New Studies Suggest Glyphosate Exposure Linked to Increased Risks for Humans

TWN Info Service on Biosafety
4 January 2024
Third World Network
www.twn.my

Dear Friends and Colleagues

New Studies Suggest Glyphosate Exposure Linked to Increased Risks for Humans

Two new studies provide fresh evidence of the potential impacts of glyphosate, widely used in conjunction with GM herbicide-resistant crops, on human health.

The first study (Item 1) assessed glyphosate levels and their association with overall mortality in a representative sample of the US adult population from the 2013 to 2016 National Health and Nutrition Examination Survey. The findings showed that recent exposure to glyphosate could be associated with increased mortality.

The second study (Item 2), which included licensed pesticide applicators in Iowa and North Carolina, suggests that greater lifetime glyphosate use (reported as number of days) was associated with higher prevalence of a chromosomal alteration that is commonly detected in the blood cells of adult male humans and is associated with hematopoietic malignancies. The authors observed a dose–response relationship.

 

With best wishes,
Third World Network

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URINARY GLYPHOSATE LEVELS AND ASSOCIATION WITH MORTALITY IN THE 2013-2016 NATIONAL HEALTH AND NUTRITION EXAMINATION SURVEY (NHANES).

Untalan, M., Ivic-Pavlicic, T., & Taioli, E.
Carcinogenesis, bgad088.
https://doi.org/10.1093/carcin/bgad088
https://academic.oup.com/carcin/advance-article-abstract/doi/10.1093/carcin/bgad088/7458038
2 December 2023

ABSTRACT

Objectives

Glyphosate is the most commonly used herbicide in the USA; however, its safety is still under debate. We assessed glyphosate levels and their association with overall mortality in a representative sample of the US adult population from the 2013 to 2016 National Health and Nutrition Examination Survey.

Methods

We extracted data on urinary glyphosate (N=2910) measured by ion chromatography isotope-dilution tandem mass spectrometry. Associations between glyphosate concentrations and demographic, lifestyle and other exposures were analyzed. Data were linked to public-use Mortality Files for 2019.

Results

The mean (STD) glyphosate level was 0.53 (0.59) ng/ml, with 25.7% of the subjects having glyphosate levels at or below the detection limit. At multivariate analysis, age and creatinine were associated with glyphosate urinary levels (both P<0.0001). There was a borderline association between glyphosate levels and mortality (HRadj 1.33; 95% CI 0.99–1.77 P=0.06). When 3,5,6-trichloropyridinol was excluded from the Cox model, glyphosate exhibits a significant association with mortality (HRadj 1.33; 95% CI 1.00–1.77; P=0.0532).

Conclusions

These nationally representative data suggest that recent exposure to glyphosate could be associated with increased mortality. More studies are necessary to understand population-level risk associated with the product, given its widespread use in agriculture.

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Item 2

INVITED PERSPECTIVE: IMPORTANT NEW EVIDENCE FOR GLYPHOSATE HAZARD ASSESSMENT

Schinasi, L. H., & De Roos, A. J.
Environmental Health Perspectives, 131(12), 121305.
https://ehp.niehs.nih.gov/doi/full/10.1289/EHP14256
6 December 2023

Glyphosate is the most widely used pesticide in the world.1 It is also, arguably, the most controversial. Since being classified as “probably carcinogenic to humans” by the International Agency for Research on Cancer (IARC) in 2015,2 glyphosate has received close scrutiny from scientists and regulatory bodies. A new study in this issue of Environmental Health Perspectives by Chang et al.3 provides important new evidence to support glyphosate hazard assessment.

The IARC conclusion was driven by the results of animal cancer bioassays and mechanistic studies—mostly produced in vitro or, in nonhumans, in vivo—indicating DNA and chromosomal damage and oxidative stress induced by glyphosate and glyphosate formulations.4 The evidence from human studies of cancer was considered “limited” by IARC given that it included positive associations between glyphosate and incidence of non-Hodgkin’s lymphoma from several retrospective case–control studies but no such association from the Agricultural Health Study, the only prospective cohort study published at the time of the agency’s review.4 Limitations of the body of evidence and differences in interpretation have influenced subsequent hazard assessments, such as those from the U.S. Environmental Protection Agency5 and the European Chemicals Agency.6

Cited limitations of the previous epidemiologic studies include glyphosate exposure misclassification (due to differential recall in case–control studies or general measurement error), selection bias (introduced because of low participation and missing data), and residual confounding (especially by other pesticides). These issues are difficult to overcome in observational studies, especially when studying cancer outcomes from environmental chemicals, because of the need to characterize an exposure window relevant to carcinogenesis over a number of years and with a potentially long latency period. Furthermore, because glyphosate is readily excreted from the human body,7 biological measurement of glyphosate or its metabolites to reflect chronic or lifetime exposure is not possible.

The new study by Chang et al. fills important gaps in the epidemiologic literature on glyphosate by quantifying associations between lifetime occupational use and mosaic loss of chromosome Y (mLOY) as a marker of genotoxicity. mLOY is a chromosomal alteration that is commonly detected in the blood cells of adult male humans and has been associated with hematopoietic malignancies.8 Results from the study by Chang et al., which included licensed pesticide applicators in Iowa and North Carolina, suggest that greater lifetime glyphosate use (reported as number of days) was associated with higher prevalence of expanded mLOY, or mLOY affecting ≥10% of cells.3 Associations were strongest among applicators who were ≥70 years of age, those who were never smokers, and those who were not obese. Particularly compelling is that the authors observed a dose–response relationship, with incrementally higher odds of mLOY as total lifetime days of glyphosate use increased (ptrend=0.03). This work provides important mechanistic support for genotoxicity of glyphosate in an observational, population-based context. Strengths of the study are avoidance of exposure recall issues by its prospective design, as well as consideration of multiple pesticides as potential confounders. It is also the largest human study of its kind, with 1,606 participants, of whom 343 had mLOY.

Research on biomarker end points, like that conducted by Chang et al., can indicate intermediate effects of exposure that lead to development of cancer. Studies of intermediate effects have several advantages over traditional epidemiologic studies of cancer end points. Intermediate effects, by definition, occur sooner after exposure than do incident cancers, so studies can reduce uncertainty by capturing exposures closer to the time of data collection. In addition, intermediate effects are generally more common than cancers because only a fraction go on to develop cancer. A relatively large proportion of the study population with the biomarker end point of interest may translate into adequate statistical power to estimate associations. Case in point, Chang et al. detected expanded mLOY in 9.8% of farmers.3 This provides substantial study power compared with studies of incident cancers, especially rare cancers of interest such as specific types of lymphomas and leukemias. Finally, identification of biomarkers of effect in human populations can support causal inference by enhancing biological plausibility of carcinogenicity. This is important for hazard assessment, especially when faced with conflicting findings from epidemiologic studies of cancer end points or when considering novel findings, such as the reported association between glyphosate use and acute myeloid leukemia from the most recent analysis of Agricultural Health Study cohort data.9

Evidence for intermediate effects from studies like that by Chang et al.—of humans in real-world exposure settings—is especially valuable; it avoids uncertainties from extrapolating effects found in nonhumans or from in vitro experiments. Furthermore, studies of intermediate effects can be performed sooner after the introduction of a new pesticide to the consumer and commercial markets, as compared with studies of cancer incidence, thus allowing more rapid identification of carcinogens. Therefore, supplementing the body of evidence with human studies of biomarkers of effect can go a long way toward improving hazard assessments. However, equally important will be studies demonstrating the risks of cancer development and progression, subsequent to the intermediate effect.

Chang et al. were not able to completely rule out concerns about exposure misclassification.3  Furthermore, the study results—based on a U.S. population of predominantly European ancestry—may not generalize to lower- and middle-income country populations or to other U.S. populations (such as migrant or seasonal farmworkers) with different patterns of exposure coupled with social environmental stressors that may have implications for cancer incidence.10,11 Nevertheless, this new work represents a critical step forward in filling knowledge gaps about the mechanisms of glyphosate carcinogenicity in humans, and it will surely inform future hazard assessments. There is a critical need for further population-based research studies of this kind for glyphosate, as well as for other pesticides currently in use, particularly in lower- and middle- income countries, where pesticide use is often greater than in the United States and the use of personal protective equipment may be limited.12

References

  1. Benbrook CM. 2016. Trends in glyphosate herbicide use in the United States and globally. Environ Sci Eur28(1):3. https://www.ncbi.nlm.nih.gov/pubmed/27752438https://doi.org/10.1186/s12302-016-0070-0.
  2. IARC Working Group on the Evaluation of Carcinogenic Risks to Humans. 2017. Some organophosphate insecticides and herbicides. IARC Monogr Eval Carcinog Risks Hum112:1–464. https://www.ncbi.nlm.nih.gov/pubmed/31829533https://publications.iarc.fr/549[accessed 1 November 2023].
  3. Chang VC, Zhou W, Berndt SI, Andreotti G, Yeager M, Parks CG, et al. 2023. Glyphosate use and mosaic loss of chromosome Y among male farmers in the Agricultural Health Study. Environ Health Perspect131(12):127006, https://doi.org/10.1289/EHP12834.
  4. Guyton KZ, Loomis D, Grosse Y, El Ghissassi F, Benbrahim-Tallaa L, Guha N, et al. 2015. Carcinogenicity of tetrachlorvinphos, parathion, malathion, diazinon, and glyphosate. Lancet Oncol16(5):490–491. https://www.ncbi.nlm.nih.gov/pubmed/25801782https://doi.org/10.1016/S1470-2045(15)70134-8.
  5. U.S. EPA (U.S. Environmental Protection Agency). 2018. Revised Glyphosate Issue Paper: Evaluation of Carcinogenic Potential. DP Barcode: 444689. TXR#: 0057688. Washington, DC: U.S. EPA. https://cfpub.epa.gov/si/si_public_file_download.cfm?p_download_id=534487[accessed 1 November 2023].
  6. ECHA (European Chemicals Agency). 2017. Glyphosate not classified as a carcinogen by ECHA. ECHA/PR/17/06. https://echa.europa.eu/-/glyphosate-not-classified-as-a-carcinogen-by-echa[accessed 1 November 2023].
  7. Connolly A, Jones K, Basinas I, Galea KS, Kenny L, McGowan P, et al. 2019. Exploring the half-life of glyphosate in human urine samples. Int J Hyg Environ Health222(2):205–210. https://www.ncbi.nlm.nih.gov/pubmed/30293930https://doi.org/10.1016/j.ijheh.2018.09.004.
  8. Zhang Q, Zhao L, Yang Y, Li S, Liu Y, Chen C, et al. 2022. Mosaic loss of chromosome Y promotes leukemogenesis and clonal hematopoiesis. JCI Insight7(3):e153768. https://www.ncbi.nlm.nih.gov/pubmed/35132955https://doi.org/10.1172/jci.insight.153768.
  9. Andreotti G, Koutros S, Hofmann JN, Sandler DP, Lubin JH, Lynch CF, et al. 2018. Glyphosate use and cancer incidence in the Agricultural Health Study. J Natl Cancer Inst110(5):509–516. https://www.ncbi.nlm.nih.gov/pubmed/29136183https://doi.org/10.1093/jnci/djx233.
  10. Zahm SH, Blair A. 1993. Cancer among migrant and seasonal farmworkers: an epidemiologic review and research agenda. Am J Ind Med24(6):753–766. https://www.ncbi.nlm.nih.gov/pubmed/8311105https://doi.org/10.1002/ajim.4700240612.
  11. Hansen E, Donohoe M. 2003. Health issues of migrant and seasonal farmworkers. J Health Care Poor Underserved14(2):153–164. https://www.ncbi.nlm.nih.gov/pubmed/12739296https://doi.org/10.1353/hpu.2010.0790.
  12. Food and Agriculture Organization of the United Nations. 2022. Pesticides use, pesticides trade and pesticides indicators. Global, regional and country trends, 1990–2020. FAOSTAT Analytical Brief 46. New York, NY: Food and Agriculture Organization of the United Nations. https://www.fao.org/3/cc0918en/cc0918en.pdf [accessed 1 November 2023].
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