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Exploiting the Freshwater Shrimp Neocaridina denticulata as Aquatic Invertebrate Model to Evaluate Nontargeted Pesticide Induced Toxicity by Investigating Physiologic and Biochemical Parameters
Siregar et al., 2021. Antioxidants 10(3): 391.
This record is a claim boundary, not a quality badge. Evidence class and species relationship describe what was studied. They do not make the result universal, complete or automatically applicable to a home aquarium.
- Source taxon as published
- Research-centre animals labelled Neocaridina denticulata; no diagnostic or molecular identification method reported
- Environment
- Small plastic exposure tanks using reverse-osmosis water at pH 7.0 to 7.5 after seven days of laboratory holding at 26.5 C
- Life stages
- research shrimp averaging 1 to 1.5 cm total length; sex not reported
- Reviewed
- 2026-08-12
What was studied
Study shape: A commercial 28.8 percent imidacloprid formulation was diluted to nominal 0.03125, 0.0625, 0.125, 0.25, 0.5 and 1 ppm for up to 96 hours. The paper describes 20 shrimp in one 200 mL plastic tank per treatment and 12 animals per group for movement, heartbeat and maxilliped-movement endpoints. A separate four-group series placed 24 animals per 500 mL tank, exposed three groups to nominal 1 ppm imidacloprid for 24 hours, then transferred them to fresh water or nominal 0.1 or 1 ppm acetylcholine for three days.
Experimental unit: Exposure tank for treatment assignment, apparently one tank per concentration or rescue group; individual shrimp were later measured in multiwell plates. Repeated video recordings and animal-level measurements do not create independent treatment-tank replication.
Endpoints: tracked distance and immobilization, image-derived heartbeat, maxilliped movement used as a gill-ventilation proxy, whole-animal oxidative-stress and energy-metabolism kit measurements, fresh-water and acetylcholine post-exposure trajectories, surrogate-protein molecular docking.
Claim boundary
What it can support: Under this formulation and fasting protocol, imidacloprid-treated groups showed lower tracked movement across 24 to 72 hours, and higher nominal treatments had lower heartbeat and maxilliped-movement rates at 96 hours. The small whole-animal assay series reported no group differences in its selected oxidative-stress or energy-metabolism measures.
What it cannot support: Independent exposure tanks, random allocation, formulation-only controls and measured water concentrations were not reported. The text conflicts between 12 endpoint animals and 20 exposed animals per group, and treatment is confounded with the apparent single tank while animal measurements are analysed as replicates. Starvation changed heartbeat and maxilliped movement, acetylcholine itself changed the measured endpoints, and the rescue comparison also appears to use one tank per group. Docking used a snail acetylcholine-binding protein rather than a shrimp receptor and cannot prove the in vivo mechanism. The study does not validate acetylcholine as an antidote, identify imidacloprid from behaviour, establish recovery, chronic safety, a plant or flea-product rule, an aquarium dose or a universal threshold.
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Historical record needs follow-up decision (1)
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How this record is classified
Controlled experiment: An assigned treatment or controlled comparison. The treatment, unit, duration and endpoint still limit the claim.
Direct Neocaridina evidence: The source measured animals named within Neocaridina. Direct still does not mean universal or sufficient.
Topics: Chemical exposure, Behaviour, Health
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- Independent unit: What unit was independently assigned or sampled, and how many units support each comparison? Animal counts do not create independent replication when animals share a vessel, site, family or treatment history.
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- Endpoint and measurement: Which endpoint was measured, with what method, unit, timing, resolution and decision rule? One endpoint cannot silently become survival, welfare, diagnosis, reproduction or long-term population performance.
- Denominators and missingness: Are starting counts, exclusions, losses, missing observations and analysis denominators reconciled? Unreported or changing denominators can alter the apparent direction, precision and applicability of a result.
- Transfer boundary: What is the nearest tempting aquarium claim that this source design cannot establish? Direct evidence can still be narrow, and adjacent evidence can be useful only while the inference remains visible.
- Treatment assignment: Were independent units assigned to treatments, and were baseline conditions comparable? Unclear allocation or baseline imbalance can confound the treatment comparison.
- Replication: Were treatment vessels or other exposure units independently replicated rather than subsampled? Repeated animals or assays inside one exposure unit do not replicate the environmental treatment.
- Exposure verification: Was the treatment, dose, feed intake or environmental exposure measured and maintained as described? Nominal treatment labels may not equal the exposure animals actually received.
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