By Zameer Qureshi
On November 23, 2016, the European Court of Justice (ECJ) issued two landmark judgments in Case C-673/13 P (Commission v Stichting Greenpeace Nederland and Pan Europe) and Case C-442/14 (Bayer CropScience and Stichting De Bijenstichting v College voor de toelating van gewasbeschermingsmiddelen en biociden).
In Case C-673/13 P, the associations Stichting Greenpeace Nederland and Pesticide Action Network Europe (PAN Europe) submitted a request to the European Commission (EC) under Regulation (EC) No 1367/2006 for access to a number of documents relating to the initial marketing authorization for glyphosate, one of the most widely used herbicides in the world for agricultural weeding and the maintenance of urban and industrial areas. The EC granted access to the documents, with the exception of part of the draft assessment report prepared by Germany. The EC justified its refusal by stating that the document in question contained confidential information on the intellectual property rights of the applicants for the glyphosate authorization.
The associations brought an action before the General Court of the European Union (EU) for annulment of the EC’s decision. The General Court upheld that action in its judgment of October 8, 2013. The General Court considered that certain segments of the document in question contained information relating to emissions into the environment. Consequently, the EC was not entitled to invoke the confidentiality of commercial and industrial information, and “should have granted the associations access to those parts.” The EC was not satisfied with the judgment and asked the ECJ to set it aside.
In Case C-442/14, Bijenstichting, a Dutch bee protection association, submitted a request to the Netherlands’ authority responsible for authorizing the marketing of plant protection products and biocidal products (i.e., College voor de toelating van gewasbeschermingsmiddelen en biociden (CTB)) for disclosure of 84 documents concerning marketing authorizations issued by the authority. Bayer, a company holding a large number of these authorizations, objected to the disclosure on the basis that it would “infringe copyright and adversely affect the confidentiality of commercial or industrial information.” CTB authorized disclosure of 35 of the 84 requested documents because they contained information on emissions into the environment, “even though such disclosure could have an adverse effect on the confidentiality of commercial or industrial information.” Under Directive 2003/4/EC, commercial and industrial confidentiality may not be invoked to prevent disclosure of such information.
Bijenstichting and Bayer appealed CTB’s decision before the Netherlands courts, which referred several questions to the ECJ for a preliminary ruling regarding, among other things, whether the information requested by Bijenstichting falls within the concept of “information on emissions into the environment” -- with the consequence that it should be disclosed without Bayer being entitled to object on the grounds that such disclosure could adversely affect the confidentiality of commercial or industrial information.
The ECJ’s judgments clarify what must be understood by “emissions into the environment” and “information on [or which relates to] emissions into the environment” within the meaning of the Regulation applicable in Case C-673/13 P and the Directive applicable in Case C-442/14. In both judgments, the ECJ found that the concept of “emissions into the environment” includes the release into the environment of products or substances (e.g., plant protection products or biocides or active substances contained in those products) to the extent that the release is actual or foreseeable under “normal or realistic conditions of use of the product or substance.”
The ECJ concluded, therefore, that this concept is indistinguishable from the concepts of “release” and “discharge” and cannot be restricted to emissions emanating from industrial installations. The ECJ decided that the concept covers emissions resulting from spraying of a product into the air or its use on plants, in water, or in soil. Such limitations, the ECJ opined, would be “at odds with the objective of the regulation and directive for disclosing environmental information as widely as possible.” Additionally, the ECJ decided that Directive 2003/4/EC and Regulation (EC) No 1367/2006 cover information on actual and foreseeable emissions from a product into the environment. The ECJ concluded that “purely hypothetical emissions” are not covered by the laws.
The ECJ stated that the concept of “emissions into the environment” must be interpreted as covering not only information on emissions, but also information enabling the public to “check whether the assessment of actual or foreseeable emissions,” on the basis of which the Competent Authority authorized the product or substance in question, is correct.
In Case C-673/13 P, the ECJ set aside the judgment of the General Court insofar as the General Court considered that it is sufficient that information relates “in a sufficiently direct manner” to emissions into the environment for it to be covered by Regulation (EC) No 1367/2006. The ECJ referred the case back to the General Court of the EU for determination of whether the information at issue relates to emissions into the environment, and, if necessary, for ruling on the parties’ arguments that were not examined in its judgment. Case C-442/14 has also been referred back to the lower court.
The ECJ’s judgments clarify that public interest in “information on emissions into the environment” is important and oftentimes overrides commercial interests. The ECJ’s rulings have potentially significant and widespread implications for companies seeking to protect trade secrets and other sensitive information. The ECJ’s reasoning in its judgment can be applied to information submitted in relation to chemical products other than pesticides that are intended for uses that involve releases into the environment. The ECJ’s judgments have been criticized for not addressing risks of substantial harm to pesticide industry innovators and their proprietary rights if studies are now deemed subject to the EU’s disclosure mandate -- data developers will need to consider this possibility and take measures to protect their sensitive information.
By James V. Aidala and Margaret R. Graham
On January 12, 2017, the U.S. Environmental Protection Agency (EPA) released its Policy to Mitigate the Acute Risk to Bees from Pesticide Products (Mitigation Policy) which describes methods for addressing acute risks to bees from pesticides. EPA states that this Mitigation Policy is “more flexible and practical than the proposed policy” that was issued on May 29, 2015, and it has “made modifications to its approach with the goal of better targeting compounds that pose an acute risk, and with the goal of reducing potential impact of this effort on growers.” EPA states that it will use its Tier 1 acute risk assessment to, in part, determine the products that trigger concerns about pollinator risk that the label restrictions are intended to address. EPA will begin implementing this Policy in 2017 by sending letters to registrants describing steps that must be taken to incorporate the new labeling. More information on the Mitigation Policy, including its supporting documents, and EPA’s response to comments submitted on the proposed policy, is available on www.regulations.gov under Docket ID EPA-HQ-OPP-2014-0818.
Also on January 12, 2017, EPA published preliminary pollinator-only risk assessments for the neonicotinoid insecticides clothianidin, thiamethoxam, and dinotefuran, and an update to its preliminary risk assessment for imidacloprid, published in January 2016. EPA states that the preliminary assessments for clothianidin, thiamethoxam, and dinotefuran are similar to the preliminary pollinator assessment for imidacloprid, in that they showed that “most approved uses do not pose significant risks to bee colonies,” but “spray applications to a few crops, such as cucumbers, berries, and cotton, may pose risks to bees that come in direct contact with residue.” As for the updated imidacloprid assessment, EPA states that is looked at potential risks to aquatic species, and identified some risks for aquatic insects. Interested parties will have 60 days to comment on the preliminary risk assessments after notice is published in the Federal Register. In terms of comments, EPA states that it is especially interested in getting input from stakeholders “on the new method for assessing potential exposure and risk through pollen and nectar.” Links to risk assessment dockets for each individual insecticide are available on EPA’s website under Schedule for Review of Neonicotinoid Pesticides. EPA states it is hopes to release the final neonicotinoid risk assessments by mid-2018.
The revised Mitigation Policy has been long in coming since it was first released over eighteen months ago. The delay in revising its approach reflects the complexity of the comments submitted, and EPA’s deliberateness in more finely crafting its policies, given the passage of time and other considerations. This revised policy contains more flexibility and explicit discussion of the need for exceptions to blanket requirements in response to some of the comments received on the earlier proposal. There remains significant public and regulator concern about the possible impacts on pollinators from pesticide use, however, there is currently less of a manic tone to EPA’s statements and actions.
For example, when discussing how EPA will approach changing the labels of the affected universe of pesticide products, there is a much less onerous tone and no specific deadlines for registrants to submit revised labels “or else.” (The 2013 directives to registrants included demands for thousands of revised labels to be submitted within six weeks “or else” -- EPA would take “appropriate action” under FIFRA.) EPA reminds us all that it retains authority to impose these new requirements broadly, a statement that will strike some as regulatory overreach, but the tone and approach is more in line with past EPA “guidance” about how it will approach a new or revised regulatory concern.
Similar to what EPA previously concluded about imidacloprid, where that assessment concluded that the most controversial use -- corn seed treatments -- did not indicate a risk concern, EPA did include in its summary about the other three neonicotinoid pesticides that:
- The assessments for clothianidin, thiamethoxam, and dinotefuran, similar to the preliminary pollinator assessment for imidacloprid showed: most approved uses do not pose significant risks to bee colonies. However, spray applications to a few crops, such as cucumbers, berries, and cotton, may pose risks to bees that come in direct contact with residue.
This might unfairly be summarized as: after years of regulatory analysis EPA has concluded that if insecticides come into direct contact with insects, there is likely to be a risk to the exposed insect.
This conclusion would be too simplistic since EPA and other regulatory bodies have expressed concern about what unintended exposures to insecticides might cause, and more generally the possibility of colony level impacts on honeybee and other pollinator populations from pesticide use. Some critics will continue to insist that EPA broaden its regulatory approach to more than just pesticides used for crops under contracted pollinator services. The broader issue of pesticide drift and possible impacts on non-target species will continue to be a concern for all pesticides.
Perhaps the more deliberate consideration of needed data generation and assessment that seems to be the current approach will allow both more refined regulatory controls if needed, and a reduction in the sometimes hot rhetoric which has accompanied the pollinator issues.
Lastly, although this revised Mitigation Policy and the three new preliminary assessments are not unexpected next steps as part of the ongoing registration review program for pesticides, given their very late release -- less than ten days before the arrival of a new Administration -- some might question whether this is part of the “midnight regulations” pushing the political agenda of the outgoing Administration. The new leadership may revise what has been released, and may come to different conclusions about any needed restrictions. That said, the issue of whether certain pesticides are having a dangerous impact on honeybee populations will continue to be a concern for regulators both in the U.S. and globally.
By Lynn L. Bergeson and Carla N. Hutton
On January 4, 2017, the White House announced the release of the 2017 Update to the Coordinated Framework for the Regulation of Biotechnology (2017 Update). The Update to the Coordinated Framework provides a comprehensive summary of the roles and responsibilities of the U.S. Environmental Protection Agency (EPA), the U.S. Food and Drug Administration (FDA), and the U.S. Department of Agriculture (USDA) with respect to regulating biotechnology products. Together with the National Strategy for Modernizing the Regulatory System for Biotechnology Products, published in September 2016, the Update to the Coordinated Framework offers a “complete picture of a robust and flexible regulatory structure that provides appropriate oversight for all products of modern biotechnology.” Within that regulatory structure, the federal agencies “maintain high standards that, based on the best available science, protect health and the environment, while also establishing transparent, coordinated, predictable and efficient regulatory practices.” To help product developers and the public understand what the regulatory pathway for products might look like, the 2017 Update presents information about agency roles and responsibilities in several forms, including:
- Graphics that illustrate agency-specific overviews of regulatory roles;
- Case studies that demonstrate how a product developer might navigate the regulatory framework; and
- A comprehensive table that summarizes the current responsibilities and the relevant coordination across EPA, FDA, and USDA for the regulatory oversight of an array of biotechnology product areas.
In its blog item, “Increasing the Transparency, Coordination, and Predictability of the Biotechnology Regulatory System,” the Obama Administration acknowledges that while the 2017 Update represents “remarkable progress by the EPA, FDA, and USDA to modernize the regulatory system for biotechnology products, much work remains.” EPA, FDA, and USDA will consider the comments submitted in response to the proposed 2017 Update and information gathered during the three public engagement sessions hosted by EPA, FDA, and USDA to inform ongoing and future agency activities. In addition, the agencies commissioned an independent study by the National Academy of Sciences (NAS) on future biotechnology products. When completed, the agencies will consider the study’s findings, as well as the comments. More information on the Update to the Coordinated Framework will be available in our forthcoming memorandum, which will be available on our website under the key phrase biobased products, biotechnology.
By Lynn L. Bergeson, Oscar Hernandez, Ph.D., Lara A. Hall, MS, RQAP-GLP, and Margaret R. Graham
On December 29, 2016, the U.S. Environmental Protection Agency (EPA) issued a notice regarding the availability of final test guidelines, OCSPP Series 850 Group A -- Ecological Effects, part of a series of test guidelines established by the Office of Chemical Safety and Pollution Prevention (OCSPP) for use in testing pesticides and chemical substances to develop data for submission to EPA under the Federal Food, Drug and Cosmetic Act (FFDCA), the Federal Insecticide, Fungicide and Rodenticide Act (FIFRA), and the Toxic Substances Control Act (TSCA). The notice states that these test guidelines “serve as a compendium of accepted scientific methodologies and protocols that are intended to provide data to inform regulatory decisions,” and they “provide guidance for conducting the test, and are also used by EPA, the public, and companies that submit data to EPA.” The test guidelines will be accessible through EPA Docket ID Numbers EPA-HQ-OPPT-2009-0150 through EPAHQ-OPPT-2009-0159, and EPA-HQ-OPPT-2009-0576 on www.regulations.gov.
The changes to test guidelines are varied. Some of the changes include:
- Simple cosmetic changes, e.g., presentation of test conditions, test validity criteria, and equations for calculating response measurements;
- Housekeeping changes, e.g., the addition of final versions of draft guidelines that had not been prepared in final yet;
- The addition of a limit test option to several acute invertebrate toxicity tests;
- Changes from “cut off” dosages in existing guidelines to limit concentrations and a change in the limit concentration for industrial chemicals from “1,000 milligrams/liter (mg/L)” to “100 mg/L” for acute toxicity tests and “10 mg/L” for chronic tests; and
- Changes to terminology, e.g., to clarify 10-day versus acute exposures for sediment-dwelling invertebrate toxicity tests and saltwater versus marine conditions.
The addition of a limit test option aligns well with the new TSCA mandate to reduce vertebrate testing as a matter of federal policy. EPA notes that certain guidelines were not issued in final, but remain available for reference as draft guidelines. In that certain ecological effects guidelines relate to guidelines already developed for the Endocrine Disruptor Screening Program (EDSP), EPA notes that it will consider test design elements from the relevant EDSP guidelines in the development of OSCPP 850 series guidelines.
By Lynn L. Bergeson, Karin F. Baron, and Margaret R. Graham
On December 20, 2016, the U.S. Environmental Protection Agency (EPA) announced the start of a pilot program to evaluate the usefulness and acceptability of a mathematical tool (the GHS Mixtures Equation), which is used in the Globally Harmonized System of Classification and Labeling of Chemicals (GHS). EPA states that the goal of the pilot program is to “evaluate the utility and acceptability of the GHS Mixtures Equation as an alternative to animal oral and inhalation toxicity studies for pesticide formulations.”
For this pilot program, EPA is requesting submission of acute oral and acute inhalation toxicity study data paired with mathematical calculations (GHS Mixtures Equation data) to support the evaluation of pesticide product formulations; instruction for doing so are available on the GHS Equation Pilot Program webpage, and Guidance on the GHS Mixtures Equation is available in the Guidance on the Application of the CLP (Classification, Labeling and Packaging) Criteria.
The program is an interesting approach considering the conceptual differences of risk assessment and hazard determination that exist at the core of EPA risk approaches and GHS fundamentals. Also, the definition of the EPA Categories compared to GHS has been problematic for hazard communication applications.
Mixture calculation tools rely on the availability of data for all components and would only be applicable if the data for each were generated using the same species under similar exposure conditions.
This pilot program is being developed under EPA’s initiative to develop non-animal alternatives for acute toxicity testing, as well as EPA’s Office of Pesticide Programs’ Strategic Vision for Adopting 21st Century Science Methodologies. More information on these initiatives can be found on our Pesticide Law and Policy blog under key phrase “toxicity testing.”
By Margaret R. Graham
On November 29, 2016, the U.S. Environmental Protection Agency (EPA) announced the issuance of its new guidance for testing pesticides designed to reduce animal testing for acute dermal toxicity for pesticides, Guidance for Waiving Acute Dermal Toxicity Tests for Pesticide Formulations & Supporting Retrospective Analysis, in final. This guidance was issued as part of the Office of Pesticide Programs’ (OPP) Strategic Vision for implementing the 2007 National Research Council’s report on Toxicity Testing in the 21st Century.
OPP states that it “receives about 200-300 dermal formulation toxicity tests annually, each of which generally use 10 animals per test,” and “[w]e expect this waiver guidance to save 2,500 or more laboratory animals every year.” Further, as described in OPP Director Jack Housenger’s March 17, 2016, letter to stakeholders, “[t]his new policy represents significant progress toward EPA’s goal of significantly reducing the use of animals in acute effects testing.”
More information on OPP’s Strategic Direction for Adopting 21st Century Science Methodologies is available on EPA’s website and in our blog item EPA’s OPP Releases Guidance Documents Related to Strategic Vision for Adopting 21st Century Science Methodologies.
By Susan M. Kirsch
On November 1, 2016, the U.S. Environmental Protection Agency (EPA) published its Final National Pollutant Discharge Elimination System (NPDES) Pesticide General Permit for Point Source Discharges from the Application of Pesticides in the Federal Register, which regulates discharges to waters of the United States from the application of biological pesticides and chemical pesticides that leave a residue. 81 Fed. Reg. 75816. The 2016 NPDES Pesticide General Permit (PGP) replaces the 2011 PGP, which expired on October 31, 2016. The PGP applies to the following geographic areas where EPA serves as the NPDES permitting authority:
- The States of: Massachusetts, New Hampshire, New Mexico, and Idaho;
- District of Columbia;
- All U.S. territories except the U.S. Virgin Islands;
- Federal facilities in Delaware, Vermont, Colorado, and Washington;
- Discharges in Texas that are not under the authority of the Texas Commission on Environmental Quality, including activities associated with oil and gas exploration (see Appendix A of the Final 2016 PGP for further description); and
- All areas of Indian Country that are not covered by an EPA-approved permitting program (see Appendix A for Indian Country covered within each EPA Region).
Similar to the 2011 PGP, the 2016 PGP contains additional permit conditions and modifications that some states and tribes added through the Clean Water Act (CWA) Section 401 certification process and/or the Coastal Zone Management Act process. Part 9 of the 2016 PGP provides a detailed breakdown of any additional requirements. Forty-six states have delegated authority to administer state versions of the PGP. The majority of states recently revised and reissued their respective state PGPs for another five-year permit cycle.
The 2016 PGP applies to the same pesticide use patterns covered by the 2011 PGP, which are:
- Mosquito and Other Flying Insect Pest Control -- control of public health/nuisance and other flying insect pests (including mosquitoes and black flies) that develop or are present during a portion of their life cycle in or above standing or flowing water.
- Weed and Algae Pest Control -- control of weeds, algae, and pathogens that are pests in water and at water’s edge, including ditches and/or canals.
- Animal Pest Control -- control of animal pests, including fish, lampreys, insets, mollusks, and pathogens, in water and at water’s edge.
- Forest Canopy Pest Control -- application of a pesticide to a forest canopy to control the population of a pest species (e.g., insect or pathogen) where, to target the pests effectively, a portion of the pesticide unavoidably will be applied over and deposited to water.
The 2016 PGP requirements are nearly identical to those in the 2011 PGP, with the exception of the following two updates included in the 2016 PGP:
- Electronic reporting (Part 7.8) -- All reporting under the 2016 PGP (i.e., Notice of Intent (NOI), Annual Report, and Notice of Terminations (NOT) submissions) must be submitted via EPA’s eNOI system to be consistent with EPA’s Electronic Reporting Rule. EPA will make these reports publicly available through a searchable index tool -- eNOI search. More information on electronic reporting, and access to the Central Data Exchange for NOI, Annual Report, and NOT submissions is available here.
- Updated definition of the National Marine Fisheries Service (NMFS) Listed Resources of Concern -- Following consultation between EPA and NMFS, as required under Section 7 of the Endangered Species Act (ESA), EPA expanded the Listed Resources of Concern to include additional species not included in the 2011 PGP definition. Under Part 184.108.40.206, pesticide discharges that overlap with NMFS Listed Resources of Concern trigger additional NOI requirements to certify that the discharges and discharge-related activities are not likely to adversely affect federally listed “endangered” or “threatened” species, or federally-designated “critical habitat.” Permittees may consult EPA’s PGP NMFS Listed Resources of Concern -- Interactive Mapping Tool to determine whether a discharge activity will overlap with these Resources of Concern. Appendix I provides endangered species instructions for affected permittees. EPA states in the corresponding Fact Sheet for the 2016 PGP that it continues to estimate that less than two percent of the total number of Operators in the PGP coverage areas will need to meet additional permit requirements in order to meet ESA-related provisions.
The 2016 PGP permit conditions went into effect on October 31, 2016, and the PGP will expire in five years on October 31, 2021. 2016 PGP coverage is automatic through January 12, 2017, without the submission of an NOI, but pesticide Operators (i.e., pesticide applicators) must comply with all 2016 PGP conditions as of October 31, 2016. For any discharges commencing on or before January 12, 2017, that will continue after this date, a decision-maker must submit an NOI no later than January 2, 2017, to ensure PGP coverage, and for any discharges subsequent to January 12, 2017, an NOI submission is required no later than 10 days before the first discharge. Table 1-1 at Part 1.2.3 outlines which decision-makers must submit NOIs based on the particular pesticide use pattern, location (i.e., if discharging to a designated Outstanding National Resource Water), and acreage thresholds. Table 1-2 at Part 1.2.3 provides applicable NOI submission deadlines, including grace periods for NOI filing for discharges in response to a Declared Pest Emergency.
EPA’s webpage for pesticide NPDES permitting includes links to the final 2016 PGP, a related fact sheet, the permitting decision tool, and information on eNOI and ESA procedures.
Although the 2016 PGP largely mirrors the 2011 version of the permit, it will be important for decision-makers to familiarize themselves with the new electronic reporting requirements (Part 7.8). EPA’s eNOI system is publicly searchable and could subject PGP permit holders to additional scrutiny by citizens and advocacy groups concerned about potential environmental and public health implications of pesticide applications in their areas. Decision-makers should consult EPA’s PGP NMFS Listed Resources of Concern -- Interactive Mapping Tool and the Alternative PGP Sources of Information for NMFS Listed Resources of Concern to determine where discharges may overlap with these areas and trigger additional permit conditions.
By Lisa M. Campbell, Lisa R. Burchi, and Margaret R. Graham
The U.S. Environmental Protection Agency (EPA) has recently announced the availability of two proposed test methods and associated testing guidance for evaluating antimicrobial pesticides against two biofilm bacteria, Pseudomonas aeruginosa and Staphylococcus aureus, for comments. EPA states that registrants of antimicrobial products with public health claims are “required to submit efficacy data to EPA in support of the product’s registration” under the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA). EPA is soliciting comments on the clarity of the standard operating procedures and the regulatory guidance. The two test methods are:
The Draft Guidance to Assess the Efficacy of Antimicrobial Pesticide Products Intended to Control Public Health Biofilms on Hard, Non-Porous Surfaces describes biofilms and their public health significance; the two test procedures for developing efficacy data supporting biofilm claims; products that may be eligible for biofilm claims; test criteria; data submission procedures for efficacy data; and labeling guidance.
The draft guidance states that the term biofilm “is reserved for claims against biofilm that contain specific bacteria that are directly or indirectly infectious or pathogenic to humans,” and “biofilm claims are considered to be public health claims for which the agency must review and approve appropriate efficacy data.” EPA states: “Examples of use sites that may be supported by the biofilm test methodologies herein, and found acceptable, include restrooms, shower stalls, sink basins or drains (excluding the drain pipe) and nearby hard, non-porous surfaces of walls, countertops, and instrument trays in patient care areas of hospitals. In contrast, claims against non-public health slimicides must also be supported by appropriate efficacy data, however, submission of the data is only required when requested by the EPA.”
The Draft Guidance also sets forth examples of acceptable label claims against public health biofilms and acceptable non-public health claims. The examples of acceptable label claims against public health biofilms are:
- Kills 99.9999% of bacteria* in biofilm on a hard, non-porous surface;
- Kills a minimum of 99.9999% of bacteria* in biofilm;
- Reduces at least 99.9999% of bacteria* growing in biofilm;
- Formulated to kill 99.9999% of bacteria* in biofilm;
- Other related claims:
- Kills biofilm bacteria*; and
- Penetrates biofilm, killing the bacteria* living there.
*[List of bacteria “tested as a biofilm”; at a minimum, Pseudomonas aeruginosa and Staphylococcus aureus].
Examples of acceptable non-public health claims supported by appropriate efficacy data include:
- Cleans away microorganism slime/grunge;
- Maintains control of slime; and
- Controls slime-forming microorganisms.
Comments will be accepted until December 5, 2016.
By Lisa M. Campbell and Lisa R. Burchi
The California Department of Pesticide Regulation (DPR) recently proposed a regulation that it states is intended to “(1) provide minimum statewide standards for all agricultural pesticide applications near public K-12 schools and child day care facilities; (2) provide an extra margin of safety in case of unintended drift or when other problems with applications occur (e.g., equipment failure causes an unintended release of pesticide, or an abrupt change in weather conditions); (3) increase communication between growers and schools/child day care facilities; and (4) provide information to assist schools and child day care facilities in preparing for and responding to pesticide emergencies.”
This proposal has been long anticipated, is far reaching, and of significant concern to many growers and registrants.
In its Initial Statement of Reasons, DPR summarizes the proposed regulations, stating that they will: “require growers to notify public K-12 schools, child day care facilities (except family day care homes), and county agricultural commissioners when certain pesticide applications made for the production of an agricultural commodity near a schoolsite are planned in the coming year and also a few days prior to the applications.” The proposed regulation also would prohibit at certain times certain pesticide applications near these schoolsites. Specifically, the regulation is proposed to do the following:
- Prohibit many pesticide applications for the production of an “agricultural commodity” within a quarter mile of schoolsites from Monday through Friday between 6:00 a.m. and 6:00 p.m. “Schoolsites” are defined by Education Code section 17609(f) as: “‘any facility used as a child day care facility, as defined in Section 1596.750 of the Health and Safety Code, or for kindergarten, elementary, or secondary school purposes. The term includes the buildings or structures, playgrounds, athletic fields, vehicles, or any other area of property visited or used by pupils.” ‘Schoolsite’ does not include any postsecondary educational facility attended by secondary pupils or private kindergarten, elementary, or secondary school facilities.” DPR also proposed to exclude from the definition of schoolsite any family day care homes “because, unlike other schoolsites, the locations of these facilities are not publically available.” DPR states it considered other distances but proposed the one-quarter mile radius based on several factors, including but not limited the fact that this restriction is similar to the restrictions on fumigant labels that prohibit closer applications around schools and other difficult to evacuate sites and based on an analysis of pesticide illnesses due to drift from agricultural applications. The proposed prohibition would apply to applications by aircraft, sprinkler chemigation equipment, air-blast sprayers, and fumigant applications. In addition, dust and/or powder pesticide applications would also be prohibited during this time unless applied as a dust or powder using field soil injection equipment.
- Require California growers and pest control contractors to notify public K-12 schools and child day-care facilities and county agricultural commissioners (CAC) when certain pesticide applications are made within a quarter mile of these schools and facilities.
Under the proposed regulation, California growers would be required to provide two types of notifications to a school or child day-care facility:
An annual notification that lists all the pesticides expected to be used during the upcoming year. This must be provided to the school or child day care facility administrator by April 30 each year. The notice must include, among other things:
The name of pesticide products (and the main active ingredient) to be used;
A map showing the location of the field to be treated;
Contact information for the grower/operator and the County Agricultural Commissioner; and
The web address for the National Pesticide Information Center where additional sources of information or facts on pesticides may be obtained.
An application-specific notification which must be provided to the school or child day-care facility 48 hours before each application is made. This begins January 1, 2018, and must include, among other things:
- Name of pesticide products (and the main active ingredient) to be used;
- Specific location of the application and the number of acres to be treated; and
- Earliest date and time of the application.
Comments on the proposed regulation are due by November 17, 2016. DPR states that a final regulation is expected to become effective in September 2017.
Many have concerns with the proposed regulation, which DPR has been discussing publicly for some time. These concerns include what many believe are significant economic impacts to growers and others that they believe may not have been adequately considered and are not necessary for appropriate use of registered pesticides. Registrants and others should review the proposal carefully.
By Lisa M. Campbell and Lisa R. Burchi
The following documents have been filed in the Anderson v. McCarthy proceedings in the U.S. District Court for the Northern District of California: (1) U.S. Environmental Protection Agency’s (EPA) Notice of Motion and Motion for Summary Judgment; (2) Defendant-Intervenors CropLife America, et al.’s Notice of Motion and Motion for Summary Judgment; and (3) Plaintiffs’ Memorandum of Points and Authorities in Support of Motion for Summary Judgment.
EPA’s documents are of particular interest to those who have been following this case and are concerned about the assertions in the case regarding the treated article exemption. In its motion, EPA argues that the Ninth Circuit lacks jurisdiction to hear Plaintiffs’ claims, as the “EPA guidance document they challenge is not a judicially reviewable agency action -- much less a final action -- regarding the regulatory status of treated seed,” and Plaintiffs “have not identified any discrete, mandatory duty or action that EPA has failed to perform under [the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA)].”
EPA’s main arguments in support of its motion include:
- Plaintiffs have not identified any final agency actions. The Inspection Guidance is not an agency action, and even if the Inspection Guidance were an agency action, it is not final.
- Count II (Plaintiffs’ allegation of EPA’s failure to regulate and enforce FIFRA with respect to pesticide-treated seeds) must be dismissed because there is no nondiscretionary duty identified by Plaintiffs that is unreasonably delayed or unlawfully withheld.
- Enforcement of FIFRA is a discretionary action not subject to review.
In its motion, Defendant-Intervenors argue: “Each of Plaintiffs’ claims constitutes an impermissible programmatic attack on EPA’s existing pesticide regulatory program --specifically, the interplay between EPA’s regulation of pesticides registered to be applied as seed treatments and what Plaintiffs characterize as its categorical application of the treated article exemption to the treated seed. As a result, each of these claims is non-justiciable as a matter of law, entitling Defendants to summary judgment in their favor.” Defendant-Intervenors note that pesticides used for seed treatments are subject to “rigorous, scientifically robust review and approval under FIFRA,” making Plaintiffs’ attempt to impose a regulatory process “entirely duplicative of EPA’s existing exercise of its authority under FIFRA, while having no impact on human health or environmental safety.”
Plaintiffs’ memorandum sets forth its arguments for why the court should “find in favor of Plaintiffs on their four claims for relief: that EPA failed to enforce FIFRA against an entire class of pesticides; that EPA improperly amended the treated article exemption without following proper [Administrative Procedure Act (APA)] rulemaking procedures; that EPA’s exemption of neonicotinoid-coated seeds was ultra vires and/or arbitrary and capricious under the APA; and that EPA’s labeling requirements for unregistered pesticide-coated seed bags was arbitrary and capricious under the APA and FIFRA.” Specifically, Plaintiffs address why they believe EPA has failed to enforce FIFRA against neonicotinoid-coated seeds, why this asserted failure amounts to what they believe is “an unlawful abdication of [EPA’s] statutory responsibilities” and why they believe “EPA’s failure to enforce FIFRA against neonicotinoid-coated seeds and pesticidal dust-off is a ‘consciously and expressly adopted general policy,’ which ‘amounts to an abdication of its statutory responsibilities’ that this Court has the power to remedy.”
A hearing on EPA’s motion was set for October 27, 2016, but due to scheduling conflicts has been rescheduled for November 3, 2016. It will be important to monitor the court’s consideration of these important issues closely. More information on these proceedings can be found in our pesticide blog items District Court Declines to Rule on Jurisdictional Issues in Neonicotinoid Case until Summary Judgment and EPA Requests Dismissal of Complaint For Lack of Subject Matter Jurisdiction.
By Lisa R. Burchi and Zameer Qureshi
On August 23, 2016, the European Chemicals Agency’s (ECHA) Board of Appeal (BoA) adopted its first decision on a data sharing dispute under the Biocidal Products Regulation (BPR).
Thor GmbH (Thor) lodged the appeal in 2015 after ECHA granted permission to a company to cite studies owned by Thor for the substance reaction mass of 5-chloro-2-methyl-2H-isohtiazol-3-one and 2-methyl-2H-isothiazol-3-one (CIT/MIT). According to ECHA, Thor had insisted on a technical equivalence assessment of its substance with the other company’s active substance to check if the companies’ substances had similar chemical composition and hazard profiles. ECHA stated this was not required under BPR and data owners “do not have the right to demand any form of similarity check as a prerequisite for getting a letter of access.”
The BoA ruled in favor of Thor, which raised five pleas in law, as the companies had mutually agreed to perform a technical equivalence assessment before sharing data. The BoA concluded that while ECHA “might be correct” in concluding that the technical equivalence assessment is not a legal requirement for data sharing under BPR, “this legal observation cannot constitute an assessment of the parties’ efforts to reach an agreement within the meaning of Article 63.” The BoA stated “it is part of the Appellant’s and the prospective applicant’s contractual freedom to insert a clause relating to a technical equivalence assessment in the data sharing agreement.”
The BoA also reviewed the negotiations between the parties to determine whether those parties make every effort to reach an agreement, and found that ECHA “did not consider all the relevant facts in a balanced manner when assessing whether every effort had been made by Appellant and the prospective applicant under Article 63.” The BOA found that ECHA disregarded some of Thor’s efforts based on its legal conclusion that there was no need to perform a technical equivalence assessment. Consequently, the BoA concluded that Thor had made every effort to reach an agreement with the other company and ECHA had failed to consider all the facts of the case.
Although ECHA’s decision was annulled, there remains a question whether a new decision is required. Since the BoA’s decision, the prospective applicant submitted a successful application under Article 95, which may negate the need for the prospective applicant to cite to Thor’s data. The case was remanded to ECHA to determine whether a new decision is required.
By Zameer Qureshi
The fourth Biocides Stakeholders’ Day took place on September 1, 2016, at the European Chemicals Agency’s (ECHA) headquarters in Helsinki, Finland. The event provided biocides stakeholders with information on the Biocidal Products Regulation (BPR) and the tools and support available. The focus was on experiences from companies, ECHA, and the European Commission (EC). ECHA stated “[t]he objective was to equip companies with information about their roles and obligations to meet the legal requirements for biocides.”
The program for the event included three plenary sessions. Plenary Session 1, “Challenges and Opportunities,” was commenced by ECHA’s Executive Director, Geert Dancet. Topics discussed in Plenary Session 1 included a “[r]egulatory update from the [EC],” “[a]ctivities in 2016,” and “Union [Authorization] in Practice.” Plenary Session 2 focused on “IT Tools and Dossier Preparation,” and included discussions on IUCLID 6 and R4BP 3. IUCLID 6 is used to collect, organize, and store data on active substances and biocidal products. Dossiers generated through IUCLID 6 are submitted to ECHA and national authorities through R4BP 3, “the central hub through which all biocides applications are made.” Plenary Session 3 on the “Enforcement of Biocidal Products” consisted of discussions on enforcement by the EC and Member States, and closed with a case study on “Enforcement from an Industry Perspective.”
The Plenary Sessions were followed by Questions and Answers, closing remarks from Jack De Bruun, ECHA’s Director of Risk Management, and an opportunity for attendees to meet the ECHA staff.
By Lisa M. Campbell, Lisa R. Burchi, and Timothy D. Backstrom
On September 19, 2016, the U.S. Environmental Protection Agency’s (EPA) Office of Inspector General (OIG) issued a report, EPA Needs a Risk-Based Strategy to Assure Continued Effectiveness of Hospital-Level Disinfectants, the result of OIG’s review of EPA’s Antimicrobial Testing Program (ATP) to “determine whether the program ensures the efficacy of EPA-registered hospital sterilants, disinfectants, and tuberculocides (“hospital-level disinfectants”); and to evaluate options for improving the ATP.” OIG found that the ATP “does not assure that hospital-level disinfectant products continue to be effective after they are registered,” specifically that:
- Once the EPA tests a product and it passes, it is listed as Agency Confirmed Efficacy on the agency’s website and is typically not tested again; the long-term efficacy of the product cannot be assured.
- EPA relies on manufacturers to voluntarily submit product samples for testing. In the last three years, out of the approximately 300 registered hospital disinfectant products that have not been tested, manufacturers submitted only 12 samples to EPA for ATP efficacy testing.
Importantly, however, OIG concludes: “Although the program as currently designed and conducted does not assure that most hospital disinfectant products continue to be effective, at this point it is redundant and unnecessary to make adjustments, since the EPA is concurrently having the products re-registered.”
OIG makes two major recommendations:
- EPA should suspend administering the current Antimicrobial Testing Program until completion of the one-time re-registration process.
- EPA should develop a risk-based antimicrobial testing strategy to assure the effectiveness of public health pesticides used in hospital settings once products are in the marketplace. At a minimum, OIG states, the strategy should:
- Include a framework for periodic testing to assure products continue to be effective after registration.
- Define a program scope that is flexible and responsive to current and relevant public health risks.
- Identify risk factors for selecting products to test.
- Identify the method to be used for obtaining samples for testing.
- Designate a date to commence risk-based post-registration testing.
In its response, EPA agreed with OIG’s recommendations, and stated it will develop a plan to coordinate and implement the discontinuation of the present-day program, with the closure of the ATP program to take place by November 2017. EPA also stated that by December 2018 it plans to develop a risk-based strategy to assure the effectiveness of public health pesticides used in hospital settings once products are in the marketplace.
Registrants of the affected products should monitor closely the development of EPA’s plans both to discontinue the program and to establish this new risk-based strategy for assuring product efficacy.
By Lisa M. Campbell, Lisa R. Burchi, and Margaret R. Graham
On September 16, 2016, the U.S. Environmental Protection Agency (EPA) announced it settled an enforcement matter with Syngenta Crop Protection, LLC (Syngenta or Respondent) via a Consent Agreement and Final Order (CAFO) concerning EPA’s allegations that Syngenta violated the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA) and EPA’s Pesticide Container and Containment Rule (PCCR). The investigation took place over three years, starting in August 2012 and concluding in January 2015. The multi-regional investigation which took place over three years, from August 2012 to January 2015, was conducted by EPA Regions 4, 5, 7, and 8, and found violations in six states: Ohio, Colorado, Iowa, Kansas, Michigan and Missouri.
The CAFO listed the alleged violations in three parts:
- Failure to have repackaging agreements and failure to maintain records concerning the repackaging agreements: In the CAFO, EPA states that it identified numerous and separate occasions when Respondent distributed or sold approximately 19 registered pesticides to approximately 222 refillers “prior to having written repackaging agreements in place with such refillers,” “and/or failed to maintain records of the repackaging agreements with the refillers.” The requirements for such agreements and record keeping are set forth at 40 C.F.R. §§ 165.67(b)(3), 165.67(d), and 165.67(h).
- Distribution and sale of misbranded pesticides: In the CAFO, EPA states that at least seven inspections conducted at different facilities that were refillers of Respondent’s pesticides found pesticides affixed with outdated labels, as well as sales of such products with outdated labels. EPA states that Syngenta was the registrant of all the products at issue and had provided the refillers with the outdated labels for repackaging the pesticide products in refillable containers or bulk tanks on at least 19 separate occasions.
- Failure to maintain data submitted for pesticide registration: In the CAFO, EPA states it conducted an inspection at two laboratories to review compliance with Good Laboratory Practice requirements, and to audit the data for studies submitted by Respondent to EPA to support one of its pesticide registrations. In both cases, Respondent informed EPA that it did not maintain records or raw data associated with the studies and the laboratories confirmed they did not maintain the records at their facilities.
Syngenta neither admits nor denies these allegations, but has agreed to pay a civil penalty of $766,508, as well as to complete an environmental compliance promotion Supplemental Environmental Project (SEP) within four years at a cost of not less than $436,990. Specifically, the SEP will involve a four-year educational awareness training and campaign to educate the regulated community on FIFRA regulatory compliance requirements pertaining to the PCCR. The training will focus on the requirements relevant to bulk pesticide containers, containment, labels, storage, transportation, delivery, clean-out, repackaging agreements, and recordkeeping. The training is intended to increase awareness across a broad array of businesses that handle pesticides, including registrants, refillers, retailers, commercial applicators, and custom blenders of pesticides.
EPA states that the settlement sends “a strong message to pesticide companies to maintain compliance with all federal environmental laws.” Indeed, the breadth of EPA’s investigation and the ultimate size of the penalty signify EPA’s focus on pesticide violations and, particularly, misbranded pesticides. EPA in recent years has focused on labeling violations between registrant and supplemental distributor labels and the issues in this case have some similarities, particularly the need for written contacts between registrants and refillers or supplemental distributors, and also the need to ensure that current pesticide labels are provided before repackaging and relabeling take place.
More information concerning supplemental distributors and repackaging is available in our blog item Registrants Penalized for Actions of Third-Party Pesticide Distributor, our memorandum EPA’s Enforcement Efforts Regarding FIFRA Supplemental Distribution and How to Avoid Noncompliance and in the materials from our webinar EPA's Supplemental Distribution: Enforcement Actions Are Buzzing: How to Avoid Getting Stung.
By Lisa R. Burchi and Margaret R. Graham
On September 2, 2016, the U.S. Environmental Protection Agency (EPA) issued guidance to registrants on the process for making claims against emerging viral pathogens not on EPA-registered disinfectant labels (Guidance). A draft of this guidance was issued in April 2016 and comments were sought at that time. More information concerning the draft guidance is available in our blog item EPA Combats Emerging Pathogens Through Updating Guidance for Antimicrobial Pesticide Products.
The current Guidance document, which EPA states “provides general guidance to registrants that can be used to identify effective disinfectant products for use against emerging viral pathogens and to permit registrants to make limited claims of their product’s efficacy against such pathogens,” includes changes incorporated following EPA’s review of the three public comments received in response to that draft.
The Guidance retains the voluntary two-stage process, but amends the first stage as indicated:
- In the first stage, which may be performed prior to any outbreak, registrants with an eligible disinfectant product may submit a request, via label amendment or during the registration of a new product, to control a specific emerging viral pathogen to add a designated statement to the master label and additional terms to the product registration. If the product meets the eligibility criteria suggested in this Guidance, [EPA] generally will approve the amendment. Approval of the amendment would include additional terms and conditions of registration regarding how the designated statement may be published and communicated.
In its response to comments document, EPA responded to several comments, including:
- Changes were made to EPA’s mandated non-label statements to remove certain language that could be considered redundant.
- EPA is developing a coordinated process with the Centers for Disease Control and Prevention for the purpose of providing a more standardized and consistent approach to emerging viral pathogen outbreaks. Once this process is established, the agency expects to consult with the U.S. Department of Agriculture to develop a similar approach.
- The Guidance document allows for the addition of emerging pathogen claim language to the master label during the new product registration process if the product is eligible. Additional language has been added to multiple locations in the Guidance document to clarify that the process is appropriate for new product registrations.
- EPA “may consider allowing use of additional modes of claim communication under future versions of this Guidance document, however, hangtags and other promotional materials are not authorized at this time. Because the statements authorized under this Guidance are pesticidal claims that do not meet the FIFRA registration criteria, it is essential that these off-label claims are not made outside of an emerging pathogen outbreak as described in the Guidance. Accordingly, the Guidance limits these off-label claims primarily to communications outlets that are wholly within the registrant’s control (800 numbers, social media and websites) from which the off-label claims can be immediately removed. Hangtags and other promotional materials directed towards general consumers are largely out of the registrant’s control once the products enter the chain of commerce, and may persist long after the period during which the off-label claims are authorized.”
EPA also notes that this Guidance document “provides general guidance to EPA, pesticide registrants, applicants for pesticide registrations, and the public. This guidance is not binding on EPA or any outside parties, and EPA may depart from the guidance where circumstances warrant and without prior notice.”