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Allocation of Contribution in Pollution Cases – Part I

 

For nearly three decades, parties responsible for cleanup of polluted sites have struggled to develop a fair and technically defensible way to allocate liability and damages among themselves. In a typical multi-party site involving litigation regarding cost recovery under CERCLA, potentially responsible parties (PRPs) each hire experts to evaluate the available technical data and opine on the portion of pollution that was caused by each contributor. The methodologies employed by these experts can vary significantly and often times represent a best-guess in the absence of adequate data or technical analysis. The results may be viewed by other PRPs as merely a position statement by the expert, intended to benefit only the clients of that expert, rather than a reasonable and supportable evaluation of the available data and site information. The courts have historically provided little help in establishing universally acceptable and reasonable guidelines for allocation of liability and damages among parties. As for Federal or state environmental regulators, they have relied on the joint and several liability approach to push aside the issue of allocation altogether and let the PRPs battle it out in the courts.

In 2009, two court decisions provided guidance regarding allocation that may have far-reaching impacts on the methods for allocating liability and damages. First, In March 2009, in an insurance coverage case, the California Supreme Court issued its ruling regarding the State of California v. Allstate Insurance Co. matter, referred to as Stringfellow I in this article. Among several issues addressed in that decision, the approach to “divisibility” is likely to have significant implications on how parties evaluate their potential allocated shares of liability and damages. As with many environmental issues, both legal and technical analyses come into play. In addition, the terminology and definitions presented in Stringfellow 1 give rise to additional legal and technical considerations. It is likely that the technical implications of the Stringfellow 1 terminology and definitions will become more fully understood and developed by precedent in the near-term.

The second ruling came in May of 2009 from the United States Supreme Court in the Burlington Northern & Santa Fe Railway et al. v. United Stated et al. (BNSF Case). In that ruling, the Supreme Court held that the District Court’s analysis of the divisibility of harm and the method of apportionment were reasonable and acceptable. The District Court had apportioned one PRP’s share of the site cleanup liability based on three factors. The apportionment calculation used by the District Court included three variables: 1) the percentage of the total area of the facility owned by the RP, 2) the duration of business operations divided by the PRP’s lease term, and 3) the number of chemicals that had been spilled on the PRP’s subject property. The Supreme Court upholding this crude allocation method has raised several key issues. From a technical and engineering perspective, perhaps the most significant issue is that the ruling sets the stage for courts to begin using a broad range of allocation methods. These could range from simple approaches that could include subjective criteria, to science-based approaches that use objective criteria to converge on a more supportable result. This circumstance will have a significant impact on the range of liability and damage percentages that are presented to PRPs for settlement consideration, or that may be imposed by judgment.

The technical evaluation of contribution to an environmental pollution situation is based on Environmental Forensics (see additional article in this newsletter), and Engineering Cost Analysis. Environmental Forensics addresses the sources and mechanisms of chemical releases, transport and fate in the environment. Engineering Cost Analysis examines the investigation and remediation costs (both past and future), and other cost categories that may be appropriate for allocation.

In our next newsletter, I will examine various issues and approaches that may be employed to evaluate and arrive at reasonable allocation schemes. The selection of an appropriate methodology will ultimately always be dependent on the site-specific facts and available data.

For more information, please contact Alborz Wozniak at (925) 403-6200.

 


 

 

 

 

 

 

 

 




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