As a component to the risk assessment process for para-nonylphenol (NP
; CASRN 84852-15-3), a 90-day study was conducted in rats following U.
S. EPA TSCA guidelines and Good Laboratory Practice regulations. NP wa
s administered to four groups of rats at dietary concentrations of 0,
200, 650, or 2000 ppm which corresponded to approximate dietary intake
s of 0, 15, 50, or 150 mg/kg/day, respectively. There were 25 rats/sex
/group in the control and high-dose groups and 15 rats/sex/group in th
e low-and middose groups. Ten of the 25 rats/sex in the control and hi
gh-dose groups were designated as recovery animals and were maintained
on control diets for 4 weeks after completion of the 90-day exposure
period to assess the reversibility of any effects which might be obser
ved. To evaluate for the possible weak estrogen-like activity that has
been reported for NP in a number of screening assays, estrous cyclici
ty was monitored using vaginal cytology during Week 8 of the study, an
d sperm count, motility, and morphology were evaluated at termination.
In-life effects from NP exposure were limited to small decreases in b
ody weight and food consumption in the 2000-ppm dose group. Postmortem
measurements at Week 14 indicated a dose-related kidney weight increa
se in males and a decrease in renal hyaline globules/droplets in males
from the high-dose group. The kidney weights showed complete recovery
following the 4-week postdosing recovery period. Due to the small mag
nitude of the changes (i.e., all weights were within or near laborator
y historical control values) and the lack of correlating clinical or h
istopathological changes, the kidney weight alterations were not consi
dered toxicologically significant. The biological significance of redu
ced hyaline in the kidneys of male rats from the high-dose group is un
certain. Renal tubular hyaline is associated with the rat-specific pro
tein, cy-au-globulin, and, therefore, this finding was not considered
toxicologically relevant to humans. No other effects attributable to N
P were observed. No changes were observed for estrous cycling, sperm e
valuations, or effects on endocrine organs, NP, therefore, did not man
ifest any estrogen-like activity as measured in these parameters at di
etary concentrations as high as 2000 ppm, the maximum dose administere
d in this study. Based on the minor findings for the 2000-ppm dose gro
up, the NOAEL (no-observed-adverse-effect level) for NP in this study
is considered to be 650 ppm in the diet, corresponding to an approxima
te intake of 50 mg/kg/day. (C) 1997 Academic Press.