Tas Didem Okutman, Pavlostathis Spyros G
School of Civil and Environmental Engineering, Georgia Institute of Technology, Atlanta, Georgia 30332-0512, USA.
Environ Sci Technol. 2005 Nov 1;39(21):8264-72. doi: 10.1021/es050407+.
The reductive transformation of pentachloronitrobenzene (PCNB), an organochlorine fungicide, was investigated with a mixed, methanogenic culture developed from a contaminated estuarine sediment. Batch assays performed with this enrichment culture resulted in the biotransformation of PCNB to pentachloroaniline (PCA), which was then sequentially dechlorinated as follows: PCA --> 2,3,4,5- and 2,3,5,6-tetrachloroaniline (TeCA) --> 2,4,5- and 2,3,5-trichloroaniline (TrCA) --> 2,4-, 2,5-, and 3,5-dichloroaniline (DCA) --> 3- and 4-chloroaniline (CA) (low levels). Glucose fermentation, methanogenesis, and dechlorination were not inhibited at an initial PCNB concentration up to 40 microM, which is 27 times higher than its aqueous solubility. The addition of 25 mM 2-bromoethanesulfonate (BES) to the PCNB-amended culture resulted in the complete inhibition of methanogenesis, but the biotransformation of PCNB to PCA and its sequential dechlorination pathway were not affected. The addition of sodium azide (200 mg/L) to the PCNB-amended culture resulted in complete inhibition of methanogenesis, but did not inhibit the transformation of PCNB to PCA; however, PCA dechlorination was not observed. PCNB was also abiotically transformed to PCA in autoclaved culture media but at much lower rates as compared to the biotic assays. In contrast, the rate of PCNB to PCA transformation in autoclaved culture controls was similar to the rates observed in the azide-amended culture and the active enrichment culture, indicating that biotically derived reductants facilitated the observed transformation of PCNB to PCA. Dechlorination of PCA was not observed in any of the abiotic controls. These findings have significant environmental implications in terms of the fate and transport of PCNB, PCA, and its dechlorination products in subsurface systems.
利用从受污染河口沉积物中培养出的混合产甲烷菌培养物,研究了有机氯杀菌剂五氯硝基苯(PCNB)的还原转化过程。用这种富集培养物进行的批次试验导致PCNB生物转化为五氯苯胺(PCA),然后依次进行脱氯,过程如下:PCA→2,3,4,5-和2,3,5,6-四氯苯胺(TeCA)→2,4,5-和2,3,5-三氯苯胺(TrCA)→2,4-、2,5-和3,5-二氯苯胺(DCA)→3-和4-氯苯胺(CA)(低水平)。在初始PCNB浓度高达40微摩尔时,葡萄糖发酵、产甲烷作用和脱氯作用均未受到抑制,该浓度比其水溶性高27倍。向添加了PCNB的培养物中加入25毫摩尔的2-溴乙烷磺酸盐(BES),导致产甲烷作用完全受到抑制,但PCNB向PCA的生物转化及其依次脱氯途径未受影响。向添加了PCNB的培养物中加入叠氮化钠(200毫克/升),导致产甲烷作用完全受到抑制,但未抑制PCNB向PCA的转化;然而,未观察到PCA脱氯。在高压灭菌的培养基中,PCNB也会非生物转化为PCA,但与生物试验相比,速率要低得多。相比之下,高压灭菌培养对照中PCNB向PCA的转化速率与在添加叠氮化钠的培养物和活性富集培养物中观察到的速率相似,这表明生物来源的还原剂促进了观察到的PCNB向PCA的转化。在任何非生物对照中均未观察到PCA脱氯。这些发现对于PCNB、PCA及其脱氯产物在地下系统中的归宿和迁移具有重要的环境意义。