Executive Summary
The toxic effects of common pesticides begin with exposure, and the Centers for Disease Control detected glyphosate in the urine of 81.2 percent of Americans tested in 2013 and 2014. Acute toxicity for these compounds is settled at the enzyme level and reproducible in a clinical setting. Chronic disease causation is a separate evidentiary problem, and the two are routinely treated as one in public argument. The largest prospective cohort in the United States, 54,251 licensed applicators enrolled between 1993 and 1997 and followed through 2013, reported a rate ratio of 0.87 for non-Hodgkin lymphoma in the highest quartile of glyphosate exposure, with a confidence interval of 0.64 to 1.20.
A 2019 pooled analysis drawing on six datasets, including that same cohort, reported a meta rate ratio of 1.41 at the highest cumulative exposure, confidence interval 1.13 to 1.75. Both numbers are in the literature. An account that carries one without the other misstates the record.
This report covers the mechanisms of the compounds most often applied to residential turf and inside homes, the measured pathways by which those compounds move indoors, the veterinary and wildlife evidence, the legal structure that keeps application records out of a resident’s hands, and the cost of the alternative. Two findings are firm. Formulated products are more biologically active in human cell assays than the declared active ingredient tested alone, and federal law protects the identity of the other ingredients from disclosure. On June 25, 2026 the Supreme Court held that federal pesticide law preempts state failure to warn claims, which closes the product label as a route to compelled disclosure. What remains contested is whether residential exposure at measured levels causes cancer in children. The epidemiology reports associations of modest size. It does not establish causation, and the investigators who produced it say so.
Detailed Findings
how do the common residential pesticides poison a living thing
Every pesticide in common residential use disables a specific enzyme or receptor, and the toxic effect follows from that one mechanism. Organophosphates such as chlorpyrifos, malathion and diazinon phosphorylate acetylcholinesterase, the enzyme that clears acetylcholine from the synaptic cleft. The bond ages within hours through loss of an alkyl group, after which oxime therapy cannot reactivate the enzyme. Clinical signs appear when brain acetylcholinesterase activity falls by more than 70 percent, and blood enzyme activity does not reliably track severity. Carbamates such as carbaryl carbamylate the same enzyme, and that bond hydrolyzes spontaneously, which is why carbamate poisoning resolves faster at comparable exposure.
Pyrethroids act on voltage gated sodium channels, prolonging the open phase and driving repetitive nerve firing. Type I compounds including permethrin and bifenthrin lack a cyano group. Type II compounds including cypermethrin carry one and produce salivation and writhing. Neonicotinoids bind post synaptic nicotinic acetylcholine receptors, and because acetylcholinesterase cannot break the bound compound down, the receptor stays activated. Insect receptors bind these compounds far more tightly than mammalian receptors, and the vertebrate blood brain barrier limits central nervous system access. That is the entire basis of the selectivity claim.
Glufosinate irreversibly inhibits glutamine synthetase. Glutamate and ammonia accumulate, and glufosinate binds the NMDA receptor as a glutamate analogue, which lowers the seizure threshold. Among 464 acute pesticide poisonings treated at a Korean teaching hospital between 2011 and 2014, seizure incidence was 31.5 percent for glufosinate against 5.9 percent for pyrethroids, with no seizures among the organophosphate cases. Seizures began 12 to 24 hours after ingestion and were generalized tonic clonic in 85.7 percent of cases.
Anticoagulant rodenticides inhibit vitamin K epoxide reductase and stop hepatic production of clotting factors II, VII, IX and X. Those factors carry serum half lives of 6.2 to 16.5 hours, so coagulation times rise two to five days after ingestion and bleeding appears three to seven days after a toxic dose. Second generation compounds, brodifacoum, bromadiolone, difethialone and difenacoum, have median lethal doses 2.5 to 200 times lower than first generation compounds and are typically lethal in a single feeding. Metaldehyde slug bait hydrolyzes partly to acetaldehyde, lowers GABA, and produces tremors with body temperature above 106 degrees Fahrenheit. The canine oral median lethal dose is 210 to 600 milligrams per kilogram; the feline dose is 207.
what does the regulatory record establish about glyphosate and cancer
The federal cancer determination for glyphosate has been legally vacated since 2022 and has not been replaced. The International Agency for Research on Cancer classified glyphosate as probably carcinogenic to humans, Group 2A, in Volume 112 of its monograph series in 2015. EPA reached the opposite finding in a December 12, 2017 issue paper, finding glyphosate not likely to be carcinogenic to humans, and carried that finding into the January 2020 Interim Registration Review Decision. On June 17, 2022 the Ninth Circuit vacated the human health portion of that decision and remanded for further analysis and explanation. EPA withdrew the remaining portions on September 23, 2022. As of the agency’s August 26, 2026 update, the 2017 finding is still being revised, with an updated human health risk assessment anticipated in late 2026 and a public webinar in early 2027. Products stayed on the shelf throughout.
The chronic oral reference dose EPA carries for glyphosate is 0.1 milligrams per kilogram per day, verified in March 1986 and based on renal tubular dilation in third generation offspring in a three generation rat reproduction study. The Agency for Toxic Substances and Disease Registry set oral minimal risk levels of 1 milligram per kilogram per day for acute, intermediate and chronic exposure on a gastrointestinal endpoint in its August 2020 profile.
The epidemiology splits along study design. The prospective applicator cohort found no association with non-Hodgkin lymphoma at any exposure level, with the only nominally positive result an acute myeloid leukemia rate ratio of 2.04 in a twenty year lagged tertile analysis, confidence interval 1.05 to 3.97, one estimate among many in a study reporting 7,290 incident cancers. The 2019 pooled analysis reported 1.41 at the highest cumulative exposure. A 2026 preprint pooling ten datasets across twenty populations reported an odds ratio of 1.11 for ever exposure, confidence interval 0.98 to 1.27, and 1.38 at the highest exposure, confidence interval 1.00 to 1.90, with certainty graded moderate. That preprint has not completed peer review.
Animal data moved in 2025. A lifetime bioassay of 1,020 Sprague Dawley rats dosed from gestational day six through 104 weeks reported increased leukemias across all treatment groups at doses beginning at 0.5 milligrams per kilogram of body weight per day, which is the European acceptable daily intake. Forty percent of leukemia deaths occurred before 52 weeks of age, against no such deaths before one year among historical controls. Skin papilloma incidence reached 3.92 percent in treated males with no skin tumors in controls.
Two 2026 laboratory studies located the biological activity in the formulation and not in the molecule alone. The National Toxicology Program tested glyphosate against 13 glyphosate based formulations in human skin and liver cell systems and reported that glyphosate alone was weakly and inconsistently bioactive for oxidative stress and DNA damage while most of the formulations showed measurably greater activity. A July 2026 study in human leukemia and hepatocyte cell lines detected DNA tail length increases from one commercial formulation at 0.1 micromolar, far below cytotoxic thresholds, while the tested co-formulants alone produced no measurable genotoxicity.
California listed glyphosate under Proposition 65 effective July 7, 2017 through the Labor Code mechanism at Health and Safety Code section 25249.8(a), with a no significant risk level of 1,100 micrograms per day. On November 7, 2023 the Ninth Circuit affirmed a permanent injunction barring enforcement of the cancer warning as compelled speech under the First Amendment. The chemical remains on the state list and the warning requirement cannot be enforced against a seller.
Money has moved without waiting for the science. The 2020 settlement resolved roughly 125,000 filed and unfiled claims at a stated range of $10.1 billion to $10.9 billion. On February 17, 2026 a class settlement of up to $7.25 billion was filed in the Circuit Court of the City of St. Louis, covering exposure before that date and diagnoses arising within 16 years of final approval, structured as declining capped annual payments over as long as 21 years. A Missouri judge granted preliminary approval in early March 2026.
what the record shows for 2,4-D, dicamba and glufosinate
2,4-D is the most heavily used home and garden herbicide in the United States and carries a weaker cancer classification than glyphosate. The International Agency for Research on Cancer placed it in Group 2B, possibly carcinogenic to humans, in Volume 113 in 2015, on inadequate evidence in humans and limited evidence in experimental animals, together with strong evidence that it induces oxidative stress and moderate evidence that it causes immunosuppression. EPA classified it Category D, not classifiable as to human carcinogenicity, in 1996 and restated that in the June 30, 2005 reregistration eligibility decision, which identified the eye, thyroid, kidney, adrenals, ovaries and testes as target organs at doses above renal clearance saturation. The IRIS chronic oral reference dose is 0.01 milligrams per kilogram per day on hematologic, hepatic and renal toxicity. A 2017 meta analysis accounting for exposure level reported a pooled rate ratio of 1.38 for non-Hodgkin lymphoma among ever exposed workers, confidence interval 1.07 to 1.77, rising to 1.73 in high exposure groups, confidence interval 1.10 to 2.72. 2,4-D itself is not on the California Proposition 65 list. 2,4-D butyric acid, a separate compound with a separate registry number, has been listed since June 18, 1999.
Dicamba’s principal problem is physical. It volatilizes off the treated surface and moves. Potted soybeans showed injury from dicamba vapor at 60 meters, roughly 197 feet, from the application area in field testing. On February 6, 2024 the District of Arizona vacated EPA’s 2020 over the top registrations for three dicamba products on two notice and comment violations under federal pesticide law, and EPA issued an existing stocks order. The IRIS chronic oral reference dose is 0.03 milligrams per kilogram per day, based on maternal and fetal toxicity in a rabbit developmental study.
Glufosinate lost its European approval on July 31, 2018, when the approval lapsed because no applicant supported renewal under the third renewal programme. It carries a European reproductive toxicity classification of 1A or 1B, may damage fertility or the unborn child. EPA’s September 3, 2025 human health risk assessment set a chronic reference dose of 0.006 milligrams per kilogram per day and retained the full tenfold Food Quality Protection Act safety factor because the developmental neurotoxicity study produced no no observed adverse effect level. The critical endpoint is altered morphometrics in offspring measured as adults.
what does the insecticide record show for the human nervous system
Chlorpyrifos left residential shelves in 2000 and never left the food supply. A June 7, 2000 memorandum of agreement with the registrants, published as a cancellation order at 65 Federal Register 76233 on December 6, 2000, eliminated termite control and nearly all residential uses and restricted remaining products to containers holding at least 15 gallons of liquid or 25 pounds of dry material, which put them out of homeowner reach. Food tolerances survived. EPA revoked all of them at 86 Federal Register 48315 on August 30, 2021 under an order of the Ninth Circuit in League of United Latin American Citizens v. Regan, 996 F.3d 673 (9th Cir. 2021). The Eighth Circuit vacated that rule on November 2, 2023 in Red River Valley Sugarbeet Growers Association v. Regan, 85 F.4th 881, and the mandate issued December 28, 2023 reinstated every tolerance. A proposed rule at 89 Federal Register 99184, published December 10, 2024, would revoke the tolerances tied to cancelled uses while retaining tolerances for 11 crops. Since July 1, 2025 the compound may be applied only to those 11 crops in specified states.
The neurodevelopmental data that drove the 2021 revocation came from children born before the residential phase out took effect. In a New York City birth cohort of 265 children followed to age seven, each standard deviation increase of 4.61 picograms per gram in cord blood chlorpyrifos corresponded to a 1.4 percent decline in full scale IQ and a 2.8 percent decline in the working memory index, with a 5.3 point working memory gap between the highest and lowest exposure quartiles. An independent California agricultural cohort of 297 children found a 7 point IQ deficit between the highest and lowest quintile of averaged maternal urinary dialkyl phosphate metabolites. In the 1999 to 2000 national survey, the chlorpyrifos metabolite TCPy was detected in 96 percent of samples drawn from about 2,000 participants aged 6 to 59.
Pyrethroid exposure has moved the other direction. The geometric mean of urinary 3-phenoxybenzoic acid rose from 0.292 micrograms per liter in 1999 and 2000 to roughly 0.68 by 2017 and 2018. Among children aged 6 to 11 it rose from 0.417 to 0.790. In a cohort of 2,116 adults followed a median of 14.4 years through 2015, the highest tertile of urinary 3-phenoxybenzoic acid carried a hazard ratio of 1.56 for all cause mortality, confidence interval 1.08 to 2.26, and 3.00 for cardiovascular mortality, confidence interval 1.02 to 8.80. The cancer mortality estimate was null at 0.91.
Neonicotinoids reach about half the population. Of 3,038 participants tested in the 2015 to 2016 national survey, 49.1 percent carried at least one of six neonicotinoid biomarkers, led by N-desmethyl-acetamiprid at 35 percent and 5-hydroxy-imidacloprid at 19.7 percent. The European Union confined imidacloprid, clothianidin and thiamethoxam to permanent greenhouses through three implementing regulations adopted May 29, 2018, and outdoor approvals for all three lapsed between January 2019 and December 2020.
Paraquat sits in its own category. EPA states that one small sip can be fatal and that no antidote exists, and its incident data recorded 27 fatalities through 2014, at least eight following accidental ingestion after transfer into a beverage container. A case control study nested in the federal applicator cohort, 110 Parkinson’s disease cases against 358 controls, reported an odds ratio of 2.5 for paraquat exposure, confidence interval 1.4 to 4.7, with an identical estimate for rotenone. The European approval directive was annulled by the Court of First Instance on July 11, 2007 in Case T-229/04 for failing to satisfy the requirements relating to protection of human health. In the United States paraquat remains a restricted use pesticide available only to certified applicators. On January 17, 2025 EPA moved for a voluntary remand in the Ninth Circuit and stated that it intends to withdraw the 2021 Interim Decision, and it has since announced a volatilization data call in that the agency estimated would take at least four years. More than 6,700 personal injury suits were pending against the manufacturer as of August 2025 in the multidistrict litigation in the Southern District of Illinois.
how do lawn chemicals get inside a house
Lawn chemicals enter homes on shoes and fur, and the transport has been measured, not assumed. Studies published in 1996, 1999 and 2001 tracked 2,4-D and dicamba from treated turf into residences. Turf to carpet transfer efficiency was about 0.3 percent of the dislodgeable turf residue. Across 13 residences the median bulk floor dust loading one week after application was 6 micrograms per square meter, and the loading followed the traffic pattern inward from the entryway. Children, pets and shoes were the dominant determinants of indoor residue. Spray drift and airborne particle intrusion contributed little. Carpeted floors held more than hard floors.
Indoor air carried it as well. Within two hours of a homeowner application, indoor 2,4-D reached about 9 nanograms per cubic meter in the PM10 fraction, falling to about 3 by day three. A commercial application produced about 4 nanograms per cubic meter. The compound concentrated in the 2.5 to 10 micrometer particle range, and resuspension of floor dust was the major indoor air source. Estimated post application non-dietary exposure for young children ran 1 to 10 micrograms per day from floor contact and 0.2 to 30 micrograms per day from table top contact, roughly ten times the pre application level, against dietary intake of about 1.3 micrograms per day.
The exposure factors EPA publishes explain why children absorb the difference. A child aged one to under six ingests 100 milligrams per day of soil and dust combined at the central estimate, against 50 for an adult, and 200 milligrams per day at the upper percentile for ages three to under six. Indoor hand to mouth contact averages 20 events per hour at ages one to two, with a 95th percentile of 63. EPA rates its own confidence in those contact frequencies as low. For turf, the residential exposure standard operating procedures assume that 1 percent of the applied active ingredient is available as transferable residue and assign a dermal transfer coefficient of 49,000 square centimeters per hour to a child aged one to under two, against 180,000 for an adult.
Persistence sets how long the pathway stays open. On green turf 2,4-D remains detectable for 48 hours and on dry brown grass for 72. Reported soil half lives run about 10 days for 2,4-D, 17 to 58 days for dicamba, an average near 60 days for glyphosate across a reported range of 2 to 215 days, 40 days for imidacloprid rising to 124 days in soil recently amended with organic fertilizer and 188 to 997 days in non-agricultural soil, and 97 to 250 days for bifenthrin in aerobic soil metabolism with field dissipation half lives of 122 to 345 days. Bifenthrin applied to a yard in March is still measurably present in that soil in July.
Drift adds a neighbor’s application to a resident’s own. EPA’s April 2025 ecological mitigation document assigns ground boom spray drift buffer distances up to 100 feet for very fine to fine droplets from a high boom and 50 feet from a low boom, with a floor of 10 feet for ground applications. Field measurement of one ground applied herbicide found roughly 25 percent visual injury to soybeans at 61 meters, about 200 feet, which was the farthest sampling station in the study.
what does the epidemiology show for children
Residential pesticide exposure is associated with childhood leukemia and lymphoma, and the associations are consistent in direction and modest in size. A 2015 meta analysis of 16 observational studies reported an odds ratio of 1.47 for childhood leukemia with indoor insecticide exposure, confidence interval 1.26 to 1.72, and 1.43 for childhood lymphoma, confidence interval 1.15 to 1.78. Herbicide exposure and childhood leukemia gave 1.26, confidence interval 1.10 to 1.44. Outdoor insecticide exposure did not reach statistical significance. A 2010 systematic review of 15 studies reported an odds ratio of 2.05 for insecticide exposure during pregnancy, confidence interval 1.80 to 2.32, and 1.61 for insecticide exposure during childhood, with herbicide exposure during childhood null at 0.96.
Those estimates rest on parental recall of household pesticide use. Recall bias and exposure misclassification are the standing objections, and the authors of the 2010 review called for confirmation through methods beyond self reporting. The pooled estimates are the best available evidence of an association. They are not evidence of causation, and they were never offered as such.
The differential vulnerability of children is not contested. A 1993 National Research Council report concluded that children are not little adults, that infants and children differ both qualitatively and quantitatively from adults in exposure to pesticide residues, and that quantitative differences from absorption, metabolism and excretion typically span roughly a tenfold range. Congress wrote that finding into law three years later. The Food Quality Protection Act of 1996, Public Law 104-170, requires at 21 U.S.C. 346a(b)(2)(C)(ii)(II) an additional tenfold margin of safety for infants and children in the case of threshold effects, which the Administrator may reduce only on the basis of reliable data showing that the smaller margin will be safe. The 2012 American Academy of Pediatrics policy statement concluded that the evidence base is strongest for pediatric cancer and adverse neurodevelopment, and that multiple case control studies support a role for insecticides in brain tumor and acute lymphocytic leukemia risk.
Ewing sarcoma, the cancer at the center of the current California dispute, has no established environmental cause of any kind. United States incidence for ages under 20 is 3.0 cases per million, rising to 4.3 per million at ages 10 to 14 and 4.5 per million at ages 15 to 19, on national registry data for 2016 through 2020. Incidence is roughly nine times higher in White than in Black children. About 85 percent of cases carry the EWSR1-FLI1 fusion produced by a somatic translocation of unknown origin. No exposure, pesticide or otherwise, has been established as a cause of that translocation.
what happens to dogs, cats and wildlife
The veterinary evidence for lawn herbicides is suggestive and has never been replicated for a single active ingredient. A 1991 hospital based case control study of 491 confirmed canine malignant lymphoma cases against 466 non-tumor and 479 tumor controls reported an odds ratio of 1.3 for owner application of 2,4-D or use of a commercial lawn care service, confidence interval 1.04 to 1.67, with risk rising by number of yearly applications and reaching 2.0 at four or more owner applications. An independent expert panel raised design and analysis objections in 1992. A 1999 reanalysis of the same raw data under a redefined exposure variable confirmed neither the dose response nor the association. EPA does not accept 2,4-D as a cause of canine lymphoma, citing the absence of environmental or personal sampling and possible recall bias.
Later work supports the product category without isolating the chemical. A 2012 case control study of 263 biopsy confirmed canine lymphoma cases against 470 controls reported an odds ratio of 1.7 for professionally applied pesticides, confidence interval 1.1 to 2.7, and 2.7 for self applied insect growth regulators, confidence interval 1.1 to 6.8. Flea and tick control products showed no association. A 2004 study of 83 Scottish terriers with transitional cell carcinoma of the bladder against 83 breed matched controls reported an odds ratio of 4.42 for phenoxy herbicide exposure, confidence interval 1.74 to 11.19, rising to 7.19 where both herbicides and insecticides had been applied, confidence interval 2.15 to 24.07.
Dogs carry the residue in their urine, including dogs on untreated property. In a 2013 study, herbicides were detected in the urine of dogs in 14 of 25 households before lawn treatment, in 19 of 25 after treatment, and in 4 of 8 households that applied nothing at all. Grass residues appeared in 7 of 8 untreated control yards. Whatever the cancer question turns out to be, the exposure question in a treated neighborhood is already answered, and it does not stop at the property line.
Acute poisoning is the more common event by a wide margin. The national animal poison control center handled more than 376,000 exposure items in 2025, with rodenticides ranking seventh at 6.5 percent and insecticides ninth at 3.8 percent. Permethrin kills cats at rates that reflect a metabolic gap: the feline liver is deficient in glucuronide transferase, and canine spot on products contain 45 to 65 percent permethrin against 0.05 to 0.1 percent in feline products. In one Australian case series, tremors appeared in 58 percent of exposed cats and seizures in 38 percent, with mortality of 23 percent, against 37 percent in United Kingdom reports.
Rodenticides move up the food chain. Of 94 birds of prey tested in Massachusetts between 2012 and 2016, 96 percent carried second generation anticoagulant residues, brodifacoum appeared in 95 percent, and 66 percent carried two or more compounds. California legislative findings recorded second generation residues in more than 90 percent of tested mountain lions, 88 percent of bobcats, 85 percent of Pacific fishers and 70 percent of northern spotted owls between 2014 and 2018. The state responded with the California Ecosystems Protection Act of 2020, Chapter 250 of the Statutes of 2020, prohibiting second generation compounds pending a completed reevaluation, and extended the prohibition to first generation compounds in wildlife habitat areas through Chapter 571 of the Statutes of 2024.
Insects absorbed the largest change of all. Acute oral insecticide toxicity loading on United States agricultural land rose 48 fold between 1992 and 2014, with neonicotinoids accounting for roughly 92 percent of the total across that period, even as per acre application rates fell. In the Netherlands, where surface water imidacloprid exceeded 20 nanograms per liter, insectivorous bird populations declined an average of 3.5 percent per year, a spatial pattern that appeared only after the compound entered use in the mid 1990s and persisted after correction for farmland land use change.
why a resident cannot find out what was applied
Federal pesticide law does not require a label to name what is in the container. The registration standard directs the Administrator to register a pesticide that will perform its intended function without unreasonable adverse effects on the environment, 7 U.S.C. 136a(c)(5)(C), and defines that phrase at 7 U.S.C. 136(bb) as any unreasonable risk to man or the environment, taking into account the economic, social and environmental costs and benefits of the use of any pesticide. That is a cost benefit licensing standard, not a health based one, and it is the reason a compound with known hazards can hold a valid registration.
The disclosure gap sits one section over. 7 U.S.C. 136h(d) protects from public disclosure the identity or percentage quantity of any deliberately added inert ingredient, absent a finding of unreasonable risk. The labeling rule at 40 C.F.R. 156.10(g)(1) requires the name and percentage of each active ingredient and only the total percentage by weight of all inert ingredients. Section 156.10(g)(7) permits the Administrator to require an inert to be named where it may pose a hazard to man or the environment, a discretionary power exercised case by case. No rule caps the inert fraction. A container that is 41 percent active ingredient and 59 percent undisclosed other material satisfies the labeling rule in full.
That other material is not inert in the ordinary sense of the word. The statutory definition is purely negative: an inert ingredient is an ingredient which is not active. Toxicological work published in 2014 reported that eight of nine tested formulations were up to a thousand times more toxic to three human cell lines than their declared active principles, a finding contested on in vitro methodology and on extrapolation to whole organism risk. The 2026 National Toxicology Program work and the July 2026 cell line study reached the same directional result through different assays. The European Union acted on the point a decade ago. Commission Implementing Regulation (EU) 2016/1313, in force August 22, 2016, requires member states to ensure that glyphosate products do not contain the co-formulant polyethoxylated tallowamine. The United States has no comparable mechanism, because the identity of the co-formulant is itself the protected item.
I spent part of my early career in semiconductor fabrication, where every chemical entering the fab arrived with a full composition disclosure down to components present at fractions of a percent, because a process engineer cannot control a deposition or a strip step without knowing everything in the bottle. A homeowner standing on a freshly treated lawn has less information about the mixture underfoot than a fab technician has about a photoresist stripper. The difference is a statute, not a technical limitation.
State law narrows the gap and does not close it. California occupies the whole field of pesticide regulation to the exclusion of local rules under Food and Agricultural Code section 11501.1, and directs the state to sue localities that legislate anyway. California has required pesticide use reporting since 1990, and landscape maintenance performed by a licensed pest control business or a government agency is a reportable category. The state department’s own published summaries state that the primary exceptions to the reporting requirements are home and garden use and most industrial and institutional uses, with the exemption at Food and Agricultural Code section 11408. A resident spraying a personal yard reports nothing to anyone.
School children receive notice that the same children do not receive at home. The Healthy Schools Act of 2000, Education Code sections 17608 through 17614, requires annual written notification of the pesticide products expected to be used, individual notice at least 72 hours before an application, warning signs posted 24 hours before the application and left in place until 72 hours after, records kept four years and made available to the public, and an integrated pest management plan. The statutory definition of schoolsite at section 17609 covers public schools and child day care facilities and excludes private schools. It does not reach a homeowners association, a common interest development, or a community association maintaining playgrounds, greenbelts and trails used by the same children every afternoon.
What a resident has instead is a records demand. The Davis-Stirling Common Interest Development Act makes executed contracts not otherwise privileged, written board approvals of vendor or contractor proposals, invoices, purchase orders and statements for services rendered inspectable association records under Civil Code section 5200. Section 5205 grants the inspection right, section 5210 sets deadlines of 10 business days for current fiscal year records and 30 calendar days for the prior two fiscal years, and section 5235 authorizes reasonable costs and attorney fees plus a civil penalty of up to $500 for each separate written request unreasonably denied. The limit is written into section 5210 itself. The lookback runs three fiscal years. For a disease with a multi year induction period, the statutory window is shorter than the exposure history any investigator would need.
what the Supreme Court decided in June 2026
On June 25, 2026 the Supreme Court held seven to two that federal pesticide law expressly preempts a state law failure to warn claim that would require a cancer warning on a Roundup label. Monsanto Co. v. Durnell, No. 24-1068, reversed the Missouri Court of Appeals decision reported at 707 S.W.3d 828 (2025) and remanded. The Court distinguished Bates v. Dow Agrosciences LLC, 544 U.S. 431 (2005), on the ground that Bates concerned efficacy claims, which EPA does not evaluate at registration, noting that approval of a label reflects no determination that the pesticide will be efficacious. The dissent argued that the remand in Bates had already rejected the theory that label approval creates preemptive federal requirements.
The decision resolves a three way circuit split in favor of the Third Circuit. Hardeman v. Monsanto Co., 997 F.3d 941 (9th Cir. 2021), and Carson v. Monsanto Co., 92 F.4th 980 (11th Cir. 2024) (en banc), had held such claims parallel to the federal misbranding prohibition and therefore not preempted. Schaffner v. Monsanto Corp., 113 F.4th 364 (3d Cir. 2024), held them preempted on the reasoning that EPA’s preapproval regulation gives content to the misbranding standard. Hardeman and Carson are abrogated on the preemption question.
State legislatures had been moving the same direction. North Dakota enacted House Bill 1318 effective July 1, 2025, deeming an EPA approved label sufficient to satisfy any state requirement for warning or labeling regarding health or safety. Georgia enacted Senate Bill 144, signed May 9, 2025, with a carve out where EPA determines that the manufacturer knowingly withheld or misrepresented safety information during registration. Kentucky enacted Senate Bill 199 in March 2026 over a gubernatorial veto, limited in final form to agricultural pesticides. Comparable bills failed in at least nine other states during the 2026 sessions.
Add the enjoined Proposition 65 warning and the pattern is complete. The label is closed as a route to compelled disclosure: at the federal level by preemption, at the California level by the First Amendment, and in three states by statute. Whatever a resident learns about what was sprayed on the ground outside their door will come from contract documents and association records, not from a warning panel.
how reliable is a suspected cancer cluster as evidence
Cancer cluster investigations almost never identify a cause, and the base rate is the reason. A review covering January 1990 through September 2011 identified 428 cluster investigations conducted in 38 states, assessing community concerns about 567 cancer sites or categories. A statistical excess was confirmed for 72 of those sites, 13 percent. Three investigations found any evidence of an association with a hypothesized exposure. One identified a cause: pleural mesothelioma from asbestos exposure at a naval shipyard.
CDC and ATSDR published revised guidelines for examining unusual patterns of cancer and environmental concerns on December 8, 2022, replacing the 2013 guidelines issued jointly with the Council of State and Territorial Epidemiologists. The 2022 revision reframed the biological plausibility criterion as a plausible pathway of exposure between the suspected environmental contaminants and the cancers at issue. The agency states the arithmetic plainly. One in two men and one in three women will be diagnosed with some form of cancer, latency often runs decades, and populations move, which severs exposure from diagnosis in both time and place.
The Orange County matter now under review shows the difficulty. A California Cancer Registry evaluation in 2024 found no discernible pattern of cases at that time, and a renewed evaluation was under way as of mid 2026 with results expected in the fall. Public case counts conflict, with six children reported in a July 17, 2026 county statement and roughly nine over about two decades in other accounts. County wide cancer mortality runs below the state rate, at 131.0 deaths per 100,000 against 140.2 for California across 2014 through 2016. In July 2026 a federal prosecutor and six state legislators separately asked EPA to investigate and to review application records across roughly 4,000 acres of community maintained grounds. As of August 31, 2026 no EPA response, investigation announcement or enforcement action can be verified from a primary agency source. The association paused certain pesticide applications for 60 days, and a comparable 60 day pause was reported at county schools in August 2026.
Causation and exposure are separate inquiries that resolve on different evidence. Only the second one is answerable from records a community already holds.
what does it cost to stop spraying
Organic turf management costs more in the first two years and less after the third. A five year comparison for a school athletic field put conventional management at $45,855 against $42,742 for organic, with the annual crossover at year three, $9,055 conventional against $8,497 organic. That comparison originates in a March 2010 study by an advocacy organization and has not been peer reviewed, which is worth stating given how often the figure circulates without that qualification.
Municipal data is firmer. Springfield, Massachusetts managed 12 properties covering 67 acres organically in 2018 at $1,460 per acre per year, a total program cost of $98,080, on fields carrying 3,300 to 3,600 hours of annual use with the few cancellations attributable to weather and not to field condition. Marblehead, Massachusetts has managed all 20 acres of its public grass fields organically since 2002 at $4,250 to $4,500 per acre per year. Harvard ran a one acre organic pilot in Harvard Yard in 2008 at about $40,000 plus roughly $45,000 in composting and compost tea equipment, and reported irrigation reduced more than 30 percent against control plots, two million gallons of water saved per year, and $35,000 per year avoided in trucking organic material off campus.
Integrated pest management produces the larger reductions. One Utah school district cut applications by 99 percent, to fewer than 50 targeted applications district wide, and saved more than $160,000 from July 2008. A Colorado district cut use 90 percent and spending by half. A Florida district cut use 80 percent and cost by half. EPA describes integrated pest management as an approach that integrates multiple control methods based on site information obtained through inspection, monitoring and reports, organized around pest identification, action thresholds, prevention and control.
The volumes are smaller than the public argument implies. In 2012, the most recent year EPA has published, home and garden applications accounted for 59 million pounds of conventional pesticide active ingredient against a national total near 1.006 billion pounds, about 6 percent, with agriculture at 854 million pounds. 2,4-D led the home and garden category at 7 to 9 million pounds and glyphosate followed at 4 to 6 million. Those numbers appeared in a report EPA issued in January 2017, and the agency has published nothing newer, which means the most recent federal usage picture for American lawns describes a year that is now fourteen years in the past.
The next piece in this sequence takes up the inert ingredient record directly: what the approved inert lists actually contain, what 7 U.S.C. 136h(d) withholds from a label and from a public records request, and how far a Civil Code section 5200 records demand can carry an association member toward the application level detail that the Healthy Schools Act gives a parent at a public school and gives no one at home.
Open Questions
Will EPA’s updated glyphosate human health risk assessment evaluate formulated products or the active ingredient alone? The 2026 laboratory work located the biological activity in the formulations. An assessment limited to the molecule would not reach the compounds those studies flagged, and registrants, insurers and buyers all price risk off the federal determination.
Does the June 2026 preemption holding extend past warning claims to design defect and negligence theories? The holding is written around labeling. Plaintiffs will test whether a claim framed as defective formulation, aimed at undisclosed co-formulants and not at the warning panel, survives preemption. That outcome sets whether the $7.25 billion class settlement is a ceiling or a floor.
When will EPA act on paraquat, and what governs during the interval? The agency told the Ninth Circuit in January 2025 that it intends to withdraw the 2021 Interim Decision, and it has committed to a volatilization data call in that it estimated would take at least four years. Restricted use products stay on the market for that entire period.
What becomes of the 11 chlorpyrifos crop tolerances? The December 2024 proposed rule has not been finalized, the agency said it expected an amended proposed interim decision in 2026, and every tolerance vacated in 2021 has been back in force since December 28, 2023. Food processors and importers are buying against a standard that two circuits have already moved twice.
Does any authority require a homeowners association or common interest development to keep and disclose application level pesticide records? The Healthy Schools Act does not reach them, the state pesticide use report captures the licensed applicator and not the resident, and the Davis-Stirling lookback runs three fiscal years. An amendment extending schoolsite notice and posting duties to association maintained common areas would close the gap at modest administrative cost.
Will the California registry review report a rate or a count? A count of six or nine cases in a community of roughly 26,000 residents cannot be evaluated without an expected value and a confidence interval. The 2024 evaluation found no discernible pattern. A renewed review reaching the same finding will persuade no one unless it publishes the arithmetic that produced it.
Does the year three cost crossover for organic turf hold across several thousand acres of association maintained common area, as distinct from a single school field or a 67 acre municipal portfolio? No published data covers a property of that size, and community boards are being asked to make the decision without it.
Source List
United States Environmental Protection Agency, Glyphosate registration review page, last updated August 26, 2026. https://www.epa.gov/ingredients-used-pesticide-products/glyphosate. Primary source for the current status of the vacated 2020 Interim Decision and the timing of the updated human health risk assessment.
Monsanto Co. v. Durnell, No. 24-1068 (U.S. June 25, 2026), slip opinion. https://www.supremecourt.gov/opinions/25pdf/24-1068_n7ip.pdf. The controlling authority on federal preemption of state failure to warn claims for pesticide labels.
Federal Insecticide, Fungicide, and Rodenticide Act, 7 U.S.C. 136 et seq., in particular sections 136(bb), 136a(c)(5), 136h(d) and 136v(b). https://www.law.cornell.edu/uscode/text/7/136. The cost benefit registration standard, the inert ingredient confidentiality provision and the labeling uniformity clause.
40 C.F.R. 156.10(g), Labeling requirements for pesticides and devices, ingredient statement. https://www.ecfr.gov/current/title-40/chapter-I/subchapter-E/part-156/subpart-A/section-156.10. Establishes that only the aggregate inert percentage appears on a label.
United States Environmental Protection Agency, Integrated Risk Information System summaries for glyphosate (0057), 2,4-D (0150), dicamba (0223), atrazine (0209), carbaryl (0019), paraquat (0183) and permethrin (0185). https://iris.epa.gov. Source of every reference dose figure cited above.
Agency for Toxic Substances and Disease Registry, Minimal Risk Levels for Hazardous Substances, July 2025 list, together with the toxicological profiles for glyphosate (August 2020), 2,4-D (July 2020), chlorpyrifos (September 1997) and pyrethrins and pyrethroids (September 2003). https://www.atsdr.cdc.gov/mrls/index.html. Source of the minimal risk levels and the mechanism descriptions.
International Agency for Research on Cancer, Monographs Volume 112 (2015) and Volume 113 (2015). https://monographs.iarc.who.int. Source of the Group 2A classification for glyphosate and the Group 2B classification for 2,4-D.
United States Centers for Disease Control and Prevention, National Report on Human Exposure to Environmental Chemicals, biomonitoring data tables, updated through August 3, 2026, including glyphosate added July 19, 2022 and the pyrethroid metabolite series. https://www.cdc.gov/environmental-exposure-report/index.html. Source of the population detection frequencies and the pyrethroid trend.
Chlorpyrifos rulemaking record: 65 Federal Register 76233 (December 6, 2000), 86 Federal Register 48315 (August 30, 2021) and 89 Federal Register 99184 (December 10, 2024). https://www.federalregister.gov. Documents the residential cancellation, the tolerance revocation and the current proposal.
League of United Latin American Citizens v. Regan, 996 F.3d 673 (9th Cir. 2021); Red River Valley Sugarbeet Growers Association v. Regan, 85 F.4th 881 (8th Cir. 2023); National Association of Wheat Growers v. Bonta, No. 20-16758 (9th Cir. Nov. 7, 2023). The litigation that produced and then undid the chlorpyrifos revocation, and the injunction against the California glyphosate warning.
California Food and Agricultural Code sections 11408, 11501, 11501.1 and 12979, and 3 C.C.R. sections 6624 through 6628. https://leginfo.legislature.ca.gov. The field preemption provision and the pesticide use reporting duty, including the home and garden exemption.
California Education Code sections 17608 through 17614, Healthy Schools Act of 2000. https://www.cdpr.ca.gov/wp-content/uploads/2024/10/hsa_final_text.pdf. The notice, posting, recordkeeping and integrated pest management duties that apply to schoolsites and to no one else.
California Civil Code sections 5200, 5205, 5210 and 5235, Davis-Stirling Common Interest Development Act. https://leginfo.legislature.ca.gov. The association records a member may inspect, the deadlines, the three fiscal year lookback and the penalty for wrongful denial.
Commission Implementing Regulation (EU) 2016/1313 of August 1, 2016, and Commission Implementing Regulations (EU) 2018/783, 2018/784 and 2018/785 of May 29, 2018. https://eur-lex.europa.eu. The European co-formulant prohibition and the neonicotinoid greenhouse restriction.
United States Environmental Protection Agency, Standard Operating Procedures for Residential Pesticide Exposure Assessment, Health Effects Division, October 2012, and Exposure Factors Handbook 2011 Edition, EPA/600/R-09/052F, chapters 4 and 5. https://www.epa.gov. Source of the transfer coefficients, hand to mouth frequencies and soil and dust ingestion rates.
United States Environmental Protection Agency, Pesticides Industry Sales and Usage: 2008 to 2012 Market Estimates, January 2017. https://www.epa.gov/sites/default/files/2017-01/documents/pesticides-industry-sales-usage-2016_0.pdf. The most recent federal usage data, covering calendar year 2012.
Toxics Use Reduction Institute, University of Massachusetts Lowell, Natural Grass Playing Field Case Study: Springfield, Massachusetts (June 2019), Organic Grass Playing Fields (July 2019, revised November 2020) and Sports Turf Alternatives Assessment: Cost Analysis (September 2016). https://www.turi.org. Source of the municipal organic land care cost figures.
Peer reviewed toxicology and epidemiology cited above, in full in the bibliography, including the 2018 applicator cohort analysis, the 2019 pooled non-Hodgkin lymphoma analysis, the 2025 lifetime rodent bioassay, the 2026 National Toxicology Program cell system study, the 2015 and 2010 childhood cancer meta analyses, the canine lymphoma and bladder cancer studies, and the 2012 review of United States cancer cluster investigations.
Bibliography
Agency for Toxic Substances and Disease Registry. Minimal Risk Levels (MRLs) for Hazardous Substances. Atlanta: U.S. Department of Health and Human Services, July 2025.
Agency for Toxic Substances and Disease Registry. Toxicological Profile for Glyphosate. Atlanta: U.S. Department of Health and Human Services, August 2020.
Agency for Toxic Substances and Disease Registry. Toxicological Profile for 2,4-Dichlorophenoxyacetic Acid. Atlanta: U.S. Department of Health and Human Services, July 2020.
Andreotti, Gabriella, Stella Koutros, Jonathan N. Hofmann, Dale P. Sandler, Jay H. Lubin, Charles F. Lynch, Catherine C. Lerro, et al. “Glyphosate Use and Cancer Incidence in the Agricultural Health Study.” Journal of the National Cancer Institute 110, no. 5 (2018): 509-516.
Atwood, Donald, and Claire Paisley-Jones. Pesticides Industry Sales and Usage: 2008-2012 Market Estimates. Washington, DC: U.S. Environmental Protection Agency, Office of Pesticide Programs, January 2017.
Bao, Wei, Buyun Liu, Derek W. Simonsen, and Hans-Joachim Lehmler. “Association Between Exposure to Pyrethroid Insecticides and Risk of All-Cause and Cause-Specific Mortality in the General US Adult Population.” JAMA Internal Medicine 180, no. 3 (2020): 367-374.
Barr, Dana B., Robert Allen, Anders O. Olsson, Roberto Bravo, Lucia M. Caltabiano, Anthony Montesano, et al. “Concentrations of Selective Metabolites of Organophosphorus Pesticides in the United States Population.” Environmental Research 99, no. 3 (2005): 314-326.
Bates v. Dow Agrosciences LLC, 544 U.S. 431 (2005).
Bouchard, Maryse F., Jonathan Chevrier, Kim G. Harley, Katherine Kogut, Michelle Vedar, Norma Calderon, et al. “Prenatal Exposure to Organophosphate Pesticides and IQ in 7-Year-Old Children.” Environmental Health Perspectives 119, no. 8 (2011): 1189-1195.
Butts, Thomas R., Bradley K. Fritz, Koffi Badou-Jeremie Kouame, Jason K. Norsworthy, L. Tom Barber, W. Jeremy Ross, et al. “Herbicide Spray Drift from Ground and Aerial Applications: Implications for Potential Pollinator Foraging Sources.” Scientific Reports 12 (2022): article 18017.
California Department of Pesticide Regulation. Summary of Pesticide Use Report Data 2015. Sacramento: California Environmental Protection Agency, April 2017.
California Office of Environmental Health Hazard Assessment. “Glyphosate Listed Effective July 7, 2017 as Known to the State of California to Cause Cancer.” Sacramento: OEHHA, 2017.
Carson v. Monsanto Co., 92 F.4th 980 (11th Cir. 2024) (en banc).
Centers for Disease Control and Prevention and Agency for Toxic Substances and Disease Registry. Guidelines for Examining Unusual Patterns of Cancer and Environmental Concerns. Atlanta: CDC, December 8, 2022.
Centers for Disease Control and Prevention. National Report on Human Exposure to Environmental Chemicals: Biomonitoring Data Tables. Atlanta: National Center for Environmental Health, updated August 3, 2026.
Center for Biological Diversity v. U.S. Environmental Protection Agency, No. 4:20-cv-00555 (D. Ariz. Feb. 6, 2024).
Chen, Mengmeng, Chih-Hui Chang, Lin Tao, and Chensheng Lu. “Residential Exposure to Pesticide During Childhood and Childhood Cancers: A Meta-Analysis.” Pediatrics 136, no. 4 (2015): 719-729.
DiBartolomeis, Michael, Susan Kegley, Pierre Mineau, Rosemarie Radford, and Kendra Klein. “An Assessment of Acute Insecticide Toxicity Loading (AITL) of Chemical Pesticides Used on Agricultural Land in the United States.” PLOS ONE 14, no. 8 (2019): e0220029.
European Commission. Commission Implementing Regulation (EU) 2016/1313 of 1 August 2016 Amending Implementing Regulation (EU) No 540/2011 as Regards the Conditions of Approval of the Active Substance Glyphosate. Official Journal of the European Union L 208 (August 2, 2016): 1.
European Commission. Commission Implementing Regulations (EU) 2018/783, 2018/784 and 2018/785 of 29 May 2018. Official Journal of the European Union L 132 (May 30, 2018).
Glickman, Lawrence T., Malathi Raghavan, Deborah W. Knapp, Patty L. Bonney, and Marcia H. Dawson. “Herbicide Exposure and the Risk of Transitional Cell Carcinoma of the Urinary Bladder in Scottish Terriers.” Journal of the American Veterinary Medical Association 224, no. 8 (2004): 1290-1297.
Goodman, Michael, Joshua S. Naiman, Dina Goodman, and Judy S. LaKind. “Cancer Clusters in the USA: What Do the Last Twenty Years of State and Federal Investigations Tell Us?” Critical Reviews in Toxicology 42, no. 6 (2012): 474-490.
Hallmann, Caspar A., Ruud P. B. Foppen, Chris A. M. van Turnhout, Hans de Kroon, and Eelke Jongejans. “Declines in Insectivorous Birds Are Associated with High Neonicotinoid Concentrations.” Nature 511, no. 7509 (2014): 341-343.
Hardeman v. Monsanto Co., 997 F.3d 941 (9th Cir. 2021).
Hayes, Howard M., Robert E. Tarone, Kenneth P. Cantor, Carl R. Jessen, Dennis M. McCurnin, and Ralph C. Richardson. “Case-Control Study of Canine Malignant Lymphoma: Positive Association with Dog Owner’s Use of 2,4-Dichlorophenoxyacetic Acid Herbicides.” Journal of the National Cancer Institute 83, no. 17 (1991): 1226-1231.
International Agency for Research on Cancer. IARC Monographs on the Evaluation of Carcinogenic Risks to Humans, Volume 112: Some Organophosphate Insecticides and Herbicides. Lyon: IARC, 2015.
International Agency for Research on Cancer. IARC Monographs on the Evaluation of Carcinogenic Risks to Humans, Volume 113: DDT, Lindane, and 2,4-D. Lyon: IARC, 2016.
Kaneene, John B., and RoseAnn Miller. “Re-analysis of 2,4-D Use and the Occurrence of Canine Malignant Lymphoma.” Veterinary and Human Toxicology 41, no. 3 (1999): 164-170.
Kingdom of Sweden v. Commission of the European Communities, Case T-229/04, Court of First Instance, July 11, 2007.
Knapp, Deborah W., Wendy A. Peer, Abass Conteh, Alfred R. Diggs, Bruce R. Cooper, Nita W. Glickman, et al. “Detection of Herbicides in the Urine of Pet Dogs Following Home Lawn Chemical Application.” Science of the Total Environment 456-457 (2013): 34-41.
League of United Latin American Citizens v. Regan, 996 F.3d 673 (9th Cir. 2021).
Linnett, Peter-John. “Permethrin Toxicosis in Cats.” Australian Veterinary Journal 86, nos. 1-2 (2008): 32-35.
Merck Veterinary Manual. “Anticoagulant Rodenticide Poisoning in Animals,” “Metaldehyde Poisoning in Animals,” and “Organophosphate Toxicosis in Animals.” Rahway, NJ: Merck and Co., updated 2024-2026.
Mesnage, Robin, Nicolas Defarge, Joël Spiroux de Vendômois, and Gilles-Éric Séralini. “Major Pesticides Are More Toxic to Human Cells Than Their Declared Active Principles.” BioMed Research International 2014 (2014): article 179691.
Mineau, Pierre, and Cynthia Palmer. The Impact of the Nation’s Most Widely Used Insecticides on Birds: Neonicotinoid Insecticides and Birds. The Plains, VA: American Bird Conservancy, March 2013.
Monsanto Co. v. Durnell, No. 24-1068 (U.S. June 25, 2026).
Murray, Maureen. “Anticoagulant Rodenticide Exposure and Toxicosis in Four Species of Birds of Prey in Massachusetts, USA, 2012-2016, in Relation to Use of Rodenticides by Pest Management Professionals.” Ecotoxicology 26, no. 8 (2017): 1041-1050.
National Association of Wheat Growers v. Bonta, No. 20-16758 (9th Cir. Nov. 7, 2023).
National Research Council, Committee on Pesticides in the Diets of Infants and Children. Pesticides in the Diets of Infants and Children. Washington, DC: National Academy Press, 1993.
Natural Resources Defense Council v. U.S. Environmental Protection Agency, Nos. 20-70787 and 20-70801 (9th Cir. June 17, 2022).
Nishioka, Marcia G., Hazel M. Burkholder, Marielle C. Brinkman, Sydney M. Gordon, and Robert G. Lewis. “Measuring Transport of Lawn-Applied Herbicide Acids from Turf to Home: Correlation of Dislodgeable 2,4-D Turf Residues with Carpet Dust and Carpet Surface Residues.” Environmental Science and Technology 30, no. 11 (1996): 3313-3320.
Nishioka, Marcia G., Hazel M. Burkholder, Marielle C. Brinkman, and Robert G. Lewis. “Distribution of 2,4-Dichlorophenoxyacetic Acid in Floor Dust throughout Homes Following Homeowner and Commercial Lawn Applications: Quantitative Effects of Children, Pets, and Shoes.” Environmental Science and Technology 33, no. 9 (1999): 1359-1365.
Nishioka, Marcia G., Robert G. Lewis, Marielle C. Brinkman, Hazel M. Burkholder, Charles E. Hines, and John R. Menkedick. “Distribution of 2,4-D in Air and on Surfaces inside Residences after Lawn Applications: Comparing Exposure Estimates from Various Media for Young Children.” Environmental Health Perspectives 109, no. 11 (2001): 1185-1191.
Ospina, Maria, Andreas Schütze, Pilar Morales-Agudelo, Meghan Vidal, Lee-Yang Wong, and Antonia M. Calafat. “Exposure to Glyphosate in the United States: Data from the 2013-2014 National Health and Nutrition Examination Survey.” Environment International 170 (2022): 107620.
Ospina, Maria, Lee-Yang Wong, Samuel E. Baker, Amanda B. Serafim, Pilar Morales-Agudelo, and Antonia M. Calafat. “Exposure to Neonicotinoid Insecticides in the U.S. General Population: Data from the 2015-2016 National Health and Nutrition Examination Survey.” Environmental Research 176 (2019): 108555.
Panzacchi, Simona, Eva Tibaldi, Luana De Angelis, et al. “Carcinogenic Effects of Long-Term Exposure from Prenatal Life to Glyphosate and Glyphosate-Based Herbicides in Sprague-Dawley Rats.” Environmental Health 24 (2025): 36.
Park, Sunghwan, Dae-Eun Kim, Sun-Young Park, Hyo-Wook Gil, and Sae-Yong Hong. “Seizures in Patients with Acute Pesticide Intoxication, with a Focus on Glufosinate Ammonium.” Human and Experimental Toxicology 37, no. 4 (2018): 331-337.
Rauh, Virginia, Srikesh Arunajadai, Megan Horton, Frederica Perera, Lori Hoepner, Dana B. Barr, and Robin Whyatt. “Seven-Year Neurodevelopmental Scores and Prenatal Exposure to Chlorpyrifos, a Common Agricultural Pesticide.” Environmental Health Perspectives 119, no. 8 (2011): 1196-1201.
Red River Valley Sugarbeet Growers Association v. Regan, 85 F.4th 881 (8th Cir. 2023).
Roberts, James R., Catherine J. Karr, and the Council on Environmental Health. “Pesticide Exposure in Children.” Pediatrics 130, no. 6 (2012): e1757-e1763 (policy statement) and e1765-e1788 (technical report).
Schaffner v. Monsanto Corp., 113 F.4th 364 (3d Cir. 2024).
Schinasi, Leah, and Maria E. Leon. “Non-Hodgkin Lymphoma and Occupational Exposure to Agricultural Pesticide Chemical Groups and Active Ingredients: A Systematic Review and Meta-Analysis.” International Journal of Environmental Research and Public Health 11, no. 4 (2014): 4449-4527.
Sherif, Mahmoud, Abderrahim Nemmar, Bassam R. Ali, Kahsu Makame, Kolos Nagy, and Balázs Ádám. “Comparative Cytotoxicity and Genotoxicity of Commercial Glyphosate-Based Herbicide Formulations and Co-Formulants in Human Leukocyte and Hepatocyte Cell Lines.” Frontiers in Toxicology 8 (2026): 1770738.
Smith, Anna M., Martyn T. Smith, Michele A. La Merrill, Jane Liaw, and Craig Steinmaus. “2,4-Dichlorophenoxyacetic Acid (2,4-D) and Risk of Non-Hodgkin Lymphoma: A Meta-Analysis Accounting for Exposure Levels.” Annals of Epidemiology 27, no. 4 (2017): 281-289.e4.
Smith-Roe, Stephanie L., Michael J. DeVito, Caroll Co, Sreenivasa C. Ramaiahgari, et al. “Comparative Investigation of the Potential of Glyphosate and Glyphosate-Based Formulations to Cause Oxidative Stress and DNA Damage in Human Skin and Liver Cell Systems.” Toxicological Sciences 209, no. 3 (2026): kfag029.
Takashima-Uebelhoer, Biki B., Lisa G. Barber, Sofija E. Zagarins, Elizabeth Procter-Gray, Audra L. Gollenberg, Antony S. Moore, and Elizabeth R. Bertone-Johnson. “Household Chemical Exposures and the Risk of Canine Malignant Lymphoma, a Model for Human Non-Hodgkin’s Lymphoma.” Environmental Research 112 (2012): 171-176.
Tanner, Caroline M., Freya Kamel, G. Webster Ross, Jane A. Hoppin, Samuel M. Goldman, Monica Korell, et al. “Rotenone, Paraquat, and Parkinson’s Disease.” Environmental Health Perspectives 119, no. 6 (2011): 866-872.
Toxics Use Reduction Institute. Natural Grass Playing Field Case Study: Springfield, MA. Lowell: University of Massachusetts Lowell, June 2019.
Toxics Use Reduction Institute. Organic Grass Playing Fields. Lowell: University of Massachusetts Lowell, July 2019, revised November 2020.
Turner, Michelle C., Donald T. Wigle, and Daniel Krewski. “Residential Pesticides and Childhood Leukemia: A Systematic Review and Meta-Analysis.” Environmental Health Perspectives 118, no. 1 (2010): 33-41.
U.S. Environmental Protection Agency. Exposure Factors Handbook: 2011 Edition. EPA/600/R-09/052F. Washington, DC: National Center for Environmental Assessment, September 2011.
U.S. Environmental Protection Agency. Standard Operating Procedures for Residential Pesticide Exposure Assessment. Washington, DC: Health Effects Division, Office of Pesticide Programs, October 2012.
U.S. Environmental Protection Agency. Revised Glyphosate Issue Paper: Evaluation of Carcinogenic Potential. Washington, DC: Office of Pesticide Programs, December 12, 2017.
U.S. Environmental Protection Agency. Glyphosate Interim Registration Review Decision, Case Number 0178. Washington, DC: Office of Pesticide Programs, January 2020.
U.S. Environmental Protection Agency. Glufosinate: Human Health Risk Assessment. Washington, DC: Health Effects Division, September 3, 2025.
U.S. Environmental Protection Agency. Ecological Mitigation Support Document to Support Endangered Species Strategies, Version 2.0. Washington, DC: Office of Chemical Safety and Pollution Prevention, April 2025.
U.S. National Cancer Institute. Ewing Sarcoma and Undifferentiated Small Round Cell Sarcomas of Bone and Soft Tissue Treatment (PDQ), health professional version, incidence data 2016-2020. Bethesda: NCI, 2025.
Zhang, Luoping, Iemaan Rana, Rachel M. Shaffer, Emanuela Taioli, and Lianne Sheppard. “Exposure to Glyphosate-Based Herbicides and Risk for Non-Hodgkin Lymphoma: A Meta-Analysis and Supporting Evidence.” Mutation Research/Reviews in Mutation Research 781 (2019): 186-206.
This is a public episode. If you'd like to discuss this with other subscribers or get access to bonus episodes, visit theinnovationattorney.substack.com/subscribe