Gámez Victor M, Sierra-Alvarez Reyes, Waltz Rebecca J, Field James A
Department of Chemical and Environmental Engineering, University of Arizona, Tucson, AZ 85721, USA.
Biodegradation. 2009 Jul;20(4):499-510. doi: 10.1007/s10532-008-9239-6. Epub 2008 Dec 17.
Citrate is an important component of metal processing effluents such as chemical mechanical planarization wastewaters of the semiconductor industry. Citrate can serve as an electron donor for sulfate reduction applied to promote the removal of metals, and it can also potentially be used by methanogens that coexist in anaerobic biofilms. The objective of this study was to evaluate the degradation of citrate with sulfate-reducing and methanogenic biofilms. During batch bioassays, the citrate, acetate, methane and sulfide concentrations were monitored. The results indicate that independent of the biofilm or incubation conditions used, citrate was rapidly fermented with specific rates ranging from 566 to 720 mg chemical oxygen demand (COD) consumed per gram volatile suspended solids per day. Acetate was found to be the main fermentation product of citrate degradation, which was later degraded completely under either methanogenic or sulfate reducing conditions. However, if either sulfate reduction or methanogenesis was infeasible due to specific inhibitors (2-bromoethane sulfonate), absence of sulfate or lack of adequate microorganisms in the biofilm, acetate accumulated to levels accounting for 90-100% of the citrate-COD consumed. Based on carbon balances measured in phosphate buffered bioassays, acetate, CO(2) and hydrogen are the main products of citrate fermentation, with a molar ratio of 2:2:1 per mol of citrate, respectively. In bicarbonate buffered bioassays, acetogenesis of H(2) and CO(2) increased the yield of acetate. The results taken as a whole suggest that in anaerobic biofilm systems, citrate is metabolized via the formation of acetate as the main metabolic intermediate prior to methanogenesis or sulfate reduction. Sulfate reducing consortia must be enriched to utilize acetate as an electron donor in order to utilize the majority of the electron-equivalents in citrate.
柠檬酸盐是金属加工废水(如半导体行业化学机械平面化废水)的重要组成部分。柠檬酸盐可作为硫酸盐还原的电子供体,用于促进金属去除,并且厌氧生物膜中共存的产甲烷菌也可能利用它。本研究的目的是评估柠檬酸盐在硫酸盐还原生物膜和产甲烷生物膜中的降解情况。在批次生物测定过程中,监测了柠檬酸盐、乙酸盐、甲烷和硫化物的浓度。结果表明,无论使用何种生物膜或培养条件,柠檬酸盐都会迅速发酵,特定速率为每天每克挥发性悬浮固体消耗566至720毫克化学需氧量(COD)。乙酸盐被发现是柠檬酸盐降解的主要发酵产物,随后在产甲烷或硫酸盐还原条件下被完全降解。然而,如果由于特定抑制剂(2-溴乙烷磺酸盐)、缺乏硫酸盐或生物膜中缺乏足够的微生物而导致硫酸盐还原或产甲烷不可行,乙酸盐会积累到占消耗的柠檬酸盐-COD的90-100%的水平。根据磷酸盐缓冲生物测定中测得的碳平衡,乙酸盐、CO₂和氢气是柠檬酸盐发酵的主要产物,每摩尔柠檬酸盐的摩尔比分别为2:2:1。在碳酸氢盐缓冲生物测定中,H₂和CO₂的产乙酸作用增加了乙酸盐的产量。总体结果表明,在厌氧生物膜系统中,柠檬酸盐在产甲烷或硫酸盐还原之前通过形成乙酸盐作为主要代谢中间体进行代谢。必须富集硫酸盐还原菌群以利用乙酸盐作为电子供体,以便利用柠檬酸盐中的大部分电子当量。