Which Source Of Pollution Does The Clean Water Act Neglect?

T his is part of our special feature on Water in Europe and the World.

After decades of primarily country-led but incomplete work on h2o quality, in 1972, the United States' federal government enacted the contemporary structure of the Federal H2o Pollution Control Act—amend known later the 1977 amendments every bit the Make clean H2o Act (CWA).[one] 20-8 years after, the European Union (European union) adopted "Directive 2000/lx/EC of the European Parliament and of the Council establishing a framework for the Community action in the field of water policy," ameliorate known equally the Eu Water Framework Directive (WFD),[2] which replaced before and more limited policies focused on protecting sources of drinking water.[3]

While both laws seek to improve water management and the wellness of waterbodies, they differ in iii main ways. First, the European union WFD is far more comprehensive in its approach to water management than the Clean Water Deed, which—out of respect to the Usa' system of federalism—leaves many aspects of water management entirely to united states of america. 2nd, relatedly, the two laws seek have dissimilar regulatory foci. Specifically, the WFD seeks to improve the overall status of waterbodies, while the CWA concentrates on reducing surface h2o pollution from specific kinds of sources. Finally, the CWA is much easier to enforce.

The Eu H2o Framework Directive Is More Comprehensive than the United states of america Clean Water Act

"Water management" tin can refer to several types of governmental activities. These include allotment of surface water use and depletion rights, allocation of groundwater use and depletion rights, control of surface h2o pollution, command of groundwater pollution, preservation or restoration of aquatic habitat and ecosystems, and regulation of evolution near and in waterbodies, including the destruction of wetlands and mangrove forests. Nations tin can and oft do divide these different aspects of water direction among different agencies or different levels of authorities, resulting in a fragmentation of management authorities that can hamper the creation of comprehensive and holistic h2o policies with clearly defined priorities for a given water resource.[iv]

The Eu WFD seeks to avert such regulatory fragmentation by addressing well-nigh all of these aspects of water management. It emphasizes its holistic approach from the Preamble, stating that "[due west]ater is not a commercial product similar whatever other only, rather, a heritage which must be protected, dedicated and treated as such."[5] The Directive addresses both water quality and water allocation,[six] seeking to comprehensibly and sustainably manage water resources.[vii] Its concerns include both ecological quality[viii] and the increasing general man pressure on water resource,[9] and it addresses both point and diffuse source h2o pollution.[ten] Finally, the WFD clearly applies to groundwater, both in terms of groundwater employ and in terms of groundwater'southward potential bear on on surface waters and their ecosystems.[xi]

United states law, in contrast, divides h2o allocation law (mostly country constabulary) from water quality constabulary (CWA implementation). Indeed, the CWA explicitly emphasizes twice—once at the beginning and once at the end—that it is non intended to interfere with country water allocations or state water rights.[12]

Similarly, the CWA's application to groundwater contamination is much more tenuous than the WFD's. The Deed applies most directly to the "navigable waters,"[13] which it and the two federal agencies that implement the Human activity, the US Environmental Protection Agency (USEPA) and Us Army Corps of Engineers (USACE), define merely in terms of surface waters.[14] Activities that pollute groundwater generally do not trigger the Act,[15] although recent litigation has led to a split among the US Courts of Appeals regarding whether the CWA applies when facilities discharge pollutants to groundwater that is hydrologically continued to surface water.[sixteen]

Interestingly, even so, both laws give boosted protections to coastal waters. The WFD'south Preamble notes the particular vulnerabilities of coastal waters and closed seas,[17] and while its ultimate aim for pollution in freshwaters "is to achieve the elimination of priority hazardous substances," for marine waters information technology seeks to achieve "concentrations . . . near groundwork values for naturally occurring substances."[18] The CWA similarly both applies to ocean waters[19] and imposes special requirements—the ocean discharge criteria—on any entity that seeks to discharge pollutants into coastal waters.[20]

The EU Water Framework Directive and Us Clean Water Human activity Have Different Regulatory Foci and Goals

Underscoring its holistic arroyo to h2o direction, the Eu WFD focuses on river basins, "so that measures in respect of surface water and groundwaters belonging to the same ecological, hydrological and hydrogeological organization are coordinated."[21] It defines a "river basin" to be "the area of land from which all surface run-off flows through a sequence of streams, rivers and, possibly, lakes into the bounding main at a single river oral cavity, estuary or delta."[22] Fellow member nations identify the private river basins within their borders and create districts to manage them,[23] requiring such districts to establish river bowl plans[24] and programs of measures[25] that ensure that each river basin achieves the WFD's goals.[26]

In contrast, the Usa CWA focuses on cleaning upwardly discharges of pollutants to surface waters from bespeak sources—that is, "any discernible, confined, and discrete conveyance" of pollutants, like a pipage or a ditch.[27] While the Human action proclaims the lofty objective "to restore and maintain the chemical, concrete, and biological integrity of the Nation's waters,"[28] its primary prohibition forbids "the discharge of any pollutant past whatsoever person" except every bit in compliance with the Act,[29] which by and large involves getting a let.[thirty] At the end of the Act's somewhat convoluted definitions of "belch of a pollutant"[31] and subsidiary terms, and subject to exceptions contained therein, the CWA applies to any entity[32] that adds pretty much anything[33] to "waters of the United States"[34]—generally surface waters, as noted to a higher place— or the ocean[35] from an identifiable and homo-controlled conveyance (the bespeak source).

Following from their differences in regulatory focus, the European union WFD and Us CWA likewise seek to achieve different goals. For almost point source polluters, the CWA seeks to ensure compliance with engineering-based effluent limitations[36]—that is, "brake[s] . . . on quantities, rates, and concentrations of chemical, concrete, biological, or other constituents which are discharged from point sources . . . ."[37] The USEPA establishes national effluent limitations for different industrial indicate source categories, such as sewage treatment plants, coal-fired ability plants, fish processing facilities, and so forth, and the Human activity mandates that effluent limitations become more than stringent over time.[38] In addition, effluent limitations are more stringent for certain kinds of pollutants: No point source can belch "any radiological, chemic, or biological warfare agent, whatsoever high-level radioactive waste, or any medical waste,"[39] while effluent limitations for toxic pollutants must exist based on "the best available technology economically achievable," including the possibility of a complete discharge prohibition.[twoscore]

The Eu WFD, in turn, seeks to achieve "expert water condition" in all European river basins within 15 years.[41] "'Good surface water status' ways the status achieved by a surface water trunk when both its ecological status and its chemical status are at least 'good.'"[42] In turn, "'[1000]ood groundwater status' ways the status achieved by a groundwater body when both its quantitative status and its chemical status are at to the lowest degree 'skillful.'"[43] "Ecological status" categorizes surface waters in terms of the structure and part of their aquatic ecosystems.[44] Expert chemical status means that a surface water body or a groundwater body meets all of the applicable chemical concentration requirements.[45] Finally, groundwater's quantitative status assesses how badly withdrawals accept depleted the aquifer.[46]

Thus, the European union WFD focuses on overall water trunk wellness, while the CWA focuses on reducing the impacts from individual point source polluters. Still, it is of import to note that the CWA does address ambient water quality through its h2o quality standards provisions.[47] Under these provisions, the states make up one's mind what uses they want the surface water bodies within their borders to attain, then plant the water quality criteria that volition allow the water body to support those uses.[48] As a event, unlike under the WFD, the CWA contains no overarching definition of what counts equally "good" water quality. Even so, as is true in the WFD,[49] a federal "antidegradation policy" ensures that waters practise not deteriorate.[l]

The United states' Clean Water Act Is Easier to Enforce than the Eu Water Framework Directive

The The states CWA contains a number of exemptions—often for agriculture, forestry, and free energy development—that limit its applicability.[51] Nevertheless, in one case a source is bailiwick to the Act's requirements, a number of different entities tin pursue enforcement through a multifariousness of ways. For example, both the USEPA and states with delegated authority can pursue administrative, civil, and criminal enforcement actions against entities who pollute without a let, violate the terms of the permit, or lie during the permitting or enforcement process.[52] The enforcement action's severity and the penalties incurred are keyed both to the violator'south mens rea and to the amount of harm caused or risked.[53] In addition, permittees must monitor their own discharges in accord with the USEPA's rules and submit Daily Monitoring Reports to the USEPA and the relevant state agency,[54] making it easy for these agencies to compare let requirements to actual discharges and detect violators.

The USEPA likewise retains considerable authority over the USACE and states that implement the Act. For example, information technology can veto individual permits that either the USACE[55] or u.s.a.[56] event, and it both approves and can withdraw land potency to result permits.[57] In addition, the USEPA must result water quality standards for states that refuse to do so,[58] ensuring that general water quality goals exist for all waters.

Beyond government enforcement, and like most federal environmental statutes in the Us, the CWA allows denizen suits—that is, civil lawsuits in federal court by "any denizen" to enforce the Act'southward provisions.[59] And then long as the person or entity bringing suit has standing to sue[60] and follows the boosted procedures required,[61] it can sue the federal government, state officials, or private entities who are violating the Human activity.[62] If successful, the plaintiff can then recover its litigation costs, including attorney and expert witness fees.[63] In the U.s., each side in litigation generally bears its own expenses, so this fee-shifting provision encourages denizen enforcement. Moreover, both permits and Daily Monitoring Reports are public documents,[64] and then denizen plaintiffs tin easily observe polluters who are violating their permits.

Finally, citizen suits can likewise keep the USEPA and USACE accountable. Starting time, the CWA'due south denizen conform provision allows civil lawsuits against the USEPA for violations of whatsoever of its mandatory duties under the Act.[65] Second, nether the general federal Administrative Procedure Act, citizens can sue any federal bureau for decisions that are unreasonable, unconstitutional, or neglect to follow required procedures.[66]

Like the CWA, the EU WFD acknowledges the importance of enforcement and requires member states to monitor river basins.[67] However, it delegates most enforcement police force to member countries.[68] In that location are exceptions: Member states must report to the European Commission,[69] the Eu Parliament and the Commission guide water pollution abatement,[seventy] and private citizens can employ general EU law to "ensure that states depict up plans with measures capable of achieving the objectives, taking into account the factual circumstances and the diverse opposing interests."[71] Nevertheless, actual enforcement of specific river basin objectives depends primarily on what individual member states allow,[72] and each private member nation determines the penalties applicable to breaches of its ain implementation of the Directive.[73]

In add-on, the WFD acknowledges that many water bodies in Europe have already been heavily adult in ways that brand information technology difficult to render them to "good" status, altering or extending a nation's obligations to comply with the WFD's good status requirements.[74] Member nations may also phase in requirements to spread out costs,[75] tin can apply new physical alternations as reasons for not coming together WFD deadlines for "good" status,[76] and tin fifty-fifty permit the deterioration of high status waters in pursuit of sustainable development.[77] These concessions to reality complicate enforcement by potentially obscuring the actual requirements that employ to any given river basin and/or delaying the fourth dimension of compliance, and, "from a legal perspective, a member country volition not have breached its obligation then long as it implements the processes required past the WFD."[78]

Determination

The EU WFD and US CWA differ not only in their comprehensiveness and enforceability, only too in their perceived success to date. While the CWA leaves many areas of water management untouched, and hence h2o quality challenges certainly remain in the U.s.a.,[79] the Act has dramatically reduced point source pollution and is generally regarded equally a success.[eighty] In dissimilarity, there is widespread agreement that the WFD has not yet achieved its highly ambitious goals,[81] at least in part considering of its lack of enforceability.[82] Of form, the CWA also has had almost three decades longer to operate than the WFD, and thus it remains to be seen whether the WFD will eventually dramatically meliorate river basins throughout Europe.

Robin Kundis Craig is the James I. Farr Presidential Endowed Professor of Constabulary at the Academy of Utah S.J. Quinney College of Law. This inquiry was fabricated possible, in part, through generous support from the Albert and Elaine Borchard Fund for Faculty Excellence.

References:

[1] Robin Kundis Craig, The Make clean Water Act and the Constitution 10-37 (2d ed. 2009).

[ii] European Committee, Surround: The EU Water Framework Directive—integrated river basin direction for Europe, http://ec.europa.eu/environment/h2o/water-framework/index_en.html (every bit updated 08 June 2022 and viewed 15 Oct. 2022).

[3] European Commission, Introduction to the new EU Water Framework Directive, http://ec.europa.eu/environs/water/water-framework/info/intro_en.htm (every bit updated 08 June 2022 and viewed 24 October. 2022).

[4] East.yard., Robin Kundis Craig, Climate Change, Regulatory Fragmentation, and Water Triage, 79 U. Colo. L. Rev. 825, 833-69 (2008); Alejandro East. Camacho, Climate Change and Regulatory Fragmentation in the Great Lakes Basin, 17 Mich. St. J. Int'l L. 139, 146-52 (2008).

[5] Directive 2000/lx/EC of the European Parliament and of the Council establishing a framework for the Customs action in the field of water policy, at Preamble ¶ 1, (23 Oct. 2000) [hereinafter Eu Water Framework Directive].

[six] Id. at Preamble ¶¶ 4, 23, 34, & art. 1(a), (c), (d), (e), art. 4(1)(a)(iv), (b)(iii), art. 7, fine art. 9.

[7] Id. at Preamble ¶¶ 3, v, xvi, & fine art. 1(b).

[8] Id. at Preamble ¶¶ 2, 11, 19, & art. 1(a).

[ix] Id. at Preamble ¶ 4, & art. 1(a), (e).

[10] Id. art. 10.

[11] Id. at Preamble ¶¶ 20, 26, 28, 34, & art. 1(d), (due east), art. four(1)(b).

[12] 33 U.Due south.C. §§ 1251(b), (g), 1370(2).

[13] Id. §§ 1251(a), 1362(12), 1342(a), 1344(b).

[14] Id. § 1362(half-dozen); 33 UsC. § 328.iii(a); 40 C.F.R. § 122.2.

[15] Village of Oconomowoc Lake v. Dayton Hudson Corp., 24 F.3d 962, 964-66 (7th Cir. 1994); Umatilla Waterquality Protective Ass'northward, Inc. five. Smith Frozen Foods, Inc., 962 F. Supp. 1312, 1314-20 (D. Or. 1997).

[xvi] Compare Kentucky Waterways Alliance v. Kentucky Utilities Co., — F.3d —-, 2022 WL 4559315, at *seven-*10 (6th Cir. Sept. 24, 2022), and Tennessee Clean Water Network v. Tennessee Valley Auth., — F.3d —-, 2022 WL 4559103, at *half dozen-*7 (6th Cir. Sept. 24, 2022) (both holding that the fact that a coal-fired power establish'southward coal ash polluted a lake via groundwater did non subject area the power plant to Clean Water Human activity regulation), with Hawai'i Wildlife Fund 5. Canton of Maui, 886 F.3d 737, 745-47 (9th Cir. 2022) (holding that the CWA does regulate discharges of pollutants into injection wells when the pollution quickly reaches surface waters), and Upstate Forever v. Kinder Morgan Free energy Partners, L.P., 887 F.3d 637, 651-52 (fourth Cir. 2022) (holding that the CWA tin can apply to discharges into groundwater that is hydrologically continued to surface water).

[17] European union H2o Framework Directive, supra note 4, at Preamble ¶ 17.

[18] Id. at ¶ 27.

[19] 33 U.S.C. § 1362(vii)-(10), (12).

[20] Id. § 1343.

[21] European union Water Framework Directive, supra note 4, at Preamble ¶ 33; see also ¶¶ 35, 36.

[22] Id. art. 2(thirteen).

[23] Id. fine art. 3.

[24] Id. art xiii.

[25] Id. art eleven.

[26] Id. art 5.

[27] 33 U.S.C. § 1362(14).

[28] Id. § 1251(a).

[29] Id. § 1311(a).

[30] Id. §§ 1342, 1344.

[31] Id. § 1362(12).

[32] See id. § 1362(5) (broadly defining "person").

[33] See id. § 1362(six) (broadly defining "pollutant").

[34] Id. § 1362(7)

[35] Id. § 1362(eight)-(10).

[36] Id. § 1311(b), (e).

[37] Id. § 1362(eleven).

[38] Id. § 1311(b).

[39] Id. § 1311(f).

[xl] Id. § 1317(a)(two).

[41] Eu Water Framework Directive, supra note 4, art. four(1)(a)(ii), (b)(ii).

[42] Id. art. 2(18).

[43] Id. art. 2(20).

[44] Id. fine art 2(21)-(23), Addendum V.

[45] Id. arts. 2(24), (25), 4(1)(a), 16(7), Annex Five tbl. two.3.2, Annex Ix.

[46] Id. art. two(26), Annex 5 tbl. 2.ane.two.

[47] 33 U.S.C. § 1313.

[48] Id. § 1313(c).

[49] EU Water Framework Directive, supra note ane, art 4(one)(a), (b).

[fifty] 40 C.F.R. § 131.12(a).

[51] Eastward.g., 33 U.S.C. §§ 1342(fifty), 1344(f), 1362(6), 1362(14).

[52] Id. § 1319.

[53] Id.

[54] Id. § 1318.

[55] Id. § 1344(c).

[56] Id. § 1342(d).

[57] Id. § 1342(b), (c).

[58] Id. § 1313(c)(4).

[59] Id. § 1365(a).

[60] Id. § 1365(g).

[61] Id. § 1365(b).

[62] Id. § 1365(a)(1).

[63] Id. § 1365(d).

[64] Id. § 1318(b), 1342(j), 1344(o).

[65] Id. § 1365(a)(2).

[66] v U.Southward.C. § 706.

[67] European union Water Framework Directive, supra notation four, fine art. 8.

[68] Id. at Preamble ¶ 53.

[69] Id. art. xv.

[lxx] Id. arts. 16, 17.

[71] Olivia Odom Light-green, Ahjond S. Garmestani, Helena F. M. W. Van Rijswick, & Andrea Thou. Keessen, EU h2o governance: striking the correct residuum between regulatory flexibility and enforcement?, 18(2) Environmental and Order ten, at 4 (2013). http://dx.doi.org/10.5751/ES-05357-180210.

[72] European union Water Framework Directive, supra note 4, art. 24.

[73] Id. art. 23.

[74] Id. art. 4(iii), 4(v).

[75] Id. at Preamble ¶ 29, art. ix.

[76] Id. art. 4(7).

[77] Id.

[78] Sarah Thomas, The Water Framework Directive: To Succeed or Not to Succeed?, 26:5 Water & Wastewater Int'l (Sept. ane, 2022), https://www.waterworld.com/articles/wwi/impress/volume-26/issue-5/regulars/legal-perspective/the-water-framework-directive-to-succeed-or-not-to-succeed.html.

[79] E.g., Paul Greenberg, The Clean Water Act at 40: There's Withal Much Left to Do, YaleEnvironment360 (May 21, 2022), https://e360.yale.edu/features/the_clean_water_act_at_40_theres_still_much_left_to_do.

[80] James Salzman, Why Rivers No Longer Fire: The Clean Water Act Is One of the Greatest Successes in Environmental Police, Slate.com (Dec. 10, 2022), https://slate.com/technology/2012/12/clean-water-act-40th-anniversary-the-greatest-success-in-ecology-law-made-rivers-stop-burning.html; Jeff Inglis, Tom Van Heeke, Gideon Weissman, Lindsey Hallock, & John Rumpler, Surroundings America Inquiry & Policy Center, Waterways Restored: The Make clean H2o Act's Impact on 15 American Rivers, Lakes and Bays (Oct. 2022), available at https://environmentamerica.org/sites/environment/files/EA_waterways_scrn.pdf.

[81] Eastward.grand., Nikolaos Voulvoulis, Karl Dominic Arpon, &, Theodoros Giakoumis, The Eu H2o Framework Directive: From great expectations to bug with implementation, 575 Sci. Total Env't 358, 358-66 (2017).

[82] East.g., Green et al., supra note 71, at half-dozen-7.

Photo: H2o is poured | Shutterstock
Published on December eleven, 2022.

Source: https://www.europenowjournal.org/2018/12/10/water-quality-law-in-the-us-and-eu-a-comparison-of-the-clean-water-act-and-water-framework-directive/

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