49
BARIUM AND BARIUM COMPOUNDS
3. HEALTH EFFECTS
Gastrointestinal Effects.
All cases of acute oral barium poisoning in adults exhibit gastrointestinal
disturbances as the initial symptoms. These include gastric pain, vomiting, and diarrhea (Das and Singh
1970; Diengott et al. 1964; Downs et al. 1995; Gould et al. 1973; Jha et al. 1993; Lewi and Bar-Khayim
1964; McNally 1925; Morton 1945; Ogen et al. 1967; Phelan et al. 1984; Silva 2003; Talwar and Sharma
1979; Wetherill et al. 1981). In one case, severe gastrointestinal hemorrhage occurred in an adult male
victim (Diengott et al. 1964).
Although gastrointestinal effects have been observed in some animal studies, most studies have not found
effects. Inflammation of the intestines was noted in rats receiving a single gavage dose of 198 mg
barium/kg as barium chloride (Borzelleca et al. 1988); but not in rats administered 10 doses of 198 mg
barium/kg/day (Borzelleca et al. 1988). Stomach rupture, bowel obstruction, and gastrointestinal
hemorrhage have been observed in rats dosed with barium sulfate; however, those adverse effects were
most likely due to the massive doses of barium sulfate used in the study (25–40% of body weight) and not
necessarily to barium toxicity (Boyd and Abel 1966). A 15-day exposure of male and female rats and
mice to 110 or 70 mg barium/kg/day as barium chloride in drinking water, respectively, did not result in
histological alterations in the gastrointestinal tract (NTP 1994). No gross or microscopic lesions of the
esophagus, stomach, pancreas, small intestines, or colon were noted in several intermediate and chronic
experiments in which male and female rats were exposed to doses as high as 180 mg barium/kg/day as an
unspecified barium compound or barium chloride in drinking water (McCauley et al. 1985; NTP 1994) or
male and female mice exposed to doses as high as 450 mg barium/kg/day as barium chloride (NTP 1994).
Hematological Effects.
Results of animal studies indicate that acute, intermediate, and chronic oral
exposure to barium is not associated with any adverse hematological effects. No alterations were found
in rats administered 198 mg barium/kg/day as barium chloride for 10 days (Borzelleca et al. 1988) or in
rats or mice exposed to 110 or 70 mg/kg/day, respectively, as barium chloride in drinking water for
15 days (NTP 1994). Intermediate and chronic oral exposure of rats to barium acetate and barium
chloride in drinking water has not been associated with any significant or treatment-related changes in a
variety of hematological parameters (NTP 1994; Tardiff et al. 1980). Elemental barium doses in these
intermediate and chronic drinking water studies ranged from 15 to 450 mg/kg/day.
Musculoskeletal Effects.
The predominant musculoskeletal effect observed in cases of barium
toxicity in humans is progressive muscle weakness, often leading to partial or total paralysis (Das and
Singh 1970; Diengott et al. 1964; Gould et al. 1973; Lewi and Bar-Khayim 1964; McNally 1925; Morton
1945; Ogen et al. 1967; Phelan et al. 1984; Wetherill et al. 1981). In severe cases, the paralysis affects
50
BARIUM AND BARIUM COMPOUNDS
3. HEALTH EFFECTS
the respiratory system (Das and Singh 1970; Gould et al. 1973; Lewi and Bar-Khayim 1964; Morton
1945; Ogen et al. 1967; Phelan et al. 1984; Wetherill et al. 1981). The likely cause of the muscle
weakness was the barium-induced hypokalemia rather than a direct effect on muscles.
Very limited animal data are available regarding the musculoskeletal effects of barium following oral
exposure. No gross and microscopic lesions were observed in skeletal system of several intermediate and
chronic experiments in which rats were exposed to an unspecified barium compound or barium chloride
in drinking water at doses as high as 180 mg barium/kg/day for intermediate duration and as high as
60 mg barium/kg/day for chronic duration (McCauley et al. 1985; NTP 1994; Tardiff et al. 1980);
similarly, no effects were observed in mice exposed to 450 or 160 mg barium/kg/day as barium chloride
in drinking water for intermediate or chronic durations, respectively (NTP 1994).
Hepatic Effects.
In one case study involving accidental acute ingestion of barium carbonate in an
adult female, some degeneration of the liver was noted post-mortem (McNally 1925). Adverse hepatic
effects in animals following oral barium exposure have been minor or have not been observed. Decreased
liver/brain weight ratio and darkened liver were observed in rats administered a single gavage dose of
198 mg barium/kg as barium chloride; however, these changes were not associated with any microscopic
hepatic lesions or alterations in serum enzymes (e.g., serum glutamic-oxaloacetic transaminase [SGOT],
serum glutamic pyruvic transaminase [SGPT], alkaline phosphatase). No histological or liver weight
alterations were observed in rats dosed with 198 mg barium/kg/day as barium chloride for 1 or 10 days
(Borzelleca et al. 1988) or in rats and mice exposed to 110 or 70 mg barium/kg/day, respectively, as
barium chloride in drinking water for 15 days (NTP 1994). Intermediate and chronic studies involving
oral exposure of rats or mice to barium in drinking water did not find significant alterations in liver
weight or liver histopathology following exposure to doses as high as 180 mg barium/kg/day for rats and
450 mg barium/kg/day for mice (McCauley et al. 1985; NTP 1994; Schroeder and Mitchener 1975a,
1975b; Tardiff et al. 1980).
Renal Effects.
Toxic effects on the kidneys have been observed in several adult cases of acute barium
poisoning. Effects include hemoglobin in the urine (Gould et al. 1973) (which may be indicative of
kidney damage), renal insufficiency (Lewi and Bar-Khayim 1964; Phelan et al. 1984), degeneration of the
kidneys (McNally 1925), and acute renal failure (Wetherill et al. 1981).
Studies in animals suggest that the kidney is a critical target of barium toxicity. An increase in relative
kidney weight (kidney/brain weight ratio) was observed in male and female rats receiving a single gavage