United States v. NCR Corporation ( 2014 )


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  •                              In the
    United States Court of Appeals
    For the Seventh Circuit
    ____________________
    Nos. 13-2436 & 13-2441
    UNITED STATES OF AMERICA,
    Plaintiff-Appellee,
    v.
    P. H. GLATFELTER COMPANY and
    NCR CORPORATION,
    Defendants-Appellants.
    ____________________
    Appeal from the United States District Court for the
    Eastern District of Wisconsin.
    No. 1:10-cv-00910-WCG — William C. Griesbach, Chief Judge.
    ____________________
    ARGUED FEBRUARY 28, 2014 — DECIDED SEPTEMBER 25, 2014
    ____________________
    Before WOOD, Chief Judge, and KANNE and TINDER, Circuit
    Judges.
    TINDER, Circuit Judge. Today we issue two decisions relat-
    ed to the cleanup of the Lower Fox River and Green Bay Su-
    perfund Site in northeastern Wisconsin. This decision ad-
    dresses a claim brought by the United States to enforce a
    2007 unilateral administrative order issued by the Environ-
    mental Protection Agency (EPA) under § 106 of the Com-
    2                                            Nos. 13-2436 & 13-2441
    prehensive Environmental Response, Compensation, and
    Liability Act of 1980 (CERCLA), 42 U.S.C. § 9606. 1 EPA’s
    2007 order directs several potentially responsible parties
    (PRPs) to clean up the portion of the Site downstream of Lit-
    tle Lake Butte des Morts. Some of the issues relevant to the
    government’s claim to enforce EPA’s order were resolved on
    summary judgment, then the district court held a bench trial.
    After trial, the court ruled in favor of the government and
    entered a declaratory judgment and permanent injunction
    requiring the PRPs to comply with EPA’s order.
    Four PRPs appealed—NCR Corporation, P.H. Glatfelter
    Company, Menasha Corporation, and WTM I Company—
    and their appeals were consolidated. However, shortly after
    oral argument, the government lodged in the district court a
    proposed consent decree that would resolve its claims
    against Menasha and WTM. Thus, we have deconsolidated
    the appeals of those two PRPs, and we will resolve only the
    appeals of NCR and Glatfelter in this opinion. For the rea-
    sons that follow, we affirm in part and reverse in part.
    I.    BACKGROUND
    The Superfund Site at issue encompasses both the Lower
    Fox River and Green Bay. The history of the Site is more ful-
    ly described in our contemporaneously issued opinion in
    NCR Corp. v. George A. Whiting Paper Co., No. 13-2447 (7th
    Cir. Sept. 25, 2014). For now, suffice it to say that several pa-
    per mills discharged wastewater containing polychlorinated
    1 In the same action, the United States and the State of Wisconsin have
    brought claims to recover response costs and natural resource damages un-
    der § 107 of the CERCLA, 42 U.S.C. § 9607. Those claims are pending in
    the district court and are not at issue here.
    Nos. 13-2436 & 13-2441                                       3
    biphenyls (PCBs) into the River from the mid-1950s through
    the 1970s, and since 1998, the Site has been the subject of
    massive remedial efforts conducted pursuant to CERCLA.
    The Lower Fox River begins at the outlet of Lake Winne-
    bago and flows northeast for approximately 39 miles before
    it enters Green Bay. In 1998, EPA began working with the
    Wisconsin Department of Natural Resources (WDNR) to de-
    velop a remedial plan for the Site. As part of that plan, the
    Site was divided into five geographic sections, or “operable
    units,” which are used “when phased analysis and response
    is necessary or appropriate given the size or complexity of
    the site.” 40 C.F.R. § 300.430(a)(1)(ii)(A). Operable Unit 1 or
    “OU1” runs from the outlet of Lake Winnebago to the Ap-
    pleton Dam, a stretch of the River also known as Little Lake
    Butte des Morts; OU2 runs from the Appleton Dam to the
    Little Rapids Dam; OU3 runs from the Little Rapids Dam to
    the De Pere Dam; OU4 runs from the De Pere Dam to the
    mouth of the River at Green Bay; and OU5 is Green Bay it-
    self. Only OU2–OU5 are at issue here, as the cleanup of OU1
    was litigated separately and carried out pursuant to a con-
    sent decree. The Site and its operable units are shown in the
    figure below, which is taken from the agencies’ 2007 record
    of decision amendment.
    4                                    Nos. 13-2436 & 13-2441
    NCR and Glatfelter are PRPs under CERCLA § 107(a), 42
    U.S.C. § 9607(a), because they or their corporate predeces-
    sors formerly owned and operated paper mills that dis-
    charged wastewater containing PCBs into the River. NCR is
    responsible for two mills that produced carbonless copy pa-
    per using an emulsion containing PCBs and then discharged
    PCB-contaminated wastewater into OU2. Glatfelter is re-
    sponsible for a mill that recycled scraps of carbonless copy
    Nos. 13-2436 & 13-2441                                     5
    paper unusable by the original manufacturer and then dis-
    charged PCB-contaminated wastewater into OU1.
    In 2002, EPA and WDNR issued a record of decision
    (ROD) that selected a remedy for OU1–OU2. That remedy
    called for the dredging of approximately 784,000 cubic yards
    of sediment in OU1 but was limited to monitored natural
    recovery in OU2, with the exception of some dredging in
    Deposit DD at the downstream end of OU2 that would be
    undertaken as part of the OU3 remedy. In 2003, EPA and
    WDNR issued a second ROD, which selected a remedy for
    OU3–OU5. That remedy called for the dredging of approxi-
    mately 9,000 cubic yards of sediment in Deposit DD at the
    downstream end of OU2, approximately 586,800 cubic yards
    of sediment in OU3, and approximately 5,880,000 cubic
    yards of sediment in OU4. For OU5, the remedy was limited
    to monitored natural recovery, with the exception of some
    dredging near the mouth of the River.
    In the years that followed, Glatfelter and other OU1 PRPs
    agreed to perform the necessary remedial design and action
    in OU1. Meanwhile, NCR and one other PRP agreed to per-
    form the remedial design work for OU2–OU5. In 2007, based
    on information obtained during the full-scale remediation
    activities in OU1 and the remedial design work for OU2–
    OU5, the agencies decided to amend the ROD for OU2–OU5.
    The agencies determined that the all-dredging remedy they
    previously selected would not sufficiently reduce PCB con-
    centrations in OU2–OU5 and that an approach that utilized
    capping or sand covering in some areas would cure that de-
    ficiency. The agencies also determined that capping and
    sand covering would be less expensive than dredging and
    that a remedy incorporating those methods would therefore
    6                                               Nos. 13-2436 & 13-2441
    be more cost effective. Ultimately, the agencies adopted a
    hybrid remedy, which maintained dredging as the default
    approach but allowed for capping and sand covering where
    certain design criteria were met.
    In November 2007, EPA issued a unilateral administra-
    tive order pursuant to CERCLA § 106(a), 42 U.S.C. § 9606(a),
    directing the PRPs to conduct the cleanup required by the
    ROD amendment for OU2–OU5. Thereafter, NCR led the
    remedial efforts in OU2 and OU3 and conducted a signifi-
    cant amount of remedial action in OU4. Even so, NCR main-
    tained that it should not be responsible for all of the cleanup
    costs. Thus, in 2008, it filed an action seeking contribution
    from the other PRPs. In response, the other PRPs filed coun-
    terclaims seeking contribution from NCR. Near the end of
    2009, the district court ruled against NCR on its claim for
    contribution, and in 2011, it ruled in favor of the other PRPs
    on their counterclaims, holding that NCR was required to
    reimburse them for their response costs.
    Meanwhile, in 2010, the agencies determined that they
    had significantly underestimated the costs associated with
    the cleanup of OU2–OU5. Thus, they published an explana-
    tion of significant differences, which adjusted their estimat-
    ed total project costs for OU2–OU5 by about 62 percent,
    from about $432 million to about $701 million. 2
    Shortly after the district court held that NCR was re-
    quired to reimburse the other PRPs for their response costs,
    2 The 2007 ROD amendment estimated total project costs at about $390
    million, in 2005 U. S. Dollars. In the 2010 explanation of significant differ-
    ences, the agencies adjusted that number to 2009 U. S. Dollars, resulting in
    an estimate of about $432 million, so as to provide a proper basis for com-
    parison with their revised cost estimates.
    Nos. 13-2436 & 13-2441                                        7
    NCR decided that it would no longer comply with EPA’s
    2007 order. NCR cut its remediation work in half during
    2011, and it refused to commit to perform any work in 2012.
    This action ensued, in which the United States sought pre-
    liminary and permanent injunctive relief, along with a de-
    claratory judgment, requiring NCR and the other PRPs to
    comply with EPA’s order.
    In 2012, the district court entered a preliminary injunc-
    tion against NCR, requiring it to complete the remediation
    work scheduled for that year, and we affirmed. United States
    v. NCR Corp., 
    688 F.3d 833
    (7th Cir. 2012). Thereafter, the dis-
    trict court resolved two issues on summary judgment. First,
    it upheld the remedy selected by EPA and WDNR. Second, it
    held that Glatfelter and the other OU1 PRPs were liable for
    downstream cleanup costs. Then, in December 2012, the dis-
    trict court held an eleven-day bench trial, and a few months
    later, it ruled in favor of the government and entered a de-
    claratory judgment and permanent injunction requiring the
    nonsettling PRPs to comply with EPA’s 2007 order.
    On appeal, NCR and Glatfelter ask us to vacate the de-
    claratory judgment and permanent injunction. They attack
    the district court’s summary judgment rulings, as well as its
    findings of fact and conclusions of law following the bench
    trial. For the reasons that follow, we hold that the district
    court erred in its consideration of NCR’s divisibility defense
    and in its decision to enter a permanent injunction but cor-
    rectly resolved the other issues before it. Therefore, we af-
    firm in part and reverse in part.
    8                                       Nos. 13-2436 & 13-2441
    II.   SUMMARY JUDGMENT RULINGS
    The district court’s summary judgment rulings came af-
    ter the parties filed cross-motions for summary judgment on
    the propriety of the remedy, and the United States moved
    for summary judgment on the OU1 Defendants’ liability.
    “As with any summary judgment motion, we review cross-
    motions for summary judgment ‘construing all facts, and
    drawing all reasonable inferences from those facts, in favor
    of the non-moving party.’” Laskin v. Siegel, 
    728 F.3d 731
    , 734
    (7th Cir. 2013) (quoting Wis. Cent., Ltd. v. Shannon, 
    539 F.3d 751
    , 756 (7th Cir. 2008)). Summary judgment is appropriate if
    “there is no genuine dispute as to any material fact and the
    movant is entitled to judgment as a matter of law.” Fed. R.
    Civ. P. 56(a).
    A. PROPRIETY OF THE REMEDY
    When the government brings an action under 42 U.S.C.
    § 9606 to enforce an administrative cleanup order, CERCLA
    allows for judicial review of EPA’s decision in selecting the
    response action. 42 U.S.C. § 9613(h)(2). However, the court
    must “uphold [EPA’s] decision in selecting the response ac-
    tion unless the objecting party can demonstrate, on the ad-
    ministrative record, that the decision was arbitrary and ca-
    pricious or otherwise not in accordance with law.” 
    Id. § 9613(j)(2).
    EPA’s remedy selection for the Site is reflected in
    the 2007 ROD amendment and the 2010 explanation of sig-
    nificant differences. For different reasons, both Glatfelter
    and NCR challenged that remedy on summary judgment,
    and they reassert their arguments on appeal.
    Nos. 13-2436 & 13-2441                                                      9
    1. EPA and WDNR’s Cooperative Agreement
    First, Glatfelter argues that EPA’s decision in selecting
    the response action was not in accordance with law because
    EPA delegated the task of conducting a remedial investiga-
    tion and feasibility study to WDNR without a valid coopera-
    tive agreement. CERCLA allows for the delegation of re-
    sponsibility for remedial action as follows:
    A State or political subdivision thereof or Indi-
    an tribe may apply to [EPA] to carry out ac-
    tions authorized in this section. If [EPA] de-
    termines that the State or political subdivision
    or Indian tribe has the capability to carry out
    any or all of such actions in accordance with
    the criteria and priorities established pursuant
    to section 9605(a)(8) of this title and to carry
    out related enforcement actions, [EPA] may en-
    ter into a contract or cooperative agreement
    with the State or political subdivision or Indian
    tribe to carry out such actions. [EPA] shall
    make a determination regarding such an appli-
    cation within 90 days after [EPA] receives the
    application. 3
    42 U.S.C. § 9604(d)(1)(A). Glatfelter argues that a state has no
    authority to “carry out the actions authorized” by CERCLA
    without a cooperative agreement and therefore the lack of a
    cooperative agreement between EPA and WDNR would un-
    dermine the selected remedy for the Site.
    3 The President has delegated to EPA the authority to undertake response
    action under CLERCLA; thus, where the statute refers to the President, we
    substitute EPA. See Exec. Order No. 12,580, 52 Fed. Reg. 2923 (Jan. 23, 1987).
    10                                     Nos. 13-2436 & 13-2441
    Glatfelter’s argument is academic, however, because EPA
    and WDNR did in fact enter into a cooperative agreement
    regarding the remedial investigation and feasibility study
    for the Site, and the government filed authenticated copies of
    that agreement in the district court. Glatfelter complains that
    the cooperative agreement was not included in the adminis-
    trative record, but nothing in CERCLA or the national con-
    tingency plan requires that cooperative agreements be in-
    cluded in the administrative record. The administrative rec-
    ord need only include “the documents that form the basis
    for the selection of a response action.” 40 C.F.R. § 300.800(a).
    Typically, that includes the following:
    (1) Documents containing factual information,
    data and analysis of the factual information,
    and data that may form a basis for the se-
    lection of a response action. …
    (2) Guidance documents, technical literature,
    and site-specific policy memoranda that
    may form a basis for the selection of the re-
    sponse action. …
    (3) Documents received, published, or made
    available to the public under § 300.815 for
    remedial actions, or § 300.820 for removal
    actions. …
    (4) Decision documents. …
    (5) Enforcement orders. … ; and
    (6) An index of the documents included in the
    administrative record file. …
    Nos. 13-2436 & 13-2441                                        11
    
    Id. § 300.810(a).
    Notably, this list contains no mention of
    cooperative agreements. Instead, it emphasizes documenta-
    tion of the substantive factors that play a role in the selection
    of a remedy. As a result, we find no support for Glatfelter’s
    argument that the failure to include the cooperative agree-
    ment in the administrative record undermines the selected
    remedy.
    It is true that as a general matter “judicial review of any
    issues concerning the adequacy of any response action taken
    or ordered by [EPA] shall be limited to the administrative
    record.” 42 U.S.C. § 9613(j)(1). But “[o]therwise applicable
    principles of administrative law shall govern whether any
    supplemental materials may be considered by the court.” 
    Id. Those principles
    allow a reviewing court to consider materi-
    als outside the administrative record “when it is necessary to
    create a record without which the challenge to the agency’s
    action cannot be evaluated.” USA Grp. Loan Servs., Inc. v. Ri-
    ley, 
    82 F.3d 708
    , 715 (7th Cir. 1996).
    Here, it would be impossible to evaluate Glatfelter’s chal-
    lenge to the selected remedy without considering the docu-
    ments that the government contends make up the coopera-
    tive agreement between EPA and WDNR. Thus, the district
    court properly considered those documents. Moreover,
    those documents show that EPA and WDNR entered into a
    valid cooperative agreement, which granted WDNR authori-
    ty to conduct a remedial investigation and feasibility study
    for the Site. As a result, EPA’s reliance on WDNR to com-
    plete those tasks was in accordance with the national contin-
    gency plan and does not provide a basis for reversal.
    12                                      Nos. 13-2436 & 13-2441
    2. Substantive Review of the Remedy
    Next, Glatfelter argues that the district court failed to
    undertake any substantive review of the selected remedy,
    instead focusing on the process by which the selection was
    made. We agree that to determine whether an agency’s deci-
    sion was arbitrary or capricious, the reviewing court “must
    go beyond the agency’s procedures to include the substan-
    tive reasonableness of its decision.” James Madison Ltd. v.
    Ludwig, 
    82 F.3d 1085
    , 1098 (D.C. Cir. 1996). This is because
    “reasonable procedures alone cannot absolve a court from
    making a ‘thorough, probing, in-depth review’ to determine
    if the agency has considered the relevant factors or commit-
    ted a clear error of judgment.” 
    Id. (quoting Citizens
    to Pre-
    serve Overton Park, Inc. v. Volpe, 
    401 U.S. 402
    , 416 (1971)). But
    “the reasonableness of the agency’s procedures is relevant to
    the court’s inquiry,” James Madison 
    Ltd., 82 F.3d at 1098
    , and
    although the district court stated that “arbitrary and capri-
    cious are terms that describe the manner of remedy selection
    more than they do the result,” it did in fact engage in sub-
    stantive review of the selected remedy. Moreover, “[e]ven if
    the district court here based its decision on the strength of
    the process alone—which we do not believe is the case—our
    de novo review of the record satisfies us that the agency’s
    conclusions were not arbitrary.” 
    Id. Under the
    arbitrary-and-capricious standard of review,
    an agency’s decision must be upheld unless it
    has relied on factors which Congress had not
    intended it to consider, entirely failed to con-
    sider an important aspect of the problem, of-
    fered an explanation for its decision that runs
    counter to the evidence before the agency, or is
    Nos. 13-2436 & 13-2441                                       13
    so implausible that it could not be ascribed to a
    difference in view or the product of agency ex-
    pertise.
    Nat’l Ass’n of Home Builders v. Defenders of Wildlife, 
    551 U.S. 644
    , 658 (2007) (quoting Motor Vehicle Mfrs. Ass’n v. State
    Farm Mut. Auto. Ins. Co., 
    463 U.S. 29
    , 43 (1983)) (internal quo-
    tation marks omitted).
    The district court concluded that the agencies’ decision to
    maintain a preference for dredging in the amended remedy
    was rationally related to the facts before them. In particular,
    the court noted that dredging represents a more permanent
    solution because it actually removes PCBs from the Site,
    while capping and sand covering merely contain PCB-
    contaminated sediment. Moreover, capping and sand cover-
    ing require long-term monitoring to ensure their effective-
    ness, and they are susceptible to failure during catastrophic
    events like floods. Ultimately, the district court concluded
    that the agencies acted rationally by adopting “a mild pref-
    erence for the benefits of dredging and viewed these as be-
    ing worth their added expense.” We agree.
    Most of the attacks Glatfelter levies against the agencies’
    remedy selection have to do with the 2003 all-dredging rem-
    edy, which of course has been abandoned. Glatfelter argues
    that the problems with that remedy also infect the amended
    remedy, because in 2007 the agencies failed to reconsider all
    of the alternatives they had considered in 2003, even though
    by 2007 they had obtained more accurate information on the
    cost and effectiveness of the various remedial approaches.
    More specifically, Glatfelter contends that the agencies
    14                                     Nos. 13-2436 & 13-2441
    should have reconsidered an all-capping remedy, which
    would have been shown to be more cost-effective.
    However, as the government points out, an all-capping
    remedy was never on the table. In the 2003 ROD, the agen-
    cies explained that capping is limited by “Site-specific condi-
    tions such as water depth, average river current, river cur-
    rent under flood conditions, wave energy, ice scour, and
    boat traffic.” Thus, the agencies never considered an all-
    capping alternative, as Glatfelter suggests. Instead, they con-
    sidered an alternative that would involve “capping to the
    maximum extent practicable with dredging in areas where
    capping is not appropriate.” Under the criteria developed
    for the 2003 ROD, this would have resulted in capping only
    about 2.25 million cubic yards of contaminated sediment and
    dredging the rest of the contaminated sediment. In contrast,
    the 2007 ROD amendment called for capping (or sand cover-
    ing) about 3.5 million cubic yards of contaminated sediment.
    In other words, the alternative that Glatfelter contends
    the agencies should have reconsidered in 2007 actually
    called for less capping and more dredging than the remedy
    the agencies adopted. There is no indication that Glatfelter
    wanted the agencies to reconsider a more expensive remedy,
    so its argument makes little sense. Moreover, it was not arbi-
    trary or capricious for the agencies to refuse to consider a
    pure capping remedy, because such a remedy was infeasible.
    As a result, Glatfelter has failed to show that the selected
    remedy should be overturned.
    3. The 2010 Explanation of Significant Differences
    NCR argues that the selected remedy is not in accordance
    with law because the agencies failed to amend the ROD
    Nos. 13-2436 & 13-2441                                     15
    when their cost estimates increased dramatically in 2010.
    The district court rejected this argument, holding that the
    agencies complied with the national contingency plan in
    publishing an explanation of significant differences rather
    than amending the ROD in 2010.
    Sometimes new information arises during the remedial
    design or action phases of a CERCLA cleanup, and the rem-
    edy selected in the ROD must be altered. Under such cir-
    cumstances, the national contingency plan gives the lead
    agency two options. 40 C.F.R. § 300.435(c)(2). If “the differ-
    ences in the remedial or enforcement action … significantly
    change but do not fundamentally alter the remedy selected
    in the ROD with respect to scope, performance, or cost,”
    then the lead agency may simply publish “an explanation of
    significant differences.” 
    Id. § 300.435(c)(2)(i).
    However, “if
    the differences in the remedial or enforcement action … fun-
    damentally alter the basic features of the selected remedy
    with respect to scope, performance, or cost,” then the lead
    agency must propose an amendment to the ROD. 
    Id. § 300.435(c)(2)(ii).
    Amending the ROD is a more cumber-
    some process that involves receiving and responding to pub-
    lic comments on the proposed changes. 
    Id. The explanation
    of significant differences that EPA and
    WDNR published in 2010 left intact the remedial approach
    outlined in the 2007 ROD amendment but revised the cost
    estimates associated with that approach. Specifically, the to-
    tal cost of the remedial action in OU2–OU5, which was orig-
    inally estimated at about $432 million, was now expected to
    be about $701 million, an increase of roughly 62 percent.
    NCR argues that such a drastic increase in cost “fundamen-
    tally alter[s] the basic features of the selected remedy with
    16                                    Nos. 13-2436 & 13-2441
    respect to ... cost” and that as a result, EPA and WDNR were
    required to propose an amendment to the ROD.
    In the 2010 explanation of significant differences, EPA
    and WDNR explained their decision to forgo another ROD
    amendment as follows:
    As set forth in the EPA guidance document en-
    titled, “A Guide to Developing and Documenting
    Cost Estimates During the Feasibility Study,” EPA
    540-R-00-002 OSWER 9355.0-75 (July 2000), the
    expected accuracy range of a cost estimate for a
    detailed analysis of remedial action alterna-
    tives is -30% to +50%. As the current estimated
    cost of the OU 2 - 5 remedial action is 62%
    greater than the original estimate, it is nearly
    within EPA’s expected accuracy range for the
    cost of a remedial action and represents a “sig-
    nificant” but not “fundamental” change from
    the 2007 ROD Amendment.
    As NCR points out, however, the guidance document cited
    by the agencies contemplates that a “detailed analysis of al-
    ternatives” will be completed without the benefit of remedi-
    al design work. This was the case with the 2003 ROD, which
    explicitly cited the -30% to +50% accuracy range for its cost
    estimates. But the 2007 ROD amendment was issued after
    substantial remedial design work had been completed. Thus,
    we might expect its cost estimates to be more accurate.
    In fact, EPA also thought the 2007 ROD amendment’s
    cost estimates would be more accurate. Its response to com-
    ments questioning the accuracy of those estimates included
    the following statement:
    Nos. 13-2436 & 13-2441                                      17
    The cost estimates for the ROD Amendment
    should be more reliable than the cost estimates
    in the 2003 ROD because new estimates are
    based on substantially more engineering anal-
    ysis and a much larger number of sediment
    samples (i.e., 10,000 sediment samples versus
    1,700 sediments samples prior to the 2003
    ROD).
    Thus, EPA represented to the public that the 2007 ROD
    amendment would be more accurate than the 2003 ROD,
    which identified a cost uncertainty range of -30% to +50%.
    We do not know how accurate the 2007 cost estimates were
    expected to be, because neither the 2007 ROD amendment
    nor the basis of design report on which it relied identified a
    range of uncertainty for total project costs. However, we
    would expect the range to be smaller than -30% to +50% but
    larger than -10% to +15%, which, according to the EPA guid-
    ance document cited by the agencies, is the range expected
    to be achieved after the remedial design process is complete.
    As a result, we reject the government’s argument that a
    cost increase of 62 percent is only marginally outside the
    range of uncertainty associated with the cost estimates in the
    2007 ROD amendment. But even so, another ROD amend-
    ment was not necessarily required. We must still determine
    whether “the differences in the remedial or enforcement ac-
    tion … fundamentally alter[ed] the basic features of the se-
    lected remedy with respect to scope, performance, or cost.”
    40 C.F.R. § 300.435(c)(2)(ii). This standard is ambiguous as it
    relates to the change at issue, i.e., an increase in cost unac-
    companied by any change in the remedial approach. As a
    18                                     Nos. 13-2436 & 13-2441
    result, EPA’s interpretation of the regulation, which it
    promulgated, is relevant.
    Indeed, an agency’s interpretation of its own regulation
    is controlling unless it is “plainly erroneous or inconsistent
    with the regulation,” or there is “reason to suspect that the
    interpretation does not reflect the agency’s fair and consid-
    ered judgment on the matter in question.” Auer v. Robbins,
    
    519 U.S. 452
    , 461–62 (1997) (citation and internal quotation
    marks omitted). “This might occur when the agency’s inter-
    pretation conflicts with a prior interpretation, or when it ap-
    pears that the interpretation is nothing more than a conven-
    ient litigating position or a post hoc rationalizatio[n] ad-
    vanced by an agency seeking to defend past agency action
    against attack.” Christopher v. SmithKline Beecham Corp., 
    132 S. Ct. 2156
    , 2166–67 (2012) (citations and internal quotation
    marks omitted).
    The preamble to the national contingency plan makes
    EPA’s position clear: “EPA believes that the appropriate
    threshold for amending a ROD is when a fundamentally dif-
    ferent approach to managing hazardous wastes at a site is
    proposed.” 55 Fed. Reg. 8666, 8771 (March 8, 1990). In con-
    trast, “[s]ignificant changes to a remedy are generally incre-
    mental changes to a component of a remedy that do not fun-
    damentally alter the overall remedial approach.” 
    Id. at 8772.
    Moreover, EPA’s position is that a change in cost alone does
    not fundamentally alter the remedial approach and thus
    does not require a ROD amendment. See 
    id. (“Where [a]
    new
    requirement would affect a basic feature of the remedy, such
    as timing or cost, but not fundamentally alter the remedy
    specified in the ROD (i.e., change the selected technology),
    Nos. 13-2436 & 13-2441                                      19
    the lead agency would need to issue an explanation of signif-
    icant differences announcing the change.”).
    In other words, EPA takes the view that to “fundamen-
    tally alter the basic features of the selected remedy with re-
    spect to … cost” is to choose a different remedial approach
    that costs more, not to stick with the same remedial approach
    but decide that it will cost more than previously thought.
    Because of the national contingency plan’s emphasis on
    “fundamentally alter[ing] the basic features of the selected
    remedy,” we cannot say that this interpretation is “plainly
    erroneous or inconsistent with the regulation.” 
    Auer, 519 U.S. at 461
    (internal quotation marks omitted).
    Moreover, EPA adopted this interpretation in an attempt
    “to develop an administrative process which balances the
    public’s continuing need for information about, and input
    into, post-ROD remedial action decisions, with the lead
    agency’s need to move forward expeditiously with design
    and implementation of the remedy after fundamental deci-
    sions have been made in the ROD.” 55 Fed. Reg. at 8773.
    And EPA’s approach seems to us an eminently reasonable
    way to balance these competing interests. Thus, we have no
    “reason to suspect that the interpretation does not reflect the
    agency’s fair and considered judgment on the matter in
    question.” 
    Auer, 519 U.S. at 462
    . Consequently, EPA’s inter-
    pretation of its regulation is binding, and the agencies were
    not required to amend the ROD in 2010.
    Having disposed of each of Appellants’ arguments on the
    propriety of the remedy, we will affirm the district court’s
    entry of summary judgment in favor of the government on
    that issue.
    20                                    Nos. 13-2436 & 13-2441
    B. GLATFELTER’S LIABILITY
    Next, Glatfelter challenges the district court’s entry of
    summary judgment on the issue of its liability for response
    costs in OU4, where remediation work is ongoing. Section
    107(a) of CERCLA imposes strict liability for response costs
    upon four classes of responsible parties. 42 U.S.C. § 9607(a).
    With respect to Glatfelter, the relevant class is any former
    owner or operator of a facility at which hazardous substanc-
    es were disposed of and “from which there is a release, or a
    threatened release which causes the incurrence of response
    costs, of a hazardous substance.” 
    Id. This is
    because Glat-
    felter is the corporate successor to Bergstrom Paper Compa-
    ny, which formerly operated a paper recycling mill in
    Neenah, Wisconsin, and discharged PCB-contaminated
    wastewater into Little Lake Butte des Morts.
    The question we must decide is whether the government
    established Glatfelter’s liability for response costs in OU4,
    even though the Bergstrom Mill was located at the upstream
    end of OU1. In this regard, Glatfelter argues that the gov-
    ernment should have been required to prove that PCB dis-
    charges from the Bergstrom Mill made their way into OU4 in
    sufficient quantities to “cause[] the incurrence of response
    costs” there. The district court disagreed, holding that
    there need be no “nexus” between a given de-
    fendant’s release and a specific response cost
    incurred—it is enough that (a) the defendant
    released a pollutant and (b) response costs
    were incurred to clean up “a” release. If the de-
    fendant truly released a minimal amount, that
    speaks not to its own liability (for which there
    Nos. 13-2436 & 13-2441                                     21
    is no de minimis defense) but to whether that li-
    ability is divisible.
    On appeal, Glatfelter argues that the district court improper-
    ly relieved the government of its burden of proof on causa-
    tion by instead requiring Glatfelter to disprove causation in
    relation to its divisibility defense.
    Section 107(a) of CERCLA is ambiguous as to whether
    proof of a causal relationship between the incurrence of re-
    sponse costs and an actual (as opposed to threatened) release
    of a hazardous substance is required to establish liability.
    Again, the statute imposes liability upon those responsible
    for a facility “from which there is a release, or a threatened
    release which causes the incurrence of response costs, of a
    hazardous substance.” 
    Id. § 9607(a).
          [T]he phrase “from which there is a release ...”
    omits a comma after “threatened release”—
    suggesting that the clause is restrictive—while
    simultaneously using the word “which”—
    suggesting that the clause is nonrestrictive.
    That is, the missing comma implies that a per-
    son can be held liable for an actual release even
    when that release does not “cause the incur-
    rence of response costs,” while the word
    “which” suggests just the opposite.
    Asarco LLC v. Cemex, Inc., No. No. EP–12–CV–155–PRM, 
    2014 WL 2112121
    , at *11 n.19 (W.D. Tex. Mar. 31, 2014). However,
    we need not resolve this ambiguity today, because even if
    the government were required to establish a causal relation-
    ship between the incurrence of response costs and the actual
    22                                      Nos. 13-2436 & 13-2441
    release of PCBs from the Bergstrom Mill, it has satisfied that
    burden.
    Where Glatfelter’s argument goes astray is in its assump-
    tion that the government must prove all of the elements of
    liability in relation to each operable unit of the Site. Such a
    requirement is nowhere to be found in the statute. Instead,
    once it is established that a party is responsible for a facility
    “from which there is a release, or a threatened release which
    causes the incurrence of response costs, of a hazardous sub-
    stance,” that party “shall be liable for … all costs of removal
    or remedial action incurred by the United States Govern-
    ment or a State or an Indian tribe not inconsistent with the
    national contingency plan.” 42 U.S.C. § 9607(a).
    In short, even assuming that a release for which the de-
    fendant is responsible must have caused the incurrence of
    response costs, nothing in the statute limits the defendant’s
    liability to the response costs its release caused. Instead, the
    defendant is liable for all response costs “not inconsistent
    with the national contingency plan.” 
    Id. The national
    contin-
    gency plan authorizes removal or remedial action at the
    “site,” 40 C.F.R. §§ 300.415, 300.435, and it defines “on-site”
    to mean “the areal extent of contamination and all suitable
    areas in very close proximity to the contamination necessary
    for implementation of the response action,” 
    id. § 300.5.
    Where, as here, releases from multiple facilities contaminate
    an interconnected environmental system like a river, the en-
    tire system falls within this definition. Thus, in this case, the
    Site was properly defined to include the entire Lower Fox
    River and Green Bay, and so long as PCBs released from the
    Bergstrom Mill caused the incurrence of some response costs
    Nos. 13-2436 & 13-2441                                         23
    within the Site, Glatfelter may be held liable for all response
    costs within the Site.
    Glatfelter does not dispute that PCB discharges from the
    Bergstrom Mill caused the incurrence of response costs in
    Little Lake Butte des Morts, which is within the Site. Yet it
    insists that its liability should not extend to OU4, where dis-
    charges from the Bergstrom Mill may not have caused the
    incurrence of response costs. In essence, Glatfelter wants us
    to treat OU4 as a separate site for which the government
    must establish liability. But this is inconsistent with the na-
    tional contingency plan, which defines an operable unit as “a
    discrete action that comprises an incremental step toward
    comprehensively addressing site problems.” 
    Id. To put
    it
    simply, operable units are not separate sites; thus, they do
    not determine the extent of a party’s liability.
    Of course, an operable unit “may address geographical
    portions of a site,” 
    id., and in
    some cases, a divisibility de-
    fense may prevail based upon those same geographic por-
    tions. However, the burden to prove divisibility rests on the
    defendant. The government need not prove each party’s lia-
    bility in relation to each geographic unit of a site the first in-
    stance. It need only prove each party’s liability as to the site
    as a whole. In this case, the undisputed facts establish Glat-
    felter’s liability as to the Lower Fox River and Green Bay
    Site.
    Glatfelter protests that holding it liable for response costs
    in OU4 is like holding it liable for “the Sheboygan River or
    the Hudson River, two other, unrelated, sediment PCB
    sites.” But of course, OU4 is not unrelated to OU1, nor is it a
    separate site; rather, OU1 and OU4 are part of the same site.
    Glatfelter cannot be held liable for cleanup in the Sheboygan
    24                                       Nos. 13-2436 & 13-2441
    River or the Hudson River because EPA could not define the
    Site to include those rivers, which are not part of “the areal
    extent of contamination and all suitable areas in very close
    proximity to the contamination necessary for implementa-
    tion of the response action.” 
    Id. However, as
    Glatfelter con-
    cedes, EPA properly defined the Site to include the entire
    Lower Fox River. Therefore, Glatfelter may be held liable for
    cleanup costs there, and the district court properly granted
    summary judgment to the government on the issue of Glat-
    felter’s liability.
    III.    TRIAL RULINGS
    In December 2012, the district court held an eleven-day
    bench trial on the government’s claim to enforce EPA’s 2007
    cleanup order. The trial focused on the defendants’ divisibil-
    ity defenses as to OU4, the only operable unit where active
    remediation work is ongoing. Ultimately, the district court
    rejected the defendants’ divisibility defenses and entered a
    declaratory judgment and permanent injunction requiring
    the defendants to comply with EPA’s order. On appeal, NCR
    and Glatfelter argue that the district court wrongly rejected
    their divisibility defenses and that, even apart from those
    defenses, injunctive relief was improper. “Because the issues
    before this Court were adjudicated pursuant to a full bench
    trial, we review the district court’s conclusions of law de novo
    and its findings of fact for clear error.” Carpet Serv. Int’l, Inc.
    v. Chi. Reg’l Council of Carpenters, 
    698 F.3d 394
    , 397 (7th Cir.
    2012), cert. denied, 
    133 S. Ct. 1856
    (2013).
    A. DIVISIBILITY
    NCR and Glatfelter each presented a divisibility defense
    at trial, but the theories were quite different. NCR conceded
    Nos. 13-2436 & 13-2441                                     25
    that it contributed to the contamination in OU4 but argued
    that the harm was capable of apportionment. Glatfelter, on
    the other hand, maintained that it did not cause any of the
    contamination in OU4 and that it should therefore not be li-
    able for any of the cleanup costs in OU4. We address each
    argument in turn.
    1. NCR
    In NCR’s prior appeal, we affirmed the district court’s
    entry of a preliminary injunction because, at that stage, NCR
    had failed to show that the harm was capable of apportion-
    ment. In doing so, we relied on the principle that courts
    should not apportion responsibility for a single harm among
    multiple sufficient causes. United States v. NCR 
    Corp., 688 F.3d at 839
    . In applying this principle, we agreed with the
    Ninth Circuit that the harm in CERCLA cases is properly
    characterized as the “contamination traceable to each de-
    fendant.” 
    Id. at 841
    (quoting United States v. Burlington N. &
    Santa Fe Ry. Co., 
    520 F.3d 918
    , 939 (9th Cir. 2008)) (internal
    quotation marks omitted). We further noted that while
    “cleanup costs, on their own, are not exactly equal to harm,”
    United States v. NCR 
    Corp., 688 F.3d at 840
    , they “may some-
    times be a relevant factor for courts to use to determine the
    level of contamination, and thus the level of harm, caused by
    each polluter,” 
    id. at 841.
        The sparse record before us in the prior appeal indicated
    that the contamination (and consequently the harm) in the
    Lower Fox River was binary in nature: PCB concentrations
    above 1.0 ppm were harmful, but PCB concentrations below
    1.0 ppm were not. See 
    id. at 839
    (“EPA has set a maximum
    safety threshold of 1.0 ppm of PCB. Anything above that
    amount is dangerous to human life and requires remedia-
    26                                            Nos. 13-2436 & 13-2441
    tion.”); 
    id. at 841
    (“[C]ontamination occurs whenever PCBs
    pass a threshold level (thereby triggering remedial require-
    ments).”). Because NCR failed to refute the proposition that
    its discharges were sufficient by themselves to cause the con-
    tamination in OU4 (i.e, to cause PCB concentrations in OU4
    to surpass the 1.0 ppm threshold), we agreed with the dis-
    trict court that the harm was not capable of apportionment.
    
    Id. at 839.
        After the case was tried, the district court continued to
    treat the harm as binary, but the evidence presented at trial
    shows that this was an oversimplification. The 1.0 ppm re-
    medial action level is not quite the line of demarcation it
    previously appeared to be. Indeed, it is not even EPA’s re-
    medial goal. Instead, EPA seeks to achieve a surface-
    weighted average concentration (SWAC) of 0.25 ppm
    throughout OU4,4 and it has determined that this can be
    achieved by undertaking some form of remediation wherev-
    er PCB concentrations exceed 1.0 ppm. Thus, sediment with
    a PCB concentration of 0.99 ppm will be left alone, not be-
    cause it is uncontaminated, but because it is insufficiently
    contaminated to push the SWAC for the operable unit as a
    whole above 0.25 ppm, at least after other areas with higher
    concentrations have undergone remediation.
    EPA has identified SWAC as the relevant metric for re-
    medial purposes because SWAC drives the ultimate harm
    with which EPA is concerned, i.e., the harm to human health
    and the environment. A particular SWAC leads to a particu-
    lar concentration of PCBs in fish tissue, which presents a
    4 Surface-weighted average concentration measures the average concentra-
    tion of PCBs in the top 10 centimeters of sediment over the surface area of
    an entire operable unit.
    Nos. 13-2436 & 13-2441                                    27
    particular risk that humans or piscivorous animals will con-
    tract a disease or experience other adverse health effects.
    And because SWAC drives the ultimate harm, it is also the
    appropriate measure of contamination for our purpose, i.e.,
    determining whether the harm is divisible.
    But even EPA’s target SWAC of 0.25 ppm does not
    amount to a boundary between harmfulness and geniality.
    EPA’s “sediment quality thresholds,” which identify SWAC
    levels that pose acceptable risks, are typically lower than
    0.25 ppm. Consequently, those thresholds will not be
    achieved through active remediation efforts. Instead, they
    will be achieved through a process of natural recovery that
    will take many years after the active remediation work is
    complete. For example, EPA estimates that 20 years of natu-
    ral recovery will be required to achieve acceptable noncan-
    cerous health risks to recreational anglers from walleye con-
    sumption. The corresponding time required to achieve an
    acceptable cancer risk is estimated at 45 years. And even
    then, some risk of harm will remain. EPA estimates that
    more than 100 years of natural recovery will be required to
    achieve PCB concentrations at which no adverse health ef-
    fects have been observed.
    As a result, the harm resulting from PCB contamination
    in the Lower Fox River cannot be characterized as binary.
    PCB concentrations below the 1.0 ppm remedial action level
    and even the 0.25 ppm target SWAC still pose a threat to
    human health and the environment. Even in areas where no
    remediation is required, higher PCB concentrations contrib-
    ute more to the risk of harm and require a longer period of
    natural recovery to achieve an acceptable risk. Moreover, not
    all concentrations above EPA’s remedial thresholds are
    28                                    Nos. 13-2436 & 13-2441
    equally harmful; the risk of harm increases with concentra-
    tion even at high levels.
    The continuous (as opposed to binary) nature of PCB
    contamination in the Lower Fox River leads us to reexamine
    EPA’s remediation rules to determine whether remediation
    costs are still a useful approximation of the contamination
    caused by each party. As with the contamination, the district
    court thought that remediation costs resembled an on/off
    switch: sediment with PCB concentrations below 1.0 ppm
    would impose no remediation costs, while sediment with
    PCB concentrations above 1.0 ppm would always impose
    about the same remediation costs. We think the district court
    got this wrong as well. In fact, remediation costs increase
    with the degree of contamination above 1.0 ppm. As a result,
    remediation costs are still a useful approximation of the de-
    gree of contamination caused by each party.
    The default remedial approach is dredging, but if certain
    criteria are met, an alternative approach such as capping
    (with various cap thicknesses) or sand covering may be
    used. Dredging is the most expensive approach, sand cover-
    ing is the cheapest, and capping lies somewhere in between
    (with thicker caps being more costly). Location-specific de-
    sign requirements do come into play; for example, a cap
    cannot be used if the required depth of the navigation chan-
    nel cannot be maintained. But all else being equal, higher
    PCB concentrations nearer the surface are more likely to re-
    quire dredging, while lower concentrations at greater depths
    are more likely to be eligible for capping or even sand cover-
    ing. Thus, the cost of the remedial approach in a particular
    area is positively correlated with the level of contamination
    Nos. 13-2436 & 13-2441                                     29
    near the surface of that area, which contributes to the opera-
    ble unit’s SWAC, and consequently, the harm.
    In sum, neither the PCB contamination in OU4 nor the
    associated remediation costs are binary in nature. However,
    remediation costs are still a useful approximation of the de-
    gree of contamination, because both remediation costs and
    the relevant measure of contamination (SWAC) are positive-
    ly correlated with the concentration of PCBs near the sur-
    face, even for concentrations that exceed the remedial action
    level of 1.0 ppm. As a result, we think the harm would be
    theoretically capable of apportionment if NCR could show
    the extent to which it contributed to PCB concentrations in
    OU4. And if NCR cleared that hurdle, we think a reasonable
    basis for apportionment could be found in the remediation
    costs necessitated by each party.
    Two of NCR’s experts, Dr. John Connolly and Philip Si-
    mon, estimated the percentages of PCB mass attributable to
    each party in OU4. A third expert, John Butler, took these
    mass percentages and multiplied them by the actual concen-
    trations of PCBs in OU4, which he obtained from a database
    of core samples, to determine the concentrations of PCBs at-
    tributable to each party. Butler then used these concentra-
    tions to calculate the remediation costs caused by each party
    using EPA’s remediation rules.
    The district court thoroughly critiqued the mass-
    percentage estimates provided by Simon and Dr. Connolly,
    and we agree that those estimates likely understated NCR’s
    contribution to the PCBs in OU4. However, Butler also ran
    his analysis using the higher estimates provided by Georgia-
    Pacific’s expert, Dr. John Wolfe. The district court failed to
    explain why Dr. Wolfe’s mass-percentage estimates were
    30                                       Nos. 13-2436 & 13-2441
    unreliable. Moreover, apart from its assumption that the
    PCB contamination in the Lower Fox River is binary in na-
    ture, the district court levied no criticism at Butler’s applica-
    tion of the mass-percentage estimates he used. There may be
    reasons to find that Dr. Wolfe’s mass-percentage estimates
    are unreliable, and there may be reasons to find that Butler’s
    use of those estimates was unsound, but we will not under-
    take such factfinding in the first instance. Therefore, we will
    reverse the district court’s decision on NCR’s divisibility de-
    fense and remand for further proceedings.
    2. Glatfelter
    Although PCB discharges from the Bergstrom Mill un-
    disputedly made their way into OU4, Glatfelter has made no
    attempt to quantify what percentage of the contamination in
    OU4 it may have caused. Instead, even in relation to its di-
    visibility defense, Glatfelter insists that it caused none of the
    contamination in OU4. Because the burden to prove divisi-
    bility rests on the defendant, Glatfelter is playing an all-or-
    nothing game, and we agree with the district court that it has
    lost.
    Glatfelter’s theory of divisibility relied almost entirely
    upon the expert opinion of Dr. Victor Magar. As part of his
    analysis, Dr. Magar estimated that only 14,000 kg were dis-
    charged into the river from the Bergstrom Mill. In contrast,
    government estimates ranged from 128,000 to 188,000 kg. To
    reach his much lower estimate, Dr. Magar first measured the
    mass of the sludge in the mill’s adjacent landfill, as well as
    the PCB concentrations in that sludge. He then used compa-
    ny records to establish the efficiency with which solids were
    removed from Bergstrom’s wastewater and deposited in the
    landfill, which allowed him to estimate the mass of solids
    Nos. 13-2436 & 13-2441                                      31
    that remained in Bergstrom’s wastewater and were dis-
    charged into the river. Then, assuming that the discharged
    solids had the same concentration of PCBs as the solids de-
    posited in the landfill, he calculated the mass of PCBs dis-
    charged into the river.
    Relying on other experts, the district court soundly criti-
    cized Dr. Magar’s PCB mass estimate for the Bergstrom Mill.
    As the court noted, the clarifier used to remove solids from
    Bergstrom’s wastewater would have allowed larger solids to
    settle out and be removed while leaving smaller particles
    suspended in the wastewater. Because PCBs adsorb (attach)
    to the surface of solids, and because smaller particles have
    higher surface-to-mass ratios, PCB concentrations in masses
    of smaller particles tend to be higher. Thus, Dr. Magar’s as-
    sumption that the PCB concentrations in Bergstrom’s landfill
    were equal to the concentrations in the solids it discharged
    into the River was unsound. The district court’s finding on
    this point was not clearly erroneous. Therefore, we accept
    the fact that Dr. Magar greatly understated the mass of PCBs
    discharged into river by Bergstrom, for which Glatfelter is
    now responsible.
    Next, Dr. Magar opined that PCBs from the Bergstrom
    Mill would not have reached OU4 in concentrations above
    the 1.0 ppm threshold because (1) PCBs that deposited in the
    downstream part of OU1 generally did so in concentrations
    below 1.0 ppm, (2) the downstream part of OU1 was similar
    to OU4 in terms of its depositional properties, and (3) PCB
    concentrations decline as contaminated sediment moves
    downstream and mixes with clean sediment. Thus,
    Dr. Magar thought that PCBs from the Bergstrom Mill
    32                                     Nos. 13-2436 & 13-2441
    would have been diluted to concentrations far below 1.0
    ppm by the time they reached OU4.
    However, the district court soundly criticized this aspect
    of Dr. Magar’s opinion as well. Relying on other experts, the
    court found that lower OU1 was not nearly as depositional
    as Dr. Magar claimed. Thus, in the district court’s words,
    “high-concentration PCB deposits were absent in lower OU1
    not because PCB concentrations had already petered out, but
    because the PCBs simply were not permanently depositing
    in that part of the river.” This finding was not clearly erro-
    neous. Thus, we accept the fact that Dr. Magar greatly un-
    derestimated the concentrations at which PCBs from the
    Bergstrom Mill would have entered OU4.
    Consequently, Glatfelter failed to prove that it was not a
    sufficient cause of at least some of the contamination in OU4,
    and this alone is enough for us to affirm the district court’s
    decision on its divisibility defense. But the district court did
    not stop there. The court also found that even if Glatfelter
    had proved that it was not a sufficient cause of contamination
    in OU4, it failed to prove that it was not a necessary cause of
    such contamination. Glatfelter argues that it could not possi-
    bly have been a necessary but insufficient cause of contami-
    nation in OU4 and that the district court only reached this
    conclusion because it failed to grasp how PCB concentra-
    tions are calculated. We disagree.
    Dr. Magar opined that if PCBs from the Bergstrom Mill
    made their way into OU4 in concentrations less than the re-
    medial action level of 1.0 ppm, they could not have been a
    necessary cause of the cleanup in OU4 because, as he put it,
    “This is not an additive process. This would be an averaging
    process.”
    Nos. 13-2436 & 13-2441                                     33
    For example, if 30 mg PCBs in 1 kg of suspend-
    ed solids (30 mg/kg PCBs) were mixed with 1
    mg PCBs in 1 kg of suspended solids (1 mg/kg
    PCBs). The resulting mixture would contain 31
    mg PCBs and 2 kg of suspended soils. The mix-
    ture concentration, which is equal to the mass
    of PCBs divided by the mass of suspended
    soils, would be equal to 31 mg PCB/ 2 kg sus-
    pended soils or 15.5 mg/kg. Thus, the concen-
    tration is the weighted average of the two
    sources.
    Expert Report of Victor Magar, PhD, PE, at 18-19, Sep. 28,
    2012. In Dr. Magar’s opinion, this averaging process means
    that PCBs entering OU4 at a concentration below 1.0 ppm
    and mixing with other PCB-contaminated solids could never
    push the combined PCB concentration above 1.0 ppm.
    We have no qualms with the general proposition that
    when two masses of PCB-contaminated solids mix, their
    combined concentration is the mass-weighted average of
    their separate concentrations. It does not follow, however,
    that removing the PCBs that came in at a lower concentra-
    tion increases the average concentration. This is because the
    solids to which that lower concentration of PCBs would
    have attached still join the mix, only now they are PCB-free,
    resulting in a lower average concentration. Dr. Magar’s mis-
    take was ignoring the clean solids that would remain after
    removing the lower concentration of PCBs.
    Perhaps this is best illustrated through an example. In his
    expert report, Dr. Magar expressed the averaging concept
    34                                         Nos. 13-2436 & 13-2441
    through the following formula, where C is PCB concentra-
    (𝐶1 × 𝑇𝑆1 ) + (𝐶2 × 𝑇𝑆2 )
    tion in mg/kg and TS is the total solid mass in kg:
    𝐷𝑜𝑤𝑛𝑠𝑡𝑟𝑒𝑎𝑚 𝐶𝑜𝑛𝑐𝑒𝑛𝑡𝑟𝑎𝑡𝑖𝑜𝑛 =
    𝑇𝑆1 + 𝑇𝑆2
    Let us suppose that Party 1 discharges enough PCBs to cre-
    ate a concentration of 1.5 ppm (mg/kg) in 1.0 kg of sediment,
    and Party 2 discharges enough PCBs to create a concentra-
    tion of 0.5 ppm (mg/kg) in 1.0 kg of sediment. When these
    two masses combine, Dr. Magar’s formula yields the follow-
    (𝐶1 × 𝑇𝑆1 ) + (𝐶2 × 𝑇𝑆2 ) (1.5 × 1.0) + (0.5 × 1.0)
    ing concentration:
    =                          = 1.0 𝑝𝑝𝑚
    𝑇𝑆1 + 𝑇𝑆2                  1.0 + 1.0
    Thus, there are just enough PCBs to require remedial action.
    Now, let us assume that Party 2 discharged no PCBs, but the
    sediment to which Party 2’s PCBs would have attached still
    combines with the sediment to which Party 1’s PCBs have
    attached. Dr. Magar’s formula then yields the following con-
    (𝐶1 × 𝑇𝑆1 ) + (𝐶2 × 𝑇𝑆2 ) (1.5 × 1.0) + (0.0 × 1.0)
    centration:
    =                          = 0.75 𝑝𝑝𝑚
    𝑇𝑆1 + 𝑇𝑆2                  1.0 + 1.0
    Thus, remediation is required if Party 2’s PCBs are included,
    but remediation is not required if Party 2’s PCBs are exclud-
    ed, even though Party 2’s PCBs entered the mix at a concen-
    tration below the 1.0 ppm remedial action level. This goes to
    show that Dr. Magar’s conclusion that it is impossible to
    have necessary but insufficient causes does not follow from
    the principle on which he relied, i.e., that concentrations av-
    erage rather than add.
    In sum, Glatfelter failed to prove that the PCB discharges
    for which it is responsible were not a sufficient, or at least a
    Nos. 13-2436 & 13-2441                                          35
    necessary, cause of at least some of the contamination in
    OU4. Therefore, the district court correctly ruled against
    Glatfelter on its all-or-nothing divisibility defense.
    B. INJUNCTIVE RELIEF
    Finally, NCR and Glatfelter attack the district court’s de-
    cision to enter a permanent injunction. We are persuaded by
    Glatfelter’s argument that permanent injunctive relief is an
    inappropriate mechanism to enforce an administrative order
    under § 106(b) of CERCLA, 42 U.S.C. § 9606(b). Therefore,
    we vacate the permanent injunction.
    In United States v. Ottati & Goss, Inc., 
    900 F.2d 429
    , 433 (1st
    Cir. 1990), then-Judge Breyer explained that there are four
    statutory paths EPA might pursue to achieve a CERCLA
    cleanup. Two of those paths warrant discussion here, and
    both arise under § 106 of CERCLA, 42 U.S.C. § 9606. The first
    is found in the first sentence of § 106(a), which provides as
    follows:
    [W]hen [EPA] determines that there may be an
    imminent and substantial endangerment to the
    public health or welfare or the environment
    because of an actual or threatened release of a
    hazardous substance from a facility, [it] may
    require the Attorney General of the United
    States to secure such relief as may be necessary
    to abate such danger or threat, and the district
    court of the United States in the district in
    which the threat occurs shall have jurisdiction
    to grant such relief as the public interest and
    the equities of the case may require.
    36                                     Nos. 13-2436 & 13-2441
    42 U.S.C. § 9606(a). This provision allows EPA to seek an in-
    junction requiring PRPs to take remedial action in “an emer-
    gency situation, where the agency has not yet had time to
    compile a thorough record and to issue an” administrative
    order. Ottati & 
    Goss, 900 F.2d at 433
    . And it explicitly makes
    relevant “the public interest and the equities,” which indi-
    cates that the traditional elements of injunctive relief must be
    established. See Old Republic Ins. Co. v. Emp’rs Reinsurance
    Corp., 
    144 F.3d 1077
    , 1081 (7th Cir. 1998) (listing the elements
    that must be proved to obtain permanent injunctive relief,
    which include considerations of equity and the public inter-
    est).
    In less urgent situations, EPA may proceed under the
    second sentence of § 106(a), which allows it to follow the
    necessary administrative procedures and issue “such orders
    as may be necessary to protect public health and welfare and
    the environment.” 42 U.S.C. § 9606(a). Then, if the PRPs fail
    to comply with such an order, the government may bring an
    action under § 106(b)(1), which provides as follows:
    Any person who, without sufficient cause,
    willfully violates, or fails or refuses to comply
    with, any order of [EPA] under subsection (a)
    of this section may, in an action brought in the
    appropriate United States district court to en-
    force such order, be fined not more than
    $25,000 for each day in which such violation
    occurs or such failure to comply continues.
    
    Id. § 9606(b)(1).
    In such an action, the court may review the
    selected remedy. 
    Id. § 9613(h)(2).
    However, its review is lim-
    ited to the administrative record, and EPA’s decision must
    Nos. 13-2436 & 13-2441                                                     37
    be upheld unless it “was arbitrary and capricious or other-
    wise not in accordance with law.” 
    Id. § 9613(j).
    Thus, unlike
    an action under the first sentence of § 106(a), equitable con-
    siderations play no part in an action to enforce an adminis-
    trative order under § 106(b). Instead, “[w]hen the EPA asks a
    court ... to enforce a lawful (nonarbitrary) EPA order, the
    court must enforce it.” Ottati & 
    Goss, 900 F.2d at 434
    .
    As a result, if courts were to undertake the traditional
    analysis for injunctive relief in deciding whether to enforce
    an EPA order, they would inject equitable considerations
    where they do not belong. Moreover, as Glatfelter points
    out, the entry of an injunction that simply orders PRPs to
    comply with a complex cleanup order issued by EPA may
    run afoul of Federal Rule of Civil Procedure 65(d)(1)(C),
    which requires that every injunction “describe in reasonable
    detail—and not by referring to the complaint or other docu-
    ment—the act or acts restrained or required.” Accordingly,
    permanent injunctive relief is incongruous with the nature
    and purpose of an action to enforce an administrative clean-
    up order under CERCLA § 106(b). 5
    Further, permanent injunctive relief is unnecessary as a
    means of enforcing an administrative cleanup order, as the
    statute already provides for civil penalties of $25,000 per day
    that a PRP fails to comply with such an order “without suffi-
    cient cause.” Nothing we have said prevents the government
    from seeking declaratory relief to establish that a PRP lacks
    sufficient cause for noncompliance, such as the arbitrariness
    5In contrast, preliminary injunctive relief may be appropriate in an action to
    enforce an EPA cleanup order, as it was in this case. Equitable principles are
    an appropriate consideration when deciding whether to require PRPs to
    undertake remedial action pending review of an EPA cleanup order.
    38                                    Nos. 13-2436 & 13-2441
    of the selected remedy or a defense to liability. And if the
    government obtains such declaratory relief, the PRP’s obli-
    gation to comply with the administrative order or face civil
    penalties will be established. In such circumstances, adding
    an injunction to the mix does little more than enjoin the de-
    fendant to obey the law, a practice we have criticized. See,
    e.g., EEOC v. AutoZone, Inc., 
    707 F.3d 824
    , 841–42 (7th Cir.
    2013). For all of these reasons, we hold that the permanent
    injunction entered by the district court in this case was im-
    proper and must be vacated.
    IV.    CONCLUSION
    The district court’s summary judgment rulings on the
    propriety of the remedy and Glatfelter’s liability are
    AFFIRMED. The permanent injunction entered by the district
    court is VACATED. The declaratory judgment entered by the
    district court is AFFIRMED as to Glatfelter, but VACATED as to
    NCR, and Case No. 13-2441 is REMANDED for the district
    court to reconsider NCR’s divisibility defense consistent
    with this opinion. Circuit Rule 36 shall not apply on remand.