Ammonia and greenhouse gas emissions from slurry storage - A review
•Slurry storage emission data were assembled from 120 papers into a data base.•The variability in emissions from untreated slurry stored uncovered is large.•Baseline emissions are determined for NH3, N2O, CH4 and CO2.•All cover types substantially reduce NH3 emissions from slurry storage.•Emission m...
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Veröffentlicht in: | Agriculture, ecosystems & environment ecosystems & environment, 2020-09, Vol.300, p.106963, Article 106963 |
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Zusammenfassung: | •Slurry storage emission data were assembled from 120 papers into a data base.•The variability in emissions from untreated slurry stored uncovered is large.•Baseline emissions are determined for NH3, N2O, CH4 and CO2.•All cover types substantially reduce NH3 emissions from slurry storage.•Emission mitigation due to store covers varies for greenhouse gases.
Storage of slurry is an important emission source for ammonia (NH3), nitrous oxide (N2O), methane (CH4), carbon dioxide (CO2) and hydrogen sulfide (H2S) from livestock production. Therefore, this study collected published emission data from stored cattle and pig slurry to determine baseline emission values and emission changes due to slurry treatment and coverage of stores. Emission data were collected from 120 papers yielding 711 records of measurements conducted at farm-, pilot- and laboratory-scale. The emission data reported in a multitude of units were standardized and compiled in a database. Descriptive statistics of the data from untreated slurry stored uncovered revealed a large variability in emissions for all gases. To determine baseline emissions, average values based on a weighting of the emission data according to the season and the duration of the emission measurements were constructed using the data from farm-scale and pilot-scale studies. Baseline emissions for cattle and pig slurry stored uncovered were calculated. When possible, it was further distinguished between storage in tanks without slurry treatment and storage in lagoons which implies solid-liquid separation and biological treatment. The baseline emissions on an area or volume basis are: for NH3: 0.12 g m−2 h-1 and 0.15 g m−2 h-1 for cattle and pig slurry stored in lagoons, and 0.08 g m−2 h-1 and 0.24 g m−2 h-1 for cattle and pig slurry stored in tanks; for N2O: 0.0003 g m−2 h-1 for cattle slurry stored in lagoons, and 0.002 g m−2 h-1 for both slurry types stored in tanks; for CH4: 0.95 g m-3 h-1 and 3.5 g m-3 h-1 for cattle and pig slurry stored in lagoons, and 0.58 g m-3 h-1 and 0.68 g m-3 h-1 for cattle and pig slurry stored in tanks; for CO2: 6.6 g m−2 h-1 and 0.3 g m−2 h-1 for cattle and pig slurry stored in lagoons, and 8.0 g m−2 h-1 for both slurry types stored in tanks; for H2S: 0.04 g m−2 h-1 and 0.01 g m−2 h-1 for cattle and pig slurry stored in lagoons. Related to total ammoniacal nitrogen (TAN), baseline emissions for tanks are 16% and 15% of TAN for cattle and pig slurry, respectively. Emissions of N2O and CH4 relat |
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ISSN: | 0167-8809 1873-2305 |
DOI: | 10.1016/j.agee.2020.106963 |