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CAS 76-87-9

Triphenyltin hydroxide (TPTH)

organotinfungicideHAPPBTendocrine disruptor

Triphenyltin hydroxide is an organotin compound used as a fungicide on potatoes, peanuts, and sugar beets — a compound whose immune system toxicity, endocrine disruption, and neurodevelopmental effects have drawn increasing concern even at low environmental concentrations, and which bioaccumulates in aquatic food chains from agricultural runoff.

Where It Comes From

Triphenyltin (TPTH) compounds were developed in the 1950s-60s as highly effective fungicides and antifouling biocides — the same triphenyltin acetate and hydroxide that became staples of potato blight and sugar beet leaf fungal disease control [1]. Related compounds (tributyltin, TBT) were used in marine antifouling paints and caused dramatic disruption of marine mollusk reproduction (imposex — the development of male reproductive organs in female gastropods) at nanogram-per-liter concentrations in harbor water, eventually leading to a global ban on TBT in ship paint [2]. TPTH was used in U.S. potato production until EPA cancelled most registrations following concerns about immune toxicity and developmental effects. Limited registrations persist for some agricultural uses globally [1]. Organotins persist in sediments and bioaccumulate through aquatic food chains [2].

How You Are Exposed

Agricultural workers applying TPTH fungicide formulations face inhalation and dermal exposure [1]. Dietary residues on potatoes, peanuts, and sugar beets represent a consumer exposure pathway where TPTH is still registered [2]. Environmental contamination from agricultural runoff enters aquatic systems where TPTH bioaccumulates in shellfish and fish [1].

Why It Matters

Triphenyltin compounds selectively suppress thymus-dependent immune responses — T-cell proliferation is inhibited at low concentrations, reducing resistance to infections and impairing immune surveillance [1]. TPTH also acts as a thyroid peroxidase inhibitor, disrupting thyroid hormone synthesis, and shows retinoid receptor disruption (RXR agonism) that may affect metabolism and differentiation at very low doses [2]. EPA classifies it as a probable (B2) carcinogen based on animal studies [1]. The endocrine disruption at environmental concentrations makes it of concern for fish and wildlife, and potentially for human fetal development through maternal dietary transfer [2].

Who Is at Risk

Potato and peanut farmworkers [1]. Consumers of produce grown with TPTH fungicides [2]. Pregnant women consuming fish from TPTH-contaminated water bodies [1].

How to Lower Your Exposure

1. Choose organic or TPTH-free certified potatoes and peanut products [1]. 2. Farmworkers should use full PPE during TPTH application [2]. 3. Avoid consuming shellfish from areas with organotin contamination [1].

References

  1. [1]EPA (2002). Triphenyltin Hydroxide Reregistration Decision. https://www.epa.gov/
  2. [2]Fent K (1996). Organotin compounds in municipal wastewater and sludge. Science of the Total Environment. https://doi.org/10.1016/0048-9697(95)04968-9

Recovery & Clinical Information

Body Half-Life

Organotins are metabolized by CYP3A4 — blood half-life approximately days to weeks [1]. Accumulate in liver and fat [2].

Testing & Biomarkers

Blood/urine organotin speciation by GC-MS/MS [1]. Thyroid function tests [2].

Interventions

Remove from exposure [1]. Thyroid function monitoring and support if disruption detected [2].

Recovery Timeline

Blood TPTH declines over weeks to months [1].

Recovery References

  1. [1]Fent K (1996). Organotin compounds. Science of the Total Environment. https://doi.org/10.1016/0048-9697(95)04968-9
  2. [2]ATSDR (2005). Toxicological Profile for Tin. https://www.atsdr.cdc.gov/toxprofiles/tp55.pdf

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