Abstract

PurposeSewage sludge samples from a water treatment plant in Nigeria were subjected to an in-vessel composting (using sawdust as a bulking agent) and thermal sludge processing to improve its quality for agricultural applications.MethodsTreated samples were analyzed for physicochemical and microbiological properties using standard analytical and aerobic culture protocols.ResultsMicrobiological analysis of the initial fresh mixture (sewage sludge/sawdust) showed that the total heterotrophic bacteria was 1.17 × 106 CFU/g of fresh compost, coliforms 4.7 × 104 CFU/g, Salmonella sp., and Shigella sp. 7.3 × 104 CFU/g, yeasts and moulds 9.0 × 104 CFU/g. These values were significantly (p = 0.05) reduced after 40 days of in-vessel composting to 4.3 × 104 CFU/g for total heterotrophic bacteria, 7.4 × 102 CFU/g for coliforms, while yeasts and moulds, Salmonella and Shigella sp. were not detected in the final compost. The results of the physicochemistry revealed variation in pH, temperature, and nutrients status of treated sludge.ConclusionSalmonella sp., Staphylococcus aureus, and Shigella sp. were eliminated, while a 2-log reduction in coliform counts occurred after 40 days of composting. Composting had a better processing impact by increasing the ash as well as reducing the carbon/nitrogen ratio of treated sludge, while thermal processing improved the sulfate and phosphate components of treated sludge. The treated sludge (biosolids) met the permissible limits of microbiological and nutritional standards recommended by US EPA for land application of sludge and could, therefore, be used as a biofertilizer, soil conditioner and also for land reclamation.

Highlights

  • ResultsMicrobiological analysis of the initial fresh mixture (sewage sludge/sawdust) showed that the total heterotrophic bacteria was 1.17 9 106 CFU/g of fresh compost, coliforms 4.7 9 104 CFU/g, Salmonella sp., and Shigella sp. 7.3 9 104 CFU/g, yeasts and moulds 9.0 9 104 CFU/g

  • Purpose Sewage sludge samples from a water treatment plant in Nigeria were subjected to an in-vessel composting and thermal sludge processing to improve its quality for agricultural applications

  • Microbiological analysis of the initial fresh mixture showed that the total heterotrophic bacteria was 1.17 9 106 CFU/g of fresh compost, coliforms 4.7 9 104 CFU/g, Salmonella sp., and Shigella sp. 7.3 9 104 CFU/g, yeasts and moulds 9.0 9 104 CFU/g. These values were significantly (p = 0.05) reduced after 40 days of in-vessel composting to 4.3 9 104 CFU/g for total heterotrophic bacteria, 7.4 9 102 CFU/g for coliforms, while yeasts and moulds, Salmonella and Shigella sp. were not detected in the final compost

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Summary

Results

Microbiological analysis of the initial fresh mixture (sewage sludge/sawdust) showed that the total heterotrophic bacteria was 1.17 9 106 CFU/g of fresh compost, coliforms 4.7 9 104 CFU/g, Salmonella sp., and Shigella sp. 7.3 9 104 CFU/g, yeasts and moulds 9.0 9 104 CFU/g. Microbiological analysis of the initial fresh mixture (sewage sludge/sawdust) showed that the total heterotrophic bacteria was 1.17 9 106 CFU/g of fresh compost, coliforms 4.7 9 104 CFU/g, Salmonella sp., and Shigella sp. 7.3 9 104 CFU/g, yeasts and moulds 9.0 9 104 CFU/g These values were significantly (p = 0.05) reduced after 40 days of in-vessel composting to 4.3 9 104 CFU/g for total heterotrophic bacteria, 7.4 9 102 CFU/g for coliforms, while yeasts and moulds, Salmonella and Shigella sp. Were eliminated, while a 2-log reduction in coliform counts occurred after 40 days of composting. The treated sludge (biosolids) met the permissible limits of microbiological and nutritional standards recommended by US EPA for land application of sludge and could, be used as a biofertilizer, soil conditioner and for land reclamation

Introduction
Materials and methods
Results and discussion
Conclusion
Compliance with ethical standards
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