Park C, Marchand E A
Department of Civil and Environmental Engineering, University of Nevada at Reno, Reno, NV 89557-0152, USA.
J Appl Microbiol. 2006 Jul;101(1):222-33. doi: 10.1111/j.1365-2672.2006.02950.x.
To determine the mathematical kinetic rates and mechanisms of acclimated perchlorate (ClO)-reducing microbial cultures by incorporating a term to relate the inhibitory effect of high salinity during biological reduction of concentrated perchlorate solutions.
Salt toxicity associated with the biodegradation of concentrated perchlorate (200, 500, 1100, 1700 and 2400 mg l(-1) as ClO) was investigated using two microbial cultures isolated from a domestic wastewater treatment plant [return activated sludge (RAS) and anaerobic digester sludge (ADS)]. Experiments were performed in wastewaters containing various sodium chloride concentrations, ranging from 0% to 4.0% (w/v) NaCl (ionic strength: 0.14-0.82 mol l(-1), total dissolved solids: 5.3-42.6 g l(-1)) at near-neutral values of pH (6.7-7.8). Perchlorate biodegradation was stimulated through stepwise acclimation to high salinity. The ADS culture was capable of reducing perchlorate at salinities up to 4% NaCl, while the RAS culture exhibited complete inhibition of perchlorate degradation at 4% NaCl, probably resulting from either a toxic effect or enzyme inactivation of the perchlorate-reducing microbes. Further, a kinetic growth model was developed based on experimental data in order to express an inhibition function to relate specific growth rate and salinity.
Biological reduction of concentrated perchlorate wastewaters using either acclimated RAS or ADS cultures is feasible up to 3% or 4% NaCl, respectively. In addition, the kinetic model including a salinity inhibition term should be effective in many practical applications such as improving reactor design and management, furthering the understanding of high salinity inhibition, and enhancing bioremediation under high salinity loading conditions.
Applications of these findings in water treatment practice where ion exchange or membrane technologies are used to remove perchlorate from water can have the potential to increase the overall attractiveness of these processes by eliminating the need to dispose of a concentrated perchlorate solution.
通过纳入一个与高盐度在高浓度高氯酸盐溶液生物还原过程中的抑制作用相关的项,来确定适应高氯酸盐(ClO)还原的微生物培养物的数学动力学速率和机制。
使用从生活污水处理厂分离得到的两种微生物培养物[回流活性污泥(RAS)和厌氧消化污泥(ADS)],研究了与高浓度高氯酸盐(200、500、1100、1700和2400 mg l⁻¹ 以ClO计)生物降解相关的盐毒性。实验在含有不同氯化钠浓度的废水中进行,氯化钠浓度范围为0%至4.0%(w/v)NaCl(离子强度:0.14 - 0.82 mol l⁻¹,总溶解固体:5.3 - 42.6 g l⁻¹),pH接近中性(6.7 - 7.8)。通过逐步适应高盐度来刺激高氯酸盐的生物降解。ADS培养物能够在高达4% NaCl的盐度下还原高氯酸盐,而RAS培养物在4% NaCl时表现出高氯酸盐降解的完全抑制,这可能是由于高氯酸盐还原微生物的毒性作用或酶失活。此外,基于实验数据建立了动力学生长模型,以表达一个抑制函数来关联比生长速率和盐度。
分别使用适应的RAS或ADS培养物对高浓度高氯酸盐废水进行生物还原,在高达3%或4% NaCl时是可行的。此外,包含盐度抑制项的动力学模型在许多实际应用中应是有效的,如改进反应器设计和管理、加深对高盐度抑制的理解以及在高盐度负荷条件下增强生物修复。
这些发现在水处理实践中的应用,即在使用离子交换或膜技术从水中去除高氯酸盐的过程中,有可能通过消除处理浓缩高氯酸盐溶液的需求来提高这些工艺的整体吸引力。