Archive for the tag 'Water Resources'

NJ Appeals Court addresses permits for combined sewer overflows.

SteveK March 12th, 2013

The Appellate Division recently handed down an opinion in In re Petition to Revoke Statewide General CSO Permit.  In that case, a group of private environmental watchdog groups brought suit to force the NJDEP to cancel certain Combined Sewer Overflow (CSO) general permits issued to municipalities with combined sewer systems.
In 1994, the USEPA issued a national control policy for CSOs, which created a framework for controlling CSO discharges through the use of permits.  This policy provided what are known as the “Nine Minimum Controls” aimed at reducing the prevalence and impacts of CSOs without necessitating major construction or significant engineering studies.
In 2004, NJDEP issued a General CSO Permit to affected municipalities in accordance with these Nine Minimum Controls, which would allow those municipalities to operate their sewer systems and to discharge CSOs when necessary.  The General Permit went into effect on August 1, 2004, and was set to lapse on July 31, 2009.  However, prior to the expiration date, the affected municipalities requested an administrative extension, which, under N.J.A.C. 7:14-2.8(a), triggers a continuation of that permit’s effect until such a time as the extension is either granted or denied.  Accordingly, the 2004 permit remains in effect.  On April 15, 2011, the plaintiff environmental groups filed a written request that the NJDEP revoke and replace the General Permit with individualized permits involving tighter controls.
On September 15, 2011, NJDEP issued its final decision denying appellants’ request that the General Permit be revoked and reissued with conditions, stating that it did “not agree that this existing General Permit is inconsistent with State or federal law.”  Further, revocation was not necessary because NJDEP “intend[ed] to reissue the existing general permit with revised conditions to reflect the current status of the compliance with the nine minimum controls and Long Term Control Plan requirements.”  This appeal followed.
After the notice of appeal was filed, NJDEP advised that its plans had changed with regard to the General Permit.  Specifically, rather than reissuing a new General Permit, it would replace it with individual permits issued to each CSO owner, and to modify or renew existing individual permits to sewerage treatment plants that receive sewer flows.
The parties agreed that CSOs are a problem and that changes need to be made to the way the municipalities and sewer treatment plants which discharge them should be regulated, but they differed as to how that should occur.  The environmental group plaintiffs argued that the General Permit must be immediately revoked and simultaneously reissued, or replaced with individual permits, with a variety of new conditions to address their concerns.  NJDEP, on the other hand, argued that it would be a waste of time and resources to prosecute a revocation action against each of the affected municipalities when it was already in the process of issuing new individual permits to replace the disputed General Permit.
The court noted that N.J.A.C. 7:14A-16.6(a), which sets forth the valid “causes for revocation,” specifically states that the conditions therein are “causes for suspending or revoking a permit during its term.”  On the other hand, the General Permit at issue had expired and was on administrative extension, under which circumstances N.J.A.C. 7:14A-2.8 applies.  That provision gives NJDEP a variety of options, including revocation or replacement of the extended permit.  Accordingly, NJDEP’s action under these circumstances was fully supported by these regulatory provisions.
Further, the court agreed that “it makes little practical sense to initiate a costly and time-consuming revocation process against twenty-one municipalities when the General permit has expired and is on an administrative extension.”  Instead, “[b]y focusing on reissuing new individual permits, with more stringent conditions, DEP will make better use of its scarce resources and reach the same end result now sought by appellants.”  Ultimately, “there is simply no need for DEP to first revoke the General Permit in order to issue the new individual permits[;] [i]t may simply propose and issue the new permits.”
Finally, because the affected municipalities were not parties to the present appeal, and it did not even appear that they were notified of the request to revoke the General Permit, the court would be unable to grant the requested relief in the first instance.  “No permit can be revoked unless each permittee is given the opportunity to request a contested case hearing concerning the proposed revocation.”

DiFrancesco, Bateman, Coley, Yospin, Kunzman, Davis, Lehrer & Flaum, PC (www.dbnjlaw.com ) is a full service law firm in New Jersey which provides a broad range of legal services, including the representation of clients in environmental and defense of toxic exposure matters. For additional information about the matters in this bulletin or in the firm’s environmental practice, please contactSteven A. Kunzman, Esq. who heads our Environmental and Latent Injury Litigation Department.

The information contained in this blog is intended solely for informational purposes; it is a advertising publication of DiFrancesco, Bateman, Coley, Yospin, Kunzman, Davis, Lehrer & Flaum P.C.This publication is intended to alert recipients of developments in the law and is not intended to provide legal counsel, advice or opinion on any specific facts or circumstances. The contents are intended as general information only. You are urged to consult a member of this firm or your own attorney concerning your particular situation and any specific legal questions you might have.

 

Courts Define Limits of EPA’s Control of Storm Water under Clean Water Act

SteveK February 13th, 2013

Recent decisions U.S. District Court in the Eastern District of Virginia and the U.S. Supreme Court define the limits of the extent to which authorities can control discharges of storm water under the Clean Water Act (CWA). On January 3, 2013, in Virginia Dept. of Transp. V. U.S. E.P.A., the Eastern District of Virginia held that the EPA is authorized to set Total Maximum Daily Loads (TMDL) of pollutants permitted to be discharged into bodies of water under the CWA; however, TMDLs do not apply to storm water carrying sediment, because storm water runoff is not a pollutant under the CWA.  As a result of prior unrelated litigation, the EPA was required to set TMDL limits for discharges into the Accotink Creek, a tributary of the Potomac River in Fairfax County, Va. , because the creek was determined to have “ ‘benthic impairments,’ which is to say the community of organisms that live on the bottom of the creek were not as numerous or healthy as they should be.” The EPA placed a limit on the flow of storm water into the creek due, in part, to a determination that the storm water contained sediment which is considered a pollutant. The Court analyzed the language of the CWA and concluded that although it authorizes the establishment of TMDLs for pollutants, and sediment is a pollutant, it could not place limits on storm water containing sediment because storm water is not a pollutant under the act. The Court concluded that Congress had been very specific in providing “precise standards and definite guidelines on how the environment should be protected” and does not extend the authority to the EPA to establish TMDLs for non-pollutants as surrogates for pollutants. Accordingly, the limits placed on the storm water flow rate into the creek were voided.Five days later, on January 8, 2013, the Supreme Court issued a decision in Los Angeles County Flood Control District v. NRDC 568 U.S. ___(2013) which held that a “discharge of pollutants” does not occur when polluted water flows from one portion of a navigable water body through “concrete channel or other engineered improvement” into another section of the water body.  In the case, the Flood Control District operates a “municipal separate storm sewer system” that collects and discharges storm water. The Court concluded that it does not qualify as a discharge of pollutants under the CWA, quoting from the Second Circuit decision, Catskill Mountains Chapter of Trout Unlimited, Inc. v.  New. York, 273 F. 3d. 481, 492 (CA2 2001) “…[i]f one takes a ladle of soup from a pot, lifts above the pot, and pours it back into the pot, one has not added soup or anything else to the pot.”These two decisions demonstrate an intention to strictly construe the CWA, and provide a practical, if not holistic, view of the hydrogeological systems. Although not specifically stated in Virginia DOT, storm water may be seen as a natural source of water that drains into navigable waters, and therefore, is not subject to discharge limits that would apply to industrial discharges into the same water body. This is supported by the Los Angeles Flood Control decision, which concludes that the collection and discharge of storm water does not constitute the discharge of a pollutant. Arguably, this concept should be able to be applied to sewage systems which have been authorized and controlled by governmental bodies, as they also are a part of the system of water collection naturally flowing into the regional water “drainage” into navigable waters.

DiFrancesco, Bateman, Coley, Yospin, Kunzman, Davis, Lehrer & Flaum, PC (www.dbnjlaw.com ) is a full service law firm in New Jersey which provides a broad range of legal services, including the representation of clients in environmental and defense of toxic exposure matters. For additional information about the matters in this bulletin or in the firm’s environmental practice, please contactSteven A. Kunzman, Esq. who heads our Environmental and Latent Injury Litigation Department.

The information contained in this blog is intended solely for informational purposes; it is a advertising publication of DiFrancesco, Bateman, Coley, Yospin, Kunzman, Davis, Lehrer & Flaum P.C.This publication is intended to alert recipients of developments in the law and is not intended to provide legal counsel, advice or opinion on any specific facts or circumstances. The contents are intended as general information only. You are urged to consult a member of this firm or your own attorney concerning your particular situation and any specific legal questions you might have.

 

Environmental Case Summaries- 2012

SteveK January 9th, 2013

The following are summaries of selected environmental decisions from 2012 focusingon New Jersey decisions, with some cases addressing other issues on a federal level.

New Jersey Spill Act

In NJDEP v. Dimant, 212 N.J. 153 (2012) the New Jersey Supreme Court ruled that  in order for there to be Spill Act liability, there must be a nexus between a discharge of contaminants, the discharger,and the contamination to be remediated at a particular site.

The decision from the Appellate Division was previously reported in our blog on July 5, 2011. In the case, the defendants included succession of owners and operators of a dry cleaning establishment. The contamination in the groundwater included the well-known dry cleaning chemical, PCE, as well as the byproducts of its degradation: TCE and DCE. There was evidence that the PCE was related to the dry cleaning operations. All but one of the direct defendants settled with the State. The remaining defendant went to trial. The trial judge found that although there were discharges or releases of PCE during the stewardship of the remaining defendant, there was no proof that those discharges went through the asphalt and contaminated the environment.

The Court began its analysis by noting that, under the Spill Act, a discharge occurs pursuant to N.J.S.A. 58:10-23.11b when a hazardous substance is spilled or leaked, or otherwise released, “into the waters or onto the lands of the State, or into waters outside the jurisdiction of the State when damage may result to the lands, waters or natural resources within the . . . State.”  There was some dispute between the parties as to whether the “damage may result” language applies to releases of hazardous substances “into the waters or onto the lands of the State,” or only to releases outside the State.  The Court concluded based on the grammatical construction of the sentence, that the better interpretation of this provision would include mere release of hazardous substances, irrespective of whether “damage may result,” should qualify as a “discharge” for the purposes of the Spill Act.  Accordingly, the fact that Sue’s “operated a business where, on at least one occasion, an exterior building pipe emitted an uncontrolled drip  of fluid with a high concentration of PCE onto the ground” was sufficient to qualify as a “discharge,” whether or not that PCE ever made it to the now-contaminated groundwater.

However, the Legislature’s stated purpose in passing the Spill Act was “to provide liability for damage sustained within this State as a result of any discharge of said substances.”  Accordingly, one who is “in any way
responsible for any hazardous substance” is strictly liable, upon its
discharge, for “all cleanup and removal costs no matter by whom incurred.”  The Court pointed out that the phrase “in any way responsible” necessarily requires some connection between the discharge complained of and the alleged discharger, noting that “[t]hat nexus is what ties the discharger to the discharge that is alleged to be the, or a, culprit in the environmental contamination in issue.”  Such a nexus must be demonstrated also to exist between the discharge for which one is “in any way responsible” and the contaminated site for which cleanup and other related authorized costs are incurred.  In fact, the statute itself states that “cleanup and removal costs” are costs “associated with a discharge.”

In analyzing the particular level of causation which should be required under the Spill Act, the Court turned to the Act’s legislative history.  Specifically,
this analysis led the Court to note that despite the lack of express direction
from the Legislature as to the requisite connection between liability and all
forms of relief, there is no basis to apply a proximate-cause analysis in
assessing the bases for relief, as this would thwart the public purpose of the
statute.  Rather, because the Spill Act provides for a range of forms of relief, including injunctive relief and recovery of damages and costs, the causation standard to be applied must accommodate these varying forms of available relief, “as the request for relief is framed.”  Therefore, “while a plaintiff need not trace the cause of the response costs to each defendant in a multi-defendant case involving a contaminated site, it is not enough for a
plaintiff to simply prove that a defendant produced a hazardous substance and that the substance was found at the contaminated site and ask the trier of fact to supply the link.”  Accordingly, the Court concluded that “in an action to obtain damages, authorized costs and other similar relief under the Act there must be shown a reasonable link between the discharge, the putative discharger, and the contamination at the specifically damaged site.”

Applying this standard to the case at bar, the fact that DEP representatives had detected impermissibly high levels of PCE emanating from a pipe connected to Sue’s business, without any record of cracks in the pavement below or any other potential mechanism by which this alleged PCE might have made its way to the now-contaminated groundwater, was insufficient.  “There was no basis – on the state of these proofs as found by the trial court – to shift to Sue’s liability for compensatory damages for cleanup of the wells that were tainted, or even for the investigatory expenses associated with remediation of the natural-resource damage, because the DEP never made the requisite connection showing how the dripping PCE at Sue’s reasonably could have made its way into the groundwater.”

In “two-site” cases (wherein a release of contaminants at one site results in contamination somewhere else), “in order to make out a prima facie case, the plaintiff must establish a causal connection between the defendant’s release of  hazardous substances and the plaintiff’s response costs incurred in cleaning them up.”  The Court explained that the plaintiffs here could have satisfied their burden of production by (1) identifying the hazardous substance at their site; (2) identifying the same hazardous substance at defendant’s site; and (3) providing evidence of a plausible migration pathway by which the contaminant could have traveled from the defendant’s facility to the plaintiff’s site.  However, in the absence of a “plausible migration pathway,” there is no basis on which to hold the defendant liable.

With respect to the DEP’s claim that Sue’s should be required to investigate its contamination and determine a remedy for its own discharge, the Court held that “it would be fundamentally unfair to saddle Sue’s with such an investigatory obligation, on a joint and several liability basis, at this time, considerable more than a decade after the DEP discovered the dripping pipe during Sue’s operation.”

In Dalton v. Shanna Lynn Corp., an unreported decision from the New Jersey Appellate Division, the court ruled that in order for a party to seek contribution under the Spill Act, a party must first remediated the property.

The case arose from the failure and leaking of an underground oil tank on the plaintiffs’ property, which they purchased from the defendants years prior.  After a fire destroyed the motel on the premises and the plaintiffs began rebuilding, an excavator informed them that the ground was contaminated
with fuel oil.

Ultimately the court held that it would not force the defendants to contribute toward paying the expenses for remediating the contamination until the work was completed.  In so holding, the court pointed to the language of the Spill Act, which says that “whenever one or more dischargers or persons cleans up and removes a discharge of a hazardous substance, those dischargers and persons shall have a right of contribution against all other dischargers and persons in any way responsible for a discharged hazardous substance . . . .”  N.J.S.A. 58:10-23.11f(a)(2)(a).  In other words, “one must first cleanup and remove the discharge in order to recover for discharge of a hazardous substance.”

Because the plaintiffs had not even begun remediating the property at the time they filed this suit, they had no way of knowing “the extent of the spill much less the nature of the work to remediate the site and its cost.”
Accordingly, until this work was completed and the costs associated with
it were certain, the plaintiffs were unable to recover from the other
responsible parties.

In State Farm Fire & Casualty Co. v. Shea, an unreported decision from the N.J. Appellate Division, the Court held that the innocent purchaser defense requires the purchaser to have taken basic measures with regard to potential for environmental problems.

This case arose from a dispute regarding who should bear responsibility for soil and groundwater contamination emanating from two residential USTs.  Rossi’s property contained a fuel oil UST buried under the driveway of her residence, which she removed as a condition of sale of the house prior to closing, and she further agreed to be held responsible for subsequent cleanup of contamination on the property.

Shea’s property was separated from Rossi’s by a driveway.  Upon his purchase
of the home, Shea did not conduct a home or environmental inspection, and
despite admittedly noticing a vent pipe in the back yard, he did not inquire
about the purpose of that pipe at any point before or after the purchase.

During the course of the litigation a significant factual dispute arose between the experts for each party which was highly fact-specific; there were two different plumes of contamination with a “clean zone” in between, as well as significant variability in the concentration of contaminants within each plume, which was argued to bring into question the trial judge’s finding that one plume each emanated from the Shea and Rossi properties.  This argument was ultimately rejected.

Shea further advanced the argument that the trial judge inappropriately imposed on him an affirmative duty to conduct a pre-purchase environmental investigation, that equitable factors should have been considered in fashioning the remedy, and that it was never addressed whether the contamination occurred during his ownership of the property.  After a discussion of the text of the Spill Act, particularly with respect to the “innocent purchaser” exemption, the court explained the significance of Shea’s failure to inquire about the pipes in the back yard which he admitted that he noticed prior to purchase.

“The issue . . . is not whether every buyer of a home must conduct an environmental assessment prior to purchase but whether, having observed a pipe protruding from the ground, Shea had a duty, at a minimum, to inquire.”  It was significant that “[h]is ignorance [was] solely associated with his failure to ask a basic question about something most people do not expect to encounter in the backyard of their home,” and so “[i]t is not unreasonable to require him to ask questions under these circumstances to identify the pipe and then take whatever measures are warranted by the response to those questions.”  Accordingly, the “innocent purchaser” exemption from liability was inapplicable here.

In an unreported decision, NJDEP v. The Pole Tavern Mobil Site, et al., the Appellate Division rejected defendants efforts to avoid the obligations it assumed under an ACO with the NJDEP for site remediation.

Defendant Harmeet Kohli purchased the “Pole Tavern Mobil Site” in Upper Pittsgrove in 2002, and Nanak Auto Fuel, Inc. operates a gas station on the property which contains a UST system.  The NJDEP issued a AONOCAPA with respect to the property, which ultimately led to an ACO between Kohli and the DEP.  Pursuant to the ACO, Kohli was required to conduct a remedial investigation of the property, submit a remedial action work plan, and implement the plan pursuant to DEP approval.

Central to the present dispute is the requirement in the ACO that Kohli establish and maintain a “remediation funding source,” the initial amount of which was required to be $50,000.  Kohli submitted a “line of credit agreement” between Nanak and Sun National Bank establishing a line of credit for “remediation of the site pursuant to [the ACO],” expiring on December 28 of that year.  The following January 31, the DEP requested evidence of the continuation of this line of credit, but Kohli and Nanak failed to provide any.

Consequently, the DEP issued a notice of violation, but stated it would not assess a penalty if Nanak paid the surcharge and offered the required evidence within 30 days.  Nanak paid the surcharge but asked the department to waive the line of credit requirement because “Nanak has already spent $25,000 to $35,000 in remediation work” on the property – however, this request was rejected.  Later that month, Sun National Bank informed the DEP that Kohli and Nanak had “set aside $25,000 for the purpose of remediation,” but forwarded no documentation to support this.

The DEP issued an AONOCAPA ordering compliance with the ACO’s funding requirement and assessing a $5,000 penalty.  Kohli and Nanak requested a
hearing, at which they asserted that they could not afford to establish the
required $50,000 line of credit and that $25,000 was “sufficient.”  However, the ALJ issued a decision, finding that merely because the costs of remediation exceeded expectations, “that is not a defense under the consent order.”  The DEP Commissioner issued a final agency decision adopting the ALJ decision in its entirety.

On appeal, the court held that nothing in the record suggested that the DEP Commissioner acted arbitrarily, unreasonably or capriciously, or that the decision was unsupported by evidence in the record.  “Where the parties have
agreed to the terms of a settlement, second thoughts are entitled to absolutely
no weight as against our policy in favor of settlement.”  Accordingly the decision of the NJDEP Commissioner was affirmed.

Spill Act and Common Law Trespass

In an unreported decision of the U.S. District Court in N.J. Woodcliff, Inc. v. Jersey Constr., Inc., the trial judge addressed a summary judgment motion by the New Jersey Department of Transportation (“NJDOT”) on the basis of an exemption from liability for certain activities by governmental entities, and
because trespass is an inappropriate means of asserting environmental claims under these circumstances.
Ultimately the motion was granted in part and denied in part.

Plaintiff Woodcliff, Inc. (“Woodcliff”) was owner/developer of a residential community in Hamilton, New Jersey.  During the course of Woodcliff’s
development activities, Jersey Construction, Inc. (“JCI”) was performing road
construction work elsewhere, which required removal 8,000 cubic yards of soil.  JCI offered this excess soil to Woodcliff for use in its development activities, and Woodcliff accepted.  The soil originated from a JCI roadwork
project which NJDOT required in connection with the development of a shopping center by Stanberry Hamilton LLC (“Stanberry”) in order to alleviate the increased traffic caused by the shopping center.  However, a year after Woodcliff’s acceptance of the soil, it was discovered that it was contaminated with arsenic.  Accordingly, Woodcliff filed suit against JCI
and NJDOT asserting claims under the Spill Act and for common-law trespass. NJDOT moved for summary judgment.

The court first addressed NJDOT’s argument that certain Spill Act exceptions from liability for governmental entities should apply.  NJDOT had argued
that N.J.S.A. 58:10-23.11f, which states that a “governmental entity which
acquires ownership of real property through . . . any circumstance in which the governmental entity involuntarily acquires title by virtue of its function as
sovereign, or where the governmental entity acquires the property by any means for the purpose of promoting the redevelopment of that property, shall not be liable . . . to the State or to any other person for any discharge which
occurred or began prior to that ownership,” should preclude liability here.  Specifically, NJDOT argued that the redevelopment exception was applicable, as well as the “involuntary” acquisition of title by way of the developer agreement with Stanberry which required the work at issue.

The court, however, rejected this argument on the basis that the record was insufficient to establish that there was no genuine issue of material fact.
The record was composed solely of a short affidavit from a NJDOT
employee and a copy of the Developer Agreement between NJDOT and
Stanberry.  These were insufficient to resolve the remaining questions as to where the contaminated soil originated, how that property was acquired, and for what purpose it was acquired.  Accordingly, summary judgment was held to be improper at this stage of the litigation, before any significant discovery had taken place.

As to the plaintiff’s trespass claim, the court noted that “[t]respass is a cause of action for one’s unauthorized entry (usually of tangible matter) onto the property of another.”  The basis of this claim was that although the plaintiff consented to the delivery of soil to its property, it did not consent to the arsenic being discharged there.  However, the court was quick to point out
that “use of trespass liability [under such circumstances] has been held to be
an inappropriate theory of liability and an endeavor to torture old remedies to
fit factual patterns not contemplated when those remedies were fashioned.”  Accordingly, liability for trespass under these facts was not available, and summary judgment as to this claim was granted.

Eminent Domain: Valuation of Contaminated Property

In Borough of Paulsboro v. Essex Chem. Corp., 427 N.J. Super 123 (App. Div., 2012) cert. denied, 56 A. 3d 395 (21012) the Court clarified the manner in which to value contaminated property in eminent domain proceedings, ruling that sites that have completed
an approved remediation are not subject to special procedures for property valuation.

The Borough of Paulsboro, New Jersey sought to acquire through its power of eminent domain from Essex Chemical Corporation a sixty-seven-acre riverfront tract of land containing a DEP-approved seventeen-acre closed landfill.  In Hous. Auth. of the City of New Brunswick v. Suydam Investors, LLC, 177 N.J. 2 (2003), the New Jersey Supreme Court established that contaminated property acquired through eminent domain must be valued as if the contamination had been remediated, and that the portion of the condemnation award required to pay the costs of remediation should be deposited into a trust-escrow account.  In this case, the Appellate Division addressed whether that special methodology for valuing contaminated
property applies in an eminent domain action for acquisition of property
containing a landfill that has been closed with the approval of the DEP.

At trial, it was determined that the fair market value of the property was approximately $1.5 million, based on a per-acre value of $22,500 applied uniformly to the entire sixty-seven-acre tract, including the seventeen acres of closed landfill.  On appeal, Paulsboro argued that the trial court improperly failed to follow the principles set forth in Suydam by valuing the property as if the landfill had been removed but denying its motion to escrow the condemnation award to pay the costs of that removal.

However, the Appellate Division rejected this argument.  The court explained that “the prerequisite for use of the special valuation methodology established in Suydam, under which the subject property is valued as if remediated and the estimated cost of remediation is deposited into a trust-escrow account, is the reality of a condemnee’s liability for the costs of remediation under the Spill Act and like statutory initiatives.”  On the other hand, “[i]f a site has been remediated with the DEP’s approval and the condemnee is not subject to any additional liability for remediation, the condemnee is no longer exposed to what the court in Suydam described as ‘double liability,’ and therefore, the special valuation methodology established in that case does not apply.”

Put more succinctly, the Suydam framework was inappropriate here because Essex was not subject to any additional obligation for remediation of the site – despite the continued presence of the landfill, the “remediation” pursuant to the relevant environmental statutes had already occurred, as evidenced by the DEP’s approval of the landfill closing.  The court illustrated that “[a]lthough the removal of the landfill undoubtedly would increase the property’s value, the removal is not required under any environmental statute, and is not what the court in Suydam meant by remediation of environmental contamination.”
Though the presence of the landfill could be considered in assigning a fair market value to the property under normal valuation techniques, there was
no “contamination” on the property to justify application of the framework
established in Suydam.

New Jersey Industrial Site Recovery Act (ISRA)

In Des Champs Laboratories, Inc. v. Martin, 472 N.J. Super 84(App. Div., 2012) the Court rejected requirements for applicability of the de minimis quantity exemption under the Industrial Site Recovery Act of 1993 (“ISRA”), N.J.S.A. 13:1K-6 et seq., the Site Remediation Reform Act of 2009 (“SRRA”), N.J.S.A. 58:10C-1 et seq., or any other statute authorizes the DEP to impose certain obligations on owners or operators of industrial establishments that stored or handled small amounts of hazardous materials as a
condition of obtaining a “de minimis quantity exemption” (“DQE”) from ISRA requirements.
Specifically, the court examined the validity
of certain recently-amended regulations requiring an applicant for a DQE to
certify that the property where the de minimis quantities had been present was now below DEP-established acceptable levels, and other regulations requiring applicants to remediate the property if the DEP disapproved their application.

Des Champs Laboratories, Inc., (“Des Champs”) operated an industrial facility in Livingston, New Jersey for approximately 14 years, manufacturing heat recovery ventilators.  In anticipation of ceasing operations at the facility, Des Champs’ environmental consultant submitted required documentation to the DEP pursuant to the ISRA certifying that there had been no discharges of
hazardous substances.  After the DEP issued a no further action letter, they sold the premises to intervenor R&K Associates, LLC.  Then, eight years
later, the DEP determined that unreported groundwater contamination in the area originated from the Des Champs property, causing it to rescind its prior NFA letter and require submission of a variety of remediation documentation.

Instead of complying with DEP’s requirements, Des Champs submitted a DQE affidavit pursuant to ISRA, and certified that it had handled a de minimis quantity of hazardous substances, thereby exempting it from ISRA.  However,
the DEP denied its DQE request.  Des Champs twice requested that the DEP reconsider this decision, but to no avail –the DEP issued a final determination that to regain compliance, Des Champs was required to hire an LSRP to investigate the source of the groundwater and undertake to remediate it.  It then filed this appeal, and R&K Associates intervened with the court’s permission.

On appeal, Des Champs contended that ISRA was enacted to alleviate the harsh requirements of its predecessor statute, the Environmental Cleanup Responsibility Act of 1983 (“ECRA”), N.J.S.A. 13K-6 et seq., by codifying a de minimis exemption which allowed such de minimis users of hazardous substances to avoid bearing just this sort of  investigation and cleanup costs.  It further argued that the DEP’s attempts to impose such obligations through administrative regulations was ultra vires, and that those regulations should be deemed invalid.

After examining the legislative history of these enactments, the court went on to determine that the DEP had acted beyond its legislatively-delegated powers in enacting the challenged regulations by “injecting into the DQE process a requirement that the governing statutes do not authorize, i.e., forcing an applicant that has only handled or stored de minimis quantities of hazardous materials to provide a certification that the property is free of contamination before its operations can be closed or title to its property transferred.”  The court pointed out that nothing in the legislative history of ISRA suggests that the statutory DQE provisions were intended to impose such onerous conditions, and in fact such conditions run counter to the stated objectives of
ISRA and SRRA to “streamline the regulatory process” and “minimize governmental involvement in certain business transactions” for private parties who have handled only de minimis amounts of hazardous substances.

Accordingly, the regulations adopted in
May 2012, N.J.A.C. 7:26B-5.9(e)(1) (slightly lessening the requirements so that a DQE applicant must certify only that the property is not contaminated “to the best of [its] knowledge”) were ultra vires and therefore constituted an invalid exercise of regulatory rulemaking because the certifying owner or operator would be ineligible for the DQE exemption if it knew of a prior owner’s discharge, even if the applicant had complied with the de minimis requirements provided by the statute.  The court found “no basis in the statute to saddle such a hypothetical innocent owner or operator with such obligations in order to obtain the DQE exemption it otherwise is entitled to under the law.”

However, the court made clear that it would not “preclude the [DEP] from pursuing appropriate enforcement action against appellant and other DQE applicants under the Spill Act or other legislatively-authorized regulations, where the facts support such enforcement action,” and further that it would not preclude anyone “from invoking their contractual or other legal rights to compel DQE applicants to investigate and to remediate industrial sites.”  The
opinion was narrowly aimed at the ultra vires nature of the DEP’s rulemaking
with regard to the DQE exemption requirements under ISRA and SRRA.

Penalties for construction in floodways

In Asdal Builders v. Dep’t of Envt’l Protection,  425 N.J. Super 564 (App. Div. 2012) cert. denied, 55 A.3d 727 (2012) the  court considered an appeal from a final decision of the New Jersey Department of Environmental Protection (“DEP”) imposing penalties related to the renovation and construction of structures located within a floodway and rejected the imposition of penalties. The project at issue involved the restoration of historic civil war-era structures located in the flood hazard area near the South Branch of the Raritan River into a zero-energy bed and breakfast inn.  The renovations maintained the
structures’ historic character while incorporating modern “green technology,”
but the DEP had determined that Asdal’s failure to obtain a stream  encroachment permit (“SEP”) prior to undertaking these renovations warranted various penalties against Asdal Builders and personal penalties against its principals, and that a retroactive SEP was inappropriate under the circumstances.  Finding that the Commissioner of the DEP had improperly rejected the prior findings of the administrative law judge assigned to the case and that its actions were grounded on improper interpretation and application of the law, the Appellate Division largely vacated the DEP’s penalty assessments.

Asdal had purchased the tract in a state of neglect and disrepair, ultimately removing “1,200 yards  of debris, 4,000 yards of wood debris, and another 100 yards of  garbage, including 14 tons of tires,” and then “engaged a farmer to re-establish the farm lands as historically operated.”  Additionally,
the pre-existing historical structures were renovated, although a garage was
razed and a new one built in a different location.  Further, Asdal sought a Stream Encroachment Jurisdiction Decision regarding the replacement of the septic system, which resulted in a determination that an SEP was not required because the drawings submitted to the  DEP showed that “[t]he proposed system will not  require the placement of any fill above the existing grades.”  Once Asdal obtained township building permits, the work began.

Responding to a complaint of “development in the floodway,” the DEP investigated and ultimately issued a series of notices of violation (“NOVs”) asserting violations of the Flood Hazard Area Control Act (“FHACA”) for the garage construction, mowing and replanting of vegetation, and constructing the septic system “nine inches higher than grade.”  The builder’s application for an after-the-fact SEP was denied, civil penalties were imposed on the corporation and its principal individually, and he was ordered to remediate the area.  Asdal’s challenge to these determinations was heard by an administrative law judge, who determined that the total fill impact resulting from the activities on the property was “insignificant,” and that the DEP’s
denial of the SEP to renovate and expand an existing use was arbitrary and
capricious.  However, the Commissioner declined to adopt these findings, instead going forward with the penalty assessments as originally determined by the DEP.

On appeal, the court first noted that the Commissioner’s determination that “responsible corporate officer” liability under the FHACA and FWPA was not available prior to recent amendments to those Acts in 2008 and 2006 respectively, at which point the definition of “person” was expanded to include “responsible corporate officers.”  Because the actions which were the basis for these penalties, and the issuance of the relevant NOVs, took place between 2003-2005, individual liability for Asdal himself was not appropriate.  Further, the Environmental Enforcement Enhancement Act (“EEEA”), which increased penalties for environmental violations and allowed for direct enforcement by the DEP without requiring court involvement, was not enacted until 2007, after which enhanced penalties were applied retroactively to Asdal’s alleged violations.  The court rejected the DEP’s position that these penalties were permissible on account of “ongoing violations,” noting that “[u]nlike ongoing pollution violations, the violations claimed here are because the renovated structures remain on the property,” and the EEEA’s enhanced penalty provisions could not be imposed for pre-existing conditions.  Additionally, because Asdal’s violations were clearly not “knowing” violations, the highest penalties were inappropriate under the circumstances.

NON-NEW JERSEY FEDERAL CASES

Pre-enforcement review

In Sackett v. Environmental Protection Agency, 132 s. Ct. 1367 (2012), the United States Supreme Court held that the factual and legal conclusions on which an EPA compliance order is based may be challenged in court pursuant to the Administrative Procedures Act, even before the EPA initiates an action to enforce that order.

The EPA had issued a compliance order to the Sacketts when they filled in part of their lot with dirt and rock in preparation for construction on the property.  The lot was located just north of Priest Lake in Idaho, but was separated from the lake by several other lots with permanent structures on them.  In the compliance order, the EPA stated that the Sacketts’ property “contains wetlands within the meaning of 33 C.F.R. §328.4(8)(b)”; was “adjacent to Priest lake within the meaning of 33 C.F.R. § 328.4(8)(c)”; and that they “discharged fill material into wetlands” on their property.  The Sacketts, however, did not believe that their property was subject to the act, and sought to challenge these conclusions by filing suit under Chapter 7 of the Administrative Procedures Act (“APA”), which allows individuals to challenge “final agency action” in the federal courts.

Whereas the trial court and the Ninth Circuit Court of Appeals had held that the APA “preclude[s] pre-enforcement judicial review of compliance orders,” in this case the Supreme Court disagreed, overturning the lower courts’ decisions, and allowing for easier access to the courts for challenges to EPA compliance orders.

In discussing whether the issuance of a compliance order constitutes “final agency action” such that the APA would provide for judicial review, the Court pointed out that it has “all of the hallmarks of APA finality” according to Supreme Court precedent.  Specifically, through the order, the EPA had
“determined” “rights or obligations,” resulting in a legal obligation to restore the property and to give the EPA access to the property and “records and documents related to” the property.  Additionally, the order “expose[d] the Sacketts to double penalties in a future enforcement proceeding,” and limited their ability to obtain a permit for their fill from the Army Corps of Engineers.

Moreover, according to the Court, the order marked “the consummation of the agency’s decisionmaking process,” as the “findings and conclusions” contained in the order were not genuinely reviewable.  Though there was a portion of the order inviting the Sacketts to “engage in informal discussion of the terms and requirements” of the order, the Court was unsatisfied with the “mere possibility that an agency might reconsider” in light of such discussions.  This did not constitute an entitlement to further agency review for the purposes of the APA’s finality requirement.

Further, the requirement under the APA that there be “no other adequate remedy in a court” was satisfied, because while judicial review was possible, the Sacketts could not initiate that process – they had to wait for EPA to engage in an enforcement action, all while incurring up to $75,000 per day in potential liability.

Finally, the Court held that the fact that Congress gave the EPA a choice between judicial proceedings and administrative action does not express an intent to allow judicial review of only the former.  The Court was untroubled
by the assertion that while compliance orders “provid[e] a means of notifying
recipients of potential violations and quickly resolving the issues through
voluntary compliance,” the EPA is “less likely to use the orders if they are
subject to judicial review.”  Specifically, “APA’s presumption of judicial review is a repudiation of the principle that efficiency of regulation conquers all,” and “[i]t is entirely consistent with this function to allow judicial review when the
recipient does not choose voluntary compliance.”

CERCLA – contracts

In United States v. ARG Corp., 2011 U.S. Dist. LEXIS 86423, 41 ELR 20271 (N.D. Ind. Aug. 4, 2011), the court addressed how contractual language influences CERCLA liability for environmental cleanup costs.

The City of South Bend, Indiana, had purchased a tract of land from ARG Corporation, but days after the closing determined that there may have been hazardous substances on the property posing a danger to public health and safety.  When the City reported this to the EPA, an investigation ensued and
ultimately ARG was ordered to clean up the site.  When ARG refused, the government went forward with a $841,000 cleanup project to remove the hazardous substances.  Ultimately the government filed suit under
CERCLA seeking reimbursement from ARG.  Contending that it was not responsible for such costs, but that South Bend had assumed responsibility for any such cleanup, ARG filed a third-party complaint against the City.

The court began its analysis by examining the language of the contract of sale between the parties.  That contract stated that “the seller shall remain solely financially responsible for the remediation activities arising from the seller’s ownership, use or operation of the property prior to the closing date,” and “the purchaser shall be solely financially responsible for the remediation activities arising from the purchaser’s ownership, use or operation of the property after the closing date.”  The court found this to unambiguously state
that ARG is solely responsible for remediation occasioned by its use of the
property.  Further, contractual language that South Bend agreed “not to execute against any of [ARG’s] assets to satisfy [ARG’s] financial responsibilities for remediation of pre-closing environmental damage” was interpreted to mean only that if South Bend believed ARG to be responsible for a cleanup, it would only seek recovery from ARG’s insurance policies – not that South Bend agreed to indemnify ARG for such costs.  Evidence of pre-closing negotiations which allegedly demonstrated that South Bend had agreed to assume responsibility for any cleanup were irrelevant, as the contract was unambiguous on its face.

ARG’s argument that hazardous substances were “disposed of” during South Bend’s ownership was held to be without merit.  The court noted that CERCLA holds liable “any person who at the time of disposal of any hazardous substances owned or operated any facility at which such hazardous substances were disposed of,” and that “disposal” is defined for purposes of that Act as “discharge, deposit, injection, dumping, spilling, leaking or placing” of hazardous waste into the land or water.  The remediation
process by which contaminants were removed from the ground did not constitute “disposal” under CERCLA.

Summing up, the court held that “just because the clean-up occurred when South Bend owned the property does not mean the hazardous substances arose from South Bend’s ownership, use or operation of the property.”

Global Warming – Nuisance, Clean Air Act

In American Electrical Power Co. v. Connecticut, 131 S.Ct. 2527 (2012) the United States Supreme Court rejected plaintiffs public nuisance claims based on federal common law for the nuisance of global warming. In this case, eight states and the City of New York, as well as three nonprofit land trusts, brought suit against four carbon-dioxide emitters based on public nuisance under federal common law.  The plaintiffs alleged that by contributing to global warming, the defendants emissions created a “substantial and unreasonable interference with public rights” in violation of federal common law of interstate nuisance and/or state tort law.
They sought injunctive relief in the form of an immediate cap on carbon
dioxide emissions and a gradual lowering of that cap over time.

The Court began its analysis by noting that the Clean Air Act (“CAA”)authorizes federal regulation of carbon dioxide, among other greenhouse gases.  The EPA subsequently issued rules in collaboration with the Department of Transportation regulating emissions from various forms of vehicles.  At the same time, it began phasing in requirements that certain greenhouse gas emitting facilities utilize the “best available control technology” and began rulemaking as to emissions from fossil fuel fired power plants.

It was ultimately held that “the Clean Air Act and the EPA actions it authorizes displace any federal common law right to seek abatement of carbon-dioxide emissions from fossil-fuel fired power plants.”  Despite the fact that EPA had not yet implemented any regulation as to the type of emissions involved in this case, the Court pointed out that “[e]ach standard of performance EPA sets must take into account the cost of achieving emissions reduction and any nonair quality health and environmental impact and energy requirements,” and the CAA “entrusts such complex balancing to EPA in the first instance.”

Furthermore, “[i]t is altogether fitting that Congress designated an expert agency . . . as best suited to serve as primary regulator of greenhouse gas emissions.  The expert agency is surely better equipped to do the job than individual district judges, issuing ad hoc, case-by-case injunctions.”  Such a scheme would be unmanageable and unjust, but more importantly it “cannot be reconciled with the decisionmaking scheme Congress enacted.

DiFrancesco, Bateman, Coley, Yospin, Kunzman, Davis, Lehrer &
Flaum, PC (
www.dbnjlaw.com ) is a full service law firm in New Jersey which provides a broad range of legal services, including the representation of clients in environmental and defense of toxic
exposure matters. For additional information about the matters in this bulletin or in the firm’s environmental practice, please contact
Steven A. Kunzman, Esq. who heads our Environmental and Latent Injury Litigation Department.

The information contained in this blog is intended solely for
informational purposes; it is a advertising publication of DiFrancesco, Bateman, Coley, Yospin, Kunzman, Davis, Lehrer & Flaum P.C.This publication is intended to alert recipients of developments in the law and is not intended to provide legal counsel, advice or opinion on any specific facts or circumstances. The contents are intended as general information only. You are
urged to consult a member of this firm or your own attorney concerning your particular situation and any specific legal questions you might have.

 

SUMMARY OF DEVELOPMENTS IN CERCLA AND NJ SPILL ACT: 2011

SteveK January 16th, 2012

This is a summary of some of the significant decisions of 2011 in CERCLA and N.J Spill Act litigation. ( Some of the decisions were previously reviewed in this blog.)

CERCLA

Arranger and Operator Liability:

In Nu-West Mining Inc. v. United States,786 F.Supp 2d 1082 (D.C. Idaho, 2011) the Federal District Court held that the U.S. Government was liable as both an arranger and operator under CERCLA at a site in the Caribou-Targhee National Forest that had been leased to a mining company. The court concluded that the permitting, inspection and oversight functions at four mines were sufficient involvement and control of the operations by the U.S. to impose liability.

The Court reviewed the law on arranger and operator liability.

A party is considered an arranger under CERCLA according to Burlington Northern & Santa Fe Railway Co. v. United States (BNSF), 129 S. Ct. 1870 (2009) when it “takes intentional steps to dispose of a hazardous substance.” Id. at 1879. Mere knowledge that spills would occur did not amount to “intent.” Further, the Court held that the analysis “requires a fact-intensive inquiry that looks beyond the parties’ characterization of the transaction as a ‘disposal’ or ‘sale’ and seeks to discern whether the arrangement was one Congress intended to fall within the scope of CERCLA’s strict-liability provisions.” Id.

For a party to be considered an operator of a facility under CERCLA  it must “manage, direct, or conduct operations specifically related to pollution, that is, operations having to do with the leakage or disposal of hazardous waste,  or decision about compliance with environmental regulations.” United States v. Bestfoods 524 U.S. 51, 66-67 (1998). If a party had the authority to control the cause of the contamination at the time of disposal, and actually exercised that control, then it is considered an operator. Id., citing, Kaiser Aluminum & Chem. Co. v. Catellus Dev. Corp., 976 F. 2d 1338, 1341 (9th Cir. 1992).

The Government began leasing mineral rights in the National Forest to various mining companies.  In accordance with the leases the Government inspected the mines to monitor the environmental conditions, properly disposing of mining waste, and to confirm royalty payments. The lease also required the lessees to “[prospect] diligently and to meet certain ore production requirements, and to pay a royalty fee.”  The Government also issued Special Use Permits so that rock waste dumps could be constructed on National Forest Lands adjacent to the leased lands. The Government also required the lessees to obtain “approval of plans for mining, waste disposal, and reclamation.”

The mine sites were determined to be contaminated with selenium, a naturally occurring chemical element that is found in a rock layer between phosphate ore zones. The mines were operated from 1960 until the 1990s. When the contamination was discovered in the 1990s, the lessee, Nu-West entered into Administrative Orders with the Government to remediate the sites. Nu-West claims to have spent over $10 million dollars and seeks to recoup those costs. In a motion for partial summary judgment Nu-West argued that the Government was an owner, arranger and operator under CERCLA. The motion did not address or resolve any defense to which the Government may be entitled, or any issue of damages.

The Court found that the Government not only owned the source of the contamination, it also had the authority to control the disposal of mining waste at the dump sites. The Court specifically noted that the lease provided that “no mining waste disposal could occur without its approval.” Further, the Court found that the Government exercised control over the disposal, and “showed its intent that disposal take place” by directing how the dumps should be covered.  The Court rejected the Government’s argument that it was acting in purely in a regulatory capacity, finding that its actions constituted a waiver of its sovereign immunity.” Citing, U.S. v. Shell Co. 294 F. 3d 1045, 1052-54 (9th Cir. 2002.); 42 U.S.C. §9620(a)(1) Accordingly, the Government was held as an arranger.

The Court also found there to be operator liability because the Government managed design and location of the dumps. In addition, the Government regularly inspected the dumps to ensure compliance with the mining plans and waste disposal guidelines.

In a subsequent motion reported at 2011 U.S. Dist. LEXIS 70854, the Court denied Nu-West’s motion for summary judgment on the Government’s counterclaim, seeking a ruling that the Government would not be entitled to legal fees. The Court was unable to conclude what costs may be “enforcement costs”  which a government may recover, as opposed to “necessary cost of response” which is what a private party may recover.

This case clarifies some of the issues on Governmental liability for actions at CERCLA sites, including that the Government can be liable when it is controlling the operations for its own benefit, not just in the use of its police power or in its sovereign capacity.

 

Owner Liability

In Los Angeles v. San Pedro Boat Works, 635 F. 3d 440 (9th Cir. 2011,) the Court held that the holder of a “revocable permit”  for a ship-berth in Los Angeles harbor had a mere possessory interest which did not arise to an ownership interest under CERCLA.

In this case, contamination arose from ship repairing activities that took place in Los Angeles Harbor. Pacific American purchased a revocable permit from the Harbor Commission in 1969 and held the permit for approximately 10 months. San Pedro Boat Works, a wholly owned subsidiary of Pacific American, was assigned the permit from Pacific American in 1970. San Pedro Boat Works was subsequently sold. Pacific American was acquired by BCI-Coca-Cola Bottling Company of Los Angeles in 1993.

Contamination was discovered in 1995 at the berth. The City cleaned up the contamination and commenced suit against San Pedro and Coca-Cola to recover the costs. San Pedro filed for bankruptcy shortly after suit was filed.

In deciding in favor of Coca-Cola, the Court first looked to CERCLA, but concluded that the definition of owner was tautological: an owner is “any person owning a facility.” 42 U.S.C. §9601(20)(A)(ii). The Court elected to rely upon the common law of the jurisdiction which distinguished title ownership from possessory interest.  It concluded that the “holder of a permit for a specific use of real property is not the owner of that real property.”  The Court, therefore, concluded that the permit holder was not the owner under CERCLA.  The Court rejected the test applied by the Second Circuit in Commander Oil Corp. v Barlo Equip, Co. 215 F. 3d 321 (2nd Cir. 2000) for de facto ownership: 1) whether the lease is for an extensive term and admits of no rights in the owner/lessor to determine how the property is used; 2) whether the lease cannot be terminated by the owner before it expires; 3) whether the leasee has the right to sublet all or some of the property without notifying the owner; 4) whether the lessee is responsible for payment of all taxes, assessments, insurance an operation and maintenance costs; and 5) whether the lessee is responsible for making all structural repairs. Id. at 330-331.

As a result there is a conflict as to what test is to be applied in the analysis of what constitutes an owner where the concepts of control over the operations and activities are at issue. The Ninth Circuit has focused on the common law, and has held this way both for the holder of an easement, see, Long Beach Unified School Distric v. Dorothy B. Godwin Cal. Living Trust, 32 F 2d 1364 (9th Cir. 1994), and now for a permit. Although the 2nd Circuit test was determined to create a “nebulous and flexible analytic framework” by the 9th Circuit, the Circuits are split on what test is to be applied.  It is unclear how the actual results would vary.

Arranger Liability

In Team Enterprises LLC v. Western Investment Real Estate Trust 2011 U.S.  App LEXIS 19881, the 9th Circuit concluded that the manufacturer of a dry cleaning machine was not liable for contribution to environmental cleanup costs under CERCLA.  Thea Plaintiff, a dry cleaner, used dry cleaning equipment manufactured by R.R. Street & Co. (Street) for their operations. The PCE-laden residue from the operations was deposited into a bucket for reuse; however, some was poured down the drain and leaked into the soil.

The Court analyzed whether a party can be considered an arranger under CERCLA where the equipment was sold for legitimate business purposes and was not created with the intent and purpose of disposing of hazardous waste. The Court took into account the requirement under BNSF that a party “must take intentional steps to dispose of a hazardous substance” to be considered an arranger. Supra, 129 S. Ct at 1879.

The Court also rejected the argument that Street had “exercised control over the disposal process” by designing the equipment that required the dry cleaner to dispose of the wastewater into the sewer.  The Court concluded that the instructions that suggested that the waste be poured into a bucket (which, according to the Plaintiffs, left no alternative but for the operator to pour that waste into the drain) did not present anything more than a suggestion or “recommendation;” there was no directive or other manner of control. Even the argument that Street knew that was how dry cleaners handled the residual waste was unavailing.  The Court affirmed the decision from the lower court that the facts do not support the requisite intent to dispose of waste as set forth by the Supreme Court in BNSF.

Arranger and Divisibility

The Lower Fox River cleanup litigation continues to provide interesting issues and analysis of a variety of issues under CERCLA.  There were a number of decisions in the case in 2011, the most significant one being Appleton Papers, Inc. et. al. v. George Whiting Paper Co., 776 F. Supp 2d 857 (E.D. Wis. 2011).

The Court had previously held that the Plaintiffs were not entitled to contribution for the expenses they had and will incur for cleanup costs “because they knowingly took that risk that the product that they mobilized [PCBs] would have long-lasting environmental consequences.” Id. at 859. Defendants sought to have the Court require that Appleton reimburse them for the costs they have incurred for their investigation and remediation at the site.  The Court conducted a thorough analysis and crafted a decision that placed most of the responsibility on the Plaintiff, except with regard to Operable Unit -1 (OU-1) which was upstream.

First, the Court addressed arguments that the Plaintiff should be liable as a successor to an arranger for the disposal of pollutants in OU-1. The predecessor, Appleton Coated Paper Company (ACPC) made carbon paper which utilized PCBs. ACPC sold waste from their processes through a broker that was used by other companies for making paper. The waste paper (known as “broke”) was recycled by the acquiring companies which resulted in PCBs being discharged into the Fox River Site.  Defendants argue that in this manner, ACPC arranged to dispose of a hazardous substance, thus making them liable for contamination at OU-1, even though their own discharges did not wind up in OU-1.  The Court conducted a thorough analysis of arranger liability under BNSF and concluded that although they did “enter into a transaction for the sole purpose of discarding a used and no longer useful hazardous substance;” however, there was insufficient evidence to support the conclusion that ACPC had the intent to dispose of the waste along with “the particular knowledge that non-trivial amounts of the broke waste product would inevitably end up in the river.” Id. at 864. The Court concluded that there were questions of fact, but indicated that it was unlikely that there would be sufficient evidence to support such a claim.

The Court also rejected that argument that all the operable units at the site were intertwined, and thus, Plaintiff could not obtain contribution from the Defendants (and therefore they were entitled to reimbursement) for costs for OU-1. The Court, however, confirmed a prior ruling that the costs for OU-2 through 5 fall squarely and completely on the Plaintiffs on the basis of fault, and that fault was such an overriding factor that is outweighed by any basis to impose equitable shares on the Defendants.  The Court then went on the wrestle with particular costs, including deciding that the costs that have been incurred were not outside the statutory limitations periods.

Subsequent Work Causing Release

In Saline River Properties LLC v. Johnson Controls, 2011 U.S. Dist. LEXIS 119516 the U.S. District Court for the Eastern District of Michigan, addressed whether a developer could be liable under CERCLA for conducting  development activities that may have moved contamination on the site and required additional cleanup.  Johnson Controls had owned property that it was remediating under a state issued administrative order.  Plaintiff became the operator of the property and at some point destroyed the building slab which Johnson alleges resulted in the migration of contaminants that would not have otherwise occurred.  The Court concluded that although passive migration would not have resulted in liability, there were questions of fact as to whether this action caused a release.

Citizens’ Suits

In Pakootas v. Teck Cominco (Pakootas II), 2011 U.S. App. LEXIS 10931 the 9th Circuit ruled that environmental groups, Indian tribes and other non-EPA parties may not bring a citizens’ suit to enforce the penalty provisions of CERCLA.

Pakootas II is part of the continuing dispute concerning the pollution of the Columbia River. The pollution originated from mining operations in British Columbia. Teck Cominco Metals, a Canadian mining company operated a smelter north of the U.S. –Canadian border which generated and disposed of slag into the Columbia River. Negotiations between the EPA and Teck Cominco American, Inc. faltered on issues of Canadian sovereignty and jurisdiction. The EPA eventually issued a unilateral administrative order (Order) directing Teck to investigate the nature and extent of contamination in the Upper Columbia River basin, and to evaluate remedial options.  Teck did not comply and the EPA took no enforcement actions, nor did it seek penalties.

Plaintiffs, later joined by the Confederated Tribes of the Colville Reservation and the State of Washington, pursued a citizens’ suit seeking:  (1) a declaration that Teck had violated the Order; (2) injunctive relief compelling Teck to comply with the Order; (3) penalties for non-compliance with the Order;  and(4) attorney fees and costs.

After Teck’s motion to dismiss the case based upon the argument that EPA could not apply CERCLA extra-territorially was denied, Teck and the EPA entered into a “contractual agreement” to address the contamination at the site.  As part of the agreement, the EPA agreed to a covenant not to sue Teck for penalties or injunctive relief relating to non-compliance with the Order, subject to its satisfactory performance of its obligations under the agreement.

Plaintiffs amended their complaint and dismissed the claims for injunctive and declaratory relief, but continued to assert the claims for penalties for non-compliance with the Order. The 9th Circuit affirmed the dismissal of the suit concluding that the penalty provisions are a “hammer” to be wielded exclusively by the EPA to compel compliance. Further, the Court aptly noted that if Teck were compelled to pay the penalties to Plaintiffs prior to the agreed upon remediation,” it might find it economically advantageous to walk away from the further cleanup efforts…” which would have a perverse result, and would not further the intent to compel site remediation.

 

Section 113 & Private Nuisance Claims

On August 13, 2011, the Federal District Court for the District of New Jersey continued to clarify the limits of Section 113 claims under CERCLA and  also addressed common law claims of a subsequent property owner in Queens West Development Corporation v. Honeywell International, Inc. 2011 U.S. Dist. LEXIS 91795. Plaintiff acquired property formerly operated by Warren Chemical Works, which was subsequently acquired by Honeywell. The property was contaminated from discharges of substantial amounts of creosote, coal tar, and related substances. The property was to be redeveloped by plaintiff for residential, commercial and recreational uses. Plaintiff claimed to have incurred over $16 million in investigation and remediation costs, and anticipated total response costs that would be equal to or exceed $20 million. Defendant moved for dismissal of various counts of the complaint including claims in Count Two of the Complaint, under Section 113 of CERCLA, claims in Count Three for common law private nuisance, and claims in Count Four for restitution.  In deciding the case, the Court addressed the intersection between claims under Section 107 of CERCLA and Section 113. The Court noted that the case presented a unique issue: “whether a party that voluntarily undertakes a cleanup action can maintain a claim for contribution under § 113(f)(3)(B), when it has simultaneously asserted a claim for cost recovery under § 107(a).” The Court noted that courts have explained that Section 107 “authorizes the United States, a state, or `any other person’ to seek reimbursement for all removal or remedial costs associated with the hazardous materials on the property, provided that those actions are consistent with the National Contingency Plan,” and that the United States Supreme Court held in Atlantic Research that the “plain language” of § 107 “authorizes cost-recovery action by any private party, including PRPs.” As a result, a private party is not required to establish its own liability in order to assert a claim under  Section 107. Section 113(f)(3)(B), however, allows the assertion of a right of contribution only “to PRPs that have settled their CERCLA liability with a [S]tate or the United States through either an administrative or judicially approved settlement.” Since Plaintiff had voluntarily incurred the response costs, is not a PRP, and did not enter into an approved settlement or resolved all their liability to the U.S. or the State of New York, they could not maintain the  Section 113 claim. Thus, the Court dismissed the  Section 113 claim contained in the Second Count.

The Court next addressed the claims for private nuisance. As the proceeding was in New Jersey, but involved New York property, the Court considered the law of private nuisance in both jurisdictions. The Court concluded that the law was the same, and that although a private nuisance “consists of an interference with one’s interest in the private use and enjoyment of land” it only applies to interference with use of adjoining land, not to subsequent owners of the same property.

Finally, the Court refused to dismiss the restitution claim. Defendants argued that it should be dismissed since it is preempted by CERCLA. The Court refused to dismiss the claim, however, since it remained an alternative common law claim that would survive if the Plaintiff fails to prove the claim under Section 107 of CERCLA.

Case to Watch: Sackett

Sackett v. EPA is a case that is scheduled for argument before the U.S. Supreme Court this term. Although it is not a CERCLA case, it may have a significant impact on enforcement of federal environmental statutes.  The primary issue presented by Sackett is whether pre-enforcement review is available for EPA administrative orders. Pre-enforcement review refers to the ability of the recipient of such an order to obtain judicial review of the order without having to wait to be sued by the EPA. This is not applicable to CERCLA since CERCLA has an express provision prohibiting pre-enforcement review. 42 U.S.C. §9613(h).

The Court will consider whether a bar to pre-enforcement review can be implied into the Clean Water Act (CWA), as has been argued by the EPA, and whether such an implied ban would violate the due process clause of the U.S. Constitution.

In Sackett the plaintiffs had filled a wetland area on their 0.63 acre parcel without a CWA permit. The EPA issued an administrative compliance order requiring that the fill be removed and that the wetland be restored.  The Sacketts petitioned the EPA for a hearing to challenge the wetland determination. After the EPA refused, the Sacketts filed suit.  The District Court dismissed the suit and the Sacketts appealed to the 9th Circuit.  Before the 9th Circuit they argued (1) that the Administrative Procedures Act (APA) allows pre-enforcement review of CWA compliance orders; and (2) that pre-enforcement review is required by due process.

The Circuit Court rejected both arguments. It rejected the argument under the APA essentially finding that pre-enforcement review is not provided for in the CWA and that the presumption in favor of judicial review is overcome where “congressional intent to preclude judicial review is fairly discernible in the statutory scheme.” Sackett v. EPA 622 F. 3d 1139,1143 (9th Cir, 2010). The Court concluded that pre-enforcement review would frustrate the goal of addressing environmental problems quickly and would negate the EPA’s statutorily created choice between filing a suit or acting unilaterally through an administrative order.

The 9th Circuit rejected the due process arguments finding that it had been satisfied because: (1) judicial review was available once the EPA brings an enforcement action; (2) the Sacketts could have sought to obtain a §404 permit to fill the property, which would be reviewable by the district court if denied; and (3) the court, not the EPA, can impose penalties under the CWA based upon a range of factors. [1] The decision could have far reaching implications, even effecting CERCLA if the Supreme Court reverses on the basis of due process. [2]

 

NEW JERSEY SPILL ACT

Primary Jurisdiction

In Magic Petroleum, Inc. v. Exxon Mobil, 2011 N.J. Super. Unpub. LEXIS 2021, the New Jersey Appellate Division dismissed, without prejudice, Magic’s claim for contribution of remedial costs against Exxon due to NJDEP’s primary jurisdiction of the remedial investigation at the plaintiff’s property. Plaintiff had been the subject of an administrative consent order (ACO) to investigate and remediate contamination at its property resulting from leaking underground storage tanks.  Plaintiff contended that the majority of the contamination came from the neighboring Exxon station and refused to comply with its obligations under the ACO until the NJDEP required Exxon to participate in the investigation. Magic litigated its obligations under the ACO through administrative proceedings, and was required to follow the order. Magic, however,  continued to refuse to conduct the investigation, insisting that the investigation should be imposed upon and shared by Exxon. The NJDEP eventually took over the investigation of the plaintiff’s property. Magic then commenced a contribution action against Exxon.

Exxon filed a motion to stay or dismiss the proceedings, without prejudice, pending the NJDEP’s investigation and remediation of the Magic property, arguing that the NJDEP’s efforts must precede any decision by the court. The trial judge dismissed the case, deferring to the NJDEP’s primary jurisdiction. The Appellate Division affirmed.  The Appellate Court noted that under the doctrine of “primary jurisdiction” a court may defer to an agency where the resolution of an issue is within the special competence of the agency. The court further noted that private contribution rights under the Spill Act require the court to allocate responsibility for remediation costs, but that the initial determination of whether a party is responsible can be decided by the NJDEP, and that “only the DEP can define the contaminants, determine the extent of the discharge, identify the authorized forms of investigative testing, and permissive methodology of cleanup.” Furthermore, “to be entitled to reimbursement and contribution under the Spill Act, a party must obtain written approval under from the DEP of the investigation and proposed remedial action.”  Accordingly, the court concluded that these decisions were within the scope of the special expertise of the DEP and should be determined prior to the case being able to proceed.

This decision demonstrates that a responsible party under the Spill Act that does not conduct investigation and remediation, but allows it to be done by the State, does so at its peril. To do so may have a significant impact in the party’s ability to pursue a contribution claim against other responsible parties, as it allows the NJDEP to determine and define the scope of the investigation, remediation, and possibly to potentially influence any future contribution claim or allocation. It is interesting to consider the effect of the Site Remediation Reform Act (SRRA) on the statements by the court that the DEP will define the contaminants, the extent of the discharge, the forms of investigation and the method of cleanup. Under the SRRA these determinations can be made by a Licensed Site Remediation Professional (LSRP), in accordance with the regulations for site investigation and remediation, referred to the Tech. Regs.  Accordingly, it may not be that the DEP has to make these decisions. This points, again, to the importance of the party seeking contribution to address and control the response in order to be able to develop the information, and assert and control the contribution claim.

Nexus

In NJDEP v. Ofra Dimant, et.al 418 N.J. Super 530 (App. Div. 2011), cert. granted, 208 N.J. 381 (2011), the New Jersey Appellate Division recently confirmed that liability under the Spill Act, requires a connection between the discharge of a contaminant and the contamination of the environment of that contaminant that was caused by the discharge. In that case, the defendants included succession of owners and operators of a dry cleaning establishment. The contamination in the groundwater included the well-known dry cleaning chemical, PCE, as well as the byproducts of its degradation: TCE and DCE.  There was evidence that the PCE was related to the dry cleaning operations. All but one of the direct defendants settled with the State.  The remaining defendant went to trial. The trial judge found that although there were discharges or releases of PCE during the stewardship of the remaining defendant, there was no proof that those discharges went through the asphalt and contaminated the environment.  Since there was no nexus between the discharge and the remediation, the claims against the defendant were dismissed. The State also sought leave to amend the complaint to add certain other prior operators. The denial of that motion by the trial judge was affirmed as being made too late in the case; in fact, it was made near the end of the trial.  This case affirms the need for the State or any plaintiff in a Spill Act case to demonstrate a nexus; and further reaffirms that there is no liability for passive migration of contaminants during the ownership of property.

NRD Common Law Claims – Limitations of Actions

In New Jersey Dep’t of Env. Protection v. Exxon Mobil Corp, 405 N.J. Super 395 (App. Div. 2011) the court held that the State’s common law strict liability claims for NRDs were not barred by the general ten-year statute of limitations applicable to actions commenced by the State. N.J.S.A. 2A:14-1.2. The court, reversing the trial court, held that an exception to the ten-year statute, specific to environmental laws, known as the Extension Statute, N.J.S.A. 58:10B-17.1, applies not only to statutory environmental laws, but also to common law causes of action implementing environmental programs.
The Extension Statute provides:

b. (1) Except where a limitations provision expressly and specifically applies to actions commenced by the State or where a longer limitations period would otherwise apply, and subject to any statutory provisions or common law rules extending limitations periods, any civil action concerning the payment of compensation for damage to, or loss of, natural resources due to the discharge of a hazardous substance, commenced by the State pursuant to the State’s environmental laws, shall be commenced within five years and six months next after the cause of action shall have accrued.

Exxon argued that the Extension Statute’s use of the term “environmental laws” after a listing of 9 prior statutes,  limited the extension to statutory causes of action. The Appellate Division, however, looked to legislative history and concluded that the legislature intended to expand the scope of the authority of the DEP, not to limit it. As a result, NJDEP has the ability to pursue common law causes of action, along with the strict liability provision of Spill Act, in matters involving NRDs; neither of which will be constrained by the general ten-year statute. This decision may be important as common law remedies and damages may be broader and may permit the State to seek to present their case before a jury as there is some question whether there is a right to a jury trial under the Spill Act.

 

In a separate decision, the Appellate Court also ruled on the State’s claim for an interlocutory payment by Exxon Mobil for natural resource damage assessment costs of approximately $1 million.  The costs represent the invoices of five experts that prepared reports for DEP regarding the claimed natural resource damages under the Spill Act. The Court affirmed the trial court’s denial of the interim payment since there is a significant dispute as to the reasonableness of the costs and whether they are duplicative of defendant’s efforts. The panel concluded that the award of such costs is best reserved until resolution of the factual issues at trial.

NRD : Use of Resource Equivalency Analsyis (REA)

In  NJDEP v. Union Carbide, (Middlesex County, MID-L-5632-07, March 29, 2011) the trial Court rejected for the second time the State’s effort to employ a resource equivalency analysis (REA) or habitat equivalency analysis (HEA) to place a value on the loss of use of groundwater as a natural resource. The trial court had previously rejected REA in NJDEP v. Essex Chemical, (Middlesex County, Docket No.: MID-L-5685-07, July, 2010). The trial court concluded that the expert had not conducted a proper analysis of the particular services that were claimed to have been lost by the public due to the contamination, other than the remedial costs which were being conducted by the defendant. The court also ruled that there was no basis to compel the defendants to cleanup more expeditiously since the entire remedial endeavor had been with the approval and oversight of the NDJEP, albeit a different arm than the Office of Natural Resources and Recovery (ONRR). Finally, the court rejected the State’s nuisance claim since the plaintiff’s had not satisfied their burden of showing that the contamination of the groundwater interfered with the public’s use or enjoyment of the resource, further noting that the groundwater in question was never available to the public since it was below private property; therefore. “Plaintiffs have not shown how the public has been deprived of anything.” [Slip. Op. p. 13]


[1] Similar issues were addressed by the N.J. Supreme Court in In the Matter of the Directive to Kimber Peteroleum, 110 N.J. 69 (1988)

[2] It may be questionable whether the Court would go so far, considering it refused to consider a similar challenge regarding CERCLA administrative orders in General Electric v. Jackson, 595 F. Supp. 2d 8 (D.D.C. 2009).

DiFrancesco, Bateman, Coley, Yospin, Kunzman, Davis, Lehrer & Flaum, PC (www.dbnjlaw.com ) is a full service law firm in New Jersey which provides a broad range of legal services, including the representation of clients in environmental and defense of toxic exposure matters. For additional information about the matters in this bulletin or in the firm’s environmental practice, please contactSteven A. Kunzman, Esq. who heads our Environmental and Latent Injury Litigation Department.

The information contained in this blog is intended solely for informational purposes; it is a advertising publication of DiFrancesco, Bateman, Coley, Yospin, Kunzman, Davis, Lehrer & Flaum P.C.This publication is intended to alert recipients of developments in the law and is not intended to provide legal counsel, advice or opinion on any specific facts or circumstances. The contents are intended as general information only. You are urged to consult a member of this firm or your own attorney concerning your particular situation and any specific legal questions you might have.


Steven Kunzman to Co-Chair Seminar on Groundwater Contamination

SteveK August 15th, 2011

Steve Kunzman, partner in the firm, will be a co-chair of a comprehensive conference:

Groundwater Contamination and Vapor Intrusion Cases

The seminar, which will be put on by Law Seminars International, will take place at the Sheraton Newark Airport Hotel on September 15 and 16.

For more information and to register go to: http://www.lawseminars.com/seminars/11GWATNJ.php

The speakers include noted attorneys, remediation consultants and and other noted experts in the field. The seminar is co-chaired by Ira Gottlieb of McCarter & English. Steven and Ira will also be speaking on insurance coverage issues relating to groundwater claims.

DOT held liable as an “arranger” under CERCLA for design and management of stormwater system.

SteveK November 10th, 2010

In United States v. Washington State Department of Transportation, the U.S. District Court in Washington recently held the Washington State Department of Transportation (WSDOT) liable as an “arranger” of the discharge of hazardous materials under CERCLA.  The case involved a portion of the Commencement Bay-Nearshore Tideflats Superfund Site in Tacoma, Washington, known as the Thea Foss and Wheeler Osgood Waterways.  The U.S. contended that the WSDOT was responsible for contributing to the contamination at the site as an owner and operator of the highways and drainage structures, and as an arranger for the design and construction of the drainage structures that allowed contaminants to be discharged into the waterways.  The issues of the responsibilities and liabilities of the WSDOT were considered by the court in a series of motions decided from June through September.

Ultimately, the court concluded that the WSDOT designed the stormwater system with the specific purpose to discharge the highway runoff into the environment, knowing that the runoff contained hazardous substances.  The court further noted that the WSDOT could have designed the system to redirect, contain or treat the runoff, which would have avoided the discharges.

The WSDOT had also asserted that the discharge was a “federally permitted release,” and thus was exempt from CERCLA liability under ’107(j) as the drainage system was operated under a National Pollution Discharge Elimination System (NPDES) permit. The U.S. countered that there limitations of the permit had been exceeded and there were numerous unpermitted releases.  The court concluded that there was insufficient evidence to determine the scope of the permits and whether the resulting injury from any impermissible discharges was divisible.

This decision provides an expansive view of the concept of arranger liability based upon the Supreme Court decision in Burlington Northern, whereas other courts have been taking a more narrow view.  In most other matters, courts conduct a detailed analysis of the facts of the intent to discharge; whereas, in this decision, the factual analysis is somewhat limited.

DiFrancesco, Bateman, Coley, Yospin, Kunzman, Davis & Lehrer, PC (www.dbnjlaw.com ) is a full service law firm in New Jersey which provides a broad range of legal services, including the representation of clients in environmental and defense of toxic exposure matters. For additional information about the matters in this bulletin or in the firm’s environmental practice, please contactSteven A. Kunzman, Esq. who heads our Environmental and Latent Injury Litigation Department

EPA releases Draft Clean Water Strategy and seeks further comment.

SteveK August 20th, 2010

On August 20, 2010, the EPA posted its Draft Clean Water Strategy for review and comment. The Draft resulted from the Coming Together for Clean Water Conference which was hosted by EPA Administrator Lisa P. Jackson this past April. The Draft identifies the challenges to continuing the efforts launched by the 1972 passage of the Clean Water Act. While acknowledging the significant progress that has occurred since then, the community involved recognizes that much more needs to be done to revitalize the resources. The Draft further presents the significant economic benefits which can be realized from having clean water and in taking the actions and building the infrastructure to achieve the goals. The Draft demonstrates the continued viewpoint that environmental protection is not a drain on economic growth but a significant component of our development.

A copy of the Draft, information on the April conference, and information on providing comments on the draft, can be found on the EPA website at: http://blog.epa.gov/waterforum/ Comments will be accepted until September 17, 2010.

DiFrancesco, Bateman, Coley, Yospin, Kunzman, Davis & Lehrer, PC (www.dbnjlaw.com ) is a full service law firm in New Jersey which provides a broad range of legal services, including the representation of clients in environmental and defense of toxic exposure matters. For additional information about the matters in this bulletin or in the firm’s environmental practice, please contactSteven A. Kunzman, Esq. who heads our Environmental and Latent Injury Litigation Department