Hydraulic fracturing regulation in the US | Practical Law

Hydraulic fracturing regulation in the US | Practical Law

This article provides an overview of shale gas development using hydraulic fracturing and briefly describes the regulatory responses to this rapidly growing field.

Hydraulic fracturing regulation in the US

Practical Law UK Articles 5-521-7563 (Approx. 11 pages)

Hydraulic fracturing regulation in the US

by Samuel B Boxerman and Joel F Visser, Sidley Austin LLP
Law stated as at 01 Oct 2012USA (National/Federal)
This article provides an overview of shale gas development using hydraulic fracturing and briefly describes the regulatory responses to this rapidly growing field.
Development of shale gas resources using hydraulic fracturing has been one of the most significant advances in US energy production in the past decade. By combining horizontal drilling and hydraulic fracturing, previously unrecoverable gas reserves have become economically viable. This development offers enormous potential for economic growth and energy security. In response, regulators have begun issuing new rules and guidance governing the use of hydraulic fracturing.

Shale gas development using hydraulic fracturing

Shale formations are comprised of fine-grained, organic-rich sedimentary rock. Natural gas is trapped in small pores within shale formations, but does not flow through the rock unless natural or artificial fractures connect the gas pores. As a result, these gas deposits, or "plays" cannot be effectively and economically developed using conventional drilling technology. However, by combining horizontal drilling and hydraulic fracturing, it is possible to recover significant quantities of natural gas from shale formations. In addition to "dry gas" plays, which are comprised solely of natural gas, some shale plays produce "wet gas," from which both natural gas and petroleum fractions can be recovered.
Both horizontal drilling and hydraulic fracturing have been used for many decades in oil and gas development across the US. With advances in technology, the two techniques have been combined to develop shale gas resources. Initially, a vertical well bore is drilled deep into the shale formation, often more than a mile below the surface. Steel and cement casings are then added to isolate the target shale formation and prevent migration out of the well bore. Once the vertical well bore is completed, the drill bit is turned laterally, and the well bore is extended horizontally (in some cases for another mile or more) through the shale formation. After the horizontal well casing is in place, that portion of the well casing is perforated, and small charges are used to create fractures in the surrounding shale. Fracturing fluid (primarily made up of water and a "proppant" (usually sand)) is then pumped into the well bore at high pressure to stimulate the well. The proppant fills the newly created fractures in the shale and ensures that they remain open during production. Fracturing fluids also include very small concentrations of other proprietary and non-proprietary chemical additives, which are used to prevent bacterial growth and corrosion, reduce friction in the well bore, and manage well pressure. The fracturing process takes several days to complete and a portion of the fracturing fluids return to the surface as produced water. Once the well development is finished (or the well is "completed"), the drilling equipment is removed and production occurs on a small well pad.
Shale plays containing natural gas and oil are found throughout the US. The major plays include:
  • Marcellus (Pennsylvania, New York, Ohio, West Virginia, Kentucky).
  • Bakken (North Dakota, Wyoming).
  • Haynesville (Texas, Louisiana).
  • Barnett (Texas).
  • Eagleford (Texas).
  • Fayetteville (Arkansas).
  • Antrim (Michigan, Illinois, Ohio).
  • Woodford (Oklahoma).
  • Niobara (Colorado, Kansas, Wyoming).
The US Energy Information Administration (EIA) estimates that there are 482 trillion cubic feet (tcf) of unproved, technically recoverable shale gas resources in the US, which accounts for a third of domestic natural gas resources (EIA Annual Energy Outlook 2012). As a comparison, total US natural gas consumption in 2011 was 24.3 tcf. EIA 2012. In the past decade, shale gas production has increased dramatically, from 0.4 tcf in 2000 to 4.8 tcf in 2012 (EIA Annual Energy Outlook 2012). EIA projects that production will increase to 13.6 tcf by 2035.
The expansion of shale gas production using hydraulic fracturing has important energy security implications, and the EIA projects that the US will become a net exporter of natural gas by 2021.
The development of shale gas resources using hydraulic fracturing also promises significant economic benefits. A recent study found that in 2010 the shale gas industry directly employed 148,000 workers and was responsible for an additional 450,000 indirect and induced jobs (IHS Global Insight, The Economic and Employment Contributions of Shale Gas in the US (2011)). The IHS study found that the shale gas industry contributed US$76 billion to the US GDP and nearly US$20 billion in federal, state, and local taxes and royalty revenues. In addition to energy production, shale gas development is spurring growth in other industries. For example, ethane, the second largest component of natural gas after methane, is a primary raw material for ethylene production. In response to ample supplies of natural gas, four petrochemical producers have recently announced plans to build or recommission ethane crackers and production facilities near shale gas plays.
Despite its promise, shale gas development using hydraulic fracturing has been controversial, as some have raised concerns over potential environmental impacts. In 2011, the Secretary of Energy Advisory Board (SEAB) solicited the views of interested organisations, and SEAB's final report summarises environmental concerns raised by some commenters, although the concerns are disputed by industry (Secretary of Energy Advisory Board, Shale Gas Production Subcommittee 90-Day Report (Aug. 18, 2011) (SEAB Report)). For example, commenters expressed concern that:
  • Fracturing shale formations could allow natural gas or fracturing fluids to migrate up into groundwater aquifers. (The fractured shale is typically located several thousand feet below groundwater aquifers and, while the US Environmental Protection Agency (EPA) has investigated allegations of groundwater impacts from hydraulic fracturing, to date there are no proven cases of groundwater contamination due to migration of fracturing fluids through shale formations.)
  • Improperly sealed well casings could permit gas or fracturing fluids to migrate directly into an aquifer from the well bore because the vertical well bore is drilled through groundwater aquifers.
  • The on-site storage of fracturing fluids and wastewater could increase the risk of spills into surface water.
  • The drilling and hydraulic fracturing process produces a variety of air emissions, including volatile organic compounds (VOCs) and methane.
  • Some researchers believe the underground injection of fracturing wastewater (or "flowback" from the fracturing process), which occurs off-site after well completion, can produce minor seismic activity. (Other researchers dispute those conclusions.)

State regulation of hydraulic fracturing

Historically, states have played the primary role in regulating oil and natural gas development in the US, and this trend has continued for the regulation of hydraulic fracturing. State regulation allows each state to evaluate the unique characteristics of its oil and gas plays by tailoring regulations to address the specific issues that are presented. Therefore, even in the absence of specific new regulations, hydraulic fracturing is subject to the general oil and gas regulations in each state.
Virtually every state with significant shale gas reserves has responded in some manner to the development of hydraulic fracturing. Many states have embraced hydraulic fracturing by adopting new regulations that specifically address natural gas development using hydraulic fracturing and allow these activities to proceed. Opponents of hydraulic fracturing typically have an opportunity to challenge such regulations in court. The natural gas industry has also been proactive in developing best management practices for hydraulic fracturing operations that supplement and, in many cases, inform state regulations, including the:
  • American Petroleum Institute (API) Guidance Document HF1 (2009) (well construction and integrity).
  • API Guidance Document HF2 (2010) (water management).
  • API Guidance Document HF3 (2011) (surface impacts).
  • API Std. 65, Part 2 (2010) (isolating flow zones during well construction).
  • API RP 51R (2009) (environmental protection).
A few states have issued temporary moratoria on hydraulic fracturing to conduct additional studies before developing new regulations. However, a majority of states with shale gas reserves have issued new technical regulations for hydraulic fracturing, including:
  • Colorado (Colo. Code Regs. § 404-1 et seq).
  • Ohio (Ohio Rev. Code § 1509, Ohio Admin Code § 1501:9).
  • Oklahoma (Okla. Admin. Code § 165:10-1-1 et seq).
  • Pennsylvania (25 Pa. Code § 78.1 et seq).
  • Arkansas (Ark. Oil & Gas Comm'n Gen R and Reg. B-19).
  • Louisiana (La. Admin Code tit 43, pt XIX).
  • Michigan (Supervisor of Wells Instruction 1-2011).
  • Montana (Mont. Admin. Rs 36.22.608, 1010, 1106).
  • West Virginia (W. Va. Code R 22-6A-1 et seq).
  • Idaho (Idaho Admin. Code r 20.07.02.056).
  • North Dakota (N.D. Admin Code 43-02-03-05 et seq).
State disclosure requirements for chemical additives included in fracturing fluids also exist in the following states:
  • Wyoming (Wyo. Oil & Gas Comm'n R. and Regs., Ch. 3, § 45).
  • Arkansas (Ark. Oil & Gas Comm'n Gen. R. and Reg. B-19).
  • Louisiana (La. Admin Code tit. 43, pt. XIX, § 118).
  • Michigan (Supervisor of Wells Instruction 1-2011).
  • Montana (Mont. Admin. R. 36.22.1015).
  • West Virginia (W. Va. Code R. 22-6A-7).
  • Colorado (Colo. Code Regs. § 404-1:205A).
  • Idaho (Idaho Admin. Code r. 20.07.02.056).
  • Indiana (312 Ind. Admin. Code Emergency Rule 12-292).
  • New Mexico (N.M. Code R. § 19.15.16.19).
  • North Dakota (N.D. Admin. Code § 43-02-03-27.1).
  • Ohio (Ohio Rev. Code § 1509.10, Ohio Admin Code § 1509).
  • Pennsylvania (58 Pa. Const. Stat. § 3222.1).
  • Texas (16 Tex. Admin. Code § 3.29).
  • Oklahoma (Okla. Admin. Code § 165:10-3-10).
The scope and content of state regulations varies considerably. Some states, such as Colorado, Ohio, and Pennsylvania, have adopted comprehensive regulations that impose a range of requirements on the well development process, including background water sampling, well construction and casing, well stimulation, and wastewater storage and disposal (Colo. Code Regs. § 404-1 et seq; Ohio Admin. Code § 1501:9; 25 Pa. Code § 78.1 et seq). In some cases, state agencies have adopted regulations in response to new hydraulic fracturing laws passed by state legislatures. Other states have taken more modest approaches. Texas has adopted regulations requiring disclosure of chemical additives in fracturing fluids (16 Tex. Admin. Code § 3.29) but relies on established technical regulations for well construction and hydraulic fracturing. Michigan has not adopted new regulations specifically designed for hydraulic fracturing, but has instead issued guidelines applying pre-existing regulations to hydraulic fracturing operations (Michigan DEQ, Supervisor of Wells Instruction 1-2011). Despite their diversity, hydraulic fracturing regulations typically address a similar suite of technical issues.

Groundwater quality surveys

Many states require well operators to conduct background sampling of nearby drinking water supplies before well construction. For example, Ohio requires testing of all water wells within 1,500 feet of the proposed well (Ohio Rev. Code § 1509.06(A)(8)). In Colorado, background water testing is part of an industry-led programme administered by the Colorado Oil & Gas Association. Well operators in Pennsylvania are not required to conduct background water sampling before drilling. However, if contamination is later discovered, an operator who fails to conduct background water testing is legally precluded from arguing that the contamination was a pre-existing condition (25 Pa. Code § 78.52).

Setbacks and geographic restrictions

States also restrict the location of wells employing hydraulic fracturing by creating buffer zones between wells and public water supplies, private wells, and surface water. The size of buffer zones varies considerably between states. For example, Ohio requires a 50-foot setback for streams (Ohio Rev. Code § 1509.021), while Pennsylvania requires a 300-foot setback. (58 Pa. Cons. Stat. § 3215). Buffer zones may also vary based on the type of water body involved (Colo. Code Regs. § 404-1-317B).

Well casing requirements

Well operators are required to install steel and cement casings that isolate the productive shale producing zones and prevent migration of fracturing fluids and gas out of the well bore. While the regulations contain specific and technical requirements, they share some common characteristics. For example, Ohio and Pennsylvania require that the surface casing be set 50 feet below the deepest freshwater aquifer (Ohio Admin. Code § 1501:9-1-08; 25 Pa. Code § 78.83), Colorado requires that surface casing be "sufficient to protect all freshwater" and in the case of deep groundwater aquifers, requires a solid cement plug extending 50 feet above and below the aquifer (Colo. Code Regs. 404-317).

Pressure testing and monitoring

Because well stimulation involves injecting fracturing fluids at high pressures, states have included regulations designed to ensure that well pressure is managed and maintained properly. Some states require steel casings to be rated at a pressure in excess of the highest anticipated pressure that will be encountered during the fracturing process (Ohio Admin. Code § 1501:9-1-08; 25 Pa. Code § 78.84). Other states require pre-fracturing testing to ensure that the well casing can withstand anticipated fracturing pressures (Colo. Code Reg. § 404-1-317). In addition, blowout prevention equipment may be required (25 Pa. Code § 78.72). States may also require pressure monitoring during the fracturing process to ensure well integrity (Colo. Code Reg. § 404-1-341).

Fracturing fluid and wastewater storage

The on-site storage of fracturing fluids and wastewater is also regulated in many states. Typically, states require that on-site storage pits be equipped with impermeable liners to prevent fluid leakage (Colo Code Regs. § 404-1-904; 25 Pa. Code § 78-56). States may also require a minimum freeboard height to prevent overtopping of the storage pits (25 Pa. Code § 78-56).

Wastewater disposal

Disposal of wastewater is also regulated. For example, Ohio requires that all wastewater from hydraulic fracturing be disposed of through underground injection (Ohio Rev. Code § 1509.22). Some states permit wastewater to be discharged after processing in a waste treatment facility (25 Pa. Code § 95.10). Other states have added regulations to encourage recycling of wastewater for reuse in future hydraulic fracturing operations (La. Admin. Code tit. 43, Part XIX, § 565).

Disclosure requirements

Most states require well operators to disclose the chemical additives used in hydraulic fracturing fluids, along with other pertinent data. Typically, disclosure is required after a well is completed, and operators are not required to disclose proprietary chemicals that qualify as trade secrets (Ohio Rev. Code § 1509.10; 25 Pa. Code § 78.122). However, a few states require some form of pre-disclosure of chemical additives used in hydraulic fracturing (Ark. Oil & Gas Comm'n Gen. R. And Reg. B 19; Wyo. Oil & Gas Gomm'n R. And Rgs. Ch. 3, § 45). In other cases, the rules require operators to disclose non-proprietary chemical additives directly to an internet-based registry known as FracFocus (see website, www.fracfocus.org), where it is immediately available to the public (Colo. Code Reg. § 404-1-205A).

Temporary moratoria on hydraulic fracturing

In contrast to the states described above, a few states have taken a different approach and imposed moratoria on hydraulic fracturing while they conduct further studies. These states have advised that they plan to develop regulations that address issues identified in their studies before any well construction occurs.
The most widely publicised state moratorium was instituted in New York state. New York is located in the centre of the Marcellus Shale and has the potential to become a major producer of shale gas. In 2008, the New York State Department of Environmental Conservation (NYSDEC) responded to the potential expansion of natural gas development using hydraulic fracturing in the state by beginning preparation of a study known as a Supplemental Generic Environmental Impact Statement (SGEIS). In 2010, the New York legislature passed a one-year moratorium on new permits for development using hydraulic fracturing. After vetoing the legislation, Governor Paterson issued an executive order that announced a moratorium on "high volume" hydraulic fracturing using horizontal drilling until the NYSDEC completed its SGEIS and issued new regulations (Exec. Order No. 41 (13 Dec. 2010)).
In September 2011, NYSDEC issued a draft SGEIS report along with draft regulations for hydraulic fracturing (Proposed N.Y. Comp. Codes R. & Regs. tit. 6, parts 52, 190, 550-556, 560, 750). The proposed rules would prohibit hydraulic fracturing within 4,000 feet of the New York city water supply watershed (which is located within the Marcellus Shale region), while proposing smaller buffer zones for other water resources. The proposal also includes chemical disclosure, testing and monitoring, and wastewater disposal requirements. Legal challenges are likely once the final regulations are issued.
In addition to New York, several other states have, at times, instituted differing moratoria on hydraulic fracturing:
  • Maryland: In June 2011, Maryland's governor issued an executive order that established an advisory commission to study hydraulic fracturing and make regulatory recommendations. Until the advisory commission's work is complete, the executive order acts as a de facto ban on hydraulic fracturing.
  • New Jersey: In August 2011, New Jersey's governor established a one-year moratorium on hydraulic fracturing (Press Release, Gov. Chris Christie (Aug. 25, 2011)). The moratorium would allow the state to evaluate ongoing federal studies regarding hydraulic fracturing and use those studies to assess the proper course for the state.
  • North Carolina: In July 2012, North Carolina's legislature reversed a long-standing ban on horizontal drilling and hydraulic fracturing by passing the Clean Energy and Economic Security Act over the governor's veto (2012 N.C. Sess. Laws 143). The Act requires the Mining and Energy Commission to develop hydraulic fracturing regulations by 1 October 2014.
  • Vermont: In May 2012, Vermont banned hydraulic fracturing, directing the state agency to report back to the legislature after federal studies are completed (House Bill 464). However, the ban may be viewed as symbolic in nature, as there are no proven shale gas reserves in Vermont.

Local government regulation of hydraulic fracturing

A number of local governments have instituted bans on hydraulic fracturing within their jurisdictions. To date, such bans have been instituted in Colorado, Maryland, New Jersey, New York, North Carolina, Ohio, Pennsylvania and West Virginia. The legality of local bans has come under scrutiny because comprehensive state regulation of oil and gas development may pre-empt local governments from issuing ordinances that prohibit or otherwise regulate hydraulic fracturing.
The legality of local bans is dependent on state laws and the results of litigation have been mixed. In New York, two trial courts held that the state's Oil, Gas and Solution Mining Law's pre-emption provisions only apply to technical regulations for oil and gas development, allowing local governments to issue zoning ordinances that ban hydraulic fracturing (Anschutz Exploration Corp. v. Town of Dryden, No. 2011-0499 (N.Y. Sup. Ct., Feb. 21, 2012); Cooperstown Holstein Corp. v. Town of Middlefield, No. 011-0930 (N.Y. Sup. Ct., Feb. 24, 2012)). The New York decisions are now on appeal. Conversely, a West Virginia trial court held that regulations issued by the state Department of Environmental Protection pre-empted local ordinances restricting hydraulic fracturing (Northeast Natural Energy, LLC v. City of Morgantown, CA No.11-C-411 (Cir. Ct. of Monongalia Co. Aug. 12, 2011)). Because no state supreme court has taken up this issue, the legality of these local bans remains an open question.
Pennsylvania has taken a different approach. There the legislature enacted Act 13, which added new state-wide rules governing hydraulic fracturing, but prohibited local governments from establishing local bans on the activity. That law has been challenged and was recently ruled unconstitutional (Robinson Twp. V. Pennsylvania, No. 284 M.D. 2012 (Pa. Commw. Ct. June 6, 2012)). It too is currently on appeal.

Federal regulation of hydraulic fracturing

Although the federal government does not have primary responsibility for regulating oil and gas development, a number of broad environmental programmes administered by EPA could potentially be applied to hydraulic fracturing. Any federal regulations would overlap with the state regulations described above, requiring natural gas developers to comply with both state and federal regulations. While EPA has not been active in regulating natural gas development to date, some non-governmental organisations have urged the agency to take a more active role, and there have been reports that the agency intends to increase its regulatory efforts. The following sections describe the EPA programmes that could be used to regulate hydraulic fracturing.

Safe Drinking Water Act (SDWA)

The SDWA, which is designed to protect drinking water quality, is one federal programme that could regulate hydraulic fracturing, as SWDA's Underground Injection Control (UIC) programme generally regulates the underground injection of fluids for storage or disposal (42 USC. § 300h et seq). However, in the Energy Policy Act of 2005, Congress expressly excluded hydraulic fracturing activities from the UIC programme, although the exclusion does not apply to the injection of fluids containing diesel fuels (42 USC. § 300h(d)(1)(B)). As a result, most hydraulic fracturing activities are not regulated under SDWA.
To date, EPA has not attempted to implement a permitting programme for hydraulic fracturing using diesel fuels. However, it recently issued a draft guidance document that would effectively impose permitting requirements (EPA, Permitting Guidance for Oil and Gas Hydraulic Fracturing Activities Using Diesel Fuels – Draft: Underground Injection Control Program Guidance #84 (May 2012)). The draft guidance lists specific chemicals EPA proposes to define as "diesel fuels" and includes permitting guidelines to address unique features of hydraulic fracturing, including high injection pressures, horizontal well bores, and the intentional fracturing of shale formations during well stimulation. EPA's proposed guidance is now subject to a public comment process. If finalised, the guidance would be used for federal permitting in a limited number of states, but the guidance would not be mandatory for states that have been given authority by EPA to administer their own UIC programme.
UIC permits are also required for underground disposal of wastewater from hydraulic fracturing. Wastewater disposal wells are regulated as Class II oil and gas related wells and must comply with 40 C.F.R. § 146, which includes:
  • Casing and cementing requirements.
  • Limitations on injection pressure, flow rates and injection volumes.
  • Monitoring and reporting requirements.
39 states have been authorised to administer the UIC programme for Class II wastewater disposal wells and must apply requirements at least as stringent as those applied by EPA (40 C.F.R. § 145.11).

Clean Water Act (CWA)

The CWA requires a permit for discharges of pollutants into waters of the United States. Permit standards for industrial wastewater discharges are typically based on nationally-applicable effluent guidelines and prohibit the direct discharge of waste water from onshore oil and gas operations, including natural gas development using hydraulic fracturing, into surface waters (40 C.F.R. § 435.32). Wastewater from hydraulic fracturing may, however, be discharged after it is processed in a treatment plant. Although EPA has not developed effluent guidelines that specifically address the treatment of wastewater from shale gas extraction, it has announced a plan to do so by 2014. Development of well pad sites for site gas extraction may also be subject to permit requirements under CWA § 404, which regulates discharges to and disturbance of wetlands.
Other aspects of well construction and hydraulic fracturing are largely exempt from the CWA. Water, gas and other material that are injected into a well to facilitate oil or gas production are not considered "pollutants" under the CWA if the activity is permitted by the state where the well is located (33 USC. § 1362(6)(B)). In addition, oil and gas operations are exempt from CWA storm water permitting requirements as long as the storm water runoff is kept separate from raw material and waste products at the well site (33 USC. § 1342(l)(2)). In 2005, Congress broadened this exemption to include all activities "associated with exploration, production, processing, or treatment operations or transmission facilities" (33 USC. § 1362(24)).

Clean Air Act (CAA)

Under the CAA, EPA can regulate air emissions from all sources, including hydraulic fracturing operations. Hydraulic fracturing operations are subject to new source performance standards (NSPS), prevention of significant deterioration (PSD), and national emissions standards for hazardous air pollutants (NESHAPs) that are applicable to all oil and gas operations (42 USC. §§ 7411-12). On 16 August 2012, EPA published the first NSPS and NESHAP regulations that specifically address hydraulic fracturing operations (77 Fed. Reg. 49,490 (16 August 2012)). EPA expects these regulations to reduce VOC emissions by 95% and toxic air emissions by more than 12,000 tonnes per year.

Resource Conservation and Recovery Act (RCRA)

The RCRA regulates the disposal of solid waste. Subpart C imposes "cradle-to-grave" record keeping and disposal requirements for hazardous wastes (42 USC. §§ 6921-6939b), while subpart D allows states to regulate disposal of non-hazardous waste based on minimum federal guidelines (42 USC. §§ 6941-6949a). Under RCRA, all oil and gas wastes, including those from hydraulic fracturing, are exempt from regulation as hazardous waste under subpart C and are instead regulated by the states as non-hazardous waste (42 USC. § 6921(b)(2); 53 Fed. Reg. 25,477 (6 July 1988)). However, hazardous waste products that are not uniquely associated with oil and gas operations may still be regulated by EPA under subpart C.

Comprehensive Environmental Response Compensation and Liability Act (CERCLA)

The CERCLA (or "Superfund") governs the cleanup of releases of hazardous substances into the environment. CERCLA imposes strict liability and, under most circumstances, the parties who generate hazardous substances that are released, or own or operate a site where they are released, are jointly and severally liable for the costs of cleanup. Releases of natural gas or other chemicals injected to stimulate natural gas development under a state permit are exempted from CERCLA liability (42 USC. § 9601(10), (14)). EPA has, however, relied on its investigative authority under CERCLA to study claims of groundwater contamination from hydraulic fracturing operations.

Toxic Substances Control Act (TSCA)

The TSCA authorises EPA to issue reporting, record keeping, and testing requirements for chemicals that are used or produced by a facility and, if necessary, to restrict the use of chemicals that pose health risks. TSCA includes a citizen petition process that allows individuals or organisations to petition EPA to regulate additional chemicals, products or processes (15 USC. § 2650). In August 2011, a group of 120 environmental and public health organisations petitioned EPA to adopt testing and disclosure regulations for chemicals used in hydraulic fracturing. EPA declined to issue a testing rule, but granted the petition to begin a rulemaking process regarding record keeping and reporting requirements for chemicals and mixtures used in hydraulic fracturing. EPA has announced plans to solicit comments from interested parties, but has not yet begun the rulemaking process.

Hydraulic fracturing on federal land

Natural gas development using hydraulic fracturing on federal land is already subject to Bureau of Land Management (BLM) permitting regulations issued under the Mineral Leasing Act (30 USC. § 189; 43 C.F.R. § 3162.3-2). These include rules similar to the oil and gas regulations historically issued by states. In May 2012, BLM proposed to revise its rules to address hydraulic fracturing (77 Fed. Reg. 27,691 (11 May 2012)). The proposed regulations would require pre-approval of hydraulic fracturing operations, well integrity testing before and during the hydraulic fracturing process, and the disclosure of chemical additives after well completion. BLM is taking public comment on its proposal.
In addition, federal agencies that manage land with shale gas reserves must comply with the National Environmental Policy Act (NEPA) (42 USC. § 3421 et seq). NEPA is a procedural statute that requires federal agencies to evaluate the environmental impacts of a proposed action, consider alternative actions, and provide an opportunity for public comment before reaching a final decision. NEPA does not limit an agency's ability to issue natural gas leases once the environmental evaluation process is complete.

Federal studies

In the past two years, the federal government has commissioned two studies of hydraulic fracturing under the auspices of the SEAB and the EPA. In May 2011, the SEAB commissioned a Natural Gas Subcommittee to make recommendations regarding the safety and environmental performance of hydraulic fracturing. After soliciting comments from interested stakeholders, the committee issued the SEAB Report, which made a series of recommendations for:
  • Increased disclosure of information related to hydraulic fracturing operations.
  • Increased communication among regulators.
  • New measures regarding air quality and water quality.
  • A greater emphasis on considering the potential for impacts to local communities, land use and wildlife.
The committee also recognised industry-led efforts to develop best practices to manage hydraulic fracturing.
In November 2011, EPA released a Plan to Study the Potential Impacts of Hydraulic Fracturing on Drinking Water Resources (EPA Study Plan) in response to a direction by the Congress. According to EPA, the agency will study the ways in which hydraulic fracturing could potentially affect drinking water resources, including water acquisition, chemical mixing, well injection, flowback and produced water, and wastewater treatment and disposal. The study will employ case studies, laboratory studies, and toxicological assessments. EPA plans to release a preliminary report in late 2012 and a final report in 2014.

Contributor details

Samuel B Boxerman

Sidley Austin LLP

T +1 202 736 8547
F +1 202 736 8711
E [email protected]
W www.sidley.com
Qualified. District of Columbia, 1996; Illinois, 1987
Areas of practice. Environmental; international arbitration.
Recent transactions
  • Represents clients in environmental regulatory, administrative and litigation matters.
  • Represents clients' shale gas development and hydraulic fracturing, including assisting clients with comments on agency proposals and handling regulatory litigation.
  • Represents private and sovereign clients in arbitrations before the International Center for the Settlement of Investment Disputes.

Joel F Visser

Sidley Austin LLP

T + 1 202 736 8883
F + 1 202 736 8711
E [email protected]
W www.sidley.com
Qualified. Michigan, 2009; District of Columbia, 2011
Areas of practice. Environmental.
Recent transactions
  • Represents clients in environmental regulatory, administrative and litigation matters.
  • Represents clients' shale gas development and hydraulic fracturing in administrative rulemaking and regulatory litigation.