Prevalence of symptoms of neurotoxicity and potential occupational pesticide and solvent exposures among high school students in Starr County, Texas: A pilot study

Numerous harmful occupational exposures affect working teens in the United States. Teens working in agriculture and other heavy-labor industries may be at risk for occupational exposures to pesticides and solvents. The neurotoxicity of pesticides and solvents at high doses is well-known; however, the long term effects of these substances at low doses on occupationally exposed adolescents have not been well-studied. To address this research gap, a secondary analysis of cross-sectional data was completed in order to estimate the prevalence of self-reported symptoms of neurotoxicity among a cohort of high school students from Starr County, Texas, a rural area along the Texas-Mexico border. Multivariable linear regression was used to estimate the association between work status (i.e., no work, farm work, and non-farm work) and symptoms of neurotoxicity, while controlling for age, gender, Spanish speaking preference, inhalant use, tobacco use, and alcohol use. The sample included 1,208 students. Of these, the majority (85.84%) did not report having worked during the prior nine months compared to 4.80% who did only farm work, 6.21% who did only non-farm work, and 3.15% who did both types of work. On average, students reported 3.26 symptoms with a range from 0-16. The most commonly endorsed items across work status were those related to memory impairment. Adolescents employed in non-farm work jobs reported more neurotoxicity symptoms than those who reported that they did not work (Mean 4.31; SD 3.97). In the adjusted multivariable regression model, adolescents reporting non-farm work status reported an average of 0.77 more neurotoxicity symptoms on the Q16 than those who did not work (P = 0.031). The confounding variables included in the final model were all found to be factors significantly associated with report of neurotoxicity symptoms. Future research should examine the relationship between these variables and self-report of symptoms of neurotoxicity.^

Presence of three pesticides in rural drinking water sources in Kenya

A cross-sectional study on the use of three pesticides and their presence in drinking water sources was conducted in Githunguri/Kiaria community between January 1994-March 1995. The main objective of the study was to determine the extent to which some of the pesticides used by the Githunguri/Kiaria agricultural community were polluting their drinking water sources. Due to monetary and physical limitations, only DDT, its isomers and metabolites, carbofuran and carbaryl pesticides were identified and used as surrogates of pollution for the other pesticides.^ The study area was divided into high and low lying geographic surface areas. Thirty-four and 38 water sampling sites were randomly selected respectively. During wet and dry seasons, a total of 144 water samples were collected and analyzed at the Kenya Bureau of Standards Laboratory in Nairobi. Gas chromatography was used to analyze samples for possible presence of DDT, its isomers and metabolites, while high pressure liquid chromatography was used to analyze samples for carbofuran and carbaryl pesticides.^ Six sites testing positively for DDT, its isomers and metabolites represented 19.4% of the total sampled sites, with a mean concentration of 0.00310 ppb in the dry season and 0.0130 ppb in the wet season. All the six sites testing positively for the same pesticide exceeded the European maximum contaminant limit (MCL) in the wet season, and only one site exceeded the European MCL in the dry season.^ Those sites testing positively for carbofuran and carbaryl represented 5.6% of the total sampled sites. The mean concentration for the carbofuran at the sites was 2.500 ppb and 1.590 ppb in the dry and wet seasons respectively. Similarly, the mean concentration for carbaryl at the sites was 0.281 ppb in the dry season and 0.326 ppb in the wet season.^ One site testing positively for carbofuran exceeded the European MCL and WHO set limit in the wet season, while one site testing positively for the same pesticide exceeded the USA, Canada, European and WHO MCLs in the dry season. Similarly, one site which tested positively for carbaryl pesticide exceeded the European MCL in both seasons.^ Out of the 2,587 community members in the study area, 333 (13%) were exposed through their drinking water sources to the three pesticides investigated by this study. As a public health measure, integrated pest management approaches (IPM), protection of the wells and education of the community is necessary to minimize the pollution of the environment and safeguard the drinking water sources from pollution by the pesticides. ^

STUDIES OF DISULFOTON TOLERANCE IN RATS

Disulfoton (O,O, diethyl S-2-(ethylthio)ethyl phosphorodithioate) and other organophosphorus ester compounds are insecticides which inhibit acetylcholinesterase. Chemicals of this class cause signs of toxicity in mammals which are referable to acculmulation of acetylcholine at neuroeffector sites. A tolerance to this toxic action can be induced in experimental animals by giving multiple, sublethal doses of the compounds. There is strong evidence that disulfoton tolerance occurs because of a reduction in the sensitivity of tissues in the affected animals to acetylcholine.^ Experiments were designed to test the possibility that a decrease in the number of muscarinic cholinergic receptors could be downmodulating the sensitivity of tissues to acetylcholine. It was found that, concomitant with the onset of disulfoton tolerance, there was a decrease relative to control values in the specific binding of {('3)H} quinuclidinyl benzilate ({('3)H}QNB, a compound which selectively labels muscarinic cholinergic receptors) to homogenates of rat brain and ileal muscle. The decrease in {('3)H}QNB binding was due to a reduction in the density of muscarinic receptors. There was, however, no alteration in the binding of {('3)H} QNB, or the muscarinic agonists {('3)H} oxotremorine-M and oxotremorine to atria from disulfoton-tolerant rats. The possibility that cardiac tissue was not subsensitive to cholinergic agonists was ruled out in experiments testing the effect of the muscarinic agonist carbachol on heart rate in vivo, and the negative chronotropic effect of oxotremorine on atria from disulfoton-tolerant rats: a clear reduction in the sensitivity to cholinergic agonists was seen in each case. It was, therefore concluded that the specificity and temporal correlation of {('3)H}QNB binding decreases suggested that the loss of muscarinic receptors might play a role in modulating the sensitivity of several tissues to acetylcholine, but that other mechanisms also contribute to the tolerance phenomenon.^ Other experiments revealed that disulfoton tolerance, as measured by resistance to the lethal effects of carbachol, could be induced by feeding rats low levels of the organophosphorus ester in the diet. The concentration of disulfoton used inhibited acetylcholinesterase, but not to the extent that overt signs of toxicity were observed. These results suggested that tolerance to organophosphorus ester insecticides could be induced in rodents with a dosing scheme which more closely modeled the sort of low level exposures which would be expected in humans environmentally or occupationally in contact with these compounds. ^

THE ESTROGENIC PROPERTIES OF O,P'-DDT

o,p'-DDT is a major component of the pesticide DDT (dichlorodiphenyltrichloro ethane, technical grade). Although possessing little insecticidal ability, the o,p'- isomer has two major biological activities which affect mammalian reproductive systems: it is estrogenic, and it induces hepatic mixed function oxidase enzymes. The focus of this work is the characterization of the estrogenic properties of o,p'-DDT in rodents.^ Initial studies examined the ability of o,p'-DDT to bind to and interact with elements of the estrogen receptor system. In an in vitro assay, DDT was shown to compete with 17(beta)-estradiol (E(,2)) for binding to cytoplasmic estrogen receptors (R(,c)) from normal and neoplastic tissues in two rodent species. The following phenomena were studied by measuring receptor levels from uteri (whole uteri and/or uterine cell types) taken from immature ovariectomized rats given one acute injection of o,p'-DDT or E(,2): the translocation of the R(,c) to the nucleus, nuclear receptor (R(,n)) retention patterns, and the subsequent reappearance of R(,c) in the cytoplasm.^ The magnitude and temporal patterns of the biological responses of uteri from similar immature rats were compared following o,p'-DDT and E(,2) exposure. The responses examined included increased "Induced Protein" synthesis (in vitro); and uterine wet weight, DNA synthesis and mitosis (in vivo).^ From dose-response data, correlations were made between R(,n) levels and levels of subsequent biological responses. The aim was to lend support to the premise that biological responses to o,p'-DDT exposure occur as a result of its interaction with the classical estrogen receptor system. Correlation coefficients of 0.95 to 0.98 were obtained between R(,n) levels and levels of responses examined, strongly supporting this hypothesis.^ Finally, o,p'-DDT was shown to be as effective as E(,2) in supporting the growth of a transplantable estrogen-responsive mammary tumor in adult rats (although it was unable to support the growth of a transplantable estrogen-dependent renal tumor in hamsters). While the positive result cannot be directly extrapolated to human or animal exposure to environmental estrogens, it suggests that hyperplastic responses of estrogen sensitive tissues should be considered as a possible toxicity of o,p'-DDT, related compounds having estrogenic properties, and other environmental estrogens. ^

Lindane induced cellular dysfunction in MDCK cells: The role of the peripheral benzodiazepine receptor

The central nervous system GABAA/Benzodiazepine (GABAA/BZD) receptors are targets for many pharmaceutical agents and several classes of pesticides. Lindane is an organochlorine pesticide, although banned from production in the U.S. since 1977, still imported for use as an insecticide and pharmaceutically to control ectoparasites (ATSDR, 1994). Lindane functions as a GABA/BZD receptor antagonist within the central nervous system (CNS). Outside of the CNS, peripheral BZD receptors have been localized to the distal tubule of the kidney. Previous research in our laboratory has shown that incubation of renal cortical slices with lindane can produce an increase in kallikrein leakage, suggesting a distal tubular effect. In this study, Madin Darby Canine Kidney (MDCK) cells were used as an in vitro system to assess the toxicity of lindane. This purpose of this study was to determine if interactions between a renal distal tubular BZD-like receptor and lindane could lead to perturbations in renal distal cellular chloride (Cl−) transport and mitochondrial dysfunction and ultimately, cellular death. ^ Pertubations in renal chloride transport were measured indirectly by determining if lindane altered cell function responsiveness following osmotic stress. MDCK cells pre-treated with lindane and then subjected to osmotic stress remained swollen for up to 12 hours post-stress. Lindane-induced dysfunction was assessed through stress protein induction measured by Western Blot analysis. Lindane pretreatment delayed Heat Shock Protein 72 (HSP72) induction by 36 hours in osmotically stressed cells. Pretreatment with 1 × 10 −5 M LIN followed by osmotic stress elevated p38 and Stress Activated Protein Kinase (SAPK/JNK) at 15 minutes which declined at 30 minutes. Lindane appeared to have no effect on Endoplasmic Reticulum Related Kinase (ERK) induction. Lindane did not effect osmotically stressed LLC-PKI cells, a control cell line. ^ Lindane-treated MDCK cells did not exhibit necrosis. Instead, apoptosis was observed in lindane-treated MDCK cells in both time- and dose-dependent manners. LLC-PKI cells were not affected by LIN treatment. ^ To better understand the mechanism of lindane-induced apoptosis, mitochondrial function was measured. No changes in cytochrome c release or mitochondrial membrane potential were observed suggesting the mitochondrial pathway was not involved in lindane-induced apoptosis. ^ Further research will need to be conducted to determine the mechanism of lindane-induced adverse cellular effects. ^

Back pain in migrant farmworker families and farmworker high school students from Starr County, Texas

Back symptoms are a major global public health problem with the lifetime prevalence ranging between 50-80%. Research suggests that work-related factors contribute to the occurrence of back pain in various industries. Despite the hazardous nature, strenuous tasks, and awkward postures associated with farm work, little is known about back injury and symptoms in farmworker adults and children. Research in the United States is particularly limited. This is a concern given the large proportion of migrant farmworkers in the United States without adequate access to healthcare as well as a substantial number of youth working in agriculture. The present study describes back symptoms and identifies work-related factors associated with back pain in migrant farmworker families and farmworker high school students from Starr County, TX. Two separate datasets were used from two cohort studies "Injury and Illness Surveillance in Migrant Farmworkers (MANOS)" (study A: n=267 families) and "South Texas Adolescent Rural Research Study (STARRS)" (study B: n=345). Descriptive and inferential statistics including multivariable logistic regression were used to identify work-related factors associated with back pain in each study. In migrant farmworker families, the prevalence of chronic back pain during the last migration season ranged from 9.5% among youngest children to 33.3% among mothers. Chronic back pain was significantly associated with increasing age; fairly bad/very bad quality of sleep while migrating; fewer than eight hours of sleep at home in Starr County, TX; depressive symptoms while migrating; self-provided water for washing hands/drinking; weeding at work; and exposure to pesticide drift/direct spray. Among farmworker adolescents, the prevalence of severe back symptoms was 15.7%. Severe back symptoms were significantly associated with being female; history of a prior accident/back injury; feeling tense, stressed, or anxious sometimes/often; lifting/carrying heavy objects not at work; current tobacco use; increasing lifetime number of migrant farmworker years; working with/around knives; and working on corn crops. Overall, results support that associations between work-related exposures and chronic back pain and severe back symptoms remain after controlling for the effect of non-work exposures in farmworker populations. ^

Evaluation of oxidative damage and renal distal tubule cell stress response following exposure to lindane

Lindane, or γ-hexachlorocyclohexane, is a chlorinated hydrocarbon pesticide that was banned from U.S. production in 1976, but until recently continued to be imported and applied for occupational and domestic purposes. Lindane is known to cause central nervous system (CNS), immune, cardiovascular, reproductive, liver, and kidney toxicity. The mechanism for which lindane interacts with the CNS has been elucidated, and involves antagonism of the γ-aminobutyric acid/benzodiazepine (GABAA/BZD) receptor. Antagonism of this receptor results in the inhibition of Cl- channel flux, with subsequent convulsions, seizures, and paralysis. This response makes lindane a desirable defense against arthropod pests in agriculture and the home. However, formulation and application of this compound can contribute to human toxicity. In conjunction with this exposure scenario, workers may be subject to both heat and physical stress that may increase their susceptibility to pesticide toxicity by altering their cellular stress response. The kidneys are responsible for maintaining osmotic homeostasis, and are exposed to agents that undergo urinary excretion. The mechanistic action of lindane on the kidneys is not well understood. Lindane, in other organ systems, has been shown to cause cellular damage by generation of free radicals and oxidative stress. Previous research in our laboratory has shown that lindane causes apoptosis in distal tubule cells, and delays renal stress response under hypertonic stress. Characterizing the mechanism of action of lindane under conditions of physiologic stress is necessary to understand the potential hazard cyclodiene pesticides and other organochlorine compounds pose to exposed individuals under baseline conditions, as well as under conditions of physiologic stress. We demonstrated that exposure to lindane results in oxidative damage and dysregulation of glutathione response in renal distal tubule (MDCK) cells. We showed that under conditions of hypertonic stress, lindane-induced oxidative stress resulted in early onset apoptosis and corresponding down-regulated expression of the anti-apoptotic protein, Bcl-xL. Thus, the interaction of lindane with renal peripheral benzodiazepine receptors (PBR) is associated with attenuation of cellular protective proteins, making the cell more susceptible to injury or death. ^