Panthi Sudan Raj, Wareham David Geraint
Department of Civil and Natural Resources Engineering, University of Canterbury, Christchurch, New Zealand.
J Environ Sci Health A Tox Hazard Subst Environ Eng. 2008 Aug;43(10):1192-7. doi: 10.1080/10934520802171758.
A lab-scale sequencing batch reactor (SBR) was operated at a solids retention time (SRT) of 20 +/- 2.5 days to develop a consortium of denitrifying bacteria with a mean specific denitrification rate of 0.11 g nitrate (NO(3)(-)-N)/g volatile suspended solids (VSS)/day. This biomass was used in a series of denitrification batch tests which used volatile fatty acids (VFAs) as their external carbon source. The VFAs were generated from an anaerobic digester that had an effluent VFA concentration of 5655 +/- 876 mg/L (expressed as acetic acid (HAc)). The denitrification batch reactors were spiked with NO(3)(-)-N (carbon-to-nitrogen (C:N) ratio of 3.0) and different concentrations of arsenite (a trivalent arsenic salt) in order to quantify the effect of arsenite on the denitrification process. A steady deterioration in the ability of the biomass to denitrify under increasing arsenite concentrations was observed with the mean specific denitrification rate dropping from 0.183 g NO(3)(-)-N/gVSS/day at an arsenite concentration of 5 mg/L, to a value of 0.047 g NO(3)(-)-N/gVSS/day at a concentration of 25 mg/L.
一个实验室规模的序批式反应器(SBR)在固体停留时间(SRT)为20±2.5天的条件下运行,以培养一个反硝化细菌群落,其平均比反硝化速率为0.11克硝酸盐(NO₃⁻-N)/克挥发性悬浮固体(VSS)/天。该生物量用于一系列以挥发性脂肪酸(VFAs)为外部碳源的反硝化批次试验。VFAs由一个厌氧消化器产生,其出水VFAs浓度为5655±876毫克/升(以乙酸(HAc)表示)。反硝化批次反应器加入了NO₃⁻-N(碳氮比(C:N)为3.0)和不同浓度的亚砷酸盐(一种三价砷盐),以量化亚砷酸盐对反硝化过程的影响。随着亚砷酸盐浓度增加,观察到生物量反硝化能力持续恶化,平均比反硝化速率从亚砷酸盐浓度为5毫克/升时的0.183克NO₃⁻-N/克VSS/天降至浓度为25毫克/升时的0.047克NO₃⁻-N/克VSS/天。