Halden R U, Tepp S M, Halden B G, Dwyer D F
Department of Civil Engineering, University of Minnesota, Minneapolis, Minnesota 55455, USA.
Appl Environ Microbiol. 1999 Aug;65(8):3354-9. doi: 10.1128/AEM.65.8.3354-3359.1999.
Pseudomonas pseudoalcaligenes POB310(pPOB) and Pseudomonas sp. strains B13-D5(pD30.9) and B13-ST1(pPOB) were introduced into soil microcosms containing 3-phenoxybenzoic acid (3-POB) in order to evaluate and compare bacterial survival, degradation of 3-POB, and transfer of plasmids to a recipient bacterium. Strain POB310 was isolated for its ability to use 3-POB as a growth substrate; degradation is initiated by POB-dioxygenase, an enzyme encoded on pPOB. Strain B13-D5 contains pD30.9, a cloning vector harboring the genes encoding POB-dioxygenase; strain B13-ST1 contains pPOB. Degradation of 3-POB in soil by strain POB310 was incomplete, and bacterial densities decreased even under the most favorable conditions (100 ppm of 3-POB, supplementation with P and N, and soil water-holding capacity of 90%). Strains B13-D5 and B13-ST1 degraded 3-POB (10 to 100 ppm) to concentrations of <50 ppb with concomitant increases in density from 10(6) to 10(8) CFU/g (dry weight) of soil. Thus, in contrast to strain POB310, the modified strains had the following two features that are important for in situ bioremediation: survival in soil and growth concurrent with removal of an environmental contaminant. Strains B13-D5 and B13-ST1 also completely degraded 3-POB when the inoculum was only 30 CFU/g (dry weight) of soil. This suggests that in situ bioremediation may be effected, in some cases, with low densities of introduced bacteria. In pure culture, transfer of pPOB from strains POB310 and B13-ST1 to Pseudomonas sp. strain B13 occurred at frequencies of 5 x 10(-7) and 10(-1) transconjugant per donor, respectively. Transfer of pPOB from strain B13-ST1 to strain B13 was observed in autoclaved soil but not in nonautoclaved soil; formation of transconjugant bacteria was more rapid in soil containing clay and organic matter than in sandy soil. Transfer of pPOB from strain POB310 to strain B13 in soil was never observed.
将产碱假单胞菌POB310(pPOB)、假单胞菌属菌株B13 - D5(pD30.9)和B13 - ST1(pPOB)引入含有3 - 苯氧基苯甲酸(3 - POB)的土壤微观系统中,以评估和比较细菌的存活情况、3 - POB的降解以及质粒向受体细菌的转移。菌株POB310因其能够利用3 - POB作为生长底物而被分离出来;降解由pPOB上编码的一种酶——POB - 双加氧酶启动。菌株B13 - D5含有pD30.9,这是一个携带编码POB - 双加氧酶基因的克隆载体;菌株B13 - ST1含有pPOB。菌株POB310在土壤中对3 - POB的降解并不完全,即使在最有利的条件下(3 - POB浓度为100 ppm、添加P和N以及土壤持水量为90%)细菌密度也会下降。菌株B13 - D5和B13 - ST1将3 - POB(10至100 ppm)降解至浓度<50 ppb,同时细菌密度从10(6)增至10(8) CFU/g(干重)土壤。因此,与菌株POB310不同,改良菌株具有以下对于原位生物修复很重要的两个特征:在土壤中存活以及在去除环境污染物的同时生长。当接种量仅为30 CFU/g(干重)土壤时,菌株B13 - D5和B13 - ST1也能完全降解3 - POB。这表明在某些情况下,引入细菌的低密度也可能实现原位生物修复。在纯培养中,pPOB从菌株POB310和B13 - ST1转移至假单胞菌属菌株B13的频率分别为每供体5×10(-7)和10(-1)个接合子。在灭菌土壤中观察到了pPOB从菌株B13 - ST1转移至菌株B13,但在未灭菌土壤中未观察到;在含有粘土和有机物的土壤中比在沙质土壤中,接合子细菌的形成更快。在土壤中从未观察到pPOB从菌株POB310转移至菌株B13。