Benbrook, 2016b
Charles Benbrook, “Enhancements Needed in GE Crop and Food Regulation in the U.S.,” Frontiers in Public Health, March 31, 2016, DOI: 10.3389/FPUBH.2016.0059.
ABSTRACT:
Not Available
Perry et al., 2007
Perry MJ, Venners SA, Barr DB, Xu X., “Environmental pyrethroid and organophosphorus insecticide exposures and sperm concentration,” Reproductive Toxicology, 2007, 23:1, DOI: 10.1016/J.REPROTOX.2006.08.005.
ABSTRACT:
BACKGROUND: There is growing concern that poisoning and other adverse health effects are increasing because organophosphorous (OP) insecticides are now being used in combination with pyrethroid (PYR) insecticides to enhance the toxic effects of PYR insecticides on target insects, especially those that have developed PYR resistance.
OBJECTIVES: We conducted a pilot biomonitoring study to determine whether men in our reproductive cohort study were being exposed to pesticides environmentally by virtue of frequenting an agricultural setting.
METHODS: We screened 18 randomly selected urine samples collected from male participants of reproductive age for 24 parent compounds and metabolites of pesticides and examined the results in relation to sperm concentration.
RESULTS: Results showed high prevalence of exposure to OP and PYR pesticides and our preliminary analyses provided some suggestion that the higher exposure group had lower sperm concentration.
CONCLUSIONS: The potential of OP/PYR mixtures to have enhanced human toxicity needs more research attention.
Perry et al., 2006
Melissa J. Perry, Anne Marbella, Peter M. Layde, “Nonpersistent Pesticide Exposure Self-report versus Biomonitoring in Farm Pesticide Applicators,” Annals of Epidemiology, 2006, 16:9, DOI: 10.1016/J.ANNEPIDEM.2005.12.004.
ABSTRACT:
PURPOSE: Few studies using biologic markers to examine nonpersistent pesticide exposure among pesticide applicators were conducted in field settings. This study compares self-reported dermal, inhalation, and ingestion exposures with urinalysis results after one-time application of the commonly used herbicide atrazine to field crops. It was hypothesized that: i) applicator reports of exposure would be associated positively with detection of urinary atrazine metabolites, and ii) applicator reports of personal-protective-equipment (PPE) use would be associated negatively with detection of urinary atrazine metabolites.
METHODS: Wisconsin dairy farmers were randomly selected to participate in 1997 to 1998 and were instructed to collect a urine sample 8 hours after the first pesticide application of the season. Farmers then were interviewed within 1 week of their first application to report on application practices. Eighty-six urine samples were analyzed for deethylatrazine, a major atrazine metabolite.
RESULTS: Comparing urinalysis results with self-reported dermal, inhalation, and ingestion exposure showed poor agreement between self-reported exposure and urinary deethylatrazine detections (all κ < 0.40). Multivariate linear regression modeling with deethylatrazine level as the outcome showed that self-reported practices did not significantly predict atrazine metabolite levels.
CONCLUSIONS: Possible explanations for the discrepancies between urinalysis results and self-reported data include: i) inaccuracies in self-reported data and ii) substantial interpersonal variation in atrazine metabolism, resulting in major differences in body burden for similar exposures. Either explanation poses challenges for epidemiologic studies of the health effects of pesticides, which rely solely on self-reported measures of exposure. Additional evaluation of determinants of accuracy in self-assessed occupational and environmental exposures is needed.
Glynnis English et al., 2012
René Glynnis English, Melissa Perry, Mary M. Lee, Elaine Hoffman, Steven Delport, Mohamed Aqiel Dalvie, “Farm residence and reproductive health among boys in rural South Africa,” Environment International, 2012, 47, DOI: 10.1016/J.Envint.2012.06.006.
ABSTRACT:
Few studies have investigated reproductive health effects of contemporary agricultural pesticides in boys. To determine the association between pesticide exposure and reproductive health of boys. We conducted a cross-sectional study in rural South Africa of boys living on and off farms. The study included a questionnaire (demographics, general and reproductive health, phyto-estrogen intake, residential history, pesticide exposures, exposures during pregnancy); and a physical examination that included sexual maturity development ratings; testicular volume; height, weight, body mass index; and sex hormone concentrations. Among the 269 boys recruited into the study, 177 (65.8%) were categorized as farm (high pesticide exposures) and 98 (34.2%) as non-farm residents (lower pesticide exposures). Median ages of the two groups were 11.3 vs 12.0 years, respectively (p<0.05). After controlling for confounders that included socioeconomic status, farm boys were shorter (regression coefficient (RC)=-3.42 cm; 95% confidence interval (CI): -6.38 to -0.45 cm) and weighed less (RC=-2.26 kg; CI: -4.44 to -0.75 kg). The farm boys also had lower serum lutenizing hormone (RC=-0.28 IU/L; CI: -0.48 to -0.08 IU/L), but higher serum oestradiol (RC=8.07 pmol/L; CI: 2.34-13.81 pmol/L) and follicle stimulating hormone (RC=0.63 IU/L; CI: 0.19-1.08 U/L). Our study provides evidence that farm residence is associated with adverse growth and reproductive health of pubertal boys which may be due to environmental exposures to hormonally active contemporary agricultural pesticides.
Perry, 2008
Melissa J. Perry, “Effects of environmental and occupational pesticide exposure on human sperm: a systematic review,” Human Reproduction Update, 2008, 14:3, DOI: 10.1093/HUMUPD/DMM039.
ABSTRACT:
Relatively recent discoveries of the hormone disrupting properties of some pesticides have raised interest in how contemporary pesticide exposures, which primarily take the form of low level environmental or occupational exposures, impact spermatogenesis. The objective of the present review was to summarize results to date of studies examining pesticide effects on human sperm. Outcomes evaluated included sperm parameters, DNA damage and numerical chromosome aberrations (aneuploidy (disomy, nullisomy) or diploidy). Studies investigating sperm in men environmentally and/or occupationally exposed to any types of pesticides were included in the review. The targeted literature search over the last 15 years showed a range of pesticide classes have been investigated including pyrethroids, organophosphates, phenoxyacetic acids, carbamates, organochlorines and pesticide mixtures. None of the studies involved acute exposure events such as chemical accidents. There were 20 studies evaluating semen quality, of which 13 studies reported an association between exposure and semen quality; 6 studies evaluating DNA damage, of which 3 reported an association with exposure; and 6 studies assessing sperm aneuploidy or diploidy, of which 4 reported an association with exposure. Studies varied widely in methods, exposures and outcomes. Although suggestive for semen parameters, the epidemiologic evidence accumulated thus far remains equivocal as to the spermatotoxic and aneugenic potential of pesticides given the small number of published studies. This question warrants more investigation and suggestions for future studies are outlined. FULL TEXT
Young et al., 2013
Heather A Young, John D Meeker, Sheena E Martenies, Zaida I Figueroa, Dana Boyd Barr and Melissa J Perry, “Environmental exposure to pyrethroids and sperm sex chromosome disomy: a cross-sectional study,” Environmental Health, 2013, 12:111, DOI: 10.1186/1476-069X-12-111.
ABSTRACT:
BACKGROUND: The role of environmental pesticide exposures, such as pyrethroids, and their relationship to sperm abnormalities are not well understood. This study investigated whether environmental exposure to pyrethroids was associated with altered frequency of sperm sex chromosome disomy in adult men.
METHODS: A sample of 75 subjects recruited through a Massachusetts infertility clinic provided urine and semen samples. Individual exposures were measured as urinary concentrations of three pyrethroid metabolites ((3-phenoxybenzoic acid (3PBA), cis- and trans- 3-(2,2-Dichlorovinyl)-1-methylcyclopropane-1,2-dicarboxylic acid (CDCCA and TDCCA)). Multiprobe fluorescence in situ hybridization for chromosomes X, Y, and 18 was used to determine XX, YY, XY, 1818, and total sex chromosome disomy in sperm nuclei. Poisson regression analysis was used to examine the association between aneuploidy rates and pyrethroid metabolites while adjusting for covariates.
RESULTS: Between 25-56% of the sample were above the limit of detection (LOD) for the pyrethroid metabolites. All sex chromosome disomies were increased by 7-30% when comparing men with CDCCA and TDCCA levels above the LOD to those below the LOD. For 3PBA, compared to those below the LOD, those above the LOD had YY18 disomy rates 1.28 times higher (95% CI: 1.15, 1.42) whereas a reduced rate was seen for XY18 and total disomy (IRR = 0.82; 95% CI: 0.77, 0.87; IRR = 0.93; 95% CI: 0.87-0.97), and no association was seen for XX18 and 1818.
CONCLUSIONS: Our findings suggest that urinary concentrations of CDCCA and TDCCA above the LOD were associated with increased rates of aneuploidy. However the findings for 3BPA were not consistent. This is the first study to examine these relationships, and replication of our findings is needed before the association between pyrethroid metabolites and aneuploidy can be fully defined. FULL TEXT
Portier et al., 2016
Christopher J Portier, Bruce K Armstrong, Bruce C Baguley, Xaver Baur, Igor Belyaev, Robert Bellé, Fiorella Belpoggi, Annibale Biggeri, Maarten C Bosland, Paolo Bruzzi, Lygia Therese Budnik, Merete D Bugge, Kathleen Burns, Gloria M Calaf, David O Carpenter, Hillary M Carpenter, Lizbeth López-Carrillo, Richard Clapp, Pierluigi Cocco, Dario Consonni, Pietro Comba, Elena Craft, Mohamed Aqiel Dalvie, Devra Davis, Paul A Demers, Anneclaire J De Roos, Jamie DeWitt, Francesco Forastiere, Jonathan H Freedman, Lin Fritschi, Caroline Gaus, Julia M Gohlke, Marcel Goldberg, Eberhard Greiser, Johnni Hansen, Lennart Hardell, Michael Hauptmann, Wei Huang, James Huff, Margaret O James, C W Jameson, Andreas Kortenkamp, Annette Kopp-Schneider, Hans Kromhout, Marcelo L Larramendy, Philip J Landrigan, Lawrence H Lash, Dariusz Leszczynski, Charles F Lynch, Corrado Magnani, Daniele Mandrioli, Francis L Martin, Enzo Merler, Paola Michelozzi, Lucia Miligi, Anthony B Miller, Dario Mirabelli, Franklin E Mirer, Saloshni Naidoo, Melissa J Perry, Maria Grazia Petronio, Roberta Pirastu, Ralph J Portier, Kenneth S Ramos, Larry W Robertson, Theresa Rodriguez, Martin Röösli, Matt K Ross, Deodutta Roy, Ivan Rusyn, Paulo Saldiva, Jennifer Sass, Kai Savolainen, Paul T J Scheepers, Consolato Sergi, Ellen K Silbergeld, Martyn T Smith, Bernard W Stewart, Patrice Sutton, Fabio Tateo, Benedetto Terracini, Heinz W Thielmann, David B Thomas, Harri Vainio, John E Vena, Paolo Vineis, Elisabete Weiderpass, Dennis D Weisenburger, Tracey J Woodruff, Takashi Yorifuji, Il Je Yu, Paola Zambon, Hajo Zeeb,Shu-Feng Zhou, “Differences in the carcinogenic evaluation of glyphosate between the International Agency for Research on Cancer (IARC) and the European Food Safety Authority (EFSA),” Journal of Epidemiology and Community Health, 2016, 0:0, DOI: 10.1136/JECH-2015-207005.
ABSTRACT:
Not Available
Cimino et al., 2017
Andria M. Cimino, Abee L. Boyles, Kristina A. Thayer, and Melissa J. Perry, “Effects of Neonicotinoid Pesticide Exposure on Human Health: A Systematic Review,” Environmental Health Perspectives, 2017, 125:2, DOI: 10.1289/EHP515.
ABSTRACT:
BACKGROUND: Numerous studies have identified detectable levels of neonicotinoids (neonics) in the environment, adverse effects of neonics in many species, including mammals, and pathways through which human exposure to neonics could occur, yet little is known about the human health effects of neonic exposure.
OBJECTIVE: In this systematic review, we sought to identify human population studies on the health effects of neonics.
METHODS: Studies published in English between 2005 and 2015 were searched using PubMed, Scopus, and Web of Science databases. No restrictions were placed on the type of health outcome assessed. Risk of bias was assessed using guidance developed by the National Toxicology Program’s Office of Health Assessment and Translation.
RESULTS: Eight studies investigating the human health effects of exposure to neonics were identified. Four examined acute exposure: Three neonic poisoning studies reported two fatalities (n = 1,280 cases) and an occupational exposure study of 19 forestry workers reported no adverse effects. Four general population studies reported associations between chronic neonic exposure and adverse developmental or neurological outcomes, including tetralogy of Fallot (AOR 2.4, 95% CI: 1.1, 5.4), anencephaly (AOR 2.9, 95% CI: 1.0, 8.2), autism spectrum disorder [AOR 1.3, 95% credible interval (CrI): 0.78, 2.2], and a symptom cluster including memory loss and finger tremor (OR 14, 95% CI: 3.5, 57). Reported odds ratios were based on exposed compared to unexposed groups.
CONCLUSIONS: The studies conducted to date were limited in number with suggestive but methodologically weak findings related to chronic exposure. Given the wide-scale use of neonics, more studies are needed to fully understand their effects on human health. FULL TEXT
Perry et al., 2011
Melissa J. Perry, Scott A. Venners, Xing Chen, Xue Liu, Genfu Tang, Houxun Xing, Dana Boyd Barr, Xiping Xu, “Organophosphorous pesticide exposures and sperm quality,” Reproductive Toxicology, 2011, 31:1, DOI: 10.1016/j.reprotox.2010.08.006.
ABSTRACT:
Many Americans are exposed to low levels of organophosphorous (OP) pesticides. It is unclear whether these exposures impact sperm production. We investigated whether there was an association between urinary OP insecticide metabolites and sperm concentration and motility in newly married men from a rural area of eastern People’s Republic of China. Ninety-four cases and 95 controls were included based on their median residual value of sperm concentration and motility after adjusting for relevant covariates. Their urine was analyzed for six dialkylphosphate (DAP) compounds. After adjustment for demographic and exposure variables, the odds of being a case were greater (odds ratio = 1.30, 95% confidence interval 1.02–1.65) in men with higher urinary concentrations of dimethylphosphate (DMP) compared to men with lower levels. No significant differences between cases and controls were found among the other DAP concentrations. DMP exposure and sperm concentration and motility should be explored further in environmental exposure studies.
Canadian Food Inspection Agency, 2017
Canadian Food Inspection Agency, “Safeguarding with Science: Glyphosate Testing in 2015-2016,” 2017, CFIA Science Branch Survey Report.
ABSTRACT:
In 2015-2016, the CFIA tested a total of 3,188 food samples for glyphosate. Glyphosate was found in 29.7% of samples. Glyphosate residues above MRLs were found in only 1.3% of samples. This data was evaluated by Health Canada and no human health concerns were identified. FULL TEXT