植生克雷伯氏菌（Klebsiella planticola 19-1）nifA-like基因的克隆

植生克雷伯氏菌(Klebsiella planticola 19-1)是从新疆鄯善地区玉米根际分离得到的一株联合固氮菌。在40℃高温下有较强的乙炔还原活性。 本工作利用Southern Blot分子杂交技术, 以Klebsiella pneumoniae的nifA为探针，证明了在K．planticola 19-1中存在nifA-like基因，由nifH-lacZ实验推论其nifA-like基因产物对高温相对稳定。经过大质粒电泳和Southern Blot分子杂交，发现nifA-like基因定位于染色体外的大质粒上。本工作进一步克隆了含有K．plonticola 19-1的nifA-like基因的DNA片段，做了它的限制性酶切图谱，并将nifA-like基因初步定位。

联合固氮菌Enteroabcter gergoviae 57-7氮代谢相关基因的克隆和泌氨工程菌的构建

从构建具有稳定泌氨能力的联合固氮工程菌的目的出发，首先构建Enterobacter gergoviae57-7 (E57-7)基因文库并与所筛选的泌氨突变株进行遗传互补实验，得到可互补 泌氨特性的克隆，经Southern杂交后推测其中包含与glnA、amtB基因无关的另一类与泌 氨相关的基因。同时根据铵载体基因amtB的已知序列设计两对简并性引物，经PCR从 E57-7 DNA中扩增得到约340bp的片段，序列分析和Blast序列同源性比较后确定为amtB 基因片段，申报并获得序列号AJ132232，最终从基因库中筛选到两个包含E57-7 amtB 基因的克隆。 用K. pneumoniae的glnA基因片段为探针，通过Southern杂交从E57-7基因库中筛选到包含有glnAntrBC基因的克隆，经亚克隆后对包含有这个操纵元的4316bp片段进行了全序列分析，申报GenBank获得序列号AF072440。在体外实验中构建了Km-cassette 插入glnA的重组质粒pA，将此质粒转入E57-7野生型菌株后经筛选同源重组子获得glnA 突变的具有稳定泌氨能力的菌株15、I9。并进行了盆栽玉米接种实验，确定在灭菌上壤实验体系下I5对玉米幼苗有显著促生效应。 利用绿色荧光蛋白(GFP-S65T，V68L，S72A)基因建立分子生物学研究手段，构建了新 型克隆载体pGreenLD，建立了绿白斑筛选重组质粒的的技术。构建组成型表达gfp的质粒载体研究了E57-7在玉米根际的定殖模式;构建nifH-gfp表达载体，确定在与植物联合生活时其固氮酶结构基因nifHDK的表达与碳源物质供应密切相关。利用不同抗性基因和gfp基因片段构建出在E57-7中组成型表达抗性和GFP的质粒载体，建立了监测接种菌在土壤中释放的双标记系统。 最后克隆了E57-7 glg cluster并测定部分glgCA和glgP基因序列，申报后获得序列号AJ132233和AJ132234，这是首例从联合固氮菌中克隆得到glg cluster的报道。

Diverse tetracycline resistant bacteria and resistance genes from coastal waters of Jiaozhou Bay

Environmental microbiology investigation was carried out in Jiaozhou Bay to determine the source and distribution of tetracycline-resistant bacteria and their resistance mechanisms. At least 25 species or the equivalent molecular phylogenetic taxa in 16 genera of resistant bacteria could be identified based on 16S ribosomal deoxyribonucleic acid sequence analysis. Enterobacteriaceae, Pseudomonadaceae, and Vibrionaceae constituted the majority of the typical resistant isolates. Indigenous estuarine and marine Halomonadaceae, Pseudoalteromonadaceae, Rhodobacteraceae, and Shewanellaceae bacteria also harbored tetracycline resistance. All the six resistance determinants screened, tet(A)-(E) and tet(G), could be detected, and the predominant genes were tet(A), tet(B), and tet(G). Both anthropogenic activity-related and indigenous estuarine or coastal bacteria might contribute to the tet gene reservoir, and resistant bacteria and their molecular determinants may serve as bioindicators of coastal environmental quality. Our work probably is the first identification of tet(E) in Proteus, tet(G) in Acinetobacter, tet(C) and tet(D) in Halomonas, tet(D) and tet(G) in Shewanella, and tet(B), tet(C), tet(E), and tet(G) in Roseobacter.

Dominant chloramphenicol-resistant bacteria and resistance genes in coastal marine waters of Jiaozhou Bay, China

Studies of abundance, diversity and distribution of antibiotic-resistant bacteria and their resistance determinants are necessary for effective prevention and control of antibiotic resistance and its dissemination, critically important for public health and environment management. In order to gain an understanding of the persistence of resistance in the absence of a specific antibiotic selective pressure, microbiological surveys were carried out to investigate chloramphenicol-resistant bacteria and the chloramphenicol acetyltransferase resistance genes in Jiaozhou Bay after chloramphenicol was banned since 1999 in China. About 0.15-6.70% cultivable bacteria were chloramphenicol resistant, and the highest abundances occurred mainly in the areas near river mouths or sewage processing plants. For the dominant resistant isolates, 14 genera and 25 species were identified, mostly being indigenous estuarine or marine bacteria. Antibiotic-resistant potential human or marine animal pathogens, such as Escherichia coli, Klebsiella pneumoniae, Proteus mirabilis and Shewanella algae, were also identified. For the molecular resistance determinants, the cat I and cat III genes could be detected in some of the resistant strains, and they might have the same origins as those from clinical strains as determined via gene sequence analysis. Further investigation about the biological, environmental and anthropogenic mechanisms and their interactions that may contribute to the persistence of antibiotic-resistance in coastal marine waters in the absence of specific antibiotic selective pressure is necessary for tackling this complicated environmental issue.