Study | Authors/Year | Herbicide | n | Exposure Assessment | Outcome Associations | Effect Size |
---|---|---|---|---|---|---|
Urinary glyphosate concentration in pregnant women in relation to length of gestation | (Lesseur et al., 2022) | Glyphosate and AMPA | 163 | Biomarkers in Second trimester urine samples | Shortened length of gestation in spontaneous births | Glyphosate: HR = 1.31, (95%CI 1.00–1.71) AMPA: HR = 1.32 (95%CI: 1.00–1.73) |
Prenatal exposure to organophosphate and pyrethroid insecticides and the herbicide 2,4-dichlorophenoxyacetic acid and size at birth in urban pregnant women | (Balalian et al., 2021) | 2,4-D | 270 | Urinary biomarkers of 2,4-D | Inverse association between concentration and head circumference | 2,4-D was associated with smaller head circumference in the second (β =  − 1.57; (95%CI: − 2.74, − 0.39) and third (β =  − 1.74, (95%CI: − 2.98, − 0.49) categories of concentration in comparison to the first category |
Prenatal exposure to pesticides and risk of preeclampsia among pregnant women: Results from the ELFE cohort | (Enderle et al., 2021) | Herbicides | 17,376 | Self-reported home application | Pre-eclampsia | Women receiving antihypertensive treatment for pre-eclampsia compared to women without pre-eclampsia (aOR = 2.20, (95%CI: 1.23, 3.93) |
Maternal urinary levels of glyphosate during pregnancy and anogenital distance in newborns in a US multicenter pregnancy cohort | (Lesseur et al., 2021) | Glyphosate and AMPA | 94 | Second trimester urine biomarker | Anogenital distance in female offspring | After adjusting for confounders, increased AMPA was associated with longer AGD in female infants, β = 1.96, (95%CI 0.44, 3.5) |
Prenatal Exposure to Glyphosate and Its Environmental Degradate, Aminomethylphosphonic Acid (AMPA), and Preterm Birth: A Nested Case–Control Study in the PROTECT Cohort (Puerto Rico) | (Silver et al., 2021) | Glyphosate and AMPA | 247 | Multiple second trimester urine biomarkers | Increased odds of preterm birth | aORs for an interquartile range increase in exposure at Visit 3 were 1.35 (95% CI: 0.99, 1.83) and 1.67 (95% CI: 1.26, 2.20) for GLY and AMPA, respectively |
Prenatal and infant exposure to ambient pesticides and autism spectrum disorder in children: population based case–control study | (Ehrenstein et al., 2019) | Glyphosate | 41,292 | GIS, California Pesticide Use records | Autism spectrum disorder | ASD: Glyphosate OR = 1.16, (95% CI 1.06, 1.27); ASD with intellectual disability: Glyphosate OR = 1.33 (95%CI 1.05,1.69) |
Atrazine Contamination of Drinking Water and Adverse Birth Outcomes in Community Water Systems with Elevated Atrazine in Ohio, 2006–2008 | (Almberg et al., 2018) | Atrazine | 14,445 | Mean gestational and trimester-specific atrazine concentrations were calculated from EPA water quality monitoring data | Term low birth weight | aOR 1.27 (95% CI 1.10, 1.45) |
Glyphosate exposure in pregnancy and shortened gestational length: a prospective Indiana birth cohort study | (Parvez et al., 2018) | Glyphosate | 71 | Urine biomarkers of exposure | Shortened length of gestation | GLY urine levels were significantly correlated with shortened gestational lengths (r =  − 0.28, p = 0.02) |
Exposure to pistachio pesticides and stillbirth: a case–control study | (Razi et al., 2016) | Proximity to pistachio orchards as a proxy for organo-phosphate pesticide exposure | 375 | Self-report | Stillbirth | In mothers living in pistachio gardens the OR = 14.1 (95% CI, 3.3, 63.4) In mothers exposed to sprayed pesticides, the OR = 5.0 (95% CI, 1.2, 28.6) |
County-level pesticide use and risk of shortened gestation and preterm birth | (Winchester et al., 2016) | Pesticides | 7,940,794 | California Pesticide Use records | Preterm birth, low birthweight percentile | Counties with higher pesticide use were associated with higher PTB (low 8.59 ± 0.11%, moderate 9.25 ± 0.07%, high 10.0 ± 0.06%, p's < 0.001) and shorter gestations (low 39.197 ± 0.014 weeks, moderate 39.126 ± 0.011 weeks, high 39.049 ± 0.011 weeks, p's < 0.001) |
Maternal Residential Atrazine Exposure and Risk for Choanal Atresia and Stenosis in Offspring | (Agopian, Cai, et al., 2013) | Atrazine | 4092 | USGS estimated residential atrazine exposure | Choanal atresia and stenosis | Mothers with high levels of residential atrazine exposure had an increased risk of choanal atresia or stenosis with an aOR = 1.79, (95% CI 1.17, 2.74) |
Maternal Residential Atrazine Exposure and Gastroschisis by Maternal Age | (Agopian, Langlois, et al., 2013) | Atrazine | 95,551 | USGS estimated residential atrazine exposure | Gastroschisis | Risk for gastroschisis in offspring was significantly increased for women ≥ 25 years with high levels of residential atrazine exposure compared to low aOR = 1.97, (CI: 1.19–3.26) |
Atrazine Exposure in Public Drinking Water and Preterm Birth | (Rinsky et al., 2012) | Public drinking water atrazine data | 71,768 | Public drinking water data | Preterm birth | Increase in the odds of preterm birth noted in those women living in counties with the highest level of atrazine exposure, OR = 1.26, (95% CI 1.19, 1.32) |
Drinking-water herbicide exposure in Indiana and prevalence of small-for-gestational-age and preterm delivery | (Ochoa-Acuña et al., 2009) | Drinking water nitrate and atrazine levels | 24,154 | Indiana geocoding logs | Small for gestational age | Mean atrazine concentrations over the entire pregnancy > 0.644 microg/L were associated with higher SGA prevalence than in the control group, adjusted PR = 1.14, (95% CI 1.03, 1.24) |
Pre- and post-conception pesticide exposure and the risk of birth defects in an Ontario farm population | (Weselak et al., 2008) | Self-Reported dicamba use | 3,412 | Self-report | Birth defects | Pre-conception exposure to dicamba in males increased the risk of birth defects, OR = 2.42, (95% CI 1.06, 5.53) |
Pesticide Exposure and Self-Reported Gestational Diabetes Mellitus in the Agricultural Health Study | (Saldana et al., 2007) | Self-reported pesticide use | 11,273 | Self-report from FFH | Gestational diabetes mellitus | Women who reported agricultural pesticide exposure (mixing or applying pesticides to crops or repairing pesticide application equipment) during pregnancy were more likely to report GDM, OR = 2.2 (95% CI 1.5, 3.3) |
Spontaneous Abortion in Spouses of Greenhouse Workers Exposed to Pesticides | (Petrelli et al., 2003) | Occupational exposure to greenhouse atrazine | 184 | Self-report | Spontaneous abortion | The OR adjusted for age, smoking, and education of both partners and for spouse’s type of work and time between the pregnancy and the interview yielded an OR = 11.8, CI: 2.3–59.6 |
Birth malformations and other adverse perinatal outcomes in four U.S. wheat-producing states | (Schreinemachers, 2003) | Geographically estimated chlorophenoxy herbicide exposures | 43,634 | Geographic estimation | Birth malformations | Significant increases in birth malformations were observed for the circulatory/respiratory category for the combined sexes, OR = 1.65, (95% CI 1.07, 2.55) |
An exploratory analysis of the effect of pesticide exposure on the risk of spontaneous abortion in an Ontario farm population | (Arbuckle et al., 2001) | Self-reported pesticide use | 3,936 | Self-report | Late spontaneous abortions | We observed moderate increases in risk of early abortions for preconception exposures to phenoxy acetic acid herbicides (OR) = 1.5, 95% CI, 1.1–2.1 |