By Lara A. Hall, MS, RQAP-GLP and Barbara A. Christianson
On December 17, 2019, the U.S. Environmental Protection Agency (EPA) will host its first annual conference in Washington, D.C., to discuss alternative test methods and strategies to reduce animal testing. EPA states that its conference “will bring together some of the leading voices in environmental and health research to discuss efforts to reduce testing on mammals.” The conference will focus on the New Approach Methods (NAM), which include “any technologies, methodologies, approaches or combinations thereof that can be used to provide information on chemical hazard and potential human exposure that can avoid or significantly reduce the use of testing on animals,” and will have U.S. and international scientific experts present information on advancements in the field. On-site participants attending the conference will have an opportunity to exchange information about scientific advancements in the NAMs field to develop a better understanding of the state of the science, discuss approaches for developing scientific confidence in using alternatives, and summarize existing studies characterizing the uncertainties in results from animal testing.
This conference is part of Administrator Wheeler’s “Directive to Prioritize Efforts to Reduce Animal Testing,” issued on September 10, 2019, which outlines EPA’s pursuit to aggressively reduce animal testing. In his directive, Administrator Wheeler calls for EPA to reduce its requests for, and funding of, mammalian studies by 30 percent by 2025 and eliminate all mammalian study requests and funding by 2035. Any mammalian studies requested or funded by EPA after 2035 will require Administrator approval on a case-by-case basis. The directive also supports scientific advancements that allow scientists to predict potential hazards for risk assessments without using traditional animal testing methods.
Information on how to register to participate in the conference by webinar is available here.
By Barbara A. Christianson and Heather F. Collins, M.S.
On September 24, 2019, the U.S. Environmental Protection Agency (EPA) announced the availability of the premises treatment final test guideline, under Series 810, Product Performance Test Guidelines. The guideline, 810.3500 Premise Treatment, provides recommendations on how to conduct efficacy testing against invertebrate pests in premises, such as cockroaches, ticks, mosquitoes, flies and wasps in connection with registration of pesticide products for use against public health pests. This guideline does not, however, apply to efficacy testing for treatment of livestock or pets, wide-area mosquito control, structural protection from termites, or bed bug products.
EPA states that “The final guideline clarifies the original guideline published in 1998 based on public comments and recommendations from the Federal Insecticide, Fungicide, and Rodenticide Act Scientific Advisory Panel (FIFRA SAP).”
Revisions to 810.3500 include
- Clarifying bait product testing;
- Offering more flexibility in testing design;
- Updating the replication recommendations based on statistical modeling and ease of obtaining pests; and
- Refining the statistical analyses recommendations.
Documents pertaining to the revision of the product performance guidelines, including public comment submissions, and the agency’s response to comments are available at www.regulations.gov in Docket Number EPA-HQ-OPP-2017-0693. More information on test guidelines is available on our blog.
By Lisa M. Campbell and Heather F. Collins, M.S.
On August 28, 2019, the U.S. Environmental Protection Agency (EPA) released the Frequently Asked Questions (FAQ) web resource for the Series 810 – Product Performance Test Guidelines: Antimicrobial Efficacy Test Guidelines. As of August 28, 2019, efficacy testing should be in compliance with the following Product Performance Test Guidelines published by EPA in February 2018:
- 810.2000: General Considerations for Testing Public Health Antimicrobial Pesticides, Guide for Efficacy Testing;
- 810.2100: Sterilants, Sporicides, and Decontaminants, Guide for Efficacy Testing; and
- 810.2200: Disinfectants for Use on Environmental Surfaces, Guide for Efficacy Testing.
The guidelines provide recommendations for the design and execution of laboratory studies to evaluate the effectiveness of antimicrobial pesticides against public health microbial pests. 83 Fed. Reg. 8666. EPA states that these FAQs “provide prompt and transparent guidance to all applicants regarding commonly asked questions concerning the 810 guidelines updated in February 2018.”
With the exception of confirmatory testing (as described under OCSPP guideline 810.2000, Section (B)(7)), all studies initiated on or after August 28, 2019, should be in compliance with the 2018 revised guidelines for testing. The study initiation date is defined under 40 CFR Part 160.3 as the date the protocol is signed by the study director. Studies that were initiated prior to the implementation date but submitted to EPA for review after the implementation date may use either the previous 2012 version of the guidelines or the 2018 revised guidelines, as appropriate. EPA states that it “intends to address confirmatory testing through a separate guidance, which will be made available for public comment prior to finalization.”
The FAQs include general testing questions and questions related to each specific guideline. The appendices to the FAQs include examples of label use-directions for dilutable products, repeat testing guidance with example scenarios, and sample virucidal calculations.
There has been some concern in the regulated community regarding the need for clarification on the guidelines before they became effective. EPA’s new FAQs are intended to provide these clarifications, but the timing of their issuance may be of concern to some. Also of interest is whether additional FAQs will be issued in the future.
By Lisa M. Campbell and Lisa R. Burchi
On November 21, 2018, in Court of Justice of the European Union (EU), the Fourth Chamber of the General Court (General Court/Fourth Chamber) issued a judgment in the appeal case T-545/11 RENV that denied all three pleas on appeal and prevented applicants Stichting Greenpeace Nederland and Pesticide Action Network Europe (Applicants) from receiving certain documents containing confidential information relating to the first authorization of the placing of glyphosate on the market as an active substance, specifically the complete list of all tests submitted by the operators seeking the inclusion of glyphosate in Annex I to Directive 91/414.
The judgment provides a detailed history of the case, beginning in 2010, when Applicants requested access to the documents in question. In this initial case, the Secretary General of the Commission agreed with the Federal Republic of Germany’s decision to refuse access to the documents (contested decision) on the basis that disclosure in Article 4(2) of Regulation No. 1049/2001 would undermine protection of the commercial interests of a natural or legal person. In upholding Germany’s decision, the Secretary General found that there was “no evidence of an overriding public interest in disclosure” within the meaning of Article 4(2) of Regulation No. 1049/2001, and also that the information “did not relate to emissions into the environment” within the meaning of Article 6(1) of Regulation No. 1367/2006 concerning public disclosure of information on the environmental effects of glyphosate. As such, “protection of the interests of the manufacturers of that substance had to prevail.”
The Applicants brought an action for annulment of the contested decision to the Registry of the General Court. After one of the documents at issue (a draft assessment report issued by Germany prior to the initial inclusion of glyphosate in Annex I to Directive 91/414) was produced to the court (but still not released to the Applicants), the General Court ruled to annul the contested decision. The Commission appealed this annulment, stating that the General Court erred in its interpretation of the term “information [which] relates to emissions into the environment.” The Court of Justice was persuaded by this argument, set aside the initial judgment, and referred the case back to the General Court. The case was then assigned to the Fourth Chamber. The dispute was limited to the part of the document at issue that “contains information on the degree of purity of the active substance, the ‘identity’ and quantities of all the impurities present in the technical material, the analytical profile of the batches, and the exact composition of the product developed.”
The Applicants put forward three pleas in law in support of their action. The pleas, and the basis for the General Court/Fourth Chamber’s rejections of those pleas, are as follows:
- Failure to Take Account of the Scope of Article 4(5) of Regulation No. 1049/2001: Article 4(5) of Regulation No. 1049/2001 provides that a Member State may request an institution not to disclose a document originating from that State without its prior agreement. Applicants submitted that Article 4(5) of Regulation No. 1049/2001 does not constitute a right of veto for a Member State and that the Commission may not rely on the Member State’s opinion regarding the application of an exception provided for by Article 4(2) of that Regulation. The General Court/Fourth Chamber stated that “the argument put forward cannot succeed, since Article 4(5) of Regulation No 1049/2001 is not the basis on which the Commission refused access to that document. Consequently, the first plea in law must be rejected.” Instead, Article 4(2) was the basis for Germany’s decision, and the Commission verified that Germany’s reasons for that decision were “prima facie, well founded.”
- Overriding Public Interest In Disclosing Information Relating to Emissions Into the Environment: Applicants maintained that the exception to the right of access designed to protect the commercial interests of a natural or legal person must be waived, because of an overriding public interest in disclosure of the information requested, which relates to emissions into the environment. Specifically, Applicants argued that information related to the identity and quantity of impurities present in glyphosate and related test information must be disclosed so that it could be determined “which toxic elements are emitted into the environment and are liable to remain there for some time.” With regard to the concept of “information relating to emissions into the environment,” the General Court/Fourth Chamber rejected arguments that the provision must be interpreted restrictively to mean only direct or indirect release of substances from installations. The General Court/Fourth Chamber also found, however, that the concept cannot be interpreted in a way that would “deprive of any practical effect the possibility” that a Member State could refuse to disclose environmental information or “jeopardise the balance which the EU legislature intended to maintain between the objective of transparency and the protection of [commercial] interests.” In rejecting the second plea, the General Court/Fourth Chamber states:
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. Accordingly, such information is excluded from the concept of “information relating to emissions into the environment,” in accordance with paragraph 78 of the judgement on appeal.
- Alleged Infringement of Article 4(2) of Regulation No. 1049/2001 and Article 4 of the Aarhus Convention: Applicants argued that the contested decision is not in accordance with Article 4(2) of Regulation No. 1049/2001 and Article 4 of the Aarhus Convention, on the ground that the Commission did not evaluate the actual risk of damage to the commercial interests invoked. The General Court/Fourth Chamber stated that it must be held “that the Commission correctly weighed up the relevant interests, having set out precisely and specifically the way in which the commercial interests of producers of glyphosate or plant protection products containing it would be jeopardised by the disclosure of the document at issue.”
After rejecting all three pleas, the General Court/Fourth Chamber held that the action must be dismissed in its entirety, and ordered Applicants to pay the costs relating to the various proceedings.
This case has been monitored closely because of the potential implications for companies that have submitted data or other information claimed as confidential that could be disclosed based on “overriding public interest.” The American Chemistry Council (ACC), CropLife America, CropLife International (CLI), the European Chemical Industry Council (Cefic), the European Crop Care Association (ECCA), the Association européenne pour la protection des cultures (ECPA) and the National Association of Manufacturers (NAM) all intervened in support of the form of the order sought by the Commission. The decision, and, in particular, the limitations placed on the scope of what is to be considered “information on emissions into the environment” provides helpful guidance and ensures that the exceptions provided for disclosure do not swallow the general rules under which institutions must refuse access to documents.
More information on glyphosate issues is available on our blog.
By Lisa M. Campbell and Timothy D. Backstrom
On December 6, 2018, the U.S. Environmental Protection Agency (EPA) announced it was proposing a rule (83 Fed. Reg. 62760) to harmonize the EPA-specific regulations regarding research involving human subjects conducted or sponsored by EPA or submitted to EPA for regulatory purposes with the revised regulations of the Federal Policy for the Protection of Human Subjects (Common Rule) issued on January 19, 2017 (82 Fed. Reg. 7149). Specifically, EPA is proposing to amend subparts C, D, K, and M of its regulations relating to human research. Subpart K, titled “Basic Ethical Requirements for Third-Party Human Research for Pesticides Involving Intentional Exposure of Non-Pregnant, Non-Nursing Adults,” contains the majority of the revisions. Subparts C and D will be revised to update several numerical citations and subpart M will be revised to correct a typographical error.
By way of background, the Common Rule governs research with human subjects conducted or supported by federal agencies, but EPA has also promulgated parallel requirements governing research conducted by third parties and then submitted to EPA for regulatory purposes. In particular, Subpart K addresses human research that may be conducted by third parties and then utilized to support registration of pesticides. Congress mandated various revisions to the Common Rule (including additional requirements for research involving pregnant women, fetuses, and children), and EPA is now modifying the EPA-specific requirements for human research to assure consistency and uniformity. These changes are also intended to assure that a single Institutional Review Board (IRB) review meeting the requirements of the Common Rule will be sufficient for any given study.
The proposed rule states that subpart K, “in establishing a process for review of third-party research involving intentional exposure of human subjects, borrows heavily from the provisions contained in the previous version of the Common Rule,” and that it will be revised to “maintain consistency of [IRB] review between agency-conducted or agency-sponsored human research and third-party human research.” EPA states the consequence of not resolving these discrepancies will be to “create confusion and, more seriously, potential compliance and/or legal liabilities for researchers, institutions, and sponsors who must follow EPA regulations.” Comments on the proposed rule are due by February 4, 2019.
Compliance with the revisions to the Common Rule originally was set for January 19, 2018, but it has been extended to January 21, 2019. The compliance date for the “cooperative research” Section remains January 20, 2020. This proposed rule to revise the requirements for third-party research submitted to EPA would not make substantive changes to the previously adopted final revisions to the Common Rule. The final rule states that cooperative research projects are “those projects covered by this policy that involve more than one institution,” any institution located in the United States that is engaged in cooperative research must “rely upon approval by a single IRB for that portion of the research that is conducted in the United States,” and the reviewing IRB “will be identified by the Federal department or agency supporting or conducting the research or proposed by the lead institution subject to the acceptance of the federal department or agency supporting the research.”
More information on the revision to the Common Rule is available in our blog item “Federal Agencies Announce Revision to Modernize Federal Policy for the Protection of Human Subjects” and on our blog under key phrase Common Rule.
By Lisa M. Campbell and Timothy D. Backstrom
In July 2018, the California Environmental Protection Agency’s Department of Pesticide Regulation (DPR), Human Health Assessment (HHA) Branch, issued its final toxic air contaminant (TAC) evaluation of chlorpyrifos. This final TAC evaluation updates the December 2017 draft evaluation of chlorpyrifos as a TAC for the Scientific Review Panel (SRP) which updated the August 2017 draft and was reviewed by the SRP on TACs, and incorporates certain changes based on SRP recommendations. As part of their review of the December 2017 draft, the SRP recommended “additional and detailed review of developmental neurotoxicity studies, in particular recent in vivo animal studies as well as a more in depth analysis of human effects of chlorpyrifos” and “that DPR reevaluate the critical endpoints, the associated [(uncertainty factors (UF)], and the resulting [reference concentrations (RfC)] and [reference doses (RfD)] for each endpoint.”
DPR determines that a pesticide is a TAC for a non-cancer adverse effect if the projected air concentrations associated with use of the pesticide are more than one tenth of the inhalation RfC established based on animal toxicity and epidemiology data. In the draft TAC evaluation for chlorpyrifos, DPR utilized the threshold for red blood cell acetylcholinesterase (AChE) inhibition in humans and a target margin of exposure (MOE) of 100, including a factor of 10 intended to account for potential neurodevelopmental effects below the threshold for RBC AChE inhibition. In the final TAC evaluation for chlorpyrifos, DPR increased the MOE for AChE inhibition to 300, based on deficiencies in the human inhalation parameters used to model the threshold for AChE inhibition.
In addition, the final TAC evaluation establishes a new No Observed Effect Level (NOEL) for neurodevelopmental effects in animal studies with chlorpyrifos reported at exposure levels well below the threshold for AChE inhibition. Based on this NOEL, DPR has derived a new inhalation RfC for neurodevelopmental effects, using a standard MOE of 100 consisting of 10X for interspecies sensitivity and 10X for intraspecies variability. This new inhalation RfC based on neurodevelopmental effects in animal studies is about one-half the revised inhalation RfC based on the threshold for AChE inhibition. Because the modeled spray drift air concentrations for chlorpyrifos are more than one tenth of this new inhalation RfC, DPR concludes “that chlorpyrifos meets the criteria to be listed as a TAC pursuant to the law of California.”
In the final TAC evaluation for chlorpyrifos, DPR concluded that there is sufficient evidence from animal studies to establish a new NOEL for neurodevelopmental effects, which is well below the level that has been shown to cause AChE inhibition in the same animals. Although the U.S. Environmental Protection Agency (EPA) has previously issued a determination that the default 10X safety factor for infants and children established by the Food Quality Protection Act (FQPA) should be retained for chlorpyrifos, this determination was based on epidemiology studies that purported to show adverse neurodevelopmental outcomes in humans at exposure levels below the threshold for AChE inhibition. The methodology used in these epidemiology studies has been harshly criticized by the pesticide industry. DPR views these epidemiology studies as providing corroboration, but the new DPR risk assessment is predicated instead on DPR’s view that animal studies with chlorpyrifos report neurodevelopmental effects below the threshold for AChE inhibition. The DPR risk assessment based on these animal studies uses a standard MOE of 100. How EPA may or may not view DPR’s conclusion is not known. In light of the August 9, 2018, decision by the U.S. Court of Appeals for the Ninth Circuit (Ninth Circuit) directing EPA to proceed with revocation of all tolerances and cancellation of all registrations for chlorpyrifos, the effect of the DPR conclusion on EPA actions is not clear. Nevertheless, it is worth noting that, because the mechanism by which chlorpyrifos would cause such neurodevelopmental effects is unknown and is below the level that causes AChE inhibition, any presumption by EPA that other organophosphate (OP) pesticides may cause the same type of effects will likely be vigorously disputed by industry on scientific grounds.
Please see our blog item Ninth Circuit Directs EPA to Revoke all Tolerances and Cancel All Registrations for Chlorpyrifos for more information on the Ninth Circuit’s August 9, 2018, decision.
By Timothy D. Backstrom and Lisa M. Campbell
On June 19, 2018, 16 federal agencies, including the U.S. Environmental Protection Agency (EPA), issued a final rule delaying until January 21, 2019, the general compliance date for 2017 revisions to the policy governing studies with human subjects that are sponsored or utilized for regulatory purposes by the federal government (83 Fed. Reg. 28497). These revisions to the human testing policy were adopted on January 19, 2017, in a final rule (82 Fed. Reg. 7149) that amended and expanded the “Common Rule” governing human testing originally promulgated in 1991. The 2017 revisions to the human testing policy were originally scheduled to take effect on January 19, 2018, but the agencies published an interim final rule on January 22, 2018, that delayed the effective date for the new policy until July 19, 2018. Thereafter, on April 20, 2018, the same 16 agencies published a proposed rule (83 Fed. Reg. 17595) to delay the general compliance date for an additional six-month period, and to allow regulated entities to implement certain burden-reducing provisions during this interim period.
The rule delaying the effective date of the 2017 revisions for an additional six months takes effect on July 19, 2018. In the period between July 19, 2018, and January 21, 2019, regulated entities must continue to comply with the requirements of the human testing policy as it was in effect prior to the 2017 revisions. Notwithstanding this general rule, affected institutions will be permitted (but not required) to implement, for certain research, three burden-reducing provisions. Those three provisions are:
- The revised definition of “research,” which deems certain activities not to be research covered by the Common Rule;
- The elimination of the requirement for annual continuing review with respect to certain categories of research; and
- The elimination of the requirement that institutional review boards (IRB) review grant applications or other funding proposals related to the research.
The principal purposes of the additional delay in implementation of the 2017 revisions to the human testing Common Rule are to allow more time for affected institutions to prepare for compliance and for the federal agencies that have adopted the new policy to issue further guidance. The final rule states that the agencies do not expect that any additional delay in the implementation of the policy will be needed.
More information on the federal policy for the protection of human subjects is available in our blog under key phrases human subjects and common rule.
By Carla N. Hutton
On April 10, 2018, the U.S. Environmental Protection Agency (EPA) announced the availability of a draft Science Policy document intended to reduce the use of animals in testing chemicals to evaluate whether they cause an allergic reaction, inflammation, or sensitization of the skin. According to EPA, the document, Draft Interim Science Policy: Use of Alternative Approaches for Skin Sensitization as a Replacement for Laboratory Animal Testing, “describes the science behind the non-animal alternatives that can now be used (in vitro, in silico, in chemico) to identify skin sensitization.” The draft Science Policy states that the Office of Pesticide Programs (OPP) and Office of Pollution Prevention and Toxics (OPPT) will immediately begin to accept submissions of new approach methodologies (NAM) and defined approaches (DA) as described in the draft Science Policy. EPA notes that there are multiple domestic and international activities ongoing that will allow for refinement and expansion of this draft Science Policy to other DAs and additional NAMs and support global harmonization of DAs for skin sensitization. According to the draft Science Policy, OPP and OPPT “will continue to be active participants in these activities to ensure regulatory acceptance and will continue to support cross-sector collaborations that enhance animal welfare, and accelerate the implementation of NAMs.” Comments on the draft Science Policy document must be submitted to Docket Number EPA-HQ-OPP-2016-0093 by June 9, 2018.
The draft Science Policy is the result of national and international collaboration between the Interagency Coordinating Committee on the Validation of Alternative Methods, the National Toxicology Program’s Interagency Center for the Evaluation of Alternative Toxicological Methods, the European Union Reference Laboratory for Alternatives to Animal Testing, and Health Canada’s Pest Management Regulatory Agency.
By Heather F. Collins, M.S. and Margaret R. Graham
On February 28, 2018, the U.S. Environmental Protection Agency (EPA) announced the availability of three Group B -- Antimicrobial Efficacy Test Guidelines, under Series 810, Product Performance Test Guidelines. The guidelines provide recommendations for the design and execution of laboratory studies to evaluate the effectiveness of antimicrobial pesticides against public health microbial pests. 83 Fed. Reg. 8666. The three final guidelines are:
EPA states these “test guidelines are 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. The test guidelines serve as a compendium of accepted scientific methodologies and protocols for testing that is intended to provide data to inform regulatory decisions.”
EPA issued draft guidelines in June 2015 and solicited comments. EPA states that some comments received on those draft guidelines have been incorporated into the final versions. EPA states that the revision “is more user friendly and clarifies topics such as confirmatory data, repeat testing, hard water formulation, wetness determination testing for towelettes, and internal toilet testing … [and] also includes information on supplemental testing policies such as lower certified limits, revision of the AOAC Use Dilution Method performance standards and clarified technical details for efficacy testing.”
Documents pertaining to the revision of the product performance guidelines, including public comment submissions, and the agency’s response to comments are available at www.regulations.gov, in Docket No. EPA-HQ-OPP-2015-0276. More information on test guidelines is available on our blog.
By Lisa M. Campbell, Lisa R. Burchi, and James V. Aidala
On February 1, 2018, the U.S. Environmental Protection Agency (EPA) announced it is publishing new guidance that sets forth a tiered approach intended to help manufacturers and EPA determine when the number of field trials necessary to register seed treatment uses can be reduced.
In its memo and attached Seed-Treatment Focus Group (STFG) Guidance Document dated January 26, 2018, EPA states that its Health Effect Divison (HED) has received “multiple waiver requests for seed-treatment field-trial residue data and has reviewed multiple field-trial datasets that indicated that there was the potential to reduce the number of field trials required to support the registration of seed-treatment uses.” EPA states that to evaluate this hypothesis, the HED Chemistry Science Advisory Council (ChemSAC), in collaboration with the Health Canada Pest Management Regulatory Agency (PMRA), in accordance with the July 11, 2017, Joint Canada/United States Field Trial Requirements “performed a retrospective analysis of all seed-treatment residue data that have been submitted to EPA/PMRA and has developed a tiered approach for determining if current crop-specific field trial data requirements are required to support new seed-treatment uses, or if a reduction in the number of required field trials is appropriate.” EPA’s announcement states that “the analysis showed that the data required to support registration could be substantially reduced and still be protective of human health.”
EPA developed two decision trees detailing the process for determining the residue chemistry field trial data requirements for seed-treatment uses: one for potato seed-piece (PSP) treatments only and another one for all remaining crops. EPA states that this case study demonstrates that application of the guidance set forth in these decision trees can, for both manufacturers and the agency, “potentially save considerable resources in terms of conducting, submitting, and reviewing the studies while still obtaining the data necessary to support seed-treatment pesticide registrations.”
The outlined procedure and memo document will supersede EPA’s previous guidance issued on October 28, 1999, entitled “Classification of Seed Treatments as Food or Nonfood Uses.”
More information is available on EPA’s Determining the Number of Field Trials Required to Register Seed-Treatment Uses webpage.
This announcement of improved review procedures allows EPA to cite both greater coordination across national borders (working with Canada), and reduce unnecessary data requirements. This would fit with the current Administration’s emphasis on reducing regulatory burdens and fostering greater innovation in regulated arenas. It also might be seen as general “good government,” as it updates guidance which is now almost twenty years old. Since seed treatment technology and associated policy issues have both evolved over the years, such a review and revision would seem timely regardless of any larger political directive.