Animal waste handling and disposal in confinement production of swine.
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Mice were dry-distilled at 800 degrees C for 10 min, after [32P]orthophosphate or L-[4,5-3H]leucine was intraperitoneally administered. Phosphorus-32 was quantitatively recovered in the residual solid, whereas 95% of 3H was found int he distillate (condensed water). When 14C (L-[U-14C]malic acid or L-[U-14C]leucine) was administered to mice and they were dry-distilled, 14C-radioactivity was distributed into two fractions; residual solid and exhaust gas. In these cases, the recovery percentage of 14C in residual solid was not very high but increased as the treating temperature decreased. It reached about 40% of the administered 14C at 400 degrees C for 120 min. By the dry-distillation of animals, their weight was reduced to about 10% in every animal tested (mice, rats and rabbits). The volume was reduced to about 20% in cases of mice and rats, and about 30% in case of rabbits. It was concluded that the dry-distillation can be useful as a pre-treatment for disposal of animal wastes containing radioisotopes.
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OBJECTIVES: To compare the bacteriological quality of out-house (tank or standpipe) water and in-house drinking water (storage containers) and determine the risk factors influencing it. DESIGN: A cross-sectional study. SETTING: The study was carried out in Kibera slums located 7 km southwest from the Nairobi City centre. SUBJECTS: Water samples from twenty outside tanks/standpipes and sixty from in-house water storage containers. MAIN OUTCOME MEASURES: Pour plate method was used to enumerate total bacterial counts in water, while the multiple tube technique was used to determine faecal coliform (FC) and faecal streptococci (FS) numbers. A questionnaire and environmental observation were used to determine the risk factors influencing bacteriological quality of water. RESULTS: The mean total bacterial counts (TBC) for out-house water was 46.6 per 100 ml while that for in-house water was 818.2 per 100 ml. Faecal coliforms were isolated from 7 (35%) standpipes and 57 (95%) in-house storage containers. The mean faecal coliform count was 93 and 103.4 per 100 ml for out-house and in-house water, respectively. The counts were significantly higher in the latter. Faecal streptococci were isolated from 2 (10%) standpipes and 37 (61.7%) in-house storage containers. The mean faecal streptococci counts were 35 and 65 per 100 ml for out-house and in-house water sources, respectively. Escherichia coli was isolated in 2 (10%) of out-house water and 30 (50%) of in-house. Of these, four were enteropathogenic, serotype 011 from one out-house water source and serotypes 011, 011, 0112ac from in-house water sources. CONCLUSIONS: Bacteriological contamination of water at the source with a further deterioration between the collection points and homes was observed. A defective water delivery system and inadequate environmental sanitation were a potential source of contamination for out-house water. Scoops were a major source of contamination for stored water.
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BOD (Biochemical Oxygen Demand) is utilized widely as an index of water quality. However, nitrification is a cause of significant errors in measuring BOD, particularly when a large population of nitrifying organisms are existing in water such as effluents from biological treatment plants. In this case, the use of a nitrification inhibitor is recommended, but it is not used commonly. In order to investigate the amount of nitrogenous oxygen demand (NOD) which is caused by nitrification, BOD with and without inhibitor was measured as samples in the Kitakyushu area. About 70 percent of BOD from the effluents of biological treatment plants was NOD. In the case of influent of biological treatment plant and river waters, 0-39 percent of NOD was contained in BOD.
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The paper reports the results of a study on occupational risks of a group of sewage workers of the city of Genoa vs. a control group of nonexposed subjects; the first group was divided into three subgroups according to the job characteristics. After bibliographical research on the topic, a specific questionnaire was used to analyse individual symptoms. Clinical examinations, blood and respiratory tests were also performed. The statistical analysis was performed by evaluating F test for differences between parametric measures and the relative risk for non-parametric findings. The relative risk of alterations in respiratory function (both instrumental and clinical findings) was increased among the water treatment workers. The average platelets count in the exposed workers appeared to be significantly reduced compared to non-exposed subjects although both were within the normal limits. There was non evidence of an increased prevalence of positive A hepatitis markers in the exposed workers.