Effects of Anaerobic Digestion and Solids Separation on Ammonia Emissions from Stored and Land Applied Dairy Manure

• Published in: Water, air, and soil pollution air, and soil pollution, 2015-09, Vol.226 (9), p.153, Article 301
• Main Authors: Neerackal, G. M., Ndegwa, P. M., Joo, H. S., Wang, X., Harrison, J. H., Heber, A. J., Ni, J.-Q., Frear, C.
• Format: Article
• Language: English
• Subjects: Advertising executives; Air pollution control; Alternative energy sources; Ammonia; Anaerobic digestion; Atmospheric Protection/Air Quality Control/Air Pollution; Biodegradation; Biogas; Carbon dioxide; Chemical properties; Climate Change/Climate Change Impacts; Dairy products industry; Earth and Environmental Science; Effluents; Emissions; Environment; Environmental monitoring; Fatty acids; Fertilizers; Hydrogeology; Laboratories; Manures; Nitrogen; Odors; Separation processes; Soil Science & Conservation; Solids; VOCs; Volatile organic compounds; Water Quality/Water Pollution
• ISSN: 0049-6979; 1573-2932
• DOI: 10.1007/s11270-015-2561-9

Field and laboratory studies were conducted to evaluate the effects of anaerobic digestion (AD) and solids-liquid separation on emissions during subsequent storage and land application. The lab storage tests were conducted for 21 days with manure samples obtained at the following four points in a full-scale AD system: raw manure (RM) delivery, raw manure supplemented with other substrates (AD influent), AD effluent, and AD effluent after solids-liquid separation (AD liquid effluent). Ammonia fluxes from stored AD effluent declined from 3.95 to 2.02 g m −2  day −1 . Lower NH 3 fluxes, however, were observed from AD liquid effluent (1.1 g m −2  day −1 ) and AD influent (0.25 g m −2  day −1 ). Ammonia emissions from full-scale manure storages were similar to those obtained in the lab. Results also indicated significantly lower volatile fatty acid (VFA) in AD effluent and AD liquid effluent compared with that from the AD influent, indicating significant reduction in odor generation potential due to AD and solids-liquid separation processes. Two manure application methods (surface application and manure injection) for both non-AD and AD manures were simulated in the lab and studied for 9 days. Surface-applied non-AD manure exhibited the highest NH 3 flux (0.78 g m −2  day −1 ), while injected AD manure led to the lowest NH 3 flux (0.17 g m −2  day −1 ). Similar NH 3 emissions results were observed from the field studies. Overall, while AD of dairy manure resulted in significant increases in NH 3 emissions from stored effluent, the AD process significantly reduced NH 3 emissions following application of AD manure on land.