3/1/2017 LINES OF EVIDENCE FOR EVALUATING POTENTIAL IMPACTS FROM PRODUCED WATER ON GROUNDWATER GWPC UIC Conference, Austin TX John Connor, P.E., P.G., BCEE Lisa Molofsky, P.G. Ileana Rhodes, PhD Ann Smith, P.E., BCEE 22 February 2017 IDENTIFYING A PRODUCED WATER IMPACT Indicators of a Produced Water Impact: Cl - Na +2 TDS CHALLENGE: Increases in Cl, Na, and TDS can be related to causes other than a produced water impact. KEY Geochemical and isotopic methods can POINT: differentiate source(s) of salinity. 2 1 3/1/2017 SOURCES OF PRODUCED WATER IMPACTS: Conventional Wells Unconventional Wells • Spills of flowback water Historical produced water pits • Improperly disposed flowback water Injection wells Improperly plugged and abandoned wells 3 OTHER POSSIBLE CAUSES FOR INCREASED SALINITY IN GROUNDWATER: Other Salinity Sources: Naturally occurring saline groundwater Upconing of deeper water Seawater Halite Solution Road Salt Agriculture Before After Effects of Storm Surge: Louisiana from space before and after hurricane Rita 4 2 3/1/2017 OTHER POSSIBLE CAUSES FOR INCREASED SALINITY IN GROUNDWATER: Changes in salinity within a water supply well over multiple sampling events: Wells may be fed by multiple fractures and/or aquifers. Changes in water usage, well depth and water table can alter mixing dynamics within a well. Source: CSG Geotechnical Services 5 OTHER POSSIBLE CAUSES FOR INCREASED SALINITY IN GROUNDWATER: Composition of Different Waters in Appalachian Basin: Groundwater from restricted flow fractures commonly contains naturally elevated salinity 3 3/1/2017 TIERED EVALUATION APPROACH TO IDENTIFYING SOURCE OF SALINITY Challenge with Investigations: Source(s) of salinity difficult to distinguish Numerous evaluation techniques Best tool dependent on sitespecific characteristics Multiple lines-of-evidence may be needed KEY Match level of effort and complexity of POINT: evaluation to site-specific conditions. 7 TIERED EVALUATION APPROACH Tier 1: Initial Screening Process Is there a salinity impact, and if so, is the source easily identified? Tier 2: Basic Geochemical Analyses Can the major and trace ionic composition identify the source(s)? Tier 3: Advanced Geochemical Analyses Are there advanced isotopic and geochemical analyses that can identify the source(s)? KEY Match level of effort and complexity of POINT: evaluation to site-specific conditions. 8 4 3/1/2017 TIERED EVALUATION APPROACH TIER 1: INITIAL SCREENING PROCESS TDS or Cl Below Applicable Criteria No TDS or Cl < Background Yes No TIER 2: BASIC GEOCHEMICAL ANALYSIS Source of Elevated Salinity Conclusive Yes No Basic Geochemical Analyses Conclusive Yes TIER 3: ADVANCED GEOCHEMICAL ANALYSIS Advanced Geochemical Analyses Conclusive No Yes No Yes NO FURTHER EVALUATION WARRANTED ADDITIONAL DATA/ REVISED METHODS PENDING PUBLICATION: Paquette et al., 2017 (Groundwater Journal) 9 Chloride Conc. TIER 1: INITIAL SCREENING PROCESS BACKGROUND CRITERIA NO INJURY NFA SOURCE CONCLUSIVE MANAGEMENT SOURCE INCONCLUSIVE 10 TIER 2 5 3/1/2017 TIER 2: BASIC GEOCHEMICAL EVALUATION Plots of Major Ions and Trace Ions Basic Visualization Techniques Piper Durov Schoeller Histogram 11 TIER 2: BASIC GEOCHEMICAL EVALUATION Plots of Major Ions and Trace Ions Basic Visualization Techniques Stiff Radial Circular Bar 12 6 3/1/2017 TIER 2: BASIC GEOCHEMICAL EVALUATION Plots of Major Ions and Trace Ions Basic Visualization Techniques K/Cl (Weight Ratio) Bivariate 0.1 Bivariate Background Aquifer Seawater 0.01 Produced water Common Major and Trace Ions: Cl, Na, Ca, Br, K, Mg, I, SO4, Sr, B, Li Common Ion Ratios: 0.001 100 1000 10000 100000 Cl (mg/L) Ions and ion ratios are commonly plotted against chloride. Powerful for identifying mixtures & small contributions from a salinity source. Cl/Br, Na/Cl, K/Cl, Sr/Cl, I/Cl, SO4/Cl, Ca/Mg,(Ca+Mg)/SO4, (Ba+Sr)/Mg 13 TIER 3: ISOTOPES Isotopes of Water: δ2H and δ18O Local Meteoric Water Line (LMWL) represents the δ2H and δ18O values of meteoric water in a localized area. 30 δD-H2O (‰ VSMOW) 20 10 0 -10 -20 Groundwater and Surface Water: -30 -40 Typically plots on LMWL -50 -8 -3 2 δ18O-H2O (‰ VSMOW) 14 7 3/1/2017 TIER 3: ISOTOPES Isotopes of Water: δ2H and δ18O Local Meteoric Water Line (LMWL) represents the δ2H and δ18O values of meteoric water in a localized area. 30 δD-H2O (‰ VSMOW) 20 10 0 -10 Produced Water: -20 Typically formed in evaporative basins, plots below the LMWL -30 -40 -50 -8 -3 2 δ18O-H2O (‰ VSMOW) 15 TIER 3: ISOTOPES Strontium Isotope Ratio: 87Sr/86Sr Application: The 87Sr/86Sr ratio is a good diagnostic parameter Application: in evaluation of potential impacts to GW from produced water or other shallow zones of salinity. 87Sr/86Sr ratio of Marcellus produced water versus other formations in Appalachian Basin. Adapted with permission from: Chapman et al., 2012, ES&T 8 3/1/2017 TIER 3: ISOTOPES δ13C of Dissolved Inorganic Carbon (DIC) δ13C of DIC is highly enriched in Application: some produced water. Application: Marcellus δ13C-DIC values of various waters in the Appalachian Basin. δ13CDIC (‰VPDB) 20 Groundwater 10 0 -10 -20 Marcellus Shale Groundwater Coal Mine Upper Devonian Formations Discharge Shale Surface Waters Sharma et al., 2013, Groundwater Journal TIER 3: ISOTOPES Radium Isotopes: Ra-228/ Ra-226 Application: Ra-228/ Ra-226 ratio can differ significantly in produced water Application: vs. other water sources. Marcellus Produced Water PA Non-Marcellus Waters Ra-228/ Ra-226: Ra-228/ Ra-226: Typically <0.3 Typically >1 Ref: Rowan et.al, 2010, USGS Scientific Investigations Report 2011–5135 9 3/1/2017 Other Isotopes Common Application Isotopic Analysis Tracing sources of salinity and water sources with different evolutionary histories: δ34S, δ37Cl, δ81Br, δ11B Age dating of groundwater: 3H, 14C Dating older waters and tracing sources of salinity: 129I, 129I/127I Advantages: Holding time of several years. Disadvantages: Reference data may not exist for comparison, some analyses are expensive and have longer turnaround times. 19 REFERENCES Paquette et al. 2017 (Pending). A Tiered Approach to Evaluating Sources of Salinity in Water at Oil and Gas Production Sites. Groundwater Journal. Chapman et al. 2012. Geochemical and strontium isotope characterization of produced waters from Marcellus Shale natural gas extraction. Environmental Science & Technology. Sharma et al. 2013. Isotope Approach to Assess Hydrologic Connections During Marcellus Shale Drilling. Groundwater Journal. Rowan et al. 2011. Radium content of Oil- and gas-Field Produced Water in the Northern Appalachian Basin (USA): Summary and Discussion. USGS Scientific Investigations Report 2011-5135. Richter and Kreitler. 1991. Identification of Sources of Ground-Water Salinization Using Geochemical Techniques. United States Environmental Protection Agency EPA/600/291/064. Williams et al. 1998. Hydrogeology and groundwater quality of the glaciated valleys of Bradford, Tioga, and Potter Counties, Pennsylvania. USGS Water Resources Report No. 68. 20 10 3/1/2017 John Connor, PE, PG, BCEE Lisa Molofsky, P.G. Ileana Rhodes, PhD Ann Smith, PE, BCEE 21 February 2017 21 LINES OF EVIDENCE FOR EVALUATING POTENTIAL IMPACTS FROM PRODUCED WATER: OUTLINE 1 Indicator parameters 2 Diagnostic cations and anions 3 Stable isotopes of water: δ2H and δ18O 4 Strontium isotopic ratios: 87Sr/86Sr 5 δ13C of dissolved inorganic carbon (DIC) 6 Ra-228/Ra-226 and other isotopes 7 Tiered approach to identifying source of salinity 11
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