PLANNING FOR THE TEMPORARY DISPOSAL OF DISASTER DEBRIS “WHERE ARE YOU GOING TO PUT IT?” Robert C. Swan 12472 Lake Underhill Road Orlando, FL 32828 Weather related disasters have increased in intensity and occurrence during the past 20 years. Twenty-one of these disasters occurred during the August 1992-May 1997 period with total damages/costs of approximately $90 billion and 911 deaths. In 2003, Hurricane Isabel created over 20 million cubic yards of debris within Virginia alone. Hurricanes Charlie, Frances, Ivan, and Jeanne set new records for vegetative debris within the State of Florida and highlighted the need to identify temporary debris staging and volume reduction sites prior to a potential debris-generating disaster. Palm Beach County alone moved over 2.5 million cubic yards of debris to ten temporary staging sites in 56 days following Hurricanes Frances and Jeanne. Urban population centers continue to grow into areas of high risk for potential property loss due to major debris-generating events such as hurricanes, floods, tornadoes, wildfires, earthquakes and terrorist activities. The costs associated with cleaning up after such events continue to grow at an unprecedented rate, not to mention the associated costs for lost property and wages due to lengthy debris removal and disposal operations. Over $4.3 million reimbursement from FEMA for Hurricane Isabel and over $1.5 million for the California fires. The costs associated with debris removal and disposal operations for the 2004 Florida hurricanes will be in the billions of dollars. This paper addresses the issue of managing the disposal of debris associated with a catastrophic disaster debris-generating event. Emphasis is placed on local and county debris planning and management responsibilities with regard to identifying and permitting potential Temporary Debris Staging and Reduction (TDSR) sites. The first step in developing a comprehensive Debris Management Plan is to determine how much debris will be generated and where will it be disposed of. Current static spreadsheet prediction models and Geographic Information System (GIS) based debris modeling applications are means available to assist in predicting debris quantities and evaluating the impact on existing landfill capacities. In most cases disaster debris must be taken to a temporary staging site for either separation or volume reduction to lessen the impact on critical landfill space. Having pre identified TDSR sites as part of a complete Debris Management Plan will expedite the cleanup process. Most natural disasters generate debris in quantities that will overwhelm existing solid waste management facilities and force communities to use disposal options that otherwise would not be acceptable. Failure to act in a timely manner may impact community health and economic recovery. Debris removal is an important key to timely recovery of business, the viability of neighborhoods and the continuity of government. Unfortunately, the debris management of the marketplace has traditionally been left to chance, market forces, or ad hoc liaisons created in the chaotic aftermath of the event. A sound Debris Management Plan will help a community to overcome these forces resulting in a coordinated approach to expedite the debris removal and disposal effort. A systematic means to identify and classify potential TDSR sites becomes a critical element of the planning process and the results an important appendix to the Debris Management Plan. The first step in identifying TDSR sites is to have a method to predict potential debris quantities. Quantities can be predicted using past experience, or debris modeling methods. The US Army Corps of Engineers, (USACE) develop a spreadsheet debris prediction model following Hurricane Andrew. It was based on factors observed from numerous Gulf of Mexico and Atlantic Ocean Hurricanes. The formula developed by the USACE has a predicted accuracy of + or – 30%. 1 The primary factors utilized are: • Cubic yards of debris generated per household per storm category • Vegetative cover • Commercial density • Precipitation. Household debris includes damage to the house, contents and surrounding shrubs and trees. The vegetative cover includes all trees and shrubbery located along public rights-of-way, parks, and residential areas. Commercial density includes debris generated by damage to business and industrial facilities. Precipitation from very wet storms will cause ground saturation resulting in increased probability of complete trees falling. The model can be used for worst case scenario planning for the subject area. A sample spreadsheet of the USACE Debris Prediction Model for the City of Clearwater, FL is shown on the following page. Note that the formula used is Q= H (C)(V)(B)(S) where • • • • • • Q is the quantity of debris in cubic yards H is the number of single family households C is the storm category factor in cubic yards V is the vegetation characteristic multiplier B is the commercial/business/industrial use multiplier S is the storm precipitation characteristic multiplier The C value is: Category 1=2cy; Category 2=8cy; Category 3=26cy; Category 4=50cy; and Category 5=80 cy The vegetation multipliers are 1.1, 1.3, and 1.5 for light, medium, and heavy vegetation. The commercial multipliers are 1.0, 1.2 and 1.3 for light, medium, and heavy commercial density. The precipitation multiplier is 1.0 for none to light and 1.3 for medium to heavy. The USACE model can also be used to arrive at estimated TDSR site requirements using the following formula: Total volume per acre= 4,840 square yards (sy) x 3.33 yards (y) [Estimated debris pile stack height of 10 feet]. 4,840 x 3.33 = 16,117 cy per acre. If you have an estimate of 2,000,000 cubic yards of debris you will need approximately 124 acres of open space for temporary debris staging and reduction operations. As can be seen the USACE Debris Prediction Model is a static spread sheet that cannot be easily applied after an event. It treats the entire area as being impacted uniformly and was designed for predicting only debris from hurricanes. Geographic Information System (GIS) Debris Management Applications are a major improvement over the USACE Debris Prediction Model. Utilizing the latest in computer technology and available local or county data bases, GIS can manipulate the data to not only predict debris prior to landfall, but estimate quantities by either region, municipal boundaries, or by defining selected areas impacted by the debris generating event. Moreover, GIS applications can also be used for predicting or estimating flooding, tornadoes, and even bomb blast debris quantities. Expanded capabilities also include tracking of debris cleanup following the disaster at street level. Available digital photographs of the area can be utilized to identify potential TDSR sites and data bases can be quickly quarried to determine size and ownership. 2 US ARMY CORPS OF ENGINEERS DEBRIS PREDICTION MODEL Category 1 Hurricane Estimated Debris Quantities Category 2 Hurricane Category 3 Hurricane Clearwater, FL Population: Category 4 Hurricane Category 5 Hurricane 108,787 74-95 MPH Winds 96-110 MPH Winds 111-130 MPH Winds 131-155 MPH Winds 155+ MPH Winds Estimated damage @ 50% of total single family homes Category 1 Single Family Homes Affected Category Factor Vegetation Commercial Density Precipitation 56,802 Category 2 Category 3 Category 4 Category 5 50% C V B S 28,401 2 1.5 1 1.3 28,401 8 1.5 1 1.3 28,401 26 1.5 1 1.3 28,401 50 1.5 1 1.3 28,401 80 1.5 1 1.3 Cubic Yds 110,764 443,056 1,439,931 2,769,098 4,430,556 1.66 640 Cubic Yds Acres Acres Sq. Miles 110,764 7 11 0.0 443,056 27 46 0.1 1,439,931 89 148 0.2 2,769,098 171 285 0.4 4,430,556 274 455 0.7 30.00% 70.00% Cubic Yds Cubic Yds 33,229 77,535 132,917 310,139 431,979 1,007,951 830,729 1,938,368 1,329,167 3,101,389 42.00% 5.00% 15.00% 38.00% Cubic Yds Cubic Yds Cubic Yds Cubic Yds 32,565 3,877 11,630 29,463 130,258 15,507 46,521 117,853 423,340 50,398 151,193 383,022 814,115 96,918 290,755 736,580 1,302,583 155,069 465,208 1,178,528 Q= H(C)(V)(B)(S) Debris Reduction Site Requirements 1 Acre (ac) 10 Feet stack height Total volume per acre Q=H(C)(V)(B)(S) Acres Required Road Buffers, etc. 1 sq. mile = 640 acres 4840 3.3 16117.17 Debris Classification Clean woody debris Mixed C&D Mixed C&D Burnable Soil Metals Landfilled 3 The GIS Debris Management Applications can be a very valuable tool in the management of debris cleanup operations and the preliminary selection of TDSR sites. However, whatever method is used to determine the predicted or actual quantity of debris and the size of the area for staging and reduction, someone must still make a ground reconnaissance and evaluate the site before any debris is transported to the site. An example site investigation form is show below. Temporary Debris Staging and Reductin (Tdsr) Site Investigation Form TEMPORARY DEBRIS STAGING AND REDUCTIN (TDSR) SITE INVESTIGATION FORM DATE SITE NAME SITE ADDRESS SITE COORDINATES SITE DESCRIPTION SITE RECOMMENDED FOR USE: CHARACTERISTIC Public Property In 100 Year Floodplain >200 Acres >100 Acres >50 Acres <50 Acres YES YES NO NO CHARACTERISTIC Surface Drainage Noise Acceptability Smoke Acceptability Suitable Ingress/Egress Suitable in Wet Weather Site Lends Itself to Easy Preparation GOOD FAIR POOR Close to Schools, Hospitals, Residential, Churches Obvious Environmental Concerns Mostly Open/Clear Wetlands/Creeks/Ponds Developed Brownfield Paved Surfaces Already Fenced Adjacent to Airfield On-site Utilities Requires Access Roads/Internal Roads Capable of Handling Large No. of Vehicles Proximity to Major Roadway COMMENTS: VEGETATIVE COVER: NONE LIGHT CLOSEST LANDFILL AND APPROX. DISTANCE: OWNER’S NAME: OWNER’S ADDRESS: PHOTOGRAPHS WERE TAKEN: YES PHOTOGRAPH NUMBERS: MEDIUM DENSE NO SKETCH ON BACK Site Selection Teams Pre-disaster site selection teams should be created using local officials who are familiar with the area. The teams should have engineering and environmental representation. Environmental sensitive areas should be avoided. Examples include wetlands, endangered plants or animals, and critical habits. Historical and archaeological sites should also be avoided. These restrictions are noted on the TDSR Site Investigation Form. 4 The TDSR Site Investigation Form is used to evaluate the suitability of the site for future debris staging and volume reduction operations. If the site meets established acceptance criteria additional steps must be taken before opening the site for operations. Some states have specific guidance that must be followed to get the TDSR site permitted before it can be used. The following is a modified example of the permitting procedures that must be followed in the Commonwealth of Virginia as specified by the Virginia Department of Environmental Quality. Refer to the Virginia Department of Environmental Quality web site at: http://www.deq.virginia.gov/waste/wastepermit11.html for complete instructions. Emergency Debris Permitting Criteria EMERGENCY DEBRIS WASTEPILE PERMITTING CRITERIA This is an application for an emergency permit to dispose of waste generated as the result of natural or manmade disasters. The emergency permit request may be oral or written. If oral, it shall be followed within five days by a written emergency permit application. Oral responses can only be given if the applicant is fully aware of the siting requirements outlined in this application, otherwise a written request must be provided using this application. Mail or fax the written request to the Department of Environmental Quality • • • • • • • • • • • Expected or current emergency Authority or Agency Primary Contact’s Name, Address, City, State, Zip, Phone Number / Fax Number Site Location (latitude/longitude or directions from major roads) Site Name City, State, Zip Owner of Site Owner’s Address, City, State, Zip, Phone Number / Fax Number Approximate size (acres) List expected types of waste Typical treatment, storage and disposal options EMERGENCY DEBRIS WASTEPILE SITING CRITERIA 1. Site Location Map Attached (Not prone to base floods [100 year flood plain, coastal flooding] or inundation. 2. Copy of FEMA Map or Equivalent is attached 3. Site is geologically stable. 4. Site has adequate berm area and terrain to manage leachate release. Not closer than 100 feet from any regularly flowing surface water body or river. 5. 200 feet from any well, spring, or other groundwater source of drinking water. (WETLANDS SHALL NOT BE IMPACTED.) 6. US Fish and Wildlife Service National Wetlands Inventory Map is attached. • Site characteristics • Slopes less than 33% • No springs seeps or other groundwater intrusions • No gas, water, sewage, or electrical or other transmission lines under the site • No existing open dump, unpermitted landfill, lagoon, or similar facility on site. 7. Specific site conditions which may be considered for exemption (applies only to site characteristics) 8. No strip mines, exposed bedrock or quarries present. 9. Fifty-foot firebreak around disposal areas and from all tree lines 10. Does not impact cemeteries (public, private, pet) or culturally sensitive areas. 11. Has ample access for delivery vehicles. 12. Is anticipated waste acceptable for disposal? 5 13. Can the waste be segregated for disposal? 14. Public notice form with required information attached. 15. For pre-selected sites, was a public meeting held? • Public Meeting Location: Date: ______/______ /________ (mm/dd/yyyy) 16. Can the site be closed in accordance with Department standards? Conclusion In conclusion, identification, selection, and permitting of Temporary Debris Staging and Reduction sites are not easy procedures. This is especially true if sites are not identified prior to a major debris-generating event and local solid waste officials are under pressure to expedite the cleanup process. Consequently, local solid waste officials should continually update their Debris Management Plans to insure that current sites are still available and that potential sites are properly evaluated and permitted prior to the next debris-generating event. Are you prepared? References: Federal Emergency Management Agency Public Assistance Debris Management Guide, FEMA 325, April 1999 Virginia Department of Environmental Quality Web site: http://www.deq.virginia.gov/waste/wastepermit11.html 6
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