Abstract

Cholinesterases and carboxylesterases belong to the group of B-esterases, the serine superfamily of esterases that are inhibited by organophosphorus compounds. It is now generally accepted that before using the B-esterases as biomarkers of exposure to organophosphorus and carbamates in a given species, the biochemical characteristics of these enzymes should be carefully studied. In this study, the enzyme/s and the tissue/s to be selected as sensitive biomarkers of organophosphorus exposition in the freshwater gastropod Biomphalaria glabrata were investigated. Firstly, the substrate dependence of cholinesterase and carboxylesterase activities in whole organism soft tissue and in different tissues of the snail (head-foot, pulmonary region, digestive gland, and gonads) was analyzed. Measurements of cholinesterase activity were performed using three substrates: acetylthiocholine (AcSCh), propionylthiocholine (PrSCh), and butyrylthiocholine (BuSCh). Carboxylesterase activity was determined using four different substrates: 1-naphthyl acetate (1-NA), 2-naphthyl acetate (2-NA), p-nitrophenyl acetate (p-NPA), and p-nitrophenyl butyrate (p-NPB). Regardless of the tissue analyzed, the highest specific activity was obtained when using AcSCh, followed by PrSCh. Cholinesterase activity measured with BuSCh was very low in all cases. On the other hand, the highest cholinesterase activity was measured in head-foot and in pulmonary region, representing in the case of AcSCh hydrolysis 196% and 180% of the activity measured in whole organism soft tissue, respectively. In contrast, AcSCh hydrolysis in digestive gland and gonads was 28% and 50% of that measured in whole organism soft tissue. Regarding carboxylesterase activity, although all tissues hydrolyzed the four substrates assayed, substrate preferences varied among tissues. In particular, digestive glands showed higher carboxylesterase activity than the other tissues (299%, 359% and 137% of whole organism soft tissue activity) when measured with 1-NA, 2-NA and p-NPA as substrates, respectively. In contrast, with p-NPB as substrate, the highest carboxylesterase activity was observed in pulmonary region. Exposure of the snails for 48h to azinphos-methyl concentrations in the range of 0.05–2.5mgL−1 resulted in different degrees of inhibition of cholinesterase and carboxylesterase activities, depending on the enzyme, pesticide concentration, the substrate, and the tissue analyzed. In general, carboxylesterase activity measured with p-NPA and p-NPB was much more sensitive to azinphos-methyl inhibition than cholinesterase activity. The results also showed that while B-esterase activities in whole organism soft tissue and pulmonary region recovered completely within 14 days, carboxylesterase activity in digestive glands remained highly inhibited. On the whole, the results of the present study emphasize how important it is to characterize and measure cholinesterase and carboxylesterase activities jointly to make a proper assessment of the impact of organophosphorus pesticides in non-target species.

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