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Sierra Club v. Environmental Protection Agency
479 F.3d 875
D.C. Cir.
2007
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*2 Before: GINSBURG, Chief Judge, TATEL, Circuit Judge, and WILLIAMS, Senior Circuit Judge.

Opinion for the Court filed PER CURIAM.
Concurring opinion filed Senior Circuit Judge WILLIAMS.
PER CURIAM: In case, this the Sierra Club challenges the Environmental Protection Agency’s air pollution standards for brick and ceramics kilns. Because most of the standards vio late the Clean Air Act as interpreted by this Court in Cement Kiln Recycling Co EPA, alition v. (D.C.Cir. F.3d 855 2001) (per curiam), and National Lime Ass’n EPA, 233 F.3d 625 (D.C.Cir.2000), and because the remaining standards vio late the Act’s requirements for “work practice standards,” we vacate the stan dards in their entirety and remand for further proceedings consistent with opinion.

I. The Act, Clean Air §§ 7401- 7671q, directs the Environmental Protec- tion Agency to establish emission stan- dards for “major sources” of hazardous air pollutants listed in the statute. Id. James S. argued Pew the cause and filed 7412(d)(1). § Kiln, we de- the briefs petitioner. scribed the Act as follows: Eric G. Hostetler, Attorney, U.S. De- Until the Clean Air Act partment Justice, argued the cause for required the Environmental Protection respondent. With him on the brief was Agency to set pollution risk-based air John Cruden, C. Deputy Assistant Attor- standards that provide would an “ample practice is achieved public protect safety to

margin ” .... source similar also 7412(b)(1)(B); see best controlled § Id. health.” sources, 151, 322 101-490, 7412(d)(3). For NO. REP. H.R. *3 the problems address not (1990). To “shall achievable deems EPA what regulation, risk-based of implementation average the than[] stringent be less in Act 1990 the amended Congress best by the achieved limitation emission stringent most the to set EPA require existing of the percent 12 performing achievable, U.S.C. 42 standards has Administrator (for the which sources “based is, standards 7412(d)(2), that § information) As we ....” Id. emissions emissions in reduction maximum the on II, EPA Lime National in explained of by application achieved can be which through requirements technology.” these implements control available best [the] (1989), first Agency 133 the 101-228, at process: two-step NO. S.REP. at News Admin. & Cong. pollutant for each U.S.Code emission sets 3385, 3518. then deter- and category source and ... 42 included amendments The 1990 standards, stricter whether mines EPA 7412(d) directs § —which limits, are “beyond-the-floor” as known listed of limiting emissions standards set in listed the factors of light in achievable (“HAPs”), id. pollutants air hazardous 629. at 7412(d)(2). F.3d 233 section major sta- (e)(l)-(2), 7412(b), §§ 7412(d)(2) pro- sources. tionary 857-58. Kiln, 255 F.3d that: vides Sier- the considered Kiln In Cement require ... shall Emission emission argument in Club’s of reduction ra degree maximum the vio- pollu- air combustors waste hazardous hazardous the of ... Act, the section the to this of subject tants section lated into consid- Administrator, taking at 859. the case. this in at issue provision such achieving of cost the eration had identified sources, EPA existing For any non-air reduction, and emission of sources percent best-performing the im- and environmental health quality Among information. it had which deter- requirements, energy pacts the me- identified then sources, EPA these or for new is achievable mines technology, control emission dian source’s .... sources achievable “maximum the it called which guidance, general Supplementing control”— “MACT technology” —or stringency minimum imposed Congress limitation emission “average” the as “emis them calls requirements —EPA Id.; 42 U.S.C. see re performers. without “apply floors”—which sion the factors identified next 7412(d)(3)(A). the other or costs § either gard in section MACT listed the using methods source worst-performing EPA, Ass’n Lime 7412(d)(2).” Nat'l the emission floor (“Na (D.C.Cir.2000) 625, 629 F.3d For at 859. F.3d source. of level ”). sources”— For “new II Lime tional ap- the same followed sources, EPA new be construction which instead except proach, stan emission publishes after gins as source median technology 7411(a)(2) § “[t]he dards, 42 U.S.C. — technology control, MACT emis of reduction degree maximum Id.; source. best-performing single ... shall achievable deemed that is sions 7412(d)(3). 42 U.S.C. see than stringent less be not The Sierra argued Club that this tech- Cement Kiln was not the first time this nology-based approach violated section court invalidated an EPA interpretation of 7412(d)(3)’srequirement that floors reflect 7412(d)(3). section Six earlier, months emissions actually “achieved” “achieved II, National Lime we considered the Sier in practice” by the best-performing ra Club’s challenge to EPA’s setting of “no sources. 255 F.3d at 861. In response, control” is, floors—that no emission floors EPA argued that 7412(d)(3)’s section floor at all—for certain HAPs emitted ce provision “is a gloss” on section 7412(d)(2), ment plants. 233 F.3d at 633-34. De which requires that beyond-the-floor emis- fending decision, its EPA relied on Sierra *4 sion standards be “achievable” by all EPA, Club v. 167 (D.C.Cir.1999) F.3d 658 sources, based on costs and other factors. (“Sierra”), in which we explained that Id. According EPA, to 7412(d)(3) section “EPA justified would be in setting incorporates 7412(d)(2)’s seetion achieva- aat level that is a reasonable esti bility requirement, meaning that emission mate of the performance of the ‘best con floors must also be achievable by all trolled similar unit’ under the worst rea sources. Id. rejected We EPA’s interpre- sonably foreseeable circumstances.” Id. at tation, finding it to be an impermissible 665. Sierra, Based on EPA argued that reading of the statute’s unambiguous lan- because plants cement used no emission guage: control technology, “no control” floors rea 7412(d)(3) ... limits the scope sonably estimated variability among the of the word “achievable” in section best performers. National II, Lime 233 7412(d)(2). While standards achievable F.3d at 633. We found EPA’s interpreta by all sources using the MACT control tion of the statute untenable: might also ultimately reflect what the

statutorily relevant Nothing sources in the achieve in statute even suggests practice, EPA may not that EPA may deviate from sec- emission levels only 7412(d)(3)’s tion requirement for that floors those listed HAPs controlled with reflect what the best performers technology. actual- To the contrary, the statute ly achieve claiming that floors must requires EPA to “promulgate regu- be achievable all lations establishing emission standards MACT technology. for each or category subcategory of ma- Id. (citing U.S.A., jor Chevron Inc. v. sources ... of Natural air hazardous pollu- Council, Res. 467 837, U.S. tants 842-43, listed regulation.” for Def. [42 U.S.C.] 104 2778, S.Ct. 81 (1984) L.Ed.2d 694 .... (holding that if Congress spoken has di Contrary to EPA’s argument, nothing rectly to the disputed issue of statutory in Sierra relieves it of the clear statuto- construction, “that is the end of the mat ry obligation to set emission standards ter; court, for the as well as the agency, for each listed HAP. Although Sierra give must effect to the unambiguously ex permits the Agency to look at technolog- pressed intent of Congress”)); see also Ne. ical controls set emission standards, Md. Waste Disposal EPA, Auth. v. 358 see 665, 167 F.3d at say does not 936, F.3d 955 (D.C.Cir.2004) curiam) (per EPA may avoid setting for standards (reiterating that floors based on achievabil HAPs not controlled with technology. ity satisfy cannot the statute’s actual achievement requirement). at chose 633-34. Following the panel deci not to file petition for rehearing en sion, banc EPA filed an unsuccessful petition for or to seek Supreme Court review. rehearing, Nat’l EPA, Lime Ass’n v. No.

879 Clay Products Structural and Brick (order 2001) de- Feb.14, (D.C.Cir. 99-1325 Manu- Clay Ceramics and Manufacturing neither sought again rehearing), but nying 26,692-94 26,690, Fed.Reg. 68 facturing, review. Court Supreme nor banc en 40 C.F.R. 2003) (to codified be (May mind, turn background this With 63). pt. are issue At case. facts rule proposed 2002, EPA issued and for brick HAP emissions limit (BSCP) and kilns products clay structural kilns. ceramics brick and and kilns new Over 500 kilns. clay ceramics Hazard- Standards Emission operate National kilns ceramics than more and and Structural Brick in- Air Pollutants ous BSCPs States. United throughout Clay Manufacturing and tile; Clay Products clay roof brick, clay pipe, clude 47,- Manufacturing, sanitaryware, Ceramics tile and include ceramics 2002) (to be codified July (proposed Production and sinks. toilets as such subcatego- 63). For pt. C.F.R. processing involves ceramics BSCPs pollu- use air no kilns few forming and which ries shales clays and common *5 proposed devices, EPA clays control tion transporting Because shapes. firing other reductions” —in infeasible, “no emissions is long distances over shales and 47,909, at Id. all. words, at no floors supply- the mines close located are kilns remaining sub- all 47,916-17. For 47,912, their in shales used and clays ing the on floors based proposed EPA categories, fired are ceramics and BSCPs products. the used devices pollution that the kilns: those types of two one in the i.e., Mins, those best-performing “tun- include continuously, which operate 47,912, 47,911, emissions. kilns; those lowest and “roller” nel” and pro- the comments 47,917. In their “period- as known cycles, in batch operate in- industry members regulations, into posed kilns brick divided EPA Mins. ic” used devices the installing brick tunnel sisted large subcategories: three be would best-performing kilns, periodic and brick Mins, tunnel small economically infeasible. and technologically into Mins ceramics It divided Mins. brick complained Club Sierra part, its ceramics For tunnel large subcategories: four non-tech- to consider failed EPA had roller ceramics tunnel Mins, small materi- type, raw fuel e.g., nology kilns. Mins, ceramics periodic and factors — ceramics Min coatings, surface and als, forth additives set standards different Reflecting con- training operator 7412(d)(3)(A), and design, —that 7412(d)(3) and sections Prot. Envtl. U.S. to emissions. into tribute subcategory each divided EPA further for Standards Emission National Agency, existing Mins. and new and Brick Pollutants Air Hazardous emit Mins ceramics and year, Each Manufacturing: Clay Products Structural hydro- HAPs, including 6,440 tons of over Re- and Comments Public Summary of acid, particu- acid, hydrochloric fluoric (hereinafter 2003) (Feb. 2-40 sponses metals, such containing toxic late matter Comments”). Public “Summary of cadmium, arsenic, beryllium, antimony, as comments, EPA’s these response In nickel, lead, manganese, cobalt, chromium, for sev- standards final se- can cause HAPs These and selenium. pollution on the based subcategories eral cancer, neuro- problems, respiratory vere second-best by the used devices adverse damage, organ logical proposed, had as performers not, Emission National effects. — reproductive “no replaced performers best Pollutants Air —and for Hazardous Standards 88 0 large reductions” floors in other sub- Most tunnel brick kilns that have

categories practice with a so-called pollution “work installed air control devices use (DLA). clean-burning standard” of dry fuels. 68 lime adsorbers Others use 26,699-26,701, 26,712-13; Fed.Reg. at see technology, including dry non-DLA lime 7412(h) § (explaining require- (DIFF), U.S.C. injection dry fabric filters lime practice ments for work (DLS/FF), filters and wet scrubber/fabric standards). (WS). in lieu of emission The Sierra scrubbers of proposed its notice reconsideration, petition Club filed rulemaking, EPA concluded that these but adhered to its pollution standards. Na- “repre- non-DLA control devices tional Emission Standards for Hazardous Reg. sented] control[ 67 Fed ].” 47,907. Pollutants Brick and Structural percentile Because the 94th (the Clay Products Manufacturing, median of the top percent) (reconsidered 69,655, 2005) 69,657 Nov. best-performing large tunnel brick kilns (to 63). pt. be codified at 40 C.F.R. non-DLA technology, EPA—as re- quired by Kiln—proposed floor The petitions Sierra Club now for re- 47,911. technology. based on this Id. at 7607(b)(1) (autho- view. See receiving But after “numerous comments rizing petitions for pro- review of EPA’s industry representatives” saying from standards). mulgation of emission The kilns were unable retrofit with WS be- Industry Brick Association and two ceram- cause of a lack of sewer access to treat ics producers intervene support of EPA. device, wastewater or with DIFF *6 production, without affecting DLS/FF II. EPA changed course in final its rule. 68 argues The Sierra Club that EPA’s 26,694. Finding that non- in methodology brick and DLA technology “potentially would have ceramics kilns violates the Clean Act’s significant impacts production on the pro- plain language interpreted by as Cement cess,” 26,695, id. at contrary to Ce- Kiln and agree. National Lime II. We requirement ment Kiln’s that floors reflect See Nat’l Cable & Telecomms. Ass’n emission levels of the best-performing Servs., X Brand Internet 545 U.S. sources, EPA excluded non-DLA technolo- 982, 125 (2005) S.Ct. 162 L.Ed.2d 820 gy from its ranking best-performing (“A judicial prior court’s construction of a kilns, 26,700. id. at It then set the floor trumps agency statute an construction ... for existing large tunnel brick kilns based prior if the court decision holds that its on DLA. Id. unambiguous construction follows from the statute.”). terms of the EPA argues “reasonably that it has con- the term performing’ strue[d] ‘best ... to ” “Achieved, not “Achievable” allow it to consider whether retrofitting above, As discussed we held particular Cement kilns with a pollution control Kiln that “EPA may not technology deviate from technically is feasible.” 7412(d)(3)’s section requirement Resp’t’s that floors Br. 27. But EPA cannot circum- reflect what the performers actually best holding vent Cement Kiln’s that section by claiming achieve that floors must be requires floors based on the by using achievable all sources MACT actually by emission level achieved (those technology.” 255 F.3d at In setting performers 861. best with the lowest the floor for existing large levels), tunnel brick emission not the emission level kilns, however, just sources, EPA did by that. by achievable all simply rede- relationship. the relevant Some to mean those strate performing” fining “best by- Agency’s citations to the record achievable of the emission levels with sources merely ap- contain assertions “[the] at 861. More- 255 F.3d all sources. See for normal fully kilns accounts over, excluding proach EPA’s rationales variability.” The actual varia- technology process non-DLA equipped with suggest only that large bility data EPA cites best-performing ranking its (the given retrofitting from sources infeasibility of tunnel kilns range, over a wide not that technology vary non-DLA kilns certain all with by high emission levels achieved other non-DLA negative impact and the range of that reflect productivity) sources one end would have on technology by sources at the other a concern levels achieved nothing more than amount to end, best-performing is nor ensuring its floor achievable about range experience wide subcategory—precisely sources ever all kilns variability at all. rejected in Cement Kiln. position omitted). (citations 255 F.3d at 865 III. Here, pro- the same flawed run large emission standards and small cess set floors for new National Cement Kiln and as well as counter tunnel brick and ceramics vari In respects—all existing large II in other tunnel brick kilns. its Lime several explained fundamental failure that it “used Agency’s rulemaking, ations on the actually levels highest at the emission level associated to set floors [i.e., sources. best-performing performers all DLA-con- achieved the[] the emission standard to set kilns] trolled Variability emis- it was intent [EPA’s] because the performance limits that reflect sion unlawful Kiln we declared continually the best-controlled estimating variability EPA’s method of *7 variability.” 68 Fed. considering achieve by lowering among performers the best 26,700 (justifying technology-based Reg. performer the to the level of worst floors kilns); Sum- existing for see also approach technology. explained: We using the same (same, mary at 2-54 of Public Comments by EPA’s claim unpersuaded are [W]e kilns). Citing range a regard to new best-performing for the that to account DLA- datapoints single from a of emission it variability, had to operational sources’ kiln, explained EPA that “[a]ll equipped performers’ floors on the worst base the sources, including the best-controlled recognized have emissions. we While sources, in emissions.” 68 variability have experience oper- a can given that control 26,700. Because these rea- variability, question relevant ational the level achieved using the emission sons technologies here is not whether predict worst-performing kilns to by the all, variability at whether experience but performers of dif- variability the the by the best- variability experienced the gave EPA little from the reasons fer by can be estimated performing sources Kiln, Agency’s this element of the relying on data the similarly floor-setting is un- methodology worst-performing using the sources lawful. case, In this the evi- MACT control. points EPA to Defending approach, its support EPA the MACT dence cites to Now v. Action accounting for Mossville Environmental as a means of approach (D.C.Cir.2004), in EPA, F.3d 1232 variability fails to demon- operational 2 may legitimately

which we held that floors fect proved “impossible reliably quanti- variability fy,” id. at that account because “each “floors must be [specified] by using must meet stan- achievable all sources MACT [source] every operating technology,” all id. at day explained: dard and under 864. We Mossville, at 1242. In conditions.” Id. factors technology [I]f other than MACT however, record evidence demonstrated do perform- indeed influence a source’s ance, reasonably the floor estimated the that not sufficient that EPA is con- variability best-performing using only actual sidered sources ... MACT (noting source. “factual data” controls....

standard on the worst-performing based accepting Even proposition “reasonably per- estimates the affecting performance factors source Here, top performers”). quantify formance defining are difficult to when contrast, control, by although EPA has in. nothing some evi- MACT the stat- performers experience requires dence that the best ute to use the MACT variability, approach. requires it has failed to show that the only set floors at the emission by per- emission levels achieved the worst best-performing level achieved given pollution formers sources. If EPA cannot meet this re- actually predict range device of emis- quirement using the MACT methodolo- sion perform- levels achieved the best gy, it must devise a approach different ers using that device. Given Cement capable producing satisfy holding may Kiln’s that EPA not use emis- the Clean Act. performers sion levels the worst esti- variability of performers mate the best Id. at 864-65. without relationship a demonstrated be- EPA’s emission two, tween the we conclude that the emis- large large brick tunnel kilns and new large sion floors for new tunnel small small tunnel and ceramics kilns suf- kilns, brick and ceramics as well as for (in fer from the same defect addition to the existing large tunnel brick violate above). defects noted rulemaking, its Act. EPA noted that it had reviewed non-tech- nology pollution prevention techniques—in Non-technology Factors particular the substitution of fuels and Kiln, rejected

In Cement clays with lower amounts of hazardous approach given MACT constituents. It found that fuel type had *8 record other evidence that factors than emissions, no appreciable effect on that technology affected emissions. 255 F.3d clays transporting long over distances was so, at In doing 863-65. we noted our impractical, and that in changes either in conclusion National Lime II that ability duplicate could affect kilns’ to their methodology, purely technology- MACT existing product 26,- lines. at satisfy approach, based would the Clean 699. Given these EPA findings, set floors Air pollution technology Act “if control only pollution based technology, on control only determining were the factor emission explaining that agree we that fac- “[w]hile (internal levels that HAP.” Id. at 863 [technology] type tors other than can af- omitted) quotation (quoting emissions, marks Nation fect we do not have the data to II, 633). al Lime 233 F.3d at We were specific degree determine the of the effect unpersuaded justifications by EPA’s twin [technology] of factors other than on emis- for refusing sions, that, to consider the effect other and we believe for the BSCP emissions, factors on namely industry, that the ef- [technology] factors other than for existing floor ... control EPA’s failure to set floors not viable MACT use are that small tunnel brick kilns and options.” Id. Though acknowledging factor, clay periodic new brick kilns violates section non-technology one at least precisely for same reason. on emis- type, appreciable had an effect justi- EPA set “no emissions sions, reductions” floors articulated the same has for tunnel kilns in Cement Kiln existing small be- fications it offered floors, kiln no i.e., percentile cause the 94th air a lack technology-based pollution technology of non- because quantify to the effects data non-technology in changes that factors were technology factors and a concern or “appropriate” not “viable.” 67 Fed. clay on clean would be unac- floors based 47,909 Reg. (explaining EPA’s rationale inability of kilns to hievable because floors, Agency for “no control” which Id. These justifications are clays. switch rule). adopted later in final EPA also they in set no more here than were valid “no all pe- emissions reductions” Cement Kiln. they explaining riodic brick too Air Act’s argues the Clean pollution technology. use no that it the emission “con- command assess has again claiming Other than that it no or “achieved” refers trol” “limitation” obligation to set floors unless sources take steps kiln take operators the deliberate to control emis- some deliberate action “hap- than to the reduce emissions rather sions, any EPA has failed to offer reason being near cleaner penstance” of located it what did here from distinguishing squarely Yet clay. Resp’t’s Br. 33-34. we what we invalidated in National Lime II. Lime II that the Clean held National in an intentional ac- requires Act neither IV. strategy tion nor a deliberate to reduce in brings This us to the one issue As explained, emissions. we Clean “[t]he neither this case controlled Air Act EPA to MACT requires the II, namely EPA’s Kiln nor National Lime ‘average upon based practice so-called work achieved’; use of sug- it nowhere limitation[s] of emission floors for the remain instead gests achievement must be 7412(h) of kilns. ing subcategories product specific of a intent.” 233 F.3d “if Air Act it is (citation omitted). provides of the Clean decision in of the Admin judgment not feasible exclusively technology even base floors prescribe or enforce an emis istrator to though non-technology factors affect emis- ..., may, Administrator sion standard Act. sion levels thus violates the thereof, promulgate design, lieu “No Control” Floors equipment, practice, operational work 7412(h)(1). That standard.” above, Lime National As noted explains that is “not section further II found unlawful EPA’s “no control” *9 standard when feasible” to set an emission categories in which the emission floors methodol application “the of measurement performers no emission of is not ogy particular to a class As we technology. 233 F.3d 633-34. and eco practicable technological due to statutory has obli explained, a “clear 7412(h)(2)(B). nomic limitations.” § for each gation to set emission standards 7412(h), HAP,” adopted Invoking not it to section listed which does allow clean- practice con standard setting standards for HAPs not work “avoid existing ceramics kilns Id. at 634. burning fuels for technology.” trolled with periodic new and roller ceramics kilns. writ of certiorari. meantime, In the it 26,712, 26,713. To justify obey must the Clean Air Act as written by its use of work practice standards, EPA Congress and interpreted by this court. pointed out that kilns, ceramics like peri- So ordered. odic use pollution no devices and cannot feasibly substitute WILLIAMS, Senior Judge, Circuit clays. Rather than setting “no control” concurring. floors, however, EPA imposed a clean- I agree entirely with the opinion court’s burning fuels standard. Id. According to and only write a paradox note in the EPA, setting a precise more floor based on relationship key beiween provisions two the emission levels achieved by the use of § 112 of the Clean Act. clean-burning fuels was not given feasible 112(d)(2) Section calls for emissions the absence of data necessary to make this standards that are the most stringent that 26,712. calculation. Id. at the EPA finds to be “achievable,” taking agree We with the Sierra Club that into account a variety of factors including EPA’s use of practice work in- cost. 42 § 7412(d)(2); see Per Cu- stead of emission floors violates section riam at 3. 112(d)(3) provides that 7412(h). That provision allows EPA to the standards “shall not be stringent” less substitute work practice standards than the emission controls that have been only if measuring emission “achieved practice.” 42 U.S.C. levels is technologically or economically § 7412(d)(3); see Per Curiam at 4. The impracticable. Here, EPA never deter- “achievable” standards have come to be mined that measuring emissions from ce- known as the “beyond-the-floor” stan- ramics kilns was impracticable; it deter- dards, see id. at meaning, obviously, only mined that it lacked emissions data ones more stringent than the “floors” es- from ceramics kilns. EPA thus had no 112(d)(3). § tablished under The language basis 7412(h) under section for using work thus embodies an assumption stan- practice sure, standards. To be as EPA dards on based achievability will be more points out, because ceramics kilns already stringent than ones merely based past use fuels, clean-burning practice work achievement. standard would have impact no on their What if meeting the “floors” is extreme- products. For reason, the same course, ly or even prohibitively costly for particu- it would have impact no on emissions. lar plants because of conditions specific to plants those (e.g., adoption of the neces-

Y. sary technology requires very costly retro- For the foregoing reasons, we vacate the fitting, or the required technology cannot, emission standards for both brick and given ce- local inputs whose use is essential, ramics kilns and remand pro- further “floor”)? achieve the For plants, these it ceedings consistent with opinion. If would seem that what has been “achieved” the Environmental Protection Agency dis- 112(d)(3) § under would not be “achiev- agrees with the Clean Air Act’s require- able” under in light of the lat- ments for standards, ter’s mandate to EPA to consider cost. should take its concerns to Congress. (Notice If that here EPA issued “beyond- no EPA disagrees with this court’s interpreta- standards, the-floor” petitioner makes *10 tion of the Act, Clean Air it should seek no complaint on score.) In other rehearing en banc or a petition file words, for a as applied to sources, some

885 statutory language by the compelled floor Appellee America, STATES UNITED “be- than stringent more to be appears yond-the-floor.” v. PERRY, Appellant. aof talking Michael all, might be Antoine were

If this produced words literal whose statute No. 05-3119. with “demonstrably at odds so result Appeals, Court States judi- justify United as to drafters” of its intentions Circuit. of Columbia District Ron States United See surgery. cial 242, 235, Inc., U.S. 489 Enterprises, Pair 13, 2006. Argued Oct. (1989) 290 1026, L.Ed.2d 103 S.Ct. 16, 2007. March Decided Contractors, v. Oceanic (quoting Griffin 3245, 73 S.Ct. Inc., U.S. (internal quotation (1982))

L.Ed.2d omitted).

marks a statute. such is not § 112

Happily Adminis- 112(d)(1) authorizes classes, types among “distinguish

trator or category within of sources sizes

and of subsec- language and the

subcategory,” refers (3) pervasively

tions “category in each for sources

standards generate authority The

subcategory.” unqualified; obviously not is

subcategories usual by the limited be it must least is not there And of reasonableness.

ideas that, with even any guarantee

necessarily every source subcategorization,

suitable meet to achieve be able

will rea- 112(d)(3) to §of application

a lawful Nonethe- subcategories.

sonably defined addi- creating basis

less, legitimate one interest be subcategories must

tional “achieved” between the relation keeping common in accord “achievable” meaning reasonable

sense

statute.

Case Details

Case Name: Sierra Club v. Environmental Protection Agency
Court Name: Court of Appeals for the D.C. Circuit
Date Published: Mar 13, 2007
Citation: 479 F.3d 875
Docket Number: 03-1202, 06-1013
Court Abbreviation: D.C. Cir.
AI-generated responses must be verified and are not legal advice.