 178 130 8409.1 6136.4 2272.7 179 130 5454.5 6136.4 -681.9 179 131 5454.5 6136.4 -681.9 179 132 9700 9772.7 Same Date 179 132 9772.7 9772.7 0 179 132 9700 9772.7 -72.7 179 133 9772.7 9772.7 0 179 133 9200 9772.7 -572.7 179 134 8409.1 9772.7 -1363.6 179 135 7727.3 9772.7 -2045.4 179 136 8636.4 9772.7 -1136.3 179 137 8863.6 9772.7 -909.1 179 138 9318.2 9772.7 -454.5 179 139 9200 9772.7 -572.7 179 140 8636.4 9772.7 -1136.3 179 141 8863.6 9772.7 -909.1 179 142 7954.5 9772.7 -1818.2 179 143 8636.4 9772.7 -1136.3 179 144 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 47 6136.4 9772.7 -3636.3 179 145 7954.5 9772.7 -1818.2 179 146 8409.1 9772.7 -1363.6 179 147 5454.5 9772.7 -4318.2 179 148 5454.5 9772.7 -4318.2 179 149 9772.7 9700 72.7 180 149 9700 9700 0 180 149 9772.7 9700 72.7 181 149 9200 9700 -500 181 150 8409.1 9700 -1290.9 181 151 7727.3 9700 -1972.7 181 152 8636.4 9700 -1063.6 181 153 8863.6 9700 -836.4 9318.2 9700 -381.8 181 155 9200 9700 -500 181 156 8636.4 9700 -1063.6 181 157 8863.6 9700 -836.4 181 158 7954.5 9700 -1745.5 181 159 8636.4 9700 -1063.6 181 160 6136.4 9700 -3563.6 181 161 7954.5 9700 -1745.5 181 162 8409.1 9700 -1290.9 181 163 5454.5 9700 -4245.5 181 164 5454.5 9700 -4245.5 181 165 9700 9772.7 Same Date 181 165 9772.7 9772.7 0 181 165 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 48 9200 9772.7 -572.7 181 166 8409.1 9772.7 -1363.6 181 167 7727.3 9772.7 -2045.4 181 168 8636.4 9772.7 -1136.3 181 169 8863.6 9772.7 -909.1 181 170 9318.2 9772.7 -454.5 181 171 9200 9772.7 -572.7 181 172 8636.4 9772.7 -1136.3 181 173 8863.6 9772.7 -909.1 181 174 7954.5 9772.7 -1818.2 181 175 8636.4 9772.7 -1136.3 181 176 6136.4 9772.7 -3636.3 181 177 7954.5 9772.7 -1818.2 181 178 8409.1 9772.7 -1363.6 181 179 5454.5 9772.7 -4318.2 181 180 5454.5 9772.7 -4318.2 181 181 9772.7 9700 72.7 182 181 9200 9700 -500 182 182 8409.1 9700 -1290.9 182 183 7727.3 9700 -1972.7 182 184 8636.4 9700 -1063.6 182 185 8863.6 9700 -836.4 182 186 9318.2 9700 -381.8 182 187 9200 9700 -500 182 188 8636.4 9700 -1063.6 182 189 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 49 8863.6 9700 -836.4 182 190 7954.5 9700 -1745.5 182 191 8636.4 9700 -1063.6 182 192 6136.4 9700 -3563.6 182 193 7954.5 9700 -1745.5 182 194 8409.1 9700 -1290.9 182 195 5454.5 9700 -4245.5 182 196 5454.5 9700 -4245.5 182 197 9200 9772.7 -572.7 182 198 8409.1 9772.7 -1363.6 182 199 7727.3 9772.7 -2045.4 182 200 8636.4 9772.7 -1136.3 182 201 8863.6 9772.7 -909.1 182 202 9318.2 9772.7 -454.5 182 203 9200 9772.7 -572.7 182 204 8636.4 9772.7 -1136.3 182 205 8863.6 9772.7 -909.1 182 206 7954.5 9772.7 -1818.2 182 207 8636.4 9772.7 -1136.3 182 208 6136.4 9772.7 -3636.3 182 209 7954.5 9772.7 -1818.2 182 210 8409.1 9772.7 -1363.6 182 211 5454.5 9772.7 -4318.2 182 212 5454.5 9772.7 -4318.2 182 213 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 50 8409.1 9200 -790.9 182 214 7727.3 9200 -1472.7 182 215 8636.4 9200 -563.6 182 216 8863.6 9200 -336.4 182 217 9318.2 9200 118.2 183 217 9200 9200 0 183 217 8636.4 9200 -563.6 183 218 8863.6 9200 -336.4 183 219 7954.5 9200 -1245.5 183 220 8636.4 9200 -563.6 183 221 6136.4 9200 -3063.6 183 222 7954.5 9200 -1245.5 183 223 8409.1 9200 -790.9 183 224 5454.5 9200 -3745.5 183 225 5454.5 9200 -3745.5 183 226 7727.3 8409.1 -681.8 183 227 8636.4 8409.1 227.3 184 227 8863.6 8409.1 454.5 185 227 9318.2 8409.1 909.1 186 227 9200 8409.1 790.9 187 227 8636.4 8409.1 227.3 188 227 8863.6 8409.1 454.5 189 227 7954.5 8409.1 -454.6 189 228 8636.4 8409.1 227.3 190 228 6136.4 8409.1 -2272.7 190 229 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 51 7954.5 8409.1 -454.6 190 230 8409.1 8409.1 0 190 230 5454.5 8409.1 -2954.6 190 231 5454.5 8409.1 -2954.6 190 232 8636.4 7727.3 909.1 191 232 8863.6 7727.3 1136.3 192 232 9318.2 7727.3 1590.9 193 232 9200 7727.3 1472.7 194 232 8636.4 7727.3 909.1 195 232 8863.6 7727.3 1136.3 196 232 7954.5 7727.3 227.2 197 232 8636.4 7727.3 909.1 198 232 6136.4 7727.3 -1590.9 198 233 7954.5 7727.3 227.2 199 233 8409.1 7727.3 681.8 200 233 5454.5 7727.3 -2272.8 200 234 5454.5 7727.3 -2272.8 200 235 8863.6 8636.4 227.2 201 235 9318.2 8636.4 681.8 202 235 9200 8636.4 563.6 203 235 8636.4 8636.4 0 203 235 8863.6 8636.4 227.2 204 235 7954.5 8636.4 -681.9 204 236 8636.4 8636.4 0 204 236 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 52 6136.4 8636.4 -2500 204 237 7954.5 8636.4 -681.9 204 238 8409.1 8636.4 -227.3 204 239 5454.5 8636.4 -3181.9 204 240 5454.5 8636.4 -3181.9 204 241 9318.2 8863.6 454.6 205 241 9200 8863.6 336.4 206 241 8636.4 8863.6 -227.2 206 242 8863.6 8863.6 0 206 242 7954.5 8863.6 -909.1 206 243 8636.4 8863.6 -227.2 206 244 6136.4 8863.6 -2727.2 206 245 7954.5 8863.6 -909.1 206 246 8409.1 8863.6 -454.5 206 247 5454.5 8863.6 -3409.1 206 248 5454.5 8863.6 -3409.1 206 249 9200 9318.2 Same Date 206 249 8636.4 9318.2 -681.8 206 250 8863.6 9318.2 -454.6 206 251 7954.5 9318.2 -1363.7 206 252 8636.4 9318.2 -681.8 206 253 6136.4 9318.2 -3181.8 206 254 7954.5 9318.2 -1363.7 206 255 8409.1 9318.2 -909.1 206 256 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 53 5454.5 9318.2 -3863.7 206 257 5454.5 9318.2 -3863.7 206 258 8636.4 9200 -563.6 206 259 8863.6 9200 -336.4 206 260 7954.5 9200 -1245.5 206 261 8636.4 9200 -563.6 206 262 6136.4 9200 -3063.6 206 263 7954.5 9200 -1245.5 206 264 8409.1 9200 -790.9 206 265 5454.5 9200 -3745.5 206 266 5454.5 9200 -3745.5 206 267 8863.6 8636.4 227.2 207 267 7954.5 8636.4 -681.9 207 268 8636.4 8636.4 0 207 268 6136.4 8636.4 -2500 207 269 7954.5 8636.4 -681.9 207 270 8409.1 8636.4 -227.3 207 271 5454.5 8636.4 -3181.9 207 272 5454.5 8636.4 -3181.9 207 273 7954.5 8863.6 -909.1 207 274 8636.4 8863.6 -227.2 207 275 6136.4 8863.6 -2727.2 207 276 7954.5 8863.6 -909.1 207 277 8409.1 8863.6 -454.5 207 278 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 54 5454.5 8863.6 -3409.1 207 279 5454.5 8863.6 -3409.1 207 280 8636.4 7954.5 681.9 208 280 6136.4 7954.5 -1818.1 208 281 7954.5 7954.5 0 208 281 8409.1 7954.5 454.6 209 281 5454.5 7954.5 -2500 209 282 5454.5 7954.5 -2500 209 283 6136.4 8636.4 -2500 209 284 7954.5 8636.4 -681.9 209 285 8409.1 8636.4 -227.3 209 286 5454.5 8636.4 -3181.9 209 287 5454.5 8636.4 -3181.9 209 288 7954.5 6136.4 1818.1 210 288 8409.1 6136.4 2272.7 211 288 5454.5 6136.4 -681.9 211 289 5454.5 6136.4 -681.9 211 290 8409.1 7954.5 454.6 212 290 5454.5 7954.5 -2500 212 291 5454.5 7954.5 -2500 212 292 5454.5 8409.1 -2954.6 212 293 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 55 5454.5 8409.1 -2954.6 212 294 5454.5 5454.5 0 212 294 S Statistic = 212 - 294 = -82 ============================================ Tied Group Value Members 1 7727.3 2 2 9090.9 2 3 7954.5 3 4 8863.6 3 5 6136.4 2 6 9772.7 3 7 9700 2 8 9200 2 9 8409.1 2 10 8636.4 3 11 5454.5 2 ============================================ Time Period Observations 8/8/2003 1 2/26/2004 1 5/20/2004 1 6/28/2004 1 7/21/2004 1 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 56 8/13/2004 1 9/30/2004 1 10/27/2004 1 11/18/2004 1 12/29/2004 1 1/7/2005 1 3/21/2005 1 6/15/2005 2 6/16/2005 2 9/29/2005 1 10/14/2005 1 11/30/2005 1 1/20/2006 1 6/29/2006 1 9/15/2006 1 6/15/2007 2 9/27/2007 1 9/12/2008 1 9/26/2008 1 3/6/2009 1 4/22/2009 1 6/9/2009 1 9/10/2009 1 6/29/2010 1 7/7/2010 1 There are 3 time periods with multiple data Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 57 ============================================ A = 390 B = 54 C = 24 D=0 E = 38 F=6 a = 74976 b = 294624 c = 2112 Group Variance = 4140.77 Z-Score = -1.25876 Comparison Level at 95% confidence level = -1.65463 (downward trend) -1.25876 >= -1.65463 indicating no evidence of a downward trend Summary: A downward trend was observed in the nitrate-nitrogen data for WVWD Well 11. Thus, only the most recent results were used in the HHRA to determine the exposure point concentration, in order to not include results from years in which the nitrate-nitrogen concentration in this well was decreasing, and to better represent current and future well concentrations for this analyte. Based on the trend analysis results, the range of sample dates used in the HHRA for this analyte and well were from 8 August 2003 to October 2010, which includes 33 sample results. Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 58 B.4 Perchlorate, Rialto Well 6 Time-series plot of all perchlorate data from Rialto Well 6 that are part of the human health risk assessment database: ChemStat software output of Mann-Kendall upward trend analysis for the same dataset: Mann-Kendall Trend Analysis Parameter: PERCHLORATE Location: RIALTO-CITY Original Data (Not Transformed) Non-Detects Replaced with Detection Limit 95% Confidence Level ============================================ Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 59 Xj ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 5 ND<4 ND<4 6 6 5 9 6 7 7 9 10 9 9.7 9 13 ND<4 8 8 14 15 16 20 21 19 19 23 38 26 24 27 30 31 32 34 32 35 Xk ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 Xj - Xk -1 -1 -1 -1 -1 -1 -1 -1 -1 -1 -1 -1 0 -1 -1 1 1 0 4 1 2 2 4 5 4 4.7 4 8 -1 3 3 9 10 11 15 16 14 14 18 33 21 19 22 25 26 27 29 27 30 Positives 0 1 0 2 0 3 0 4 0 5 0 6 0 7 0 8 0 9 0 10 0 11 0 12 0 12 0 13 0 14 1 14 2 14 2 14 3 14 4 14 5 14 6 14 7 14 8 14 9 14 10 14 11 14 12 14 12 15 13 15 14 15 15 15 16 15 17 15 18 15 19 15 20 15 21 15 22 15 23 15 24 15 25 15 26 15 27 15 28 15 29 15 30 15 31 15 32 15 Negatives Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 60 41 46 36 40 42 45 45 ND<4 45 45 52 53 56 57 57 57 62 68 71 65 62 65 76 69 73 80 82 88 94 92 86 89 110 94 130 130 130 140 140 150 180 170 180 180 190 180 230 210 180 270 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 36 41 31 35 37 40 40 -1 40 40 47 48 51 52 52 52 57 63 66 60 57 60 71 64 68 75 77 83 89 87 81 84 105 89 125 125 125 135 135 145 175 165 175 175 185 175 225 205 175 265 33 34 35 36 37 38 39 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60 61 62 63 64 65 66 67 68 69 70 71 72 73 74 75 76 77 78 79 80 81 15 15 15 15 15 15 15 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 61 190 190 210 210 300 230 280 320 200 210 210 280 220 210 250 200 310 300 230 200 220 250 210 230 230 260 280 33 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 185 185 205 205 295 225 275 315 195 205 205 275 215 205 245 195 305 295 225 195 215 245 205 225 225 255 275 28 82 83 84 85 86 87 88 89 90 91 92 93 94 95 96 97 98 99 100 101 102 103 104 105 106 107 108 109 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 5 ND<4 ND<4 6 6 5 9 6 7 7 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 0 0 0 0 0 0 0 0 0 0 0 1 0 0 2 2 1 5 2 3 3 109 109 109 109 109 109 109 109 109 109 109 110 110 110 111 112 113 114 115 116 117 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 62 9 10 9 9.7 9 13 ND<4 8 8 14 15 16 20 21 19 19 23 38 26 24 27 30 31 32 34 32 35 41 46 36 40 42 45 45 ND<4 45 45 52 53 56 57 57 57 62 68 71 65 62 65 76 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 5 6 5 5.7 5 9 0 4 4 10 11 12 16 17 15 15 19 34 22 20 23 26 27 28 30 28 31 37 42 32 36 38 41 41 0 41 41 48 49 52 53 53 53 58 64 67 61 58 61 72 118 119 120 121 122 123 123 124 125 126 127 128 129 130 131 132 133 134 135 136 137 138 139 140 141 142 143 144 145 146 147 148 149 150 150 151 152 153 154 155 156 157 158 159 160 161 162 163 164 165 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 63 69 73 80 82 88 94 92 86 89 110 94 130 130 130 140 140 150 180 170 180 180 190 180 230 210 180 270 190 190 210 210 300 230 280 320 200 210 210 280 220 210 250 200 310 300 230 200 220 250 210 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 65 69 76 78 84 90 88 82 85 106 90 126 126 126 136 136 146 176 166 176 176 186 176 226 206 176 266 186 186 206 206 296 226 276 316 196 206 206 276 216 206 246 196 306 296 226 196 216 246 206 166 167 168 169 170 171 172 173 174 175 176 177 178 179 180 181 182 183 184 185 186 187 188 189 190 191 192 193 194 195 196 197 198 199 200 201 202 203 204 205 206 207 208 209 210 211 212 213 214 215 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 64 230 230 260 280 33 ND<4 ND<4 ND<4 ND<4 ND<4 226 226 256 276 29 216 217 218 219 220 16 16 16 16 16 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 5 ND<4 ND<4 6 6 5 9 6 7 7 9 10 9 9.7 9 13 ND<4 8 8 14 15 16 20 21 19 19 23 38 26 24 27 30 31 32 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 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443 443 443 444 445 446 447 448 449 450 451 452 453 454 455 456 456 457 458 459 460 461 462 463 464 465 466 467 468 469 470 471 472 473 474 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 70 32 35 41 46 36 40 42 45 45 ND<4 45 45 52 53 56 57 57 57 62 68 71 65 62 65 76 69 73 80 82 88 94 92 86 89 110 94 130 130 130 140 140 150 180 170 180 180 190 180 230 210 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 28 31 37 42 32 36 38 41 41 0 41 41 48 49 52 53 53 53 58 64 67 61 58 61 72 65 69 76 78 84 90 88 82 85 106 90 126 126 126 136 136 146 176 166 176 176 186 176 226 206 475 476 477 478 479 480 481 482 483 483 484 485 486 487 488 489 490 491 492 493 494 495 496 497 498 499 500 501 502 503 504 505 506 507 508 509 510 511 512 513 514 515 516 517 518 519 520 521 522 523 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 71 180 270 190 190 210 210 300 230 280 320 200 210 210 280 220 210 250 200 310 300 230 200 220 250 210 230 230 260 280 33 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 176 266 186 186 206 206 296 226 276 316 196 206 206 276 216 206 246 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22 20 23 26 27 28 30 28 31 37 42 32 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 75 40 42 45 45 ND<4 45 45 52 53 56 57 57 57 62 68 71 65 62 65 76 69 73 80 82 88 94 92 86 89 110 94 130 130 130 140 140 150 180 170 180 180 190 180 230 210 180 270 190 190 210 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 36 38 41 41 0 41 41 48 49 52 53 53 53 58 64 67 61 58 61 72 65 69 76 78 84 90 88 82 85 106 90 126 126 126 136 136 146 176 166 176 176 186 176 226 206 176 266 186 186 206 702 703 704 705 705 706 707 708 709 710 711 712 713 714 715 716 717 718 719 720 721 722 723 724 725 726 727 728 729 730 731 732 733 734 735 736 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19 34 22 20 23 26 27 28 30 28 31 37 42 32 36 38 41 41 0 41 41 48 49 52 53 53 53 58 64 67 61 58 61 72 65 69 76 78 84 90 88 82 85 792 793 794 795 796 797 798 799 800 801 802 803 804 805 806 807 808 809 810 811 812 813 814 815 816 816 817 818 819 820 821 822 823 824 825 826 827 828 829 830 831 832 833 834 835 836 837 838 839 840 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 78 110 94 130 130 130 140 140 150 180 170 180 180 190 180 230 210 180 270 190 190 210 210 300 230 280 320 200 210 210 280 220 210 250 200 310 300 230 200 220 250 210 230 230 260 280 33 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 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16 16 16 16 16 16 16 16 16 16 16 16 16 16 0 1 0 0 2 2 1 5 2 3 3 5 6 5 5.7 5 9 0 4 4 10 11 12 16 17 15 15 19 34 22 20 23 26 27 28 30 28 31 37 42 32 36 38 41 41 0 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 87 45 45 52 53 56 57 57 57 62 68 71 65 62 65 76 69 73 80 82 88 94 92 86 89 110 94 130 130 130 140 140 150 180 170 180 180 190 180 230 210 180 270 190 190 210 210 300 230 280 320 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 41 41 48 49 52 53 53 53 58 64 67 61 58 61 72 65 69 76 78 84 90 88 82 85 106 90 126 126 126 136 136 146 176 166 176 176 186 176 226 206 176 266 186 186 206 206 296 226 276 316 1261 1262 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23 23 5 9 6 7 7 9 10 9 9.7 6 6 6 6 6 6 6 6 6 -1 3 0 1 1 3 4 3 3.7 1876 1877 1877 1878 1879 1880 1881 1882 1883 24 24 24 24 24 24 24 24 24 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 100 9 13 ND<4 8 8 14 15 16 20 21 19 19 23 38 26 24 27 30 31 32 34 32 35 41 46 36 40 42 45 45 ND<4 45 45 52 53 56 57 57 57 62 68 71 65 62 65 76 69 73 80 82 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 3 7 -2 2 2 8 9 10 14 15 13 13 17 32 20 18 21 24 25 26 28 26 29 35 40 30 34 36 39 39 -2 39 39 46 47 50 51 51 51 56 62 65 59 56 59 70 63 67 74 76 1884 1885 1885 1886 1887 1888 1889 1890 1891 1892 1893 1894 1895 1896 1897 1898 1899 1900 1901 1902 1903 1904 1905 1906 1907 1908 1909 1910 1911 1912 1912 1913 1914 1915 1916 1917 1918 1919 1920 1921 1922 1923 1924 1925 1926 1927 1928 1929 1930 1931 24 24 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 101 88 94 92 86 89 110 94 130 130 130 140 140 150 180 170 180 180 190 180 230 210 180 270 190 190 210 210 300 230 280 320 200 210 210 280 220 210 250 200 310 300 230 200 220 250 210 230 230 260 280 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 82 88 86 80 83 104 88 124 124 124 134 134 144 174 164 174 174 184 174 224 204 174 264 184 184 204 204 294 224 274 314 194 204 204 274 214 204 244 194 304 294 224 194 214 244 204 224 224 254 274 1932 1933 1934 1935 1936 1937 1938 1939 1940 1941 1942 1943 1944 1945 1946 1947 1948 1949 1950 1951 1952 1953 1954 1955 1956 1957 1958 1959 1960 1961 1962 1963 1964 1965 1966 1967 1968 1969 1970 1971 1972 1973 1974 1975 1976 1977 1978 1979 1980 1981 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 26 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 102 33 6 27 1982 26 9 6 7 7 9 10 9 9.7 9 13 ND<4 8 8 14 15 16 20 21 19 19 23 38 26 24 27 30 31 32 34 32 35 41 46 36 40 42 45 45 ND<4 45 45 52 53 56 57 57 57 62 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 4 1 2 2 4 5 4 4.7 4 8 -1 3 3 9 10 11 15 16 14 14 18 33 21 19 22 25 26 27 29 27 30 36 41 31 35 37 40 40 -1 40 40 47 48 51 52 52 52 57 1983 1984 1985 1986 1987 1988 1989 1990 1991 1992 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015 2016 2017 2018 2019 2019 2020 2021 2022 2023 2024 2025 2026 2027 2028 26 26 26 26 26 26 26 26 26 26 27 27 27 27 27 27 27 27 27 27 27 27 27 27 27 27 27 27 27 27 27 27 27 27 27 27 27 27 28 28 28 28 28 28 28 28 28 28 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 103 68 71 65 62 65 76 69 73 80 82 88 94 92 86 89 110 94 130 130 130 140 140 150 180 170 180 180 190 180 230 210 180 270 190 190 210 210 300 230 280 320 200 210 210 280 220 210 250 200 310 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 63 66 60 57 60 71 64 68 75 77 83 89 87 81 84 105 89 125 125 125 135 135 145 175 165 175 175 185 175 225 205 175 265 185 185 205 205 295 225 275 315 195 205 205 275 215 205 245 195 305 2029 2030 2031 2032 2033 2034 2035 2036 2037 2038 2039 2040 2041 2042 2043 2044 2045 2046 2047 2048 2049 2050 2051 2052 2053 2054 2055 2056 2057 2058 2059 2060 2061 2062 2063 2064 2065 2066 2067 2068 2069 2070 2071 2072 2073 2074 2075 2076 2077 2078 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 104 300 230 200 220 250 210 230 230 260 280 33 5 5 5 5 5 5 5 5 5 5 5 295 225 195 215 245 205 225 225 255 275 28 2079 2080 2081 2082 2083 2084 2085 2086 2087 2088 2089 28 28 28 28 28 28 28 28 28 28 28 6 7 7 9 10 9 9.7 9 13 ND<4 8 8 14 15 16 20 21 19 19 23 38 26 24 27 30 31 32 34 32 35 41 46 36 40 42 45 45 ND<4 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 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250 210 230 230 260 280 33 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 -30 60 -20 -20 0 0 90 20 70 110 -10 0 0 70 10 0 40 -10 100 90 20 -10 10 40 0 20 20 50 70 -177 7290 7291 7291 7291 7291 7291 7292 7293 7294 7295 7295 7295 7295 7296 7297 7297 7298 7298 7299 7300 7301 7301 7302 7303 7303 7304 7305 7306 7307 7307 206 206 207 208 208 208 208 208 208 208 209 209 209 209 209 209 209 210 210 210 210 211 211 211 211 211 211 211 211 212 270 190 190 210 210 300 230 280 180 180 180 180 180 180 180 180 90 10 10 30 30 120 50 100 7308 7309 7310 7311 7312 7313 7314 7315 212 212 212 212 212 212 212 212 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 215 320 200 210 210 280 220 210 250 200 310 300 230 200 220 250 210 230 230 260 280 33 180 180 180 180 180 180 180 180 180 180 180 180 180 180 180 180 180 180 180 180 180 140 20 30 30 100 40 30 70 20 130 120 50 20 40 70 30 50 50 80 100 -147 7316 7317 7318 7319 7320 7321 7322 7323 7324 7325 7326 7327 7328 7329 7330 7331 7332 7333 7334 7335 7335 212 212 212 212 212 212 212 212 212 212 212 212 212 212 212 212 212 212 212 212 213 190 190 210 210 300 230 280 320 200 210 210 280 220 210 250 200 310 300 230 200 220 250 210 230 230 260 280 33 270 270 270 270 270 270 270 270 270 270 270 270 270 270 270 270 270 270 270 270 270 270 270 270 270 270 270 270 -80 -80 -60 -60 30 -40 10 50 -70 -60 -60 10 -50 -60 -20 -70 40 30 -40 -70 -50 -20 -60 -40 -40 -10 10 -237 7335 7335 7335 7335 7336 7336 7337 7338 7338 7338 7338 7339 7339 7339 7339 7339 7340 7341 7341 7341 7341 7341 7341 7341 7341 7341 7342 7342 214 215 216 217 217 218 218 218 219 220 221 221 222 223 224 225 225 225 226 227 228 229 230 231 232 233 233 234 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 216 190 210 210 300 230 280 320 200 210 210 280 220 210 250 200 310 300 230 200 220 250 210 230 230 260 280 33 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 0 20 20 110 40 90 130 10 20 20 90 30 20 60 10 120 110 40 10 30 60 20 40 40 70 90 -157 7342 7343 7344 7345 7346 7347 7348 7349 7350 7351 7352 7353 7354 7355 7356 7357 7358 7359 7360 7361 7362 7363 7364 7365 7366 7367 7367 234 234 234 234 234 234 234 234 234 234 234 234 234 234 234 234 234 234 234 234 234 234 234 234 234 234 235 210 210 300 230 280 320 200 210 210 280 220 210 250 200 310 300 230 200 220 250 210 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 190 20 20 110 40 90 130 10 20 20 90 30 20 60 10 120 110 40 10 30 60 20 7368 7369 7370 7371 7372 7373 7374 7375 7376 7377 7378 7379 7380 7381 7382 7383 7384 7385 7386 7387 7388 235 235 235 235 235 235 235 235 235 235 235 235 235 235 235 235 235 235 235 235 235 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 217 230 230 260 280 33 190 190 190 190 190 40 40 70 90 -157 7389 7390 7391 7392 7392 235 235 235 235 236 210 300 230 280 320 200 210 210 280 220 210 250 200 310 300 230 200 220 250 210 230 230 260 280 33 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 0 90 20 70 110 -10 0 0 70 10 0 40 -10 100 90 20 -10 10 40 0 20 20 50 70 -177 7392 7393 7394 7395 7396 7396 7396 7396 7397 7398 7398 7399 7399 7400 7401 7402 7402 7403 7404 7404 7405 7406 7407 7408 7408 236 236 236 236 236 237 237 237 237 237 237 237 238 238 238 238 239 239 239 239 239 239 239 239 240 300 230 280 320 200 210 210 280 220 210 250 200 310 300 230 200 220 250 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 90 20 70 110 -10 0 0 70 10 0 40 -10 100 90 20 -10 10 40 7409 7410 7411 7412 7412 7412 7412 7413 7414 7414 7415 7415 7416 7417 7418 7418 7419 7420 240 240 240 240 241 241 241 241 241 241 241 242 242 242 242 243 243 243 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 218 210 230 230 260 280 33 210 210 210 210 210 210 0 20 20 50 70 -177 7420 7421 7422 7423 7424 7424 243 243 243 243 243 244 230 280 320 200 210 210 280 220 210 250 200 310 300 230 200 220 250 210 230 230 260 280 33 300 300 300 300 300 300 300 300 300 300 300 300 300 300 300 300 300 300 300 300 300 300 300 -70 -20 20 -100 -90 -90 -20 -80 -90 -50 -100 10 0 -70 -100 -80 -50 -90 -70 -70 -40 -20 -267 7424 7424 7425 7425 7425 7425 7425 7425 7425 7425 7425 7426 7426 7426 7426 7426 7426 7426 7426 7426 7426 7426 7426 245 246 246 247 248 249 250 251 252 253 254 254 254 255 256 257 258 259 260 261 262 263 264 280 320 200 210 210 280 220 210 250 200 310 300 230 200 220 250 210 230 230 230 230 230 230 230 230 230 230 230 230 230 230 230 230 230 230 230 230 230 50 90 -30 -20 -20 50 -10 -20 20 -30 80 70 0 -30 -10 20 -20 0 0 7427 7428 7428 7428 7428 7429 7429 7429 7430 7430 7431 7432 7432 7432 7432 7433 7433 7433 7433 264 264 265 266 267 267 268 269 269 270 270 270 270 271 272 272 273 273 273 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 219 260 280 33 230 230 230 30 50 -197 7434 7435 7435 273 273 274 320 200 210 210 280 220 210 250 200 310 300 230 200 220 250 210 230 230 260 280 33 280 280 280 280 280 280 280 280 280 280 280 280 280 280 280 280 280 280 280 280 280 40 -80 -70 -70 0 -60 -70 -30 -80 30 20 -50 -80 -60 -30 -70 -50 -50 -20 0 -247 7436 7436 7436 7436 7436 7436 7436 7436 7436 7437 7438 7438 7438 7438 7438 7438 7438 7438 7438 7438 7438 274 275 276 277 277 278 279 280 281 281 281 282 283 284 285 286 287 288 289 289 290 200 210 210 280 220 210 250 200 310 300 230 200 220 250 210 230 230 260 280 33 320 320 320 320 320 320 320 320 320 320 320 320 320 320 320 320 320 320 320 320 -120 -110 -110 -40 -100 -110 -70 -120 -10 -20 -90 -120 -100 -70 -110 -90 -90 -60 -40 -287 7438 7438 7438 7438 7438 7438 7438 7438 7438 7438 7438 7438 7438 7438 7438 7438 7438 7438 7438 7438 291 292 293 294 295 296 297 298 299 300 301 302 303 304 305 306 307 308 309 310 210 210 280 200 200 200 10 10 80 7439 7440 7441 310 310 310 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 220 220 210 250 200 310 300 230 200 220 250 210 230 230 260 280 33 200 200 200 200 200 200 200 200 200 200 200 200 200 200 200 200 20 10 50 0 110 100 30 0 20 50 10 30 30 60 80 -167 7442 7443 7444 7444 7445 7446 7447 7447 7448 7449 7450 7451 7452 7453 7454 7454 310 310 310 310 310 310 310 310 310 310 310 310 310 310 310 311 210 280 220 210 250 200 310 300 230 200 220 250 210 230 230 260 280 33 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 210 0 70 10 0 40 -10 100 90 20 -10 10 40 0 20 20 50 70 -177 7454 7455 7456 7456 7457 7457 7458 7459 7460 7460 7461 7462 7462 7463 7464 7465 7466 7466 311 311 311 311 311 312 312 312 312 313 313 313 313 313 313 313 313 314 280 220 210 250 200 310 300 230 200 220 250 210 230 230 210 210 210 210 210 210 210 210 210 210 210 210 210 210 70 10 0 40 -10 100 90 20 -10 10 40 0 20 20 7467 7468 7468 7469 7469 7470 7471 7472 7472 7473 7474 7474 7475 7476 314 314 314 314 315 315 315 315 316 316 316 316 316 316 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 221 260 280 33 210 210 210 50 70 -177 7477 7478 7478 316 316 317 220 210 250 200 310 300 230 200 220 250 210 230 230 260 280 33 280 280 280 280 280 280 280 280 280 280 280 280 280 280 280 280 -60 -70 -30 -80 30 20 -50 -80 -60 -30 -70 -50 -50 -20 0 -247 7478 7478 7478 7478 7479 7480 7480 7480 7480 7480 7480 7480 7480 7480 7480 7480 318 319 320 321 321 321 322 323 324 325 326 327 328 329 329 330 210 250 200 310 300 230 200 220 250 210 230 230 260 280 33 220 220 220 220 220 220 220 220 220 220 220 220 220 220 220 -10 30 -20 90 80 10 -20 0 30 -10 10 10 40 60 -187 7480 7481 7481 7482 7483 7484 7484 7484 7485 7485 7486 7487 7488 7489 7489 331 331 332 332 332 332 333 333 333 334 334 334 334 334 335 250 200 310 300 230 200 220 250 210 230 230 260 280 210 210 210 210 210 210 210 210 210 210 210 210 210 40 -10 100 90 20 -10 10 40 0 20 20 50 70 7490 7490 7491 7492 7493 7493 7494 7495 7495 7496 7497 7498 7499 335 336 336 336 336 337 337 337 337 337 337 337 337 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 222 33 210 -177 7499 338 200 310 300 230 200 220 250 210 230 230 260 280 33 250 250 250 250 250 250 250 250 250 250 250 250 250 -50 60 50 -20 -50 -30 0 -40 -20 -20 10 30 -217 7499 7500 7501 7501 7501 7501 7501 7501 7501 7501 7502 7503 7503 339 339 339 340 341 342 342 343 344 345 345 345 346 310 300 230 200 220 250 210 230 230 260 280 33 200 200 200 200 200 200 200 200 200 200 200 200 110 100 30 0 20 50 10 30 30 60 80 -167 7504 7505 7506 7506 7507 7508 7509 7510 7511 7512 7513 7513 346 346 346 346 346 346 346 346 346 346 346 347 300 230 200 220 250 210 230 230 260 280 33 310 310 310 310 310 310 310 310 310 310 310 -10 -80 -110 -90 -60 -100 -80 -80 -50 -30 -277 7513 7513 7513 7513 7513 7513 7513 7513 7513 7513 7513 348 349 350 351 352 353 354 355 356 357 358 230 200 220 250 210 230 230 260 280 300 300 300 300 300 300 300 300 300 -70 -100 -80 -50 -90 -70 -70 -40 -20 7513 7513 7513 7513 7513 7513 7513 7513 7513 359 360 361 362 363 364 365 366 367 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 223 33 300 -267 7513 368 200 220 250 210 230 230 260 280 33 230 230 230 230 230 230 230 230 230 -30 -10 20 -20 0 0 30 50 -197 7513 7513 7514 7514 7514 7514 7515 7516 7516 369 370 370 371 371 371 371 371 372 220 250 210 230 230 260 280 33 200 200 200 200 200 200 200 200 20 50 10 30 30 60 80 -167 7517 7518 7519 7520 7521 7522 7523 7523 372 372 372 372 372 372 372 373 250 210 230 230 260 280 33 220 220 220 220 220 220 220 30 -10 10 10 40 60 -187 7524 7524 7525 7526 7527 7528 7528 373 374 374 374 374 374 375 210 230 230 260 280 33 250 250 250 250 250 250 -40 -20 -20 10 30 -217 7528 7528 7528 7529 7530 7530 376 377 378 378 378 379 230 230 260 280 33 210 210 210 210 210 20 20 50 70 -177 7531 7532 7533 7534 7534 379 379 379 379 380 230 260 280 33 230 230 230 230 0 30 50 -197 7534 7535 7536 7536 380 380 380 381 260 280 33 230 230 230 30 50 -197 7537 7538 7538 381 381 382 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 224 280 33 260 260 20 -227 7539 7539 382 383 33 280 -247 7539 384 S Statistic = 7539 - 384 = 7155 ============================================ Tied Group Value Members 1 5 3 2 4 16 3 6 3 4 9 4 5 7 2 6 8 2 7 19 2 8 32 2 9 45 4 10 57 3 11 62 2 12 65 2 13 94 2 14 130 3 15 140 2 16 180 5 17 190 3 18 230 5 19 210 7 20 300 2 21 280 3 22 200 3 23 220 2 24 250 2 ============================================ Time Period Observations 2/3/1999 1 3/3/1999 1 4/13/1999 1 6/23/1999 1 7/7/1999 1 8/4/1999 1 9/14/1999 1 10/6/1999 1 11/2/1999 1 12/7/1999 1 1/11/2000 1 2/1/2000 1 3/2/2000 1 4/5/2000 1 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 225 4/26/2000 5/2/2000 6/7/2000 7/11/2000 8/2/2000 9/6/2000 9/19/2000 10/3/2000 11/14/2000 12/6/2000 1/23/2001 2/21/2001 3/14/2001 4/4/2001 5/1/2001 7/10/2001 8/8/2001 9/18/2001 10/2/2001 11/20/2001 12/11/2001 1/31/2002 2/21/2002 4/16/2002 5/14/2002 8/15/2002 9/12/2002 10/1/2002 11/13/2002 12/9/2002 1/22/2003 2/24/2003 3/12/2003 4/22/2003 5/21/2003 6/5/2003 7/23/2003 8/19/2003 9/11/2003 10/22/2003 11/5/2003 12/9/2003 1/13/2004 2/26/2004 3/16/2004 4/20/2004 5/18/2004 6/16/2004 7/27/2004 8/24/2004 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 226 9/22/2004 10/13/2004 11/22/2004 12/14/2004 1/25/2005 2/24/2005 3/22/2005 4/20/2005 5/31/2005 6/29/2005 7/20/2005 8/2/2005 9/22/2005 10/19/2005 11/23/2005 12/15/2005 1/19/2006 2/21/2006 3/22/2006 4/11/2006 9/12/2006 10/23/2006 11/16/2006 12/12/2006 1/3/2007 2/15/2007 4/5/2007 5/2/2007 6/12/2007 7/17/2007 8/7/2007 9/11/2007 10/24/2007 11/6/2007 12/4/2007 1/9/2008 2/21/2008 3/11/2008 4/9/2008 5/13/2008 6/17/2008 8/12/2008 10/28/2008 11/12/2008 12/23/2008 1/6/2009 2/18/2009 3/11/2009 4/8/2009 5/6/2009 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 227 6/9/2009 1 7/13/2009 1 8/19/2009 1 9/15/2009 1 10/15/2009 1 11/10/2009 1 1/6/2010 1 2/18/2010 1 3/24/2010 1 4/27/2010 1 5/25/2010 1 6/22/2010 1 7/28/2010 1 8/18/2010 1 There are 0 time periods with multiple data ============================================ A = 11250 B=0 C = 3780 D=0 E = 410 F=0 a = 4.24282e+006 b = 1.84343e+007 c = 32512 Group Variance = 235087 Z-Score = 14.7548 Comparison Level at 95% confidence level = 1.65463 (upward trend) 14.7548 > 1.65463 indicating an upward trend ChemStat software output of Mann-Kendall upward trend analysis for most recent data Mann-Kendall Trend Analysis Parameter: PERCHLORATE Location: RIALTO-CITY Original Data (Not Transformed) Non-Detects Replaced with Detection Limit 95% Confidence Level ============================================ Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 228 Xj Xk Xj - Xk Positives 230 180 50 1 0 210 180 30 2 0 180 180 0 2 0 270 180 90 3 0 190 180 10 4 0 190 180 10 5 0 210 180 30 6 0 210 180 30 7 0 300 180 120 8 0 230 180 50 9 0 280 180 100 10 0 320 180 140 11 0 200 180 20 12 0 210 180 30 13 0 210 180 30 14 0 280 180 100 15 0 220 180 40 16 0 210 180 30 17 0 250 180 70 18 0 200 180 20 19 0 310 180 130 20 0 300 180 120 21 0 230 180 50 22 0 200 180 20 23 0 220 180 40 24 0 Negatives Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 229 250 180 70 25 0 210 180 30 26 0 230 180 50 27 0 230 180 50 28 0 260 180 80 29 0 280 180 100 30 0 33 180 -147 30 1 210 230 -20 30 2 180 230 -50 30 3 270 230 40 31 3 190 230 -40 31 4 190 230 -40 31 5 210 230 -20 31 6 210 230 -20 31 7 300 230 70 32 7 230 230 0 32 7 280 230 50 33 7 320 230 90 34 7 200 230 -30 34 8 210 230 -20 34 9 210 230 -20 34 10 280 230 50 35 10 220 230 -10 35 11 210 230 -20 35 12 250 230 20 36 12 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 230 200 230 -30 36 13 310 230 80 37 13 300 230 70 38 13 230 230 0 38 13 200 230 -30 38 14 220 230 -10 38 15 250 230 20 39 15 210 230 -20 39 16 230 230 0 39 16 230 230 0 39 16 260 230 30 40 16 280 230 50 41 16 33 230 -197 41 17 180 210 -30 41 18 270 210 60 42 18 190 210 -20 42 19 190 210 -20 42 20 210 210 0 42 20 210 210 0 42 20 300 210 90 43 20 230 210 20 44 20 280 210 70 45 20 320 210 110 46 20 200 210 -10 46 21 210 210 0 46 21 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 231 210 210 0 46 21 280 210 70 47 21 220 210 10 48 21 210 210 0 48 21 250 210 40 49 21 200 210 -10 49 22 310 210 100 50 22 300 210 90 51 22 230 210 20 52 22 200 210 -10 52 23 220 210 10 53 23 250 210 40 54 23 210 210 0 54 23 230 210 20 55 23 230 210 20 56 23 260 210 50 57 23 280 210 70 58 23 33 210 -177 58 24 270 180 90 59 24 190 180 10 60 24 190 180 10 61 24 210 180 30 62 24 210 180 30 63 24 300 180 120 64 24 230 180 50 65 24 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 232 280 180 100 66 24 320 180 140 67 24 200 180 20 68 24 210 180 30 69 24 210 180 30 70 24 280 180 100 71 24 220 180 40 72 24 210 180 30 73 24 250 180 70 74 24 200 180 20 75 24 310 180 130 76 24 300 180 120 77 24 230 180 50 78 24 200 180 20 79 24 220 180 40 80 24 250 180 70 81 24 210 180 30 82 24 230 180 50 83 24 230 180 50 84 24 260 180 80 85 24 280 180 100 86 24 33 180 -147 86 25 190 270 -80 86 26 190 270 -80 86 27 210 270 -60 86 28 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 233 210 270 -60 86 29 300 270 30 87 29 230 270 -40 87 30 280 270 10 88 30 320 270 50 89 30 200 270 -70 89 31 210 270 -60 89 32 210 270 -60 89 33 280 270 10 90 33 220 270 -50 90 34 210 270 -60 90 35 250 270 -20 90 36 200 270 -70 90 37 310 270 40 91 37 300 270 30 92 37 230 270 -40 92 38 200 270 -70 92 39 220 270 -50 92 40 250 270 -20 92 41 210 270 -60 92 42 230 270 -40 92 43 230 270 -40 92 44 260 270 -10 92 45 280 270 10 93 45 33 270 -237 93 46 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 234 190 190 0 93 46 210 190 20 94 46 210 190 20 95 46 300 190 110 96 46 230 190 40 97 46 280 190 90 98 46 320 190 130 99 46 200 190 10 100 46 210 190 20 101 46 210 190 20 102 46 280 190 90 103 46 220 190 30 104 46 210 190 20 105 46 250 190 60 106 46 200 190 10 107 46 310 190 120 108 46 300 190 110 109 46 230 190 40 110 46 200 190 10 111 46 220 190 30 112 46 250 190 60 113 46 210 190 20 114 46 230 190 40 115 46 230 190 40 116 46 260 190 70 117 46 280 190 90 118 46 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 235 33 190 -157 118 47 210 190 20 119 47 210 190 20 120 47 300 190 110 121 47 230 190 40 122 47 280 190 90 123 47 320 190 130 124 47 200 190 10 125 47 210 190 20 126 47 210 190 20 127 47 280 190 90 128 47 220 190 30 129 47 210 190 20 130 47 250 190 60 131 47 200 190 10 132 47 310 190 120 133 47 300 190 110 134 47 230 190 40 135 47 200 190 10 136 47 220 190 30 137 47 250 190 60 138 47 210 190 20 139 47 230 190 40 140 47 230 190 40 141 47 260 190 70 142 47 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 236 280 190 90 143 47 33 190 -157 143 48 210 210 0 143 48 300 210 90 144 48 230 210 20 145 48 280 210 70 146 48 320 210 110 147 48 200 210 -10 147 49 210 210 0 147 49 210 210 0 147 49 280 210 70 148 49 220 210 10 149 49 210 210 0 149 49 250 210 40 150 49 200 210 -10 150 50 310 210 100 151 50 300 210 90 152 50 230 210 20 153 50 200 210 -10 153 51 220 210 10 154 51 250 210 40 155 51 210 210 0 155 51 230 210 20 156 51 230 210 20 157 51 260 210 50 158 51 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 237 280 210 70 159 51 33 210 -177 159 52 300 210 90 160 52 230 210 20 161 52 280 210 70 162 52 320 210 110 163 52 200 210 -10 163 53 210 210 0 163 53 210 210 0 163 53 280 210 70 164 53 220 210 10 165 53 210 210 0 165 53 250 210 40 166 53 200 210 -10 166 54 310 210 100 167 54 300 210 90 168 54 230 210 20 169 54 200 210 -10 169 55 220 210 10 170 55 250 210 40 171 55 210 210 0 171 55 230 210 20 172 55 230 210 20 173 55 260 210 50 174 55 280 210 70 175 55 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 238 33 210 -177 175 56 230 300 -70 175 57 280 300 -20 175 58 320 300 20 176 58 200 300 -100 176 59 210 300 -90 176 60 210 300 -90 176 61 280 300 -20 176 62 220 300 -80 176 63 210 300 -90 176 64 250 300 -50 176 65 200 300 -100 176 66 310 300 10 177 66 300 300 0 177 66 230 300 -70 177 67 200 300 -100 177 68 220 300 -80 177 69 250 300 -50 177 70 210 300 -90 177 71 230 300 -70 177 72 230 300 -70 177 73 260 300 -40 177 74 280 300 -20 177 75 33 300 -267 177 76 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 239 280 230 50 178 76 320 230 90 179 76 200 230 -30 179 77 210 230 -20 179 78 210 230 -20 179 79 280 230 50 180 79 220 230 -10 180 80 210 230 -20 180 81 250 230 20 181 81 200 230 -30 181 82 310 230 80 182 82 300 230 70 183 82 230 230 0 183 82 200 230 -30 183 83 220 230 -10 183 84 250 230 20 184 84 210 230 -20 184 85 230 230 0 184 85 230 230 0 184 85 260 230 30 185 85 280 230 50 186 85 33 230 -197 186 86 320 280 40 187 86 200 280 -80 187 87 210 280 -70 187 88 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 240 210 280 -70 187 89 280 280 0 187 89 220 280 -60 187 90 210 280 -70 187 91 250 280 -30 187 92 200 280 -80 187 93 310 280 30 188 93 300 280 20 189 93 230 280 -50 189 94 200 280 -80 189 95 220 280 -60 189 96 250 280 -30 189 97 210 280 -70 189 98 230 280 -50 189 99 230 280 -50 189 100 260 280 -20 189 101 280 280 0 189 101 33 280 -247 189 102 200 320 -120 189 103 210 320 -110 189 104 210 320 -110 189 105 280 320 -40 189 106 220 320 -100 189 107 210 320 -110 189 108 250 320 -70 189 109 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 241 200 320 -120 189 110 310 320 -10 189 111 300 320 -20 189 112 230 320 -90 189 113 200 320 -120 189 114 220 320 -100 189 115 250 320 -70 189 116 210 320 -110 189 117 230 320 -90 189 118 230 320 -90 189 119 260 320 -60 189 120 280 320 -40 189 121 33 320 -287 189 122 210 200 10 190 122 210 200 10 191 122 280 200 80 192 122 220 200 20 193 122 210 200 10 194 122 250 200 50 195 122 200 200 0 195 122 310 200 110 196 122 300 200 100 197 122 230 200 30 198 122 200 200 0 198 122 220 200 20 199 122 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 242 250 200 50 200 122 210 200 10 201 122 230 200 30 202 122 230 200 30 203 122 260 200 60 204 122 280 200 80 205 122 33 200 -167 205 123 210 210 0 205 123 280 210 70 206 123 220 210 10 207 123 210 210 0 207 123 250 210 40 208 123 200 210 -10 208 124 310 210 100 209 124 300 210 90 210 124 230 210 20 211 124 200 210 -10 211 125 220 210 10 212 125 250 210 40 213 125 210 210 0 213 125 230 210 20 214 125 230 210 20 215 125 260 210 50 216 125 280 210 70 217 125 33 210 -177 217 126 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 243 280 210 70 218 126 220 210 10 219 126 210 210 0 219 126 250 210 40 220 126 200 210 -10 220 127 310 210 100 221 127 300 210 90 222 127 230 210 20 223 127 200 210 -10 223 128 220 210 10 224 128 250 210 40 225 128 210 210 0 225 128 230 210 20 226 128 230 210 20 227 128 260 210 50 228 128 280 210 70 229 128 33 210 -177 229 129 220 280 -60 229 130 210 280 -70 229 131 250 280 -30 229 132 200 280 -80 229 133 310 280 30 230 133 300 280 20 231 133 230 280 -50 231 134 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 244 200 280 -80 231 135 220 280 -60 231 136 250 280 -30 231 137 210 280 -70 231 138 230 280 -50 231 139 230 280 -50 231 140 260 280 -20 231 141 280 280 0 231 141 33 280 -247 231 142 210 220 -10 231 143 250 220 30 232 143 200 220 -20 232 144 310 220 90 233 144 300 220 80 234 144 230 220 10 235 144 200 220 -20 235 145 220 220 0 235 145 250 220 30 236 145 210 220 -10 236 146 230 220 10 237 146 230 220 10 238 146 260 220 40 239 146 280 220 60 240 146 33 220 -187 240 147 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 245 250 210 40 241 147 200 210 -10 241 148 310 210 100 242 148 300 210 90 243 148 230 210 20 244 148 200 210 -10 244 149 220 210 10 245 149 250 210 40 246 149 210 210 0 246 149 230 210 20 247 149 230 210 20 248 149 260 210 50 249 149 280 210 70 250 149 33 210 -177 250 150 200 250 -50 250 151 310 250 60 251 151 300 250 50 252 151 230 250 -20 252 152 200 250 -50 252 153 220 250 -30 252 154 250 250 0 252 154 210 250 -40 252 155 230 250 -20 252 156 230 250 -20 252 157 260 250 10 253 157 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 246 280 250 30 254 157 33 250 -217 254 158 310 200 110 255 158 300 200 100 256 158 230 200 30 257 158 200 200 0 257 158 220 200 20 258 158 250 200 50 259 158 210 200 10 260 158 230 200 30 261 158 230 200 30 262 158 260 200 60 263 158 280 200 80 264 158 33 200 -167 264 159 300 310 -10 264 160 230 310 -80 264 161 200 310 -110 264 162 220 310 -90 264 163 250 310 -60 264 164 210 310 -100 264 165 230 310 -80 264 166 230 310 -80 264 167 260 310 -50 264 168 280 310 -30 264 169 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 247 33 310 -277 264 170 230 300 -70 264 171 200 300 -100 264 172 220 300 -80 264 173 250 300 -50 264 174 210 300 -90 264 175 230 300 -70 264 176 230 300 -70 264 177 260 300 -40 264 178 280 300 -20 264 179 33 300 -267 264 180 200 230 -30 264 181 220 230 -10 264 182 250 230 20 265 182 210 230 -20 265 183 230 230 0 265 183 230 230 0 265 183 260 230 30 266 183 280 230 50 267 183 33 230 -197 267 184 220 200 20 268 184 250 200 50 269 184 210 200 10 270 184 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 248 230 200 30 271 184 230 200 30 272 184 260 200 60 273 184 280 200 80 274 184 33 200 -167 274 185 250 220 30 275 185 210 220 -10 275 186 230 220 10 276 186 230 220 10 277 186 260 220 40 278 186 280 220 60 279 186 33 220 -187 279 187 210 250 -40 279 188 230 250 -20 279 189 230 250 -20 279 190 260 250 10 280 190 280 250 30 281 190 33 250 -217 281 191 230 210 20 282 191 230 210 20 283 191 260 210 50 284 191 280 210 70 285 191 33 210 -177 285 192 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 249 230 230 0 285 192 260 230 30 286 192 280 230 50 287 192 33 230 -197 287 193 260 230 30 288 193 280 230 50 289 193 33 230 -197 289 194 280 260 20 290 194 33 260 -227 290 195 33 280 -247 290 196 S Statistic = 290 - 196 = 94 ============================================ Tied Group Value Members 1 180 2 2 230 5 3 210 7 4 190 2 5 300 2 6 280 3 7 200 3 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 250 8 220 2 9 250 2 ============================================ Time Period Observations 9/11/2007 1 10/24/2007 1 11/6/2007 1 12/4/2007 1 1/9/2008 1 2/21/2008 1 3/11/2008 1 4/9/2008 1 5/13/2008 1 6/17/2008 1 8/12/2008 1 10/28/2008 1 11/12/2008 1 12/23/2008 1 1/6/2009 1 2/18/2009 1 3/11/2009 1 4/8/2009 1 5/6/2009 1 6/9/2009 1 7/13/2009 1 8/19/2009 1 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 251 9/15/2009 1 10/15/2009 1 11/10/2009 1 1/6/2010 1 2/18/2010 1 3/24/2010 1 4/27/2010 1 5/25/2010 1 6/22/2010 1 7/28/2010 1 8/18/2010 1 There are 0 time periods with multiple data ============================================ A = 1320 B=0 C = 282 D=0 E = 84 F=0 a = 74976 b = 294624 c = 2112 Group Variance = 4092 Z-Score = 1.45384 Comparison Level at 95% confidence level = 1.65463 (upward trend) 1.45384 <= 1.65463 indicating no evidence of an upward trend Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 252 Summary: An upward trend was observed in the perchlorate data for Rialto Well 6. Thus, only the most recent results were used in the HHRA to determine the exposure point concentration, in order to not include results from years in which the perchlorate concentration in this well was increasing, and to better represent current and future well concentrations for this analyte. Based on the trend analysis results, the range of sample dates used in the HHRA for this analyte and well were from 11 September 2007 to October 2010, which includes 33 sample results. Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 253 B.5 Perchlorate, District Well 11 Time-series plot of all perchlorate data from District Well 11 that is part of the human health risk assessment database: ChemStat software output of Mann-Kendall upward trend analysis for the same dataset: Mann-Kendall Trend Analysis Parameter: PERCHLORATE Location: WEST VALLEY WATER DISTRICT Original Data (Not Transformed) Non-Detects Replaced with Detection Limit 95% Confidence Level ============================================ Xj Xk Xj - Xk Positives Negatives ND<5 ND<5 0 0 0 ND<5 ND<5 0 0 0 ND<4 ND<5 -1 0 1 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 254 ND<5 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 2.8 3.8 4 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 0 -1 -1 -1 -1 -1 -1 -2.2 -1.2 -1 -0.4 -0.5 -1.2 -0.3 -0.7 -4 -0.3 0.3 -0.2 -0.2 1.5 -0.1 -0.7 -1.1 -1.3 -0.9 -1.5 -1.1 -1.1 -1.4 -2.1 -1.3 -2.6 -1 -1 -1 -1 -1 -1 -1 -0.6 7 8 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 3 4 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 17 18 19 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 39 39 ND<5 ND<4 ND<5 ND<4 ND<4 ND<4 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 0 -1 0 -1 -1 -1 4 4 4 4 4 4 39 40 40 41 42 43 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 255 ND<4 ND<4 ND<4 2.8 3.8 4 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 -1 -1 -1 -2.2 -1.2 -1 -0.4 -0.5 -1.2 -0.3 -0.7 -4 -0.3 0.3 -0.2 -0.2 1.5 -0.1 -0.7 -1.1 -1.3 -0.9 -1.5 -1.1 -1.1 -1.4 -2.1 -1.3 -2.6 -1 -1 -1 -1 -1 -1 -1 -0.6 7 8 4 4 4 4 4 4 4 4 4 4 4 4 4 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 7 8 44 45 46 47 48 49 50 51 52 53 54 55 56 56 57 58 58 59 60 61 62 63 64 65 66 67 68 69 70 71 72 73 74 75 76 77 78 78 78 ND<4 ND<5 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 2.8 3.8 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 -1 0 -1 -1 -1 -1 -1 -1 -2.2 -1.2 8 8 8 8 8 8 8 8 8 8 79 79 80 81 82 83 84 85 86 87 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 256 4 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 -1 -0.4 -0.5 -1.2 -0.3 -0.7 -4 -0.3 0.3 -0.2 -0.2 1.5 -0.1 -0.7 -1.1 -1.3 -0.9 -1.5 -1.1 -1.1 -1.4 -2.1 -1.3 -2.6 -1 -1 -1 -1 -1 -1 -1 -0.6 7 8 8 8 8 8 8 8 8 8 9 9 9 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 11 12 88 89 90 91 92 93 94 95 95 96 97 97 98 99 100 101 102 103 104 105 106 107 108 109 110 111 112 113 114 115 116 117 117 117 ND<5 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 2.8 3.8 4 4.6 4.5 3.8 4.7 4.3 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 1 0 0 0 0 0 0 -1.2 -0.2 0 0.6 0.5 -0.2 0.7 0.3 13 13 13 13 13 13 13 13 13 13 14 15 15 16 17 117 117 117 117 117 117 117 118 119 119 119 119 120 120 120 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 257 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 -3 0.7 1.3 0.8 0.8 2.5 0.9 0.3 -0.1 -0.3 0.1 -0.5 -0.1 -0.1 -0.4 -1.1 -0.3 -1.6 0 0 0 0 0 0 0 0.4 8 9 17 18 19 20 21 22 23 24 24 24 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 26 27 28 121 121 121 121 121 121 121 121 122 123 123 124 125 126 127 128 129 130 130 130 130 130 130 130 130 130 130 130 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 2.8 3.8 4 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 -1 -1 -1 -1 -1 -1 -2.2 -1.2 -1 -0.4 -0.5 -1.2 -0.3 -0.7 -4 -0.3 0.3 -0.2 -0.2 1.5 -0.1 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 28 29 29 29 30 30 131 132 133 134 135 136 137 138 139 140 141 142 143 144 145 146 146 147 148 148 149 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 258 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 -0.7 -1.1 -1.3 -0.9 -1.5 -1.1 -1.1 -1.4 -2.1 -1.3 -2.6 -1 -1 -1 -1 -1 -1 -1 -0.6 7 8 30 30 30 30 30 30 30 30 30 30 30 30 30 30 30 30 30 30 30 31 32 150 151 152 153 154 155 156 157 158 159 160 161 162 163 164 165 166 167 168 168 168 ND<4 ND<4 ND<4 ND<4 ND<4 2.8 3.8 4 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 0 0 0 0 0 -1.2 -0.2 0 0.6 0.5 -0.2 0.7 0.3 -3 0.7 1.3 0.8 0.8 2.5 0.9 0.3 -0.1 -0.3 0.1 -0.5 -0.1 -0.1 -0.4 32 32 32 32 32 32 32 32 33 34 34 35 36 36 37 38 39 40 41 42 43 43 43 44 44 44 44 44 168 168 168 168 168 169 170 170 170 170 171 171 171 172 172 172 172 172 172 172 172 173 174 174 175 176 177 178 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 259 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 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Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 260 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 0 0.4 8 9 59 60 61 62 194 194 194 194 ND<4 ND<4 ND<4 2.8 3.8 4 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 0 0 0 -1.2 -0.2 0 0.6 0.5 -0.2 0.7 0.3 -3 0.7 1.3 0.8 0.8 2.5 0.9 0.3 -0.1 -0.3 0.1 -0.5 -0.1 -0.1 -0.4 -1.1 -0.3 -1.6 0 0 0 0 0 0 0 0.4 8 9 62 62 62 62 62 62 63 64 64 65 66 66 67 68 69 70 71 72 73 73 73 74 74 74 74 74 74 74 74 74 74 74 74 74 74 74 75 76 77 194 194 194 195 196 196 196 196 197 197 197 198 198 198 198 198 198 198 198 199 200 200 201 202 203 204 205 206 207 207 207 207 207 207 207 207 207 207 207 ND<4 ND<4 2.8 3.8 4 ND<4 ND<4 ND<4 ND<4 ND<4 0 0 -1.2 -0.2 0 77 77 77 77 77 207 207 208 209 209 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 261 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 0.6 0.5 -0.2 0.7 0.3 -3 0.7 1.3 0.8 0.8 2.5 0.9 0.3 -0.1 -0.3 0.1 -0.5 -0.1 -0.1 -0.4 -1.1 -0.3 -1.6 0 0 0 0 0 0 0 0.4 8 9 78 79 79 80 81 81 82 83 84 85 86 87 88 88 88 89 89 89 89 89 89 89 89 89 89 89 89 89 89 89 90 91 92 209 209 210 210 210 211 211 211 211 211 211 211 211 212 213 213 214 215 216 217 218 219 220 220 220 220 220 220 220 220 220 220 220 ND<4 2.8 3.8 4 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 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3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 0.5 -2.8 0.9 1.5 1 1 2.7 1.1 0.5 0.1 -0.1 0.3 -0.3 0.1 0.1 -0.2 -0.9 -0.1 -1.4 0.2 0.2 0.2 0.2 0.2 0.2 0.2 0.6 8.2 9.2 160 160 161 162 163 164 165 166 167 168 168 169 169 170 171 171 171 171 171 172 173 174 175 176 177 178 179 180 181 248 249 249 249 249 249 249 249 249 249 250 250 251 251 251 252 253 254 255 255 255 255 255 255 255 255 255 255 255 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 0.6 0.5 -0.2 0.7 0.3 -3 0.7 1.3 0.8 0.8 2.5 0.9 0.3 -0.1 -0.3 0.1 -0.5 -0.1 -0.1 -0.4 182 183 183 184 185 185 186 187 188 189 190 191 192 192 192 193 193 193 193 193 255 255 256 256 256 257 257 257 257 257 257 257 257 258 259 259 260 261 262 263 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 265 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4 4 4 4 4 4 4 4 4 4 4 4 4 -1.1 -0.3 -1.6 0 0 0 0 0 0 0 0.4 8 9 193 193 193 193 193 193 193 193 193 193 194 195 196 264 265 266 266 266 266 266 266 266 266 266 266 266 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 -0.1 -0.8 0.1 -0.3 -3.6 0.1 0.7 0.2 0.2 1.9 0.3 -0.3 -0.7 -0.9 -0.5 -1.1 -0.7 -0.7 -1 -1.7 -0.9 -2.2 -0.6 -0.6 -0.6 -0.6 -0.6 -0.6 -0.6 -0.2 7.4 8.4 196 196 197 197 197 198 199 200 201 202 203 203 203 203 203 203 203 203 203 203 203 203 203 203 203 203 203 203 203 203 204 205 267 268 268 269 270 270 270 270 270 270 270 271 272 273 274 275 276 277 278 279 280 281 282 283 284 285 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6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 1.8 0.2 -0.4 -0.8 -1 -0.6 -1.2 -0.8 -0.8 -1.1 -1.8 -1 -2.3 -0.7 -0.7 -0.7 -0.7 -0.7 -0.7 -0.7 -0.3 7.3 8.3 284 285 285 285 285 285 285 285 285 285 285 285 285 285 285 285 285 285 285 285 285 286 287 357 357 358 359 360 361 362 363 364 365 366 367 368 369 370 371 372 373 374 375 376 376 376 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 -0.5 -0.5 1.2 -0.4 -1 -1.4 -1.6 -1.2 -1.8 -1.4 -1.4 -1.7 -2.4 -1.6 -2.9 -1.3 -1.3 -1.3 -1.3 -1.3 -1.3 -1.3 -0.9 6.7 7.7 287 287 288 288 288 288 288 288 288 288 288 288 288 288 288 288 288 288 288 288 288 288 288 289 290 377 378 378 379 380 381 382 383 384 385 386 387 388 389 390 391 392 393 394 395 396 397 398 398 398 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 270 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 0 1.7 0.1 -0.5 -0.9 -1.1 -0.7 -1.3 -0.9 -0.9 -1.2 -1.9 -1.1 -2.4 -0.8 -0.8 -0.8 -0.8 -0.8 -0.8 -0.8 -0.4 7.2 8.2 290 291 292 292 292 292 292 292 292 292 292 292 292 292 292 292 292 292 292 292 292 292 293 294 398 398 398 399 400 401 402 403 404 405 406 407 408 409 410 411 412 413 414 415 416 417 417 417 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 1.7 0.1 -0.5 -0.9 -1.1 -0.7 -1.3 -0.9 -0.9 -1.2 -1.9 -1.1 -2.4 -0.8 -0.8 -0.8 -0.8 -0.8 -0.8 -0.8 -0.4 7.2 8.2 295 296 296 296 296 296 296 296 296 296 296 296 296 296 296 296 296 296 296 296 296 297 298 417 417 418 419 420 421 422 423 424 425 426 427 428 429 430 431 432 433 434 435 436 436 436 4.9 6.5 -1.6 298 437 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 271 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 -2.2 -2.6 -2.8 -2.4 -3 -2.6 -2.6 -2.9 -3.6 -2.8 -4.1 -2.5 -2.5 -2.5 -2.5 -2.5 -2.5 -2.5 -2.1 5.5 6.5 298 298 298 298 298 298 298 298 298 298 298 298 298 298 298 298 298 298 298 299 300 438 439 440 441 442 443 444 445 446 447 448 449 450 451 452 453 454 455 456 456 456 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 -0.6 -1 -1.2 -0.8 -1.4 -1 -1 -1.3 -2 -1.2 -2.5 -0.9 -0.9 -0.9 -0.9 -0.9 -0.9 -0.9 -0.5 7.1 8.1 300 300 300 300 300 300 300 300 300 300 300 300 300 300 300 300 300 300 300 301 302 457 458 459 460 461 462 463 464 465 466 467 468 469 470 471 472 473 474 475 475 475 3.9 3.7 4.1 3.5 3.9 3.9 4.3 4.3 4.3 4.3 4.3 4.3 -0.4 -0.6 -0.2 -0.8 -0.4 -0.4 302 302 302 302 302 302 476 477 478 479 480 481 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 272 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 -0.7 -1.4 -0.6 -1.9 -0.3 -0.3 -0.3 -0.3 -0.3 -0.3 -0.3 0.1 7.7 8.7 302 302 302 302 302 302 302 302 302 302 302 303 304 305 482 483 484 485 486 487 488 489 490 491 492 492 492 492 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 -0.2 0.2 -0.4 0 0 -0.3 -1 -0.2 -1.5 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.5 8.1 9.1 305 306 306 306 306 306 306 306 306 307 308 309 310 311 312 313 314 315 316 493 493 494 494 494 495 496 497 498 498 498 498 498 498 498 498 498 498 498 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 0.4 -0.2 0.2 0.2 -0.1 -0.8 0 -1.3 0.3 0.3 0.3 0.3 0.3 0.3 0.3 317 317 318 319 319 319 319 319 320 321 322 323 324 325 326 498 499 499 499 500 501 501 502 502 502 502 502 502 502 502 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 273 4.4 12 13 3.7 3.7 3.7 0.7 8.3 9.3 327 328 329 502 502 502 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 -0.6 -0.2 -0.2 -0.5 -1.2 -0.4 -1.7 -0.1 -0.1 -0.1 -0.1 -0.1 -0.1 -0.1 0.3 7.9 8.9 329 329 329 329 329 329 329 329 329 329 329 329 329 329 330 331 332 503 504 505 506 507 508 509 510 511 512 513 514 515 516 516 516 516 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 0.4 0.4 0.1 -0.6 0.2 -1.1 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.9 8.5 9.5 333 334 335 335 336 336 337 338 339 340 341 342 343 344 345 346 516 516 516 517 517 518 518 518 518 518 518 518 518 518 518 518 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 0 -0.3 -1 -0.2 -1.5 0.1 0.1 0.1 0.1 0.1 0.1 346 346 346 346 346 347 348 349 350 351 352 518 519 520 521 522 522 522 522 522 522 522 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 274 ND<4 4.4 12 13 3.9 3.9 3.9 3.9 0.1 0.5 8.1 9.1 353 354 355 356 522 522 522 522 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 -0.3 -1 -0.2 -1.5 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.5 8.1 9.1 356 356 356 356 357 358 359 360 361 362 363 364 365 366 523 524 525 526 526 526 526 526 526 526 526 526 526 526 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 3.6 3.6 3.6 3.6 3.6 3.6 3.6 3.6 3.6 3.6 3.6 3.6 3.6 -0.7 0.1 -1.2 0.4 0.4 0.4 0.4 0.4 0.4 0.4 0.8 8.4 9.4 366 367 367 368 369 370 371 372 373 374 375 376 377 527 527 528 528 528 528 528 528 528 528 528 528 528 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 2.9 2.9 2.9 2.9 2.9 2.9 2.9 2.9 2.9 2.9 2.9 2.9 0.8 -0.5 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.5 9.1 10.1 378 378 379 380 381 382 383 384 385 386 387 388 528 529 529 529 529 529 529 529 529 529 529 529 2.4 3.7 ND<4 3.7 ND<4 3.7 -1.3 0.3 0.3 388 389 390 530 530 530 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 275 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 0.3 0.3 0.3 0.3 0.3 0.7 8.3 9.3 391 392 393 394 395 396 397 398 530 530 530 530 530 530 530 530 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 1.6 1.6 1.6 1.6 1.6 1.6 1.6 2 9.6 10.6 399 400 401 402 403 404 405 406 407 408 530 530 530 530 530 530 530 530 530 530 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 0 0 0 0 0 0 0.4 8 9 408 408 408 408 408 408 409 410 411 530 530 530 530 530 530 530 530 530 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 0 0 0 0 0 0.4 8 9 411 411 411 411 411 412 413 414 530 530 530 530 530 530 530 530 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 0 0 0 0 0.4 8 9 414 414 414 414 415 416 417 530 530 530 530 530 530 530 417 417 417 530 530 530 ND<4 ND<4 0 ND<4 ND<4 0 ND<4 ND<4 0 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 276 4.4 12 13 ND<4 0.4 ND<4 8 ND<4 9 418 419 420 530 530 530 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 ND<4 0 0 0.4 8 9 420 420 421 422 423 530 530 530 530 530 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 0 0.4 8 9 423 424 425 426 530 530 530 530 4.4 12 13 ND<4 0.4 ND<4 8 ND<4 9 427 428 429 530 530 530 12 13 4.4 4.4 7.6 8.6 430 431 530 530 13 12 1 432 530 S Statistic = 432 - 530 = -98 ============================================ Tied Group Value Members 1 5 4 2 4 15 3 3.8 2 4 4.7 2 5 4.3 2 6 4.8 2 7 3.9 3 8 3.7 2 ============================================ Time Period Observations 3/26/1999 1 5/19/1999 1 8/2/1999 1 9/24/1999 1 3/9/2000 1 3/16/2001 1 7/28/2001 1 6/28/2002 1 12/20/2002 1 8/8/2003 1 2/26/2004 1 5/20/2004 1 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 277 6/28/2004 1 7/21/2004 1 8/13/2004 1 9/30/2004 1 10/27/2004 1 12/29/2004 1 1/7/2005 1 3/21/2005 1 4/26/2005 1 5/25/2005 1 6/15/2005 1 6/16/2005 1 7/21/2005 1 9/29/2005 1 10/14/2005 1 11/30/2005 1 1/20/2006 1 3/22/2006 1 5/18/2006 1 6/29/2006 1 7/19/2006 1 9/15/2006 1 10/20/2006 1 11/3/2006 1 2/28/2007 1 3/20/2007 1 4/24/2007 1 6/15/2007 1 9/27/2007 1 11/30/2007 1 9/26/2008 1 3/6/2009 1 4/22/2009 1 6/29/2010 1 7/7/2010 1 There are 0 time periods with multiple data ============================================ A = 7662 B=0 C = 2760 D=0 E = 238 F=0 a = 214038 b = 875610 c = 4324 Group Variance = 11465.3 Z-Score = -0.905896 Comparison Level at 95% confidence level = 1.65463 (upward trend) -0.905896 <= 1.65463 indicating no evidence of an upward trend Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 278 ChemStat software output of Mann-Kendall downward trend analysis for the same dataset: Mann-Kendall Trend Analysis Parameter: PERCHLORATE Location: WEST VALLEY WATER DISTRICT Original Data (Not Transformed) Non-Detects Replaced with Detection Limit 95% Confidence Level ============================================ Xj Xk Xj - Xk Positives Negatives ND<5 ND<5 0 0 0 ND<5 ND<5 0 0 0 ND<4 ND<5 -1 0 1 ND<5 ND<5 0 0 1 ND<4 ND<5 -1 0 2 ND<4 ND<5 -1 0 3 ND<4 ND<5 -1 0 4 ND<4 ND<5 -1 0 5 ND<4 ND<5 -1 0 6 ND<4 ND<5 -1 0 7 2.8 ND<5 -2.2 0 8 3.8 ND<5 -1.2 0 9 4 ND<5 -1 0 10 4.6 ND<5 -0.4 0 11 4.5 ND<5 -0.5 0 12 3.8 ND<5 -1.2 0 13 4.7 ND<5 -0.3 0 14 4.3 ND<5 -0.7 0 15 ND<1 ND<5 -4 0 16 4.7 ND<5 -0.3 0 17 5.3 ND<5 0.3 1 17 4.8 ND<5 -0.2 1 18 4.8 ND<5 -0.2 1 19 6.5 ND<5 1.5 2 19 4.9 ND<5 -0.1 2 20 4.3 ND<5 -0.7 2 21 3.9 ND<5 -1.1 2 22 3.7 ND<5 -1.3 2 23 4.1 ND<5 -0.9 2 24 3.5 ND<5 -1.5 2 25 3.9 ND<5 -1.1 2 26 3.9 ND<5 -1.1 2 27 3.6 ND<5 -1.4 2 28 2.9 ND<5 -2.1 2 29 3.7 ND<5 -1.3 2 30 2.4 ND<5 -2.6 2 31 ND<4 ND<5 -1 2 32 ND<4 ND<5 -1 2 33 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 279 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 -1 -1 -1 -1 -1 -0.6 7 8 2 2 2 2 2 2 3 4 34 35 36 37 38 39 39 39 ND<5 ND<4 ND<5 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 2.8 3.8 4 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 0 -1 0 -1 -1 -1 -1 -1 -1 -2.2 -1.2 -1 -0.4 -0.5 -1.2 -0.3 -0.7 -4 -0.3 0.3 -0.2 -0.2 1.5 -0.1 -0.7 -1.1 -1.3 -0.9 -1.5 -1.1 -1.1 -1.4 -2.1 -1.3 -2.6 -1 -1 -1 -1 -1 -1 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 39 40 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 56 57 58 58 59 60 61 62 63 64 65 66 67 68 69 70 71 72 73 74 75 76 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 280 ND<4 4.4 12 13 ND<5 ND<5 ND<5 ND<5 -1 -0.6 7 8 6 6 7 8 77 78 78 78 ND<4 ND<5 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 2.8 3.8 4 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 -1 0 -1 -1 -1 -1 -1 -1 -2.2 -1.2 -1 -0.4 -0.5 -1.2 -0.3 -0.7 -4 -0.3 0.3 -0.2 -0.2 1.5 -0.1 -0.7 -1.1 -1.3 -0.9 -1.5 -1.1 -1.1 -1.4 -2.1 -1.3 -2.6 -1 -1 -1 -1 -1 -1 -1 -0.6 7 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 9 9 9 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 11 12 79 79 80 81 82 83 84 85 86 87 88 89 90 91 92 93 94 95 95 96 97 97 98 99 100 101 102 103 104 105 106 107 108 109 110 111 112 113 114 115 116 117 117 117 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 281 ND<5 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 2.8 3.8 4 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 1 0 0 0 0 0 0 -1.2 -0.2 0 0.6 0.5 -0.2 0.7 0.3 -3 0.7 1.3 0.8 0.8 2.5 0.9 0.3 -0.1 -0.3 0.1 -0.5 -0.1 -0.1 -0.4 -1.1 -0.3 -1.6 0 0 0 0 0 0 0 0.4 8 9 13 13 13 13 13 13 13 13 13 13 14 15 15 16 17 17 18 19 20 21 22 23 24 24 24 25 25 25 25 25 25 25 25 25 25 25 25 25 25 25 26 27 28 117 117 117 117 117 117 117 118 119 119 119 119 120 120 120 121 121 121 121 121 121 121 121 122 123 123 124 125 126 127 128 129 130 130 130 130 130 130 130 130 130 130 130 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 -1 -1 -1 -1 -1 -1 28 28 28 28 28 28 131 132 133 134 135 136 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 282 2.8 3.8 4 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 ND<5 -2.2 -1.2 -1 -0.4 -0.5 -1.2 -0.3 -0.7 -4 -0.3 0.3 -0.2 -0.2 1.5 -0.1 -0.7 -1.1 -1.3 -0.9 -1.5 -1.1 -1.1 -1.4 -2.1 -1.3 -2.6 -1 -1 -1 -1 -1 -1 -1 -0.6 7 8 28 28 28 28 28 28 28 28 28 28 29 29 29 30 30 30 30 30 30 30 30 30 30 30 30 30 30 30 30 30 30 30 30 30 31 32 137 138 139 140 141 142 143 144 145 146 146 147 148 148 149 150 151 152 153 154 155 156 157 158 159 160 161 162 163 164 165 166 167 168 168 168 ND<4 ND<4 ND<4 ND<4 ND<4 2.8 3.8 4 4.6 4.5 3.8 4.7 4.3 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 0 0 0 0 0 -1.2 -0.2 0 0.6 0.5 -0.2 0.7 0.3 32 32 32 32 32 32 32 32 33 34 34 35 36 168 168 168 168 168 169 170 170 170 170 171 171 171 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 283 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 -3 0.7 1.3 0.8 0.8 2.5 0.9 0.3 -0.1 -0.3 0.1 -0.5 -0.1 -0.1 -0.4 -1.1 -0.3 -1.6 0 0 0 0 0 0 0 0.4 8 9 36 37 38 39 40 41 42 43 43 43 44 44 44 44 44 44 44 44 44 44 44 44 44 44 44 45 46 47 172 172 172 172 172 172 172 172 173 174 174 175 176 177 178 179 180 181 181 181 181 181 181 181 181 181 181 181 ND<4 ND<4 ND<4 ND<4 2.8 3.8 4 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 ND<4 ND<4 ND<4 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4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 -1.2 -0.2 0 0.6 0.5 -0.2 0.7 0.3 -3 0.7 1.3 0.8 0.8 2.5 0.9 0.3 -0.1 -0.3 0.1 -0.5 -0.1 -0.1 -0.4 -1.1 -0.3 -1.6 0 0 0 0 0 0 0 0.4 8 9 92 92 92 93 94 94 95 96 96 97 98 99 100 101 102 103 103 103 104 104 104 104 104 104 104 104 104 104 104 104 104 104 104 105 106 107 221 222 222 222 222 223 223 223 224 224 224 224 224 224 224 224 225 226 226 227 228 229 230 231 232 233 233 233 233 233 233 233 233 233 233 233 2.8 3.8 4 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 -1.2 -0.2 0 0.6 0.5 -0.2 0.7 0.3 -3 0.7 1.3 0.8 0.8 107 107 107 108 109 109 110 111 111 112 113 114 115 234 235 235 235 235 236 236 236 237 237 237 237 237 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 287 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 2.5 0.9 0.3 -0.1 -0.3 0.1 -0.5 -0.1 -0.1 -0.4 -1.1 -0.3 -1.6 0 0 0 0 0 0 0 0.4 8 9 116 117 118 118 118 119 119 119 119 119 119 119 119 119 119 119 119 119 119 119 120 121 122 237 237 237 238 239 239 240 241 242 243 244 245 246 246 246 246 246 246 246 246 246 246 246 3.8 4 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 1 1.2 1.8 1.7 1 1.9 1.5 -1.8 1.9 2.5 2 2 3.7 2.1 1.5 1.1 0.9 1.3 0.7 1.1 1.1 0.8 0.1 0.9 -0.4 1.2 123 124 125 126 127 128 129 129 130 131 132 133 134 135 136 137 138 139 140 141 142 143 144 145 145 146 246 246 246 246 246 246 246 247 247 247 247 247 247 247 247 247 247 247 247 247 247 247 247 247 248 248 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 288 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 2.8 1.2 1.2 1.2 1.2 1.2 1.2 1.6 9.2 10.2 147 148 149 150 151 152 153 154 155 248 248 248 248 248 248 248 248 248 4 4.6 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 0.2 0.8 0.7 0 0.9 0.5 -2.8 0.9 1.5 1 1 2.7 1.1 0.5 0.1 -0.1 0.3 -0.3 0.1 0.1 -0.2 -0.9 -0.1 -1.4 0.2 0.2 0.2 0.2 0.2 0.2 0.2 0.6 8.2 9.2 156 157 158 158 159 160 160 161 162 163 164 165 166 167 168 168 169 169 170 171 171 171 171 171 172 173 174 175 176 177 178 179 180 181 248 248 248 248 248 248 249 249 249 249 249 249 249 249 249 250 250 251 251 251 252 253 254 255 255 255 255 255 255 255 255 255 255 255 4.6 4.5 3.8 4.7 4.3 4 4 4 4 4 0.6 0.5 -0.2 0.7 0.3 182 183 183 184 185 255 255 256 256 256 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 289 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 -3 0.7 1.3 0.8 0.8 2.5 0.9 0.3 -0.1 -0.3 0.1 -0.5 -0.1 -0.1 -0.4 -1.1 -0.3 -1.6 0 0 0 0 0 0 0 0.4 8 9 185 186 187 188 189 190 191 192 192 192 193 193 193 193 193 193 193 193 193 193 193 193 193 193 193 194 195 196 257 257 257 257 257 257 257 257 258 259 259 260 261 262 263 264 265 266 266 266 266 266 266 266 266 266 266 266 4.5 3.8 4.7 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 -0.1 -0.8 0.1 -0.3 -3.6 0.1 0.7 0.2 0.2 1.9 0.3 -0.3 -0.7 -0.9 -0.5 -1.1 -0.7 -0.7 -1 -1.7 -0.9 196 196 197 197 197 198 199 200 201 202 203 203 203 203 203 203 203 203 203 203 203 267 268 268 269 270 270 270 270 270 270 270 271 272 273 274 275 276 277 278 279 280 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 290 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 -2.2 -0.6 -0.6 -0.6 -0.6 -0.6 -0.6 -0.6 -0.2 7.4 8.4 203 203 203 203 203 203 203 203 203 204 205 281 282 283 284 285 286 287 288 289 289 289 3.8 4.7 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4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 3.8 1 2.7 1.1 0.5 0.1 -0.1 0.3 -0.3 0.1 0.1 -0.2 -0.9 -0.1 -1.4 0.2 0.2 0.2 0.2 0.2 0.2 0.2 0.6 8.2 9.2 220 221 222 223 224 224 225 225 226 227 227 227 227 227 228 229 230 231 232 233 234 235 236 237 312 312 312 312 312 313 313 314 314 314 315 316 317 318 318 318 318 318 318 318 318 318 318 318 4.3 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 -0.4 -3.7 0 0.6 0.1 0.1 1.8 0.2 -0.4 -0.8 -1 -0.6 -1.2 -0.8 -0.8 -1.1 -1.8 -1 -2.3 -0.7 -0.7 -0.7 -0.7 -0.7 -0.7 237 237 237 238 239 240 241 242 242 242 242 242 242 242 242 242 242 242 242 242 242 242 242 242 242 319 320 320 320 320 320 320 320 321 322 323 324 325 326 327 328 329 330 331 332 333 334 335 336 337 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 292 ND<4 4.4 12 13 4.7 4.7 4.7 4.7 -0.7 -0.3 7.3 8.3 242 242 243 244 338 339 339 339 ND<1 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 -3.3 0.4 1 0.5 0.5 2.2 0.6 0 -0.4 -0.6 -0.2 -0.8 -0.4 -0.4 -0.7 -1.4 -0.6 -1.9 -0.3 -0.3 -0.3 -0.3 -0.3 -0.3 -0.3 0.1 7.7 8.7 244 245 246 247 248 249 250 250 250 250 250 250 250 250 250 250 250 250 250 250 250 250 250 250 250 251 252 253 340 340 340 340 340 340 340 340 341 342 343 344 345 346 347 348 349 350 351 352 353 354 355 356 357 357 357 357 4.7 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 3.7 4.3 3.8 3.8 5.5 3.9 3.3 2.9 2.7 3.1 2.5 2.9 2.9 2.6 1.9 2.7 254 255 256 257 258 259 260 261 262 263 264 265 266 267 268 269 357 357 357 357 357 357 357 357 357 357 357 357 357 357 357 357 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 293 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 ND<1 1.4 3 3 3 3 3 3 3 3.4 11 12 270 271 272 273 274 275 276 277 278 279 280 357 357 357 357 357 357 357 357 357 357 357 5.3 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 4.7 0.6 0.1 0.1 1.8 0.2 -0.4 -0.8 -1 -0.6 -1.2 -0.8 -0.8 -1.1 -1.8 -1 -2.3 -0.7 -0.7 -0.7 -0.7 -0.7 -0.7 -0.7 -0.3 7.3 8.3 281 282 283 284 285 285 285 285 285 285 285 285 285 285 285 285 285 285 285 285 285 285 285 285 286 287 357 357 357 357 357 358 359 360 361 362 363 364 365 366 367 368 369 370 371 372 373 374 375 376 376 376 4.8 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 -0.5 -0.5 1.2 -0.4 -1 -1.4 -1.6 -1.2 -1.8 -1.4 -1.4 287 287 288 288 288 288 288 288 288 288 288 377 378 378 379 380 381 382 383 384 385 386 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 294 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 5.3 -1.7 -2.4 -1.6 -2.9 -1.3 -1.3 -1.3 -1.3 -1.3 -1.3 -1.3 -0.9 6.7 7.7 288 288 288 288 288 288 288 288 288 288 288 288 289 290 387 388 389 390 391 392 393 394 395 396 397 398 398 398 4.8 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 0 1.7 0.1 -0.5 -0.9 -1.1 -0.7 -1.3 -0.9 -0.9 -1.2 -1.9 -1.1 -2.4 -0.8 -0.8 -0.8 -0.8 -0.8 -0.8 -0.8 -0.4 7.2 8.2 290 291 292 292 292 292 292 292 292 292 292 292 292 292 292 292 292 292 292 292 292 292 293 294 398 398 398 399 400 401 402 403 404 405 406 407 408 409 410 411 412 413 414 415 416 417 417 417 6.5 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 1.7 0.1 -0.5 -0.9 -1.1 -0.7 -1.3 -0.9 -0.9 -1.2 295 296 296 296 296 296 296 296 296 296 417 417 418 419 420 421 422 423 424 425 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 295 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 4.8 -1.9 -1.1 -2.4 -0.8 -0.8 -0.8 -0.8 -0.8 -0.8 -0.8 -0.4 7.2 8.2 296 296 296 296 296 296 296 296 296 296 296 297 298 426 427 428 429 430 431 432 433 434 435 436 436 436 4.9 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 -1.6 -2.2 -2.6 -2.8 -2.4 -3 -2.6 -2.6 -2.9 -3.6 -2.8 -4.1 -2.5 -2.5 -2.5 -2.5 -2.5 -2.5 -2.5 -2.1 5.5 6.5 298 298 298 298 298 298 298 298 298 298 298 298 298 298 298 298 298 298 298 298 299 300 437 438 439 440 441 442 443 444 445 446 447 448 449 450 451 452 453 454 455 456 456 456 4.3 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 -0.6 -1 -1.2 -0.8 -1.4 -1 -1 -1.3 -2 -1.2 -2.5 -0.9 -0.9 300 300 300 300 300 300 300 300 300 300 300 300 300 457 458 459 460 461 462 463 464 465 466 467 468 469 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 296 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4.9 4.9 4.9 4.9 4.9 4.9 4.9 4.9 -0.9 -0.9 -0.9 -0.9 -0.9 -0.5 7.1 8.1 300 300 300 300 300 300 301 302 470 471 472 473 474 475 475 475 3.9 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 4.3 -0.4 -0.6 -0.2 -0.8 -0.4 -0.4 -0.7 -1.4 -0.6 -1.9 -0.3 -0.3 -0.3 -0.3 -0.3 -0.3 -0.3 0.1 7.7 8.7 302 302 302 302 302 302 302 302 302 302 302 302 302 302 302 302 302 303 304 305 476 477 478 479 480 481 482 483 484 485 486 487 488 489 490 491 492 492 492 492 3.7 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 -0.2 0.2 -0.4 0 0 -0.3 -1 -0.2 -1.5 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.5 8.1 9.1 305 306 306 306 306 306 306 306 306 307 308 309 310 311 312 313 314 315 316 493 493 494 494 494 495 496 497 498 498 498 498 498 498 498 498 498 498 498 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 297 4.1 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 0.4 -0.2 0.2 0.2 -0.1 -0.8 0 -1.3 0.3 0.3 0.3 0.3 0.3 0.3 0.3 0.7 8.3 9.3 317 317 318 319 319 319 319 319 320 321 322 323 324 325 326 327 328 329 498 499 499 499 500 501 501 502 502 502 502 502 502 502 502 502 502 502 3.5 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 4.1 -0.6 -0.2 -0.2 -0.5 -1.2 -0.4 -1.7 -0.1 -0.1 -0.1 -0.1 -0.1 -0.1 -0.1 0.3 7.9 8.9 329 329 329 329 329 329 329 329 329 329 329 329 329 329 330 331 332 503 504 505 506 507 508 509 510 511 512 513 514 515 516 516 516 516 3.9 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 0.4 0.4 0.1 -0.6 0.2 -1.1 0.5 0.5 0.5 0.5 0.5 0.5 0.5 333 334 335 335 336 336 337 338 339 340 341 342 343 516 516 516 517 517 518 518 518 518 518 518 518 518 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 298 4.4 12 13 3.5 3.5 3.5 0.9 8.5 9.5 344 345 346 518 518 518 3.9 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 0 -0.3 -1 -0.2 -1.5 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.5 8.1 9.1 346 346 346 346 346 347 348 349 350 351 352 353 354 355 356 518 519 520 521 522 522 522 522 522 522 522 522 522 522 522 3.6 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 3.9 -0.3 -1 -0.2 -1.5 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.5 8.1 9.1 356 356 356 356 357 358 359 360 361 362 363 364 365 366 523 524 525 526 526 526 526 526 526 526 526 526 526 526 2.9 3.7 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 3.6 3.6 3.6 3.6 3.6 3.6 3.6 3.6 3.6 3.6 3.6 3.6 3.6 -0.7 0.1 -1.2 0.4 0.4 0.4 0.4 0.4 0.4 0.4 0.8 8.4 9.4 366 367 367 368 369 370 371 372 373 374 375 376 377 527 527 528 528 528 528 528 528 528 528 528 528 528 3.7 2.9 0.8 378 528 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 299 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 2.9 2.9 2.9 2.9 2.9 2.9 2.9 2.9 2.9 2.9 2.9 -0.5 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.5 9.1 10.1 378 379 380 381 382 383 384 385 386 387 388 529 529 529 529 529 529 529 529 529 529 529 2.4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 3.7 -1.3 0.3 0.3 0.3 0.3 0.3 0.3 0.3 0.7 8.3 9.3 388 389 390 391 392 393 394 395 396 397 398 530 530 530 530 530 530 530 530 530 530 530 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 1.6 1.6 1.6 1.6 1.6 1.6 1.6 2 9.6 10.6 399 400 401 402 403 404 405 406 407 408 530 530 530 530 530 530 530 530 530 530 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 0 0 0 0 0 0 0.4 8 9 408 408 408 408 408 408 409 410 411 530 530 530 530 530 530 530 530 530 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 0 0 0 0 0 411 411 411 411 411 530 530 530 530 530 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 300 4.4 12 13 ND<4 0.4 ND<4 8 ND<4 9 412 413 414 530 530 530 ND<4 ND<4 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 0 0 0 0 0.4 8 9 414 414 414 414 415 416 417 530 530 530 530 530 530 530 ND<4 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 ND<4 ND<4 0 0 0 0.4 8 9 417 417 417 418 419 420 530 530 530 530 530 530 ND<4 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 ND<4 0 0 0.4 8 9 420 420 421 422 423 530 530 530 530 530 ND<4 4.4 12 13 ND<4 ND<4 ND<4 ND<4 0 0.4 8 9 423 424 425 426 530 530 530 530 4.4 12 13 ND<4 0.4 ND<4 8 ND<4 9 427 428 429 530 530 530 12 13 4.4 4.4 7.6 8.6 430 431 530 530 13 12 1 432 530 S Statistic = 432 - 530 = -98 ============================================ Tied Group Value Members 1 5 4 2 4 15 3 3.8 2 4 4.7 2 5 4.3 2 6 4.8 2 7 3.9 3 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 301 8 3.7 2 ============================================ Time Period Observations 3/26/1999 1 5/19/1999 1 8/2/1999 1 9/24/1999 1 3/9/2000 1 3/16/2001 1 7/28/2001 1 6/28/2002 1 12/20/2002 1 8/8/2003 1 2/26/2004 1 5/20/2004 1 6/28/2004 1 7/21/2004 1 8/13/2004 1 9/30/2004 1 10/27/2004 1 12/29/2004 1 1/7/2005 1 3/21/2005 1 4/26/2005 1 5/25/2005 1 6/15/2005 1 6/16/2005 1 7/21/2005 1 9/29/2005 1 10/14/2005 1 11/30/2005 1 1/20/2006 1 3/22/2006 1 5/18/2006 1 6/29/2006 1 7/19/2006 1 9/15/2006 1 10/20/2006 1 11/3/2006 1 2/28/2007 1 3/20/2007 1 4/24/2007 1 6/15/2007 1 9/27/2007 1 11/30/2007 1 9/26/2008 1 3/6/2009 1 4/22/2009 1 6/29/2010 1 7/7/2010 1 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 302 There are 0 time periods with multiple data ============================================ A = 7662 B=0 C = 2760 D=0 E = 238 F=0 a = 214038 b = 875610 c = 4324 Group Variance = 11465.3 Z-Score = -0.905896 Comparison Level at 95% confidence level = -1.65463 (downward trend) -0.905896 >= -1.65463 indicating no evidence of a downward trend Summary: No trending was observed; all results from the HHRA database for this well and analyte were used in the determination of exposure point concentrations. Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 303 B.6 Trichloroethene, Rialto Well 6 Time-series plot of all trichloroethene data from Rialto Well 6 that is part of the human health risk assessment database: ChemStat software output of Mann-Kendall upward trend analysis for the same dataset: Mann-Kendall Trend Analysis Parameter: TRICHLOROETHYLENE Location: RIALTO-CITY Original Data (Not Transformed) Non-Detects Replaced with Detection Limit 95% Confidence Level ============================================ Xj Xk Xj - Xk Positives Negatives ND<0.5 ND<0.5 0 0 0 Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 304 ND<0.5 ND<0.5 1 ND<0.5 0.5 1.6 ND<0.5 1.1 2.5 ND<0.5 2 4 ND<0.5 3.5 5.3 ND<0.5 4.8 6.3 ND<0.5 5.8 0 1 2 3 4 5 6 0 0 0 0 0 0 0 0 ND<0.5 ND<0.5 1 ND<0.5 0.5 1.6 ND<0.5 1.1 2.5 ND<0.5 2 4 ND<0.5 3.5 5.3 ND<0.5 4.8 6.3 ND<0.5 5.8 0 7 8 9 10 11 12 6 0 0 0 0 0 0 0 1 1.6 2.5 4 5.3 6.3 ND<0.5 ND<0.5 ND<0.5 ND<0.5 ND<0.5 ND<0.5 0.5 1.1 2 3.5 4.8 5.8 13 14 15 16 17 18 0 0 0 0 0 0 1.6 2.5 4 5.3 6.3 1 1 1 1 1 0.6 1.5 3 4.3 5.3 19 20 21 22 23 0 0 0 0 0 2.5 4 5.3 6.3 1.6 1.6 1.6 1.6 0.9 2.4 3.7 4.7 24 25 26 27 0 0 0 0 4 5.3 6.3 2.5 2.5 2.5 1.5 2.8 3.8 28 29 30 0 0 0 5.3 6.3 4 4 1.3 2.3 31 32 0 0 6.3 5.3 1 33 0 S Statistic = 33 - 0 = 33 Comparing at 95% confidence level (upward trend) Probability of obtaining S >= 33 is 7.25e-005 S > 0 and 7.25e-005 < 0.05 indicating an upward trend Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 305 Summary: An upward trend exists for trichloroethene in Rialto Well 6 which includes the most recent sampling results. Thus, all results in the HHRA database for this well and analyte were used in the calculation of the HHRA exposure point concentrations. Because the trend includes the most recent data available, the maximum concentration detected in the samples collected from Rialto Well 6 was used as the exposure point concentration for this well in the HHRA. Human Health Risk Assessment Report, Wellhead Treatment System Project West Valley Water District and City of Rialto G:\IS-Group\Admin\Job\10\1089040.00_WVWD\09-Reports\HHRA Rpt\appendices\AppxB_Trend_Analysis_Text_040111.docx 306 Appendix C Pro UCL Version 4.00.05 Files A B C D E F G H General UCL Statistics for Data Sets with Non-Detects 1 J K L User Selected Options 2 From File 3 ProUCL_Input.wst Full Precision OFF Confidence Coefficient 95% Number of Bootstrap Operations 2000 4 5 6 I 7 8 9 Fl_6 10 General Statistics 11 12 Number of Valid Observations 6 Number of Distinct Observations 3 13 14 Raw Statistics Log-transformed Statistics 15 16 Minimum 300 Minimum of Log Data 5.704 Maximum 400 Maximum of Log Data 5.991 Mean 323.3 17 Median 300 18 SD of log Data 0.118 SD 40.82 19 20 Mean of log Data 5.773 Coefficient of Variation 0.126 Skewness 1.783 21 22 23 24 25 26 Warning: There are only 3 Distinct Values in this data There are insufficient Distinct Values to perform some GOF tests and bootstrap methods. Those methods will return a 'N/A' value on your output display! 27 28 29 30 It is necessary to have 4 or more Distinct Values to compute bootstrap methods. However, results obtained using 4 to 9 distinct values may not be reliable. It is recommended to have 10-15 or more observations for accurate and meaningful bootstrap results. 31 32 33 Warning: A sample size of 'n' = 6 may not adequate enough to compute meaningful and reliable test statistics and estimates! 34 35 36 It is suggested to collect at least 8 to 10 observations using these statistical methods! If possible compute and collect Data Quality Objectives (DQO) based sample size and analytical results. 37 Relevant UCL Statistics 38 39 40 41 42 Normal Distribution Test Lognormal Distribution Test Shapiro Wilk Test Statistic 0.685 Shapiro Wilk Critical Value 0.788 Shapiro Wilk Test Statistic 0.692 Shapiro Wilk Critical Value 0.788 Data not Normal at 5% Significance Level Data not Lognormal at 5% Significance Level Assuming Normal Distribution Assuming Lognormal Distribution 43 44 45 46 47 48 95% Student's-t UCL 356.9 95% UCLs (Adjusted for Skewness) 95% H-UCL 359.1 95% Chebyshev (MVUE) UCL 391.3 95% Adjusted-CLT UCL (Chen-1995) 363.7 97.5% Chebyshev (MVUE) UCL 420.8 95% Modified-t UCL (Johnson-1978) 358.9 99% Chebyshev (MVUE) UCL 478.6 49 50 51 52 53 Gamma Distribution Test Data Distribution k star (bias corrected) 41.22 Theta Star 7.844 MLE of Mean 323.3 Data do not follow a Discernable Distribution (0.05) A 54 B C D E F MLE of Standard Deviation 50.36 G H I J K L nu star 494.6 55 Approximate Chi Square Value (.05) 444.1 56 Nonparametric Statistics Adjusted Level of Significance 0.0122 57 95% CLT UCL 350.7 Adjusted Chi Square Value 426.6 58 95% Jackknife UCL 356.9 95% Standard Bootstrap UCL N/A 95% Bootstrap-t UCL N/A Anderson-Darling 5% Critical Value 0.696 95% Hall's Bootstrap UCL N/A Kolmogorov-Smirnov Test Statistic 0.404 95% Percentile Bootstrap UCL N/A 95% BCA Bootstrap UCL N/A 59 Anderson-Darling Test Statistic 1.015 60 61 62 Kolmogorov-Smirnov 5% Critical Value 0.332 63 Data not Gamma Distributed at 5% Significance Level 64 95% Chebyshev(Mean, Sd) UCL 396 97.5% Chebyshev(Mean, Sd) UCL 427.4 65 Assuming Gamma Distribution 66 99% Chebyshev(Mean, Sd) UCL 489.2 95% Approximate Gamma UCL 360.2 67 95% Adjusted Gamma UCL 374.9 68 69 Potential UCL to Use 70 Use 95% Student's-t UCL 356.9 or 95% Modified-t UCL 358.9 71 72 Note: Suggestions regarding the selection of a 95% UCL are provided to help the user to select the most appropriate 95% UCL. 73 These recommendations are based upon the results of the simulation studies summarized in Singh, Singh, and Iaci (2002) 74 and Singh and Singh (2003). For additional insight, the user may want to consult a statistician. 75 76 77 78 Perc_11 79 General Statistics 80 81 82 Number of Valid Data 47 Number of Detected Data Number of Distinct Detected Data 21 Number of Non-Detect Data 19 Percent Non-Detects 40.43% 83 28 84 85 86 87 88 Raw Statistics Minimum Detected 2.4 Minimum Detected 0.875 Maximum Detected 13 Maximum Detected 2.565 Mean of Detected 4.743 Mean of Detected 1.483 SD of Detected 2.337 SD of Detected 0.355 Minimum Non-Detect 1 Minimum Non-Detect 0 Maximum Non-Detect 5 Maximum Non-Detect 1.609 Number treated as Non-Detect 43 89 90 91 Log-transformed Statistics 92 93 94 95 Note: Data have multiple DLs - Use of KM Method is recommended For all methods (except KM, DL/2, and ROS Methods), Observations < Largest ND are treated as NDs Number treated as Detected 4 Single DL Non-Detect Percentage 91.49% 96 UCL Statistics 97 98 99 100 101 Normal Distribution Test with Detected Values Only Lognormal Distribution Test with Detected Values Only Shapiro Wilk Test Statistic 0.614 5% Shapiro Wilk Critical Value 0.924 Shapiro Wilk Test Statistic 0.816 5% Shapiro Wilk Critical Value 0.924 Data not Normal at 5% Significance Level Data not Lognormal at 5% Significance Level Assuming Normal Distribution Assuming Lognormal Distribution 102 103 104 105 106 DL/2 Substitution Method DL/2 Substitution Method Mean 3.645 Mean 1.153 SD 2.256 SD 0.532 A B C D E 95% DL/2 (t) UCL F 4.197 Maximum Likelihood Estimate(MLE) Method N/A 107 G H I J K 95% H-Stat (DL/2) UCL L 4.239 108 109 Log ROS Method MLE yields a negative mean 110 111 112 113 Mean in Log Scale 1.351 SD in Log Scale 0.35 Mean in Original Scale 4.146 SD in Original Scale 1.989 95% t UCL 4.633 95% Percentile Bootstrap UCL 4.648 95% BCA Bootstrap UCL 4.808 114 115 116 117 Gamma Distribution Test with Detected Values Only 118 Data Distribution Test with Detected Values Only k star (bias corrected) 119 6.191 Data do not follow a Discernable Distribution (0.05) Theta Star 0.766 nu star 346.7 A-D Test Statistic 2.487 5% A-D Critical Value 0.747 Kaplan-Meier (KM) Method K-S Test Statistic 0.747 Mean 4.21 5% K-S Critical Value 0.166 SD 1.928 SE of Mean 0.297 120 121 122 123 124 125 126 Nonparametric Statistics Data not Gamma Distributed at 5% Significance Level 127 128 Assuming Gamma Distribution 129 Gamma ROS Statistics using Extrapolated Data 130 131 132 133 134 135 136 137 138 141 142 4.709 4.698 95% KM (jackknife) UCL 4.696 Minimum 1.825 95% KM (bootstrap t) UCL 5.049 Maximum 13 95% KM (BCA) UCL 4.781 Mean 4.726 95% KM (Percentile Bootstrap) UCL 4.732 Median 4.4 95% KM (Chebyshev) UCL 5.504 SD 1.963 97.5% KM (Chebyshev) UCL 6.063 k star 7.613 99% KM (Chebyshev) UCL 7.162 Theta star 0.621 Nu star 715.6 Potential UCLs to Use AppChi2 654.5 95% KM (t) UCL 4.709 95% Gamma Approximate UCL 5.167 95% KM (% Bootstrap) UCL 4.732 95% Adjusted Gamma UCL 5.182 139 140 95% KM (t) UCL 95% KM (z) UCL Note: DL/2 is not a recommended method. 143 Note: Suggestions regarding the selection of a 95% UCL are provided to help the user to select the most appropriate 95% UCL. 144 These recommendations are based upon the results of the simulation studies summarized in Singh, Maichle, and Lee (2006). 145 For additional insight, the user may want to consult a statistician. 146 147 148 149 Perc_6 150 General Statistics 151 152 Number of Valid Observations 33 Number of Distinct Observations 14 153 154 155 156 157 158 159 Raw Statistics Log-transformed Statistics Minimum 33 Minimum of Log Data 3.497 Maximum 320 Maximum of Log Data 5.768 Mean 228.3 Median 220 SD 52.35 Mean of log Data 5.385 SD of log Data 0.375 A 160 B C D E F Coefficient of Variation 0.229 G H I J K L Skewness -1.228 161 162 Relevant UCL Statistics 163 Normal Distribution Test 164 165 166 167 Lognormal Distribution Test Shapiro Wilk Test Statistic 0.875 Shapiro Wilk Test Statistic 0.578 Shapiro Wilk Critical Value 0.931 Shapiro Wilk Critical Value 0.931 Data not Normal at 5% Significance Level Data not Lognormal at 5% Significance Level Assuming Normal Distribution Assuming Lognormal Distribution 168 169 95% Student's-t UCL 243.7 170 95% UCLs (Adjusted for Skewness) 171 172 173 95% H-UCL 264.4 95% Chebyshev (MVUE) UCL 301.6 95% Adjusted-CLT UCL (Chen-1995) 241.2 97.5% Chebyshev (MVUE) UCL 331.1 95% Modified-t UCL (Johnson-1978) 243.4 99% Chebyshev (MVUE) UCL 389 174 Gamma Distribution Test 175 Data Distribution k star (bias corrected) 10.1 176 Data do not follow a Discernable Distribution (0.05) Theta Star 22.6 177 MLE of Mean 228.3 178 MLE of Standard Deviation 71.82 179 nu star 666.7 180 Approximate Chi Square Value (.05) 607.8 181 Nonparametric Statistics Adjusted Level of Significance 0.0419 182 Adjusted Chi Square Value 604.9 183 95% CLT UCL 243.3 95% Jackknife UCL 243.7 95% Standard Bootstrap UCL 242.8 184 Anderson-Darling Test Statistic 2.383 185 186 187 Anderson-Darling 5% Critical Value 0.747 95% Hall's Bootstrap UCL 242.9 Kolmogorov-Smirnov Test Statistic 0.225 95% Percentile Bootstrap UCL 242.1 Kolmogorov-Smirnov 5% Critical Value 0.153 188 Data not Gamma Distributed at 5% Significance Level 189 95% Bootstrap-t UCL 242.1 95% BCA Bootstrap UCL 240.6 95% Chebyshev(Mean, Sd) UCL 268 97.5% Chebyshev(Mean, Sd) UCL 285.2 190 Assuming Gamma Distribution 191 99% Chebyshev(Mean, Sd) UCL 319 95% Approximate Gamma UCL 250.4 192 95% Adjusted Gamma UCL 251.6 193 194 Potential UCL to Use 195 Use 95% Student's-t UCL 243.7 or 95% Modified-t UCL 243.4 196 197 Note: Suggestions regarding the selection of a 95% UCL are provided to help the user to select the most appropriate 95% UCL. 198 These recommendations are based upon the results of the simulation studies summarized in Singh, Singh, and Iaci (2002) 199 and Singh and Singh (2003). For additional insight, the user may want to consult a statistician. 200 201 202 203 NO3-N_6 204 General Statistics 205 206 Number of Valid Observations 5 Number of Distinct Observations 3 207 208 209 210 211 212 Raw Statistics Log-transformed Statistics Minimum 2500 Minimum of Log Data 7.824 Maximum 2955 Maximum of Log Data 7.991 Mean 2727 Median 2727 Mean of log Data 7.91 SD of log Data 0.0591 A B C D E 213 214 F SD 160.7 G H I J K L Coefficient of Variation 0.0589 Skewness -0.000934 215 216 217 Warning: There are only 3 Distinct Values in this data 218 219 220 There are insufficient Distinct Values to perform some GOF tests and bootstrap methods. Those methods will return a 'N/A' value on your output display! 221 222 223 224 It is necessary to have 4 or more Distinct Values to compute bootstrap methods. However, results obtained using 4 to 9 distinct values may not be reliable. It is recommended to have 10-15 or more observations for accurate and meaningful bootstrap results. 225 226 227 Warning: A sample size of 'n' = 5 may not adequate enough to compute meaningful and reliable test statistics and estimates! 228 229 230 It is suggested to collect at least 8 to 10 observations using these statistical methods! If possible compute and collect Data Quality Objectives (DQO) based sample size and analytical results. 231 Relevant UCL Statistics 232 233 234 235 236 Normal Distribution Test Lognormal Distribution Test Shapiro Wilk Test Statistic 0.883 Shapiro Wilk Test Statistic 0.882 Shapiro Wilk Critical Value 0.762 Shapiro Wilk Critical Value 0.762 Data appear Normal at 5% Significance Level Data appear Lognormal at 5% Significance Level Assuming Normal Distribution Assuming Lognormal Distribution 237 238 239 240 241 242 95% Student's-t UCL 2880 95% UCLs (Adjusted for Skewness) 95% H-UCL N/A 95% Chebyshev (MVUE) UCL 3041 95% Adjusted-CLT UCL (Chen-1995) 2845 97.5% Chebyshev (MVUE) UCL 3177 95% Modified-t UCL (Johnson-1978) 2880 99% Chebyshev (MVUE) UCL 3444 243 244 245 Gamma Distribution Test k star (bias corrected) 143.7 MLE of Mean 2727 247 MLE of Standard Deviation 227.5 nu star 1437 249 250 251 252 Approximate Chi Square Value (.05) 1350 Adjusted Level of Significance 0.0086 Adjusted Chi Square Value 1313 255 256 257 258 261 262 95% CLT UCL 2845 95% Jackknife UCL 2880 N/A 95% Bootstrap-t UCL N/A Anderson-Darling 5% Critical Value 0.678 95% Hall's Bootstrap UCL N/A Kolmogorov-Smirnov Test Statistic 0.307 95% Percentile Bootstrap UCL N/A 95% BCA Bootstrap UCL N/A Anderson-Darling Test Statistic 0.517 Kolmogorov-Smirnov 5% Critical Value 0.357 Data appear Gamma Distributed at 5% Significance Level 95% Chebyshev(Mean, Sd) UCL 3041 97.5% Chebyshev(Mean, Sd) UCL 3176 259 260 Nonparametric Statistics 95% Standard Bootstrap UCL 253 254 Data appear Normal at 5% Significance Level Theta Star 18.98 246 248 Data Distribution Assuming Gamma Distribution 99% Chebyshev(Mean, Sd) UCL 3442 95% Approximate Gamma UCL 2903 95% Adjusted Gamma UCL 2986 263 264 265 Potential UCL to Use Use 95% Student's-t UCL 2880 A 266 B C D E F G H I J K Note: Suggestions regarding the selection of a 95% UCL are provided to help the user to select the most appropriate 95% UCL. L These recommendations are based upon the results of the simulation studies summarized in Singh, Singh, and Iaci (2002) 267 and Singh and Singh (2003). For additional insight, the user may want to consult a statistician. 268 269 270 271 NO3-N_11 272 General Statistics 273 274 Number of Valid Observations 33 Number of Distinct Observations 18 275 276 Raw Statistics Log-transformed Statistics Minimum 5455 Minimum of Log Data 8.604 Maximum 10909 Maximum of Log Data 9.297 277 278 Mean 8359 Mean of log Data 9.018 Median 8636 SD of log Data 0.171 279 280 SD 1318 281 282 Coefficient of Variation 0.158 Skewness -0.651 283 284 Relevant UCL Statistics 285 286 287 288 289 Normal Distribution Test Lognormal Distribution Test Shapiro Wilk Test Statistic 0.942 Shapiro Wilk Test Statistic 0.903 Shapiro Wilk Critical Value 0.931 Shapiro Wilk Critical Value 0.931 Data appear Normal at 5% Significance Level Data not Lognormal at 5% Significance Level Assuming Normal Distribution Assuming Lognormal Distribution 290 291 292 293 294 295 95% Student's-t UCL 8748 95% UCLs (Adjusted for Skewness) 95% Adjusted-CLT UCL (Chen-1995) 8709 95% Modified-t UCL (Johnson-1978) 8744 95% H-UCL 8818 95% Chebyshev (MVUE) UCL 9454 97.5% Chebyshev (MVUE) UCL 9925 99% Chebyshev (MVUE) UCL 10850 296 297 298 Gamma Distribution Test k star (bias corrected) 34.23 MLE of Mean 8359 300 MLE of Standard Deviation 1429 nu star 2259 302 303 304 305 Approximate Chi Square Value (.05) 2150 Adjusted Level of Significance 0.0419 Adjusted Chi Square Value 2144 308 309 310 311 Anderson-Darling Test Statistic 0.954 314 315 95% CLT UCL 8737 95% Jackknife UCL 8748 95% Bootstrap-t UCL 8724 Anderson-Darling 5% Critical Value 0.745 95% Hall's Bootstrap UCL 8700 Kolmogorov-Smirnov Test Statistic 0.146 95% Percentile Bootstrap UCL 8733 Kolmogorov-Smirnov 5% Critical Value 0.153 95% BCA Bootstrap UCL 8712 Data follow Appr. Gamma Distribution at 5% Significance Level 95% Chebyshev(Mean, Sd) UCL 9360 97.5% Chebyshev(Mean, Sd) UCL 9792 312 313 Nonparametric Statistics 95% Standard Bootstrap UCL 8727 306 307 Data appear Normal at 5% Significance Level Theta Star 244.2 299 301 Data Distribution Assuming Gamma Distribution 99% Chebyshev(Mean, Sd) UCL 10643 95% Approximate Gamma UCL 8785 95% Adjusted Gamma UCL 8807 316 317 318 Potential UCL to Use Use 95% Student's-t UCL 8748 A 319 320 321 322 B C D E F G H I J K Note: Suggestions regarding the selection of a 95% UCL are provided to help the user to select the most appropriate 95% UCL. These recommendations are based upon the results of the simulation studies summarized in Singh, Singh, and Iaci (2002) and Singh and Singh (2003). For additional insight, the user may want to consult a statistician. L
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