3-CHLORO-1,2-PROPANEDIOL

Overview

Synonyms
3-MCPD
CAS number
96-24-2
Functional Class
Food Contaminant
CONTAMINANT

Evaluations

Evaluation year: 2016

Comments:
No genotoxic potential has been demonstrated in vivo for 3-MCPD. Two long-term carcinogenicity studies with 3-MCPD in rats were identified as pivotal studies, and renal tubular hyperplasia was identified as the most sensitive end-point. The lowest BMDL10 for renal tubular hyperplasia was calculated to be 0.87 mg/kg bw per day for male rats. After application of a 200-fold uncertainty factor, the Committee established a group PMTDI of 4 µg/kg bw for 3-MCPD and 3-MCPD esters singly or in combination (expressed as 3-MCPD equivalents). The overall uncertainty factor of 200 incorporates a factor of 2 related to the inadequacies in the studies of reproductive toxicity. The previous PMTDI of 2 µg/kg bw for 3-MCPD, was withdrawn. The Committee noted that estimated dietary exposures to 3-MCPD for the general population, even for high consumers (up to 3.8 µg/kg bw per day), did not exceed the new PMTDI. Estimates of mean dietary exposure to 3-MCPD for formula-fed infants, however, could exceed the PMTDI by up to 2.5-fold for certain countries (e.g. 10 µg/kg bw per day in the first month of life).
Tolerable Intake:
PMTDI of 4 µg/kg bw for 3-MCPD and 3-MCPD esters singly or in combination
Meeting:
83
Tox Monograph: 

Evaluation year: 2006

Comments:
As no new pivotal toxicological studies had become available the Committee retained the previously established PMTDI of 2 µg/kg bw for 3-chloro-1,2-propanediol. This PMTDI was established based on a LOEL of 1.1 mg/kg bw/d from a drinking water carcinogenicity study in Fischer/344 rats and a safety factor of 500. Estimated exposures at the national level considered a wide range of foods, including soy sauce and soy-sauce related products, ranged from 1% to 35% of the PMTDI for average exposure in the general population. For the consumers at the high percentile (95th), the estimated intakes ranged from 3% to 85% and up to 115% of the PMTDI in young children. These estimates are based on concentrations of 3-chloro-1,2-propanediol derived before any remedial action had been taken by government or industry. The Committee noted that reduction in the concentration of 3-chloro-1,2-propanediol in soy sauce and related products made with acid-HVP could substantially reduce the intake of this contaminant by certain consumers of this condiment.
Intake:
population mean: 0.7 µg/kg bw/d; 95th-percentile intake: 2.3 µg/kg bw/d, estimates include young children. Consumption of some highly-contaminated products could result in intakes exceeding the PMTDI.
Tolerable Intake:
PMTDI 2 µg/kg bw/d
Meeting:
67

Toxicological study

Pivotal Study:
Long term study of toxicity and carcinogenicity in Fisher 344 rats via drinking water administration (Sunahara et al., 1993). The Committee concluded that the LOEL for adverse effects of treatment in the kidney was close to the NOEL for this effect.
Animal Specie:
Fisher 344 rats
Effect:
Kidney proximule tubule hyperplasia
NOAEL:
Not defined
LOEL:
1.1 mg/kg bw/d
PMTDI:
2 µg/kg bw
Point of departure:
LOEL : 1.1 mg/kg bw/day
Previous Years:
2001, TRS 909-JECFA 57/114, FAS 48-JECFA 57/401. Provisional maximum tolerable daily intake (PMTDI): 2 µg/kg bw. 1993, TRS 837-JECFA 41/30,31, FAS 32-JECFA 41/267. LEVELS IN HYDROLYSED VEGETABLE PROTEINS SHOULD BE REDUCED AS FAR AS TECHNICALLY POSSIBLE
2001, TRS 909-JECFA 57/114, FAS 48-JECFA 57/401. Provisional maximum tolerable daily intake (PMTDI): 2 µg/kg bw. 1993, TRS 837-JECFA 41/30,31, FAS 32-JECFA 41/267. LEVELS IN HYDROLYSED VEGETABLE PROTEINS SHOULD BE REDUCED AS FAR AS TECHNICALLY POSSIBLE