Zipper C, Bunk M, Zehnder A J, Kohler H P
Swiss Federal Institute for Environmental Science and Technology, Zürich, Switzerland.
J Bacteriol. 1998 Jul;180(13):3368-74. doi: 10.1128/JB.180.13.3368-3374.1998.
Sphingomonas herbicidovorans MH was able to completely degrade both enantiomers of the chiral herbicide dichlorprop [(RS)-2-(2,4-dichlorophenoxy)propanoic acid], with preferential degradation of the (S) enantiomer over the (R) enantiomer. These results are in agreement with the recently reported enantioselective degradation of mecoprop [(RS)-2-(4-chloro-2-methylphenoxy)propanoic acid] by this bacterium (C. Zipper, K. Nickel, W. Angst, and H.-P. E. Kohler, Appl. Environ. Microbiol. 62:4318-4322, 1996). Uptake of (R)-dichlorprop, (S)-dichlorporp, and 2,4-D (2,4-dichlorophenoxyacetic acid) was inducible. Initial uptake rates of cells grown on the respective substrate showed substrate saturation kinetics with apparent affinity constants (Kt) of 108, 93, and 117 microM and maximal velocities (Vmax) of 19, 10, and 21 nmol min-1 mg of protein-1 for (R)-dichlorprop, (S)-dichlorprop, and 2,4-D, respectively. Transport of (R)-dichlorprop, (S)-dichlorprop, and 2,4-D was completely inhibited by various uncouplers and by nigericin but was only marginally inhibited by valinomycin and by the ATPase inhibitor N,N'-dicyclohexylcarbodiimine. Experiments on the substrate specificity of the putative transport systems revealed that (R)-dichlorprop uptake was inhibited by (R)-mecoprop but not by (S)-mecoprop, (S)-dichlorprop, or 2,4-D. On the other hand, the (S)-dichlorprop transport was inhibited by (S)-mecoprop but not by (R)-mecoprop, (R)-dichlorprop, or 2,4-D. These results provide evidence that the first step in the degradation of dichlorprop, mecoprop, and 2,4-D by S. herbicidovorans is active transport and that three inducible, proton gradient-driven uptake systems exist: one for (R)-dichlorprop and (R)-mecoprop, another for (S)-dichlorprop and (S)-mecoprop, and a third for 2,4-D.
食草鞘氨醇单胞菌MH能够完全降解手性除草剂二氯丙酸[(RS)-2-(2,4-二氯苯氧基)丙酸]的两种对映体,其中(S)对映体的降解优先于(R)对映体。这些结果与最近报道的该细菌对甲羧除草醚[(RS)-2-(4-氯-2-甲基苯氧基)丙酸]的对映选择性降解结果一致(C.齐珀、K.尼克、W.安斯特和H.-P.E.科勒,《应用与环境微生物学》62:4318-4322,1996年)。(R)-二氯丙酸、(S)-二氯丙酸和2,4-D(2,4-二氯苯氧基乙酸)的摄取是可诱导的。在各自底物上生长的细胞的初始摄取速率显示出底物饱和动力学,(R)-二氯丙酸、(S)-二氯丙酸和2,4-D的表观亲和常数(Kt)分别为108、93和117微摩尔,最大速度(Vmax)分别为19、10和21纳摩尔·分钟-1·毫克蛋白质-1。(R)-二氯丙酸、(S)-二氯丙酸和2,4-D的转运被各种解偶联剂和尼日利亚菌素完全抑制,但仅被缬氨霉素和ATP酶抑制剂N,N'-二环己基碳二亚胺轻微抑制。关于假定转运系统底物特异性的实验表明,(R)-二氯丙酸的摄取被(R)-甲羧除草醚抑制,但不被(S)-甲羧除草醚、(S)-二氯丙酸或2,4-D抑制。另一方面,(S)-二氯丙酸的转运被(S)-甲羧除草醚抑制,但不被(R)-甲羧除草醚、(R)-二氯丙酸或2,4-D抑制。这些结果证明,食草鞘氨醇单胞菌降解二氯丙酸、甲羧除草醚和2,4-D的第一步是主动转运,并且存在三种可诱导的、由质子梯度驱动的摄取系统:一种用于(R)-二氯丙酸和(R)-甲羧除草醚,另一种用于(S)-二氯丙酸和(S)-甲羧除草醚,第三种用于2,4-D。