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Last updated date: March 30, 2015
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Reports

Advisory Committee on Health Effects of Endocrine Disruptors
The Supplement II to the Intermediary Report
1.4.1.3

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3.12 Organophosphorus pesticides

  • Gas chromatography-mass spectrometry (GC/MS) of pentafluorodibromide derivatives, determination limit (S/N = 10) 1.0 g/l for DMP and 0.3 g/l for DEP, DMTP and DETP, detection limit (S/N = 3) 0.3 g/l for DMP, 0.1 g/l for DEP, DMTP and DETP:
    Urinary concentration of four dialkyl phosphates as representative metablolites were measured for a group of occupationally exposed workers and a non-exposed control group.
    The exposed workers (n = 52) showed 76.4 } 164.4 g/l DMP (range below determination limit to 880 g/l, median 17.2 g/l), 3.7 } 15.7 g/l DEP (below determination limit - 112 g/l, 0.4 g/l), 21.8 } 47.5 g/l DMTP (below determination limit - 216 g/l, 2.2 g/l) and 2.7 } 5.4 g/l DETP (below determination limit - 22 g/l, 0.2 g/l), while the control group (n = 18) showed 35.4 } 37.7 g/l DMP (below determination limit - 127 g/l, 20.1 g/l), 6.0 } 9.3 g/l DEP (below determination limit - 31 g/l, 1.3 g/l), 20.6 } 47.4g/l DMTP (below determination limit - 191 g/l, 2.7 g/l) and 4.3 } 7.8 g/l DETP (below determination limit - 33 g/l, 1.4 g/l). In short, the four dialkyl phosphates were present in both workers and control group at approximately the same levels, except for higher levels of DMP in some workers. The DMP level in the control group was somewhat higher than the counterpart in the U.S., suggesting a need for more extensive measurements for exposure estimation.7)
3.13 Organochlorine compounds (DDTs, PCBs and dioxins)
  • The levels of residual organochlorine compounds in fat tissues (45 samples) were DDTs > PCBs > HCHs1 > CHLs2 > HCB3 > TCPMe4 > TCPMOH5. The concentrations of TCPMe and TCPMOH in the fat tissues were 2.7-44 ng/g fat (average 18) and 0.28-31 ng/g fat (average 12), respectively, which were lower by two orders of magnitude than DDT concentrations. The level of these compounds in the liver were 1.1-20 (average 7.0) and <4.0-38 (average 19) ng/g lipid, respectively. In bile, TCPMe level was <5.0-62 (average 17) ng/g lipid, i.e. somewhat higher than in the liver, but TCPMOH was under the detection limit. DDTs were present in fat at a level of 160-8100 ng/g lipid (average 2300), the highest among the compounds studied. The levels of HCHs, CHLs and HCB in the fat tissue were approximately the same as previously reported. The concentrations of HCHs in the fat tissue were 47-3200 ng/g lipid (average 680), which were higher than the levels of CHLs (average 310 ng/g lipid) and HCB (average 60 ng/g lipid).5)
  • In order to investigate effects on children, a project for estimation of background exposure to PCBs and dioxins in the fetal and infantile stages was started in Hokkaido. Non-ortho PCBs, mono-ortho PCBs, Coplanar PCBs and total TEQ were low in pregnant women under 30; PCDDs-TEQ, PCDFs-TEQ, DDDF and total TEQ were high in primigravidas. The blood dioxin levels in this study were generally lower than those found in other areas studied in the past.8)
  • Analysis of dioxins, PCBs and organochlorine-based pesticides for 80 women with chief complaint of infertility (26-43 years of age) resulted in a median of 25.1 pg/g lipid of the total TEQ. 2,3,7,8-TCDD was found in 7 patients (9%) in a range of 1.7-4.2 pg/g lipid (cf. determination limit 1.7-12.2 pg/g lipid). The level in serum of dioxins, PCBs and organochlorine pesticides tended to increase with the intake frequency of fish. Such correlation was not observed for other foods.3)
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1 Hexachlorohexane
2 Chlordane
3 Hexachlorobenzene
4 Tris(4-chlorophenyl)methane
5 Tris(4-chlorophenyl)methanol

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