N-(1,3-Dimethylbutyl)-N
N-(1,3-Dimethylbutyl)-N
N-(1,3-Dimethylbutyl)-N
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OECD SIDS<br />
N-(1,3-DIMETHYLBUTYL)-N´-PHENYL-1,4-PHENYLENEDIAMINE<br />
3 HUMAN HEALTH HAZARDS<br />
3.1 Effects on Human Health<br />
3.1.1 Toxicokinetics, Metabolism and Distribution<br />
There are no studies on the toxicokinetics of 6PPD available.<br />
However, some conclusions can be drawn from toxicity studies with acute and repeated application:<br />
The appearance of systemic toxicity after oral and dermal exposure shows the principal<br />
bioavailability of 6PPD via these routes.<br />
Biomonitoring of workers in the rubber industry detected 6PPD in urine thereby demonstrating that<br />
the substance can be resorbed from the respiratory tract and possibly after dermal contact (Rimatori<br />
and Castellino, 1989).<br />
3.1.2 Acute Toxicity<br />
Inhalation<br />
There are no data available.<br />
Dermal<br />
There are no studies according to the current OECD guideline but there are 2 older studies which<br />
give sufficient information to evaluate this endpoint: No mortality was observed after a 24-hour<br />
semi-occlusive application of 3160, 5010 or 7940 mg 6PPD/kg bw to the clipped intact skin of 2<br />
rabbits/dose (LD 50 > 7940 mg/kg bw). Reduced appetite and activity for 3-7 days were the only<br />
clinical signs, whereas the viscera appeared normal (Randall and Bannister, 1990). In a second<br />
study 6PPD was applied at doses of 798, 1260, 2000, 3160, 5010, 7980 mg/kg bw (1 rabbit/dose)<br />
under a dressing of plastic strips. Doses of 5010 mg/kg bw caused mortality after 10-11 days<br />
accompanied by loss of appetite, lethargy and gradual wasting. Gross autopsy yielded liver<br />
discoloration and pulmonary hyperemia. According to this study the LDL 0 is in the range between<br />
3160 and 5010 mg/kg bw (Younger, 1962).<br />
Conclusion<br />
The dermal LD 50 in rabbits was > 3000 mg/kg bw. Signs of intoxication were reduced food<br />
consumption, hypoactivity and lethargy.<br />
Oral<br />
There is one study according to the OECD TG 401 (Hatano Research Institute, 1999; Ohara et al.,<br />
1999a) and some other study reports with rats which give sufficient information to evaluate this<br />
endpoint (Randall and Bannister, 1990; Younger, 1962).<br />
In the OECD guideline study 5 male and 5 female rats were dosed with 0, 250, 500, 1000 and 2000<br />
mg 6PPD/kg bw in corn oil by gavage. Deaths occurred at day 2 – 4 p.a. at 1000 mg/kg (2/5 males<br />
and 3/5 females) and at 2000 mg/kg (all animals), resulting in LD 50 values between 1000 – 2000<br />
mg/kg for male rats and 500 – 1000 mg/kg for female rats. Signs of intoxication were hypoactivity ,<br />
diarrhea, bradypnea, hypothermia and a prone position in the 1000 mg/kg or higher dosed groups,<br />
abnormal gait in 2000 mg/kg males, and lacrimation and weakness of limbs in 2000 mg/kg females.<br />
Pathological lesions were observed in digestive organs and the respiratory system (Hatano Research<br />
Institute, 1999; Ohara et al., 1999a).<br />
UNEP PUBLICATIONS 19