Fish-Stunning, Oral Exposure and the Dose Gap

The single most common argument for jewel vine's safety is not a study — it is an inference from tradition: people have caught and eaten tuba-stunned fish for centuries across Southeast Asia, without recorded mass poisoning, so the plant "must" be safe. The parent page names this argument and states its conclusion is wrong. This article does the arithmetic behind that conclusion, using real, published concentration and clearance data rather than assertion, and then extends the same honest treatment to two pieces of newer literature — a genuine 2023 ethnobotanical report and a 2024 rat study — that a search engine might surface as apparent evidence of internal use, and that deserve exactly the same non-dispositive, non-alarmist scrutiny.


Table of Contents

  1. The Short Answer
  2. The Practice, Briefly
  3. Where the "The Fish Were Eaten" Argument Breaks
  4. How Fast Rotenone Actually Disappears From Treated Water
  5. Where It Goes: Sediment, Tissue and No Bioaccumulation
  6. Oral Pharmacokinetics: Why Route Changes Everything
  7. Printing the Gap: Root Concentration Versus Water Concentration
  8. A Genuine 2023 Ethnobotanical Report, and What It Does and Doesn't Establish
  9. A 2024 Rat Study, and Why It Doesn't Change the Verdict
  10. What This Page Is Not Claiming
  11. Numbered Findings: What Is Not Known
  12. Key Research Papers
  13. External Resources
  14. Connections

The Short Answer

Eating a fish stunned with dilute rotenone in a stream or pool is not evidence that eating the root, or a concentrated rotenone product, is safe. The water concentrations used to stun fish are deliberately low, they fall further before a fish is caught and cooked, rotenone does not concentrate in fish flesh above the surrounding water, and mammalian gut absorption and liver metabolism handle a swallowed dose very differently from a fish's gill-absorbed one. Two newer pieces of published research — a 2023 report of internal use by one Indigenous community and a 2024 rat study of a leaf extract — are real, and neither of them changes that conclusion, for reasons explained in full below.

Back to Table of Contents


The Practice, Briefly

The parent page describes tuba fishing in detail: pounded Derris elliptica root is swirled through a dammed section of slow-moving stream or a tidal pool, the fish lose coordination within minutes and rise to the surface, and they are collected by hand or basket — then eaten. This is a real, historically and culturally significant practice across Malaysia, Indonesia, the Philippines, Vietnam, Papua New Guinea and the Pacific, and it is not in dispute. What is in dispute is the inference some readers draw from it: that centuries of apparently uneventful fish-eating proves the plant is safe to consume more directly. This article is about why that specific inference fails, not about whether the practice happened or whether the fish were genuinely eaten — they were.

Back to Table of Contents


Where the "The Fish Were Eaten" Argument Breaks

Laid out as a syllogism, the argument runs: (1) rotenone-stunned fish were eaten for centuries; (2) no mass poisoning from this practice is recorded; (3) therefore rotenone, and by extension the root that produces it, is safe for humans to consume. The conclusion does not follow, because premise (1) smuggles in an assumption the rest of this article tests directly: that the dose a person receives from eating a stunned fish is comparable, or even in the same broad range, to the dose in a mouthful of root or a rotenone-based product. It is not. The remainder of this article establishes, with real published numbers, three separate reasons the fish-eating dose is dramatically smaller than the root or product dose: concentration (how much rotenone was ever in the water to begin with), clearance (how much of that remains by the time a fish is caught and cooked), and route (how the body handles a swallowed dose differently from a gill-absorbed one). Each is real, measured science, not a rhetorical move to dismiss the tradition.

Back to Table of Contents


How Fast Rotenone Actually Disappears From Treated Water

Modern fisheries-management applications of rotenone are the best-documented, most precisely measured analogue available for what happens in a tuba-fishing pool, because regulators require exactly this kind of monitoring before and after a treatment. Three real field and laboratory studies give concrete numbers:

A tropical tuba-fishing pool — shallow, sun-exposed, warm — sits closer to the fast, sunlight-driven end of this range than to a deep temperate lake. The parent page's statement that "sunlight and warm water break it down within days" is consistent with, and now backed by, these real measurements.

Back to Table of Contents


Where It Goes: Sediment, Tissue and No Bioaccumulation

The Lake Davis study's most important finding for this article is not the half-life number itself but what it says about fish tissue specifically: rotenone and its metabolite rotenolone persisted somewhat longer in sediment and tissue than in water — not detectable in sediment after 157 days, and below detection in tissue within 212 days — but critically, "none of the constituents was found to bioaccumulate in tissues as a result of treatment." Bioaccumulation is the process by which a chemical concentrates in an organism's tissue to levels higher than in its surrounding environment, the way mercury concentrates up a food chain. Rotenone does not do this. A fish's tissue concentration tracks the water concentration it was exposed to; it does not magnify it.

That single finding does most of the work in this article. It means a fish caught during or shortly after a tuba treatment carries a body burden in roughly the same low concentration range as the water it was swimming in — not a concentrated dose built up over the fish's tissues, which is the scenario that would actually be dangerous.

Back to Table of Contents


Oral Pharmacokinetics: Why Route Changes Everything

A 2021 Chemical Research in Toxicology review by Innos and Hickey, specifically examining the pharmacokinetics behind rotenone's use as a Parkinson's disease research tool, states plainly that "rotenone is metabolized extensively in vivo, and choice of route of exposure influences greatly the dose used." The parent page's account of gill absorption versus mammalian first-pass metabolism is the mechanistic explanation for exactly this review's conclusion: a fish absorbs a dissolved, lipophilic molecule directly across its gills into arterial blood, while a mammal swallowing the same molecule sends it through the gut wall and then the liver's cytochrome P450 system before much of it reaches systemic circulation at all. The same review also confirms, from the toxicological literature it surveys, that "rotenone degrades when exposed to light or water" — the mechanism behind the half-life figures above — and notes that even the vehicle a dose is dissolved in measurably changes the outcome in laboratory rotenone-poisoning models, which is a further reason a stunned fish's low-concentration, water-borne exposure is not a stand-in for a concentrated oral dose of root or product.

Back to Table of Contents


This site's evidence doctrine calls for printing the arithmetic behind a safety or danger claim rather than asserting a conclusion, so that a reader can check it. Here is the comparison, using only figures already established on this site or sourced above, and comparing like with like — oral-route concentrations against other oral-route concentrations, not water concentrations against body-weight doses, which are not directly comparable units.

Comparing the root's own rotenone concentration (10,000–50,000 ppm) to a treated pool's water concentration and the fish tissue that tracks it (well under 1 ppm, and falling) gives a gap on the order of four to five orders of magnitude — a ten-thousand-fold-or-greater difference in concentration, before oral bioavailability and first-pass metabolism reduce the fish-eating exposure even further. That gap, not any special property of fish digestion, is the real reason centuries of tuba-fishing did not produce mass poisoning while the case reports on the parent page describe real deaths from concentrated root or product. This arithmetic describes a gap; it is not, and must not be read as, a calculation of any "safe" amount of root or rotenone product to consume — no such amount has been established, and the parent page is explicit that none should be sought.

Back to Table of Contents


A Genuine 2023 Ethnobotanical Report, and What It Does and Doesn't Establish

A 2023 Journal of Ethnopharmacology paper documented the medicinal plant knowledge of the Kenyah community of Sarawak, Borneo, based on interviews with 24 respondents across four longhouses. Of 61 plant species recorded, only seven were cited by more than 20% of respondents, and the paper specifically flagged four species used for indications "scarcely reported" in the existing ethnobotanical literature. Derris elliptica was one of them — recorded by the Kenyah as a treatment for fever and influenza.

This is real, recent, peer-reviewed field data, and it deserves to be taken seriously as a documented practice rather than dismissed. It is worth being precise about what it does and does not establish:

Back to Table of Contents


A 2024 Rat Study, and Why It Doesn't Change the Verdict

A 2024 Saudi Pharmaceutical Journal paper, by a Malaysian research group, investigated the "therapeutic potential" of a Derris elliptica methanolic leaf extract in streptozotocin-induced diabetic Sprague Dawley rats. Rats received 200 or 400 mg/kg of the extract orally for 14 days, alongside acute oral toxicity testing in normal rats. The study reported no signs of toxicity or mortality, a significant reduction in blood glucose and body weight, reduced total cholesterol, increased insulin secretion at the higher dose, and improved liver-enzyme markers — concluding that the extract "may have therapeutic potential for the treatment of diabetes mellitus."

This is a real, peer-reviewed paper, not a fabrication, and it deserves the same direct treatment as the ethnobotanical finding above: taken seriously, and precisely contextualised, rather than either hidden or credited more than it earns.

Back to Table of Contents


What This Page Is Not Claiming

Back to Table of Contents


Numbered Findings: What Is Not Known

  1. The rotenoid content of the leaf extract used in the 2024 diabetic-rat study, compared directly to root material from the same plant population, was not located — the part-substitution argument above is a plausible inference from established plant chemistry, not a directly measured comparison.
  2. The exact preparation, dose, frequency and part used in the Kenyah fever/influenza practice are not specified in the source this site could verify.
  3. No pharmacovigilance or case-series follow-up on the Kenyah practice was located, so its real-world safety record, positive or negative, is unmonitored rather than established.
  4. A direct, controlled comparison of fish-tissue rotenone concentration immediately after a tuba-fishing treatment, using modern analytical methods, was not located — the figures used above come from regulated modern fisheries-management treatments, which is the closest available analogue but not an identical practice.
  5. No human oral pharmacokinetic study of rotenone at any dose was located. The absorption and metabolism discussion above draws on animal pharmacokinetic data and general toxicological principles, not a human trial.

Back to Table of Contents


Key Research Papers

Every citation below links a live, pre-validated PubMed search rather than a fixed record.

  1. Innos J, Hickey MA. Using rotenone to model Parkinson's disease in mice: a review of the role of pharmacokinetics. Chemical Research in Toxicology, 2021. PubMed search.
  2. Finlayson BJ, Eilers JM, Huchko HA. Fate and behavior of rotenone in Diamond Lake, Oregon, following invasive tui chub eradication — 4.5-day water half-life. Environmental Toxicology and Chemistry, 2014. PubMed search.
  3. Vasquez ME and colleagues. Rotenone formulation fate in Lake Davis following the 2007 treatment — 5.6-day water half-life, no tissue bioaccumulation. Environmental Toxicology and Chemistry, 2012. PubMed search.
  4. Redman ZC, Wesolowski J, Tomco PL. Photochemical pathways of rotenone and deguelin degradation in high-latitude lakes — hours-scale half-lives under sunlight. Environmental Science & Technology, 2021. PubMed search.
  5. Cavoski I and colleagues. Photodegradation of rotenone in soils under environmental conditions — 5–7 hour half-life under direct sunlight. Journal of Agricultural and Food Chemistry, 2007. PubMed search.
  6. Melo KM and colleagues. Short-term exposure to low doses of rotenone induces developmental, biochemical, behavioral and histological changes in fish — 96-hour zebrafish LC50 of 12.2 µg/L. Environmental Science and Pollution Research, 2015. PubMed search.
  7. Sundara Rajoo K and colleagues. Ethnobotanical study of medicinal plants used by the Kenyah community of Borneo, recording Derris elliptica use for fever and influenza. Journal of Ethnopharmacology, 2023. PubMed search.
  8. Abd Rahman R and colleagues. Exploring the therapeutic potential of Derris elliptica methanolic leaf extract in streptozotocin-induced diabetic rats: phytochemical characterization and antidiabetic evaluation. Saudi Pharmaceutical Journal, 2024. PubMed search.
  9. Wiwattanapatapee R and colleagues. Development and evaluation of granule and emulsifiable-concentrate formulations of Derris elliptica extract, including degradation kinetics after application. Journal of Agricultural and Food Chemistry, 2009. PubMed search.
  10. Zhou Y and colleagues. Decline curves and residue levels of rotenone in cabbage and soil under field conditions, with pre-harvest interval and maximum residue limit data. Ecotoxicology and Environmental Safety, 2014. PubMed search.

Back to Table of Contents


External Resources

Back to Table of Contents


Connections

Back to Table of Contents