Abstract:The authors evaluated biomarker responses in caged larvae of the amphibian Rhinella arenarum in water channels during fruit production season and compared them with those elicited by a transient exposure to azinphos methyl (AzM) (0.02-2 mg/L; 4 h), the main pesticide applied in the Alto Valle region, Patagonia, Argentina, taking into account the maximum environmental concentration detected in superficial water (22.5 µg/L). The traditional biomarkers of organophosphate exposure, acetylcholinesterase (AChE) and … Show more
“…The reported maximum environmental concentrations of OP in water currently range in the micrograms per liter order, as it has been recently published for chlorpyrifos (1.16 mg/L) and azinphos methyl (22.5 mg/L) for superficial and ground water in the Alto Valle de Río Negro y Neuquén [4]. This is also suggested by biomarker responses in environmental studies on R. arenarum larvae exposed in irrigation channels [6]. The ponds and channels located in productive orchards are heavily impacted by the 500 tons of formulated pesticides that are applied annually in the region [5].…”
Section: Discussionmentioning
confidence: 71%
“…Organophosphorus pesticides have been detected in superficial and groundwater in the valley of Río Negro and Neuquén, Patagonia, Argentina [4], an area where more than 35,000 hectares are subjected to intensive agriculture. The exceedence of environmental concentrations of OPs in superficial water in this region might range from one to two orders of magnitude, as suggested by biomarker studies performed with amphibian larvae exposed in situ in irrigation channels of the region [6]; although the maximum concentration of the OP azinphos methyl detected in water was 22.5 mg/L, larvae showed altered biomarker responses compatible with 2 mg/L, as suggested by laboratory studies. Moreover, higher concentrations of these pesticides may be transiently present in ponds and irrigation channels of orchards because of aerial drift and runoff, considering that insecticide applications can reach a biweekly frequency in concentrations of approximately 100 g/L per hectare [5].…”
Section: Introductionmentioning
confidence: 80%
“…The ponds and channels located in productive orchards are heavily impacted by the 500 tons of formulated pesticides that are applied annually in the region [5]. This is also suggested by biomarker responses in environmental studies on R. arenarum larvae exposed in irrigation channels [6]. Then, polyamine metabolism and in particular ODC activity becomes an attractive biomarker for OP exposure, not related to the common cholinergic pathway but giving complementary information to be used in environmental evaluations of pesticide impact.…”
Section: Discussionmentioning
confidence: 99%
“…Moreover, higher concentrations of these pesticides may be transiently present in ponds and irrigation channels of orchards because of aerial drift and runoff, considering that insecticide applications can reach a biweekly frequency in concentrations of approximately 100 g/L per hectare [5]. The exceedence of environmental concentrations of OPs in superficial water in this region might range from one to two orders of magnitude, as suggested by biomarker studies performed with amphibian larvae exposed in situ in irrigation channels of the region [6]; although the maximum concentration of the OP azinphos methyl detected in water was 22.5 mg/L, larvae showed altered biomarker responses compatible with 2 mg/L, as suggested by laboratory studies.…”
Organophosphorus pesticides (OPs) are widely applied in the Alto Valle of Río Negro and Neuquén, Argentina, due to intensive fruit growing. Amphibians are particularly sensitive to environmental pollution, and OPs may transiently accumulate in ponds and channels of the region during their reproductive season. Organophosphorus pesticide exposure may alter amphibian embryonic development and the reproductive success of autochthonous species. In the present study, embryos of the common toad Rhinella arenarum were employed to assess developmental alterations and to study polyamine metabolism, which is essential to normal growth, as a possible target underlying the effects of the OP chlorpyrifos. As the duration of chlorpyrifos exposure increased and embryonic development progressed, the median lethal concentration (LC50) values decreased, and the percentage of malformed embryos increased. Developmental arrest was also observed and several morphological alterations were recorded, such as incomplete and abnormal closure of the neural tube, dorsal curvature of the caudal fin, reduction of body size and caudal fin length, atrophy, and edema. An early decrease in ornithine decarboxylase (ODC) activity and polyamine levels was also observed in embryos exposed to chlorpyrifos. The decrease in polyamine contents in tail bud embryos might be a consequence of the reduction in ODC activity. The alteration of polyamine metabolism occurred before embryonic growth was interrupted and embryonic malformations were observed and may be useful as a biomarker in environmental studies.
“…The reported maximum environmental concentrations of OP in water currently range in the micrograms per liter order, as it has been recently published for chlorpyrifos (1.16 mg/L) and azinphos methyl (22.5 mg/L) for superficial and ground water in the Alto Valle de Río Negro y Neuquén [4]. This is also suggested by biomarker responses in environmental studies on R. arenarum larvae exposed in irrigation channels [6]. The ponds and channels located in productive orchards are heavily impacted by the 500 tons of formulated pesticides that are applied annually in the region [5].…”
Section: Discussionmentioning
confidence: 71%
“…Organophosphorus pesticides have been detected in superficial and groundwater in the valley of Río Negro and Neuquén, Patagonia, Argentina [4], an area where more than 35,000 hectares are subjected to intensive agriculture. The exceedence of environmental concentrations of OPs in superficial water in this region might range from one to two orders of magnitude, as suggested by biomarker studies performed with amphibian larvae exposed in situ in irrigation channels of the region [6]; although the maximum concentration of the OP azinphos methyl detected in water was 22.5 mg/L, larvae showed altered biomarker responses compatible with 2 mg/L, as suggested by laboratory studies. Moreover, higher concentrations of these pesticides may be transiently present in ponds and irrigation channels of orchards because of aerial drift and runoff, considering that insecticide applications can reach a biweekly frequency in concentrations of approximately 100 g/L per hectare [5].…”
Section: Introductionmentioning
confidence: 80%
“…The ponds and channels located in productive orchards are heavily impacted by the 500 tons of formulated pesticides that are applied annually in the region [5]. This is also suggested by biomarker responses in environmental studies on R. arenarum larvae exposed in irrigation channels [6]. Then, polyamine metabolism and in particular ODC activity becomes an attractive biomarker for OP exposure, not related to the common cholinergic pathway but giving complementary information to be used in environmental evaluations of pesticide impact.…”
Section: Discussionmentioning
confidence: 99%
“…Moreover, higher concentrations of these pesticides may be transiently present in ponds and irrigation channels of orchards because of aerial drift and runoff, considering that insecticide applications can reach a biweekly frequency in concentrations of approximately 100 g/L per hectare [5]. The exceedence of environmental concentrations of OPs in superficial water in this region might range from one to two orders of magnitude, as suggested by biomarker studies performed with amphibian larvae exposed in situ in irrigation channels of the region [6]; although the maximum concentration of the OP azinphos methyl detected in water was 22.5 mg/L, larvae showed altered biomarker responses compatible with 2 mg/L, as suggested by laboratory studies.…”
Organophosphorus pesticides (OPs) are widely applied in the Alto Valle of Río Negro and Neuquén, Argentina, due to intensive fruit growing. Amphibians are particularly sensitive to environmental pollution, and OPs may transiently accumulate in ponds and channels of the region during their reproductive season. Organophosphorus pesticide exposure may alter amphibian embryonic development and the reproductive success of autochthonous species. In the present study, embryos of the common toad Rhinella arenarum were employed to assess developmental alterations and to study polyamine metabolism, which is essential to normal growth, as a possible target underlying the effects of the OP chlorpyrifos. As the duration of chlorpyrifos exposure increased and embryonic development progressed, the median lethal concentration (LC50) values decreased, and the percentage of malformed embryos increased. Developmental arrest was also observed and several morphological alterations were recorded, such as incomplete and abnormal closure of the neural tube, dorsal curvature of the caudal fin, reduction of body size and caudal fin length, atrophy, and edema. An early decrease in ornithine decarboxylase (ODC) activity and polyamine levels was also observed in embryos exposed to chlorpyrifos. The decrease in polyamine contents in tail bud embryos might be a consequence of the reduction in ODC activity. The alteration of polyamine metabolism occurred before embryonic growth was interrupted and embryonic malformations were observed and may be useful as a biomarker in environmental studies.
“…This allows overcoming a high variability in the responses depending on seasonal aspects, duration and frequency of contamination episodes, and many other factors including the organisms themselves. Even those biomarkers considered specific for a group of toxicants may show diverging responses, as reported for the biomarker of neurotoxic effects acetylcholinesterase, which was induced in R. arenarum larvae exposed in situ for 2 wk in an orchard receiving organophosphate pesticide applications [28].…”
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