TY - JOUR
T1 - Heterotrophic nitrification-aerobic denitrification potential of cyanide and thiocyanate degrading microbial communities under cyanogenic conditions
AU - Mekuto, Lukhanyo
AU - Kim, Young Mo
AU - Ntwampe, Seteno K.O.
AU - Mewa-Ngongang, Maxwell
AU - Mudumbi, John Baptist N.
AU - Dlangamandla, Nkosikho
AU - Itoba-Tombo, Elie Fereche
AU - Akinpelu, E. A.
N1 - Publisher Copyright:
© 2019 Korean Society of Environmental Engineers.
PY - 2019
Y1 - 2019
N2 - The impact of free cyanide (CN-) and thiocyanate (SCN-) on the CN- (CDO) and SCN- degraders (TDO) to nitrify and denitrify aerobically was evaluated under alkaline conditions. The CDO’s were able to nitrify under cyanogenic conditions, achieving NH4 +-N removal rates above 1.66 mg NH4 +-N.L-1.h-1, except when CN- and SCN- loading was 15 mg CN-/L and 50 mg SCN-.L-1, respectively, which slightly inhibited nitrification. The TDO’s were able to achieve a nitrification rate of 1.59 mg NH4 +-N.L-1.h-1 in the absence of both CN- and SCN-, while the presence of CN- and SCN- was inhibitory, with a nitrification rates of 1.14 mg NH4 +-N.L-1.h-1. The CDO’s and TDO’s were able to denitrify aerobically, with the CDO’s obtaining NO3 --N removal rates above 0.67 mg NO3 --N.L-1.h-1, irrespective of the tested CN- and SCN- concentration range. Denitrification by the TDO’s was inhibited by CN-, achieving a removal rate of 0.46 mg NO3 --N.L-1.h-1 and 0.22 mg NO3 --N.L-1.h-1 when CN-concentration was 10 and 15 mg CN-.L-1, respectively. However, when the CDO’s and TDO’s were co-cultured, the nitrification and aerobic denitrification removal rates were 1.78 mg NH4 +-N.L-1.h-1 and 0.63 mg NO3 --N.L-1.h-1 irrespective of CN- and SCN- concentrations.
AB - The impact of free cyanide (CN-) and thiocyanate (SCN-) on the CN- (CDO) and SCN- degraders (TDO) to nitrify and denitrify aerobically was evaluated under alkaline conditions. The CDO’s were able to nitrify under cyanogenic conditions, achieving NH4 +-N removal rates above 1.66 mg NH4 +-N.L-1.h-1, except when CN- and SCN- loading was 15 mg CN-/L and 50 mg SCN-.L-1, respectively, which slightly inhibited nitrification. The TDO’s were able to achieve a nitrification rate of 1.59 mg NH4 +-N.L-1.h-1 in the absence of both CN- and SCN-, while the presence of CN- and SCN- was inhibitory, with a nitrification rates of 1.14 mg NH4 +-N.L-1.h-1. The CDO’s and TDO’s were able to denitrify aerobically, with the CDO’s obtaining NO3 --N removal rates above 0.67 mg NO3 --N.L-1.h-1, irrespective of the tested CN- and SCN- concentration range. Denitrification by the TDO’s was inhibited by CN-, achieving a removal rate of 0.46 mg NO3 --N.L-1.h-1 and 0.22 mg NO3 --N.L-1.h-1 when CN-concentration was 10 and 15 mg CN-.L-1, respectively. However, when the CDO’s and TDO’s were co-cultured, the nitrification and aerobic denitrification removal rates were 1.78 mg NH4 +-N.L-1.h-1 and 0.63 mg NO3 --N.L-1.h-1 irrespective of CN- and SCN- concentrations.
KW - Aerobic denitrification
KW - Cyanide degraders
KW - Free cyanide
KW - Nitrification
KW - Thiocyanate
KW - Thiocyanate degrader
UR - http://www.scopus.com/inward/record.url?scp=85067597396&partnerID=8YFLogxK
U2 - 10.4491/EER.2018.147
DO - 10.4491/EER.2018.147
M3 - Article
AN - SCOPUS:85067597396
SN - 1226-1025
VL - 24
SP - 254
EP - 262
JO - Environmental Engineering Research
JF - Environmental Engineering Research
IS - 2
ER -