Bergeson & Campbell, P.C. serves small, medium, and large pesticide product registrants and other stakeholders in the agricultural and biocidal sectors, in virtually every aspect of pesticide law, policy, science, and regulation.

By Lynn L. Bergeson and Margaret R. Graham, M.S.

On May 3, 2019, the U.S. Environmental Protection Agency (EPA) announced it was seeking comments on the experts who are candidates to serve as ad hoc panelists for the review of EPA’s Draft Product Performance Test Guidelines OCSPP 810.3300:  Treatments Topically Applied to Pets to Control Certain Invertebrate Ectoparasitic Pests.  The candidate list is available on EPA’s Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA) Scientific Advisory Panel (SAP) website.  Comments on the candidates are due by May 18, 2019, to the Designated Federal Official (DFO) Dr. Suhair Shallal (.(JavaScript must be enabled to view this email address)).  EPA is requesting these comments prior to the FIFRA SAP public in-person meeting scheduled for June 11-14, 2019, from 9:00 a.m. to 5:00 p.m. (EDT), which will review EPA’s proposed guidelines referenced above and the supplemental document Sample Size for Pet Product Studies84 Fed. Reg. 15214.  The charge questions to the panel are available here (Charge Questions). 

EPA’s Federal Register notice announcing the meeting states that the meeting will be augmented with additional experts to provide independent scientific advice on the proposed guidelines.  Preceding the in-person meeting, there will be a public half-day preparatory virtual meeting to consider the scope and clarity of the draft charge questions for this peer review.  The in-person meeting on June 11-14, 2019, will be held at the EPA Conference Center, Lobby Level, One Potomac Yard (South Building), 2777 South Crystal Drive in Arlington, Virginia.  The meeting will also be available via webcast.

EPA’s original Product Performance Test Guidelines, OPPTS 810.3300, Treatments to Control Pests of Humans and Pets were published in March 1998.  EPA’s Charge Questions state that “[t]o increase clarity and consistency in efficacy testing and to include current scientific standards, the agency is revising this product performance guideline.”  Further, the proposed guidelines apply to products “in any topically applied formulation, such as a spray, spot-on, collar, shampoo, or dust, if intended to be directly applied to pets for a pesticidal purpose such as to kill, repel, or control ticks, fleas, mosquitoes, and biting flies”; do not apply “to those products exempt from FIFRA Registration under 40 CFR 152.25, products applied to humans or livestock, or product performance testing described in other agency guidelines”; and, in addition to guidance for testing efficacy against fleas, ticks, mosquitoes, and biting flies, the proposed guideline “also includes testing methods for evaluating efficacy under simulated environmental conditions.”

EPA believes the current Draft Guidelines represent the state of the science with regard to efficacy testing for these products; but is still seeking advice and recommendations from the FIFRA SAP on scientific issues related to the Draft Guidelines.  EPA states that it is committed to reducing the use of animals in testing but, at this time, no reliable non-animal alternatives are available to avoid the use of animals for efficacy testing of fleas, ticks, mosquitoes, and biting flies.  EPA is soliciting comment from the FIFRA SAP on approaches that may, in the future, support the replacement or reduction of animal use in efficacy testing of ectoparasitic pests on pets.

Information on attending the meeting in person and via webcast can be found on the FIFRA SAP website.  EPA is requesting that written comments on the documents undergoing peer review be submitted to Docket No. EPA-HQ-OPP-2019-0161 by May 17, 2019, to provide the FIFRA SAP the time necessary to consider and review the written comments.


 

By Lisa M. Campbell and Heather F. Collins, M.S.

On May 3, 2019, the U.S. Environmental Protection Agency (EPA) announced it was making final a single correction to the data requirements for antimicrobial pesticide products codified in 40 C.F.R. Part 158, subpart W.  84 Fed. Reg. 18993.  The correction clarifies that the 200 parts per billion (ppb) level described in the antimicrobial pesticides data requirements regulations (40 C.F.R. § 158.2230(d)) “is based on total estimated daily dietary intake for an individual and not on the amount of residue present on a single food,” as EPA states was incorrectly implied by the previous regulatory text.  EPA initially proposed this change on August 18, 2017 (82 Fed. Reg. 39399) because it agreed to do so in a settlement agreement with the American Chemistry Council (ACC) after ACC filed a petition for review of the 2013 final rule titled “Data Requirements for Antimicrobial Pesticides” (78 Fed. Reg. 26936 (May 8, 2013)) in the U.S. Court of Appeals for the District of Columbia Circuit.  Specifically, EPA agreed to make this correction to “make the language consistent” with the U.S. Food and Drug Administration’s (FDA) policy set forth in FDA’s “Guidance for Industry, Preparation of Food Contact Notifications for Food Contact Substances: Toxicology Recommendations. Final Guidance. April 2002.”  EPA states that the change is intended to “enhance understanding of the data required to support an antimicrobial pesticide registration and does not alter the burden or costs associated with these previously promulgated requirements” and that it is not establishing “any new data requirements or any other revisions (substantive or otherwise) to existing requirements.”  The final rule will become effective on July 2, 2019.


 

By Timothy D. Backstrom

On April 19, 2019, the U.S. Circuit Court of Appeals for the Ninth Circuit (Ninth Circuit) issued an order following an en banc rehearing in League of United Latin Am. Citizens (LULAC) v. Wheeler, No. 17-71636.  The February 6, 2019, Ninth Circuit decision to grant a U.S. Environmental Protection Agency (EPA) request for rehearing effectively vacated an August 9, 2018, decision in LULAC that had ordered EPA to revoke all tolerances and cancel all registrations for chlorpyrifos.  After rehearing, the en banc panel issued a writ of mandamus directing EPA “to issue, no later than 90 days after the filing of this order, a full and fair decision on LULAC’s objections" to an initial EPA order denying a 2007 petition to revoke all tolerances for chlorpyrifos.  The en banc order states that the court has discretion to construe the Petitioners' opening brief as a request for mandamus relief, even though the Petitioners sought judicial review of EPA's initial denial decision without waiting for EPA to rule on their objections and even though they did not file a petition for mandamus under the applicable procedural rule.  The court then states that “[c]onsidering the history and chronology of this matter and the nature of the claims, we conclude mandamus is appropriate, and we hereby GRANT the Petition for a Writ of Mandamus.”

The court states that “EPA represented that it could issue a final decision with respect to petitioners’ objections within 90 days of an order issued by this court” during oral argument on March 26, 2019.  The en banc ruling, however, does not discuss the jurisdictional issues presented when the Petitioners sought judicial review of EPA's initial denial decision without waiting for EPA to rule on their objections.  Moreover, the ruling does not discuss the substantive dispute concerning EPA's authority to decline to revoke the tolerances and cancel the registrations for chlorpyrifos based on the current administrative record.

Commentary

The procedural questions presented in the LULAC litigation are unusual and reflect a long and contentious history.  EPA’s April 5, 2017, decision to deny a 2007 petition to revoke the tolerances and cancel the registrations for chlorpyrifos came after issuance of a prior writ of mandamus that required EPA to take action on the pending petition, an EPA proposal to revoke the tolerances for chlorpyrifos issued in response to the prior writ, and a subsequent decision by EPA during the early days of the Trump administration to reverse course on the proposal and keep the tolerances in place while EPA completed the registration review process.  The Petitioners in LULAC duly filed objections to the initial denial of their tolerance petition, which was a necessary statutory prerequisite to pursuing further judicial review.  In addition, however, they elected to file for judicial review of EPA's initial denial of their tolerance petition on the same day as they filed their objections.  The Petitioners could not yet reasonably seek mandamus at that time because EPA had not been afforded any time yet to respond to their objections.  Instead, the Petitioners argued that requiring them to follow the normal administrative process would be futile.

Although the Ninth Circuit's decision after en banc rehearing may appear to a procedural victory for EPA, it can also be seen as a solution to the quandary created by the Petitioners' actions and the first court decision.  The Ninth Circuit as a whole was apparently not comfortable with the decision by the first panel that the Petitioners should be allowed to obtain review of a non-final order because waiting for final and reviewable EPA action would be a futility.  Nevertheless, by issuing a new writ of mandamus, the court seems to be sending a clear signal that it will not countenance further delays in EPA’s taking final action on the petition to revoke the chlorpyrifos tolerances.  In the relatively brief time remaining before the court deadline for final action, EPA confronts a significant challenge of ensuring all relevant data have been adequately and appropriately considered, particularly given the many controversies concerning the data that EPA used to support its initial decision to revoke the tolerances. 

More information on the protracted litigation concerning chlorpyrifos is available on our blog under key words chlorpyrifos and ninth circuit.


 

By James V. Aidala and Susan M. Kirsch

On April 23, 2019, the U.S. Environmental Protection Agency (EPA) announced it was making available its Interpretive Statement addressing whether the Clean Water Act’s (CWA) National Pollutant Discharge Elimination System (NPDES) permit program applies to releases of a pollutant from a point source to groundwater (Interpretive Statement) for comment.  84 Fed. Reg. 16810.  EPA is issuing the Interpretative statement to “provide clarity on [EPA’s] interpretation of the [CWA] given the mixed record of prior [EPA] statements and a split in the federal circuit courts regarding this issue.” EPA’s Interpretive Statement states that it “sets forth [its] interpretation of the [CWA NPDES] permit program’s applicability to releases of pollutants from a point source to groundwater that subsequently migrate or are conveyed by groundwater to jurisdictional surface waters” and “EPA concludes that the [CWA] is best read as excluding all releases of pollutants from a point source to groundwater from NPDES program coverage and liability under Section 301 of the CWA, regardless of a hydrologic connection between the groundwater and a jurisdictional surface water.”  EPA also released a fact sheet on its Interpretive Statement, available online.

The April 23 Federal Register notice states that the Interpretative Statement reflects EPA’s consideration of the public comments received in response to its February 20, 2018, Federal Register notice (83 Fed. Reg. 7126) which requested comment on EPA’s previous statements regarding whether pollutant discharges from point sources that reach jurisdictional surface waters via groundwater or other subsurface flow that has a direct hydrologic connection to the jurisdictional surface water may be subject to CWA regulation.  EPA received over 50,000 comments from a wide range of stakeholders, many of which affirmed that additional clarity from EPA was necessary.  EPA reached its conclusion based on the comments received and on “a holistic analysis of the [CWA], its text, structure, and legislative history.”  EPA also references numerous policy considerations that support excluding groundwater discharges from NPDES permitting, including existing state and federal authorities and statutes that play a role in regulating groundwater quality (e.g., Safe Drinking Water Act (SDWA) Underground Injection Control (UIC) program).

EPA is soliciting public comments on the Interpretive Statement, specifically regarding what may be needed to provide further clarity and regulatory certainty on this issue.  Comments are due by June 7, 2019.

EPA’s Interpretive Statement comes at a critical time when the U.S. Supreme Court is set to address the question of “[w]hether the [CWA] requires a permit when pollutants originate from a point source but are conveyed to navigable waters by a nonpoint source, such as groundwater” (see SCOTUSblog) in its review of the Ninth Circuit decision in County of Maui v. Hawaii Wildlife Fund (Maui).  A petition for U.S. Supreme Court review is also pending on the Fourth Circuit decision in Kinder Morgan Energy Partners v. Upstate Forever (Kinder Morgan), which held similarly to Maui that “a discharge that passes from a point source through ground water to navigable waters may support a claim under the CWA.”  A pair of September 2018 Sixth Circuit decisions (Kentucky Waterways Alliance v. Kentucky Utilities Co. and Tennessee Clean Water Network v. TVA) expressly disagreed with the holdings in Maui and Kinder Morgan -- resulting in a “circuit split.”  Although the facts in Maui (wastewater injected into UIC wells) and Kinder Morgan (gas spilled from underground pipeline) may not involve activities common in agriculture and pesticide applications, the new judicial “tests” created in these decisions could dramatically expand the scope of the NPDES universe in ways that could potentially implicate agricultural/pesticide practices.  For example, in Maui, the Ninth Circuit held that Maui County’s discharges from UIC wells to groundwater should require CWA discharge permits because the pollutants from the UIC wells that reached a navigable water were “fairly traceable” and levels reaching the navigable water were “more than de minimis.”  The Ninth Circuit’s Maui holding could be stretched broadly to support the assertion that pesticides and fertilizers applied to agricultural lands that migrate through groundwater and eventually reach a CWA jurisdictional water could be subject to NPDES permitting.  Agriculture and pesticide stakeholders may wish to closely monitor developments around groundwater discharge issues at EPA and the U.S. Supreme Court.  


 

By Lynn L. Bergeson and Margaret R. Graham, M.S.

On April 19, 2019, the U.S. Environmental Protection Agency’s (EPA) Office of Pesticide Programs (OPP) announced that it will hold a public meeting of the Pesticide Program Dialogue Committee (PPDC) on May 8, 2019, from 9 a.m. to 5 p.m. and May 9, 2019, from 9 a.m. to 12:00 p.m. (EDT) in the first-floor conference center at One Potomac Yard South, 2777 South Crystal Drive in Arlington, Virginia.  84 Fed. Reg. 16486.  The Federal Register notice states that the agenda is not yet available but that this meeting will provide advice and recommendations to EPA’s Administrator on issues associated with pesticide regulatory development and reform initiatives, evolving public policy and program implementation issues, and science issues associated with evaluating and reducing risks from use of pesticides.  The draft agenda will be available on or before May 5, 2019, on the PPDC webpage.  The meeting is open to the public and no advance registration is required.


 

By Lisa M. Campbell and James V. Aidala

On April 8, 2019, the Agency for Toxic Substances and Disease Registry (ATSDR) announced the opening of a docket on the draft toxicological profile for glyphosate. 84 Fed. Reg. 13922. ATSDR seeks comments and additional information or reports on studies about the health effects of glyphosate for review and potential inclusion in the profile.  Comments are due by July 8, 2019.

The draft profile includes a chapter on glyphosate’s potential for human exposure, which states the following in the overview:

  • “Glyphosate has not been identified in any of the 1,832 hazardous waste sites that have been proposed for inclusion on the [U.S. Environmental Protection Agency (EPA)] National Priorities List (NPL) (ATSDR 2015). However, the number of sites evaluated for glyphosate is not known.” 
  • “Occupational and residential exposure is a result of glyphosate’s use in agricultural, nonagricultural, industrial, and residential settings. The highest potential for dermal, inhalation, and ocular exposure is expected for pesticide applicators, farm workers, and home gardeners who use herbicides containing glyphosate.”
  • “The general population is exposed to glyphosate via ingestion of crops, plants, and foods with residues of this chemical. Residential exposure may occur via inhalation, dermal contact, and/or ocular contact during mixing or application of consumer products containing glyphosate or by coming into contact with crops, soils, or water to which glyphosate-containing products have been applied.”
  • “Occupational exposure to glyphosate may occur via inhalation, dermal contact, and/or ocular contact during manufacture, transport, mixing, loading, application, and disposal processes. Accidental oral exposure may occur via unintentional ingestion. Dermal contact appears to be the major route of exposure to glyphosate for individuals involved in its application.”
  • “Glyphosate mainly enters the environment as a direct result of its herbicidal use. Fate of this chemical in the environment includes degradation, transport, and partitioning processes, which are governed by its physicochemical properties and by abiotic or biotic degradation under certain environmental conditions. Glyphosate is a nonvolatile, highly polar, non-residual herbicide that has low potential for environmental persistence and is unlikely to bioaccumulate.”

 Commentary

ATSDR’s draft profile and the peer review which will follow can be expected to become part of the larger debate about the potential risks of glyphosate.  Meanwhile, EPA continues its work on the registration review of the herbicide.  In 2017, EPA evaluated the carcinogenic risk of glyphosate, and released its draft human health and ecological risk assessments.  See our December 19, 2017, blog item EPA Releases Draft Human Health and Ecological Risk Assessments for Glyphosate for Public Comment for more information.  After the public comment period for the draft human health and ecological risk assessments ended in April 2018, EPA officials have stated they hope to complete the registration review sometime this year.

 


 

By Lisa M. Campbell, Sheryl Lindros Dolan, and Margaret R. Graham, M.S.

On March 25, 2019, the U.S. Environmental Protection Agency (EPA) posted Draft Guidance for Plant Regulator Label Claims, Including Plant Biostimulants in Docket # EPA-HQ-OPP-2018-0258.  EPA issued the notice of availability in the Federal Register on March 27, 2019.  84 Fed. Reg. 11538.  Comments on the draft guidance are due by May 28, 2019

EPA states that the draft guidance is intended to “provide guidance on identifying product label claims that are considered to be plant regulator claims” by EPA under the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA) and thereby distinguish claims that would not subject plant biostimulants (PBS) to regulation under FIFRA as plant regulators.  While EPA has not yet promulgated a regulatory definition for a PBS, the draft guidance describes a PBS as “a naturally-occurring substance or microbe that is used either by itself or in combination with other naturally-occurring substances or microbes for the purpose of stimulating natural processes in plants or in the soil in order to, among other things, improve nutrient and/or water use efficiency by plants, help plants tolerate abiotic stress, or improve the physical, chemical, and/or biological characteristics of the soil as a medium for plant growth.”  EPA is seeking comment on the draft guidance itself, as well as on whether it should develop a definition for PBSs.  EPA states that there is currently no statutory definition for PBSs under FIFRA and that development of a definition for PBSs would require rulemaking.  The guidance also notes that the 2018 Farm Bill, enacted on December 20, 2018, does provide a statutory definition for PBSs, which is:  “a substance or micro-organism that, when applied to seeds, plants, or the rhizosphere, stimulates natural processes to enhance or benefit nutrient uptake, nutrient efficiency, tolerance to abiotic stress, or crop quality and yield.” 

In developing the draft guidance, EPA states that it “considered whether a PBS product, as understood by EPA, physiologically influences the growth and development of plants in such a way as to be considered plant regulators under FIFRA thereby triggering regulation as a pesticide” and that “a key consideration is what claims are being made on product labels.”  Further, as FIFRA Section 2(v) both defines plant regulator and explains which substances are excluded from the definition, “many PBS products and substances may be excluded or exempt from regulation under FIFRA depending upon their intended uses as plant nutrients (e.g., fertilizers), plant inoculants, soil amendments, and vitamin-hormone products.”

The draft guidance provides several examples of both product label claims that are considered plant regulator claims and claims that that are not considered plant regulator claims.  The examples are described in the Tables below.

  • “Product label claims generally considered ‘non-pesticidal’ (i.e. non-plant regulator claims),” including:  “plant nutrition-based claims” (Table 1a); “plant inoculant-based claims” (Table 1b); and “soil amendment-based claims” (Table 1c):

  • “Generic product label claims for products not covered by the exclusions in the FIFRA Section 2(v) definition of a plant regulator,” including “examples of generic product label claims generally considered by the Agency to be ‘non-pesticidal’” (Table 2):

  • “Plant regulator product label claims that are consistent with the FIFRA Section 2(v) plant regulator definition” including “examples of label claims that are considered … to be plant growth regulator claims that trigger regulation under FIFRA as a pesticide” (Table 3):

  • “EPA-registered, naturally-occurring, plant regulator active ingredients having modes of action and associated product label claims that are consistent with the FIFRA definition of a plant regulator” (Table 4):


 

By James V. Aidala and Margaret R. Graham, M.S.

On March 21, 2019, the U.S. Environmental Protection Agency (EPA) announced it was updating its Residual Time to 25% Bee Mortality (RT25) Data Table with information it has collected since the table was first published in 2014.  EPA states that the “RT25 data help farmers and beekeepers know about how long a specific pesticide may remain toxic to bees and other insect pollinators following foliar application to crops,” and the new data “reflect the results of studies the agency has analyzed as part of [its] routine pesticide regulatory activities.”  One example that EPA provides regarding how this new data will work is that farmers can now “choose pesticides that quickly lose their toxicity to bees,” and that applying the products in the evening “helps ensure that by morning the pests have been dealt with and blooming crops are safe for bees.” 

EPA states that RT25 values are a function of a number of factors including application rate, physical-chemical properties, dissipation, crop, and pesticide formulation.  The values provided were compiled from registrant-submitted data submitted to fulfill the data requirement for Honey Bee (Apis mellifera) Toxicity of Residues on Foliage study (OCSPP Guideline 850.3030).  EPA states that the honey bee toxicity of residues on foliage study “is a laboratory test designed to determine the length of time over which field weathered foliar residues remain toxic to honey bees, or other species of terrestrial insects” and, depending on the chemical tested, “either the technical grade active ingredient or a specific formulation was tested using either the honey bee, alfalfa leaf cutting bee, or alkali bee.”  The data table lists the test material, the species tested, and the plant species on which residues were aged.

EPA plans to update the table annually as it collects additional data going forward.  More information on EPA’s actions intended to protect pollinators is available on EPA’s website.

Commentary

In addition to providing the residual toxicity values, the table also illustrates the wide range of toxicity values among the various pesticides.  RT25 times for the different active ingredients can range between a few and over 500 hours to reach the RT25 threshold.  Even different formulations using the same active ingredient can have a significant difference in toxicity values.  This illustrates the importance of reading the specific label instructions for a pesticide, even one that might be generally familiar to the user.

EPA’s publication of this information online also imposes a duty for EPA to continually update the table, especially to capture any changes in the information appearing in an earlier listing of the data.  If, upon further review or later data submissions there are changes to the table for a product, EPA will need to alert users to potentially important changes in the information.  Again, this illustrates the need for reading the label for each pesticide at the time of application, since some important information may have changed.


 

By Lisa R. Burchi

On March 7, 2019, in the Court of Justice of the European Union (EU), the Eighth Chamber of the General Court issued two judgments in cases regarding access of confidential information related to glyphosate.  One of these decisions (Tweedale v. EFSA, Case T-716/14) related to a 2014 request for two toxicity studies that were “key studies” in the determination of glyphosate’s acceptable daily intake (ADI).  The second decision (Hautala et al. v. EFSA, Case T-329/17) related to a request from Members of the European Parliament for access to parts (i.e., “material, experimental conditions and methods” and “results and discussions”) of 12 unpublished carcinogenicity studies, described as the “‘most crucial’ studies for the peer review and [EFSA’s] conclusion that glyphosate is unlikely to pose carcinogenic hazard to humans.”  Partial access to those studies (i.e., raw data and findings aggregated in tables and figures) had been granted in an earlier 2016 decision.

A prior November 21, 2018, case related to glyphosate (Stichting Greenpeace Nederland and Pesticide Action Network Europe v. European Commission, Case T-545/11 RENV) and the General Court/Fourth Chamber’s judgment to prevent applicants from receiving access to information on the degree of purity of the active substance glyphosate, as well as the identity and quantities of impurities is discussed here.  In contrast to the Stichting decision, where access was denied, the court in the March 7, 2019, decisions annulled prior decisions dated October 16, 2017 and March 14, 2017, that refused access to the requested information.

Discussion

Article 4(2) of Regulation No. 1049/2001 (regarding public access to European Parliament, Council and Commission documents) provides that access to documents should be refused where disclosure would undermine, in part, commercial interests of a natural or legal person, including intellectual property, unless “there is an overriding public interest in disclosure.” 

Article 6(1) of Regulation No. 1367/2006 (regarding the application of the provisions of the Aarhus Convention on Access to Information, Public Participation in Decision-making and Access to Justice in Environmental Matters to Community institutions and bodies) provides that, with regard to Regulation No. 1049/2001 Article 4(2), “an overriding public interest in disclosure shall be deemed to exist where the information requested relates to emissions into the environment.”  Recital 15 of Regulation No. 1367/2006 also provides: “The grounds for refusal as regards access to environmental information should be interpreted in a restrictive way, taking into account the public interest served by disclosure and whether the information requested relates to emissions in the environment.”

Taken together, the court stated: “that means that an EU institution, hearing a request for access to a document, cannot justify its refusal to divulge it on the basis of the exception relating to the protection of the commercial interests of a particular natural or legal person for the purposes of Article 4(2), first indent, of Regulation No 1049/2001, where the information contained in that document constitutes information which ‘relates to emissions into the environment’ for the purposes of Article 6(1) of Regulation No 1367/2006.”

The General Court/Fourth Chamber thus addressed whether the information contained in the applicants’ requests constituted information which ‘relates to emissions into the environment’ for the purposes of Article 6(1) of Regulation 1367/2006. 

In the March 7, 2019, decisions, the General Court/Fourth Chamber held that EFSA cannot argue that the requested studies do not concern actual emissions or the effects of actual emissions because “an active substance contained in plant protection products, such as glyphosate, in the course of normal use, is intended to be discharged into the environment by virtue of its function, and its foreseeable emissions cannot, therefore, be regarded as purely hypothetical.”  The court further held: “It is apparent from that case-law that the concept of information which ‘relates to emissions into the environment’ for the purposes of Article 6(1) of Regulation No 1367/2006 is not limited to information which makes it possible to assess the emissions as such, but also covers information relating to the effects of those emissions.”   The Court further stated that the “concept of information which ‘relates to emissions into the environment’ for the purposes of Article 6(1) of Regulation No 1367/2006 must be interpreted as covering not only information on emissions as such, namely information concerning the nature, composition, quantity, date and place of those emissions, but also data concerning the medium to long-term consequences of those emissions on the environment.”

The court also found that EFSA’s “argument that the conditions in which the requested studies were carried out are not linked to emissions is irrelevant. What matters is not the conditions in which the requested studies were carried out, but their purpose.”  In these cases, the purpose to define a no observed adverse effect level (NOAEL) from which the ADI was calculated, or to determine the carcinogenic effects of exposing humans to glyphosate, “must be regarded as constituting information which ‘relates to emissions into the environment; for the purposes of Article 6(1) of Regulation No. 1367/2006.”

In sum, the court in Tweedale concluded:

  • It follows from the foregoing that the exception relating to the protection of commercial interests, provided for in Article 4(2), first indent, of Regulation No 1049/2001, cannot be relied upon in order to object to the disclosure of the requested studies which are regarded as information which ‘relates to emissions into the environment’ for the purposes of Article 6(1) of Regulation No 1367/2006.

The court in Hautala further stated that “an overriding public interest in disclosing the studies is deemed to exist, and EFSA could not refuse to disclose them on the ground that that would have an adverse effect on the protection of the commercial interests of the owners of the requested studies for the purposes of Article 4(2), first indent, of Regulation No 1049/2001.”

Commentary

These decisions support transparency but also may add confusion regarding any limitations placed on the scope of what is to be considered “information on emissions into the environment.”  The prior 2018 Stichting decision refused access to information on the degree of purity of the active substance glyphosate, as well as the identity and quantities of impurities, finding that such information is excluded from the concept of “information relating to emissions into the environment:”

  • Since the use, the conditions of use and the composition of a plant protection product authorised by a Member State on its territory may be very different from those of products evaluated at EU level during the approval of the active substance, it must be held that the information in the document at issue does not relate to emissions whose release into the environment is foreseeable and has, at the very most, a link to emissions into the environment.

These decisions may expand the scope of information that relates to emissions into the environment, including, for example, “data concerning the medium to long-term consequences of those emissions on the environment.”  For information that is determined to constitute information that “relates to emissions into the environment,” the decisions appear to create a presumption for disclosure that cannot be countered based on the exception relating to the protection of the commercial interests of a particular natural or legal person.

Companies should continue to monitor these decisions closely, as guidance continues to evolve regarding the scope of disclosure.

More information on glyphosate issues is available on our blog.


 

By James V. Aidala

On March 8, 2019, President Trump signed S. 483, the “Pesticide Registration Improvement Extension Act of 2018,” which reauthorizes the Pesticide Registration Improvement Extension Act (PRIA 4) through fiscal year 2023, updates the fee collection provisions and authorities available under the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA) and addresses worker protection matters.  The text is available at Congress.gov, which has not yet been updated to confirm that the bill has been signed (but this appears to be the final amended text of the bill).

On February 14, 2019, the Senate approved S. 483 to reauthorize the Pesticide Registration Improvement Extension Act (PRIA 4) and the House of Representatives approved it on February 25, 2019.  Further amendments were made and the Senate approved the amended text on February 28, 2019.  More information on the PRIA 4 legislation is available on our blog under key word PRIA.  


 
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