: The reviewers were not aware of any other studies that
should have been considered
for the derivation of the RfD.
Response: No response necessary.
B1) Are renal lesions (nephropathy) the most appropriate critical effect for deriving
the RfD? Points relevant to this determination include whether this effect demonstrated a
suitable dose-response relationship and whether the effect is considered adverse. Are these
issues objectively and transparently described?
Comment: Four reviewers concluded that nephropathy was the most appropriate critical effect
for deriving the RfD. One reviewer noted that human data were insufficient to select a critical
effect and that he was not qualified to judge the human relevance of the renal lesions in mice.
A reviewer who supported the selection of nephropathy as the critical effect stressed that
renal lesions were simply the best available data, but he did not think their use was completely
justified. In particular, this reviewer remarked that, while a dose-response relationship is
suggested, a statistically significant association at a lower dose was not found. Two other
reviewers commented on the apparent lack of a dose-response trend. Another reviewer noted
that barium may be like other nephrotoxic metals that tend to exhibit their renal effects when
body burdens are high and multiple toxic effects are likely to be seen.
Response: A dose-response relationship for chemical-related nephropathy was observed for both
male and female mice. Evidence of the dose-response relationship was derived from the
biologically significant findings of mild to moderate nephropathy at the intermediate dose (75
mg/kg-day and 90 mg/kg-day for males and females, respectively). These data in conjunction
with the statistically significant increased incidence of nephropathy at the highest dose provide
information about the effects of low dose and high dose exposures to barium in drinking water.
The severity of lesions at the intermediate dose was an important consideration in the
determination of biological significance of these findings. The lesions observed at this dose
were qualified as mild to moderate as opposed to minimal nephropathy which was observed in a
few animals that received the low dose or were untreated. Minimal nephropathy is likely to be
associated with a background incidence of renal effects. As one of the reviewers noted the
effects observed in the high dose treatment group, which had a statistically significant increase in
nephropathy, were quite severe and fatal in many cases.
A-8
B2) Is the rationale for not using hypertension as the critical effect justified and
objectively and transparently presented? Is this rationale correct?
Comment: All five reviewers agreed that the rationale for not using hypertension as the critical
effect was justified. Several reviewers commented that the presentation could be clearer and
suggested including additional information on the limitations of the studies. One reviewer noted
that due to the methodological limitations of the human studies, the effect of chronic barium
ingestion on hypertension is unknown.
Response: Two human studies have investigated the effects of barium ingestion on blood
pressure (Brenniman et al., 1981; Wones et al.,1990). Both investigations found no hypertensive
effect with their highest exposure concentrations. Brenniman et al. (1981) found no effect on
hypertension between two communities with a 70-fold difference in the barium concentrations of
their drinking water. Wones et al. (1990) found no hypertensive effect in a before-and-after
comparison of 11 subjects that were exposed to two concentrations of barium in their drinking
water over the course of 10 weeks. Coincidently, the same NOAEL of 0.21 mg/kg-day was
identified for both studies. These NOAELs were estimated by EPA using standard estimates for
drinking water intake (2 L/day) and average body weight (70 kg).
Neither Brenniman et al. (1981) nor Wones et al. (1990) provided sufficient data to
support, or refute, the hypothesis that chronic barium exposure causes hypertension.
Hypertension is a complex multifactorial condition. It is very possible that the effect of chronic
barium exposure on blood pressure is relatively small compared to other determinates such as
diet and exercise. Wones et al. (1990) attempted to control for the effect of diet by providing a
standard diet to all of the study participants. Unfortunately, the power of this study was limited
by the very small number of participants (n=11). This study was also of a short exposure
duration (4 weeks for each exposure concentration) that may not have been sufficient to observe
a chronic effect. Brenniman et al. (1981) also examined a relatively small number of subjects
(n=85) in a subpopulation that was controlled for key risk factors. Other limitations of the
Brenniman et al. (1981) study include collecting replicate blood pressure measurements from
individuals during a single 20-minute period, using community-wide exposure estimates, and not
controlling for a number of important risk factors for hypertension, including diet and exercise.
In the absence of dose-response data for barium-induced hypertension, it was not considered
scientifically sound to base the RfD on this effect. Additional text describing the limitations of
these studies has been added to Section 5.1.1 of the Toxicological Review. In addition, text has
been added to indicate the effect of barium hypertension in humans is unknown.
A-9