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31.
The cystic fibrosis (CF) gene has been observed to have the highest frequency of mutations in the Caucasian population. Prenatal diagnosis can now be performed with a high degree of accuracy since the identification of most of the gene's mutations, as well as the characterization of intragenic markers. However, the observation of a distribution of clinical phenotypes increases the need to identify a mild phenotype and avoid false-negative diagnosis. By screening most of the exons of the CFTR gene, we showed that a supposed obligate carrier of CF was in fact an asymptomatic affected woman.  相似文献   
32.
高浓度CO2对红松根际及根外土壤微生物群落结构的影响   总被引:3,自引:0,他引:3  
采用DGGE(Denaturing Gradient Gel Electrophoresis)技术,于2003年的7~9月中旬对高浓度CO2(700和500μmol·mol-1)处理下的红松幼苗根际和根外0~10 cm土壤微生物群落结构进行了研究.结果表明,大气CO2浓度升高对红松根际和非根际土壤细菌群落结构产生了较大的影响,主要表现为部分细菌物种的出现,或原有细菌数量的丰富以及原有物种的消失或其数量被削弱的现象,但主要建群种未变.  相似文献   
33.
化学-生物絮凝污水处理工艺中微生物群落结构变化分析   总被引:2,自引:0,他引:2  
利用分子生物学技术,直接从化学-生物絮凝工艺的活性污泥样品中提取DNA,对16S rDNA V3区进行PCR扩增,结合DGGE(变性浓度梯度凝胶电泳),分析了活性污泥中微生物群落结构,并对Shannon多样性指数进行分析讨论,通过研究指出系统中细菌数量的增加或减少.测定了活性污泥中部分菌种的16S rDNA V3区片段序列,通过NCBI(美国国立生物技术信息中心)基因库比对,初步确定细菌的属.结果表明,PCR—DGGE结合测序技术是一种完全可行的快速进行环境样品微生物研究的分析方法.图3表4参13  相似文献   
34.
以细菌的通用引物PCR扩增16SrRNA基因的V3可变区,结合应用双梯度变性梯度凝胶电泳(DGDGGE)技术分析除臭生物滤池中不同空间层次的微生物种群的基因多样性,以及富集前后的微生物种群结构变化,初步了解可培养细菌的情况,并回收主要的DNA片段进行序列分析.结果表明,在滤池的不同层次上呈现出明显的空间分布多样性差异,并且培养前后及不同培养基富集培养的微生物种群的多样性及特异性有很大的差别.序列比对显示,硫氧化细菌在除臭过程中占有优势地位,为进一步的菌种分离提供有益的指导,也为更好地处理恶臭气体提供可靠的科学支持.图4表2参18  相似文献   
35.
Long-term use of chlorpyrifos poses a potential threat to the environment that cannot be ignored, yet little is known about the succession of substrate microbial communities in constructed wetlands(CWs) under chlorpyrifos stress. Six pilot-scale CW systems receiving artificial wastewater containing 1 mg/L chlorpyrifos were established to investigate the effects of chlorpyrifos and wetland vegetation on the microbial metabolism pattern of carbon sources and community structure, using BIOLOG and denaturing gradient gel electrophoresis(DGGE) approaches. Based on our samples, BIOLOG showed that Shannon diversity(HV) and richness(S) values distinctly increased after 30 days when chlorpyrifos was added. At the same time, differences between the vegetated and the non-vegetated systems disappeared. DGGE profiles indicated that H Vand S had no significant differences among four different treatments. The effect of chlorpyrifos on the microbial community was mainly reflected at the physiological level. Principal component analysis(PCA) of both BIOLOG and DGGE showed that added chlorpyrifos made a difference on test results.Meanwhile, there was no difference between the vegetation and no-vegetation treatments after addition of chlorpyrifos at the physiological level. Moreover, the vegetation had no significant effect on the microbial community at the genetic level. Comparisons were made between bacteria in this experiment and other known chlorpyrifos-degrading bacteria. The potential chlorpyrifos-degrading ability of bacteria in situ may be considerable.  相似文献   
36.
不同16SrDNA靶序列对DGGE分析活性污泥群落的影响   总被引:15,自引:1,他引:14  
为探讨不同通用引物扩增16S rDNA靶序列对活性污泥微生物群落分析的影响,更合理的利用变性梯度凝胶电泳(DGGE)技术分析活性污泥样品.从连续流搅拌槽式反应器(CSTR)中获取活性污泥,以3对通用引物341f/534r、968f/1 401r和341f/926r扩增16S rDNA序列,用DGGE分离PCR扩增产物.研究表明采用不同引物对进行DGGE分析时,群落多样性和动态存在显著的差异.341f/534r和968f/1 401r的靶序列分离效果较好,341f/926r的靶序列分离效果较差.引物341f/534r和341f/926r DGGE图谱显示S2和S3相似性高,引物968f/1 401r DGGE图谱显示S1和S2相似性高.由此可见采用不同引物对进行DGGE分析时,群落结构之间的相似性和动态是不一致的.341f/534r的DGGE图谱中条带丰富,多样性最好,968f/1 401r的DGGE图谱次之,341f/926r DGGE图谱条带最少,多样性也较差.因此,在利用DGGE分析活性污泥样品时采用引物341f/534r和968f/1 401r是比较适宜的.  相似文献   
37.
Two different microbial communities able to degrade atrazine (atz) were inoculated in four different soils. The most critical factor affecting the success of inoculation was the soil pH and its organic matter (OM) content. In two alkaline soils (pH > 7), some inoculations led immediately to a strong increase of the biodegradation rate. In a third slightly acidic soil (pH = 6.1), only one inoculum could enhance atz degradation. In a soil amended with organic matter and straw (pH = 5.7, OM = 16.5%), inoculation had only little effect on atz dissipation on the short as well as on the long-term. Nine months after the microflora inoculations, atz was added again and rapid biodegradation in all alkaline inoculated soils was recorded, indicating the long-term efficiency of inoculation. In these soils, the number of atz degraders was estimated at between 6.5 × 103 and 1.5 × 106 (g of soil)-1, using the most probable number (MPN) method. Furthermore, the presence of the atz degraders was confirmed by the detection of the gene atzA in these soils. Denaturing gradient gel electrophoresis (DGGE) analysis of the 16S rDNA genes indicated that the inoculated bacterial communities had little effect on the patterns of the indigenous soil microflora.  相似文献   
38.
采集了浙江省富阳市环山乡某冶炼厂小高炉附近受铜、锌、铅、镉不同程度复合污染的4个农田土壤样品,首先扩增土壤总DNA中的16S rDNA,然后进行变性梯度凝胶电泳(Denaturing Gradient Gel Electrophoresis),分析了长期受重金属复合污染的农田土壤的微生物群落遗传多样性变化.结果表明,不同程度的重金属复合污染明显改变了农田土壤的微生物群落遗传多样性,但与多样性的改变不是简单的负相关关系,最大的多样性指数出现在中等污染程度的土壤中.  相似文献   
39.
The effect of acetanilide herbicide mefenacet on soil microbial communities was studied using paddy soil samples with different short-term treatments. The culturable bacteria (plate counts), dehydrogenase activity and changes in community structure (denaturing gradient gel electrophoresis (DGGE) analysis) were used for biological community assessments. Mefenacet was a significant stimulus to cultural aerobic bacteria and dehydrogenase activity while Sphingobacterium multivorum Y1, a bacterium efficiently degrading the mefenacet, only induced the increasing colony-forming unit (CFU) of bacteria but little effect on dehydrogenase activity during the whole experiment. The degree of similarity between the 16S rDNA profiles of the communities was quantified by numerically analyzing the DGGE band patterns. Similarity dendrograms showed that the microbial community structures of the mefenacet-treated and non-treated soils were not significantly different. But supplement of S. multivorum Y1 could increase the diversity of the microbial community in the mefenacet-polluted paddy soil. This work is a new attempt to apply the S. multivorum Y1 for remediation of the mefenacet-polluted environments.  相似文献   
40.
Manure amendment in agricultural practice can have a large effect on herbicide dissipation because the period of manure plowing is close to the period of herbicide application. In addition, manure amendment is among the frequently encountered options in ameliorating pesticide pollution. In this research, the dissipation of the herbicide pendimethalin was examined after amendment with two common green manures, Lupinus luteus (L) or Cosmos bipinnatus (C), for 110 days in pH 5.2 and 7.7 soils (Sankengtzu [Sk] and Erhlin [Eh] soil, respectively). The microbial activity and ecology changes were examined by using Biolog EcoPlate and denaturing gradient gel electrophoresis (DGGE). In Sk soil, the half-lives of pendimethalin with L, C, and blank treatment were 49.0, 54.9, and 62.2 days, respectively, whereas that in Eh soil they were 46.3, 52.6, and 34.8 days, respectively. Pendimethalin dissipated quickly in more neutral soil (Eh soil), but the addition of manure can only increase the dissipation rate in acidic soil (Sk soil), indicating that the amendment of manures exerted different effect in pendimethalin dissipation rates in different pH soils. The application of pendimethalin and/or manure altered the microbial community activity after 24 h of incubation. After 110 days, the microbial community activities in green manure–amended soil were more similar to that with blank than pendimethalin treatment in both types of soils. In comparison with treatment C, microbial communities were more similar between treatment L and blank, indicating the superior effect over pendimethalin on microbial communities when applying Lupinus luteus. The research showed that the application of herbicide pendimethalin changed soil microbial community, and the amendment of manures exerted different effect in pendimethalin dissipation rates in different pH soils. It is assumed that the change in dissipation rates was originated from the microbial community change after different manure amendment.  相似文献   
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