Measurement / residue studyindependent cross-checkfull text checked★ key study I-FSH-07 in-depth review

Pesticides and antibiotics in Nile tilapia (Egypt)

Occurrence and human health risks of pesticides and antibiotics in Nile tilapia along the Rosetta Nile branch, Egypt.

Overview

Eissa F et al.. Toxicol Rep 2020 · PMID 33384941 · DOI 10.1016/j.toxrep.2020.03.004

Most wild river tilapia sampled near drains had pesticide traces (chlorpyrifos above the EU limit in 45%) and a fifth had antibiotic traces, including EU-banned drugs; estimated non-cancer risk was low.

Does the study support the specific claim? Partly · Methodological quality: moderate

Original publication

Plain-language summary

Study explained simply
What did the researchers want to find out?

Monitor residues.

How was the study done?

Mass spectrometry.

How many people, animals or samples were studied?

72 wild tilapia, 3 river sites near drains, monthly for one year.

What was actually found?

Pesticides in 86% (chlorpyrifos 83%, 45% above EU limit); antibiotics in 21% (nitrofurazone 8.6-52 ug/kg, all from one site in spring); all THQ <1.

How large was the observed effect?

Nitrofurazone up to 52 µg/kg.

What do the results mean in everyday life?

Traces present; low estimated risk.

What are the study's limitations?

Wild fish caught near drain outlets; small numbers per site and season; risk method not suited to cancer-causing banned drugs.

What does it say about Elawady's specific claim?

Shows residues in wild river fish; does not test farmed fish or their feed.

Do the results apply to Germany and Europe?

Low.

What can explicitly not be concluded from this study?

Residue levels in farmed or market tilapia; long-term or cancer risk.

Scientific in-depth review

1. Full reference

Authors
Eissa F et al.
Journal
Toxicol Rep
Year
2020
Identifier
PMID 33384941 DOI 10.1016/j.toxrep.2020.03.004
Verification
verified – PubMed efetch 2026-10-25
Retracted
no
Corrections
none
Extent checked
full text
Conflicts of interest and funding

Authors report no competing interests; no funding statement; acknowledgement to the Central Laboratory of Residue Analysis of Pesticides and Heavy Metals in Food, Agricultural Research Center, Egypt.

2. Research question

Pesticide/antibiotic residues in Nile tilapia from the Rosetta branch and consumer risk

3. Study design and population

Study design
Measurement / residue study – One-year monthly residue monitoring (100 pesticides, chloramphenicol and 4 nitrofuran metabolites) in wild Nile tilapia caught near agricultural/wastewater drain outlets, with deterministic non-carcinogenic risk assessment (THQ)
Population

Wild Nile tilapia (Oreochromis niloticus) caught with local fishermen 1 km upstream of the El-Rahawy (Giza), Sabal (Minoufiya) and Tala (Gharbiya) drain outlets on the Rosetta branch

Country

Egypt

Period

July 2018-June 2019

Sample size

72 fish muscle samples (3 sites x 12 months, in duplicate)

Inclusion and exclusion criteria

Not applicable; dorsal muscle (edible part) analysed

4. Methods and endpoints

Exposure / intervention

Sampling site and season

Comparator

EU MRLs; US EPA reference doses (THQ threshold 1)

Endpoints

Residue frequency and concentration; THQ assuming 38.14 g fish/day, 60 kg body weight, 70-year exposure

Statistical methods

Descriptive (frequencies, ranges, seasonal/site means); QuEChERS GC-MS/MS and LC-MS/MS; ISO/IEC 17025-accredited lab (FINAS); recoveries 62-120% (pesticides), 85-97% (antibiotics); LOQ 0.01-0.05 mg/kg (pesticides), 0.075-0.5 ug/kg (antibiotics)

5. Actual results

Results

62/72 (86%) samples contained >=1 pesticide; chlorpyrifos in 83% (<LOQ-0.08 mg/kg), exceeding the EU MRL (0.01 mg/kg) in 45% of samples; p,p'-DDE in 45% (<LOQ-0.04 mg/kg); tebufenpyrad 8%; others <=3%. 15/72 (21%) contained antibiotic residues: nitrofurazone (SEM marker) 8.6-52 ug/kg in 12% (all from Sabal in spring), nitrofurantoin (AHD) 1.1-2 ug/kg in 6%, chloramphenicol <LOQ-0.17 ug/kg in 5%; none in autumn and winter. Highest loads at Sabal. All THQ <1 (max p,p'-DDE 0.06, chlorpyrifos 0.03, nitrofurazone 0.01661).

Absolute risks

not reported (THQ screening indices only)

Authors' conclusion

Consumption of Nile tilapia from the Rosetta branch is unlikely to cause detrimental effects and can be considered safe for ordinary consumers; laws should be enforced, wastewater treated and monitoring continued; detection of banned nitrofurans and chloramphenicol indicates continued use in food-producing species.

6. Strengths

  • Year-round monthly sampling at three sites
  • Wide analyte panel with accredited, validated methods
  • Separate site and season reporting

7. Weaknesses

  • Wild river fish sampled close to drain outlets (worst-case locations), not market or farmed fish
  • Small n per site-season; antibiotic findings driven by one site-season (Sabal, spring)
  • THQ is inappropriate for genotoxic carcinogens (nitrofurans, chloramphenicol have no safe threshold); no carcinogenic risk or cumulative (hazard index) assessment
  • Nitrofurazone inferred from SEM marker, which is not fully specific (reviewer note)
  • Single fish intake scenario; children not assessed
  • No funding statement

8. Risk of bias

Orienting tool
No standard tool fits (residue monitoring/exposure assessment); structured validity judgement
Type of assessment
structured assessment based on the full text by a single reviewer (no formal double review)
Full formal assessment
no
Overall risk of bias
some concerns
Rationale

Single-reviewer structured judgement based on the full text; not formal (needs two independent reviewers). Changed from low to some_concerns because of purposive near-drain sampling and the THQ approach for genotoxic residues.

8. Risk of bias
DomainJudgementRationale
Sampling / representativenesshighPurposive sampling near drain outlets; wild fish; not representative of fish sold or farmed in Egypt.
Analytical measurementlowAccredited lab, validated multi-residue methods, recoveries and LOQs reported.
Risk characterisationsome concernsTHQ only; no carcinogenic assessment for genotoxic banned drugs; no mixture assessment; default intake values.
ReportinglowFull site-season tables provided.

Full-text review (25 October 2026): Added sampling near drain outlets, chlorpyrifos MRL exceedance in 45%, antibiotic findings concentrated in one site-season, analytical validation, THQ assumptions and values, missing funding statement; noted THQ unsuitable for genotoxic residues; bias overall changed from low to some_concerns.

9. Assessment of the statistical interpretation

THQ <1 indicates low non-cancer risk at the assumed intake; it does not address the regulatory zero tolerance for nitrofurans and chloramphenicol, whose presence is a compliance signal independent of THQ. Frequencies are based on 72 samples (6 per site-season).

10. Relevance to the specific claim

C-FSH-09, C-FSH-12, C-FSH-16, C-RES-01/02. Note: these are river (not farmed) tilapia - residues come from the environment.

11. Independent contrary findings

12. Transferability to Germany and Europe

Low (Egypt-specific).

13. Overall methodological judgement

Egyptian evidence that wild river tilapia near drains carry pesticide residues (chlorpyrifos above EU MRL in 45%) and occasional banned antibiotic residues, at levels the authors judge low-risk for non-cancer effects. It concerns wild, not farmed fish, so it does not support claims specific to farmed fish feed; it rather shows that 'natural' river fish are not automatically clean.

Multidimensional assessment
Multidimensional assessment
Authenticity of the sourceverified
Methodological qualitymoderate
Risk of biassome concerns
Precision of resultslow
Directnessdirect
Reproducibilityunknown
Consistency with the overall evidenceunknown
Regional transferabilitylow
Adequacy of the interpretation (by the archive)not applicable

14. Open questions

Farmed and market tilapia with the same panel; carcinogenic risk assessment for nitrofurans; source attribution of residues.

15. Linked fact checks