City of Modesto v. Dow Chemical Co.

CourtCalifornia Court of Appeal
DecidedJanuary 8, 2018
DocketA134419
StatusPublished

This text of City of Modesto v. Dow Chemical Co. (City of Modesto v. Dow Chemical Co.) is published on Counsel Stack Legal Research, covering California Court of Appeal primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
City of Modesto v. Dow Chemical Co., (Cal. Ct. App. 2018).

Opinion

Filed 1/8/18

CERTIFIED FOR PARTIAL PUBLICATION *

IN THE COURT OF APPEAL OF THE STATE OF CALIFORNIA

FIRST APPELLATE DISTRICT

DIVISION FOUR

CITY OF MODESTO et al., Plaintiffs and Appellants, A134419 v. THE DOW CHEMICAL COMPANY et (San Francisco County Super. Ct. al., Nos. CGC-98-999345 & CGC-98-999643) Defendants and Respondents.

I. INTRODUCTION In late 1998, the City of Modesto (the City), the City of Modesto Sewer District No. 1 (the Sewer District) and the Modesto Redevelopment Agency (the RDA) sued various retail dry cleaning businesses (dry cleaners) operating in Modesto together with the manufacturers of dry cleaning equipment used at those dry cleaners, and the manufacturers and distributors of dry cleaning solvent. Plaintiffs alleged that defendants had caused the City’s groundwater, sewer system and easements, and the soil of property located within the project area of the RDA, to become contaminated with perchloroethylene (PCE), a “toxic chlorinated solvent[].” Plaintiffs sought recovery for the past, present and future costs of investigation and remediation of the contamination at numerous sites under multiple legal theories. This action has engendered nearly 14 years of litigation, including three detours to this court, and five trial phases. A final judgment was entered in November of 2011, and an amended judgment in May 2012. To the extent it can be summarized in one sentence,

* Pursuant to California Rules of Court, rules 8.1105(b) and 8.1110, Sections I, II, III.B. and Section IV.A. (except subsection 1.) of this opinion are certified for publication. 1 the judgment awarded plaintiffs damages with respect to three dry cleaning sites, including an award of punitive damages against three defendants; as to all other claims, judgment was entered in favor of defendants. An issue that has been central to this litigation from the outset is the interpretation and application of the Polanco Redevelopment Act (Health & Saf. Code, § 33459 et seq.) (the Polanco Act), 1 which, in essence, authorized redevelopment agencies to remediate contamination found in property, including private property, located in a redevelopment project area, and to recover from the “responsible parties” the costs of the cleanup. Early in the case, this division issued a decision, on a petition for writ of mandate, providing our construction of that law. Specifically, we reversed the trial court’s summary adjudication of the Polanco Act claims, concluding that the trial court erred in finding, as a matter of law, that defendants could not be “responsible parties” under the Act based on the facts put forward by the plaintiffs. (City of Modesto Redevelopment Agency v. Superior Court (2004) 119 Cal.App.4th 28 [Modesto I].) Thereafter, the Polanco Act claims were tried two times, with respect to different contaminated sites, before two different judges, with different results. In the second proceeding, the trial court concluded that Modesto I implied a special causation standard was applicable to the Polanco Act claims. In the published portion of this opinion we hold that no special causation standard applies and we will, accordingly, vacate the trial court’s ruling and order on the Phase IV Polanco Act claims. In the unpublished portion of the opinion we address the remaining issues on appeal. We will vacate the trial court’s pretrial ruling with respect to plaintiffs’ nuisance claims; the punitive damages award against defendant, the Dow Chemical Company (Dow) in Phase I; and the trial court’s directed verdict on grounds of no present injury as to various sites in Phase III. Our determinations with respect to the statute of limitations, the denial of equitable relief, the amended judgment, the prevailing parties and the allocation of settlement credits will be described in the course of the opinion.

1 All unattributed statutory cites are to the Health and Safety Code. 2 II. GENERAL BACKGROUND We begin by providing some general technical information about the characteristics of PCE, how it can contaminate groundwater, how it is used and reused in dry cleaning equipment, and how it was released into the environment. This is not a comprehensive discussion of the evidence but is intended only to supply context for our discussion of the issues on this appeal. A. Characteristics of Perchloroethylene Perchloroethylene, also known as tetrachloroethylene, is a molecule containing chlorine atoms and carbon atoms. It is also characterized as a “volatile halogenated organic compound,” a “halogenated hydrocarbon”, a “chlorinated solvent” or a “chlorinated hydrocarbon”. As shorthand, it is referred to as “perc” or PCE. All chlorinated hydrocarbons, like all solvents other than water, are “toxic.” In 1978, the National Institute for Occupational Safety Hazards (NIOSH) recommended that PCE be handled as if it were a human carcinogen. In 1980 the State of California began regulating PCE as a hazardous waste. In 1984, when the Resource Conservation Recovery Administration (RCRA) was reauthorized, its regulations brought “small dry cleaners” under the same requirements as major hazardous waste sources, with respect to PCE. The California Department of Health Services has set the maximum contamination level (MCL) for PCE in drinking water at 5 parts per billion based on its finding that PCE potentially causes cancer in humans. Applying this standard, if one cup of PCE were completely dissolved in water, it could contaminate 24 million gallons of groundwater. There are also regulations to prevent migration of PCE vapors in concentrations that could cause cancer. All parties agree that the applicable regulatory standards are not arbitrary and address genuine public health risks. PCE is a colorless liquid, and is therefore difficult to see once released into soil. It is a cleaning solvent used by dry cleaners and also in degreasing operations. Because in its pure form it is a dense non-aqueous phase liquid (DNAPL), it is heavier than water and so when placed in water it will sink and sit below the water. This is distinguished

3 from a light non-aqueous phase liquid (LNAPL), such as gasoline, that is lighter than water and will therefore float on top. PCE also has lower viscosity (internal friction) than water and so it is very mobile and can move quickly to penetrate, for example, small cracks or joints in concrete. PCE does not readily dissolve in water—thus, “non- aqueous”—although it will dissolve very slowly over time. PCE is also quite volatile, meaning it will quickly become a gas when it is heated or released into soil where it mixes with the soil gas. As is explained below, PCE is particularly “persistent” and “long lived” compared to other contaminants, making it extremely difficult to accomplish complete remediation. B. The Flow and Transport of PCE in a Groundwater System The City of Modesto uses groundwater as a primary source of its drinking water supply. The hydrologic cycle for groundwater is fairly straightforward. The rain falls and sinks into the “soil zone” which is the layer near the surface where plants and trees take it up with their roots. The rest of the water continues to move downward through the soil into the “vadose zone,” in which there are various types of soils—fine grain such as clay or silt and coarse grain such as sand or gravel. Some of the water may “perch” on the fine grain materials but other water will flow through the coarser soil media and recharge the water table, which is at the top of the “saturated zone” from which ground water is pumped by wells. Between the vadose and saturated zones is a “capillary fringe.” This space can hold “quite a bit of liquid,” and the porous media can pull water up from the water table. As we have noted, when PCE is released into the ground it can volatilize and mix with the soil gases.

Free access — add to your briefcase to read the full text and ask questions with AI

Related

Ford Motor Co. v. Ramon Romo
538 U.S. 1028 (Supreme Court, 2003)
O'NEIL v. Crane Co.
266 P.3d 987 (California Supreme Court, 2012)
Davis v. Kiewit Pacific CA4/1
220 Cal. App. 4th 358 (California Court of Appeal, 2013)
Pfeifer v. John Crane, Inc.
220 Cal. App. 4th 1270 (California Court of Appeal, 2013)
Neff v. Ernst
311 P.2d 849 (California Supreme Court, 1957)
Stevens v. Parke, Davis & Co.
507 P.2d 653 (California Supreme Court, 1973)
Kowis v. Howard
838 P.2d 250 (California Supreme Court, 1992)
City of Pasadena v. City of Alhambra
207 P.2d 17 (California Supreme Court, 1949)
Schrader v. Neville
207 P.2d 1057 (California Supreme Court, 1949)
White v. Ultramar, Inc.
981 P.2d 944 (California Supreme Court, 1999)
People v. Hamilton
753 P.2d 1109 (California Supreme Court, 1988)
Egan v. Mutual of Omaha Insurance
598 P.2d 452 (California Supreme Court, 1979)
College Hospital, Inc. v. Superior Court
882 P.2d 894 (California Supreme Court, 1994)
Wright v. Best
121 P.2d 702 (California Supreme Court, 1942)
Gerstein v. Smirl
160 P.2d 585 (California Court of Appeal, 1945)
Walker v. Superior Court
807 P.2d 418 (California Supreme Court, 1991)
Rank v. Krug
90 F. Supp. 773 (S.D. California, 1950)
Northridge Co. v. W.R. Grace & Co.
471 N.W.2d 179 (Wisconsin Supreme Court, 1991)
Simmons v. Southern Pacific Transportation Co.
62 Cal. App. 3d 341 (California Court of Appeal, 1976)

Cite This Page — Counsel Stack

Bluebook (online)
City of Modesto v. Dow Chemical Co., Counsel Stack Legal Research, https://law.counselstack.com/opinion/city-of-modesto-v-dow-chemical-co-calctapp-2018.