Food & Water Watch, Inc. v. Environmental Protection Agency

District Court, N.D. California·Decided January 18, 2024·No. 3:17-cv-02162·Unknown

Opinion

FOOD & WATER WATCH, INC., et al., Case No. 17-cv-02162-EMC

Plaintiffs, FINAL PRETRIAL CONFERENCE v. ORDER (PHASE TWO)

PROTECTION AGENCY, et al., Defendants.

I. TRIAL DATES & LENGTH A bench trial shall be held beginning on January 31, 2024. Trial days are: January 31, February 1, 2, 5, 6, 7, 9, 12, 13 (nine days total) with one extra day available in case of logistical issues: February 14. Trial days shall begin at 8:30 a.m. and end at 1:30 p.m. Counsel are expected to be present at 8:00 a.m. at least, unless the Court orders otherwise. Each side shall have 18 hours to present their case. This includes opening statements, direct and cross-examinations, and closing arguments. II. TRIAL PROCEDURES A. Evidence and Objections A party must give the opposing party at least forty-eight (48) hours’ notice of witnesses it intends to call, exhibits it intends to use, and/or demonstratives it intends to use. Saturdays and Sundays do not count. Thus, e.g., for a Monday trial day that starts at 8:30 a.m., a party must give the opposing party notice by 8:30 a.m. on Thursday. If the opposing party has an objection, then it must notify the party by 6:00 p.m. the same day of notice, and the parties shall meet and confer to see if they can resolve their differences. If they cannot, then they shall file with the Court a joint statement twenty-four (24) hours in advance of the relevant trial day. In short, the Court requires a full day to resolve any objections. The Court emphasizes that, because this will be a bench trial, it expects objections to be kept to a minimum. B. Broadcast of Trial The emergency CARE act has sunsetted and the Judicial Conference of the United States has enacted an advisory policy that limits broadcasting in civil cases to audio-only nonevidentiary hearings. However, the Ninth Circuit has yet to rescind its broadcast policy which allows for broadcasting civil proceedings by e.g. Zoom. In light of the benefits (including educational benefits and public interest) of broadcasting, the Court will broadcast the trial live via Zoom Videoconference. C. Trial and Evidentiary Format The trial is to take place in-person. Witnesses will be testifying in person with the exception of one witness that will be testifying via deposition video. Exhibits will be displayed electronically at trial to allow for a more efficiently display of evidence. D. Proposed Findings of Fact The parties are to submit a merged document with proposed findings of fact and conclusions of law by one week prior to the start of trial, i.e., by January 24, 2024. The Court shall require the parties to file on a rolling basis iterative proposed findings of fact based on the specific evidence that was presented on a given trial day. Citations to the relevant witness testimony and/or exhibit number will be helpful but are not necessary; the document need not include reference to specific pin-cites during the trial. The parties will work together to merge the documents under a single framework for organizing the proposed findings of fact and shall file the proposed findings one week before trial.1 // // The parties do not dispute the following facts: A. Undisputed Facts from First Trial 1. According to the United States Centers for Disease Control and Prevention (CDC), as of 2014, approximately 200,000,000 people in the United States live in communities that add fluoridation chemicals to the drinking water. 2. Plaintiffs’ Citizen Petition sought to prohibit the addition of fluoridation chemicals to water on the grounds that this condition of use presents an unreasonable risk of neurologic harm. 3. Fluoridation chemicals are added to drinking water to prevent tooth decay (i.e., dental caries). In addition to being added to water, fluoride is added to dental products and certain pesticides. 4. In epidemiology, a cross-sectional study is a comparison of the prevalence of a specific health outcome across levels of a specific exposure in study subjects (or vice versa), with the exposure and outcome both measured at a given time, providing a “snapshot” of the association between the exposure and the health outcome at one time. 5. In epidemiology, a cohort study is a comparison of incidence rates of a specific health outcome between study subjects with various levels of a specific exposure who are observed over time. 6. A person’s individual response to fluoride exposure depends on factors such as age, kidney function, body weight, activity level, nutrition, and other factors. 7. Human urine fluoride concentrations (biomonitoring) measure an internal dose. 8. Various factors can affect the concentration of fluoride in a urine sample, such as an individual’s metabolism, when a urine sample is collected, and the time since the last void of the individual who provided the sample. 9. Historically, most studies to investigate the impact of fluoride on IQ in humans have used cross-sectional study designs. Most of these cross-sectional studies have been conducted in in water. By contrast, fluoride is added to water in the United States to reach a concentration of 0.7 mg/L. 10. Prospective cohort studies have been conducted in Mexico City (ELEMENT cohort), where fluoride is added to salt, and Canada (MIREC cohort), where fluoride is added to water. These studies are the most methodologically reliable human studies to date on the impact of fluoride on neurodevelopment.2 11. Risk assessment is the process by which scientific judgments are made concerning the potential for toxicity in humans. 12. The National Research Council (NRC, 1983) has defined risk assessment as including the following components: hazard identification, dose-response assessment, exposure assessment, and risk characterization. 13. The term “risk evaluation” is a specialized term under TSCA. 14. Together, the components of EPA’s risk assessment process, coupled with the ultimate risk determination, constitute a “risk evaluation” under TSCA. 15. The final step of a risk evaluation is to weigh a variety of factors to determine whether the chemical substance, under the conditions of use, presents an unreasonable risk of injury to health or the environment, referred to as the “risk determination” step in the TSCA risk- evaluation process. 16. EPA does not require that human exposure levels exceed a known adverse effect level to make an unreasonable risk determination under TSCA.3 17. In the ideal world, all risk assessments would be based on a very strong knowledge base (i.e., reliable and complete data on the nature and extent of contamination, fate and transport processes, the magnitude and frequency of human and ecological exposure, and the inherent toxicity of all of the chemicals). However, in real life, information is usually

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Food & Water Watch, Inc. v. Environmental Protection Agency, (N.D. Cal. 2024).

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