
The National Toxicology Program Interagency Center for the Evaluation of Alternative Toxicological Methods (NICEATM) provides validation support for US Federal agencies and the US Tox21 interagency consortium, an interagency collaboration that is using high throughput screening (HTS) and other advanced approaches to better understand and predict chemical hazards to humans and the environment. The use of HTS data from assays relevant to the estrogen receptor signaling data pathway is used as an example of how HTS data can be combined with computational modeling to meet the needs of US agencies. As brief summary of US efforts in the areas of biologics testing, acute toxicity, and skin sensitization will also be provided.
Considerable worldwide interest exists in developing an understanding of how biologic pathways become engaged in toxicity responses. The intent is that knowledge about these pathways would lead to the development of predictive, integrated testing strategies that likely would combine in silico approaches and multiple in vitro or high-throughput assays with limited, targeted testing in laboratory animals. There are various statistical approaches to assembling components of a ‘most predictive’ test battery as well as different statistical models for integrating all relevant information and assay results. Both the batteries and models as alternative methods may warrant consideration by U.S. agencies. In addition, numerous efforts are underway to develop in silico and in vitro approaches for screening and prioritization of chemicals for testing. Ultimately, the application of these alternative methods may differ (regulatory testing for safety evaluation or risk assessment compared with screening or prioritization), and as such, the concept of validation in the context of use needs to be considered. US agencies intend to engage the public in discussions about the concept of validation and its role in this new paradigm. In the future, more complex batteries of tests that evaluate systemic toxicity will need to be assembled. As a consequence, US agencies will place less emphasis on replacement of in vivo toxicity endpoints with a single alternative assay and more emphasis on assembling batteries of assays and including in silico approaches to interpret and analyze data from such batteries. In addition to changing the concept of validation, agencies anticipate that reevaluating standing policy in response to new data could substantially affect the number of animals used for regulatory safety testing.
In 2000, the ICCVAM Authorization Act established the Interagency Coordinating Committee on the Validation of Alternative Toxicological Methods (ICCVAM) as a permanent interagency committee of the NIEHS under NICEATM (1). ICCVAM is composed of representatives from 15 U.S. Federal agencies (Consumer Product Safety Commission, Department of Agriculture, Department of the Interior, Department of Transportation, Environmental Protection Agency, Food and Drug Administration, and Occupational Safety and Health Administration, Agency for Toxic Substances and Disease Registry, National Institute for Occupational Safety and Health, National Cancer Institute, National Institute of Environmental Health Sciences, National Library of Medicine, National Institutes of Health, Department of Defense, and Department of Energy) that require, use, generate or disseminate toxicological and safety testing information. ICCVAM’s mission is to “facilitate development, validation, and regulatory acceptance of new and revised regulatory test methods that reduce, refine, and replace the use of animals in testing while maintaining and promoting scientific quality and the protection of human health, animal health, and the environment.” ICCVAM relies on stakeholders to carry out research, development, and validation, providing guidance to test method developers where needed. As such, ICCVAM does not carry out validation studies on behalf of test method developers, but evaluates alternative toxicological test methods submitted by stakeholders and reviews validation data, organizes expert peer reviews of promising methods, and makes recommendations on the use of reviewed test methods to appropriate U.S. Federal agencies. To optimize utilization of resources and avoid duplication of effort, ICCVAM coordinates test method evaluation activities with ICATM partner organizations (currently Korea, Japan, European Union, and Canada). International collaboration is also facilitated through ICCVAM agency participation in the Organization for Economic Cooperation and Development (OECD). Broader engagement with the scientific community and stakeholders is achieved through focused workshops, webinars and face-to-face forums.
The NTP Interagency Center for the Evaluation of Alternative Toxicological Methods (NICEATM) is part of the National Institute of Environmental Health Sciences (NIEHS). NICEATM activities support the development and evaluation of new, revised, and alternative methods to identify potential hazards to human health and the environment, with a focus on replacing, reducing, or refining animal use. NICEATM activities include:
Conducting and publishing analyses and evaluations of data from new, revised, and alternative testing approaches
Providing information to test method developers, regulators, and regulated industry through this Website and other communications and by organizing workshops and symposia on topics of interest
Supporting the Interagency Coordinating Committee on the Validation of Alternative Methods (ICCVAM)
It is important to note the distinction in the roles of ICCVAM and NICEATM; ICCVAM is responsible for determining the relevance and priority of test method nominations, whereas NICEATM conducts their scientific review by making use of its competencies in validation study design, computational toxicology, chemoinformatics, data management and data analysis.
Tox21 is a multiagency collaboration that includes NIEHS-NTP, the NIH’s National Center for Advancing Translational Sciences, the EPA’s National Center for Computational Toxicology, and the Food and Drug Administration. The objective of this partnership is to shift the assessment of chemical hazards away from traditional laboratory animal toxicology studies to an evaluation based on target-specific, mechanism-based, biologic observations largely obtained by using in vitro assays, with the ultimate aim of improving risk assessment for humans and the environment. Tox21’s strategy is to use in vitro high-throughput and high-content screening technologies to test a broad variety of approximately 10,000 substances and consider data from those screens collectively to assess effects on biologic pathways related to toxicity. Data from Tox21 testing will be used to develop a better understanding of these toxicity or ‘adverse outcome’ pathways (AOPs), ideally enabling the eventual use of in vitro assay data to predict the adverse effects of chemical exposures in vivo. More information about Tox21 can be found on the NTP website (
Beginning in 2013, NICEATM expanded its activities beyond ICCVAM. In her Environmental Health Perspectives editorial NIEHS and NTP Director Linda Birnbaum enlarged the scope of NICEATM to include providing bio-informatic and computational toxicology support to the interagency Tox21 effort (2). The intent was to position NICEATM in a bridging role between ICCVAM and Tox21. These organizations are working together to promote more efficient approaches to develop and validate methods that employ the 3Rs, and they are exploring options that would allow these methods to be expeditiously accepted by regulators and used by stakeholders.
The International Cooperation on Alternative Test Methods (ICATM) ICATM was established in 2009 to promote consistent and enhanced voluntary international cooperation, collaboration, and communication among national validation organizations. The goals of ICATM are to: 1) ensure the optimal design and conduct of validation studies; 2) ensure high-quality independent scientific peer reviews of alternative test methods; 3) ensure consistent and transparent stakeholder involvement; 4) achieve greater efficiency and effectiveness by internationally leveraging limited resources and avoiding duplication of effort; and 5) support the timely international adoption of alternative test methods. This cooperation enables scientifically valid alternative methods or strategies to be more readily accepted worldwide for regulatory use. In addition to ICCVAM, the current ICATM partner organizations are The European Union Reference Laboratory for Alternatives to Animal Testing (EURL_ECVAM); The Japanese Center for the Validation of Alternative Methods (JaCVAM); Health Canada’s Environmental Health Science and Research Bureau; and The Korean Center for the Validation of Alternative Methods (KoCVAM).
The US EPA’s Endocrine Disruptor Screening Program (EDSP) was established in 1999 for the purpose of evaluating potential risk of endocrine disruption in humans and wildlife from exposure to pesticide chemicals and drinking water contaminants. To screen chemicals for potential endocrine bioactivity, EPA developed a battery of five in vitro and six in vivo Tier 1 screening assays1. In response to the US National Academy, of Sciences report, Toxicity Testing in the 21st Century (3), EPA began a transition from existing EDSP test methods towards utilizing more rapid, cost-effective computational models and high-throughput assays. EPA’s Toxicity Forecaster (ToxCast) program generates data on ~2000 chemicals of interest to the EPA. ToxCast uses high-throughput screening methods and computational toxicology approaches to rank and prioritize chemicals. EPA’s Endocrine Disruption Screening Program (EDSP) is now using ToxCast data to rank and prioritize chemicals based on their potential ER bioactivity, serving as an alternative for some of the existing EDSP Tier 1 in vitro and in vivo assays (4).
In order to use new computational toxicology approaches in the existing EDSP screening and testing framework, the new approaches must be validated and perform as well or better than existing methods currently in practice. The validation of the new screening approach for ER bioactivity is briefly described here. High-throughput in vitro screening assay data from 16 different ER-based assays in the EPA’s ToxCast program were integrated into a computational model of the ER pathway bioactivity (5), and model performance was compared with in vitro and in vivo reference chemicals identified from the peer-reviewed literature (6). Details of the in vitro assays have been previously published (7,8) and are also are described on EPA’s ToxCast website (
ICCVAM has identified several projects where the science has advanced substantially and where there is a reasonable likelihood of implementation into regulatory use within the next 5 years.
Regarding biologics in general and
In the realm of acute oral and dermal toxicity testing, the US Environmental Protection Agency is evaluating the relative contribution of acute and dermal LD50 tests in providing information related to hazard labeling and the use of personal protective equipment. In addition, ICCVAM is investigating the utility of in vitro assays (for example, 3T3 NRU) for predicting oral LD50 values.
Another priority area of ICCVAM for the next 5 years is skin sensitization. Great strides have been made in putting together a battery of in silico, in chemico, and in vitro tests for the assessment of skin sensitization. Such nonanimal alternative assays have been developed for the various key events in the adverse outcome pathway of skin sensitization. With support from the Environmental Protection Agency, Consumer Product Safety Commission, and Food and Drug Administration, ICCVAM has announced the development of a plan for the evaluation of alternative skin sensitization test methods and testing strategies. Activities proposed as part of the plan include collaboration with international partners to support ongoing development and validation of in vitro skin sensitization test methods; evaluation of alternative test method and testing strategy submissions for skin sensitization; and promotion of validated methods through workshops, webinars, and guidance documents. The newly established ICCVAM Skin Sensitization Working Group is reviewing and evaluating the public’s response to the plan and will advance recommendations for appropriate ICCVAM activities for the next several years. More information about the ICCVAM plan to evaluate alternative skin sensitization test methods can be obtained on the NTP website (http://ntp.niehs.nih.gov/go/40498).
In the future, many ICCVAM efforts will be focused on In Vitro to In Vivo Extrapolation (IVIVE) Historically, toxicological testing has relied largely on the use of laboratory animals, and is therefore low throughput, high cost, and presents difficulties inherent to inter-species extrapolation. In comparison, high throughput screening (HTS) assays can accelerate and reduce the overall cost of the screening process and are being actively pursued through programs such as the Federal Tox21 consortium and the U.S. EPA’s Tox-Cast project. However, before in vitro HTS assays can be used for risk assessment and regulatory decision-making, the ability of in vitro activity to predict in vivo dose-response relationships needs to be evaluated. There are many factors affecting in vitro to in vivo extrapolation. The primary question is how closely a bioactive chemical concentration from an in vitro assay corresponds to blood and tissue levels that cause adverse effects in vivo. ICCVAM and US Federal agencies will increasingly focus on developing and evaluating methods that enable the accurate characterization of concentration activity relationships in both in vitro and in vivo systems.
CASRN | Name | Bioactivity |
---|---|---|
57-91-0 | 17alpha-Estradiol | Active |
57-63-6 | Ethinyl Estradiol | Active |
56-53-1 | Diethylstilbestrol (DES) | Active |
50-28-2 | Estradiol | Active |
474-86-2 | Equilin | Active |
53-16-7 | Estrone | Active |
50-27-1 | Estriol | Active |
72-33-3 | Mestranol | Active |
17924-92-4 | Zearalenone | Active |
1478-61-1 | Bisphenol AF | Active |
446-72-0 | Genistein | Active |
68-22-4 | Norethindrone | Active |
58-18-4 | Methyltestosterone | Active |
77-40-7 | Bisphenol B | Active |
80-05-7 | Bisphenol A | Active |
104-43-8 | 4-Dodecylphenol | Active |
521-18-6 | Dihydrotestosterone | Active |
131-55-5 | Benzophenone-2 | Active |
140-66-9 | 4-(1,1,3,3-Tetramethylbutyl)phenol | Active |
789-02-6 | o,p’-DDT | Active |
599-64-4 | p-Cumylphenol | Active |
5153-25-3 | Benzoic acid, 4-hydroxy-, 2-ethylhexyl ester | Active |
80-46-6 | 4-(1,1-Dimethylpropyl)phenol | Active |
131-56-6 | 2,4-Dihydroxybenzophenone | Active |
80-09-1 | Bisphenol S | Active |
72-43-5 | Methoxychlor | Active |
94-26-8 | Butylparaben | Active |
98-54-4 | p-tert-Butylphenol | Active |
556-67-2 | Octamethylcyclotetrasiloxane | Active |
520-18-3 | Kaempferol | Inactive |
84-74-2 | Dibutyl phthalate | Inactive |
84-61-7 | Dicyclohexyl phthalate | Inactive |
84-75-3 | Dihexyl phthalate | Inactive |
51630-58-1 | Fenvalerate | Inactive |
103-23-1 | Bis(2-ethylhexyl)hexanedioate | Inactive |
117-81-7 | Bis(2-ethylhexyl)phthalate | Inactive |
1461-22-9 | Tributylchlorostannane | Inactive |
1912-24-9 | Atrazine | Inactive |
61-82-5 | Amitrole | Inactive |
84-66-2 | Diethyl phthalate | Inactive |
87-86-5 | Pentachlorophenol | Inactive |
99-96-7 | 4-Hydroxybenzoic acid | Inactive |