Tag: Landfill

  • Environmental Engineering Expert Witness’ Testimony About Emissions From Alternative Odor Sources Excluded

    Environmental Engineering Expert Witness’ Testimony About Emissions From Alternative Odor Sources Excluded

    This case concerns the operation of the Jefferson Parish Landfill in Waggaman, Louisiana (the “JPLF”), and the resulting odors emitted from the JPLF between July 1, 2017, and December 31, 2019 (the “relevant time period”). Plaintiffs, who are Jefferson Parish residents, filed several individual lawsuits that were consolidated into a mass action, Addison v. Louisiana Regional Landfill Co., which contains over 500 individual Plaintiffs.

    The Defendants asserted several “alternative source arguments,” including that: (1) Plaintiffs’ alleged damages were sustained in whole or in part as a result of intervening or superseding causes, including noxious odors originating from sources other than the JPLF; and (2) Plaintiffs’ claims are barred or diminished to the extent their injuries were caused by their own comparative fault or the comparative fault of third parties or sources of odors for which the Defendants are not responsible.

    The Defendants offered Michael Corn, P.E., as an expert in emissions rates, fate and effect analysis, and non-landfill odors and emissions sources.

    The Plaintiffs sought to exclude Corn’s testimony under Rules 401403, and 702, insofar as Corn’s testimony is not relevant, is unreliable, and will not assist the trier of fact, and has the potential to confuse the issues and mislead the jury.

    Environmental Engineering Expert Witness

    Michael Corn has over 50 years of experience as an environmental and water resources engineer and environmental consultant, working in industrial and government-operated facilities, like the non-landfill emissions sources.

    Corn has conducted or supervised other engineers and scientists in developing air emissions estimates, air permitting, air modeling, and Toxics Release Inventory reporting.

    Get the full story on challenges to Michael Corn’s expert opinions and testimony with an in-depth Challenge Study. 

    Discussion by the Court

    The subject of Corn’s testimony may be relevant under Rule 401

    The Defendants contended that Corn’s testimony supports their alternative source arguments and is directly relevant to the causation element of Plaintiffs’ claims.

    On July 17, 2024, the Court issued its Order and Reasons determining, in relevant part, that “evidence related to Defendants’ alternative source arguments is relevant under Rule 401, as ‘any potential alternative theories of causation go directly toward a key underlying issue’ in this case.” Because Corn’s proposed testimony is relevant to the Defendants’ alternative source arguments, the Court will not exclude Corn’s testimony under Rule 401.

    Corn’s testimony will be excluded under Rules 702 and 403

    Corn expressed four distinct opinions based on his findings:

    • First, given that the weather data collected do not show a preferential wind direction, it is my opinion that no one source (i.e., the Landfill) could have impacted all [Trial Plaintiffs] at all times.
    • Second, emissions from the alternative odor sources, permitted or not, resulted in odors in areas that the [Trial Plaintiffs] lived and traveled through.
    • Third, the proximity of the receptor to sources released at or near ground level is more likely to impact a receptor. 
    • Fourth, given the variable wind direction in the area and the plaintiffs’ close proximity to many known odor sources, he opined that the [Trial Plaintiffs] are more likely than not subjected to multiple different pollutants released from the industrial facilities

    Plaintiffs argued Corn’s testimony should be excluded under Rule 702 because his opinions are “matters of common knowledge,” which “ordinary jurors” can ascertain from their own experience without “special expertise or training,” and thus will not assist the trier of fact.

    A. Non-Facility Emissions Sources

    Corn supports Opinion No. 2 in part by his finding that localized emissions from the Sewer System generated odors that likely impacted the Trial Plaintiffs “resid[ing] nearby.” The Court held that Corn provides no analysis of the extent of the impact of this one event or how long the impact would have lasted. Corn’s documentation of this one incident report does not support his finding that localized emissions from the Sewer System generated odors that likely impacted the Trial Plaintiffs.

    Corn supports Opinion No. 2 by pointing to the “the large expanse of wetlands and forested wetlands that surround the local areas,” which he says “presents a significant likely alternative emissions source to the [Trial Plaintiffs] at their residences and the areas [through which] they travel.” The Court held that Corn’s finding, which is based purely on his speculation with no data relevant to the specific wetlands at issue, does not provide sufficient support for Opinion No. 2. His speculation does not support his finding that localized emissions from the Wetlands generated odors that likely impacted the Trial Plaintiffs.

    B. Facility Emissions Sources

    Corn based Opinion No. 2 in part by his finding that several “industrial and municipal facilities . . . more likely than not” emitted odiferous pollutants in quantities sufficient to “impact[] the individual [Trial Plaintiffs] at their residence[s].”

    The Court held that to the extent Corn relies on LDEQ Incident Reports of emissions events outside the 30-month relevant time period (i.e., July 1, 2017, through December 31, 2019), his findings on those facilities are excludable under Rule 401 because they are irrelevant to the issue of whether an alternative source of odors impacted the Trial Plaintiffs during the relevant time period. 

    1. Cornerstone Chemical Complex

    Corn supported Opinion No. 2 in part by his finding that several operating facilities within the Cornerstone Complex generated emissions that likely impacted the Trial Plaintiffs.

    The Court held that Corn does not explain the significance of the emissions rates reported therein of other pollutants or explain how the data is relevant to his finding that operating facilities in the Cornerstone Complex generated odors that could have been detected by the Trial Plaintiffs, effectively nullifying any probative value they may have.

    a. The Acrylonitrile Plant

    Corn based Opinion No. 2 in part by his finding that the Acrylonitrile Facility is a potential alternative source of odors that may have impacted the Trial Plaintiffs.

    The Court held that assumptions based on emissions events that occurred outside the relevant time period are irrelevant to the issue of whether the Acrylonitrile Plant impacted the Trial Plaintiffs during the relevant time period. Because the basis of Corn’s finding on the Acrylonitrile Plant is unreliable and irrelevant, it does not support Opinion No. 2.

    b. The Urea and Melamine Plant

    Corn supports Opinion No. 2 in part by his finding that the Urea and Melamine Plant is an alternative source of odors that “might have” impacted the Trial Plaintiffs.

    The Court held that Corn’s documentation of the facility’s air permit, the two incident reports during the relevant time period, the several incident reports that occurred outside the relevant time period, and the Facebook video does not support his finding that emissions from the Urea and Melamine Plant generated odors that likely impacted the Trial Plaintiffs.

    c. The Sulfuric Acid Regeneration Plant

    Corn supports Opinion No. 2 in part by his finding that the Sulfuric Acid Regeneration Plant (the “Regeneration Plant”) is an alternative source of “regularly occurring” emissions that “likely” impacted nearby Trial Plaintiffs.

    Summarizing Corn’s evidence to support his finding that the Regeneration Plant “likely” impacted the Trial Plaintiffs during the relevant period, the Court found there was one odor complaint during the 30-month relevant time period, documented in the LDEQ Incident Report dated December 13, 2018. The other two LDEQ Incident Reports and the two Cornerstone Letters cited in the Corn Report concern releases from the facility for which there were no related odor complaints. Corn failed to provide evidence or opinion supporting his finding that the isolated incident, which was the subject of the odor complaint “likely” affected the Trial Plaintiffs.

    d. The Utilities Plant/Site Services

    Corn based Opinion No. 2 in part by his finding that the Utilities Plant “was a source of likely odors in Jefferson Parish.”

    The Court held that the finding was unreliable because it was based on the unfounded and speculative extrapolation of three isolated incidents of de minimis releases during the 30-month relevant time period.

    e. The Dyno Nobel Ammonia Plant

    Corn bases Opinion No. 2 in part by his finding that the Dyno Nobel Ammonia Plant is an alternative source of odors that “likely” impacted some of the Trial Plaintiffs.

    The Court held that Corn’s documentation of the facility’s air permit, TRI Reports, two incident reports from the relevant time period, and the Facebook video does not support his finding that emissions from the Dyno Nobel Ammonia Plant generated odors that likely impacted the Trial Plaintiffs.

    f. The Roehm America Plant

    Corn based Opinion No. 2 in part by his finding that the Roehm America Plant is an alternative source of odors that may have impacted the Trial Plaintiffs.

    The Court held that Corn’s documentation of the facility’s air permit, TRI Reports, and the one incident report during the relevant time period does not support his finding that emissions from the Roehm America Plant generated odors that likely impacted the Trial Plaintiffs.

    g. The Kemira Chemicals Plant

    With respect to the Kemira Chemicals Plant located within the Cornerstone Complex, Corn represents the Kemira Chemicals Plant has a Title V Permit and presents information related to the facility’s Title V Permit for the relevant time period in Table 19 of the Corn Report.

    The Court held that inferring the types and quantities of pollutants emitted by a facility from the facility’s air permit is unreliable. Accordingly, the basis of any purported finding of Corn on the Kemira Chemicals Plant is unreliable and does not support Opinion No. 2. Corn’s documentation of the facility’s air permit does not support his finding emissions from the Kemira Chemicals Plant generated odors that likely impacted the Trial Plaintiffs.

    2. The ARTCO Facility

    Corn supported Opinion No. 2 in part by his finding that the ARTCO Facility is an alternative source of odors that “likely impacted nearby [Trial Plaintiffs].”

    The Court held that Corn does not describe the duration of this event nor how the odor travelled. To the extent that Corn’s finding on the ARTCO Facility is based on the unfounded and speculative extrapolation of one isolated incident of a de minimis release during the 30-month relevant time period, the finding is unreliable.

    3. The IMTT Facility

    Corn supported Opinion No. 2 in part by his finding that the IMTT Facility is an alternative source of odors that “might have” had an impact on the Trial Plaintiffs.

    The Court held that Corn’s documentation of the facility’s air permit and one incident report from outside the relevant time period does not support his finding that emissions from the IMTT Facility generated odors that might have impacted the Trial Plaintiffs.

    4. The Harahan Waste Treatment Plant

    Corn based Opinion No. 2 in part by his finding that the Harahan WTP is an alternative source of odors that “likely” had an impact on the Trial Plaintiffs.

    The Court held that Corn bases his vague conclusion on two isolated complaints of sewage intrusion onto individuals’ properties during the relevant time period, rather than any widespread complaint of noxious odors in the air. 

    5. The ADM Grain Facility

    Corn supported Opinion No. 2 in part by his finding that the ADM Grain Facility is an alternative source of odors that “might have” had an impact on the Trial Plaintiffs.

    The Court held that Corn’s documentation of the facility’s air permit and incident reports from outside the relevant period does not support his finding that the ADM Grain Facility generated odors that might have impacted on the Trial Plaintiffs.

    6. The Cargill Westwego Marine Terminal

    Corn supports Opinion No. 2 in part by his finding that Cargill is an alternative source of odors that “might have” had an impact on the Trial Plaintiffs.

    The Court held that Corn’s documentation of the facility’s air permit and four incident reports during the relevant time period does not support his finding that emissions from Cargill generated odors that might have impacted the Trial Plaintiffs.

    7. Kirby Inland Marine

    Corn supported Opinion No. 2 in part by his finding that Kirby Inland Marine is an alternative source of odors that “likely” impacted Trial Plaintiffs.

    The Court held that assumptions based on emissions events that occurred outside the relevant time period are irrelevant to the issue of whether emissions from Kirby Inland Marine impacted the Trial Plaintiffs during the relevant time period. Further, to the extent that Corn’s finding on Kirby Inland Marine is based on the unfounded and speculative extrapolation of one isolated incident of a de minimis release during the 30-month relevant time period, the finding is unreliable. 

    8. The Composing Facility

     Corn supported Opinion No. 2 in part by his finding that “odor emissions (ammonia, hydrogen sulfide, etc.) during composting are practically unavoidable,” thus “numerous unpermitted air emissions events” associated with the Composting Facility that occurred “before the relevant time period . . . illustrate the impacts the facility might have [had] on [the Trial Plaintiffs] during the relevant time period.”

    The Court held that Corn’s documentation of the facility’s incident reports from outside the relevant time period does not support his finding that emissions from the Composting Facility generated odors that might have impacted the Trial Plaintiffs.

    9. Non-landfill operations at the River Birch Landfill

    Corn supported Opinion No. 2 in part by his finding that non-landfill operations at the River Birch Landfill constituted alternative sources of odors that might have impacted the Trial Plaintiffs.

    The Court held that Corn’s documentation of the facility’s air permit and one incident report during the relevant time period does not support his finding that emissions from River Birch generated odors that might have impacted the Trial Plaintiffs.

    Held

    The Court granted Plaintiffs’ motion in limine to exclude the testimony of Michael Corn.

    Key Takeaway:

    Rule 702 charges the Court as “gate-keeper” with the responsibility of conducting a preliminary assessment into whether the reasoning and methodology underlying expert testimony is scientifically valid and reliable. As set forth above, the proponent of expert testimony must prove by a preponderance of the evidence that the testimony is reliable. Having conducted a comprehensive review of Opinion No. 2 and the relevant reliance documents, the Court finds that the Defendants have not satisfied their burden of proving Corn’s testimony is reliable by a preponderance of the evidence. Corn’s opinion is peppered with his statements that the emissions sources “may have” or “might have” impacted the Trial Plaintiffs, or at the very best “likely” did so. 

    Please refer to the blog previously published about this case: Environmental Engineering Expert Witness’ Testimony About the Source of H2S is Not Fully Admissible

    Case Details:

    Case Caption: Addison, Et Al. V. Louisiana Regional Landfill Company
    Docket Number: 2:19cv11133
    Court: United States District Court for the Eastern District of Louisiana
    Order Date: July 30, 2024
  • Environmental Engineering Expert Witness’ Testimony About the Source of H2S is Not Fully Admissible

    Environmental Engineering Expert Witness’ Testimony About the Source of H2S is Not Fully Admissible

    This case concerns the operation of the Jefferson Parish Landfill in Waggaman, Louisiana (the “JPLF”), and the resulting odors emitted from the JPLF between July 1, 2017, and December 31, 2019 (the “relevant time period”). Plaintiffs, who are Jefferson Parish residents, filed several individual lawsuits that were consolidated into a mass action, Addison v. Louisiana Regional Landfill Co., which contains over 500 individual Plaintiffs.

    The Defendants asserted several “alternative source arguments,” including that: (1) Plaintiffs’ alleged damages were sustained in whole or in part as a result of intervening or superseding causes, including noxious odors originating from sources other than the JPLF; and (2) Plaintiffs’ claims are barred or diminished to the extent their injuries were caused by their own comparative fault or the comparative fault of third parties or sources of odors for which the Defendants are not responsible.

    Motion to preclude

    The Defendants engaged Matthew Stutz, P.E.—represented to be an expert in “landfill design, engineering, management, and operations”—to offer opinions about modeled emissions and emission rates of landfill gas and hydrogen sulfide (“H2S”) from the JPLF and two neighboring landfills, the River Birch Landfill (the “RBLF”) and the Highway 90 construction and demolition (“C&D”) Landfill (the “Hwy 90 Landfill” or “Hwy 90”).

    Stutz is also offered as a rebuttal expert to rebut the opinions of Plaintiffs’ experts, specifically regarding: (1) the generation and emissions of landfill gas and hydrogen sulfide; (2) the design, operation, and maintenance of the JPLF, including its cover, leachate, landfill gas, and odor control systems; and (3) the acceptance of nonhazardous industrial waste at the JPLF. Stutz expressed several opinions in his expert report (the “Stutz Report”) related to modeled gas generation and emissions estimates for the JPLF, the RBLF, and the Hwy 90 Landfill.

    Plaintiffs filed their Motion in Limine seeking to preclude Stutz from offering testimony related to certain opinions expressed in the Stutz Report under the law-of-the-case doctrine and Federal Rule of Evidence Rule 702.

    Environmental Engineering Expert Witness

    Matthew K. Stutz is a Principal with Weaver Consultants Group, LLC. He has extensive work experience in landfill gas collection and control system design, leachate systems, and air quality permitting and compliance, and he has prepared numerous landfill gas collection and control system designs, landfill gas evaluations, emission inventories, air quality permits, emission calculations, and odor control plans.

    Stutz received a Bachelor of Science in Civil/Environmental Engineering in 1997, from The University of Texas at Arlington. He currently serves on a panel of the U.S. Environmental Protection Agency (“EPA”) which provides comments on landfill air quality regulations.

    Get the full story on challenges to Matthew Stutz’s expert opinions and testimony with an in-depth Challenge Study. 

    Discussion by the Court

    After preparing landfill gas generation models and emissions estimates for the JPLF, the RBLF, and the Hwy 90 Landfill, using mathematical analysis and relevant source material, Stutz expressed several opinions in his Report.

    Stutz’s testimony related to the Hwy 90 Landfill will be excluded under Rule 702

    Plaintiffs sought to exclude the portion of Opinion No. 2B in which Stutz opines “the Hwy 90 Landfill was the largest and most significant source of H2S emissions of the three landfills” during the relevant time period. The Stutz Report represents “[a] main component[] used in gas generation modeling is the concentration of the specific gas being modeled,” which in this case is H2S.

    After comparing the modeled H2S emission rates for the Hwy 90 Landfill, the RBLF, and the JPLF, Stutz concluded “the majority of H2S emissions during [the relevant time period] came from Hwy 90.”

    The Court found that the scant and uncharacteristic H2S concentration data from February 2008, on which Stutz based the Hwy 90 Model for the relevant time period, rendered Opinion No. 2B unreliable.

    In this case, Stutz relied on two data points collected on a single day nearly one decade before the relevant time period to derive the H2S concentration that informs his Hwy 90 Model. Hwy 90 records demonstrate the landfill experienced elevated H2S concentrations in 2008, which likely resulted from the burial of organic vegetative and gypsum sheetrock debris when the LDEQ designated the landfill an Emergency Debris Site post-Hurricane Katrina.

    The Court also found that the probative value of Stutz’s testimony on the Hwy 90 Landfill is substantially outweighed by the risk of misleading the jury. Thus, the Court will also exclude Stutz’s testimony related to the Hwy 90 Landfill under Rule 403.

    Stutz may offer testimony on the JPLF and the RBLF

    Stutz’s testimony on the JPLF and RBLF will not be excluded
    under Rule 702

    Plaintiffs also sought to exclude the portion of Opinion No. 2B in which Stutz expressed findings related to the JPLF and the RBLF under Rule 702. Plaintiffs argued Stutz improperly neglected to calculate the total H2S that may be generated from material at the landfills, which rendered his modeled H2S emissions from those facilities “nothing more than a wild guess.” Specifically, Plaintiffs claim Stutz’s modeled H2S emissions from the JPLF are not the product of reliable principles or methods because his model does not account for “the forty-six million [] pounds of spent lime buried in [Phase IVA].”

    The Court has reviewed the bases of the portions of Opinion No. 2B related to the JPLF and the RBLF. Unlike the H2S concentration used in his Hwy 90 Model, a review of Opinion Nos. 1B and 2B reveals the H2S concentrations Stutz used in the H2S Generation Models for the JPLF and the RBLF (the “JPLF Model” and “RBLF Model,” respectively) are more “grounded in the methods and procedures of science” than in Stutz’s unsupported speculative or subjective belief.

    With respect to the JPLF Model, Stutz represented he “uses the same average H2S concentrations as the Plaintiffs’ experts,” and Plaintiffs do not challenge this assertion. With respect to the RBLF Model, although Stutz’s H2S concentration is based on limited data, the H2S concentration is based on a study from June 2018, during the relevant time period.

    Stutz’s testimony on the JPLF will not be excluded under the law-of-the-case doctrine

    Plaintiffs sought to exclude the remaining contested opinions on the basis that the opinions relate to issues adjudicated in the general causation phase and should be excluded under the law-of-the-case doctrine.

    The Court has reviewed the Stutz Report and finds Plaintiffs’ argument is without merit. Table 4 of the Stutz Report provides a comparison of 2019 H2S concentrations at the JPLF, which identifies an average H2S concentration at the JPLF Phase IVA of: (1) 3,633 ppm (i.e., 3,633,000 ppb) collected inside the landfill; (2) 0.43 ppm (i.e., 430 ppb) at the landfill surface; and (3) 1.126 ppm (i.e., 1,126 ppb) collected from ambient readings at approximately three feet from the landfill surface. To the extent the Plaintiffs challenge Stutz’s opinions under the law-of-the-case doctrine, Stutz input the H2S concentration of 3,633 ppm into his JPLF Model for Phase IVA, which is the same figure relied upon by Plaintiffs’ H2S emissions model.

    Held

    The Court granted in part and denied in part the Plaintiffs’ motion to exclude expert testimony of Matthew Stutz. Stutz may not offer testimony related to the Hwy 90 Landfill. He may offer testimony related to the JPLF and the RBLF. Stutz may offer his rebuttal of Plaintiffs’ experts’ opinions on the JPLF and RBLF, as necessary, but may not offer rebuttal opinion related to the Hwy 90 Landfill.

    Key Takeaways:

    • Stutz offered no explanation as to the validity or general acceptance in the scientific community of his methodology for deriving an H2S concentration based on such scant and uncharacteristic data.
    • To the extent Plaintiffs challenge Stutz’s omission of site-specific data, including his failure to calculate the total H2S generated at the landfills, the Court finds these concerns go to the weight of Stutz’s opinions rather than their reliability and should be left for the factfinder’s consideration.

    Case Details:

    Case Caption: Addison, Et Al. V. Louisiana Regional Landfill Company, Et Al
    Docket Number: 2:19cv11133
    Court: United States District Court, Louisiana Eastern
    Order Date: July 31, 2024