SALMONELLAE IN CRUDE SEWAGE, SEWAGE EFFLUENT AND SEWAGE-POLLUTED NATURAL WATERS.
Explore the source record for details and available documents.
SEARCH · PubMed Health
Explore indexed PubMed citations for clinical trials, systematic reviews and public health research. Read source abstracts and follow each citation to its original PubMed record.
Quote a phrase for an exact phrase match. Source license links do not imply unrestricted reuse.
Explore the source record for details and available documents.
Explore the source record for details and available documents.
Explore the source record for details and available documents.
The quantity and serotypes of enteroviruses (EVs) in the influent of a local sewage treatment plant were compared to local clinical EV cases to determine if testing of sewage is adequate for an EV surveillance system. The study was carried out from August 1994 to December 2002. Monthly influent specimens were processed by organic flocculation, and dilutions of concentrate were inoculated onto a number of different cell types for virus isolation. EVs were detected in 88 of 100 monthly influent samples. Sewage EV titers were calculated by using software provided by the U.S. Environmental Protection Agency for most-probable-number determination. All 1,068 sewage EV isolates were further grouped (echovirus, coxsackievirus B, coxsackievirus A, or poliovirus) by cell culture host range analysis (growth pattern of isolates on passage to seven cell lines), and 39.0% of the 1,022 EV isolates categorized as non-poliovirus EVs were specifically serotyped. For clinical cases, primary virus isolation tests were performed on specimens submitted by local hospitals and EV isolates submitted by hospitals were serotyped. Clinical EVs were documented for 81 of the 100 months studied. In all, 694 EV isolates from clinical cases were serotyped. Annually, between 4 and 11 different serotypes of non-poliovirus EVs were identified in sewage and from 9 to 19 different non-poliovirus EV serotypes were identified from clinical specimens. Usually, the most commonly detected sewage EV serotypes were similar to the most commonly detected clinical serotypes; e.g., for 1997, echovirus 6 accounted for 53.1% of the typed sewage isolates and 39.4% of the clinical infections, while in 1998, echovirus 30 accounted for 50.0 and 46.1%, respectively. In 1999, 60.3% of the EVs from clinical cases and 79.7% of the sewage isolates were echovirus 11; in 2000, 33.3% of the EVs from clinical cases and 40.7% of the sewage isolates were coxsackievirus B5; and in 2001, 44.1% of the EVs from clinical cases and 36.2% of the sewage isolates were echovirus 13. Annual peaks of both sewage EV titers and clinical cases occurred in late summer or early fall. In some years, early spring sewage EVs portended some of the EVs that would predominate clinically during the following summer.
Explore the source record for details and available documents.
Explore the source record for details and available documents.
The numbers of salmonella serotypes in raw sewage, sewage sludge and final effluent at a sewage treatment works were determined. Resting gulls which had previously been feeding on the sewage were disturbed and individual faecal samples tested for the presence of salmonellae. The serotypes were compared with those in the sewage. Six serotypes were isolated from the sewage, Salmonella stanley being found in all types of samples. Eleven of the twenty gull faeces samples were positive for salmonellae, a carriage rate of 55%. Seven serotypes were found, S. stanley being most frequent. Three serotypes were found in both sewage and gull faeces.
The author reviews the agricultural use of night-soil, sewage, and sewage sludge from two points of view: the purely agricultural and the sanitary.Knowledge of the chemistry and bacteriology of human faecal matter is still rather scant, and much further work has to be done to find practical ways of digesting night-soil in a short time into an end-product of high fertilizing value and free of pathogens, parasites, and weeds.More is known about sewage and sewage sludge, but expert opinion is not unanimous as to the manner or the value of their use in agriculture. The author reviews a number of studies and experiments made in many countries of the world on the content, digestion, composting, agricultural value, and epidemiological importance of sewage and sewage sludge, but draws from these the conclusion that the chemistry, biology, and bacteriology of the various methods of treatment and use of waste matter need further investigation. He also considers that standards of quality might be set up for sludge and effluents used in agriculture and for water conservation.
Of the 41 kt of phosphorus reaching the sewage works in England and Wales 15 kt is removed in sewage sludge and the remainder is disposed of to rivers. 60% of the sewage sludge is now used as fertilizer and this proportion will no doubt increase in the future. The total use of sewage sludge, however, represents only about 5% of the current annual usage of artificial phosphorus fertilizer. At present there is no general economic incentive to make better use of the phosphorus in effluents. Phosphorus removal is expensive--about 2--3 pence/m3. If all the sewage effluents in England and Wales were to be so treated the cost would be about 100--150 million pounds annually, that is about 50% of the present costs of sewage treatment. In certain cases, but rarely in the UK, phosphate is removed, not to conserve phosphorus but to minimize the problems it creates in the environment. The phosphorus removed has little value as fertilizer. Alternative methods of using the phosphorus in effluents by the production and harvesting of crops of algae or aquatic plants have so far proved uneconomic. However, these methods need to be reviewed periodically as they may in the future become economically more attractive, especially in warmer climates where plant growth can be maintained throughout the year.
In order to evaluate quantitatively the effectiveness of virological examinations of sewage, a labeled virus in a dose of 7.5X10(9) PFU was introduced into the canalization system of a community. Such an amount of virus could be found in the canalization system if 5--10% of the residents would excrete it simultaneously. The labeled virus was selectively detected in the community sewage. This procedure has demonstrated that the routine methods for sewage collection, specimen treatment, and virus isolation permit virus detection when 5--10% of this virus excretors are available. The labeled virus entered the canalization system most actively within the first 2 hours after administration, then its amount declined, and within 24 hours ceased. The labeled virus was found on all swabs which were in the sewage flow since the time of administration to the 7th day. The maximum amount of virus was found on the swab which was in the sewage flow for the first 2 hours after virus administration. By 7 days the amount of labeled virus on swabs decreased 10-fold. Under experimental conditions, in sewage kept at 25 degrees C enteroviruses of the group of poliomyelitis, ECHO, and Coxsackie had approximately similar inactivation rate (0.16--0.22 Ig TCD50 per day) and the half-life period (1.3 days), that is, in 7 days the virus titer on a swab should decline by 1.0--1.5 Ig TCD50.
An increase in the concentration of Cu, Zn, Cr and Mn, and a decrease in the activities of aspartate amino transferase, alanine amino transferase and peroxidase were observed in the different fractions of wheat plants, following raw and differentially diluted (66% and 50%) sewage irrigation and dry primary settled sewage-sludge amendments of soils. The grain enrichment efficiencies for Cu, Zn and Mn were significantly low under all experimental conditions. On the other hand, the grain enrichment efficiency for Cr was low under all sewage irrigation conditions only. Except in the earheads of wheat plants from sludge-amended soil, catalase activities were significantly low in roots, stems and earheads of wheat plants, under all other treatment conditions investigated. The decrease in the proteinase activity was statistically significant in roots and earheads of sewage-irrigated plants; the activity in the stem was low following irrigation with raw and 66% sewage only. Proteinase activity was also significantly low in all fractions of wheat plants harvested from soil amended with 20 tonnes of sludge per hectare. The observed results appear to be due to an overall decrease in the metabolic status of the plants following sewage irrigation and sludge amendment of soils. Grain yields, however, were not reduced despite this metabolic effect.
Using the VIRMETADEN (acronym derived from virus adsorption enumeration) method to count cytopathogenic viruses adsorbed to cellulose nitrate membrane filters from prefiltered and decontaminated sewage samples was shown to be feasible. The numbers of naturally occurring enteroviruses recovered by the VIRMETADEN method were significantly higher than those obtained by standard plaque assay. For prefiltration of sewage samples, low protein binding polyvinylidene fluoride (PVDF) membranes of 0.65 and 5 microm pore size proved to be at least as good as prefilters used previously, both in the volume that could be filtered and in the low virus retention. Regarding decontamination, 0.22 microm pore size PVDF membranes were as good as chloroform treatment. Alternatively, decontamination with 0.05% phenol followed by filtration through 0.65 microm PVDF membrane filters proved to be an excellent method for clarifying and decontaminating the sample prior to enumerating viruses using the VIRMETADEN method. It allows good recovery and greater decontaminated sample volumes. The application of VIRMETADEN to decontaminated raw sewage and secondary effluent gave recoveries of approximately 100% of vaccinal polioviruses seeded in sewage. The advantage of this approach is that the same method is applicable to sewage affluents and effluents with a simple and fast method, which implies lower material and labour costs.
Samples of sewage, sewage sludge and sewage effluent from one or more of four sewage treatment plants were examined for the presence of Leptospira, Mycobacterium, Escherichia coli, Brucella abortus and Bacillus anthracis. Brucella abortus and Bacillus anthracis were not isolated. Eleven strains of E. coli potentially enteropathogenic for calves or piglets, eight pathogenic strains of Mycobacterium and one patho;genic Leptospira strain were isolated from 101, 189 and 189 samples respectively. Sewage sludge is no;t considered to play a major part in the epidemiology of disease caused by these organisms.
Simultaneous examinations for the presence of enteroviruses were carried out on sewage of the central aeration station, periferal collectors of the most populous institutions, preschool children's institutions as well as feces of children attending these institutions in a community of urban type. A high degree of coincidence of spectra of enteroviruses isolated from sewage of the central station, periferal collectors, sewage of children's institutions, and from the feces of most virus excretors was demonstrated. No enteroviruses found in occasional virus excretors were detected in sewage. Enteroviruses were regularly found in sewage of periferal collectors if approximately 10% of children excreted a certain virus type simultaneously.
Recent concern over the environmental impact of sewage sludge application to agricultural land has drawn particular attention to the wide range of organic contaminants that may enter sewage treatment processes and persist in biosolids for disposal. This paper discusses processes influencing the fate and behaviour of organic contaminants during wastewater treatment and reviews literature relating to specific contaminants identified in sewage sludge. The difficulties associated with the development of specific methods for the analysis of trace residues of organic contaminants in complex matrices such as sludge are discussed. Some potential issues relating to impact of sewage sludge disposed to agricultural land are also considered.
A new synthetic medium has been developed for routine use in laboratory-scale sewage treatment simulation and biodegradation tests, such as OECD guideline 302A & 303A or ISO method 11733. The new medium, Syntho, was designed to meet the following objectives: 1) to be more representative of real sewage than the existing standard OECD synthetic sewage, 2) the COD:N:P ratio and mineral composition must allow a good degree of biological nutrient (N, P) removal, and 3) the medium should result in stable unit operation, including good sludge settling and minimal need for control actions. The IAWQ Activated Sludge Model No. 2 (ASM2,) was used to help design the medium and predict reactor performance for different possible media compositions. The results obtained with Syntho indicate that Continuous Activated Sludge (CAS) units with or without nutrient removal can be operated routinely on this feed. The new medium was also characterized by means of a respiration test. The different influent fractions applied in the model were validated, and a respiration profile indicated that Syntho is a close approximation of real sewage.
A total of 882 samples of settled sewage, sewage sludges and final effluents from eight sewage treatment plants were examined for the presence of salmonellas. Of these samples 68% were positive, isolations being made most frequently from settled sewage (85%), raw sludge (87%) and anaerobically digested sludge (96%). Fewer isolations were made from final effluent (24%) and processed sludges (58%). Samples usually contained less than 200 salmonellas/100 ml and arguments are presented that such concentrations should not lead to disease in animals if suitable grazing restrictions are followed.
Deficient sanitation poses a serious threat to human and animal health, involving complex relationships between environments, animals, refuse, food, pathogens, parasites, and man. However, by sanitizing and stabilizing the organic matter of sewage sludge, agriculture can utilize it to maintain soil, water, and air quality. As ingredients in soil amendments, such bioresidues are a source of nutrients for plants. Stabilization and sanitation of sewage sludge safely couple its recycling and disposal. This coupling becomes increasingly important as economic and environmental constraints make strategies for waste disposal more difficult to apply. The occurrence of viruses, bacteria, yeasts, fungi, and zooparasites in sewage sludge is reviewed in this article, and consequential epidemiologic concerns that arise from sewage sludge recycling is also addressed.