National Ass'n of Clean Water Agencies v. Environmental Protection Agency
734 F.3d 1115
D.C. Cir.2013Background
- EPA promulgated MACT emission standards for sewage sludge incineration units under Clean Air Act §129 in March 2011 after a court-ordered deadline; EPA treated such units as "solid waste incineration units" under §129(g)(1).
- EPA subdivided units into two categories (multiple hearth and fluidized bed), surveyed a targeted set of facilities (data from 9 municipalities plus state databases), and set MACT floors using that dataset and statistical methods.
- EPA used (1) control-technology targeting to choose units to test, (2) a statistical formula to judge whether datasets <12% of population could represent the top 12%, (3) an "upper prediction limit" (99% UPL) to account for variability, and (4) a three-times method-detection-level test to handle nondetects.
- Petitioners (NACWA and Sierra Club) challenged EPA's authority to regulate under §129 (vs §112) and challenged multiple aspects of EPA's MACT-floor methodology (insufficient/targeted dataset, use of control-technology proxy, UPL and variability treatment, nondetect handling, monitoring, subcategorization). MaxWest intervened but raised issues outside petitioners' scope.
- The D.C. Circuit upheld EPA's §129 jurisdiction (Chevron deference) but remanded parts of the MACT-floor methodology for further explanation (without vacating the standards): specifically EPA must clarify the role of Part 503 data, the UPL and variability analysis, and the statistical extrapolation used to fill dataset gaps.
Issues
| Issue | Plaintiff's Argument | Defendant's Argument | Held |
|---|---|---|---|
| Authority to regulate sewage sludge incinerators under §129 vs §112 | NACWA: "from the general public" means proximate source; sewage sludge is produced by POTWs and thus not covered by §129 | EPA: "from" may refer to original/but-for source; sewage sludge ultimately originates from the public; §129 reasonably covers these units | Court: statute ambiguous; EPA's original-source interpretation is reasonable under Chevron step two — EPA has authority under §129 |
| Use of control-technology targeting (selecting units by controls rather than by measured emissions) | Sierra Club: unlawful/arbitrary because non-technology factors affect emissions; EPA must show control tech largely determines emissions | EPA: Part 503 and targeted selection make sludge streams relatively homogeneous; control tech is a reasonable proxy | Court: EPA failed to show with substantial evidence that non-technology factors are negligible; remand for EPA to explain/support the proxy choice |
| Dataset insufficiency and statistical extrapolation (<12% sample; sample-size formula) | NACWA/Sierra Club: §129 requires MACT floors reflect best-performing 12%; EPA cannot lawfully extrapolate from less-than-12% data or must justify representativeness | EPA: statute allows estimation; used a statistical formula to determine minimum observations and relied on normality assumptions and conservative variable choices | Court: EPA may estimate but must substantiate its statistical method and choice of parameters; remand for detailed justification of the extrapolation and variable selection |
| Variability and Upper Prediction Limit (UPL) to set floors | Sierra Club/NACWA: UPL does not clearly represent the "average emissions limitation achieved" or worst-foreseeable conditions; UPL may misstate true average; UPL may not capture sludge-content variability | EPA: UPL models a 99%-confidence upper bound for future 3-run averages and accounts for intra- and (EPA says) inter-unit variability; Part 503 reduces sludge variability | Court: EPA must clarify (1) how UPL equates to the §129 "average" requirement, (2) why UPL reasonably predicts worst-foreseeable performance, and (3) whether and how UPL accounts for more than intra-unit variability; remand for explanation |
| Non-detect data handling (3x representative MDL) | Sierra Club: three-times-MDL approach may not reflect what best performers actually achieve | EPA: measurement imprecision near MDL justified inflating to 3x to reach reasonably precise values; method has technical basis | Court: upheld EPA's nondetect method as reasonable and within technical deference |
| Monitoring and subcategorization | Sierra Club: EPA should mandate continuous emissions monitoring for all pollutants; NACWA: more subcategories (e.g., backup/emergency units) needed | EPA: statute allows parameter monitoring and discretion on subcategorization; no reliable data supported more subcategories | Court: monitoring scheme lawful (continuous monitoring not required by §129); subcategorization into two types (multiple hearth/fluidized bed) upheld; EPA's refusal to further subdivide not arbitrary |
Key Cases Cited
- Chevron U.S.A., Inc. v. Natural Resources Defense Council, 467 U.S. 837 (agency deference framework)
- Natural Resources Defense Council v. EPA, 489 F.3d 1250 (D.C. Cir. 2007) (interpretation of §129 definitions)
- Sierra Club v. EPA, 167 F.3d 658 (D.C. Cir. 1999) (MACT-floor estimation principles)
- Cement Kiln Recycling Coalition v. EPA, 255 F.3d 855 (D.C. Cir. 2001) (limitations on MACT-technology proxy)
- Sierra Club v. EPA ("Brick MACT"), 479 F.3d 875 (D.C. Cir. 2007) (rejecting MACT approach when non-technology factors matter)
- Mossville Environmental Action Now v. EPA, 370 F.3d 1232 (D.C. Cir. 2004) (upholding use of existing standard when variability prevents identifying best performers)
- Northeast Md. Waste Disposal Authority v. EPA, 358 F.3d 936 (D.C. Cir. 2004) (agency's MACT data-gathering latitude and remand standards)
- Husqvarna AB v. EPA, 254 F.3d 195 (D.C. Cir. 2001) (deference on cost-effectiveness judgments)
