U.S. v. Weitzenhoff, Nos. 92-10105

Decision Date03 August 1993
Docket Number92-10108,Nos. 92-10105
Citation1 F.3d 1523
Parties, 23 Envtl. L. Rep. 21,322 UNITED STATES of America, Plaintiff-Appellee, v. Michael H. WEITZENHOFF and Thomas W. Mariani, Defendants-Appellants.
CourtU.S. Court of Appeals — Ninth Circuit

Philip H. Lowenthal, Wailuku, HI, for defendant-appellant Weitzenhoff.

Peter C. Wolff, Jr., Honolulu, HI, for defendant-appellant Mariani.

Craig H. Nakamura, Asst. U.S. Atty., Honolulu, HI, for plaintiff-appellee.

Appeal from the United States District Court for the District of Hawaii.

Before: GOODWIN and FLETCHER, Circuit Judges, and HUFF, * District Judge.

FLETCHER, Circuit Judge:

Michael H. Weitzenhoff and Thomas W. Mariani, who managed the East Honolulu Community Services Sewage Treatment Plant, appeal their convictions for violations of the Clean Water Act ("CWA"), 33 U.S.C. Secs. 1251 et seq., contending that 1) the district court misconstrued the word "knowingly" under section 1319(c)(2) of the CWA; 2) the court improperly permitted witnesses to testify as to the meaning of the terms and provisions of the permit issued to the East Honolulu plant; 3) the court erred in concluding that the permit was not unconstitutionally vague; 4) evidence they sought to introduce concerning a regulation proposed by the EPA was improperly excluded; 5) the court erred in refusing their proposed instruction on entrapment by estoppel; and 6) the court should have granted a mistrial due to prosecutorial misconduct. In addition, Mariani contends that his sentence was improperly adjusted upward for obstruction of justice based on his testimony at trial.

We affirm the convictions and sentence.

FACTS AND PROCEDURAL HISTORY

In 1988 and 1989 Weitzenhoff was the manager and Mariani the assistant manager of the East Honolulu Community Services Sewage Treatment Plant ("the plant"), located not far from Sandy Beach, a popular swimming and surfing beach on Oahu. The plant is designed to treat some 4 million gallons of residential wastewater each day by removing the solids and other harmful pollutants from the sewage so that the resulting effluent can be safely discharged into the ocean. The plant operates under a permit issued pursuant to the National Pollution Discharge Elimination System ("NPDES"), which established the limits on the Total Suspended Solids ("TSS") and Biochemical Oxygen Demand ("BOD")--indicators of the solid and organic matter, respectively, in the effluent discharged at Sandy Beach. During the period in question, the permit limited the discharge of both the TSS and BOD to an average of 976 pounds per day over a 30-day period. It also imposed monitoring and sampling requirements on the plant's management.

The sewage treatment process that was overseen by Weitzenhoff and Mariani began with the removal of large inorganic items such as rags and coffee grounds from the incoming wastewater as it flowed through metal screens and a grit chamber at the head of the plant. The wastewater then entered large tanks known as primary clarifiers, where a portion of the organic solids settled to the bottom of the tanks. The solid material which settled in the primary clarifiers, known as primary sludge, was pumped to separate tanks, known as anaerobic digesters, to be further processed. Those solids that did not settle continued on to aeration basins, which contained microorganisms to feed on and remove the solids and other organic pollutants in the waste stream.

From the aeration basins the mixture flowed into final clarifiers, where the microorganisms settled out, producing a mixture that sank to the bottom of the clarifiers called activated sludge. The clarified stream then passed through a chlorine contact chamber, where the plant's sampling apparatus was, and emptied into the plant's outfall, a long underground pipe which discharged the plant's effluent into the ocean through diffusers 1,100 to 1,400 feet from shore (the "Sandy Beach outfall").

Meanwhile, the activated sludge that had settled in the final clarifiers was pumped from the bottom of the clarifiers. A certain portion was returned to the aeration basins, while the remainder, known as waste activated sludge ("WAS"), was pumped to WAS holding tanks. From the holding tanks, the WAS could either be returned to other phases of the treatment process or hauled away to a different sewage treatment facility.

From March 1987 through March 1988, the excess WAS generated by the plant was The evidence produced by the government at trial showed that WAS was discharged directly into the ocean from the plant on about 40 separate occasions from April 1988 to June 1989, resulting in some 436,000 pounds of pollutant solids being discharged into the ocean, and that the discharges violated the plant's 30-day average effluent limit under the permit for most of the months during which they occurred. Most of the WAS discharges occurred during the night, and none was reported to the DOH or EPA. DOH inspectors contacted the plant on several occasions in 1988 in response to complaints by lifeguards at Sandy Beach that sewage was being emitted from the outfall, but Weitzenhoff and Mariani repeatedly denied that there was any problem at the plant. In one letter responding to a DOH inquiry in October 1988, Mariani stated that "the debris that was reported could not have been from the East Honolulu Wastewater Treatment facility, as our records of effluent quality up to this time will substantiate." (U.S. Excerpts of Record ("U.S.E.R.") at 37.) One of the plant employees who participated in the dumping operation testified that Weitzenhoff instructed him not to say anything about the discharges, because if they all stuck together and did not reveal anything, "they [couldn't] do anything to us." (2 R.T. at 66-67.)

hauled away to another treatment plant, the Sand Island Facility. In March 1988, certain improvements were made to the East Honolulu plant and the hauling was discontinued. Within a few weeks, however, the plant began experiencing a buildup of excess WAS. Rather than have the excess WAS hauled away as before, however, Weitzenhoff and Mariani instructed two employees at the plant to dispose of it on a regular basis by pumping it from the storage tanks directly into the outfall, that is, directly into the ocean. The WAS thereby bypassed the plant's effluent sampler so that the samples taken and reported to Hawaii's Department of Health ("DOH") and the EPA did not reflect its discharge.

Following an FBI investigation, Weitzenhoff and Mariani were charged in a thirty-one-count indictment with conspiracy and substantive violations of the Clean Water Act ("CWA"), 33 U.S.C. Secs. 1251 et seq. At trial, Weitzenhoff and Mariani admitted having authorized the discharges, but claimed that their actions were justified under their interpretation of the NPDES permit. The jury found them guilty of six of the thirty-one counts. 1

Weitzenhoff was sentenced to twenty-one months and Mariani thirty-three months imprisonment. Each filed a timely notice of appeal.

DISCUSSION
A. Intent Requirement

Section 1311(a) of the CWA prohibits the discharge of pollutants into navigable waters without an NPDES permit. 33 U.S.C. Sec. 1311(a). Section 1319(c)(2) makes it a felony offense to "knowingly violate[ ] section 1311, 1312, 1316, 1317, 1318, 1321(b)(3), 1328, or 1345 ..., or any permit condition or limitation implementing any of such sections in a permit issued under section 1342."

Prior to trial, the district court construed "knowingly" in section 1319(c)(2) as requiring only that Weitzenhoff and Mariani were aware that they were discharging the pollutants in question, not that they knew they were violating the terms of the statute or permit. According to appellants, the district court erred in its interpretation of the CWA and in instructing the jury that "the government is not required to prove that the defendant knew that his act or omissions were unlawful," (14 R.T. at 117), 2 as well as in rejecting their proposed instruction based on the defense that they mistakenly believed their conduct was authorized by the permit. 3 Apparently, no court of appeals has confronted the issue raised by appellants.

We review a question of statutory construction de novo. United States v. Richison, 901 F.2d 778, 780 (9th Cir.1990). "In construing statutes in a case of first impression, we first look to the language of the controlling statutes, and second to legislative history." Central Mont. Elec. Power Coop., Inc. v. Administrator of Bonneville Power Admin., 840 F.2d 1472, 1477 (9th Cir.1988). Whether a jury instruction misstates elements of a statutory crime is also a question of law reviewed de novo. United States v. Johnson, 956 F.2d 197, 199 (9th Cir.1992). If the district court was correct in its interpretation of the statute, then it did not err in giving the instruction it did or refusing to submit appellants' mistake of law defense to the jury.

As with certain other criminal statutes that employ the term "knowingly," it is not apparent from the face of the statute whether "knowingly" means a knowing violation of the law or simply knowing conduct that is violative of the law. We turn, then, to the legislative history of the provision at issue to ascertain what Congress intended.

In 1987, Congress substantially amended the CWA, elevating the penalties for violations of the Act. See H.R.Conf.Rep. No. 1004, 99th Cong., 2d Sess. 138 (1986). Increased penalties were considered necessary to deter would-be polluters. S.Rep. No. 50, 99th Cong., 1st Sess. 29 (1985). With the 1987 amendments, Congress substituted "knowingly" for the earlier intent requirement of "willfully" that appeared in the predecessor to section 1319(c)(2). 4 The Senate report accompanying the legislation explains that the changes in the penalty provisions were to ensure that "[c]riminal liability shall ... attach to any...

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