Thermal drying of the solid fraction from biogas digestate: Effects of acidification, temperature and ventilation on nitrogen content.

Drying of solids produced from digestate is prone to N losses through NH3 volatilisation. The applicability of acidification as an NH3 emission mitigation technique during the drying of solids from digestate was assessed in a drying experiment. Operating conditions comprised four drying temperatures (70-160°C), two air ventilation rates (natural, 420ml/min) and three pH levels (9.2, 6.5 and 5.5) of the solids, modified by the addition of concentrated sulphuric acid. Acidification of the solids from digestate significantly decreased the NH3 emission during drying, irrespective of the drying conditions. A parallel decrease in the organic nitrogen content and an increase in the ammonium content of the solids was observed after acidification of the solids. It was confirmed that acidification before thermal concentration of solids from digestate, minimised NH3 losses under a wide range of drying conditions.

[1]  Herbert H. P. Fang,et al.  Influences of Extracellular Polymeric Substances (EPS) on Flocculation, Settling, and Dewatering of Activated Sludge , 2003 .

[2]  Panyue Zhang,et al.  Degradation properties of protein and carbohydrate during sludge anaerobic digestion. , 2015, Bioresource technology.

[3]  K. Cen,et al.  Moisture distribution in sludges based on different testing methods. , 2011, Journal of environmental sciences.

[4]  Didier Lecomte,et al.  Efficient sludge thermal processing: from drying to thermal valorisation , 2012 .

[5]  P. Mcmurry,et al.  H2SO4 vapor pressure of sulfuric acid and ammonium sulfate solutions , 1997 .

[6]  Søren Husted,et al.  Reducing ammonia loss from cattle slurry by the use of acidifying additives: The role of the buffer system , 1991 .

[7]  J. Coutinho,et al.  Treatment by acidification followed by solid-liquid separation affects slurry and slurry fractions composition and their potential of N mineralization. , 2009, Bioresource technology.

[8]  G. Gu,et al.  Effect of acid and surfactant treatment on activated sludge dewatering and settling. , 2001, Water research.

[9]  Jean-François Cabaraux,et al.  Ammonia emissions from pig houses: Influencing factors and mitigation techniques , 2011 .

[10]  Marc Pansu,et al.  Handbook of Soil Analysis: Mineralogical, Organic and Inorganic Methods , 2006 .

[11]  Lars Stoumann Jensen,et al.  Chemical and biochemical variation in animal manure solids separated using different commercial separation technologies. , 2009, Bioresource technology.

[12]  O. Oenema,et al.  Ammonia volatilization from dairy farming systems in temperate areas: a review , 1998, Nutrient Cycling in Agroecosystems.

[13]  C. Rotz Management to reduce nitrogen losses in animal production. , 2004, Journal of animal science.

[14]  D. Fangueiro,et al.  Acidification of animal slurry--a review. , 2015, Journal of environmental management.

[16]  F. da Borso,et al.  Changes during processing in the organic matter of composted and air-dried poultry manure , 1996 .

[17]  J. Webb,et al.  Algorithms determining ammonia emission from buildings housing cattle and pigs and from manure stores , 2006 .

[18]  Claudia Maurer,et al.  Ammonia (NH3) emissions during drying of untreated and dewatered biogas digestate in a hybrid waste‐heat/solar dryer , 2012 .

[19]  J. Civit,et al.  Manure processing technologies , 2012 .

[20]  J. Eriksen,et al.  Effects of slurry acidification with sulphuric acid combined with aeration on the turnover and plant availability of nitrogen , 2009 .

[21]  A. Ghaly,et al.  DRYING POULTRY MANURE FOR POLLUTION POTENTIAL REDUCTION AND PRODUCTION OF ORGANIC FERTILIZER , 2013 .

[22]  J. Coutinho,et al.  Impact of cattle slurry acidification on carbon and nitrogen dynamics during storage and after soil incorporation , 2013 .

[23]  Romana Marinšek-Logar,et al.  Effect of pH, temperature and air flow rate on the continuous ammonia stripping of the anaerobic digestion effluent , 2011 .

[24]  K. H. Laursen,et al.  Multielement plant tissue analysis using ICP spectrometry. , 2013, Methods in molecular biology.

[25]  P. Hobbs,et al.  Additives to reduce ammonia and odor emissions from livestock wastes: a review. , 2001, Journal of environmental quality.

[26]  A. Mujumdar Handbook of Industrial Drying , 2020 .

[27]  J. P. Frost,et al.  Effect of acidification with sulphuric acid on the volatilization of ammonia from cow and pig slurries , 1989, The Journal of Agricultural Science.

[28]  N. Bolan,et al.  Losses and transformation of nitrogen during composting of poultry manure with different amendments: An incubation experiment , 1994 .

[29]  D. Massé,et al.  The effect of pH on the separation of manure nutrients with reverse osmosis membranes , 2008 .

[30]  J. Webb,et al.  Emissions of Ammonia, Nitrous Oxide and Methane During the Management of Solid Manures , 2012 .

[31]  R. Peck,et al.  Generalized drying curves for porous solids , 1975 .

[32]  C. Alan Rotz,et al.  The role of carbon dioxide in emission of ammonia from manure , 2013 .

[33]  P. Derikx,et al.  Effect of pH on the behaviour of volatile compounds in organic manures during dry-matter determination , 1994 .

[34]  P. Aarne Vesilind,et al.  Effect of Drying Temperature On the Fuel Value of Wastewater Sludge , 1996 .

[35]  A. Bonmatí,et al.  Pig Slurry Concentration by Vacuum Evaporation: Influence of Previous Mesophilic Anaerobic Digestion Process , 2003, Journal of the Air & Waste Management Association.