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Invisible invaders: range expansion of feral Neocaridina davidi offers new opportunities for generalist intracellular parasites
Prati et al., 2024. Biological Invasions 26: 2499-2523.
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
- Neocaridina davidi
- Environment
- European feral populations with field sampling and molecular parasite work
- Life stages
- field population
- Reviewed
- 2026-08-12
What was studied
Study shape: Feral occurrence, environmental conditions and intracellular parasite relationships were investigated.
Experimental unit: Field population, site and sampled animal, depending on endpoint
Endpoints: feral occurrence, range expansion, microsporidian detection, environmental context.
Claim boundary
What it can support: Feral populations and intracellular parasite associations exist in the sampled locations.
What it cannot support: One site value is not a care boundary, and field parasite detection is not a prevalence estimate for the aquarium trade.
Publication status audit
Matched in dated Crossref query
The canonical DOI appeared in the dated broad query and carried no registered update in that response. This is a metadata observation, not proof that the work has never changed.
Metadata snapshot reviewed 2026-08-12. Inspect the method, unmatched queue and limitations.
Correction impact
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Editorial review required (10)
This curated wording or synthesis must be reconsidered when the source boundary changes. A passing generator test cannot decide the new scientific meaning.
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Generated from governing registry (22)
This surface derives from a governing registry and should update with it, but release tests must still prove parity and routing.
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The typography-only visual and exact accessibility description derive from the curated decision-card registry and must preserve every card section. - Invisible invaders: range expansion of feral Neocaridina davidi offers new opportunities for generalist intracellular parasites Canonical evidence page
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How this record is classified
Field observation: Animals were observed in a field population. Occurrence and association do not create a home-aquarium optimum or prove causation.
Direct Neocaridina evidence: The source measured animals named within Neocaridina. Direct still does not mean universal or sufficient.
Topics: Health, Wild populations, Species and taxonomy
Critically appraise this source without a score
These questions fit this record's field observation role. They are prompts, not automatic judgments. Open the original source to answer them.
- Identity and provenance: How were the organism, population, stock and life stage identified and sourced? A published name or seller label can hide a taxonomic, population or life-stage transfer.
- 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.
- Comparison and context: What was the actual comparator, allocation process, environment, duration and material condition? A result has meaning only against the comparison and conditions that produced it.
- 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.
- Sampling frame: How were sites, dates, habitats and animals selected, and what population can that sampling represent? Convenient or uneven sampling limits prevalence, abundance and seasonal inference.
- Sampling effort: Was effort standardized or recorded across sites, times and environmental conditions? Observed counts can change because detectability or effort changed rather than the population.
- Association: Which co-varying environmental or biological factors could explain the observed association? Field correlation does not by itself identify cause or a husbandry intervention.
- Detection and absence: Could non-detection reflect gear, visibility, season, behavior or identification limits? Not observed is not equivalent to absent.
Where it is used
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