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Mr. Erik Milito - The House Committee on Natural Resources ...

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WATER MANAGEMENT ASSOCIATED WITH HYDRAULIC FRACTURING 17<br />

may be suffering from current water supply c<strong>on</strong>straints, especially during periods of drought, so the l<strong>on</strong>g term<br />

reliability of supplies from municipal water suppliers needs to be carefully evaluated.<br />

6.2.4 Wastewater and Power Plant Cooling Water<br />

Other possible opti<strong>on</strong>s for source water to support hydraulic fracturing operati<strong>on</strong>s that could be c<strong>on</strong>sidered are<br />

municipal wastewater, industrial wastewater, and/or power plant cooling water. Clearly, the specificati<strong>on</strong>s of this water<br />

source need to be compatible with the target formati<strong>on</strong> and the plan for fracturing as well as whether treating is<br />

technically possible and whether treatment can deliver an overall successful project. In some cases, required water<br />

specificati<strong>on</strong> could be achieved with the proper mixing of supplies from these sources with supplies from surface<br />

water or groundwater sources.<br />

6.2.5 Reservoir Water and Recycled Flow Back Water<br />

Produced reservoir water and recycled flow back water can be treated and reused for fracturing, depending <strong>on</strong> the<br />

quality of the water. <strong>Natural</strong> formati<strong>on</strong> water has been in c<strong>on</strong>tact with the reservoir formati<strong>on</strong> for milli<strong>on</strong>s of years and<br />

thus c<strong>on</strong>tains minerals native to the reservoir rock. Some of this formati<strong>on</strong> water is recovered with the flow back water<br />

after hydraulic fracturing, so that both c<strong>on</strong>tribute to the characteristics of the flow back water. <str<strong>on</strong>g>The</str<strong>on</strong>g> salinity, TDS, and<br />

overall quality of this formati<strong>on</strong>/flow back water mixture can vary by geologic basin and specific rock strata. For<br />

example, water salinity can range from brackish (5,000 parts per milli<strong>on</strong> (ppm) to 35,000 ppm TDS), to saline (35,000<br />

ppm to 50,000 ppm TDS), to supersaturated brine (50,000 ppm to >200,000 ppm TDS). Other water quality<br />

characteristics that may influence water management opti<strong>on</strong>s for fracturing operati<strong>on</strong>s include c<strong>on</strong>centrati<strong>on</strong>s of<br />

hydrocarb<strong>on</strong>s (analyzed as oil and grease), suspended solids, soluble organics, ir<strong>on</strong>, calcium, magnesium, and trace<br />

c<strong>on</strong>stituents such as benzene, bor<strong>on</strong>, silicates, and possibly other c<strong>on</strong>stituents.<br />

Several efforts are underway to examine the c<strong>on</strong>diti<strong>on</strong>s where the use of reservoir water and recycled flow back water<br />

for fracturing operati<strong>on</strong>s may be ec<strong>on</strong>omically viable. [27] Typically, the water must be treated. This opti<strong>on</strong> is discussed<br />

in more detail elsewhere in this guidance document.<br />

Some coalbed methane operati<strong>on</strong>s may also have discharge water that is appropriate for hydraulic fracturing use.<br />

Finally, operators should be aware that black shales, as well as other formati<strong>on</strong>s that are often the target formati<strong>on</strong>s<br />

for hydraulic fracturing operati<strong>on</strong>s, sometimes c<strong>on</strong>tain trace levels of naturally occurring radioactive materials<br />

(NORM). Gamma ray logs indicate, for example, that this is true of the Marcellus shale. Gas wells can bring NORM to<br />

the surface in the cuttings, flow back fluid and producti<strong>on</strong> brine, and NORM can accumulate in pipes and tanks (pipe<br />

scale). NORM c<strong>on</strong>tained in the discharge of fracturing fluids or producti<strong>on</strong> brine may be subject to discharge<br />

limitati<strong>on</strong>s. <str<strong>on</strong>g>The</str<strong>on</strong>g> Envir<strong>on</strong>mental Sciences Divisi<strong>on</strong> of Arg<strong>on</strong>ne Nati<strong>on</strong>al Laboratory has addressed explorati<strong>on</strong> and<br />

producti<strong>on</strong> (E&P) NORM disposal opti<strong>on</strong>s in detail and maintains a Drilling Waste Management Informati<strong>on</strong> System<br />

website [28] that links to regulatory agencies in all oil and gas producing states. API also has published several<br />

documents providing guidance <strong>on</strong> the management of NORM in oil and gas operati<strong>on</strong>s. [29]<br />

6.2.6 Make-up Water Requirements, Availability and Quality<br />

In situati<strong>on</strong>s where water is recycled and/or reused, or additi<strong>on</strong>al sources of industrial wastewater make some<br />

c<strong>on</strong>tributi<strong>on</strong> to supply water for fracturing operati<strong>on</strong>s, additi<strong>on</strong>al make up water may be required. In these cases,<br />

water management alternatives to be c<strong>on</strong>sidered will depend <strong>on</strong> the volume and quality of both the recycled water<br />

and the make up water, to ensure compatibility with each other and with the formati<strong>on</strong> being fractured.<br />

6.3 Fluid Handling And Storage C<strong>on</strong>siderati<strong>on</strong>s<br />

6.3.1 General<br />

Fluids handled at the well site both before and after hydraulic fracturing often must be stored <strong>on</strong> site, and must be<br />

transported from the source of supply to the point of ultimate treatment and/or disposal. Fluids used for hydraulic

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