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Relationship: 452
Title
AchE Inhibition leads to Increased Mortality
Upstream event
Downstream event
AOPs Referencing Relationship
| AOP Name | Adjacency | Weight of Evidence | Quantitative Understanding | Point of Contact | Author Status | OECD Status |
|---|---|---|---|---|---|---|
| Acetylcholinesterase inhibition leading to acute mortality | non-adjacent | High | Moderate | Cataia Ives (send email) | Under Development: Contributions and Comments Welcome | Under Development |
Taxonomic Applicability
Sex Applicability
Life Stage Applicability
- Acetylcholinesterase (AChE) inhibition leads to mortality via overstimulation of neuronal cholinergic signalling pathways that control factors essential for respiration (Costa in Casarett and Doull's).
| ID | Experimental Design | Species | Upstream Observation | Downstream Observation | Citation (first author, year) | Notes |
|---|
| Title | First Author | Biological Plausibility |
Dose Concordance |
Temporal Concordance |
Incidence Concordance |
|---|
Biological Plausibility
Dose Concordance Evidence
Temporal Concordance Evidence
Incidence Concordance Evidence
Uncertainties and Inconsistencies
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Development of AChE Tolerance: Under certain circumstances, tolerance to AChE inhibition can develop, instead of mortality. Rats exposed to acutely toxic, near-lethal amounts of AChE inhibitor become tolerant. Adaptation to AChE inhibitor has been described in humans in association with Myasthenia graves, asthenic syndrome, and after long exposure to some insecticides. (Stavinoha, 1969)(The reference listed here references 3 papers on rats published between ‘52-’64).
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In vivo AChE Inhibition Measurement Challenges
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Correlating in vivo measures of AChE inhibition with mortality endpoints have not always been successful possibly due to interference from other esterases and partitioning issues across tissues (Wilson 2010).
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A QSAR (quantitative structure activity relationship) model developed to predict the acute LC50 for rainbow trout (Oncorhynchus mykiss) using the pI50 (concentration that inhibits AChE by 50%) found a statistically relevant linear relationship, but the model only explained 59% of the variation in toxicity observed for the series of carbamates tested (Call et al., 1989). QSAR models to estimate fish toxicity (LC50) for a series of OPs based on the reaction rate constants associated with inhibition of AChE in electric eel did result in a significant model, but the model only explained 23% of the variation in toxicity (De Bruijn and Hermens 1993).
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Challenges correlating In vivo and In vitro AChE Activity Measurements: Although relationships can be made between the in vitro AChE inhibition and in vivo toxicity values observed for direct acting OPs and carbamates, these relationships typically are not significant (Wilson 2010). Factors contributing to the failure of these correlations include the tissue analyzed, method used to assay AChE or acetylcholine, organism life stage, dose compared to body size, and metabolic differences including detoxification pathways (Wilson 2010; Ludke et al., 1975; Hamadain and Chambers, 2001).
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Mammals
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The relationship between AChE inhibition and lethality was evaluated by comparing mortality dose-response for 7 OPs in guinea pigs, and also for 1 OP (soman) in mice, rats, rabbits, and non-human primates. Regression analysis indicated that 93% of the variation in median lethal doses was explained by their in vitro rate constants for AChE inhibition (Maxwell et al 2006).
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A dose response curve between percent mortality and the AChE-inhibitor, disulfoton, in Holzman and Charles River rats was used to establish a chronic 10-day LD50 at 1.8 mg/kg. Rats were dosed with 10, 25 or 50 ppm DiSystron.
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Birds
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Evaluations of incidents of bird poisonings from OPs and carbamates found that events were correlated with a >50% inhibition of brain AChE, with exposure confirmed by the detection of the pesticide within the stomach contents of the analyzed bird (Fleischli et al., 2004).
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Fish
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Statistically significant effects were observed in fish mortality at 80% inhibition of brain AChE, with the maximum inhibition observed at 3-7 days after the first application of chlorpyrifos (Macek et al., 1972).
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In embryonic zebrafish exposed to 9 uM diazinon for three days, 35% mortality was observed, and some fish displayed developmental malformations (In Yen, 2011 citing Osterauer and Kohler, 2008).
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A study using zebrafish exposed to chlorpyrifos, resulted in 75-100% mortality at 3-30 uM concentrations, and 80% inhibition of AChE at 0.3 uM from 0-5 dpf. The study also demonstrated an increase in AChE activity in control fish from 0-5 dpf, with 0.3 uM chlorpyrifos significantly inhibiting AChE at 3 dpf (~50%) with inhibition increasing through to 5 dpf (80%) (Yen et al., 2011).
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Response-response Relationship
Time-scale
Known Feedforward/Feedback loops influencing this KER
Taxonomic Applicability
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Russom et al performed two parallel approaches to examine AChE sensitivity across multiple taxa: insects, crustaceans, fish, amphibians, mollusks, annelids, and plants. They generated species sensitivity curves from empirical evidence pulled from systemic searches for acute lethality toxicity data for terrestrial and aquatic species in the ECOTOX database. Daphnids were consistently found to be highly sensitive to organophosphates and carbamates. Next, they used the Daphnia pulex AChE protein sequence was used as the query sequence to make cross-species susceptibility predictions. There was strong agreement between the empirical evidence and the species sensitivity predictions based on the protein sequence similarity approach. Insects and crustaceans include the species most sensitive the AChE inhibition, followed by fish and amphibians and then by mollusks and annelids (Russom, 2014; LaLone, 2013).
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Amongst fish, amphibians, mammals and birds, Wallace summarized comparative sensitivities from multiple studies. Across these groups, birds are highly sensitive to AChE inhibition, mammals are moderately sensitive and fish and amphibians are the least sensitive to AChE inhibition.
Life Stage Applicability
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Studies in zebrafish have shown that mortality coincides with the onset of organogenesis for dichlorvos and diazinon and with the end of organogenesis/onset of hatching for chlorpyrifos (Watson, 2014)
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In Xenopus, OP-induced mortality occurs at a time well after organogenesis and before the physiological changes associated with metamorphosis. At the peak of Xenopus mortality, the larva was swimming actively, had a well-developed mouth, and was in the process of developing hind limbs (stage 49) (Watson, 2014)