中南大学本科论文 中文摘要 中南大学 本科生毕业论文 题 目 浸矿体系微生物群落基因组芯片的构建与评 估 学生姓名 指导教师 学 院 谢 明 刘学端 教授 资源加工与生物工程学院 专业班级 生物工程 0202 完成时间 2006 年 6 月 22 日 1 Index Abstract in Chinese ··········································································· 1 Abstract in English ··········································································· 2 Chapter 1 Introduction ······································································· 3 Chapter 2 Review ············································································· 4 2.1 Challenges in microbial community analysis ·································· 4 2.2 Molecular methods in microbial community research: development and limitations ······················································································ 5 2.2.1 Conventional molecular methods in microbial analysis ················· 5 2.2.2 Microarrays for research in microbial community ······················· 6 2.3 Conclusion and future trend toward microbial community study ··········· 8 Chapter 3 Materials and experiment ······················································· 9 3.1 Materials and instruments used in experiments ································ 9 3.2 Bacteria cultivation and the extraction of genomic DNA ···················· 10 3.3 CGA fabrication ···································································· 12 3.3.1 Sample Pretreatment: target DNA preparation ··························· 12 3.3.2 Microarray fabrication ······················································· 12 3.4 Hybridization of CGA for examining its sensitivity, specificity and quatitative potential ··········································································· 13 3.4.1 Fluorescent labeling of Probe ··············································· 13 3.4.2 Hybridization of labeled probe to CGA ··································· 14 3.4.3 Scanning of hybridization result ············································ 15 Chapter 4 Results and discussion ··························································· 15 4.1 The quantitation of probe DNA concentration ································· 15 4.2 Surface scanning of CGA after hybridization ·································· 16 4.3 CGA capability evaluation ························································ 18 4.3.1 Evaluation of CGA sensitivity ·············································· 18 4.3.2 Evaluation of CGA specificity ·············································· 18 4.3.3 Evaluation of CGA quantitative potential ································· 19 Chapter 5 Conclusion ········································································ 23 Acknowledgement ············································································ 25 References ····················································································· 25 摘 要 用传统分离培养方法进行浸矿体系微生物群落结构分析工作量大,耗时多。 而常规分子生物学方法虽然灵敏度、精确度高但平行测试能力有限。基因芯片技 术为复杂样品分析提供了强大的工具, 而基于基因芯片技术发展的群落基因组 芯片为检测自然环境微生物群落种群数量及其相对丰度提供了新的思路和方法。 本论文提取来自细菌Leptospirillum属的10个菌株,Acidithiobacillous Ferrooxidan 种的9个菌株,以及Acidiphilum属的5个菌株的基因组DNA构建了浸矿微生物群落 基因组芯片。优化了芯片检测的杂交反应条件。对所构建的芯片的灵敏度、特异 性以及定量性能进行了评估。结果显示所构建的群落基因组芯片特异性良好,几 乎不存在交叉杂交;芯片灵敏度达到0.11ng左右,高于文献报道水平;杂交信号 强度与探针样品浓度之间存在较好的线性关系,可以用于定量分析。 关键词:基因芯片;群落基因组芯片;微生物群落;生物浸出 中南大学本科论文 英文摘要 Abstract The identification for the community structure in bioleaching systems used to be a fatiguing and time-consuming task. The newly developed method—Community Genome Array (CGA), which is based on microarray technology, provides a brand-new strategy for the detection of microorganism populations, their presence and abundance in bioleaching systems. In this assay, Community Genome Array containing genomic DNA from 10 strains of Leptospirillum, 9 strains of Acidithiobacillous Ferrooxidan, and 5 strains of Acidiphilum is designed and constructed. The reaction condition for the hybridization of this CGA is carefully examined and optimized. The capability of this Community Genome Array is tested in terms of sensitivity, specificity and quantitative potential. Results suggest that the CGA fabricated is highly sensitive as it can detect 0.11ng of sample DNA; little cross hybridization is observed, suggesting that the CGA is capable of differentiating DNA of bacteria in the species level. Besides, linear relationship between the hybridization signal and probe DNA concentration is obtained, thus, the CGA fabricated can be applied in quantitative analysis. Keywords: mcrioarray; community genome array; microbial community; bioleaching system 2 中南大学本科论文 第 1 章 前言 Chapter 1 Introduction In recent decades, microorganisms in bioleaching systems have aroused more and more interest in researchers because of their potential in alleviating environmental pollution as well as extracting and refining minerals (such as Fe, Cu) from low grade ores. Generally, microorganisms in bioleaching systems are chemolithoautotrophic, Gram-negative, aerobic bacteria (there are existence of aechaea and even eukaryotes though) grow in extremely acidic fluids (typical pH values are within 1.8~3.5) containing abundant minerals. This kind of ecology system is proved to be simpler than common fields because it owns fewer kinds of substances, and there are very little organic compounds. Microorganisms in bioleaching systems obtain the energy required for their metabolism and reproduction mainly through the oxidation of inorganic substance such as Fe2+, sulfur and the reduction of Fe3+, etc. Dominant bacteria in bioleaching systems are typically: Acidithiobacillous Ferrooxidan (At.f), Leptospirillum (L), and Acidiphilum (A.p). There are also archaea in such environments, but the bulk of these archaea belong to genus Thermoplasmatales and Sulfolobales. Besides, There have been a few reports of the presence of eukaryotes [1]. In this assay, we focus on the detection and analysis of bacteria in the community level: their presence and relative abundance, and the interaction of organisms within the community and with the environment. The distinct environment in which these microorganisms live and reproduce has tremendously perturbed the course of detecting, identifying certain microorganisms and analyzing the structure & metabolism networks for the community of interest. Conventional methods, which are originally designed for research of microorganisms grown in modest environment, cannot be applied to these systems because of the harsh environmental condition (extremely acidic fluid, the lack of organic substance, high temperature, etc). For example, a newly developed method—Biolog System (first designed by Biolog Company), which is capable of identifying pure culture and analyzing different microbial community with high accuracy [2], proved to be limited for the detection and analysis of bacteria in bioleaching systems because these microorganisms do not utilize carbon as their main source of energy. For the reasons above, microarray becomes a ideal research tool for the analysis of microbial community in bioleaching systems because it has no requirements for the metabolism style of organisms to be tested, which means this method is relatively unbiased and non-directed. This novel type of technology has offered a brand-new method which is capable of detecting hundreds, even thousands kinds of microorganisms at one time (high throughput) with high sensitivity, specificity and accuracy. Besides, with the help of computer, we will be able to quantify the information obtained from the hybridization of microarrays, as there have been several kinds of microarrays that already proved to be potentially quantitative, such as Functional Gene Array (FGA) and Community Genome Array (CGA). 3 中南大学本科论文 第 2 章 综述 Our goal here is to construct a Community Genome Array in order to identify the community structure of the sample obtained directly from bioleaching systems. Compared to traditional method in depicting the community structure in natural environment, which may take years to isolate bacteria within the system, analysis based on CGA will cost only several days to comprehensively reveal the community structure information. However, the microarray we fabricated here is a prototype CGA, as it contains only 24 strains of bacteria; but in later experiments, genomic DNA from other bacteria will be successively planted on other chips and thus the capability of the CGA will be enhanced. Although Community Genome Array is powerful in detecting and identifying microorganisms, the design and construction of this type of microarray require special technology and equipment. Moreover, the hybridization condition needs to be carefully examined because some subtle change in hybridization condition (temperature, solution, etc) may produce data that are remarkably different, which may lead to inaccurate conclusion of the community under investigation. After fabricating this CGA, we evaluated its capacity, sensitivity and quantitative potential. Suggestions are made for promoting CGA performance. Chapter 2 Review: the development of methods in microbial community analysis in bioleaching systems 2.1 Challenges in microbial community analysis The study of microbial community can offer us the overall information about the microorganisms of interest, their metabolic function, genetics, species diversification, evolution and regulatory networks. However, the traditional ‘isolate and study’ research strategy proved to be quite limited for analysis in community level, because this strategy follows the way of simplifying a complex system while our effort is aimed directly at the integrated system—the microbial community as a whole. Thus, conventional research methods, which are centered with acquiring and maintaining the pure culture of certain microorganisms, proved to be limited in the study of microorganisms in the community level, especially for microbial community in special environments (such as the AMD system and bioleaching systems). Besides, other challenges occur as we are to explore microorganism and to obtain information about the metabolic, genetic function and regulatory networks in their community context. First of all, it is extremely difficult for us to acquire community structure information that exactly represents the original sample because our ability to conduct research in-situ is limited. This is of great importance for research works oriented at environmental application (such as study concerning bioleaching systems and the mitigation of environmental pollution), as the results are obtained from samples that are not representative of microbial community in nature. For example, researchers conducting experiments towards the AMD system have once reached the conclusion that bacterium Acidithiobacillus Ferrooxidans is the dominant species in most AMD systems. But recent report pointed out that the conclusion above may just brought by the fact that bacteria of the Acidithiobacillous Ferrooxidan species is easier to 4 中南大学本科论文 第 2 章 综述 cultivate and thus a significant part of experiments are designed for the detection and analysis of these bacteria [3]. FISH experiment examining the microbial community directly in the Richmond Mine, California, USA, revealed that the bacteria of species Acidithiobacillus Ferrooxidan only takes up a small portion in the community, some of the species which are thought to be of great amount in nature proved to be too few to be detected [4]. Secondly, the preservation of genomic information for species that are scarce in the community requires special technology. Though Polymerase Chain Reaction (PCR) technology has greatly promoted analysis in molecular level, it is still difficult for us to design proper primers to avoid biased duplication, which may lead to false conclusion as the DNA of some minor populations in the community may thrive because the primers are homologous and the real dominant species is neglected. Thirdly, because of the diversity and the heterogeneity of microorganisms, limitations arise due to the lack of reproducibility of experiments, which means the results gained from former experiments may not match successive studies of exactly the identical system. For all the reasons above, novel research strategy of unbiased analysis is developed and methods with higher throughput, specificity, sensitivity and accuracy are designed. 2.2 Molecular methods in microbial community research: development and limitations 2.2.1 Conventional molecular methods in microbial analysis An overall understanding of microbial community structure, the partitioning of metabolic function among populations, and the roles each of the species performs in the consortia will greatly enhance our ability to discover important metabolic function and the regulation of microbial activity. Genomic study and molecular methods will provide insights into the essence of the ecology and evolution of microorganism in natural environment. We might be able to design novel cultivation strategy, which may lead to successfully isolation of special microbial species. For example, utilizing genomic information of the AMD system in Richmond Mine at Iron Mountain, California, USA, researchers successfully isolated the microorganism Leptospirillum group III [5]. In recent years, researchers have developed various kinds of methods based on the metabolic and molecular character of microorganisms for the study of microbial community. For instance, based on the different extent to which microorganisms utilizing 95 kinds of carbon sources (metabolic level), the Biolog system can build up the metabolic matrix depiction of certain microorganism and the metabolic fingerprint of environmental sample. Besides, the development in molecular methods has largely enhanced our ability to survey environmental microbial community. Among these methods are Single-Strand Conformation Polymorphism (SSCP), Denatured/Temperature Gradient Gel Electrophoresis (DGGE/TGGE), Fluorescent In-Situ Hybridization (FISH), Terminal Restriction 5 中南大学本科论文 第 2 章 综述 Fragment Length Polymorphism (T-RFLP), Reverse Sample Genome Probing (RSGP), etc. Molecular methods are advantageous as they are generally more sensitive, specific and accurate. The information obtained from these methods provides insight into the genetic character of microorganisms in microbial community. Besides, PCR technology has allowed experiment toward little DNA sample. However, due to the diversity of microorganisms in natural environment (as we know that 1 gram of soil sample may contain more than 1000 microorganism species), the methods above seem to be weak in the detection and identification of all the species in the community simultaneously, that is, their parallel capacity is limited. For example, the newly ameliorated FISH: Multicolor FISH can detect only 7 kinds of target genomic DNA fragments at one time. Further, as PCR manipulation is essential to almost all the methods based on the hybridization of nucleic acid molecule (because we cannot obtain enough amount of DNA to conduct these experiments directly from cultivation), the biased PCR amplification, which we have no ideal solutions so far, should be taken great consideration, as it may bring in feint information about the community structure. Moreover, methods such a FISH, T-RFLP, SSCP, etc. require stringent reaction condition, which resulted in the lack of reproducibility. Subtle change in reaction temperature, pH value or solution constitution may produce data with significant difference. In a word, all these methods owns its peculiar advantage in certain aspect, but may be weak in other fields, thus, the combination of several methods or the development of comprehensive new strategy may be promising for research work in the future. 2.2.2 Microarrays: powerful tool for research in microbial community Microarray technology-the production of the combination of chemistry, physics, mathematics and bioinformatics, first designed by Mark Schena etc. in 1998, developed rapidly in recent decade because of its great potential in analyzing samples containing hundreds, even thousands kinds of DNA (or protein, etc.) at one time (which is referred to as ‘high-throughput’) as well as detecting & identifying samples with high sensitivity, specificity and accuracy. Generally, microarrays are chemically modified smooth optic glass slides containing huge amount of special information (such as the functional gene of bacteria, antibody of certain antigen, etc.). DNA molecules are planted on the chip through electronic interaction with positive residue or covalent binding on the surface of the slide. This novel technology can be utilized to monitor gene expression, detect specific mutations in DNA sequences and characterize microorganisms in environmental samples. The application of this new technology will help us to penetrate the microbial community in various kinds of natural environment. In recent years, professor Jizhong Zhou and his co-workers in his laboratory in Oak Ridge National Laboratory, USA have designed several novel kinds of microarrays which are referred to as Functional Gene Array (FGA), Phylogenetic Oligonucleotide Array (POA), Whole-genome Open Reading Frame 6 中南大学本科论文 第 2 章 综述 Arrays, and the Community Genome Array, etc. The comparison of the characteristics of these four kinds of microarrays is listed in Table 2.1[6]. The Functional Gene Arrays (FGAs) contain functional gene sequence information and are primarily used for the functional analysis of microbial community activity in the environment. FGAs based on PCR product is capable of differentiate genes possessing <80–85% sequence identity, while FGAs based on oligonucleotides (about 50 base pair in length) can clearly differentiate genes with less than 86–90% sequence identity using hybridization conditions of 50 º C and 50% formamide [6]. The Phylogenetic Oligonucleotide Array can provide phylogenetic information about the community under investigation; and the Whole-genome open reading frame array can be used to reveal genome diversity and relatedness among closely related organisms. The Community Genome Array is distinctive among these various kinds of microarrays, because it is fabricated using genomic DNA of the bacteria, which may more than 20kb in fragment length. CGA is specific enough to tell microorganisms in species, even strain level under stringent condition [7](see reference 7 for detail). Besides, a significant characteristic of CGA is that detection works using this sort of microarray dose not require the sequence information of the probes fabricated on the chip beforehand. This is of great importance and utility, because the lack of sequence information of isolated microorganisms (the fact is little or nothing is known about the majority of such organism) will no longer perturb research works of detecting the presence and relative abundance of these microorganisms. For CGA analysis, once some new kind of bacteria is isolated and identified, we can use its genomic DNA to detect its presence in environmental sample without knowledge of its DNA sequence, which will greatly reduce research workload. Considering DNA consumption, CGA is also advantageous than traditional DNA-DNA reassociation approach, as its fabrication needs only 2µg of DNA, while the latter method requires about 100µg of DNA [6]. Despite all of the advantages of CGA, the capability of this sort of microarray still depends on the isolation we obtained beforehand, because in order to detect certain kinds of microorganisms, we must first acquire the pure culture in order to extract genomic DNA we needed to fabricate the chip. Thus, more isolation we get, more representative information about the community under concern we may obtain through later on experiments. This reveals one important weakness in CGA: it is still pure-culture dependent (which means it cannot be used for the detection of uncultivated microorganisms) although the successive hybridization and detection work can be carried out without culturing. Besides, there are other problems concerning microarray analysis in microbial community, including CGA. ① : Fluctuation in internal hybridization of microarray is critical, as it precludes comparison of data between experiments conducted in different laboratory, even the serial experiments in the same laboratory using the same strategy. ②:The threshold of detection sensitivity is still not clear. ③: Data produced through microarray hybridization may be extremely huge, but the development of tools for the analysis of such data has fallen behind, thus it is difficult to reveal effective information from data obtained; internal hybridization and background signal may bring false conclusion [8]. 7 中南大学本科论文 第 2 章 综述 Table 2.1 Major differences of various types of microarrays for environmental studies (contents of this table are excerpted from reference 6) Probe size Information provided Targeted microorganisms Specificity Sensitivity (ng of DNA) Quantitation Taxonomic resolution CGAs PCR-based FGAs Oligonucleiotide-based FGAs Whole Genomic DNA 200-1000bp 50-70bp Phylogenetic Functional Functional Culturable and non-culturable <80%-85% sequence homology Culturable and non-culturable <86%-90% sequence homology About 0.2 About 1 About 8 Yes Yes Yes Genus-species Genus-species Species-strains culturable species 2.3 Conclusion and future trend toward microbial community study Although there has been great challenges in research of microbial communities in environment, numerous new methods has provided powerful tool to penetrate the true character of the metabolism, genetics, ecology, and regulatory networks of microorganisms of interest, and to utilize these organism for environmental application. Methods such as FISH have allowed in-situ research, which is critical in revealing microbial community characteristic in natural environment [9]. However, our ability to conduct in-situ study is still limited because of the complexity of natural sample. Microarray technology has great potential as a specific, sensitive, quantitative, parallel high-throughput tool for microbial detection, identification and characterization in natural environments. Genomic method based on microarray technology may revolutionize the analysis of the structure, function, and kinetics of microbial community. However, the application of microarray in microbial community study has just started, and there are many problems preventing microarray technology to work its full power. The combination of in-situ methods with microarray may be effective for environmental application, as it is capable of analyzing the complex community structure of environmental sample (high parallel capacity of microarray) directly in the field (in-situ study). For Community Genome Array (CGA), though this novel method is still isolation- dependent for now, there are ways to make it possible for detecting uncultivated microorganisms in the future, such as accessing high-molecular weight DNA of microorganisms that are not isolated through Bacterial Artificial Chromosomes (BACs). So far, CGAs are usually built with genome DNA from bacteria, but in natural environment, microbial communities 8 中南大学本科论文 第 3 章 实验流程 are constituted with bacteria, aechaea and eukaryotes (such as fungi). In the future, CGA should contain genomic information from bacteria, aechaea and eukaryotes in order to be more representative, because even in simple systems that contain relatively fewer kinds of microbial species (such as the AMD system), there has been report about the existence of aechaea and eukaryotes besides bacteria, let alone systems in modest natural field. Through CGA fabricated with genomic DNA from bacteria, aechaea and eukaryotes, we will be able to obtain more comprehensive, and thus more representative information about the structure of the microbial community under investigation. In all, various molecular methods have provided useful tool for research in microbial community because of their sensitivity and accuracy. Microarray technology has built a novel platform for research in microbial community because of its obvious advantages in capacity, sensitivity, accuracy and the potential in giving quantitative information. Although there are still various problems concerning the experimental system and data analysis, microarray technology has allowed comprehensive research in function, genetics as well as regulatory networks and may bring study in microbial community into a new era. Chapter 3 Materials and experiment 3.1 Materials and instruments used in experiments Reagents and materials used in experiment are listed in table 3.1 Table 3.1 Reagents and materials used in experiment Reagents Manufacturer (NH4)2SO4 Shantou Xilong Chemical Factory, Guangdong KCl Damao Chemical Factory, Tianjin Chenfu Chemical Factory, Tianjin MgSO4•7H2O Shantou Xianhua Chemical Factory, Guangdong FeSO4•7H2O K2HPO4 Shiyi Chemical Reagent Co., Ltd. Shanghai Ca(NO3)2 Chenfu Chemical Factory, Tianjin Formamide Damao Chemical Factory, Tianjin Lysozyme Amersco Inc. USA Protainase K Merck Inc. USA Rnase Sigma Inc. USA Dimethyl Sulphoxide (DMSO) Shantou Xianhua Chemical Factory, Guangdong Double distilled water / H2SO4 Shantou Xilong Chemical Factory, Guangdong NaOH Shiyi Chemical Reagent Co., Ltd. Shanghai DNA Marker λDNA/Hind III Lot#F4324 Tiangen Inc. Beijing DNA Marker λDNA/Hind III Lot#E3912 Tianweishidai Inc. Beijing Random Primer Invitrogen Inc. USA dNTP Invitrogen Inc. USA Klenow Invitrogen Inc. USA Cy5dye Amersham Bioscience Limited UK Herring Sperm DNA Invitrogen Inc. USA 5%SDS Shiyi Chemical Reagent Co., Ltd. Shanghai Laboratory Film Pechiney Plastic Racking Company USA Array Slides Corming Inc. USA Conical flask Tianheng laboratory Instruments Company, Ningbo Instruments used in the whole experiment process are listed in table 3.2 9 中南大学本科论文 第 3 章 实验流程 Table 3.2 Instruments in experiment process Instruments Rocking Incubator Centrifugator Constant Temperature Water Incubator Electrophoresis system Gel Image analysis system Optical Microscopes Concentrator Super Clean Benches PCR equipment Scanner Model SKY 1102 C 5804 R SC-15 DYY-2C T230 CX 31 5301 CBV 1500A 576BR 0958 Genepix Personel 4100A Manufacturer Sukun Eppendorf Inc. Germany Ningbo City, China Liuyi Company China UVitec Inc. USA Olympus Inc. Japan Eppendorf Inc. Germany Regal Inc. Shanghai China Bio-Rad Inc. USA Axon instruments Inc. USA 3.2 Bacteria cultivation and the extraction of genomic DNA In order to fabricate Community Genome Array for the detection and evaluation of microbial community in bioleaching systems, 27 strains of bacteria Acidiphilum, Acidithiobacillous Ferrooxidan, Leptospirillum were isolated beforehand by doctor Gao et al. All these bacteria are sampled in various domestic mining areas. Table 3.1 introduces the locus information about each of these bacteria from where they were isolated. All the bacteria are isolated from samples obtained in various mine system except Acidithiobacillous Ferrooxidan 23270, which is bought from USA and is used as a modeling bacteria. The DNA of other three bacteria S-1, S-2, and J-1 are offered by Doctor Gao etc. Among these bacteria, 10 strains of Acidithiobacillous Ferrooxidan are cultivated in 9k medium ( (NH4)2SO4 (3.0g/L), KCl (0.1g/L), MgSO4•7H2O (0.1g/L), K2HPO4 (0.5g/L), Ca(NO3)2 (0.01g/L) , the pH value was adjusted to 2) with the addition of FeSO4 (44.6g/L); 10 strains of Leptospirillum are cultivated in 9k medium with FeSO4•7H2O (40g/L) and the pH value was adjusted to 1.6; 7 strains of Acidiphilum were cultivated in 9k medium added with glucose (10g/L) and the pH value is adjusted to 3.0. The inoculation of the bulk of the bacteria mentioned above has succeeded, but we failed to successfully inoculate some of these bacteria, which we also denoted in Table 3.1. After placed in constant-temperature incubator and cultivated for about 3~4 days under 30ºC, the bacteria are collected and washed with H2SO4 and distilled water in order to reduce the attachment of bacteria to mineral particles formed during cultivation. Then the genomic DNA was extracted using the EZ-10 Spin Column Genomic DNA Minipreps Kit Protocol-BS423 (Bio Basic Inc. USA) and preserved in refrigerator at 4ºC. The extraction processes are listed as follows: (1). Sample Preparation for cells grown in suspension Spin appropriate number of cells (max.5 million cells) at 10000rpm for 5min at room temperature. Remove supernatant completely and discard. Wash the cell pellet twice with PBS and resuspend in 200ul cold TE buffer, continue the procedure with Step2. (2). Add 400ul Digestion Solution to 200ul sample from step 1 Mix well. Add 20ul lysozyme and 40~50ulRNase(10mg/ml), place the system for 5min in room temperature. Add 20ul proteinase K solution (1ug/ul), and incubate at 55ºC for 10 10 中南大学本科论文 第 3 章 实验流程 minutes. Table 3.3 Locations from where the isolated bacteria are sampled (bacteria are named after their sample location instead of taxonomic name for the convenience of research) Genus Acidithiobacillous Ferrooxidan Leptospirillum Acidiphilium Bacteria Isolation F1 F2 F3 F4 F5 F6 BY TK YN 23270 YN4 DY J5 LY BY GXLF JE Y17 FTH ZTS DBS1 DBS2 DBS3 S-1 J-1 S-2 DBS4 DX1-1 DX5 DX6 Sample Location Chengmenshan Copper Mine (Jiangxi ) Qixiashan Vanadium Mine (Nanjing) Dabaoshan Copper Mine (Guangdong) Yangtaowu Reservoir (Jiangxi) Liuyang Mine (Hunan) Dexing Copper Mine (Jiangxi) Baiyin Copper Mine (Gansu) Gaofeng Copper Mine (Guangxi) Yunnan Province Bought from USA Yunnan Province Daye Hubei Province Dexing Copper Mine (Jiangxi) Liuyang Hunan Province Baiyin Yunan Province Guangxi Province Dexing Copper Mine (Jiangxi) Yunnan Province Dexing Copper Mine (Jiangxi) Zhongtiao Mountain Dabaoshan Copper Mine (Guangdong) Dabaoshan Copper Mine (Guangdong) Dabaoshan Copper Mine (Guangdong) DNA offered by others DNA offered by others DNA offered by others Dabaoshan Copper Mine (Guangdong) Dexing Copper Mine (Jiangxi) Dexing Copper Mine (Jiangxi) Dexing Copper Mine (Jiangxi) Inoculation Success Success Success Success Failed Success Success Success Success Success Success Success Success Success Success Success Success Success Success Success Success Success Failed / / / Success Failed Failed Success (3). Add 260ul of anhydrous ethanol, and mix well. Apply the mixture to column that is in a 2.0 ml collection tube. Spin at 10000 rpm for 1 minute. (4). Discard the flow-through in the collection tube. Add 500ul of Wash Solution, and spin at 10000 rpm for 1 minute. (5). Repeat washing step 4. (6). Discard flow-through. Spin at 12000 rpm for an additional minute to remove residual amount of Wash Solution. (7). Place the column into a clean 1.5 ml microfuge tube. Add 30-50ul Elution Buffer into the center part of membrane in the column. Incubate the tube at 37 or 50.C for 2 minutes. Incubate at 37 or 50ºC could increase recovery yield. 11 中南大学本科论文 第 3 章 实验流程 (8). Spin at 10000 rpm for 1 minute to elute DNA from the column. (9). Measure DNA quantity by UV absorption at A260 (1.0 OD unit is equivalent of 50ug). Assess genomic DNA quality through 0.7% agarose gel electrophoresis. Isolated genomic DNA should not contain RNA. This kit is capable of extracting DNA longer than 50 kb, as it claims in its instruction book, but due to various factors such as flux in incubation time and temperature in our experiment, the DNA fragments we obtain are generally about 20kb in length. The length and the concentration of the DNA obtained were examined through agarose gel electrophoresis. Results showed that the DNA acquired were about 23kb in length, which is qualified for the fabrication of a CGA. DNA concentration was adjusted to about 100ng/µl (±20ng/µl) through condensation and dilution, as the fabrication of target do not require stringent amount of sample concentration. Besides, reports from Jizhong Zhou et al. suggest that the combination of DNA to the chip will saturate when the DNA concentration is more than 200ng/µl [7]. 3.3 CGA fabrication 3.3.1 Sample Pretreatment: target DNA preparation Target DNA refers to the genomic DNA we extracted from various pure culture of bacteria and will be printed on the surface of the slides and will combine with the active sites on the surface of the slides. It will then be used to detect probe DNA through hybridization experiments. After adjusting DNA concentration, the following manipulations has been done to produce DNA molecule suitable for target printing: (1). Add 5ul of each DNA sample (24 DNA samples in total) successively into a 384-pore plate (2). Add 5ul Dimethyl Sulphoxide (DMSO) to each of the DNA sample. (2). Centrifuge the mixture shortly at 2000 rpm. (3). Cover the plate tightly with laboratory film; place the plate in an incubator (30ºC 180rpm) for 30min to thoroughly mix the solution. (4). Centrifuge the mixture shortly at 2000 rpm for another 1 minute. 3.3.2 Microarray fabrication In total 8 slides, with 1 array that contains 10(2*5) identical 4*7 subarrays on each one of them, were fabricated in uniform in order to produce statistical data. TE buffer is used as the negative control. The position information about the samples planted on the array is listed in table 3.4: Table 3.4 Community Genome Array: subarray structure (TE buffer has been used as negative control (blank) in all successive experiments) Subrow 1 Subrow 2 Subrow 3 Subrow 4 Subc ol 1 blank blank blank blank Subcol 2 Subcol 3 Subcol 4 Subcol 5 Subcol 6 Subcol 7 DBS2(A.p) S-1(A.p) J-1(A.p) S-2(A.p) ZTS(L) JE(L) LY(L) DX6(A.p) YN(L) J5(L) GXLF(L) DY(L) TK(At.f) FTH(L) BY(L) Y17(L) F4(At.f) F6(At.f) YN(At.f) BY (At.f) 23270 F1(At.f) F2(At.f) F3(At.f) 12 中南大学本科论文 第 3 章 实验流程 The printing work is done in about 1 hour plus 50 minutes through OmniGrid Accent Microarrayer (GeneMachines Inc. USA) and its corresponding software. After printed onto the slides, the negative phosphate group on the skeleton of DNA molecule will combine with the positive (NH3)+ group because of electrostatic interaction. Thus the DNA molecule will lie on the surface of the slides, while in aldehyde-silane coated surface the DNA molecule will erect on the surface because of the covalent binding. This process should be defined as absorption, as the binding of DNA molecule to (NH3)+ group is nonspecific. The reaction is illustrated in Figure 3.1[10] below: Figure 3.1 Combination of target DNA to amide group (excerpted from reference 10) This figure illustrates the combination of target DNA to the active sites on the surface of the slides. The interaction between the negative phosphate group of the DNA molecule and the positive NH3+ group makes them combine and thus the target is anchored on the surface of the slide. The slides were placed inside the Microarrayer for about 15 hours to stabilize the combination. Afterward, all the 8 slides were put into UV Crosslinker Model CL-1000 (UVP Inc. USA) in order to perform crosslinking. This part of manipulation is done for two purposes: one is to further stabilize the combination of DNA fragment with the amidogen on the surface of the slides, the other is to block all other blank active positions on the surface of the slides to prevent of false signal brought by the hybridization of probe DNA to unblocked active site. During this process, the slides received irradiation with energy of 600,000µJ/cm2 for about 2 minutes. Then the slides were taken out and cautiously put inside special plastic box and stored at room temperature for later on experiments. 3.4 Hybridization of CGA for examining its sensitivity, specificity and quantitativity potential. In order to test the overall performance of the CGA fabricated, the sensitivity, specificity and quantitative potential needs to be carefully examined. Among the three parameters, the sensitivity refers to the lower threshold of the amount of DNA probe that can be detected through our microarray; specificity refers to the extent to which hybridization between probe and target took place, if species with lower than 70% homologous can hybridize with the target, the microarray is limited in performing highly specific detection; the quantitative potential of a microarray refers to the existence of linear relationship between probe concentration and the intensity of 13 中南大学本科论文 第 3 章 实验流程 hybridization signal. For examining performance of the CGA, we have to conduct just one hybridization experiment. But at first, the probe must be labeled beforehand. 3.4.1 Fluorescent labeling of Probe Genomic DNA from bacteria TK of species Acidithiobacillous Ferrooxidan is selected to test the capability of the chip we fabricated. The relative quantitation of sample DNA concentration is done through electrophoresis and the corresponding image analysis system. DNA marker (longest fragment 23kb, 477 ng/µl) is used as the control. 4µl of the TK sample is diluted to 1×, 0.1×, 0.01×, and 0.001× respectively to form the concentration gradient. Then the probes are dyed through direct labeling with the following procedure: (1). Prepare Mix 1(35µl for each tube) Random Primer 20µl gDNA (0.5-2.0µg) 5µl ddH2O 10µl (2). Add 35µl of Mix 1 to each tube. (3). Incubate the system at 98°C for 5 minutes. (4). Quickly cool down on ice and centrifuge for 10 seconds. (5). Add dNTP (5mM dA/G/CTP, 2.5mM dTTP) 1.0µl, Klenow 2.0µl, Cy5dye 0.5µl and ddH2O 11.5µl, mix up and incubate the system at 37°C for 3 hours, quickly cool down on ice. (6). Add 1N NaOH 2.5µl and incubate at 37°C for 10 minutes. (7). Add 1N HCl 2.5µl to neutralize the above solution. (8). Add Tris-HCl (pH 7.0-7.5) 5.0µl. (9). Transfer the solution into an absorption column, add 600µl Binding Buffer (10). Centrifuge at 12,000rpm for 30 seconds. (11). Add 500µl of Washing Buffer, centrifuge at 12,000rpm for 30 seconds, and then wash again. (12). Add 50µl of Buffer EB, transfer the column into a new centrifuge pipe (1.5ml), incubate at room temperature for 2 minutes, centrifuge at 12,000rpm for 30 seconds. (13). Condense the solution in vacuum concentrator for about 20 minutes. 3.4.2 Hybridization of labeled probe to the microarray We have fabricated 8 pieces of CGA in total, among them 4 were tested here to produce statistical data, that is, the data produced by 40 dots of the identical strain (in total 24*40=960) were collected and analyzed. Before hybridization, the slides to be tested are taken out and boiled in distilled water for 2 minutes and washed in 95% ethanol. The hybridization procedure is as follows: (1). Add formamide 15µl and ddH2O 5.6µl into a PCR tube; the total volume of the system is 20.6µl. (2). Solute the fluorescent labeled DNA in the solution above. (3). Add the following reagents into the PCR pipe: 20×SSC 5.04µl Herring Sperm DNA (10µg/µl) 2.4µl 5% SDS 2µl 14 中南大学本科论文 第 2 章 综述 Thus, the total volume of the system is 30µl. (4). Place the above mixture inside the Bio-Rad PCR equipment and incubate at 95°C for 5 minutes. Cool down the system to 60°C. (5). Place 4 pieces of the CGA we fabricated inside the UV Crosslinker under 600,000µJ/cm2 for 2 minutes, then place the chips in the Bio-Rad PCR equipment, incubate at 60°C for 5 minutes. (6). Transfer the above solution on the surface of the slides; cover it with cover glass, then add one drop of sterile water to two sides of the hybridization box. Close the hybridization box tight and place it in the water incubator, hybridize at 55°C overnight. (7). Washing after hybridization. (Note that the water used for washing should be about 50°C). Washing step 1: Put the chips inside a clean beaker, add 93ml distilled water, 5ml 20×SSC and 2ml of 10×SDS, shake the beaker slightly to move off the cover glass, wash for 5 minutes, discard the fluid. Washing step 2: Add 97.5ml distilled water, 0.5ml 20×SSC and 2ml of 10×SDS; wash for 10 minutes, discard the fluid. Washing step 3: Add 99.5ml distilled water and 0.5ml 20×SSC, and wash for 30 seconds. (8) Take out the chips carefully; dry the chips using a blower, then the chips can be scanned for result check. 3.3.3 Scanning of hybridization result The hybridization result is scanned using scanner Genepix Personel 4100A (Axon instruments Inc. USA) and its corresponding software: Genepix Pro 6.0. Note that the positive surface (surface planted target) of the chips should be adown. Chapter 4 Results and discussion The experiments above have produced a series of data. In this part of the assay, the analysis work is depicted, the results are shown and discussion is made. 4.1 The quantitation of DNA probe concentration. The quantitation of DNA probe concentration proved to be intractable. Although UV Spectrophotometer has provided strategy for detecting the concentration of DNA sample, its capacity in detecting trace amount of DNA is limited. Because the total volume of DNA we extracted is often less than 100µl, there isn’t enough DNA sample for us to conduct UV absorption experiment. Instead, we find a way to relatively quantify sample DNA concentration through agarose gel electrophoresis and the corresponding analyzing software. Figure 4.1 is the picture of electrophoresis result of bacteria TK, the parameters are used directly as in the software and explanations are given according to the instruction book of the software, here we select parameter ‘volume’ for our work to relatively quantify the concentration of DNA probe. 15 中南大学本科论文 第 2 章 综述 Figure 4.1 Electrophoresis result of TK and Marker The gel image analysis system software is able to detect the total signal intensity-which is defined as ‘volume’. According to the detection result, the volume of the first band of Marker is 99049, and the volume of our sample TK is 119927. Both Marker and TK are sampled 4µl to run electrophoresis. The signal intensity is proportional to sample DNA concentration, the Marker we use here has labeled its concentration of each band (477ng/5µl for the first 23120bp band). Thus, the DNA concentration of our sample TK can be estimated through the following equation (X represents the DNA concentration of sample TK): 4 477 / 5 99049 4 119927 X=115.5ng/µl Thus, the concentration of bacteria TK is about 115.5ng/µl. 4.2 Surface scanning of CGA after hybridization After hybridization, the results are checked through scanner Genepix Personel 4100A, the image obtained are shown in Figure 4.1: A (1×) B(0.1×) C(0.01×) D(0.001×) Sample DNA concentration reduce following the direction of the arrow Figure 4.2 Hybridization result through scanning 16 中南大学本科论文 第 4 章 数据处理与结果讨论 The four pictures presented in the last page shows the fluorescent signal after hybridization the CGA with DNA of bacteria TK, which are in gradient1×, 0.1×, 0.01×, and 0.001×. Chip A is hybridized with 1× TK DNA; chip B is hybridized with 0.1×TK DNA; chip C is hybridized with 0.01×TK DNA, and chip D is hybridized with 0.001×TK DNA. The signal intensity can be easily differentiated among each other, and chip D, which is hybridized to 0.001×TK DNA (about 0.11ng of DNA), still shows clear signal and hybridization specificity. For successive test of the specificity and quantitative potential, the images shown in Figure 4.2 were modified through the software Genepix Pro 6.0 and are shown below in Figure 4.3: One subarray A (1×) B(0.1×) C(0.01×) D(0.001×) Figure 4.3 Modified images of picture A, B, C and D Modified images of scanning result. The background (color blue) and interference signals are automatically subtracted through the software Genepix Pro 6.0. Thus, the contrast of spots that have hybridization signal to spots that no hybridization has taken place is largely enhanced. For the quantitation of hybridization signal, image modify is also necessary as the original images prove to be too coarse to provide information accurate enough. The images above also present clear trend of change in hybridization signal intensity from left to right. 17 中南大学本科论文 第 4 章 数据处理与结果讨论 4.3 CGA capability evaluation 4.3.1 Evaluation of CGA sensitivity The sensitivity of the CGA is depicted in Table 4.1 Table 4.1 Result of hybridization signal (positive or negative) under different concentration of probe DNA Probe Concentration Hybridization Signal (115ng) Positive Negative (11.5ng) (1.15ng) (0.011ng) The result shows that the CGA we fabricated is capable of detecting extremely small amount of DNA. In Figure 4.1, from left to right the pictures present the hybridization results of CGA to sample DNA in concentration gradient 115ng, 11.5ng, 1.15ng and 0.115ng. According to Figure 4.1 picture D, 0.115ng of sample DNA gives clear fluorescent signal, which means the CGA fabricated is capable of detecting 0.115ng DNA sample. Note that the surface where the hybridization box placed should be horizontal, thus the thickness of the fluid between the chip and the cover glass will be uniform, which guarantees the uniformity of probe DNA distribution. The capability of the lower limitation of detection capability may still been underestimated because of the lack of more diluted gradient. But considering environmental application, the sensitivity of the CGA may not be as high as the experiments prove here, as in the experiment we use the DNA from a single pure culture. When utilizing this CGA to detect DNA in mixed natural sample, the sensitivity of the CGA should be lower because of the interference of various kinds of DNA molecule and chemical compounds existing in the solution. After all, in terms of testing the sensitivity of the CGA, we reach the conclusion that the CGA we fabricated is capable of detecting DNA sample as little as 0.11ng. 4.3.2 Evaluation of CGA specificity As reported, the specificity of CGA is to differentiate species, and under stringent conditions it may be possible for the CGA to distinguish tell different strains within a species. The hybridization condition is 50% formamide at temperature 55°C, the whole hybridization process lasted for about 13 hours. After hybridization, the chip are taken our from the hybridization box and carefully washed as described in chapter 3. In order to examine the hybridization result more clearly. We need to refer to Figure 4.2 for more contrasted information. Cross hybridization were observed in strains DBS2, S-1 and J-1. The reason for this phenomenon is discussed later. Despite the cross hybridization, hybridization signals are obtained in target 23270, F1, F2, F3, F4, F6, YN, and BY (At.f). All of the targets listed above are Acidithiobacillous Ferroxidans. Ten strains of bacteria Leptospirillum showed no hybridization signal. Thus, the resolution of hybridization of the CGA we fabricated is species, as the hybridization result shows that the CGA cannot successfully tell different strains of the same species Acidithiobacillous Ferroxidan. Table 4.2 shows the result of 18 中南大学本科论文 第 2 章 综述 hybridization specificity. Table 4.2 Hybridization result of each of the target in a subarray Subrow 1 Subrow 2 Subcol 1 Blank Blank Subcol 2 DBS2(A.p) S-1 (A.p) Subcol 3 ZTS(L) JE (L) Subrow 3 Blank J-1 (A.p) LY (L) Subrow 4 Blank S-2 (A.p) DX6(A.p) Subcol 4 YN (L) J5 (L) GXLF (L) DY (L) Subcol 5 TK (At.f) FTH(L) Subcol 6 F4 (At.f) F6 (At.f) Subcol 7 23270(At.f) F1 (At.f) BY(L) YN (At.f) F2 (At.f) Y17(L) BY (At.f) F3 (At.f) Those labeled ‘’ own detectable hybridization signal, while those labeled ‘’ have no hybridization signal. Explanation of the hybridization signal from target DBS2, S-1, and J-1 should be made, as they are claimed to be Acidiphilium. In theory, bacteria strains of Acidiphilium should not be hybridized with DNA from bacteria of Acidithiobacillous Ferroxidan, as the target DNA are the genomic DNA that are longer than 20kb (about 23 kb), DNA molecule as long as that should be well enough to ensure the hybridization specificity. One possible reason for the signal here is that the Acidiphilium S-1, J-1 and DBS2 are not pure cultures, that is, the target prepared using DNA of the three bacteria above contains DNA molecule of Acidithiobacillous Ferroxidans. Maybe the isolation of these bacteria failed to obtain a pure culture. Evidence for the hypothesis here is that there has been report suggesting that bacteria Acidiphilium and Acidithiobacillous Ferroxidans are closely related in environment, their metabolic functions promotes each other, thus it is unlikely that the pure isolation of Acidiphilium could be obtained through conventional isolation strategy. So the signal detected from bacteria S-1, J-1 and DBS2 may still be the result of hybridization of our sample probe with Acidithiobacillous Ferroxidans DNA that are extracted simultaneously with the Acidiphilium in the same culture and planted onto the surface of the chip. 4.3.3 Evaluation of quantitative potential In order to evaluate the quantitative potential of the CGA fabricated, the signal intensity of hybridization result image is obtained through software Genepix Pro 6.0. The microarray A, B, C and D were hybridized with probe concentration 115ng/µl, 11.5ng/µl, 1.15ng/µl and 0.115ng/µl, respectively. The data of four chips are collected and sorted out respectively. The comparison of data is made between the same bacteria species hybridized at different probe concentration. That is, we collected the data lengthways and the data is compared transverse to produce reliable and intuitionistic result. There are 10 identical subarrays on each slide, that is, each of the target has ten replicates in order to produce statistical data (though the data that departed too much from the average value are neglected). We calculated the average signal intensity of each bacteria strain and the result is listed in Table 4.3: Besides, standard deviance and the log value of each of the signal intensity are also calculated; the log value of 19 中南大学本科论文 第 4 章 数据处理与结果讨论 the average signal intensity is obtained for the purpose of successive construction work. Table 4.3 Signal intensity of each bacteria strain Column Row Name Average Average Intensity Average Intensity Average Intensity Intensity for for chip A for chip B for chip C chip D 1 1 23270 9930.6 7466.875 1940.5 182.75 2 1 F1(At.f) 13157.3 10373.625 3736.11 274.625 3 1 F2(At.f) 11134.78 8081.875 2422.125 242.625 4 1 F3(At.f) 17573.56 15846.125 5219.375 548.5 1 2 F4(At.f) 9014 6961.75 2063.9 176 2 2 F6(At.f) 9698.44 7748.125 2264.4 185 3 2 YN(At.f) 11809.33 10460.75 4402.89 544.25 4 2 BY (At.f) 14193.78 12027.75 4014.4 345.625 1 3 TK(At.f) 6881.11 4939.875 1404 117.125 2 3 FTH(L) 86.33 41 15.8 6.875 3 3 BY(L) 198.5 122.86 37.4 10.375 4 3 Y17(L) 44.6 35 12.5 8.375 1 4 YN(L) 47.4 28.7 12.8 5.5 2 4 J5(L) 24.2 20.3 8.2 9 3 4 GXLF(L) 19.8 18 7.6 5.9 4 4 DY(L) 31.4 26.7 12.3 8 1 5 ZTS(L) 10.6 12.8 9.9 4.4 2 5 JE(L) 22.5 19 5.2 6.9 3 5 LY(L) 15.6 15.4 5.3 5.9 4 5 DX6(A.p) 822.4 690.9 225.5 16.25 1 6 DBS2(A.p) 10278.22 8278.143 2274.7 158.375 2 6 S-1(A.p) 12041.67 7796.9 2125.7 2068.78 3 6 J-1(A.p) 4205.78 3174.8 849.5 1070.75 4 6 S-2(A.p) 89.3 20.3 10.8 7.375 1 7 blank 11.3 9.2 6.2 6.2 2 7 blank 5.3 5.9 5.4 4.9 3 7 blank 6.7 6.2 5 3.1 4 7 blank 4.3 3.7 3.8 3.8 Through the data listed above, we can easily discover that the signal intensity reduce as the concentration of probe DNA reduce. This table also can be used to demonstrate the specificity of CGA, as the signal intensity for Leptospirillum is magnificently fewer than that of Acidithiobacillous Ferroxidans (the signal for Acidiphilium is explained in 4.3.2). After obtaining these data, we use the log value of hybridization signal intensity and the log value of probe DNA amount to from data pairs (X, Y). These spots are then placed in coordinates for the purpose of checking CGA quantitative potential. Because there are 9 Acidithiobacillous Ferroxidans on the 20 中南大学本科论文 第 4 章 数据处理与结果讨论 4.2 4.4 4.0 4.2 3.8 4.0 3.6 3.8 Log Signal Intensity Log Siganl Intensity chip, and the probe DNA is from strain TK, which is also within this species, all 9 series of data pairs are sorted and portrayed from Figure 4.4 to Figure 4-12: 3.4 3.2 3.0 2.8 3.6 3.4 3.2 3.0 2.6 2.8 2.4 2.6 2.2 2.4 2.0 2.2 -1.0 -0.5 0.0 0.5 1.0 Log DNA amount/ng (1) 23270 2 r =0.91 p<0.05 1.5 2.0 -1.0 2.5 -0.5 0.0 0.5 1.0 Log DNA amount/ng (2) F1 1.5 2.0 2.5 1.5 2.0 2.5 2 r =0.87 p<0.07 Figure 4.4 Figure 4.5 4.8 4.4 4.6 4.2 4.4 4.2 3.8 Log Signal Intensity Log Signal Intensity 4.0 3.6 3.4 3.2 3.0 4.0 3.8 3.6 3.4 3.2 2.8 3.0 2.6 2.8 2.4 2.6 2.2 -1.0 -0.5 0.0 0.5 1.0 Log DNA amount/ng (3) F2 1.5 2.0 2.5 2 2.4 -1.0 -0.5 0.0 0.5 1.0 Log DNA amount/ng (4) F3 2 r =0.91 p<0.05 r =0.89 p<0.06 Figure 4.6 Figure 4.7 21 第 4 章 数据处理与结果讨论 4.2 4.2 4.0 4.0 3.8 3.8 3.6 Log Signal Intensity Log Signal Intensity 中南大学本科论文 3.4 3.2 3.0 3.6 3.4 3.2 3.0 2.8 2.8 2.6 2.6 2.4 2.4 2.2 2.2 2.0 2.0 -1.0 -0.5 0.0 0.5 1.0 Log DNA amount/ng (5) F4 1.5 2.0 -1.0 2.5 -0.5 2 r =0.89 p<0.06 Figure 4.8 0.0 0.5 1.0 Log DNA amount/ng (6) F6 2 r =0.89 p<0.06 1.5 2.0 2.5 2.0 2.5 Figure 4.9 4.6 4.4 4.4 4.2 4.2 4.0 3.8 Log Signal Intensity Log Signal Intensity 4.0 3.6 3.4 3.2 3.8 3.6 3.4 3.2 3.0 3.0 2.8 2.6 2.8 2.4 2.6 2.2 -1.0 -0.5 0.0 0.5 1.0 1.5 2.0 -1.0 2.5 Log DNA amount/ng (7) YN 2 r =0.86 p<0.08 -0.5 0.0 0.5 1.0 Log DNA amount/ng (8) BY 2 r =0.87 p<0.07 Figure 4.10 Figure 4.11 22 1.5 中南大学本科论文 第 5 章 结论 4.0 3.8 Log Signal Intensity 3.6 3.4 3.2 3.0 2.8 2.6 2.4 2.2 2.0 1.8 -1.0 -0.5 1.0 0.5 0.0 Log DNA amount/ng (9) TK 1.5 2.0 2.5 2 r =0.91 p<0.05 Figure 4.12 Figures above shows the relationship of the intensity of hybridization signal and the corresponding probe DNA concentration. The log value of signal intensity data is calculated and the standard deviances are shown in the figures above. Although some of the point showed remarkable deviance, the trends of increase in signal intensity with the increase of probe concentration of the 9 strains of bacteria are nearly identical. Linear regression results suggest that the CGA we fabricated is potentially quantitative. Figure 4.11 shows the linear regression result of bacteria TK hybridized with DNA of itself (r2=0.91 p<0.05) and thus is the most representative one in demonstrating the quantitative potential of the CGA to detect pure DNA sample. Chapter 5 Conclusion The capability of the CGA we fabricated is examined in terms of sensitivity, specificity and quantitative potential. Analysis of the results suggests that the CGA fabricated is capable of detecting sample DNA as little as 0.11ng while still possessing good specificity. All of the hybridization of target DNA with DNA from bacteria TK are in the species Acidithiobacillous Ferrooxidan except for J-1, S-1, and DBS-2, suggesting that the CGA fabricated is capable of differentiating bacteria in the species level. The hybridization signal observed in target J-1, S-1, and DBS-2 may because of the culture from where the target DNA were extracted is not pure itself, as there have been report claiming that bacteria Acidiphilium and Acidithiobacillous Ferrooxidan are closely related in natural environment and it is extremely difficult to isolate the pure culture of Acidiphilium. Thus, the hybridization signal observed between probe DNA and J-1, S-1, and DBS-2 should still be brought by hybridization 23 中南大学本科论文 第 5 章 结论 occurred between the probe DNA and the DNA of Acidithiobacillous Ferrooxidan mixed in the above Acidiphilium bacteria. More stringent hybridization condition (such as higher hybridization temperature and longer washing time) may further enhance the resolution of the CGA and makes it possible for the CGA to detect different strains of bacteria. The fact that the target DNA of bacteria TK did not prove to be show the strongest fluorescent signal as we expected may because of the lower DNA concentration of the TK target printed on the chip. Dying result using Sybr Green (Figure 5.1) proves that the target of TK possess fewer amount of DNA than other bacteria target, the picture also explains the strong signal intensity of target YN, because the target itself contains remarkably more amount of DNA. Target TK Target YN Figure 5.1 Target DNA concentration check Target DNA concentration is checked through dying using Sybr Green (trade name), spots with light yellow color indicate fewer DNA and spots in brown or red indicate more amount of DNA. The target DNA of TK is lower than the other bacteria of Acidithiobacillous Ferrooxidan in concentration. Bacteria target YN possesses the highest DNA concentration. This explains why YN is always the one that shows strongest hybridization signal. The above result suggests that the quantitation of DNA concentration for the preparation of target is of magnificent importance. Hybridization result will be more representative and reliable when the target DNA concentrations are uniform. Considering quantitative potential, the analysis of hybridization signal intensity data produced by different probe DNA concentration has provided evidence for the quantitative potential of the CGA. In total, the construction of CGA is successful: high sensitivity has enhanced its capability to detect minor species in environmental sample. Species level resolution will remarkably reduce cross-hybridization, and the resolution still have the potential to be improved to strain level by changing hybridization conditions, more stringent hybridization will wash off the probe combined to the less homologous target while correct hybridization will stay because the combination is more stable. The quantitativity of the CGA can provide useful in determining the relative abundance of detectable species in environmental sample. The quantitation potential of CGA may be further determined through analysis of more parallel data, that is, we can obtain probe DNA concentration of 300ng/µl, 250ng/µl, 200ng/µl, 150ng/µl, 100ng/µl, 50ng/µl, 20ng/µl, and 10ng/µl through condensation and dilution to form a more complex concentration gradient. Thus, we will be able to obtain a lot more detailed data about the influence of probe DNA 24 中南大学本科论文 致谢及参考文献 concentration on hybridization signal intensity. One weakness of the CGA fabricated is the lack of richness of species diversity, but this could be compensated by later on isolation and cultivation of various bacteria. The bacteria DNA we extracted are stored at –20ºC, thus these sample can still be used to fabricate new chips, once new isolation or cultivation is obtained, its genomic DNA can instantly be applied in CGA fabricating, the richness of target genomic DNA will be expanded continually. Besides, methods such as utilizing BACs to obtain genomic DNA of uncultivated species have offered new strategy in CGA fabrication. The limitations of CGA application will be impaired and CGA will work its full power in research toward various environmental applications. Acknowledgement The experimenting process, including the inoculation and cultivation of bacteria, DNA extraction and concentration adjusting, microarray fabrication and successive testing and examining, lasted for more than four months. The authur wish to thank professor Liu xueduan for his continous guiding throughout the whole period and docter Gao Jian, master Zhang Yanfei for offering the bacteria isolations. I sincerely thank graduate student Chen Qijiong and other graduate students for the cooperation in the whole experimenting process. Besides, teachers in our laboratory have also helped me a lot in inquiring and instructing experimental instruments manipulation. In the end, I also thank my classmates for sharing a happy and meaningful time in the last semester of undergraduate year in Central South University. References: 1.Brett J. Baker, Jillian F. Banfield Microbial communities in acid mine drainage [J]. FEMS Microbiology Ecology, 2003, 44, 139-152 2.席劲英,胡洪营,钱易.Biolog方法在环境微生物群落研究中的应用 [J]. 微生物学报, 2003,43:138-141 3.Schrenk, M.O., Edwards, K.J., Goodman, R.M., Hamers, R.J. and Banfield, J.F. (1998) Distribution of Thiobacillus ferrooxidans and Leptospirillum ferrooxidans: implications for generation of acid mine drainage. [J] Science 279, 1519^1522. 4.Edwards, K.J., Gihring, T.M. and Banfield, J.F. (1999) Seasonal variations in microbial populations and environmental conditions in an extreme acid mine environment. [J]Appl. Environ. Microbiol. 65, 3627^3632. 5.Eric E. Allen* and Jillian F. Banfield COMMUNITY GENOMICS IN MICROBIAL ECOLOGY AND EVOLUTION [J]. Nature. 2005, volume 3, 489-498 6.Jizhong Zhou. Microarrays for bacterial detection and microbial community analysis [J]. Current Opinion in Microbiology 2003, 6:288–294 7.Jizhong Zhou, Xueduan Liu et al. Development and Evaluation of Micro-array-Based Whole-Genomoe Hybridizatin for Detection of Microorganisms within the Context of Environmental Applications. [J] Environmental Science & Technology, 2004 38, 6775-6782 8.刘学端, 肖启明等. 基因芯片在环境微生物研究中的应用. [J] 微生物学通报, 2004, 44,406-410 9.McCaig, A.E., Glover, A. and Prosser, J.I. (1999) Molecular analysis of bacterial community structure and diversity in unimproved and improved upland grass pastures. Appl. Environ. Microbiol. 65, 1721^1730. 10. Mark Schena 等著, 张亮等译 . [M] . 北京 .科学出版, 2004 25 中南大学本科论文 参考文献 11.HU HONG-YING, TONG ZHONG-HUA. Bacterial quinone profile for the study of microbial community structure in environmental samples [J]. Microbiology, 2002, 29(4): 95-98. 12. GLUCKSMAN A M, SKIPPER H D, BRIGMON R L, et al. Use of the MIDI-FAME technique to characterize groundwater communities [J]. Journal of Applied Microbiology, 2000, 88: 711-719. 13. GRIFFITHS B S, RITZ K, GLOVER L A, et al. Broad-scale approaches to the determination of soil microbial community structure: application of the community DNA hybridization technique [J]. Microbial Ecology, 1996, 31:269-280. 14. TORSVIK V, GOSKYR J, DAAE F L. High diversity in DNA of soil bacteria[J]. Applied Environmental Microbiology, 1990, 56:782-787. 15.Murphy D. Gene expression studies using microarrays:priciples, problems and prospects [J] Adv Physiol Educ,2002,26(4):256-270. 16.Meltzer P S.Spotting the target:microarrays for disease gene discovery. [J] Current Opinion Genetic Development, 2001, 11(3):258-263 17. Silverman, M.P. and Ehrlich, H.L. (1964) Microbial formation and degradation of minerals. In: Advances in Applied Microbiology (Umbreit, W.W., Ed.), Vol. 6, pp. 153^206. Academic Press, New York. 18. Druschel, G.K., Baker, B.J., Gihring, T. and Ban¢eld, J.F. Acid mine drainage biogeochemistry at Iron Mountain, California, in review. 19. INSAM H. A new set of substrates proposed for community characterization in environmental samples[A]. In: INSAM H, RANGGER A, Eds. Microbial Communities[C]. Heidelberg: Springer, 1997: 259-260. 20. Chandler, D.P., Brockman, F.J., Bailey, T.J. and Fredrickson, J.K. (1998) Phylogenetic diversity of archaea and bacteria in a deep subsurface paleosol. Microbiol. Ecol. 36, 37^50. 21. Bond, P.L. and Ban¢eld, J.F. (2001) Design and performance of rRNA targeted oligonucleotide probes for in situ detection and phylogenetic identification of microorganisms inhabiting acid mine drainage environments. Microbial Ecol. 41, 149^161. 22. Isolation and phylogenetic characterization of acidophilic microorganisms indigenous to acidic drainage waters at an abandoned Norwegian copper mine. Environ. Microbiol. 3, 630^637. 23. Baker, B.J., Hugenholtz, P., Dawson, S.C. and Banfield, J.F. A novel protist/bacteria symbiotic relationship in acid mine drainage, in preparation. 24. Kishimoto, N., Kosako, Y. and Tano, T. (1991) Acidobacterium capsulatum gen. nov., sp. nov.: an acidophilic chemoorganotrophic bacterium containing menaquinone from acidic mineral environment. Curr. Microbiol. 22, 1^7. 25. Lutz, M., Bond, P.L. and Ban¢eld, J.F. (2001) Fungi in acid mine drainage communities at Iron Mountain, CA. Senior thesis. University of Wisconsin, Madison, WI. 26.Bond, P.L., Druschel, G.K. and Ban¢eld, J.F. (2000) Comparison of acid mine drainage microbial communities in physically and geochemically distinct ecosystems. Appl. Environ. Microbiol. 66, 4962^4971. 27.马立人, 蒋中华. 生物芯片 [M]. 北京: 化学工业出版社 , 2002 ,1 – 43 28.阎章才, 东秀珠. 微生物的生物多样性及应用前景.[J] 微生物学通报, 2001, 28(1):96~102 29. Wu L, Thompson D, Li G, Hurt RA, Tiedje JM, Zhou J: Development and evaluation of functional gene arrays for detection of selected genes in the environment. Appl Environ Microbiol 2001, 67:5780-5790. 30. Murray AE, Lies D, Li G, Nealson K, Zhou J, Tiedje JM: DNA–DNA hybridization to microarrays reveals gene-specific differences between closely related microbial genomes. Proc Natl Acad Sci USA 2001, 98:9853-9858. 31. Salama N, Guillemin K, McDaniel TK, Sherlock G, Tompkins L, Falkow S: A whole-genome microarray reveals genetic diversity among Helicobacter pylori strains. Proc Natl Acad Sci USA 2000, 97:14668-14673. 26 中南大学本科论文 32.Guschin DY, 参考文献 Mobarry BK, Proudnikov D, Stahl DA, Rittmann BE, Mirzabekov AD: Oligonucleotidemicrochips as genosensors for determinative and environmental studies in microbiology. Appl Environ Microbiol 1997, 63:2397-2402. 33. Debouck, C., and P. N. Goodfellow. 1999. DNA microarrays in drug discovery and development: progress and potential. Biochem. Pharmacol. 62:1311–1336. 34.Kane, M. D., T. A. Jatkoe, C. R. Stumpf, J. Lu, J. D. Thomas, and J. M. Madore. 2000. Assessment of the specificity and sensitivity of oligonucleotide (50mer) microarrays. Nucleic Acids Res. 28:4552–4557. 35.Rhee, S. K., X. Liu, L. Wu, S. C. Chong, X. Wan, and J. Zhou. 2004. Detection of biodegradation and biotransformation genes in microbial communities using 50-mer oligonucleotide microarrays. Appl. Environ. Microbiol. 70:4303–4317. 36.Shchepinov, M. S., S. C. Case-Green, and E. M. Southern. 1997. Steric factors influencing hybridization of nucleic acids to oligonucleotide arrays. Nucleic Acids Res. 25:1155–1161. 37.Zhou, J., M. A. Bruns, and J. M. Tiedje. 1996. DNA recovery from soils of diverse composition. Appl. Environ. Microbiol. 62:461–468. 38. Zhou, J., and D. K. Thompson. 2002. Challenge in applying microarrays to environmental studies. Curr. Opin. Biotechnol. 13:204–207. 27