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. 2017 Jan 1:574:1544-1558.
doi: 10.1016/j.scitotenv.2016.08.167. Epub 2016 Sep 22.

A decision analysis framework for estimating the potential hazards for drinking water resources of chemicals used in hydraulic fracturing fluids

Affiliations

A decision analysis framework for estimating the potential hazards for drinking water resources of chemicals used in hydraulic fracturing fluids

Erin E Yost et al. Sci Total Environ. .

Abstract

Despite growing concerns over the potential for hydraulic fracturing to impact drinking water resources, there are limited data available to identify chemicals used in hydraulic fracturing fluids that may pose public health concerns. In an effort to explore these potential hazards, a multi-criteria decision analysis (MCDA) framework was employed to analyze and rank selected subsets of these chemicals by integrating data on toxicity, frequency of use, and physicochemical properties that describe transport in water. Data used in this analysis were obtained from publicly available databases compiled by the United States Environmental Protection Agency (EPA) as part of a larger study on the potential impacts of hydraulic fracturing on drinking water. Starting with nationwide hydraulic fracturing chemical usage data from EPA's analysis of the FracFocus Chemical Disclosure Registry 1.0, MCDAs were performed on chemicals that had either noncancer toxicity values (n=37) or cancer-specific toxicity values (n=10). The noncancer MCDA was then repeated for subsets of chemicals reported in three representative states (Texas, n=31; Pennsylvania, n=18; and North Dakota, n=20). Within each MCDA, chemicals received scores based on relative toxicity, relative frequency of use, and physicochemical properties (mobility in water, volatility, persistence). Results show a relative ranking of these chemicals based on hazard potential, and provide preliminary insight into chemicals that may be more likely than others to impact drinking water resources. Comparison of nationwide versus state-specific analyses indicates regional differences in the chemicals that may be of more concern to drinking water resources, although many chemicals were commonly used and received similar overall hazard rankings. Several chemicals highlighted by these MCDAs have been reported in groundwater near areas of hydraulic fracturing activity. This approach is intended as a preliminary analysis, and represents one possible method for integrating data to explore potential public health impacts.

Keywords: Exposure assessment; Hazard evaluation; Hydraulic fracturing.

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Figures

Fig. 1
Fig. 1
The MCDA employed in this study is a three-part prioritization model, which incorporates data on toxicity, occurrence, and physicochemical properties.
Fig. 2
Fig. 2
Venn diagram depicting the availability of data for input into the MCDA (nationwide analysis). Values shown in the diagram reflect all of the toxicity and physicochemical properties data that is available on the draft database of EPA's hydraulic fracturing study (US EPA, 2015c), as well as all of the chemical usage data that is available on EPA's FracFocus 1.0 project database (US EPA, 2015b). Chemicals that had available data for all three criteria (toxicity, occurrence, and physicochemical properties) were selected for inclusion in the MCDA.
Fig. 3
Fig. 3
Results of the noncancer MCDA, based on a nationwide analysis (37 chemicals total), depicting the Toxicity, Occurrence, and Physicochemical Properties Scores for each chemical. Chemicals are ordered from high to low based on Total Hazard Potential Score.
Fig. 4
Fig. 4
Results of the cancer MCDA, based on a nationwide analysis (10 chemicals total), depicting the Toxicity, Occurrence, and Physicochemical Properties Scores for each chemical. Chemicals are ordered from high to low based on Total Hazard Potential Score.
Fig. 5
Fig. 5
Results of the noncancer MCDA, based on state-specific analysis for Texas (31 chemicals total), depicting the Toxicity, Occurrence, and Physicochemical Properties Scores for each chemical. Chemicals are ordered from high to low based on Total Hazard Potential Score.
Fig. 6
Fig. 6
Results of the noncancer MCDA, based on state-specific analysis for Pennsylvania (18 chemicals total), depicting the Toxicity, Occurrence, and Physicochemical Properties Scores for each chemical. Chemicals are ordered from high to low based on Total Hazard Potential Score.
Fig. 7
Fig. 7
Results of the noncancer MCDA, based on state-specific analysis for North Dakota (20 chemicals total), depicting the Toxicity, Occurrence, and Physicochemical Properties Scores for each chemical. Chemicals are ordered from high to low based on total hazard potential score.

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