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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Toxicological information

Basic toxicokinetics

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Administrative data

Endpoint:
basic toxicokinetics in vivo
Type of information:
experimental study
Adequacy of study:
key study
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: Well designed and performed study reported in the peer-reviewed literature. Not GLP or specific testing guidelines

Data source

Referenceopen allclose all

Reference Type:
publication
Title:
Unnamed
Year:
2006
Reference Type:
publication
Title:
Unnamed
Year:
2008
Report date:
2008

Materials and methods

Objective of study:
other: other: Determine systemic bioavailability after oral adminstration in rats; disposition in humans
Test guideline
Qualifier:
no guideline followed
GLP compliance:
no

Test material

Radiolabelling:
yes

Test animals

Species:
other: rat, human
Strain:
Sprague-Dawley
Sex:
male/female
Details on test animals or test system and environmental conditions:
6 male rats; 3 male and 2 female human volunteers

Administration / exposure

Route of administration:
other: oral gavage (rat); gel capsule (human)
Vehicle:
corn oil
Duration and frequency of treatment / exposure:
Rats: single oral gavage dose of 300 mg/kg bw, dose volume of 3.2 ml
Humans: single gel capsule orally, 0.1 mg/kg bw
Doses / concentrations
Remarks:
Doses / Concentrations:
Rats: single oral gavage dose of 300 mg/kg bw, dose volume of 3.2 ml
Humans: single gel capsule orally, 0.1 mg/kg bw

No. of animals per sex per dose / concentration:
6 male rats
3 human males; 2 human females

Control animals:
no

Results and discussion

Main ADME resultsopen allclose all
Type:
metabolism
Results:
Metabolized mainly to sulfate conjugates in the rat, and to glucuronide conjugates in humans.
Type:
excretion
Results:
Rats: fecal excretion of unchanged TBBPA (>80% dose), trace amounts of sulfate-congugate in urine; Human: <0.1% dose in urine; feces not collected
Type:
distribution
Results:
Rats: TBBPA-sulfate main form in plasma followed by TBBPA and trace amounts of TBBPA-glucuronide ; Humans: TBBPA not detected in plasma, TBBPA-glucuronide was circulating form; trace amounts of TBBPA-sulfate in blood

Toxicokinetic / pharmacokinetic studies

Details on excretion:
Results in rats indicate sulfate and glucuronide conjugates are cleaved in the feces to the parent molecule.

Metabolite characterisation studies

Metabolites identified:
yes
Details on metabolites:
Rats: primarily TBBPA-sulfate
Humans: primarily TBBPA-glucuronide
Trace amounts of the disulfate and diglucuronide and/or tribombisphenol A conjugates

Applicant's summary and conclusion

Conclusions:
Interpretation of results (migrated information): no bioaccumulation potential based on study results
TBBPA is rapidly metabolized and eliminated as glucuronide and/or sulfate conjugates by humans and rats, such that its systemic bioavailability is low. The conjugate(s) is/are the circulating form of TBBPA in blood
Executive summary:

This study reports the characterization of the toxicokinetics of TBBPA in human subjects and in rats. A single oral dose of 0.1 mg/kg TBBPA was administered to five human subjects. Rats were administered a single oral dose of 300 mg TBBPA/kg body weight. Urine and blood concentrations of TBBPA and its metabolites were determined by LC/MS-MS. TBBPA-glucuronide and TBBPA-sulfate were identified as metabolites of TBBPA in blood and urine of the human subjects and rats. In blood, TBBPA-glucuronide was detected in all human subjects, whereas TBBPA-sulfate was only present in blood from two individuals. Maximum plasma concentrations of TBBPA-glucuronide (16 nmol/l) were obtained within 4 h after administration. In two individuals where TBBPA-sulfate was present in blood, maximum concentrations were obtained at the 4-h sampling point; the concentrations rapidly declined to reach the limit of detection (LOD) after 8 h. Parent TBBPA was not present in detectable concentrations in any of the human plasma samples. TBBPA-glucuronide was slowly eliminated in urine to reach the LOD 124 h after administration. In rats, TBBPA-glucuronide and TBBPA-sulfate were also the major metabolites of TBBPA present in blood; in addition, a diglucuronide of TBBPA, a mixed glucuronide-sulfate conjugate of TBBPA, tribromobisphenol A, and the glucuronide of tribromobisphenol A were also present in low concentrations. TBBPA plasma concentrations peaked at 103 μmol/l 3 h after administration and thereafter declined with a half-life of 13 h; maximal concentrations of TBBPA-glucuronide (25 μmol/l) were also observed 3 h after administration. Peak plasma concentrations of TBBPA-sulfate (694 μmol/l) were reached within 6 h after administration. In conclusion, TBBPA is rapidly metabolized after absorption by conjugation resulting in a low systemic bioavailability of TBBPA.