Csd No. 2 of Los Angeles v. County of Kern

Citation127 Cal.App.4th 1544,27 Cal.Rptr.3d 28
Decision Date01 April 2005
Docket NumberNo. F043095.,F043095.
CourtCalifornia Court of Appeals
PartiesCOUNTY SANITATION DISTRICT NO. 2 OF LOS ANGELES COUNTY et al., Plaintiffs, Cross-defendants and Appellants, California Association of Sanitation Agencies et al., Plaintiffs and Appellants, v. COUNTY OF KERN, Defendant, Cross-complainant and Appellant; Kern County Board of Supervisors, Defendant and Appellant; Arvin-Edison Water Storage District et al., Interveners and Respondents.

M. Hogan, San Diego, for Defendant, Cross-complainant and Appellant and for Defendant and Appellant.

Law Offices of Young Wooldridge, Ernest A. Conant, Scott K. Kuney and Steven M. Torigiani, Bakersfield, for Intervener and Respondent Arvin-Edison Water Storage District.

McMurtrey, Hartsock & Worth, James A. Worth; and Linda Alvarado, Bakersfield, for Interveners and Respondents Cawelo Water District and West Kern Water District.

OPINION

DAWSON, J.

This appeal concerns the validity of an ordinance that restricts the application of sewage sludge on land located within the jurisdiction of Kern County.1 Sanitation agencies from Southern California2 appeal adverse rulings from the trial court. The sanitation agencies contend (1) County was required to prepare an environmental impact report (EIR) under the California Environmental Quality Act (CEQA)3 prior to adopting the ordinance, (2) the ordinance violated the commerce clause as well as other constitutional and statutory provisions, and (3) a biosolids impact fee of $3.37 per ton violated the prohibition in Vehicle Code section 9400.8 against local fees for the privilege of using roads. County contests all of these allegations. It contends that the ordinance benefited the Kern County environment and that any potential adverse environmental impacts were too remote and speculative to justify preparing an EIR.

We hold County was required to prepare an EIR under CEQA. This is because CEQA requires the preparation of an EIR whenever substantial evidence supports a fair argument that an ordinance will cause potentially significant adverse environmental impacts. CEQA thus sets a low threshold for the required preparation of an EIR. Here, the evidence in the administrative record establishes a reasonable possibility that the ordinance will have both positive and adverse impacts on the environment in Kern County and other areas of California, principally because alternative methods of disposal must be implemented. The positive effects of a project do not absolve the public agency from the responsibility of preparing an EIR to analyze the potentially significant negative environmental effects of the project, because those negative effects might be reduced through the adoption of feasible alternatives or mitigation measures analyzed in the EIR. Therefore, County was required to prepare an EIR.

We hold also that plaintiffs have failed to show that the ordinance discriminates against interstate commerce. We reject plaintiffs' constitutional and statutory attacks on the validity of the ordinance, except that we hold the biosolids impact fee was invalid to the extent it was a local fee for road use.

We will remand with directions to the trial court to issue a writ of mandate directing County to prepare an EIR for the ordinance, and for further proceedings to determine the extent to which the biosolids impact fee was a fee for road use. Otherwise, the rulings of the trial court in favor of County on plaintiffs' complaint will be affirmed.

County cross-appeals from the trial court's denial of its CEQA cross-claims against the sanitation agencies. We address County's contention that CEQA required those agencies to conduct an environmental examination in connection with certain biosolids disposal contracts they entered or extended near the time the ordinance in question was enacted. We hold that the agencies' contract activities were within the scope of their program EIR's covering their wastewater treatment projects and, therefore, were "[s]ubsequent activities in the program" that should have been subjected to an examination in accordance with title 14, section 15168 of the California Code of Regulations4 to determine if further CEQA review was necessary. We further hold that, as to expired contracts, this question is moot. Therefore, judgment on County's cross-claims will be reversed and the matter remanded to the trial court with directions to (1) conduct further proceedings to make a complete determination of which contracts have expired, (2) enter an order dismissing as moot County's causes of action that are based on contracts that have expired, and (3) issue writs of mandate under the remaining causes of action directing the appropriate sanitation agency to conduct an examination to determine if additional environmental documents must be prepared in connection with the contracts and extensions.

HISTORICAL BACKGROUND

Sewage sludge is a product of wastewater treatment. The safe and efficient disposal of sludge is a modern and worldwide concern — a by-product of population growth and modernization.5 Recent decades have witnessed increasing governmental involvement in the effort to safely and efficiently treat sewage and dispose of sewage sludge. In the United States, efforts at regulation have involved the executive, legislative and judicial branches of government at the federal, state and local levels. This historical background briefly describes the process that reduces sewage to sewage sludge and then discusses the disposal and use of that sludge.

"Sewage sludge" is defined by federal regulations as the "solid, semi-solid, or liquid residue generated during the treatment of domestic sewage in a treatment works." (40 C.F.R. § 503.9(w) (2005).) More generally, sewage sludge refers to the mud-like deposit originating from sewage and created by the treatment processes used to decontaminate wastewater before it is released into local waterways.6 Sewage sludge typically consists of water and 2 to 28 percent solids.7 (68 Fed.Reg. 61084, 61086 (Oct. 24, 2003).) To illustrate, the Joint Water Pollution Control Plant located in Carson, California (Carson Plant) produces sewage sludge by detaining wastewater solids in an anaerobic digester for approximately 18 days. After digestion, the remaining solids are dewatered in a centrifuge that produces a residue that is approximately 25 percent solids. The Carson Plant refers to these residues as "biosolids" — a term that is not defined by federal regulation, and the meaning of which varies with the context in which it is used. (Goldfarb, Sewage Sludge, supra, 26 B.C. Envtl. Aff. L.Rev. at p. 688.) Some use the term to mean sewage sludge that has been stabilized and disinfected for beneficial use. (Id., fn. 6.) To others, the term helps emphasize the material is a recyclable resource with potential beneficial properties. (Goldfarb, Sewage Sludge, at p. 688.)

Scope of Sewage Sludge Production
National Production

The United States Environmental Protection Agency (EPA) recently estimated the annual production of sewage sludge from the 16,000 wastewater treatment plants in the United States at both 7 million tons and 8 million dry metric tons.8 (Compare 68 Fed.Reg. 68813, 68817 (Dec. 10, 2003) with 68 Fed.Reg. 61086 (Oct. 24, 2003).) In 2003, the EPA estimated that approximately 60 percent of sewage sludge was treated and applied to farmland, 17 percent was buried in landfills, 20 percent was incinerated, and 3 percent was used as landfill or mine reclamation cover. (68 Fed.Reg. 68817 (Dec. 10, 2003).) The land application of sewage sludge occurred on approximately 0.1 percent of the agricultural land in the United States. (68 Fed.Reg. 61086 (Oct. 24, 2003).) Other application sites include forests, strip-mines, reclamation sites, and public spaces like parks, golf courses, and highway median strips. (Ibid.)

California

CASA estimated that in 1998 California produced approximately 672,330 dry tons of biosolids and approximately 67.8 percent was applied to land, 10.6 percent was composted, 9.1 percent was buried in landfills, 5.6 percent was incinerated, and 6.9 percent was put in onsite and offsite storage.9

The EPA estimated that in 2003 California produced 777,480 dry tons of treated sewage sludge.10 Approximately 50 percent of this sewage sludge was applied to land, 30 percent was put in landfills, 10 percent was transported out of state, 3 percent was incinerated, and the balance was put in long-term storage or treatment or put to other uses.11

Conflict between urban and rural interests has caused controversy over the land application of sewage sludge in California. In 1998, approximately 73 percent of land-applied biosolids in California was applied within the...

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