Temperature-induced changes in treatment efficiency and microbial structure of aerobic granules treating landfill leachate.
This paper investigates the effect of temperature on nitrogen and carbon removal by aerobic granules from landfill leachate with a high ammonium concentration and low concentration of biodegradable organics. The study was conducted in three stages; firstly the operating temperature of the batch reactor with aerobic granules was maintained at 29 °C, then at 25 °C, and finally at 20 °C. It was found that a gradual decrease in operational temperature allowed the nitrogen-converting community in the granules to acclimate, ensuring efficient nitrification even at ambient temperature (20 °C). Ammonium was fully removed from leachate regardless of the temperature, but higher operational temperatures resulted in higher ammonium removal rates [up to 44.2 mg/(L h) at 29 °C]. Lowering the operational temperature from 29 to 20 °C decreased nitrite accumulation in the GSBR cycle. The highest efficiency of total nitrogen removal was achieved at 25 °C (36.8 ± 10.9 %). The COD removal efficiency did not exceed 50 %. Granules constituted 77, 80 and 83 % of the biomass at 29, 25 and 20 °C, respectively. Ammonium was oxidized by both aerobic and anaerobic ammonium-oxidizing bacteria. Accumulibacter sp., Thauera sp., cultured Tetrasphaera PAO and Azoarcus-Thauera cluster occurred in granules independent of the temperature. Lower temperatures favored the occurrence of denitrifiers of Zooglea lineage (not Z. resiniphila), bacteria related to Comamonadaceae, Curvibacter sp., Azoarcus cluster, Rhodobacter sp., Roseobacter sp. and Acidovorax spp. At lower temperatures, the increased abundance of denitrifiers compensated for the lowered enzymatic activity of the biomass and ensured that nitrogen removal at 20 °C was similar to that at 25 °C and significantly higher than removal at 29 °C.
Department of Environmental Biotechnology, University of Warmia and Mazury in Olsztyn, Słoneczna 45 G, 10-709, Olsztyn, Poland.
Dorian
D
Mieczkowski
Department of Environmental Biotechnology, University of Warmia and Mazury in Olsztyn, Słoneczna 45 G, 10-709, Olsztyn, Poland. agnieszka.cydzik@uwm.edu.pl.
Agnieszka
A
Cydzik-Kwiatkowska
Department of Environmental Biotechnology, University of Warmia and Mazury in Olsztyn, Słoneczna 45 G, 10-709, Olsztyn, Poland.
Paulina
P
Rusanowska
Department of Environmental Biotechnology, University of Warmia and Mazury in Olsztyn, Słoneczna 45 G, 10-709, Olsztyn, Poland.
Piotr
P
Świątczak
D000332:Aerobiosis; D064751:Ammonium Compounds / Q000378:metabolism; D001420:Bacteria, Aerobic / Q000254:growth & development / Q000378:metabolism / Q000502:physiology*; D001673:Biodegradation, Environmental; D018533:Biomass; D002244:Carbon / Q000378:metabolism; D004789:Enzyme Activation; D017404:In Situ Hybridization, Fluorescence / Q000379:methods; D058465:Nitrification; D009573:Nitrites / Q000378:metabolism; D009584:Nitrogen / Q000378:metabolism; D012722:Sewage / Q000737:chemistry / Q000382:microbiology; D013696:Temperature; D062065:Wastewater / Q000382:microbiology; D014874:Water Pollutants, Chemical / Q000378:metabolism*
D064751:Ammonium Compounds; D002244:Carbon; D009573:Nitrites; D009584:Nitrogen; D012722:Sewage; D062065:Wastewater; D014874:Water Pollutants, Chemical
Aerobic granules; Denitrifiers; FISH; Landfill leachate; Temperature