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Comparison of five organic wastes regarding their behaviour during composting: Part 2, nitrogen dynamic
Authors:A de Guardia  P Mallard  C Teglia  A Marin  C Le Pape  M Launay  JC Benoist  C Petiot
Institution:1. Lodz University of Technology, Institute of Fermentation Technology and Microbiology, Wólczańska 171/173, 90-924 ?ód?, Poland;2. Lodz University of Technology, Faculty of Process and Environmental Engineering, Wólczańska 213, 90-924 ?ód?, Poland;1. Swedish University of Agricultural Sciences (SLU), Department of Energy and Technology, Box 7032, SE-750 07, Uppsala, Sweden;2. KTH Royal Institute of Technology, Department of Sustainable Development, Environmental Science and Engineering (SEED), School of Architecture and the Built Environment (ABE), Kungliga Tekniska Högskolan, SE-100 44, Stockholm, Sweden;3. Swedish University of Agricultural Sciences (SLU), Department of Molecular Sciences, Box 7015, SE-750 07, Uppsala, Sweden;1. NEPERS, Centro de Engenharias, Universidade Federal de Pelotas, Pelotas, RS, Brazil;2. ReproPel, Faculdade de Veterinária, Universidade Federal de Pelotas, Pelotas, RS, Brazil;3. Instituto Federal de Educação, Ciência e Tecnologia Sul-Rio-Grandense, Pelotas, RS, Brazil;4. Instituto de Ciências Biológicas, Universidade Federal do Rio Grande, Rio Grande, RS, Brazil;1. State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environment Sciences, Beijing 100012, China;2. College of Resources and Environment, University of Chinese Academy of Sciences, Beijing 100049, China;3. State Key Laboratory of Atmospheric Boundary Layer Physics and Atmospheric Chemistry, Institute of Atmospheric Physics, Chinese Academy of Sciences, Beijing 100029, China;4. Institute of Plant Quarantine, Chinese Academy of Inspection and Quarantine, Beijing 100029, China;5. Department of Forest Ecology and Management, Swedish University of Agricultural Sciences, S 90183 Umeå, Sweden
Abstract:This paper aimed to compare household waste, separated pig solids, food waste, pig slaughterhouse sludge and green algae regarding processes ruling nitrogen dynamic during composting. For each waste, three composting simulations were performed in parallel in three similar reactors (300 L), each one under a constant aeration rate. The aeration flows applied were comprised between 100 and 1100 L/h. The initial waste and the compost were characterized through the measurements of their contents in dry matter, total carbon, Kjeldahl and total ammoniacal nitrogen, nitrite and nitrate. Kjeldahl and total ammoniacal nitrogen and nitrite and nitrate were measured in leachates and in condensates too. Ammonia and nitrous oxide emissions were monitored in continue. The cumulated emissions in ammonia and in nitrous oxide were given for each waste and at each aeration rate. The paper focused on process of ammonification and on transformations and transfer of total ammoniacal nitrogen. The parameters of nitrous oxide emissions were not investigated. The removal rate of total Kjeldahl nitrogen was shown being closely tied to the ammonification rate. Ammonification was modelled thanks to the calculation of the ratio of biodegradable carbon to organic nitrogen content of the biodegradable fraction. The wastes were shown to differ significantly regarding their ammonification ability. Nitrogen balances were calculated by subtracting nitrogen losses from nitrogen removed from material. Defaults in nitrogen balances were assumed to correspond to conversion of nitrate even nitrite into molecular nitrogen and then to the previous conversion by nitrification of total ammoniacal nitrogen. The pool of total ammoniacal nitrogen, i.e. total ammoniacal nitrogen initially contained in waste plus total ammoniacal nitrogen released by ammonification, was calculated for each experiment. Then, this pool was used as the referring amount in the calculation of the rates of accumulation, stripping and nitrification of total ammoniacal nitrogen. Separated pig solids were characterised by a high ability to accumulate total ammoniacal nitrogen. Whatever the waste, the striping rate depended mostly on the aeration rate and on the pool concentration in biofilm. The nitrification rate was observed as all the higher as the concentration in total ammoniacal nitrogen in the initial waste was low. Thus, household waste and green algae exhibited the highest nitrification rates. This result could mean that in case of low concentrations in total ammoniacal nitrogen, a nitrifying biomass was already developed and that this biomass consumed it. In contrast, in case of high concentrations, this could traduce some difficulties for nitrifying microorganisms to develop.
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