When cattle were allowed to graze land previously used as orchards, residues of DDE [1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene] were detectable in milk fat and adipose tissues. Concentrations of DDE exceeded .3 micrograms/g at times. Concentrations of DDE in adipose tissue were similar to those in milk fat at the beginning of lactation; residues in first lactation cows were approximately three times higher than in multiparous cows that were grazing similarly. Based on the equation [DDE, micrograms/g]milk fat = .28 (daily dose, mg).82, consumption of soil was likely not the sole source of residue when soil concentrations of DDT [1,1,1-trichloro-2,2-bis(p-chlorophenyl) ethane], DDE, and DDD [1,1-dichloro-2,2-bis(p-chlorophenyl)ethane] ranged from non-detected to 3.6, 2.1, and .655 micrograms/g, respectively. Grass appeared to be the likely source. Four plots were located on three orchard locations and one control location. Grasses in subplots were harvested at 2-, 4-, or 6-wk intervals during the 18-wk study. Grasses were extracted differentially to determine DDT and DDE residues adhering to the plant surface and those associated with plant tissue. Surface residue was not significant. The DDE averaged between .01 and .11 micrograms/g in dry grass tissues. Differences between residues in grasses among plots were associated with soil residue concentrations. Concentrations of DDE were not associated with air or soil temperature, relative humidity, solar radiation, or dry biomass harvested. Precipitation increased the volatilization of residues from soil and deposition in 2- and 4-wk grass samples.(ABSTRACT TRUNCATED AT 400 WORDS)

The toxicity of a commercial preparation of polybrominated biphenyl was determined in 24 pregnant Holstein heifers that were alloted randomly to one of four experimental groups given 0 (I), .25 (II), 250 (III), and 25,000 (IV) mg per day of fireMaster BP-6 for 60 days or until the animals became moribund. Clinicopathologic determinations were on day -1 prior to dosing, days 15, 30 and 60 during dosing, and following dosing on days 80, 110, 150, and 190 from start of dosing. In addition, samples were collected from moribund heifers of Group IV immediately prior to necropsy. Toxicity was not evident in heifers in Groups I, II, or III. Toxicity was induced in heifers in Group IV. Glutamic-oxaloacetic transaminase of serum was increased and calcium decreased as early as day 15 whereas significant increases in lactate dehydrogenase, urea nitrogen, and bilirubin, and decreases in albumin were not observed until day 30 in heifers of Group IV. Analysis of urine from moribund heifers of Group IV revealed moderate proteinuria and decreased specific gravity. Evaluation of clinicopathologic data has suggested that the polybrominated biphenyls fed were renal toxins with no clear evidence of hepatotoxicity.

Sixty dairy animals were utilized in seven experiments to determine aspects of the distribution and clearance of FireMaster BP-6. Experimental protocols of various studies provided daily exposures from 0.25 to 25,000 mg, exposures for I to 202 days, and total study periods from 10 to 1100 days. Necropsy of 28 animals provided information on residue concentrations in 35 tissues, and the excretion in milk was determined in 15 animals. These studies showed that the major brominated biphenyls of this commercial mixture were absorbed from the gastrointestinal tract and appeared in the blood plasma within 4 hr. With continued exposure to the residue plasma concentrations reached a steady state by 15 days. Free PBB was not detectable in urine. During PBB feeding feces was the major route of excretion, representing approximately 50%o of the amount fed to animals not displaying signs of toxicosis. Following withdrawal of PBB, fecal concentrations declined to 1 to 2% of concentrations during dosing, yet, feces remained the major excretory route in nonlactating animals. In contrast, in post-exposure lactating animals milk fat became an important excretory route removing three-times the quantity of residue cleared in feces. Following parturition, concentrations of PBB in milk fat declined approximately twofold in 6 days. Thereafter, the residue concentration in milk fat was approximately 0.4 that in depot fats. PBB had a predilection for lipid tissues with similar concentrations in various depot fats. Concentrations of the residue were notably low in tissues of the nervous system despite the high content of lipid material. Liver contained residue concentrations that were disproportionately high when compared to the lipid content of the organ. Calves born to PBB-exposed cows had similar distribution of residues in body tissues although concentrations were less than those of the dam.

The toxicity of a commercial blend of polybrominated biphenyls was determined in 24 pregnant Holstein heifers that were allotted randomly to one of four experimental groups given 0, .25, 250, or 25,000 mg/day of fire-Master BP-6. The polybrominated biphenyls were mixed with finely ground corn and given by bolus for 60 days or until the animal became moribund. Average body weight of heifers at onset of experiment was 381 kg. No clinical signs of toxicosis were evident in heifers fed 0, .25 or 250 mg/day. Toxicosis was induced in heifers fed 25,000 mg/day resulting in reduced dry matter intake, body weight, heart rate, and respiration rate. Clinical signs were anorexia, emaciation, dehydration, excessive lacrimation and salivation, diarrhea, depression, and abortion or fetal death. All heifers fed 25,000 mg/day became moribund within 33 to 66 days.

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