Harvesters in strawberry fields: A literature review of pesticide exposure, an observation of their work activities, and a model for exposure prediction.

Strawberry harvesters hand-pick fruit that may result in pesticide exposure from hand foliar contact. This paper included a review of publications on harvester pesticide exposure, an observation of their work activities, and development of an alternative model for pesticide exposure prediction. Previous studies monitored the dermal pesticide exposure of strawberry harvesters and found most of the exposure (>70%) was on the hands. Exposure rates (ERs) were calculated as pesticide amount on the skin per hour worked, assuming foliar contact is proportional to daily work hours. Transfer factors (TFs), used for predicting exposure, were calculated by dividing the ER by the amount of dislodgeable foliar pesticide residue. However, the ERs for harvesters working in the same field at the same time varied by as much as 10-fold, and TFs calculated from different studies varied by up to 100-fold. We tested the assumption of foliar contact time being proportional to daily work hours. We observed full work-day activities of 32 strawberry harvesters. We found that their foliar contact time per work minute differed by up to 46%. We suggested using the amount of strawberries picked to predict harvester foliar contact. For all observed harvesters, their foliar contact time per kg of strawberries picked was 35±5 s. This value was similar among harvesters with varying years of experience, of different gender, and using gloves or not. We proposed a predictive model using the amount of strawberries picked to predict harvester pesticide exposure. The exposure predicted by the model is close to the exposure measured in previous monitoring studies (R2: 0.84). The model slope is 0.33±0.03 × 103 cm2/kg. Model prediction accuracy was confirmed by monitoring captan exposure to harvesters in two fields. The model may be used as a quick screening method to estimate pesticide exposure before conducting complex human monitoring research.

Factors affecting the estimated probabilistic acute dietary exposure to captan from apple consumption.

The effect of the number of pesticide residue values below the LOQ/LOD of analytical methods, the variability of residues in individual fruits, mass of fruit units and the number of bootstrap iterations was studied on the probabilistically estimated acute exposure of consumers. The 4720 daily apple consumption data and the results of 1239 apple sample analyses for captan residues, performed within the Hungarian monitoring programme between 2005 and 2011, were used in this study as model matrix. Up to about 95th percentile exposure (µg/(kg bw·day)), simply multiplying each residue in composite samples with each consumption value gave similar estimates to those obtained with the complex procedure taking also into account the mass of and residues in individual fruits. However, the exposure above the 95th percentile calculated with the complex procedure gradually increased with increasing percentile level compared to the simple procedure. Including the high number of non-detects reduced the estimated exposure, which was the highest when only the residues measured in treated fruits were taken into account. The number of bootstrap iterations between 100 and 10,000 did not significantly affect the calculated exposure. The 99.99th percentile exposure amounted to 17.9% of the acute reference dose of 300 µg/(kg bw·day) for women of childbearing age.

Toxicokinetics of captan and folpet biomarkers in orally exposed volunteers.

The time courses of key biomarkers of exposure to captan and folpet was assessed in accessible biological matrices of orally exposed volunteers. Ten volunteers ingested 1 mg kg(-1) body weight of captan or folpet. Blood samples were withdrawn at fixed time periods over the 72 h following ingestion and complete urine voids were collected over 96 h post-dosing. The tetrahydrophthalimide (THPI) metabolite of captan along with the phthalimide (PI) and phthalic acid metabolites of folpet were then quantified in these samples. Plasma levels of THPI and PI increased progressively after ingestion, reaching peak values ~10 and 6 h post-dosing, respectively; subsequent elimination phase appeared monophasic with a mean elimination half-life (t(½) ) of 15.7 and 31.5 h, respectively. In urine, elimination rate time courses of PI and phthalic acid evolved in parallel, with respective t(½) of 27.3 and 27.6 h; relatively faster elimination was found for THPI, with mean t(½) of 11.7 h. However, phthalic acid was present in urine in 1000-fold higher amounts than PI. In the 96 h period post-treatment, on average 25% of folpet dose was excreted in urine as phthalic acid as compared with only 0.02% as PI. The corresponding value for THPI was 3.5%. Overall, THPI and PI appear as interesting biomarkers of recent exposure, with relatively short half-lives; their sensitivity to assess exposure in field studies should be further verified. Although not a metabolite specific to folpet, the concomitant use of phthalic acid as a major biomarker of exposure to folpet should also be considered.

Toxicokinetic modeling of captan fungicide and its tetrahydrophthalimide biomarker of exposure in humans.

Measurement of tetrahydrophthalimide (THPI) in urine has been used for the biomonitoring of exposure to the widely used captan fungicide in workers. To allow a better understanding of the toxicokinetics of captan and its key biomarker of exposure, a human multi-compartment model was built to simulate the transformation of captan into THPI and its subsequent excretion while accounting for other non-monitored metabolites. The mathematical parameters of the model were determined from best-fits to the time courses of THPI in blood and urine of five volunteers administered orally 1mg/kg and dermally 10mg/kg of captan. In the case of oral administration, the mean elimination half-life of THPI from the body (either through faeces, urine or metabolism) was found to be 13.43 h. In the case of dermal application, mean THPI elimination half-life was estimated to be 21.27 h and was governed by the dermal absorption rate. The average final fractions of administered dose recovered in urine as THPI were 3.6% and 0.02%, for oral and dermal administration, respectively. Furthermore, according to the model, after oral exposure, only 8.6% of the THPI formed in the GI reaches the bloodstream. As for the dermal absorption fraction of captan, it was estimated to be 0.09%. Finally, the average blood clearance rate of THPI calculated from the oral and dermal data was 0.18 ± 0.03 ml/h and 0.24 ± 0.6 ml/h while the predicted volume of distribution was 3.5 ± 0.6l and 7.5 ± 1.9l, respectively. Our mathematical model is in complete accordance with both independent measurements of THPI levels in blood (R(2)=0.996 for oral and R(2)=0.908 for dermal) and urine (R(2)=0.979 for oral and R(2)=0.982 for dermal) as well as previous experimental data published in the literature.

Determinants of captan air and dermal exposures among orchard pesticide applicators in the Agricultural Health Study.

OBJECTIVES: To identify and quantify determinants of captan exposure among 74 private orchard pesticide applicators in the Agricultural Health Study (AHS). To adjust an algorithm used for estimating pesticide exposure intensity in the AHS based on these determinants and to compare the correlation of the adjusted and unadjusted algorithms with urinary captan metabolite levels. METHODS: External exposure metrics included personal air, hand rinse, and dermal patch samples collected from each applicator on 2 days in 2002-2003. A 24-h urine sample was also collected. Exposure determinants were identified for each external metric using multiple linear regression models via the NLMIXED procedure in SAS. The AHS algorithm was adjusted, consistent with the identified determinants. Mixed-effect models were used to evaluate the correlation between the adjusted and unadjusted algorithm and urinary captan metabolite levels. RESULTS: Consistent determinants of captan exposure were a measure of application size (kilogram of captan sprayed or application method), wearing chemical-resistant (CR) gloves and/or a coverall/suit, repairing spray equipment, and product formulation. Application by airblast was associated with a 4- to 5-fold increase in exposure as compared to hand spray. Exposure reduction to the hands, right thigh, and left forearm from wearing CR gloves averaged ∼80%, to the right and left thighs and right forearm from wearing a coverall/suit by ∼70%. Applicators using wettable powder formulations had significantly higher air, thigh, and forearm exposures than those using liquid formulations. Application method weights in the AHS algorithm were adjusted to nine for airblast and two for hand spray; protective equipment reduction factors were adjusted to 0.2 (CR gloves), 0.3 (coverall/suit), and 0.1 (both). CONCLUSIONS: Adjustment of application method, CR glove, and coverall weights in the AHS algorithm based on our exposure determinant findings substantially improved the correlation between the AHS algorithm and urinary metabolite levels.

Captan exposure and evaluation of a pesticide exposure algorithm among orchard pesticide applicators in the Agricultural Health Study.

Pesticide exposure assessment in the Agricultural Health Study (AHS) has relied upon two exposure metrics: lifetime exposure days and intensity-weighted lifetime exposure days, the latter incorporating an intensity score computed from a questionnaire-based algorithm. We evaluated this algorithm using actual fungicide exposure measurements from AHS private orchard applicators. Captan was selected as a marker of fungicide exposure. Seventy-four applicators from North Carolina and Iowa growing apples and/or peaches were sampled on 2 days they applied captan in 2002 and 2003. Personal air, hand rinse, 10 dermal patches, a pre-application first-morning urine and a subsequent 24-h urine sample were collected from each applicator per day. Environmental samples were analyzed for captan, and urine samples were analyzed for cis-1,2,3,6-tetrahydrophthalimide (THPI). Task and personal protective equipment information needed to compute an individual's algorithm score was also collected. Differences in analyte detection frequency were tested in a repeated logistic regression model. Mixed-effects models using maximum-likelihood estimation were employed to estimate geometric mean exposures and to evaluate the measured exposure data against the algorithm. In general, captan and THPI were detected significantly more frequently in environmental and urine samples collected from applicators who used air blast sprayers as compared to those who hand sprayed. The AHS pesticide exposure intensity algorithm, while significantly or marginally predictive of thigh and forearm captan exposure, respectively, did not predict air, hand rinse or urinary THPI exposures. The algorithm's lack of fit with some exposure measures among orchard fungicide applicators may be due in part to the assignment of equal exposure weights to air blast and hand spray application methods in the current algorithm. Some modification of the algorithm is suggested by these results.

Modelling non-systemic pesticide residues in fruits with initial deposit variability and weather effects.

A flexible and generic model was developed to predict the decline of residues of a non-systemic pesticide for both single and multi-spray situations as well as for different tree canopy zones. The model predicts not only the average residue levels, but also the confidence interval of the residues through either a deterministic or a stochastic approach. This generic model includes several key aspects of residue fates in the environment: initial deposit, physical loss and growth dilution. The model considers a tree canopy in three distinct zones for which initial deposition of pesticides may differ. In addition to predicting the average residue within each zone, it also estimates the 95 and 99% confidence intervals of residues on individual fruit within each zone. For the purpose of evaluation, this model was parameterized specifically for captan, one of the most important non-systemic fungicides used to control disease in horticultural crops. The observed average initial deposit for each zone was used in the evaluation. The overall correlation between predicted average residues and those observed on apple fruit in two applications was 0.93. Confidence intervals were also predicted accurately.

Urine mutagenicity and lymphocyte DNA damage in fruit growers occupationally exposed to the fungicide captan.

AIMS: To determine haematological parameters, urine mutagenicity (on three Salmonella typhimurium strains), and DNA damage (using the comet assay) in mononuclear leucocytes of farmers before and after a one-day spraying period of pear and apple trees with the fungicide captan in usual conditions. METHODS: Fruit growers were exposed to captan during the 1998 (n = 12) and/or the 2000 spraying seasons (n = 17). Biological samples were collected on the morning of the day of spraying (S1), the evening after spraying (S2), and the morning of the day after (S3). The UK Predictive Operator Exposure Model (UK-POEM) was used to quantify pesticide exposure intensity. RESULTS: No effect was observed on haematological parameters for these two spraying seasons. Proportions of mutagenic urine samples did not significantly differ between S1 and S2/S3 sampling points. In contrast with strains TA97a and YG1041 mainly sensitive to frameshift mutations, a positive trend was observed between the difference (S3-S1) of mutagenic power on strain TA102 detecting base-pair mutations and the exposure predicted value given by UK-POEM, mainly due to parameters related to protective clothing. No significant variations in DNA damage levels were observed between S1 and S3, nor were correlations observed with parameters of pesticide exposure. CONCLUSIONS: A one-day spraying period with captan and other pesticides does not significantly induce DNA damages in mononuclear leucocytes. In contrast, an inefficient protective clothing could correlate with an increase in urine mutagenicity as assessed by the TA102 tester strain.

Occupational dermatitis in Danish gardeners and greenhouse workers (II). Etiological factors.

The aim of the study was to assess the distribution of different types of occupational eczema among employees in floristry and detect the allergens most commonly involved. Based on a postal questionnaire, 253 gardeners and greenhouse workers with occupational skin symptoms and 52 randomly-selected without symptoms were examined and patch tested. Routine tests comprised the standard series, the Compositae mix, feverfew and 3 fungicides, with additional testing based on case records. 184 persons from the symptom group and 1 from the random group had occupational eczema. Irritant occupational contact eczema was suspected in 150 persons (59%). Nevertheless, 48% of the 250 persons patch tested had at least 1 positive reaction, most frequently to nickel, followed by Compositae which were positive in 25 cases (10%), of whom 24 were possibly occupationally sensitized. 13 persons from symptom group had positive reactions to fungicides. Occupational allergic eczema was suspected in 43 persons (17%), most often caused by plants belonging to the Compositae, Geraniaceae and Liliaceae families. New plant sensitizers were Exacum affine and Begonia lorraine. Exposure to specific plant species seemed to be the most important eliciting factors in both allergic and irritant occupational dermatitis in floristry, and preventive measures should include reduction of contact with plants.

Effects of pesticide mixtures at the acceptable daily intake levels on rat carcinogenesis.

Possible modifying effects of pesticide mixtures on tumorigenesis were investigated with medium-term carcinogenesis protocols for rapid detection of carcinogenic agents using male F344 rats. In the 8-wk liver model, administration of 20 pesticides (19 organophosphorus compounds and one organochlorine), added to the diet each at acceptable daily intake (ADI) levels, did not enhance rat liver preneoplastic lesion development initiated by diethylnitrosamine. In contrast, a mixture of these 20 pesticides at 100 times the ADI significantly increased the number and area of liver lesions. In the second experiment using a multi-organ carcinogenicity protocol of 28 wk, mixtures of 40 pesticides (high production examples) or 20 pesticides (suspected carcinogens) added to the diet at their respective ADI levels did not modulate carcinogenesis in any organ initiated by five known potent carcinogens in combination. These results thus provide direct support for the safety factor (usually 100) approach using ADI values for the quantitative risk evaluation of pesticides.

The incorporation of radiolabelled sulphur from captan into protein and its impact on a DNA binding study.

Repeated administration of high doses of captan is known to produce tumours specifically in the duodenum of mice. Captan is not carcinogenic in the rat. In this study, DNA purified from the liver, stomach, duodenum and jejenum of mice dosed with 35S radiolabelled captan was found to contain radioactivity equivalent to Covalent Binding Indices in the range 38-91; that from the bone marrow had a CBI of 2.8. The distribution of radioactivity between the various tissues did not reflect the target organ specificity of captan. Attempts to further purify the DNA samples using caesium chloride gradients resulted in partial separation of the radioactivity from the DNA suggesting that covalent binding to the DNA may not have occurred. A study of the chemical breakdown of captan showed that captan is unstable, producing a variety of potentially reactive species containing sulphur. Evidence was further obtained to show that the sulphur of captan is incorporated into endogenous amino acids and protein. Hepatic DNA from mice dosed with 35S radiolabelled N-acetylcysteine, and two thiazolidine derivatives which are analogous to known metabolites of captan, was radiolabelled to a similar extent to that from captan treated mice. Furthermore, the DNA from each of these treatments had similar properties on caesium chloride gradients. It was concluded that the radioactivity associated with DNA in the captan DNA binding study was present in the low levels of protein which are always associated with purified DNA samples.

Estudo da influência de agrotóxicos sobre o desenvolvimento do Rhizobium leguminosarum biovar phaseoli / Study of the agrotoxics influence over the development of the Rhizobium leguminosarum biovar phaseoli

As bactérias fixadoras de nitrogênio atmosférico, via processo simbiótico, repassam N2 às leguminosas sob forma de amônia, proporcionando aumento na produçäo de alimentos protéicos, reciclagem biológica de nitrogênio do ar, evitando o alto custo da adubaçäo nitrogenada e o efeito potencialmente poluidor do nitrato lixiviado. Testou-se quatro estirpes de Rhizobium phaseoli frente a quatro fungicidas indicados para o tratamento de sementes de Phaseolus vulgaris L. (feijoeiro), no Estado do Rio Grande o sul (Brasil). Considerando-se as dosagens recomendadas dos fungicidas, houve crescimento bacteriano das quatro estirpes frente a Benomil e inibiçäo total frente a Captan; porém, para PCNB e Thiram, a resistência dependeu do tipo de estirpe. Observou-se que näo há influência de fungicidas sobre o desenvolvimento do Rhizobium phaseoli quando seleciona-se a estirpe adequada ao fungicida corretamente dosado.

Captan metabolism in humans yields two biomarkers, tetrahydrophthalimide (THPI) and thiazolidine-2-thione-4-carboxylic acid (TTCA) in urine.

Captan fungicide (N-(trichloromethylthio)-4-cyclohexene-1,2-dicarboximide) metabolism in two human volunteers rapidly yields THPI (tetrahydrophthalimide) and TTCA (thiazolidine-2-thione-4-carboxylic acid). The work was done to evaluate usefulness of TTCA and THPI as biomarkers of occupational exposure and to compare human and rat dermal absorption and metabolism. THPI in 12h urine ranged from MDL (5 ppb) to 640 ppb and was stable for at least one year. TTCA was also a stable metabolite, but the MDL was 50 ppb. THPI was detectable in urine for 72 hours following oral dosages of 1 mg/kg, but most was eliminated 0-24 h. No THPI was detectable in urine following application of a chloroform solution to hands, forearms, or inguinal region. Dermal absorption and metabolism of captan are substantially different in humans and rats.

Subchronic oral toxicity study of captafol in B6C3F1 mice.

The effects of subchronic administration of captafol were studied in B6C3F1 mice given dose levels of 0, 0.3, 0.625, and 1.25% in the diet for 12 wk. There was a dose-related decrease in body weight gain during the 12-wk experiment and a loss of body weight in the 1.25% group of both sexes. Whiles the mice given captafol consumed less diet than the control mice, this was not directly dose-related. The relative weights of liver demonstrated a tendency for dose-dependent increase. Light-microscopic examination revealed cytoplasmic vacuolar degeneration, depending in severity on the dosage, in the livers of both sexes given captafol. In conclusion, the findings obtained from the present subchronic toxicity study indicated the liver to be a primary target organ.

Dermal penetration of [14C]captan in young and adult rats.

Age dependence in dermal absorption has been a major concern in risk assessment. Captan, a chloroalkyl thio heterocyclic fungicide, was selected for study of age dependence as representative of this class of pesticides. Dermal penetration of [14C]captan applied at 0.286 mumol/cm2 was determined in young (33-d-old) and adult (82-d-old) female Fischer 344 rats in vivo and by two in vitro methods. Dermal penetration in vivo at 72 h was about 9% of the recovered dose in both young and adult rats. The percentage penetration was found to increase as dosage (0.1, 0.5, 2.7 mumol/cm2) decreased. Two in vitro methods gave variable dermal penetration values compared with in vivo results. A static system yielded twofold higher dermal penetration values compared with in vivo results for both young and adult rats. A flow system yielded higher dermal penetration values in young rats and lower penetration values in adults compared with in vivo results. Concentration in body, kidney, and liver was less in young than in adult rats given the same absorbed dosage. A physiological pharmacokinetic model was developed having a dual compartment for the treated skin and appeared to describe dermal absorption and disposition well. From this model, tissue/blood ratios of captan-derived radioactivity for organs were found to range from 0.35 to 3.4, indicating no large uptake or binding preferences by any organ. This preliminary pharmacokinetic model summarizes the experimental findings and could provide impetus for more complex and realistic models.

Carcinogenicity of captafol in F344/DuCrj rats.

Captafol was administered at dietary levels of 0 (control), 750 and 1,500 parts per million (ppm) to groups of 50 male and 50 female F344/DuCrj rats for 104 weeks, and then all animals were maintained without captafol for a further 8 weeks, and killed in week 113. Renal cell carcinoma was found in eight of 50 male rats treated with 1,500 ppm and in one of 50 male rats treated with 750 ppm of captafol. The incidences of renal adenomas, including micro-adenomas, and basophilic altered cell tubules were significantly higher in both sexes treated with captafol than in controls, and the increases were apparently dose-dependent except that of adenomas in females. The incidences of neoplastic and preneoplastic lesions of the kidney in captafol-treated animals were higher in males than in females. Captafol also induced hepatocellular carcinomas in four of 50 female rats in the 1,500 ppm group. The incidences of hyperplastic (neoplastic) nodules and foci of cellular alterations in the liver were also significantly increased in both sexes treated with captafol, the increases being dose-dependent. In conclusion, captafol induced renal cell carcinomas in male rats and hepatocellular carcinomas in female rats.

Mammalian host- and fluid-mediated mutagenicity assays of captan and streptozotocin in Salmonella typhimurium.

The mutagenicity of captan and of streptozotocin was tested in vivo by reversion of hisG46 base-pair substitution histidine auxotrophs of Salmonella typhimurium in the peritoneal cavity or in blood, plasma or urine of rats or mice. Genetic response was determined by the frequency of revertants (quantitative test) or by the number of revertants per plate (semiquantitative test). In quantitative HMA captan gave negative results following 3 hourly 500 mg/kg s.c. doses or 1000 mg/kg oral dose in mice with the hisG46 mutant or 2000 mg/kg oral dose in rats with the hisG46, uvrB (TA1950) mutant. The positive control SZN induced many reversions at 0.5 mg/kg i.p. or 10 or 100 mg/kg oral doses. In semiquantitative in vivo blood or urine assays captan gave negative results after a 250 mg/kg oral dose with hisG46. SZN in the same experiment gave positive results in both semiquantitative and quantitative in vivo blood assays following 1000 mg/kg i.p. or 2000 mg/kg oral doses in the rat with TA1950. Rat blood mixed with captan for 45 min before adding TA1950 cells inactivated 1000 mug captan/ml but not 5000 mg/ml in the semiquantitative test. Corresponding figures in the quantitative test were 500 mu/ml and 1000 mug/ml. Rat plasma inactivated the mutagenicity of about 10 times less captan than rat blood. Human blood inactivated about as much captan as rat blood. The mutagenicity of captan was inactivated more efficiently than of SZN by blood. The results of the experiments suggested that captan's mutagenicity is probably inactivated by glutathione of the erythrocytes. Rat S-9 liver microsomal fraction also strongly decreased captan's mutagenicity in a semiquantitative test with the R factor, uvrB, hisG46 (TA100) mutant.