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CERCLA, CWA and State Law: Complexities With Overlapping Authorities - - PowerPoint PPT Presentation

Presenting a live 90-minute webinar with interactive Q&A CERCLA, CWA and State Law: Complexities With Overlapping Authorities Navigating Requirements for Soil and Sediment Remediation and Storm and Surface Water Management THURSDAY, AUGUST


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CERCLA, CWA and State Law: Complexities With Overlapping Authorities

Navigating Requirements for Soil and Sediment Remediation and Storm and Surface Water Management

Today’s faculty features:

1pm Eastern | 12pm Central | 11am Mountain | 10am Pacific

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THURSDAY, AUGUST 8, 2013

Presenting a live 90-minute webinar with interactive Q&A

Joan Snyder, Partner, Stoel Rives, Portland, Ore. Steven G. Jones, Holland & Hart, Salt Lake City, Utah

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CERCLA, CWA and State Law: Complexities With Overlapping Authorities Steven G. Jones

Holland & Hart LLP

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6

Overlapping and Sometimes Conflicting Laws and Regulations

  • Overview - what are the applicable laws and

regulations

  • What law governs soil and sediment

remediation?

  • Which laws govern storm and surface water

management?

  • Are there intersections between the two?
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7

CERCLA, State Superfund Laws & the Clean Water Act

 In the context, two primary bodies of law govern

the response to contamination

  • CERCLA and its state-law equivalents
  • The Clean Water Act (CWA)
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8

CERCLA / State Superfund Statutes

 The Comprehensive

Environmental Response Compensation and Liability Act (CERCLA) is commonly known as the Superfund statute

 Many (but not all) states have

equivalent statutes

 Some state statutes provide for

cleanup of petroleum, and may grant attorney’s fees

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9

CERCLA/State Law Approach

 These statutes are reactive:

we’ve got a mess on our hands – how are we going to clean it up and who is going to pay for it?

 Joint and several liability for

“PRPs”

  • Any PRP is responsible for 100% of

the cleanup costs

  • PRPs can seek cost recovery and

contribution from others

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10

Clean Water Act

 The Federal Water Pollution Control Act is commonly known as

the Clean Water Act. Here again, many states have equivalent statutory law

 State environmental departments can (and frequently do) have

delegated enforcement authority for the CWA, but state water quality standards may go beyond the CWA standards

 In addition to NPDES permits, most states also issue stormwater

discharge permits for industrial and construction discharges

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CWA Approach is Preventative

 CWA seeks to prevent pollution  All discharges are presumed to violate the CWA, except those

that are permitted

 “The federal Clean Water Act gives states the primary

responsibility for implementing programs to protect and restore water quality, including monitoring and assessing the nation's waters.” Dep’t of Ecology: Clean Water Act Monitoring Strategy for Washington

State

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NPDES Permits and TMDL Limits

 “Point Source” discharges are permitted using NPDES permits  These set effluent limits and, in certain instances, mixing zones  Self-reporting is usually required and can generate private party

enforcement

 TMDLs are limits issued for “impaired” water bodies , restricting

discharges of pollutants to those waters

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Implementation and Enforcement - CERCLA

 CERCLA and its state-law equivalents are enforced through

regulatory orders from EPA and/or state environmental agencies

 Based on the threat of strict, joint and several liability, privately

managed cleanups are common

 Cost recovery and contribution actions allow recovery of

disproportionate cleanup costs

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Implementation and Enforcement - CWA

 Government enforcement is done using regulatory orders  However, private party enforcement is common, based on self-

reported violations

 This includes private parties requesting action from regulators

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The Confluence – When Statutes Collide!!

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The CWA’s Permit Shield and Federally Permitted Releases Under CERCLA

 CWA ¶ 402(k) is commonly known

as the “shield” provision

 Under ¶ 402(k), compliance with an

NPDES permit is deemed compliance for all CWA enforcement sections

 The “Permit Shield” covers

pollutants specifically identified in the permit and other pollutants identified during the application process, either by the applicant or as part of that process

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CERCLA Liability and the CWA Permit Shield

 CERCLA ¶ 101(10)(H) exempts “federally permitted releases”

from the definition of “release” under CERCLA

 This exemption protects NPDES permittees from CERCLA

liability

  • If the substance is identified in the permit, and
  • The permit contains a condition addressing it

 The federally permitted release exemption applies to releases to

POTWs and from POTWs if pretreatment standards are met

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Intersection of CERCLA and CWA – Cleanup of the Foss Waterway

 United States v. Wash. State Dep’t of Transportation, W.D.

  • Wash. No. C08-5722 RJB

 Three years of litigation concerning WSDOT’s responsibility for

cleanup costs

 WSDOT counterclaims against

U.S. Army Corps for contribution from dredging the Foss – in 1904!

 WSDOT liable under CERCLA  $6 million judgment

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MTCA Example Cleanup of the Foss Waterway

 Pacificorp Environmental Remediation Co. v. WSDOT, 162

  • Wn. App. 627 (2011)

 Pacificorp’s predecessors operated a coal gasification plant  Coal tar and other discharges from the plant contaminated the

Foss Waterway

 Construction of I-705 released some of these sediments  In addition, storm drains

for the I-705 freeway drained into the waterway

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Pacificorps v. WSDOT – cont’d

 EPA sent notice letters to PRPs, including WSDOT. Some PRPs

cleaned up the waterway, then sued WSDOT for contribution

 WSDOT was found liable under MTCA as an “owner,” “operator”

and “arranger”

 Trial court entered judgment against WSDOT for $6 million in

costs, $1.6 million in attorney’s fees and a 2% share of future costs

 WSDOT’s argument that it only contributed some of the

stormwater was rejected – “no minimum level of hazardous substance is required to trigger MTCA liability.”

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21

The CWA “Permit Shield” and State Water Quality Standards

 The CWA permit shield has been

held to pre-empt state law claim for permitted releases.

 What is a “permitted” release?  Piney Run Preservation

Association v. County Commissioners of Carroll County, 268 F.3d 255 (4th Cir. 2001).

  • Plaintiffs challenged discharge of

heated effluent; “heat” was not listed as a discharge.

  • Fourth Circuit held that “all

discharges adequately disclosed to the permitting authority are within the scope of the permit’s protection.”

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Current issues: (1) Are Non-Point Sources CWA “Releases”?

Decker v. Northwest Environmental Defense Center, ___ S.Ct. ___, 2013 WL 1131708 (March 20, 2013).

  • CWA §Section 402(p) covers

stormwater “associated with industrial activity”—a term that the CWA does not define.

  • EPA’s then-current Industrial

Stormwater Rule, “exempts discharges of channeled stormwater runoff from logging roads from the NPDES permitting scheme.”

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Current issues (cont’d) (2) Regulation by Guidance Letter

Iowa League of Cities v. EPA, __ F.3d __, 2013 WL 1188039 (8th Cir. March 25, 2013).

  • Eighth Circuit rejects EPA’s argument that two

letters were “statements of policy,” subject to revision and therefore exempt from APA review

  • Construing the letters as “promulgations of

effluent limits,” on mixing zones and blending, the court held they were subject to notice and comment and judicial review.

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Current issues (cont’d) (3) Are Rail Cars CWA Point Sources?

 On June 5, the Sierra Club and

  • ther environmental groups filed suit

against BNSF and a number of coal producers: Sierra Club, et al. v. BNSF Railway, et al., W.D. Wash. Case No. 2:13-cv-00967-JCC;

 The plaintiffs allege that coal and

coal byproducts discharged from

  • pen rail cars without an NPDES

permit violate the CWA.

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For additional information . . .

Steven G. Jones

Holland & Hart LLP 801-799-5828; 206-356-3360 (cell) sjones@hollandhart.com

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 26

Presented by

Joan P. Snyder, Esq.

Stoel Rives LLP Environmental, Land Use and Natural Resources Practice Group

August 8, 2013 • Strafford live phone/web seminar

CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities: Portland Harbor Superfund Site Stormwater Source Control

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 27

Portland Harbor Superfund Site Portland, Oregon

  • Listed on NPL in 2000;

Draft Remedial Investigation (RI) and Draft Feasibility Study (FS) undergoing EPA review; Record of Decision expected 2014-15

  • 11-mile stretch of

Willamette River

  • Largely in zoned

industrial sanctuary

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 28

PORTLAND HARBOR SUPERFUND SITE STORMWATER REGULATION

  • Industries in Harbor

subject to three regulatory authorities for stormwater:

− EPA − Oregon Department of Environmental Quality (ODEQ) − City of Portland

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 29

EPA PERSPECTIVE:

  • Authority under CERCLA
  • 11-mile stretch of Willamette River

− Including bed and banks − Including upland properties if necessary for implementation of the remedy

  • Memorandum of Understanding

(MOU) with ODEQ gives ODEQ primary responsibility for source control of adjacent upland properties, subject to EPA review

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 30

ODEQ PERSPECTIVE:

  • ODEQ Cleanup Section:

− Focus on upland properties, riparian and stormwater sources − Primary authority under CERCLA and Oregon Cleanup Law, ORS 465.200 et seq. − MOU with EPA requires ODEQ to control upland sources

  • To prevent recontamination of

sediment

  • To control in-river risk to human

health and ecological receptors

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 31

ODEQ PERSPECTIVE: (cont.)

  • ODEQ Water Quality Section:

− ODEQ also has delegated Clean Water Act (CWA ) authority

  • NPDES permits:
  • Industrial
  • POTW
  • MS-4
  • NPDES General Stormwater

1200-Z permit

  • NPDES Individual Stormwater

permits

  • TMDLs
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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 32

CITY OF PORTLAND PERSPECTIVE:

  • IGA for City Outfalls:

− 2003 Intergovernmental Agreement with ODEQ to identify and control contaminant sources from City stormwater conveyance systems discharging into the Portland Harbor Study Area

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 33

CITY OF PORTLAND PERSPECTIVE:

(cont.)

  • Stormwater Permit

Authority:

− City of Portland acts as Local Agent for implementation of NPDES General Industrial Stormwater Permit 1200Z within City boundaries

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 34

CITY OF PORTLAND PERSPECTIVE:

(cont.)

  • City Code Authority:

− City regulates all discharges into its Storm Sewer system under City Code Chapter 17.39

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 35

CITY OF PORTLAND PERSPECTIVE:

(cont.)

City MS-4 stormwater Permit and sanitary sewer permits:

  • City subject to MS-4 NPDES permit for

municipal stormwater discharges

  • City subject to NPDES permit for

POTW, which includes combined sewer

  • verflows (CSOs) and emergency

sanitary sewage overflows (SSOs) caused by blockages, failures at pump stations, etc.

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 36

OVERALL TOOLS TO CONTROL

CONTAMINANTS IN STORMWATER

  • Best Management Practices (BMPs)
  • Stormwater Pollution Control Plans (SWPCPs)
  • Monitoring
  • Corrective Actions

– BMPs – Treatment – Stormwater redirection (infiltration) – Process Changes – Source remediation/removal

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 37

Think of as serially escalating . . .

LOWEST LEVEL: CITY CODE COMPLIANCE

  • If not required to have 1200-Z Stormwater

permit, but discharge to City storm sewer, then City can use City Code 17.39 to require:

– BMPs and SWPCP – Accidental Spill Prevention Plan – Monitoring data to characterize types and loads of pollutants

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 38

SECOND LEVEL: NPDES PERMIT REQUIRED

  • Could be WWTP, MS-4 NPDES Permit or individual permits
  • This discussion focuses on 1200Z Industrial General Stormwater

permit

– Listed SIC Codes, or as otherwise required by DEQ – BMPs and SWPCP – Quarterly Monitoring – Benchmarks based on meeting water quality standards for receiving water body

  • Statewide benchmarks
  • Sector specific benchmarks
  • Impairment parameters for 303(d) listed receiving waters

– Required Tier I and Tier II Corrective Actions for exceeding benchmarks

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 39

SECOND LEVEL: NPDES 1200-Z PERMIT REQUIRED (cont.)

  • Regulatory concentration goals clear and fixed (statewide

and sector-specific benchmarks and impairment reference concentrations)

  • Consequences clear:

− Tier I corrective actions required (SWPCP review and possibly additional BMPs) if exceeded in any one sampling event − Tier II correction actions (treatment) required if geometric mean of quarterly samples in second year of permit do not meet benchmark; implementation required by year 4 of permit

  • Control measures required to meet technology based effluent limits: “to the

extent achievable using control measures that are technologically available and economically practicable and achievable in light of best industry practice.”

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 40

THIRD LEVEL: SOURCE CONTROL UNDER CERCLA OR OREGON CLEANUP RULES

  • First, legal limitations (WE’LL GET BACK TO THESE... ):

– CERCLA 107(j) (“federal permit shield”):

“Recovery by any person (including the United States or any State or Indian tribe) for response costs or damages resulting from a federally permitted release shall be pursuant to existing law in lieu of this section.”

– CERCLA 101(10):

“The term ‘federally permitted release’ means (A) discharges in compliance with a [NPDES permit], [or] (B) discharges resulting from circumstances identified and reviewed and made part of the public record with respect to a [NPDES permit] and subject to a condition of such permit, [or] (C) continuous or anticipated intermittent discharges from a point source, identified in a [NPDES permit] or permit application, which are caused by events occurring within the scope of relevant operating or treatment systems . . .”

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 41

THIRD LEVEL: SOURCE CONTROL UNDER CERCLA OR OREGON CLEANUP RULES (cont.)

  • Legal limitations: (cont.)

– Oregon Cleanup Law (“Oregon permit shield”):

  • OAR 340-122-030 (2)

“Conditional Exemption of Permitted Releases. These rules do not apply to permitted or authorized releases of hazardous substances, unless the Director determines that application of these rules might be necessary in order to protect public health, safety or welfare, or the environment. These rules may be applied to the deposition, accumulation,

  • r migration resulting from otherwise permitted or

authorized releases.”

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 42

  • Implemented under Voluntary Cleanup Agreement with
  • r Order from DEQ Cleanup Section
  • Requires risk assessment, source control evaluation and

implementation of source control

  • Guidance:

– EPA/ODEQ Portland Harbor Joint Source Control Strategy (“JSCS”), 12/05 – ODEQ Guidance for Evaluating the Stormwater Pathway at Upland Sites, updated 10/10

THIRD LEVEL: SOURCE CONTROL UNDER CERCLA OR OREGON CLEANUP RULES (cont.)

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 43

EPA/ODEQ JSCS 12/05

  • EPA/ DEQ PORTLAND HARBOR JOINT SOURCE CONTROL STRATEGY
  • - FINAL, DECEMBER 2005

– Upland Site Characterization

  • Identify complete migration pathways
  • Identify site COIs
  • Collect appropriate samples and screen against against JSCS Table

3-1 Screening Level Values and apply weight of evidence approach to identify pathway specific COPCs

  • For stormwater and storm line solids, compare to DEQ “Tool for

Evaluating Stormwater Data, Appendix E to Guidance for Evaluating the Stormwater Pathway at Upland Sites, as updated October 2010 – Perform Source Control Evaluation – If necessary, implement Source Control Measures

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 44

ODEQ Guidance for Evaluating the Stormwater Pathway

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 45

  • App. E: “Knee of the Curve” Data

analysis

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 46

  • Using this guidance, consequences much less

clear than under 1200Z permit

– JSCS starts with Screening Level Values (SLVs), which are not administratively promulgated standards – Can use “knee of the curve” tool – Coupled with other “Lines of Evidence”

  • Which can include loading models, with assumptions

that can be debated all ways to Sunday

  • However, these are the tools we have to try to

make good decisions

THIRD LEVEL: SOURCE CONTROL UNDER CERCLA OR OREGON CLEANUP RULES (cont.)

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 47

Comparison: 1200Z to JSCS SCE

1200-Z NPDES Portland Harbor Cleanup Source Control Legal basis Promulgated Administrative Rule

  • -General cleanup rules
  • -Agency Guidance on

application to stormwater Who has to comply? SIC Code or

  • therwise required

Only if under VCA or Order from DEQ Cleanup section Overall Goal Meet WQSs in receiving body based

  • n model

Risk-based: meet WQSs and be protective and prevent recontamination of sediment.

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 48

Comparison: 1200Z to JSCS SCE

1200-Z NPDES Portland Harbor Cleanup Source Control

Specific Goals Benchmarks (guideline concentrations, not effluent limitations) Presumption that meet JSCS SLVs at end of pipe. How applied Single exceedance > review of SWPCP and BMPs Exceedance by GeoMean in Permit Yr 2 >Tier II treatment requirements, to be implemented by Permit Yr 4

  • Unclear. City of Portland

Outfall report (2010) focused its analysis on geometric

  • means. Oversight of industrial

sites seems focused on individual exceedances.

ODEQ NPDES 1200Z Evaluation Report: “The geometric mean tends to dampen the effect of very high or low values and is an appropriate measure of stormwater discharges given their highly variable nature.”

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 49

Parameter Specific Comparison: Lead

CWA Program: 1200-Z NPDES Cleanup Program: Portland Harbor JSCS

Pb 40 ug/l (total) benchmark 0.54 ug/l (dissolved) SLV 5-15 ug/l (total) “flat portion” of stormwater comparison curve in

  • App. E to Guidance for Evaluating

the Stormwater Pathway

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 50

Lead at 1200Z Permit Level

  • Goal: Protecting in-stream beneficial uses, focused
  • n water column exposure pathways.

– Benchmark of 40 ug/l is risk based – based on model to predict end-of-pipe concentration that has only 10% probability of exceeding in-stream water quality criteria

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 51

Lead at JSCS SCE level

  • How ODEQ/EPA currently approaching:

– Goal is to meet the JSCS SLV of 0.54 ug/l (10x lower than 1200Z permit level) – However, if

  • have implemented all practical BMPs AND
  • have achieved “flat portion” of App. E curves AND
  • loading study shows no likely adverse impact on sediment,

– then no further treatment required at this time but adaptive management required and additional treatment may be required in future.

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 52

Lead—Portland Harbor “Knee of Curve”

JSCS SLV 0.54 ug/l 1200Z benchmark 40 ug/l

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 53

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 54

Lead conclusions

  • Legal:

– EPA has no CERCLA authority to require further source control of discharge absent violation of permit since lead covered by conditions of permit – ODEQ has authority under exception to Oregon permit shield ONLY IF (1) ODEQ Director determines necessary to protect environment OR (2) applied to the deposition or accumulation of lead.

  • Hard to argue 0.54 ug/l SLV “necessary” to protect water column

because 1200Z permit, which has been through rulemaking process, determined that 40 ug/l is protective.

  • Could require more than meeting 40 ug/l benchmark if necessary to

prevent deposition that is causing environmental harm

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 55

Lead conclusions

  • Practical:
  • With respect to protection to water column, 1200Z and Cleanup

Program should require same concentration at end of pipe, both in terms of numeric benchmark/SLV and how applied (e.g. to geometric mean)

  • However, IF lead accumulation in sediments is determined through

Portland Harbor RI/FS to be posing unacceptable risk AND loading study suggests a particular stormwater outfall could be materially contributing to that risk, then further controls could be required by ODEQ

– Doesn’t seem likely. Lead considered by EPA to be contaminant of secondary ecological significance in Portland Harbor. Does not biomagnify.

  • MS-4 and SSO discharges (which include transportation corridors) also

need to meet 1200Z benchmark and/or lower concentration determined to be necessary to prevent unacceptable risk from deposition .

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 56

Parameter Specific Comparison: Copper

CWA Program: 1200-Z NPDES Cleanup Program: Portland Harbor JSCS

Cu 20 ug/l (total) benchmark— technology based 2.7 ug/l (dissolved) SLV 5-20 ug/l “flat portion” of stormwater comparison curve in

  • App. E to Guidance for Evaluating

the Stormwater Pathway

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SLIDE 57

CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 57

Copper at 1200Z Permit Level

  • Goal: Protecting in-stream beneficial uses, focused
  • n water column exposure pathways.
  • Questions regarding appropriate benchmark:

– Benchmark of 20 ug/l is technology based – Would have adopted 6 ug/l to achieve goal of <10% probability

  • f exceeding WQS but for the lack of affordable and feasible

treatment technologies – Currently questions whether appropriate to take into account chelation potential in receiving water in adjusting benchmark – Benchmark will be reconsidered in next permit modification (2017)

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 58

Copper at JSCS SCE level

  • How ODEQ/EPA currently approaching:

– Goal is to meet the JSCS SLV of 2.7 ug/l (10x below NPDES benchmark) – However, if

  • have implemented all practical BMPs AND
  • have achieved “flat portion” of App. E curves AND
  • loading study shows no likely adverse impact on sediment,

– then no further treatment required at this time but adaptive management required and additional treatment may be required in future.

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 59

Copper—Portland Harbor “Knee of Curve”

JSCS SLV: 2.7 ug/l

1200Z benchmark 20 ug/l

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CERCLA, CWA, AND STATE LAW

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 61

Copper conclusions

  • Legal:

– EPA—same as lead: EPA has no CERCLA authority absent violation of permit – ODEQ has authority under exception to Oregon permit shield ONLY IF (1) ODEQ Director determines necessary to protect environment OR (2) applied to the deposition or accumulation of lead.

  • Maybe consider that 1200Z benchmark (20 ug/l) is technology based, rather

than risk based. Permit risk-based criteria would have been 6 ug/l, compared to 2.7 ug/l JSCS SLV.

  • But hard for Director to determine it is “necessary” for a discharger under

the Cleanup program to meet more stringent criteria when it is not “necessary” for a neighboring property discharging under the 1200Z NPDES permit to do so

  • Could require more than meeting 20 ug/l benchmark if necessary to prevent

deposition that is causing environmental harm, but copper not generally deposition problem due to solubility

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 62

Copper conclusions

  • Practical:
  • As with lead, 1200Z and Cleanup Program should require same

concentration at end of pipe (numeric and method, e.g. geometric mean)

  • However, IF copper accumulation in sediments is determined through

Portland Harbor RI/FS to be posing unacceptable risk AND loading study suggests a particular stormwater outfall could be materially contributing to that risk, then further controls could be required by ODEQ

– Doesn’t seem likely. Copper considered by EPA to be contaminant of secondary ecological significance in Portland Harbor Highly soluble and does not biomagnify.

  • Many dischargers in Pdx Harbor exceed 20 ug/l and there are no known

feasible treatment technolgies, so even meeting 20 ug/l will take time

  • MS-4 and SSO discharges (which include transportation corridors) need to

meet 1200Z benchmark and/or lower concentration determined to be necessary to prevent unacceptable risk from deposition

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 63

Parameter Specific Comparison: PCBs

CWA Program: 1200-Z NPDES Cleanup Program: Portland Harbor JSCS

Total PCBs 2 ug/l impairment reference concentration for discharges into 303(d) listed water bodies (such as Portland Harbor) 0.000064 ug/l SLV

  • Approx. 0- 0.1 ug/l “flat portion”
  • f stormwater comparison curve

in App. E to Guidance for Evaluating the Stormwater Pathway

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 64

PCBs at 1200Z Permit Level

  • Goal: Protecting in-stream beneficial uses, focused
  • n water column exposure pathways.
  • Only addressed as reference concentration for 303(d)

impaired receiving water bodies (such as Portland Harbor) – Reference Concentration is 2 ug/l

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CERCLA, CWA, AND STATE LAW

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PCBs at JSCS SCE level

  • JSCS SLV of 0.000064 ug/l known to be

unrealistic (and often undetectable)

  • So, if
  • have implemented all practical BMPs AND
  • have achieved “flat portion” of App. E curves (approx. 0.1 ug/l) AND
  • loading study shows no likely adverse impact on sediment,

– then no further treatment required at this time but adaptive management required and additional treatment may be required in future.

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 66

PCBs—Portland Harbor “Knee of Curve”

JSCS SLV 0.000064 ug/l

1200Z 303(d) ref. conc. 2 ug/l

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CERCLA, CWA, AND STATE LAW

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CERCLA, CWA, AND STATE LAW

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PCB conclusions

  • Legal:

– EPA— PCBs are impairment pollutant monitored in all Portland Harbor permits so EPA has no CERCLA authority absent violation of permit – ODEQ has authority under exception to Oregon permit shield ONLY IF (1) ODEQ Director determines necessary to protect environment OR (2) applied to the deposition or accumulation of PCBs.

  • Easier to determine that “necessary” when RI shows that stormwater is a

significant source and PCBs are clear risk driver in Portland Harbor. Relatively insoluble and therefore associated with TSS and does biomagnify.

  • Primary risk pathway is bioaccumulation from sediment, so focus is on

deposition or accumulation

  • Still will lead to inequity if Director determines it is “necessary” for a

discharger under the Cleanup program to meet more stringent criteria when it is not “necessary” for a neighboring property discharging under the 1200Z NPDES permit to do so.

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR 70

PCB conclusions

  • Practical:
  • RI/FS will show PCBs posing unacceptable risk and that stormwater is

contributing to it. IF loading study suggests a particular stormwater

  • utfall could be materially contributing to that risk, then further controls

will be required by ODEQ.

  • Need way (loading studies?) to determine what level of PCB control

necessary to prevent recontamination based on site-specific and river hydrodynamic specific factors

  • MS-4 discharges (which include transportation corridors) also need to

be subject to same process to determine what controls are necessary to prevent unacceptable risk from deposition

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CERCLA, CWA, AND STATE LAW

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CERCLA, CWA, AND STATE LAW

Case Study of Overlapping Authorities THURSDAY, AUGUST 8, 2013 • STRAFFORD SEMINAR

Joan P. Snyder Stoel Rives LLP (503) 294-9657 jpsnyder@stoel.com