By Heather F. Collins
On August 28, 2017, the U.S. Environmental Protection Agency (EPA) announced the first of three feature and functionality updates to the Pesticide Submission Portal (PSP) expected this year. The portal is a web-based application allowing registrants to submit pesticide application packages to EPA electronically. The PSP application is accessed through EPA’s Central Data Exchange (CDX) Network which requires user registration.
This new PSP, version 1.4, release expands the feature to allow users to submit voluntary data related to specific registration review cases. Users can submit study citations, data matrices (Form 8570-35), cover letters and studies (protocols, study profiles, supplemental study data) using the new "Voluntary Submission" link on the PSP home page. This new release also allows users to resubmit previously submitted 90-day responses. Once a 90-day response or data submission has been successfully transmitted to the Office of Pesticide Programs (OPP), users may now modify responses to data requirements, cite additional studies, upload additional documents, and change how the product registration is supported. EPA states: “This action is another step in a phased approach that will ultimately lead to EPA’s ability to accept all pesticide applications electronically, a move that will help modernize the pesticide registration process, increase operational efficiencies and reduce paper waste.” EPA indicates that in addition to these changes, this update introduces enhancements and bug fixes.
EPA also released the OPP Pesticide Submission Portal (PSP) User Guide Version 1.4 which provides detailed instructions on how to use the PSP application and guidance on how to prepare a package for electronic submission.
Applicants using PSP need not submit multiple electronic copies of any pieces of their applications; EPA states that the requirement to submit multiple copies of data in Pesticide Registration Notice 2011-3 is applicable only to paper submissions. Pesticide registrants who previously submitted information via paper, CD, or DVD may instead use the portal and forego the courier costs of sending to EPA.
More information about the Electronic Submissions of Pesticide Applications is available on EPA’s website.
By Sheryl L. Dolan and Margaret R. Graham
On August 1, 2017, the U.S. Environmental Protection Agency (EPA) announced the availability of two final test method Standard Operating Procedures (SOP) for evaluating the efficacy of antimicrobial pesticides against two biofilm bacteria, Pseudomonas aeruginosa (P. aeruginosa) and Staphylococcus aureus (S. aureus):
EPA also released regulatory guidance for test criteria and pesticide claims for these products, specifically Guidance for Testing the Efficacy of Antimicrobial Products Against Biofilms on Hard, Non-Porous Surfaces. Drafts of the SOPs and the guidance were initially released in October 2016 for comment. EPA received comments from nine entities and revised the drafts to incorporate suggested changes. EPA posted its response to those comments in Docket EPA-HQ-OPP-2016-0357.
EPA states that the two methods are adapted from ASTM International (ASTM) standard methods. EPA MLB SOP MB-19 is used to generate the P. aeruginosa or S. aureus biofilm on coupons. EPA MLB SOP MB-20, the Single Tube Method, then is used to determine the effectiveness of an antimicrobial product in reducing bacteria in biofilm on the coupons.
Notable aspects of the test criteria and claims guidelines include:
- The mean log density for the test organisms of 8.0 to 9.5 for P. aeruginosa and 7.5 to 9.0 for S. aureus; and
- Product performance criterion of a minimum 6-log reduction.
The guidance lists several examples of claims for efficacy against public health biofilm that EPA states are acceptable.
EPA MLB SOP MB-20 is designed to evaluate the efficacy of antimicrobial products that are water soluble powders or liquid formulations. If a company wishes to test a different type of product formulation, or test different target microorganisms, or make any other proposed modifications, it would be well advised to submit proposed alternatives to EPA for review and approval. EPA specifically cautions that the current methodologies are intended for data development to support claims for products registered for use on hard, non-porous surfaces and are not suitable for use sites associated with water systems.
The EPA’s Office of Pesticide Programs’ (OPP) regulation of biofilms has been the subject of increasingly intense commercial interest for years and the availability of this testing guidance is welcome news. While not all will agree with the approach, the new guidance is a helpful addition to OPP’s testing guidance portfolio.
More information on antimicrobial pesticides is available on our blog under key phrase Antimicrobial Pesticide. More information on the methods and guidance is available on EPA’s website and in Docket No. EPA-HQ-OPP-2016-0357.
By Lisa M. Campbell and Margaret R. Graham
On June 14, 2017, the U.S. Environmental Protection Agency (EPA) issued a Federal Register notice announcing the availability of a final test guideline, Laboratory Product Performance Testing Methods for Bed Bug Pesticide Products; OCSPP Test Guideline 810.3900, part of a series of test guidelines established by the EPA’s Office of Chemical Safety and Pollution Prevention (OCSPP) for use in testing pesticides and chemical substances. 82 Fed. Reg. 27254. EPA states that this test guideline provides “guidance for conducting a study to determine pesticide product performance against bed bugs, and is used by EPA, the public, and companies that submit data to EPA,” and “recommendations for the design and execution of laboratory studies to evaluate the performance of pesticide products intended to repel, attract, and/or kill the common bed bug (Cimex lectularius) in connection with registration of pesticide products under the [Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA)].” EPA states that this guidance applies to products “in any formulation such as a liquid, aerosol, fog, or impregnated fabric, if intended to be applied to have a pesticidal purpose such as to attract, repel, or kill bed bugs.” This guideline provides appropriate laboratory study designs and methods for evaluating the product performance of pesticides against bed bugs and includes statistical analysis and reporting.
EPA issued the draft guideline on February 14, 2012. This original document was the subject of FIFRA Scientific Advisory Panel (SAP) review conducted on March 6-7, 2012. EPA indicates that the final version of the guideline reflects revisions to the original draft based on comments from the SAP and the public. EPA states that the revisions include the following:
- Decreasing the number of individuals and replicates tested;
- Rescinding the recommendation to test each field strain for its resistance ratio; and including a resistance management statement;
- Clarifying the agency's Good Laboratory Practices (GLP) requirements;
- Reducing the recommended length of time individuals are exposed to insecticides;
- Recommending individuals to be observed up to 96 hours after treatment; and
- Revising the statistical analyses recommendations.
EPA has also placed two other relevant documents in the docket:
By Lisa M. Campbell, Lara A. Hall, and Margaret R. Graham
On May 8, 2016, the U.S. Environmental Protection Agency (EPA) announced its invitation for public input regarding the “Strategic Roadmap: New Approaches to Evaluate the Safety of Chemicals and Medical Products” (Roadmap), the development of which was coordinated by the National Toxicology Program’s (NTP) Interagency Coordinating Committee on the Validation of Alternative Methods (ICCVAM). ICCVAM states that the vision of the Roadmap is to “establish new approaches for evaluating the safety of chemicals and medical products in the United States that will increase confidence in alternative methods and improve their relevance to human health outcomes while maximizing efficiency and maintaining a commitment to replace, reduce, and refine animal use.” ICCVAM’s Roadmap effort was introduced in March 2016. A detailed presentation on the development of the Roadmap is available here.
ICCVAM, a permanent committee of the National Institute of Environmental Health Sciences (NIEHS) under the National Toxicology Program Interagency Center for the Evaluation of Alternative Toxicological Methods (NICEATM), is composed of representatives from 16 U.S. federal regulatory and research agencies that require, use, generate, or disseminate toxicological and safety testing information. As a participating member of ICCVAM, EPA states that its role is to “encourage the development and use of alternatives to animal test methods, ensure that new methods are valid, review test method recommendations, and as appropriate, adopt these alternatives in our own regulatory programs.”
There are also three upcoming public meetings that will provide additional opportunities to comment on topics relevant to this effort:
- ICCVAM Public Forum: May 23, 2017, National Institutes of Health (NIH), Bethesda, Maryland;
- NTP Board of Scientific Counselors meeting: June 29, 2017, NIEHS, Research Triangle Park, North Carolina; and
- Scientific Advisory Committee on Alternative Toxicological Methods meeting: September 18-19, 2017, NIH, Bethesda, Maryland.
As ICCVAM’s commitment to replace, reduce, and refine animal use continues to draw public comment and gain support, there is an increasing need to demonstrate the utility and harmonization of predictive approaches in toxicology testing with the conventional safety evaluation of chemicals and medical products. Bergeson & Campbell, P.C. (B&C®) continues to monitor the development, validation, and implementation of alternative in vitro and in silico test methods, high throughput screening assays, and computational models as they are integrated into global regulatory frameworks.
By Lynn L. Bergeson and Margaret R. Graham
On January 19, 2017, the U.S. Environmental Protection Agency (EPA), together with a host of other federal agencies, announced revisions via a final rule to modernize, strengthen, and make more effective the Federal Policy for the Protection of Human Subjects that was originally promulgated as a Common Rule in 1991. 82 Fed. Reg. 7151. The Federal Register publication states that this final rule is intended to “better protect human subjects involved in research, while facilitating valuable research and reducing burden, delay, and ambiguity for investigators, and “these revisions are an effort to modernize, simplify, and enhance the current system of oversight.” The rule will become effective on January 19, 2018. The compliance date is also January 19, 2018, with some exceptions.
The final rule differs in important ways from the proposed rule issued on September 8, 2015; most significantly, several proposals are not being adopted. Other minor changes have been to improve the rule and for purposes of clarity and accuracy. Some of the changes include:
- It does not adopt the proposal to require that research involving nonidentified biospecimens be subject to the Common Rule, and that consent would need to be obtained in order to conduct such research.
- To the extent some of the proposals relied on standards that had not yet been proposed, the final rule either does not adopt those proposals or includes revisions to eliminate such reliance.
- It does not expand the policy to cover clinical trials that are not federally funded.
- It does not adopt the proposed new concept of ‘‘excluded’’ activities. Generally, activities proposed to be excluded are now either described as not satisfying the definition of what constitutes research under the regulations or are classified as exempt.
- The proposed revisions to the exemption categories have been modified to better align with the longstanding ordering in the final rule. It does not include the proposed requirement that exemption determinations need to be made in specified ways.
- It does not include the proposed standardized privacy safeguards for identifiable private information and identifiable biospecimens.
- It does not adopt the most restrictive proposed criteria for obtaining a waiver of the consent requirements relating to research with identifiable biospecimens.
The final rule makes the following significant changes to the Common Rule:
- Establishes new requirements regarding the information that must be given to prospective research subjects as part of the informed consent process.
- Allows the use of broad consent (i.e., seeking prospective consent to unspecified future research) from a subject for storage, maintenance, and secondary research use of identifiable private information and identifiable biospecimens. Broad consent will be an optional alternative that an investigator may choose instead of, for example, conducting the research on nonidentified information and nonidentified biospecimens, having an institutional review board (IRB) waive the requirement for informed consent, or obtaining consent for a specific study.
- Establishes new exempt categories of research based on their risk profile. Under some of the new categories, exempt research would be required to undergo limited IRB review to ensure that there are adequate privacy safeguards for identifiable private information and identifiable biospecimens.
- Creates a requirement for U.S.-based institutions engaged in cooperative research to use a single IRB for that portion of the research that takes place within the United States, with certain exceptions. This requirement becomes effective three years after publication of the final rule.
- Removes the requirement to conduct continuing review of ongoing research for studies that undergo expedited review and for studies that have completed study interventions and are merely analyzing study data or involve only observational follow up in conjunction with standard clinical care.
More information on the Federal Policy for the Protection of Human Subjects is available on the U.S. Department of Health & Human Services’ website.
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 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 James V. Aidala
The threat of the Zika Virus grows every day, and the need for clear information is especially pressing if you are pregnant. How do you prevent getting infected with the Zika Virus, and what insect repellents are best? The first question is easy to answer: public health experts agree that women who are pregnant or who might be pregnant should use insect repellents. The answer to the second question is not so simple.
I am a former senior official at the U.S. Environmental Protection Agency (EPA), and familiar with how the U.S. evaluates and approves pesticides, which include insect repellents. It is not easy for the average consumer to know what works and what does not work. Unfortunately, EPA policies have made this question much more complicated, having made important distinctions between some “natural”-type repellents and other products available in the marketplace.
Years ago, EPA de-regulated a number of natural, non-toxic materials from being subject to the registration requirements of the federal pesticide law (the Federal Insecticide, Fungicide, and Rodenticide Act). This made sense at the time since garlic, pepper, rotten eggs, vinegar, and other common chemicals are sometimes used as pesticides. Before de-regulation, these products were also subject to the same requirements as synthetic chemical pesticides with long unpronounceable names (e.g., diethyltoluamide, better known as DEET) which EPA requires to have volumes of efficacy and safety test data. Being natural does not mean a substance is non-toxic; some natural ingredients are fully evaluated and widely used. But in the interest of efficient use of resources EPA issued a list of products that could be sold as pesticides, but would not be subject to EPA data requirements and review (EPA calls them “minimum risk pesticides”).
This list of pesticides which are not subject to EPA evaluation, and which are not required to have data which proves they are effective, includes a number of botanical ingredients, such as oil of citronella, geranium, rosemary, peppermint, and many others. Many of these products can be used as pesticides -- some may work better than others -- and many work for the intended use (example: rotten eggs, or as EPA refers to them -- “putrescent whole egg solids” -- are used as a deer repellent).
Many of these ingredients have been marketed as “natural” insect repellents, and labeled as “safe” or “non-toxic” using words that will not appear on products where EPA reviews and approves the instructions on the product label.
Here is the bureaucratic distinction which matters greatly to EPA, but will not be understood by consumers:
- If the repellant label includes “public health claims” -- that it repels mosquitoes that may cause a disease (like Zika Virus or West Nile Virus) -- then the product has to have data showing that it works;
- If the product just says “repels mosquitoes,” it is not required to have data that shows it is effective, and may very well be ineffective.
Few, if any, humans outside of EPA label experts realize this important distinction: if there is no health claim on the label, then it is, in effect, a situation of “buyer beware.”
What remains: EPA’s deregulation of these products means it is legal to sell products which do not work, as long as the ingredients appear on the EPA minimum risk pesticides list.
Consumer Reports (CR) recently reported in May of this year on studies conducted on repellents. Their results:
- Using a “natural” mosquito repellent, with active ingredients such as citronella or clove, lemongrass, or rosemary oils, might seem like a good idea, especially if you’re pregnant or planning to be.
- But five of the six plant-based repellents we tested…lasted one hour or less against Aedes mosquitoes, the kind that can spread Zika.
Not all repellents with the same ingredient are equally effective, and they found that some formulations of the chemical repellents also do not work for very long in their tests. Some botanical pesticides are effective and have the public health claims on the label (example: lemon eucalyptus, a botanical ingredient not on the exempt product list, and CR testing did find it to be effective).
To reduce confusion about what works, EPA for years has struggled to correct the situation by trying to impose changes to the requirements for insect repellents.
Unfortunately, to end the confusion about the difference between “repels mosquitoes” and “repels mosquitoes that can cause the Zika Virus,” EPA has to conduct a rulemaking which requires a long and bureaucratic process to complete. The good news is that EPA is working on such a solution. The bad news is that they have been working on it for almost ten years and they still have more work to do. There are details and petitions and proposals and reasons why it has taken so long, but it is the kind of story that gives bureaucracy a bad name.
With the onset and fears about the Zika Virus, however, EPA should make the needed changes immediately to ensure that consumers are not misled into using products which are not proven effective in repelling mosquitoes.
From a consumer’s point of view, it really is that simple. Legally, it is more complicated. In the meantime, EPA should be loud and clear in its communication about the distinction, even if they cannot take immediate action to reduce the confusion.
By Lisa M. Campbell and Timothy D. Backstrom
On March 8, 2016, the U.S. Environmental Protection Agency (EPA) published a notice in the Federal Register stating that the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA) Scientific Advisory Panel (SAP) will hold a three-day meeting scheduled for April 19-21, 2016, from 9:00 a.m. to 5:00 p.m. (EDT) to consider and review Chlorpyrifos: Analysis of Biomonitoring Data. The meeting will be held at EPA’s Conference Center, Lobby Level, One Potomac Yard (South Bldg.), 2777 S. Crystal Drive, Arlington, Virginia 22202. The meeting will be webcast. More information will be posted online.
The notice states that written comments are encouraged through April 5, 2016, and that requests for oral comments are encouraged to be submitted by April 12, 2016, but that both may be submitted until the date of the meeting. Nominations of candidates to serve as ad hoc members of FIFRA SAP for the meeting are requested on or before March 23, 2016.
In this meeting, EPA states that it will solicit comment from FIFRA SAP on the evaluation of biomonitoring data using the physiologically-based pharmacokinetic (PBPK) model, proposed points of departure and extrapolation/uncertainty factors, and examples of a proposed approach to use the PBPK model to simulate internal doses of chlorpyrifos from current exposure patterns from drinking water, food, and worker exposure. The FIFRA SAP has been reviewing the human health effects of chlorpyrifos since 2008. The notice states that “at this point in time, the Agency’s analysis of biomonitoring data from the cord blood collected as part of the Columbia University epidemiology studies has progressed to a point where peer review would be useful” and that “[s]pecifically, the Agency has done additional characterization of the pharmacokinetic profile of simulated exposures from oral and dermal exposures using the PBPK model.”
The notice states that in 2008 and 2012, the FIFRA SAP “cautioned EPA against using the biomonitoring data from epidemiology studies … to directly derive points of departure due to uncertainties associated with a lack of knowledge about timing of indoor chlorpyrifos applications and a single measure of exposure (cord blood).” The 2012 FIFRA SAP recommended that EPA use the PBPK model to further characterize the dose estimates in the epidemiology studies.
The notice states that EPA would have preferred to complete its analysis of the available biomonitoring prior to commencing rulemaking, but that the timing for the proposal was directed by the U.S. Court of Appeals for the Ninth Circuit, which ordered EPA to respond to an administrative petition to revoke all chlorpyrifos tolerances by October 31, 2015.
More information on the Ninth Circuit case is available in our blog item Circuit Court Grants Writ of Mandamus Requiring EPA to Act on Petition to Ban Chlorpyrifos.
EPA’s decision to utilize biomonitoring data that was collected as part of the Columbia University epidemiology studies for chlorpyrifos to derive proposed points of departure for risk assessment purposes will be highly controversial. If EPA proceeds to use biomonitoring data from epidemiological studies to derive points of departure for risk assessment purposes, the implications for all pesticide product risk assessments could be significant. Whether EPA can defensibly do so from both a scientific and legal standpoint is a subject that will likely be debated strongly. All pesticide registrants should monitor these developments closely.