Abstract:Abstract:We analyzed the morphological and functional state of hepatopancreas in Palaemonetes argentinus from two environments with different pesticide concentrations. Los Padres lagoon (Argentina) is an area subjected to contamination due to the slow exchange of water, the shallow depth and the input of contaminated water. Prawns living in this lagoon accumulate high amounts of organochlorine pesticides in their tissues. Hepatopancreas of prawns from Canal 5, an adjacent shallow stream where the amount of pes… Show more
“…A similar result was reported by Sreeram and Menon (2005) when a pronounced increase in B-cell number was associated with exposure to sublethal concentrations of petroleum hydrocarbons in the hepatopancreas of Kadal shrimp (Metapenaeus dobsoni) and related to a detoxification mechanism at a cellular level. An increase in altered R cells of ghost shrimp (Palaemonetes argentinus) exposed to pesticides suggests that R cells may be directly involved in detoxification (Petriella, 2007), although R cells were thought to be only indirectly related to detoxification by providing active energy for this mechanism in response to environmental stress in Macrobrachium borellii Nobili, 1896, and P. argentinus Nobili, 1901 (Collins, 2010).…”
Microplastics and glyphosate-based herbicides (GBHs) unavoidably contaminate aquatic environments, yet their combined effect on aquatic organisms has been scarcely investigated. We present a short-term study on individual and combined effects of aged polyethylene (PE) microplastics and GBH exposures at environmentally relevant concentrations on oxidative damage, antioxidant responses, immune parameters, and hepatopancreas histology in shrimp (Litopenaeus vannamei). In addition, acetylcholinesterase (AChE) was evaluated as a biomarker of GBH exposure. After 96 hours of exposure, individual PE microplastic exposure slightly influenced oxidative status, immune parameters, and histology. Decreases in AChE concentration and alterations in oxidative status, immunity, and cell population in hepatopancreas were observed in single GBH-exposed shrimp. The combinations of aged PE microplastics and GBH induced some changes that differed from individual GBH exposures. For instance, some alterations implied that the presence of aged PE microplastics may alter GBH toxicity to L. vannamei (AChE concentration and some expressions of immune-related genes). In conclusion, our results suggest that single exposure of aged PE microplastics at environmental concentration may slightly affect the health of L. vannamei and that aged PE microplastics are likely to modify the toxicity of other co-exposed chemicals.
“…A similar result was reported by Sreeram and Menon (2005) when a pronounced increase in B-cell number was associated with exposure to sublethal concentrations of petroleum hydrocarbons in the hepatopancreas of Kadal shrimp (Metapenaeus dobsoni) and related to a detoxification mechanism at a cellular level. An increase in altered R cells of ghost shrimp (Palaemonetes argentinus) exposed to pesticides suggests that R cells may be directly involved in detoxification (Petriella, 2007), although R cells were thought to be only indirectly related to detoxification by providing active energy for this mechanism in response to environmental stress in Macrobrachium borellii Nobili, 1896, and P. argentinus Nobili, 1901 (Collins, 2010).…”
Microplastics and glyphosate-based herbicides (GBHs) unavoidably contaminate aquatic environments, yet their combined effect on aquatic organisms has been scarcely investigated. We present a short-term study on individual and combined effects of aged polyethylene (PE) microplastics and GBH exposures at environmentally relevant concentrations on oxidative damage, antioxidant responses, immune parameters, and hepatopancreas histology in shrimp (Litopenaeus vannamei). In addition, acetylcholinesterase (AChE) was evaluated as a biomarker of GBH exposure. After 96 hours of exposure, individual PE microplastic exposure slightly influenced oxidative status, immune parameters, and histology. Decreases in AChE concentration and alterations in oxidative status, immunity, and cell population in hepatopancreas were observed in single GBH-exposed shrimp. The combinations of aged PE microplastics and GBH induced some changes that differed from individual GBH exposures. For instance, some alterations implied that the presence of aged PE microplastics may alter GBH toxicity to L. vannamei (AChE concentration and some expressions of immune-related genes). In conclusion, our results suggest that single exposure of aged PE microplastics at environmental concentration may slightly affect the health of L. vannamei and that aged PE microplastics are likely to modify the toxicity of other co-exposed chemicals.
“…Its ecological significance for the area has been reported by several authors (Collins, 1999;Rodrigues Capı ´tulo and Freyre, 1995). Many aspects of P. argentinus have been studied: population structure, reproduction, development, molt cycle, natural and artificial feeding, osmoregulation physiology, histology (Rodrigues Capı ´tulo and Freyre, 1995;Nazary et al, 2000;Felix and Petriella, 2003;Collins, 1999;Charmantier and Anger, 1999;Sousa and Petriella, 2007), but there is little information regarding toxicology. Rodrigues Capı ´tulo (1984) studied the effect of anionic detergents on survival and energy metabolism.…”
“…A similar result was reported by Sreeram and Menon (2005) when a pronounced increase in B-cell number was associated with exposure to sublethal concentrations of petroleum hydrocarbons in the hepatopancreas of Kadal shrimp (Metapenaeus dobsoni) and related to a detoxification mechanism at a cellular level. An increase in altered R cells of ghost shrimp (Palaemonetes argentinus) exposed to pesticides suggests that R cells may be directly involved in detoxification (Petriella, 2007), although R cells were thought to be only indirectly related to detoxification by providing active energy for this mechanism in response to environmental stress in Macrobrachium borellii Nobili, 1896, and P. argentinus Nobili, 1901 (Collins, 2010).…”
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