ABSTRACT
Organic nutrient sources such as farmyard manure, sewage sludge, their biogas digestates or other animal by-products can be valuable fertilizers delivering organic matter to the soil. Currently, especially phosphorus (P) is in the focus of research since it is an essential plant nutrient with finite resources, estimated to last only for some more decades. Efficient utilization of organic P sources in agriculture will help to preserve P resources and thereby has the potential to close nutrient cycles and prevent unwanted P-losses to the environment, one of the major causes for eutrophication of water bodies. Unfortunately, organic P sources usually contain also various detrimental substances, such as potentially toxic elements or organic contaminants like pharmaceuticals as well as pathogenic microorganisms. Additionally, the utilization of some of these substrates such as sewage sludge or animal by-products is legally limited in agriculture because of the potential risk to contaminate sites with potentially toxic elements and organic contaminants. Thus, to close nutrient cycles it is important to develop solutions for the responsible use of organic nutrient sources. The aim of this review is to give an overview of the contamination of the most important organic nutrient sources with potentially toxic elements, antibiotics (as one important organic contaminant) and pathogenic microorganisms. Changes in manure and sewage sludge management as well as the increasing trend to use such substrates in biogas plants will be discussed with respect to potential risks posed to soils and water bodies. Some examples for abatement options by which contamination can be reduced to produce P fertilizers with high amounts of plant available P forms are presented.
Subject(s)
Anti-Bacterial Agents/analysis , Fertilizers/analysis , Fertilizers/microbiology , Phosphorus , Soil Pollutants/analysis , Agriculture , Animals , Manure/microbiology , Sewage/microbiology , Soil , Soil MicrobiologyABSTRACT
AIM: To investigate the inactivation of Salmonella enterica serovar Typhimurium and the faecal indicator Enterococcus faecalis in horse manure:soil mixtures by application of hydrated lime (Ca(OH)(2)). METHODS AND RESULTS: In laboratory incubations, the inhibitory effect of different concentrations of Ca(OH)(2), as well as different application techniques, was tested. Other variables were horse manure:soil ratio, incubation temperature (6 and 14°C) and soil type (sand/clay). Bacterial enumeration by the plate count method in samples taken at increasing intervals revealed that Ca(OH)(2) effectively reduced Salmonella Typhimurium numbers. However, to achieve a sufficient reduction, the Ca(OH)(2) had to be applied at a sufficient rate, and the amount required varied because of manure:soil ratio and incubation temperature. The results showed that a pH above 11 was needed and that a high pH had to be maintained for up to 7 days. An appropriate application technique for the Ca(OH)(2) was also important, so that a high pH was obtained throughout the whole material to be treated. In addition, a high manure:soil ratio in combination with a higher incubation temperature was found to rapidly neutralize the pH and to increase the risk of Salmonella re-growth. CONCLUSIONS: Application of Ca(OH)(2) can be an efficient method for treating a Salmonella-contaminated horse paddock. A high pH is a key factor in Salmonella inactivation, and thus, monitoring the pH during the treatment period is necessary. To avoid re-growth excess manure should be removed for separate treatment elsewhere. SIGNIFICANCE AND IMPACT OF THE STUDY: Persistence of Salmonella in horse paddocks poses a risk of disease transmission to healthy animals and people who come into contact with these animals. An efficient method to de-contaminate a Salmonella-contaminated soil would be a valuable tool for animal welfare and for public health.