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Regulation of fracking

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Fracking
Shale gas drilling rig near Alvarado, Texas
Shale gas drilling rig nearAlvarado, Texas
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Environmental impact
Regulation
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Countries using or considering to usefracking have implemented different regulations, including developing federal and regional legislation, and local zoning limitations.[1][2] In 2011, after public pressure France became the first nation to ban hydraulic fracturing, based on theprecautionary principle as well as the principal of preventive and corrective action of environmental hazards.[3][4][5][6] The ban was upheld by an October 2013 ruling of theConstitutional Council.[7] Some other countries have placed a temporary moratorium on the practice.[8] Countries like the United Kingdom andSouth Africa, have lifted their bans, choosing to focus on regulation instead of outright prohibition.[9][10]Germany has announced draft regulations that would allow using hydraulic fracturing for the exploitation of shale gas deposits with the exception ofwetland areas.[11]

The European Union has adopted a recommendation for minimum principles for using high-volume hydraulic fracturing.[12] Its regulatory regime requires full disclosure of all additives.[13] In the United States, the Ground Water Protection Council launched FracFocus.org, an online voluntary disclosure database for hydraulic fracturing fluids funded by oil and gas trade groups and the U.S. Department of Energy.[14][15] Hydraulic fracturing is excluded from theSafe Drinking Water Act's underground injection control's regulation, except whendiesel fuel is used. The EPA assures surveillance of the issuance of drilling permits whendiesel fuel is employed.[16]

On 17 December 2014, New York state issued a statewide ban onhydraulic fracturing, becoming the second state in the United States to issue such a ban afterVermont.[17]

Definitions

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Well stimulation
Well stimulation methods. Fracking is highlighted in yellow.


Regulation of fracking presupposes that 'fracking' is defineda priori.Well stimulation is a broad term used to describe the various techniques andwell interventions that can be used to restore or enhance the production ofhydrocarbons from anoil well, or energy from a geothermal well.

Hydraulic fracturing (fracking) and acidising are two of the most common methods for well stimulation. The flow chart shows that hydraulic fracking and acid fracking, highlighted in yellow, are two categories of unconventional hydraulic methods. But acidising is complicated by the fact that matrix acidising is considered conventional. Note that it takes place below the fracture gradient of the rock.

In the UK legislative and hydrocarbon permitting context (seeFracking in the United Kingdom), Adriana Zalucka et al. have reviewed the various definitions,[18] as well as the role of key regulators and authorities, in a peer-reviewed article published in 2021.

Zalucka et al.[18] conclude that the UK legislation concerning the legal definitions was, and remains, confusing, ambiguous, incomplete, self-contradictory, and full of legal loopholes. To solve this problem they have proposed a new robust definition for unconventional well treatments:

All well stimulation treatments of oil and gas wells which increase the permeability of the target rock volume to higher than 0.1 millidarcies beyond a 1 m radius from the borehole.

The above definition focuses on increasing permeability, rather than on any particular extraction process. It is quantitative, using the generally agreed 0.1 md cut-off value, below which rocks are considered impermeable. It exempts borehole cleaning processes like acid squeeze or acid wash from being classed as unconventional, by using the 1 m radius criterion. It avoids a definition based on, for example, the quantity of water injected, which is controversial,[19] or the injection pressure applied (whether the treatment is above or below the fracture gradient, as shown in the flow chart above). It also exempts non-hydrocarbon wells from being classed as unconventional.

The definition takes into account the views of the hydrocarbon industry and the US Geological Survey, in particular. A low permeability (by consensus defined as less than 0.1 millidarcies) implies that the resource is unconventional, meaning that it requires specialmethods to extract the resource. Above that value, conventional methods suffice. Unconventional resources are also characterised by being widelydistributed, with low energy density (i.e. in a low concentration) and ill-defined in volume. There are no discrete boundaries, in contrast to thosebounding a conventional hydrocarbon reservoir.

Approaches

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Risk-based approach

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The main tool used by this approach is risk assessment. Arisk assessment method, based on experimenting and assessing risk ex-post, once the technology is in place. In the context of hydraulic fracturing, it means that drilling permits are issued and exploitation conducted before the potential risks on the environment and human health are known. The risk-based approach mainly relies on a discourse that sacralizestechnological innovations as an intrinsic good, and the analysis of such innovations, such as hydraulic fracturing, ismade on a sole cost-benefit framework, which does not allowprevention or ex-ante debates on the use of the technology.[20] This is also referred to as "learning-by-doing".[21] Arisk assessment method has for instance led to regulations that exist in the hydraulic fracturing in the United States (EPA will release its study on the effect of hydraulic fracturing on groundwater in 2014, though hydraulic fracturing has been used for more than 60 years. Commissions that have been implemented in the US to regulate the use of hydraulic fracturing have been created after hydraulic fracturing had started in their area of regulation. This is for instance the case in the Marcellus shale area where three regulatory committees were implemented ex-post.[22]

Academic scholars who have studied the perception of hydraulic fracturing in the North of England have raised two main critiques of this approach. Firstly, it takes scientific issues out of thepublic debate since there is no debate on the use of a technology but on its effects. Secondly, it does not preventenvironmental harm from happening since risks are taken then assessed instead of evaluated then taken as it would be the case with aprecautionary approach to scientific debates. The relevance and reliability ofrisk assessments in hydraulic fracturing communities has also been debated amongst environmental groups, health scientists, and industry leaders. A study has epitomized this point: the participants to regulatory committees of the Marcellus shale have, for a majority, raised concerns about public health although nobody in these regulatory committees had expertise in public health. That highlights a possible underestimation of public health risks due to hydraulic fracturing. Moreover, more than a quarter of the participants raised concerns about the neutrality of the regulatory committees given the important weigh of the hydraulic fracturing industry.[22] The risks, to some like the participants of the Marcellus Shale regulatory committees, are overplayed and the current research is insufficient in showing the link between hydraulic fracturing andadverse health effects, while to others like local environmental groups the risks are obvious andrisk assessment is underfunded.[21]

Precaution-based approach

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The second approach relies on theprecautionary principle and the principal of preventive and corrective action of environmental hazards, using the best available techniques with an acceptable economic cost to insure the protection, the valuation, the restoration, management of spaces, resources and natural environments, of animal and vegetal species, of ecological diversity and equilibriums.[6] Theprecautionary approach has led to regulations as implementedin France andin Vermont, banning hydraulic fracturing.[5][23]

Such an approach is called upon by social sciences and the public as studies have shown in the North of England and Australia.[20][21] Indeed, in Australia, the anthropologist who studied the use of hydraulic fracturing concluded that the risk-based approach was closing down the debate on the ethics of such a practice, therefore avoiding questions on broader concerns that merely the risks implied by hydraulic fracturing. In the North of England, levels of concerns registered in the deliberative focus groups studied were higher regarding the framing of the debate, meaning the fact that people did not have a voice in the energetic choices that were made, including the use of hydraulic fracturing. Concerns relative to risks of seismicity and health issues were also important to the public, but less than this. A reason for that is that being withdrawn the right to participate in the decision-making triggered opposition of both supporters and opponents of hydraulic fracturing.

The points made to defend such an approach often relate toclimate change and theimpact on the direct environment; related to public concerns on the rural landscape for instance in the UK.[21] Energetic choices indeed affect climate change since greenhouse gas emissions from fossil fuels extraction such as shale gas and oil contribute to climate change. Therefore, people have in the UK raised concerns about the exploitation of these resources, not just hydraulic fracturing as a method. They would hence prefer a precaution-based approach to decide whether or not, regarding the issue of climate change, they want to exploit shale gas and oil.

Framing of the debate

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There are two main areas of interest regarding how debates on hydraulic fracturing for the exploitation ofunconventional oil andgas have been conducted.

"Learning-by-doing" and the displacement of ethics

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A risk-based approach is often referred to as "learning-by-doing" by social sciences. Social sciences have raised two main critiques of this approach. Firstly, it takes scientific issues out of the public debate since there is no debate on the use of a technology but on its impacts. Secondly, it does not preventenvironmental harm from happening since risks are taken then assessed instead of evaluated then taken. Public concerns are shown to be really linked to these issues of scientific approach. Indeed, the public in the North of England for instance fears "the denial of the deliberation of the values embedded in the development and application of that technology, as well as the future it is working towards" more than risks themselves. The legitimacy of the method is only questioned after its implementation, not before. This vision separates risks and effects from the values entitled by a technology. For instance, hydraulic fracturing entitles a transitional fuel for its supporters whereas for its opponents it represents afossil fuel exacerbating thegreenhouse effect andglobal warming. Not asking these questions leads to seeing only the mere economiccost-benefit analysis.[21]

This is linked to a pattern of preventing non-experts from taking part in scientific-technological debates, including their ethical issues. An answer to that problem is seen to be increasedpublic participation so as to have the public deciding which issues to address and what political and ethical norms to adopt as a society. Another public concern with the "learning-by-doing" approach is that the speed of innovation may exceed the speed of regulation and since innovation is seen as serving private interests, potentially at the expense ofsocial good, it is a matter of public concern.Science and Technology Studies have theorized "slowing-down" and theprecautionary principle as answers. The claim is that the possibility of an issue is legitimate and should be taken into account before any action is taken.[21]

Variations in risk-assessment of environmental effects of hydraulic fracturing

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Issues also exist regarding the wayrisk assessment is conducted and whether it reflects some interests more than others. Firstly, an issue exists about whetherrisk assessment authorities are able to judge theimpact of hydraulic fracturing in public health. A study conducted on the advisory committees of theMarcellus Shale gas area[22] has shown that not a single member of these committees hadpublic health expertise and that some concern existed about whether the commissions were not biased in their composition. Indeed, among 51 members of the committees, there is no evidence that a single one has any expertise inenvironmental public health, even after enlarging the category of experts to "include medical and health professionals who could be presumed to have some health background related toenvironmental health, however minimal". This cannot be explained by the purpose of the committee since all threeexecutive orders of the different committees mentionedenvironmental public health related issues. Another finding of the authors is that a quarter of the opposed comments mentioned the possibility of bias in favor of gas industries in the composition of committees. The authors conclude saying that political leaders may not want to raisepublic health concerns not to handicap further economic development due to hydraulic fracturing.

Secondly, the conditions to allow hydraulic fracturing are being increasingly strengthened due to the move from governmental agencies' authority over the issue to elected officials' authority over it. The Shale Gas Drilling Safety Review Act of 2014 issued inMaryland[24] forbids the issuance of drilling permits until a high standard "risk assessment ofpublic health andenvironmental hazards relating to hydraulic fracturing activities" is conducted for at least 18 months based on the Governor'sexecutive order.

Institutional discourse and the public

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Aqualitative study using deliberative focus groups has been conducted in the North of England,[21] where the Bowland-Hodder shale, a bigshale gas reservoir, is exploited by hydraulic fracturing. These group discussions reflect many concerns on the issue of the use ofunconventional oil and unconventional gas. There is a concern about trust linked with a doubt on the ability or will of public authorities to work for the greatersocial good since private interests and profits of industrial companies are seen as corruptive powers. Alienation is also a concern since the feeling of a game rigged against the public rises due to "decision making being made on your behalf without being given the possibility to voice an opinion". Exploitation also arises since economic rationality that is seen as favoring short-termism is accused of seducingpolicy-makers and industry. Risk is accentuated by what is hydraulic fracturing as well as what is at stake, and "blind spots" of current knowledge as well asrisk assessment analysis are accused of increasing the potentiality of negative outcomes. Uncertainty and ignorance are seen as too important in the issue of hydraulic fracturing and decisions are therefore perceived as rushed, which is why participants favored some form ofprecautionary approach. There is a major fear on the possible disconnection between the public's and the authorities' visions of what is a good choice for the good reasons.

It also appears that media coverage and institutional responses are widely inaccurate to answer public concerns. Indeed, institutional responses to public concerns are mostly inadequate since they focus onrisk assessment and giving information to the public that is considered anxious because ignorant. But public concerns are much wider and it appears that public knowledge on hydraulic fracturing is rather good.[21]

The hydraulic fracturing industry has lobbied for permissive regulation in Europe,[25] the US federal government, and US states.[26] On 20 March 2015 the rules for disclosing the chemicals used were tightened by the Obama administration.[27] The new rules give companies involved 30 days from the beginning of an operation on federal land to disclose those chemicals.[27]

See also

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References

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  1. ^Nolon, John R.; Polidoro, Victoria (2012)."Hydrofracking: Disturbances Both Geological and Political: Who Decides?"(PDF).The Urban Lawyer.44 (3):1–14. Retrieved21 December 2012.
  2. ^Negro, Sorrell E. (February 2012)."Fracking Wars: Federal, State, and Local Conflicts over the Regulation of Natural Gas Activities"(PDF).Zoning and Planning Law Report.35 (2):1–14. Retrieved1 May 2014.
  3. ^Patel, Tara (31 March 2011)."The French Public Says No to 'Le Fracking'".Bloomberg Businessweek. Archived fromthe original on 4 April 2011. Retrieved22 February 2012.
  4. ^Patel, Tara (4 October 2011)."France to Keep Fracking Ban to Protect Environment, Sarkozy Says".Bloomberg Businessweek. Archived fromthe original on 8 October 2011. Retrieved22 February 2012.
  5. ^ab"LOI n° 2011-835 du 13 juillet 2011 visant à interdire l'exploration et l'exploitation des mines d'hydrocarbures liquides ou gazeux par fracturation hydraulique et à abroger les permis exclusifs de recherches comportant des projets ayant recours à cette technique"
  6. ^ab"Article L 110-1 du Code de l'Environnement"
  7. ^"Fracking ban upheld by French court".BBC. 11 October 2013. Retrieved16 October 2013.
  8. ^Moore, Robbie."Fracking, PR, and the Greening of Gas".The International. Archived fromthe original on 21 March 2013. Retrieved16 March 2013.
  9. ^Bakewell, Sally (13 December 2012)."U.K. Government Lifts Ban on Shale Gas Fracking". Bloomberg. Retrieved26 March 2013.
  10. ^Hweshe, Francis (17 September 2012)."South Africa: International Groups Rally Against Fracking, TKAG Claims".West Cape News. Retrieved11 February 2014.
  11. ^Nicola, Stefan; Andersen, Tino (26 February 2013)."Germany agrees on regulations to allow fracking for shale gas". Bloomberg. Retrieved1 May 2014.
  12. ^"Commission recommendation on minimum principles for the exploration and production of hydrocarbons (such as shale gas) using high-volume hydraulic fracturing (2014/70/EU)".Official Journal of the European Union. 22 January 2014. Retrieved13 March 2014.
  13. ^Healy, Dave (July 2012).Hydraulic Fracturing or 'Fracking': A Short Summary of Current Knowledge and Potential Environmental Impacts(PDF) (Report).Environmental Protection Agency. Retrieved28 July 2013.
  14. ^Hass, Benjamin (14 August 2012)."Fracking Hazards Obscured in Failure to Disclose Wells". Bloomberg. Retrieved27 March 2013.
  15. ^Soraghan, Mike (13 December 2013)."White House official backs FracFocus as preferred disclosure method".E&E News. Archived fromthe original on 31 October 2020. Retrieved27 March 2013.
  16. ^[1], Environmental Protection Agency
  17. ^Editorial Board (17 December 2014)."Gov. Cuomo Makes Sense on Fracking".New York Times. Retrieved18 December 2014.
  18. ^abZalucka A, Goodenough A, and Smythe D 2021. Acid stimulation: fracking by stealth continues despite the moratorium in England,Energy Policy 153: 112244.
  19. ^Smythe, D. and Haszeldine, S. 2017. Could fracking creep under the radar?Nature [Correspondence], 24 August 2017.
  20. ^abde Rijke"Hydraulically fractured: unconventional gas and anthropology",Anthropology today, Volume 29, Number 2, April 2013
  21. ^abcdefghWilliams, Laurence, John"Framing fracking: public responses to potential unconventional fossil fuel exploitation in the North of England", Durham thesis, Durham University, 2014
  22. ^abcGoldstein, Kriesky, Pavliakova"Missing from the table: role of the environmental public health community in governmental advisory commission related to the Marcellus Shale Drilling", University of Pittsburgh, inEnvironmental Health Perspectives, Volume 120, Number 4, April 2012
  23. ^"Vermont Act 152"
  24. ^"Shale Gas Drilling Safety Review Act of 2014"
  25. ^Lipton, Eric; Hakim, Danny (18 October 2013)."Lobbying Bonanza as Firms Try to Influence European Union". The New York Times.
  26. ^Kaplan, Thomas (25 November 2011)."Millions Spent in Albany Fight to Drill for Gas". The New York Times.
  27. ^abMATTHEW DALY; JOSH LEDERMAN (20 March 2015)."Politics Fracking: US Tightens Rules for Chemical Disclosure". ABC News Internet Ventures. Associated Press. Retrieved20 March 2015.

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