Abstract:The organophosphorous compound azinphosmethyl (AzMe) is applied extensively in northern Patagonia (southern Argentina) to manage codling moths (Cydia pomonella). This area is irrigated by fast-flowing channels that provide a favorable habitat for many species, including amphipods (Hyalella curvispina) and a field-mixed population of black flies (Simulium bonaerense, Simulium wolffhuegeli, and Simulium nigristrigatum). In the present study, AzMe susceptibility and carboxylesterase (CarbE) activity from both ins… Show more
“…). This was previously stated in the 48‐h bioassays (Anguiano et al, ). The calculated LC 50 values are listed in Table .…”
Section: Resultssupporting
confidence: 71%
“…Survival was monitored daily, mortality was registered, and dead animals were removed. Animals were considered to be dead if no movement of the pleopods was visible during a 20‐s observation period using a stereoscopic microscope (Anguiano et al, ).…”
Section: Methodsmentioning
confidence: 99%
“…To compare the toxicity of AM determined in this study for H. curvispina inhabiting F. Oro irrigation channels, analysis of species sensitivity distributions was performed (ECOFRAM, 1999; Montagna et al, 2011) using acute toxicity data (LC 50 values) for aquatic freshwater organisms. Other amphipods (Nebeker and Gaufin, ; Sanders, ; Johnson and Finley, ; Mayer and Ellersieck, ; Ankley and Collard, 1995; Pantani et al, ; Anguiano et al, ) and local aquatic freshwater vertebrates evaluated in our previous studies (Ferrari et al, b) were included in the probabilistic analysis. The species were ranked by decreasing sensitivity and the rank was transformed to percentile values: [ i /( n + 1)], where i is the species rank, and n is the total number of species listed (ECOFRAM, 1999).…”
Section: Methodsmentioning
confidence: 99%
“…Both, GSH and antioxidant enzymes, have been extensively evaluated in ecotoxicological studies performed with diverse aquatic species such as fish species, amphibian embryos, aquatic gastropods, and oligochaetes (Oruç and Üner, ; Ferrari et al, ; Kristoff et al, ). Most aquatic invertebrate species exhibit higher sensitivity to OP and carbamates when compared to vertebrate species; however, in Argentina, few studies on the effects of OP have been carried out on aquatic invertebrates (Jergentz et al, ; Anguiano et al, ; Kristoff et al, ).…”
Section: Introductionmentioning
confidence: 99%
“…We have previously reported the occurrence of different populations of amphipods with differential susceptibility to OP, obtained from fruit‐producing and pristine areas, in a comparative study including other invertebrates as well (Anguiano et al, ). We could determine that an increased basal activity of the detoxifying enzyme CabE was in part responsible for the resistance to OP in these species.…”
We evaluated the acute toxicity and biochemical effects of the organophosphorus pesticide azinphos methyl (AM) in the amphipod Hyalella curvispina that inhabits ponds and irrigation channels of an intensive fruit-producing region in Rio Negro and Neuquén valley, North Patagonia, Argentina. The analysis by nonlinear regression of data from the 96 h-acute toxicity tests indicated the coexistence of two subpopulations of H. curvispina with different susceptibilities to AM. The 96 h-LC₅₀ for the resistant subpopulation (166 ± 56 μg/L) was 216-fold higher than the 96h-LC₅₀ value for the susceptible one (0.77 ± 1.33 μg/L).The two subpopulations could not be distinguished based on the biochemical measurements in control amphipods. Cholinesterase activity was significantly inhibited in AM-exposed amphipods in a concentration-dependent manner. The IC₅₀ value obtained after 96 h of exposure (2.18 ± 1.95 μg/L) was significantly lower than the 48 h-IC₅₀ value (29.6 ± 17.4 μg/L). Carboxylesterase activity was significantly inhibited after 48 h of exposure to 12.5 and 62.5 μg/L AM (inhibition, 51%). This enzyme was thus able to protect cholinesterase from inhibition at 12.5 μg/L AM. Reduced glutathione and catalase showed a significant increase after 24 h of exposure as an adaptive response to AM, whereas glutathione S-transferase activity was not significantly modified. The analysis of species sensitivity distribution showed that both subpopulations of H. curvispina were more tolerant to AM than most amphipod species, and that the susceptible subpopulation was more sensitive to AM than the other local aquatic species analyzed. The maximum concentration of AM in drainage water within the fruit-producing area reported by other studies would affect most of the amphipod species (99%) and also a 44% of local aquatic ones. The results obtained in this study point out the usefulness of including amphipods like H. curvispina in ecotoxicity studies and monitoring programs to perform pesticide risk assessments.
“…). This was previously stated in the 48‐h bioassays (Anguiano et al, ). The calculated LC 50 values are listed in Table .…”
Section: Resultssupporting
confidence: 71%
“…Survival was monitored daily, mortality was registered, and dead animals were removed. Animals were considered to be dead if no movement of the pleopods was visible during a 20‐s observation period using a stereoscopic microscope (Anguiano et al, ).…”
Section: Methodsmentioning
confidence: 99%
“…To compare the toxicity of AM determined in this study for H. curvispina inhabiting F. Oro irrigation channels, analysis of species sensitivity distributions was performed (ECOFRAM, 1999; Montagna et al, 2011) using acute toxicity data (LC 50 values) for aquatic freshwater organisms. Other amphipods (Nebeker and Gaufin, ; Sanders, ; Johnson and Finley, ; Mayer and Ellersieck, ; Ankley and Collard, 1995; Pantani et al, ; Anguiano et al, ) and local aquatic freshwater vertebrates evaluated in our previous studies (Ferrari et al, b) were included in the probabilistic analysis. The species were ranked by decreasing sensitivity and the rank was transformed to percentile values: [ i /( n + 1)], where i is the species rank, and n is the total number of species listed (ECOFRAM, 1999).…”
Section: Methodsmentioning
confidence: 99%
“…Both, GSH and antioxidant enzymes, have been extensively evaluated in ecotoxicological studies performed with diverse aquatic species such as fish species, amphibian embryos, aquatic gastropods, and oligochaetes (Oruç and Üner, ; Ferrari et al, ; Kristoff et al, ). Most aquatic invertebrate species exhibit higher sensitivity to OP and carbamates when compared to vertebrate species; however, in Argentina, few studies on the effects of OP have been carried out on aquatic invertebrates (Jergentz et al, ; Anguiano et al, ; Kristoff et al, ).…”
Section: Introductionmentioning
confidence: 99%
“…We have previously reported the occurrence of different populations of amphipods with differential susceptibility to OP, obtained from fruit‐producing and pristine areas, in a comparative study including other invertebrates as well (Anguiano et al, ). We could determine that an increased basal activity of the detoxifying enzyme CabE was in part responsible for the resistance to OP in these species.…”
We evaluated the acute toxicity and biochemical effects of the organophosphorus pesticide azinphos methyl (AM) in the amphipod Hyalella curvispina that inhabits ponds and irrigation channels of an intensive fruit-producing region in Rio Negro and Neuquén valley, North Patagonia, Argentina. The analysis by nonlinear regression of data from the 96 h-acute toxicity tests indicated the coexistence of two subpopulations of H. curvispina with different susceptibilities to AM. The 96 h-LC₅₀ for the resistant subpopulation (166 ± 56 μg/L) was 216-fold higher than the 96h-LC₅₀ value for the susceptible one (0.77 ± 1.33 μg/L).The two subpopulations could not be distinguished based on the biochemical measurements in control amphipods. Cholinesterase activity was significantly inhibited in AM-exposed amphipods in a concentration-dependent manner. The IC₅₀ value obtained after 96 h of exposure (2.18 ± 1.95 μg/L) was significantly lower than the 48 h-IC₅₀ value (29.6 ± 17.4 μg/L). Carboxylesterase activity was significantly inhibited after 48 h of exposure to 12.5 and 62.5 μg/L AM (inhibition, 51%). This enzyme was thus able to protect cholinesterase from inhibition at 12.5 μg/L AM. Reduced glutathione and catalase showed a significant increase after 24 h of exposure as an adaptive response to AM, whereas glutathione S-transferase activity was not significantly modified. The analysis of species sensitivity distribution showed that both subpopulations of H. curvispina were more tolerant to AM than most amphipod species, and that the susceptible subpopulation was more sensitive to AM than the other local aquatic species analyzed. The maximum concentration of AM in drainage water within the fruit-producing area reported by other studies would affect most of the amphipod species (99%) and also a 44% of local aquatic ones. The results obtained in this study point out the usefulness of including amphipods like H. curvispina in ecotoxicity studies and monitoring programs to perform pesticide risk assessments.
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 carboxylesterase, were inhibited in tadpoles after one week of exposure in channels potentially receiving pesticide drift, whereas the antioxidant glutathione (GSH) and the detoxifying activity of GSH S-transferase (GST) were induced. In a two-week monitoring study, AChE activity was induced in larvae exposed at the agricultural site, and carboxylesterase showed an inhibition followed by return to control values, suggesting an exposure-recovery episode. Antioxidant glutathione levels were first depleted and then surpassed control levels, whereas GST activity was continuously induced. These responses were mimicked in the laboratory by 2 mg/L AzM-pulse exposure, which notably exceeds the expected environmental concentrations. The results draw attention to the complexity of responses after pesticide exposure, strongly depending on exposure time-concentration and recovery periods, among other possible factors, and support the necessity of the integrated use of biomarkers to assess exposure episodes in agricultural areas.
Hyalella azteca are epibenthic invertebrates that are widely used for toxicity studies. They are reported to be more sensitive to pyrethroid insecticides than most other test species, which has prompted considerable use of this species in toxicity testing of ambient surface waters where the presence of pyrethroids is suspected. However, resident H. azteca have been found in some ambient water bodies reported to contain surface water and/or sediment pyrethroid concentrations that are toxic to laboratory reared H. azteca. This observation suggests differences in the sensitivities of laboratory reared and field populations of H. azteca to pyrethroids. The goal of the present study was to determine the sensitivities of laboratory reared and field populations of H. azteca to the pyrethroids bifenthrin and cypermethrin. Specimens of H. azteca were collected from resident populations at field sites that are subject to varied land-use activities as well as from laboratory populations. These organisms were exposed to bifenthrin- or cypermethrin-spiked water in 96-h water-only toxicity tests. The resulting data demonstrated that: 1) field-collected populations in urban and agricultural settings can be >2 orders of magnitude less sensitive to the pyrethroids than laboratory reared organisms; 2) field-collected organisms varied in their sensitivity (possibly based on land-use activities), with organisms collected from undeveloped sites exhibiting sensitivities similar to laboratory reared organisms; and 3) the sensitivity of field-collected "tolerant" organisms increased in subsequent generations reared under laboratory conditions. Potential mechanisms for these differences are discussed.
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