Differences in the carcinogenic evaluation of glyphosate between the International Agency for Research on Cancer (IARC) and the European Food Safety Authority (EFSA)
- Christopher J Portier1,
- Bruce K Armstrong2,
- Bruce C Baguley3,
- Xaver Baur4,
- Igor Belyaev5,
- Robert Bellé6,
- Fiorella Belpoggi7,
- Annibale Biggeri8,
- Maarten C Bosland9,
- Paolo Bruzzi10,
- Lygia Therese Budnik11,
- Merete D Bugge12,
- Kathleen Burns13,
- Gloria M Calaf14,
- David O Carpenter15,
- Hillary M Carpenter16,
- Lizbeth López-Carrillo17,
- Richard Clapp18,
- Pierluigi Cocco19,
- Dario Consonni20,
- Pietro Comba21,
- Elena Craft22,
- Mohamed Aqiel Dalvie23,
- Devra Davis24,
- Paul A Demers25,
- Anneclaire J De Roos26,
- Jamie DeWitt27,
- Francesco Forastiere28,
- Jonathan H Freedman29,
- Lin Fritschi30,
- Caroline Gaus31,
- Julia M Gohlke32,
- Marcel Goldberg33,
- Eberhard Greiser34,
- Johnni Hansen35,
- Lennart Hardell36,
- Michael Hauptmann37,
- Wei Huang38,
- James Huff39,
- Margaret O James40,
- C W Jameson41,
- Andreas Kortenkamp42,
- Annette Kopp-Schneider43,
- Hans Kromhout44,
- Marcelo L Larramendy45,
- Philip J Landrigan46,
- Lawrence H Lash47,
- Dariusz Leszczynski48,
- Charles F Lynch49,
- Corrado Magnani50,
- Daniele Mandrioli51,
- Francis L Martin52,
- Enzo Merler53,
- Paola Michelozzi54,
- Lucia Miligi55,
- Anthony B Miller56,
- Dario Mirabelli57,
- Franklin E Mirer58,
- Saloshni Naidoo59,
- Melissa J Perry60,
- Maria Grazia Petronio61,
- Roberta Pirastu62,
- Ralph J Portier63,
- Kenneth S Ramos64,
- Larry W Robertson65,
- Theresa Rodriguez66,
- Martin Röösli67,
- Matt K Ross68,
- Deodutta Roy69,
- Ivan Rusyn70,
- Paulo Saldiva71,
- Jennifer Sass72,
- Kai Savolainen73,
- Paul T J Scheepers74,
- Consolato Sergi75,
- Ellen K Silbergeld76,
- Martyn T Smith77,
- Bernard W Stewart78,
- Patrice Sutton79,
- Fabio Tateo80,
- Benedetto Terracini81,
- Heinz W Thielmann82,
- David B Thomas83,
- Harri Vainio84,
- John E Vena85,
- Paolo Vineis86,
- Elisabete Weiderpass87,
- Dennis D Weisenburger88,
- Tracey J Woodruff89,
- Takashi Yorifuji90,
- Il Je Yu91,
- Paola Zambon92,
- Hajo Zeeb93,
- Shu-Feng Zhou94
- 1Environmental Health Consultant, Thun, Switzerland
- 2The University of Sydney, Sydney, New South Wales, Australia
- 3The University of Auckland, Auckland, New Zealand
- 4Charité University Medicine Berlin, Berlin, Germany
- 5Cancer Research Institute, Bratislava, Slovak Republic
- 6Sorbonne Universités, UPMC Univ Paris 06, UMR8227, Roscoff, France
- 7CesareMaltoni Cancer Research Center, Bentivoglio (Bologna), Italy
- 8Institute for Cancer Prevention and Research, University of Florence, Italy
- 9University of Illinois at Chicago, Chicago, Illinois, USA
- 10National Cancer Research Institute, San Martino—IST Hospital, Genoa, Italy
- 11University of Hamburg, Hamburg, Germany
- 12STAMI, National Institute of Occupational Health, Oslo, Norway
- 13Sciencecorps, Lexington, Massachusetts, USA
- 14Instituto de Alta Investigación, Universidad de Tarapacá, Arica, Chile
- 15Institute for Health and the Environment, University at Albany, Rensselaer, New York, USA
- 16Toxicologist, Maplewood, Minnesota, USA
- 17National Institute of Public Health, Cuernavaca, Morelos, Mexico
- 18Boston University School of Public Health, Boston, Massachusetts, USA
- 19Department of Public Health, Clinical and Molecular Medicine, University of Cagliari, Cagliari, Italy
- 20Department of Preventive Medicine, Fondazione IRCCS Ca’ Granda Ospedale Maggiore Policlinico, Milan, Italy
- 21Department of Environment and Primary Prevention, IstitutoSuperiore di Sanità, Rome, Italy
- 22Environmental Defense Fund, Austin, Texas, USA
- 23Center for Environmental and Occupational Health, University of Cape Town, Cape Town, South Africa
- 24Environmental Health Trust, Jackson Hole, Wyoming, USA and The Hebrew University Hadassah School of Medicine, Jerusalem, Israel.
- 25Dalla Lana School of Public Health, University of Toronto, Canada
- 26Department of Environmental and Occupational Health, Drexel University, Philadelphia, Pennsylvania, USA
- 27Brody School of Medicine, East Carolina University, Greenville, North Carolina, USA
- 28Department of Epidemiology, Lazio Regional Health Service, Rome, Italy
- 29University of Louisville School of Medicine, Louisville, Kentucky, USA
- 30School of Public Health, Curtin University, Perth, Western Australia, Australia
- 31Department of Environmental Toxicology, The University of Queensland, Brisbane, Australia
- 32Department of Population Health Sciences, Virginia Tech, Blacksburg, Virginia, USA
- 33Paris Descartes University, France
- 34Epi.Consult GmbH, Musweiler, Germany
- 35Danish Cancer Society Research Center, Copenhagen, Denmark
- 36University Hospital, Orebra, Sweden
- 37Biostatistics Branch, Netherlands Cancer Institute, Amsterdam, The Netherlands
- 38Faculty of Department of Occupational and Environmental Health, Peking Univ School of Public Health, Beijing, China
- 39National Institute for Environmental Health Sciences, Research Triangle Park, North Carolina, USA
- 40University of Florida, Gainesville, Florida, USA
- 41CWJ Consulting, LLC, Cape Coral, Florida, USA
- 42Institute of Environment, Health and Societies, Brunel University London, London, UK
- 43Division of Biostatistics, German Cancer Research Center, Heidelberg, Germany
- 44Institute for Risk Assessment Sciences, Utrecht University, Utrecht, The Netherlands
- 45National Council of Scientific and Technological Research, National University of La Plata, Argentina
- 46Arnhold Institute for Global Health, Icahn School of Medicine at Mount Sinai, New York, USA
- 47Department of Pharmacology, Wayne State University School of Medicine, Detroit, Michigan, USA
- 48Department of Biosciences, University of Helsinki, Helsinki, Finland
- 49Department of Epidemiology, University of Iowa, Iowa City, Iowa, USA
- 50Cancer Epidemiology Unit, University of Eastern Piedmont, Novara, Italy
- 51Cesare Maltoni Cancer Research Center, Bentivoglio (Bologna), Italy
- 52Centre for Biophotonics, Lancaster University, UK
- 53Department of Prevention, Occupational Health Unit, National Health Service, Padua, Italy
- 54Department of Epidemiology Lazio Region, Rome, Italy
- 55Occupational and Environmental Epidemiology Unit, ISPO-Cancer Prevention and Research Institute, Florence, Italy
- 56Dalla Lana School of Public Health, University of Toronto, Canada
- 57Unit of Cancer Epidemiology, University of Turin and CPO-Piemonte, Torino, Italy
- 58Department of Environmental and Occupational Health Sciences, City University of New York School of Public Health, USA
- 59School of Nursing and Public Health, University of KwaZulu-Natal, Durban, South Africa
- 60Department of Environmental and Occupational Health, Milken Institute School of Public Health, The George Washington University, Washington DC, USA
- 61Health and Environment-Department of Prevention, Local Health Authority-Empoli, Florence, Italy
- 62Department of Biology and Biotechnology “Charles Darwin”, Sapienza Rome University, Italy
- 63Department of Environmental Sciences, School of the Coast & Environment, Louisiana State University, Baton Rouge, Los Angeles, USA
- 64Center for Applied Genetics and Genomic Medicine, University of Arizona Health Sciences, Tucson, Arizona, USA
- 65Iowa Superfund Research Program and the Interdisciplinary Graduate Program in Human Toxicology, University of Iowa, Iowa City, Iowa, USA
- 66Center for Research in Health, Work and Environment (CISTA), National Autonomous University of Nicaragua (UNAN-León), León, Nicaragua
- 67Swiss Tropical and Public Health Institute, Associated Institute of the University of Basel, Basel, Switzerland
- 68College of Veterinary Medicine, Mississippi State University, Mississippi State, USA
- 69Department of Environmental and Occupational Health, Florida International University, Miami, Florida, USA
- 70Department of Veterinary Integrative Biosciences, Texas A&M University, College Station, Texas, USA
- 71Faculty of Medicine, University of São Paulo, São Paulo, Brazil
- 72Natural Resources Defense Council and George Washington University, Washington DC, USA
- 73Nanosafety Research Centre, Finnish Institute of Occupational Health, Helsinki, Finland
- 74Radboud Institute for Health Sciences, Radboud University Medical Center, Nijmegen, The Netherlands
- 75Department of Pathology, University of Alberta, Edmonton, Alberta, Canada
- 76Department of Environmental Health Sciences, Johns Hopkins Bloomberg School of Public Health, Baltimore, Maryland, USA
- 77School of Public Health, University of California, Berkeley, California, USA
- 78Faculty of Medicine, University of New South Wales, Randwick, New South Wales Australia
- 79Program on Reproductive Health and the Environment, University of California, San Francisco, California, USA
- 80Istituto di Geosceinze e Georisorse (CNR), Padova, Italy
- 81University of Torino, Torino, Italy
- 82German Cancer Research Center, Heidelberg and Faculty of Pharmacy, Heidelberg University, Germany
- 83Fred Hutchinson Cancer Research Center, University of Washington, Seattle, Washington, USA
- 84Faculty of Public Health, Kuwait University, Kuwait City, Kuwait
- 85Department of Public Health Sciences, Medical University of South Carolina, Charleston, South Carolina, USA
- 86Department of Environmental Epidemiology, Imperial College London, London, UK
- 87Department of Research, Cancer Registry of Norway, Institute of Population-Based Cancer Research, Oslo, Norway; Department of Community Medicine, Faculty of Health Sciences, University of Tromsø, The Arctic University of Norway, Tromsø, Norway; Department of Medical Epidemiology and Biostatistics, Karolinska Institutet, Stockholm, Sweden; and Genetic Epidemiology Group, Folkhälsan Research Center, Helsinki, Finland.
- 88Department of Pathology, City of Hope Medical Center, Duarte, California, USA
- 89Program on Reproductive Health and the Environment, University of California, San Francisco, USA
- 90Okayama University, Okayama, Japan
- 91Institute of Nanoproduct Safety Research, Hoseo University, Asan, The Republic of Korea
- 92University of Padua, Padova, Italy
- 93Department of Prevention and Evaluation, Leibniz-Institute for Prevention Research and Epidemiology, Bremen, Germany
- 94College of Pharmacy, University of South Florida, Tampa, Florida, USA
- Correspondence to Dr Christopher J Portier, Environmental Health Consultant, Thun, CH-3600, Switzerland;
The International Agency for Research on Cancer (IARC) Monographs Programme identifies chemicals, drugs, mixtures, occupational exposures, lifestyles and personal habits, and physical and biological agents that cause cancer in humans and has evaluated about 1000 agents since 1971. Monographs are written by ad hoc Working Groups (WGs) of international scientific experts over a period of about 12 months ending in an eight-day meeting. The WG evaluates all of the publicly available scientific information on each substance and, through a transparent and rigorous process,1 decides on the degree to which the scientific evidence supports that substance's potential to cause or not cause cancer in humans.
For Monograph 112,2 17 expert scientists evaluated the carcinogenic hazard for four insecticides and the herbicide glyphosate.3 The WG concluded that the data for glyphosate meet the criteria for classification as a probable human carcinogen.
The European Food Safety Authority (EFSA) is the primary agency of the European Union for risk assessments regarding food safety. In October 2015, EFSA reported4 on their evaluation of the Renewal Assessment Report5 (RAR) for glyphosate that was prepared by the Rapporteur Member State, the German Federal Institute for Risk Assessment (BfR). EFSA concluded that ‘glyphosate is unlikely to pose a carcinogenic hazard to humans and the evidence does not support classification with regard to its carcinogenic potential’. Addendum 1 (the BfR Addendum) of the RAR5 discusses the scientific rationale for differing from the IARC WG conclusion.
Serious flaws in the scientific evaluation in the RAR incorrectly characterise the potential for a carcinogenic hazard from exposure to glyphosate. Since the RAR is the basis for the European Food Safety Agency (EFSA) conclusion,4 it is critical that these shortcomings are corrected.
The human evidence
EFSA concluded ‘that there is very limited evidence for an association between glyphosate-based formulations and non-Hodgkin lymphoma (NHL), overall inconclusive for a causal or clear associative relationship between glyphosate and cancer in human studies’. The BfR Addendum (p. ii) to the EFSA report explains that ‘no consistent positive association was observed’ and ‘the most powerful study showed no effect’. The IARC WG concluded there is limited evidence of carcinogenicity in humans which means “A positive association has been observed between exposure to the agent and cancer for which a causal interpretation is considered by the Working Group to be credible, but chance, bias or confounding could not be ruled out with reasonable confidence.”1
The finding of limited evidence by the IARC WG was for NHL, based on high-quality case–control studies, which are particularly valuable for determining the carcinogenicity of an agent because their design facilitates exposure assessment and reduces the potential for certain biases. The Agricultural Health Study6 (AHS) was the only cohort study available providing information on the carcinogenicity of glyphosate. The study had a null finding for NHL (RR 1.1, 0.7–1.9) with no apparent exposure–response relationship in the results. Despite potential advantages of cohort versus case–control studies, the AHS had only 92 NHL cases in the unadjusted analysis as compared to 650 cases in a pooled case–control analysis from the USA.7 In addition, the median follow-up time in the AHS was 6.7 years, which is unlikely to be long enough to account for cancer latency.8
The RAR classified all of the case–control studies as ‘not reliable,’ because, for example, information on glyphosate exposure, smoking status and/or previous diseases had not been assessed. In most cases, this is contrary to what is actually described in the publications. Well-designed case–control studies are recognised as strong evidence and routinely relied on for hazard evaluations.9 ,10 The IARC WG carefully and thoroughly evaluated all available epidemiology data, considering the strengths and weaknesses of each study. This is key to determining that the positive associations seen in the case–control studies are a reliable indication of an association and not simply due to chance or methodological flaws. To provide a reasonable interpretation of the findings, an evaluation needs to properly weight studies according to quality rather than simply count the number of positives and negatives. The two meta-analyses cited in the IARC Monograph11 are excellent examples of objective evaluations and show a consistent positive association between glyphosate and NHL.
The final conclusion5 (Addendum 1, p.21) that “there was no unequivocal evidence for a clear and strong association of NHL with glyphosate” is misleading. IARC, like many other groups, uses three levels of evidence for human cancer data.1 Sufficient evidence means ‘that a causal relationship has been established’ between glyphosate and NHL. BfR's conclusion is equivalent to deciding that there is not sufficient evidence. Legitimate public health concerns arise when ‘causality is credible’, that is, when there is limited evidence of carcinogenicity.
Evidence from animal carcinogenicity studies
EFSA concluded ‘No evidence of carcinogenicity was confirmed by the majority of the experts (with the exception of one minority view) in either rats or mice due to a lack of statistical significance in pairwise comparison tests, lack of consistency in multiple animal studies and slightly increased incidences only at dose levels at or above the limit dose/maximum tolerated dose (MTD), lack of preneoplastic lesions and/or being within historical control range’. The IARC WG review found a significant positive trend for renal tumours in male CD-1 mice,12 a rare tumour, although no comparisons of any individual exposure group to the control group were statistically significant. The WG also identified a significant positive trend for hemangiosarcoma in male CD-1 mice,13 again with no individual exposure group significantly different from controls. Finally, the WG also saw a significant increase in the incidence of pancreatic islet cell adenomas in two studies in male Sprague-Dawley rats.14–16 In one of these rat studies, thyroid gland adenomas in females and liver adenomas in males were also increased. By the IARC review criteria,1 this constitutes sufficient evidence in animals.
The IARC WG reached this conclusion using data that were publicly available in sufficient detail for independent scientific evaluation (a requirement of the IARC Preamble1). On the basis of the BfR Addendum, it seems there were three additional mouse studies and two additional rat studies that were unpublished and available to EFSA. Two of the additional studies were reported to have a significant trend for renal tumours, one in CD-1 mice (Sugimoto. 18-Month Oral Oncogenicity Study in Mice. Unpublished, designated ASB2012–11493 in RAR. 1997), and one in Swiss-Webster mice (Unknown. A chronic feeding study of glyphosate (roundup technical) in mice. Unpublished, designated ABS2012–11491 in RAR. 2001). One of these studies (Sugimoto. Unpublished, 1997) also reported a significant trend for hemangiosarcoma. The RAR also reported two studies in CD-1 mice showing significant trends for malignant lymphoma (Sugimoto. Unpublished, 1997; Unknown. Glyphosate Technical: Dietary Carcinogencity Study in the Mouse. Unpublished, designated ABS2012–11492 in RAR. 2009).
The RAR dismissed the observed trends in tumour incidence because there are no individual treatment groups that are significantly different from controls and because the maximum observed response is reportedly within the range of the historical control data (Table 5.3–1, p.90). Care must be taken in using historical control data to evaluate animal carcinogenicity data. In virtually all guidelines,1 ,17 ,18 scientific reports19 and publications20–23 on this issue, the recommended first choice is the use of concurrent controls and trend tests, even in the EC regulations cited in the RAR18 (see p.375). Trend tests are more powerful than pairwise comparisons, particularly for rare tumours where data are sparse. Historical control data should be from studies in the same time frame, for the same animal strain, preferably from the same laboratory or the same supplier and preferably reviewed by the same pathologist.17 ,18 While the EFSA final peer review4 mentions the use of historical control data from the original laboratory, no specifics are provided and the only referenced historical control data24 are in the BfR addendum.5 One of the mouse studies12 was clearly done before this historical control database was developed, one study (Sugimoto. Unpublished, 1997) used Crj:CD-1 mice rather than Crl:CD-1 mice, and one study13 did not specify the substrain and was reported in 1993 (probably started prior to 1988). Hence, only a single study (Unknown. Unpublished, 2009) used the same mouse strain as the cited historical controls, but was reported more than 10 years after the historical control data set was developed.
The RAR dismissed the slightly increased tumour incidences in the studies considered because they occurred “only at dose levels at or above the limit dose/maximum tolerated dose (MTD)”, and because there was a lack of preneoplastic lesions. Exceeding the MTD is demonstrated by an increase in mortality or other serious toxicological findings at the highest dose, not by a slight reduction in body weight. No serious toxicological findings were reported at the highest doses for the mouse studies in the RAR. While some would argue that these high doses could cause cellular disruption (eg, regenerative hyperplasia) leading to cancer, no evidence of this was reported in any study. Finally, a lack of preneoplastic lesions for a significant neoplastic finding is insufficient reason to discard the finding.
The BfR Addendum dismisses the IARC WG finding that ‘there is strong evidence that glyphosate causes genotoxicity’ by suggesting that unpublished evidence not seen by the IARC WG was overwhelmingly negative and that, since the reviewed studies were not done under guideline principles, they should get less weight. To maintain transparency, IARC reviews only publicly available data. The use of confidential data submitted to the BfR makes it impossible for any scientist not associated with BfR to review this conclusion. Further weakening their interpretation, the BfR did not include evidence of chromosomal damage from exposed humans or human cells that were highlighted in Tables 4.1 and 4.2 of the IARC Monograph 3
The BfR confirms (p.79) that the studies evaluated by the IARC WG on oxidative stress were predominantly positive but does not agree that this is strong support for an oxidative stress mechanism. They minimise the significance of these findings predominantly because of a lack of positive controls in some studies and because many of the studies used glyphosate formulations and not pure glyphosate. In contrast, the WG concluded that (p.77) ‘Strong evidence exists that glyphosate, AMPA and glyphosate-based formulations can induce oxidative stress’. From a scientific perspective, these types of mechanistic studies play a key role in distinguishing between the effects of mixtures, pure substances and metabolites.
Finally, we strongly disagree that data from studies published in the peer-reviewed literature should automatically receive less weight than guideline studies. Compliance with guidelines and Good Laboratory Practice does not guarantee validity and relevance of the study design, statistical rigour and attention to sources of bias.25 ,26 The majority of research after the initial marketing approval, including epidemiology studies, will be conducted in research laboratories using various models to address specific issues related to toxicity, often with no testing guidelines available. Peer-reviewed and published findings have great value in understanding mechanisms of carcinogenicity and should be given appropriate weight in an evaluation based on study quality, not just on compliance with guideline rules.
Science moves forward on careful evaluations of data and a rigorous review of findings, interpretations and conclusions. An important aspect of this process is transparency and the ability to question or debate the findings of others. This ensures the validity of the results and provides a strong basis for decisions. Many of the elements of transparency do not exist for the RAR.5 For example, citations for almost all references, even those from the open scientific literature, have been redacted. The ability to objectively evaluate the findings of a scientific report requires a complete list of cited supporting evidence. As another example, there are no authors or contributors listed for either document, a requirement for publication in virtually all scientific journals where financial support, conflicts of interest and affiliations of authors are fully disclosed. This is in direct contrast to the IARC WG evaluation listing all authors, all publications and public disclosure of pertinent conflicts of interest prior to the WG meeting.27
Several guidelines have been devised for conducting careful evaluation and analysis of carcinogenicity data, most after consultation with scientists from around the world. Two of the most widely used guidelines in Europe are the OECD guidance on the conduct and design of chronic toxicity and carcinogenicity studies17 and the European Chemicals Agency Guidance on Commission Regulation (EU) No 286/2011;18 both are cited in the RAR. The methods used for historical controls and trend analysis are inconsistent with these guidelines.
Owing to the potential public health impact of glyphosate, which is an extensively used pesticide, it is essential that all scientific evidence relating to its possible carcinogenicity is publicly accessible and reviewed transparently in accordance with established scientific criteria.
The IARC WG concluded that glyphosate is a ‘probable human carcinogen’, putting it into IARC category 2A due to sufficient evidence of carcinogenicity in animals, limited evidence of carcinogenicity in humans and strong evidence for two carcinogenic mechanisms.
The IARC WG found an association between NHL and glyphosate based on the available human evidence.
The IARC WG found significant carcinogenic effects in laboratory animals for rare kidney tumours and hemangiosarcoma in two mouse studies and benign tumours in two rat studies.
The IARC WG concluded that there was strong evidence of genotoxicity and oxidative stress for glyphosate, entirely from publicly available research, including findings of DNA damage in the peripheral blood of exposed humans.
The RAR concluded5 (Vol. 1, p.160) that ‘classification and labelling for carcinogenesis is not warranted’ and ‘glyphosate is devoid of genotoxic potential’.
EFSA4 classified the human evidence as ‘very limited’ and then dismissed any association of glyphosate with cancer without clear explanation or justification.
Ignoring established guidelines cited in their report, EFSA dismissed evidence of renal tumours in three mouse studies, hemangiosarcoma in two mouse studies and malignant lymphoma in two mouse studies. Thus, EFSA incorrectly discarded all findings of glyphosate-induced cancer in animals as chance occurrences.
EFSA ignored important laboratory and human mechanistic evidence of genotoxicity.
EFSA confirmed that glyphosate induces oxidative stress but then, having dismissed all other findings of possible carcinogenicity, dismissed this finding on the grounds that oxidative stress alone is not sufficient for carcinogen labelling.
The most appropriate and scientifically based evaluation of the cancers reported in humans and laboratory animals as well as supportive mechanistic data is that glyphosate is a probable human carcinogen. On the basis of this conclusion and in the absence of evidence to the contrary, it is reasonable to conclude that glyphosate formulations should also be considered likely human carcinogens. The CLP Criteria18 (Table 3.6.1, p.371) allow for a similar classification of Category 1B when there are ‘studies showing limited evidence of carcinogenicity in humans together with limited evidence of carcinogenicity in experimental animals’.
In the RAR, almost no weight is given to studies from the published literature and there is an over-reliance on non-publicly available industry-provided studies using a limited set of assays that define the minimum data necessary for the marketing of a pesticide. The IARC WG evaluation of probably carcinogenic to humans accurately reflects the results of published scientific literature on glyphosate and, on the face of it, unpublished studies to which EFSA refers.
Most of the authors of this commentary previously expressed their concerns to EFSA and others regarding their review of glyphosate28 to which EFSA has published a reply.29 This commentary responds to the EFSA reply.
The views expressed in this editorial are the opinion of the authors and do not imply an endorsement or support for these opinions by any organisations to which they are affiliated.
Contributors All authors to this commentary have participated in its development and approve the content. MCB, FF, LF, CWJ, HK, TR, MKR, IR and CS were all participants in the IARC WG. CJP was an Invited Specialist in the IARC WG. Many of the remaining authors have also served on IARC Working Groups that did not pertain to glyphosate.
Competing interests CJP, MTS and DDW are providing advice to a US law firm involved in glyphosate litigation. CJP also works part-time for the Environmental Defense Fund on issues not related to pesticides.
Provenance and peer review Commissioned; externally peer reviewed.
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