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CN106399303A - Host-enteric microbial interacting gene-based specific molecular marker 1-38 and detection method for pollution by excrement of pig - Google Patents

Host-enteric microbial interacting gene-based specific molecular marker 1-38 and detection method for pollution by excrement of pig Download PDF

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CN106399303A
CN106399303A CN201610845794.0A CN201610845794A CN106399303A CN 106399303 A CN106399303 A CN 106399303A CN 201610845794 A CN201610845794 A CN 201610845794A CN 106399303 A CN106399303 A CN 106399303A
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帅江冰
傅玲琳
张晓峰
莫虹斐
曾若雪
何永强
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ZHEJIANG ENTRY-EXIT INSPECTION AND QUARANTINE BUREAU
Zhejiang Gongshang University
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Abstract

本发明涉及猪粪便污染物检测领域,尤其涉及一种基于宿主‑肠道微生物互作基因的猪粪便污染特异性分子标记1‑38及其检测方法。本发明采用竞争性杂交基因片段富集方法(GFE)富集猪特异性宏基因组,构建宏基因文库,对文库进行序列菌群及功能分类,从而靶向筛选了宿主(猪)‑肠道微生物互作靶点有关特异性基因,并针对猪特异性互作基因设计分子标记,建立了灵敏度高、特异性强并能高效指示粪便污染源的监测方法。

The invention relates to the field of detection of pig feces pollutants, in particular to a pig feces pollution-specific molecular marker 1-38 based on a host-intestinal microorganism interaction gene and a detection method thereof. The present invention adopts the method of competitive hybrid gene fragment enrichment (GFE) to enrich the pig-specific metagenome, constructs the metagenome library, and classifies the library with sequence flora and function, thereby targeting and screening the host (pig)-intestinal microorganisms Interaction targets are related to specific genes, and molecular markers are designed for pig-specific interaction genes, and a monitoring method with high sensitivity, strong specificity, and efficient indication of fecal pollution sources has been established.

Description

一种基于宿主-肠道微生物互作基因的猪粪便污染特异性分 子标记1-38及其检测方法A specific analysis of pig fecal contamination based on host-gut microbe interaction genes Submarkers 1-38 and detection methods thereof

技术领域technical field

本发明涉及猪粪便污染物检测领域,尤其涉及一种基于宿主-肠道微生物互作基因的猪粪便污染特异性分子标记1-38及其检测方法。The invention relates to the field of detection of pig feces pollutants, in particular to a specific molecular marker 1-38 for pig feces pollution based on a host-intestinal microorganism interaction gene and a detection method thereof.

背景技术Background technique

猪肉制品作为深受国内消费者喜爱的肉制品之一,其庞大的需求量导致生猪产业迅猛发展。据农业部统计,我国生猪出栏量近年来一直占世界第一,占比维持在56%左右,并保持增长态势。由于缺乏对迅猛发展的集约化畜禽养殖业排放的有效管理,猪等畜禽粪便及其污水多以非点源的方式进入环境,引发污染并诱发健康威胁。猪粪便排泄物中不仅含有大量的病原微生物菌(戊型肝炎病毒、沙门氏菌(Salmonella)、李斯特菌(Listeria)、空肠弯曲菌(Campylobacter spp.),直接威胁到人类健康,而且含有氮,磷等物质,未经有效处理任意排放,会造成土壤,地下水,地表水及灌溉水的污染,并使水体富营养化,进而导致水产品蓄积大量的有害物质,影响水产品品质。因此,建立一种灵敏度高、特异性强并能高效指示粪便污染源的监测方法显得尤为迫切。Pork products are one of the most popular meat products among domestic consumers, and their huge demand has led to the rapid development of the pig industry. According to the statistics of the Ministry of Agriculture, the number of live pigs slaughtered in my country has always ranked first in the world in recent years, accounting for about 56% and maintaining a growth trend. Due to the lack of effective management of the rapid development of the intensive livestock and poultry farming industry, the manure of pigs and other livestock and poultry and their sewage mostly enter the environment in the form of non-point sources, causing pollution and health threats. Pig feces not only contain a large number of pathogenic microorganisms (Hepatitis E virus, Salmonella, Listeria, Campylobacter spp.), which directly threaten human health, but also contain nitrogen, phosphorus Such substances, if discharged without effective treatment, will cause soil, groundwater, surface water and irrigation water pollution, and eutrophication of water bodies, which will lead to the accumulation of a large amount of harmful substances in aquatic products and affect the quality of aquatic products. Therefore, the establishment of a It is particularly urgent to develop a monitoring method with high sensitivity, strong specificity and high efficiency to indicate the source of fecal contamination.

有研究从宿主粪便源菌群如厚壁菌门(Frimicutes)、双歧杆菌属(Bifidobacteria spp)、史氏产甲烷杆菌(Methanobrevibacter smithii)等的16S rRNA和毒力基因等筛选标签来判别污染来源。目前已鉴定的猪特异性分子标记大多基于猪肠道优势菌16S rRNA的保守区。也有从粪便中线粒体DNA、大肠埃希菌中筛选毒力基因[来判断猪粪便污染来源。然而,尽管上述特异性分子标记具有一定的特异性和灵敏性,但存在较大的局限性:1)宿主特异性不够高,2)不同宿主间存在交叉反应性,3)有地理地域差异性,4)判别动物来源的精确性不够高,因此会带来较高的错判率。Some studies have identified the source of contamination from the screening tags of 16S rRNA and virulence genes of host fecal-derived flora such as Frimicutes, Bifidobacteria spp, Methanobrevibacter smithii, etc. . Most of the identified porcine-specific molecular markers are based on the conserved region of 16S rRNA of dominant porcine intestinal bacteria. There are also screening of virulence genes from mitochondrial DNA and Escherichia coli in feces to determine the source of pig feces contamination. However, although the above-mentioned specific molecular markers have certain specificity and sensitivity, there are major limitations: 1) host specificity is not high enough, 2) there is cross-reactivity among different hosts, 3) there are geographical differences , 4) The accuracy of judging the source of animals is not high enough, so it will bring a high rate of misjudgment.

肠道微生物群落与其宿主是共同进化的,经宿主和肠道微生物之间强烈选择和协同进化可形成宿主-微生物相互作用的对宿主有益的功能保留区(互作靶点),这些互作靶点是形成肠道微生物多样性及特异性的重要因素。因此越来越多的研究从人、牛、鸡等的肠道微生物群落中筛选宿主-微生物互作基因作为宿主特异性分子标记,并证明此类分子标记具有较高的特异性和灵敏性。然而,目前尚未见以宿主-微生物互作基因作为特异性分子标记进行水体或食品中猪粪便非点源污染示踪的相关研究。The intestinal microbial community and its host are co-evolved, and the strong selection and co-evolution between the host and the intestinal microbes can form host-microbe interactions that are beneficial to the host. Points are an important factor in the formation of intestinal microbial diversity and specificity. Therefore, more and more studies have screened host-microbe interaction genes as host-specific molecular markers from the intestinal microbial communities of humans, cattle, and chickens, and proved that such molecular markers have high specificity and sensitivity. However, there are no related studies on the use of host-microbe interaction genes as specific molecular markers to trace non-point source pollution of pig feces in water or food.

发明内容Contents of the invention

为了解决上述的技术问题,本发明的一个目的是提供一种基于宿主-肠道微生物互作基因的猪粪便污染特异性的分子标记1-38,本发明的另外一个目的是提供采用上述的分子标记1-38的检测方法,本发明针对猪特异性互作基因设计分子标记,建立了灵敏度高、特异性强并能高效指示粪便污染源的监测方法。In order to solve the above-mentioned technical problems, one object of the present invention is to provide a specific molecular marker 1-38 based on the host-intestinal microorganism interaction gene for pig feces pollution. Another object of the present invention is to provide For the detection method of markers 1-38, the present invention designs molecular markers for pig-specific interaction genes, and establishes a monitoring method with high sensitivity, strong specificity, and efficient indication of feces pollution sources.

为了实现上述的第一个目的,本发明采用了以下的技术方案:In order to achieve the above-mentioned first purpose, the present invention adopts the following technical solutions:

一种基于宿主-肠道微生物互作基因的猪粪便污染特异性分子标记1-38,其该分子标记由以下的引物和探针构成:A pig feces pollution-specific molecular marker 1-38 based on host-intestinal microorganism interaction genes, which consists of the following primers and probes:

上游引物:GGAGGTGGTTAAGCCGATATGTTUpstream primer: GGAGGTGGTTAAGCCGATATGTT

下游引物:GCCCCTTTCTTGATACTTTGGADownstream primer: GCCCCTTTCTTGATACTTTGGA

探针:Fam-AAACTGATTGGAGAAGAATACAGGCG-Tam。Probe: Fam-AAACTGATTGGAGAAGAATACAGGCG-Tam.

为了实现上述的第二个目的,本发明采用了以下的技术方案:In order to achieve the above-mentioned second purpose, the present invention adopts the following technical solutions:

一种基于宿主-肠道微生物互作基因的猪粪便污染的检测方法,该方法采用所述的引物和探针与被检测样品混合,进行荧光PCR反应,在每个循环延伸结束后读数;样品无Ct值并且无扩增曲线,表示样品中无猪粪便污染;样品扩增Ct值≤35,且出现典型的扩增曲线,表示样品中存在猪粪便污染;样品Ct值>35的样本建议重做,重做结果无Ct值者为阴性,否则为阳性。A method for detecting pig feces contamination based on host-intestinal microorganism interaction genes, the method uses the primers and probes to be mixed with the sample to be tested, performs a fluorescent PCR reaction, and reads after each cycle of extension; the sample No Ct value and no amplification curve, indicating that there is no pig feces contamination in the sample; sample amplification Ct value ≤ 35, and a typical amplification curve appears, indicating that there is pig feces contamination in the sample; samples with Ct value > 35 are recommended to repeat If there is no Ct value, it is negative, otherwise it is positive.

作为优选,所述的引物和探针浓度分别为0.25μM和0.3μM。Preferably, the concentrations of the primers and probes are 0.25 μM and 0.3 μM respectively.

作为优选,所述的荧光PCR反应条件为:95℃预变性30s,40个循环的95℃变性5s和60℃退火延伸30s。Preferably, the fluorescent PCR reaction conditions are: pre-denaturation at 95°C for 30s, 40 cycles of denaturation at 95°C for 5s and annealing at 60°C for 30s.

本发明采用竞争性杂交基因片段富集方法(GFE)富集猪特异性宏基因组,构建宏基因文库,对文库进行序列菌群及功能分类,从而靶向筛选了宿主(猪)-肠道微生物互作靶点有关特异性基因,并针对猪特异性互作基因设计分子标记,建立了灵敏度高、特异性强并能高效指示粪便污染源的监测方法。The present invention adopts the method of competitive hybridization gene fragment enrichment (GFE) to enrich the pig-specific metagenome, constructs the metagenome library, and classifies the sequence flora and function of the library, thereby targeting and screening the host (pig)-intestinal microorganisms Interaction targets are related to specific genes, and molecular markers are designed for pig-specific interaction genes, and a monitoring method with high sensitivity, strong specificity, and efficient indication of fecal pollution sources has been established.

附图说明Description of drawings

图1为分子标记1-38荧光PCR检测图谱。Figure 1 is a fluorescent PCR detection map of molecular marker 1-38.

图2为分子标记3-53荧光PCR检测图谱。Figure 2 is a fluorescent PCR detection map of the molecular marker 3-53.

图3为分子标记1-38荧光PCR体系的标准曲线及扩增效率图。Fig. 3 is a standard curve and amplification efficiency diagram of the molecular marker 1-38 fluorescent PCR system.

图4为分子标记3-53荧光PCR体系的标准曲线及扩增效率图。Fig. 4 is a standard curve and amplification efficiency diagram of the molecular marker 3-53 fluorescent PCR system.

图5为分子标记1-38荧光PCR批间稳定性试验图。Fig. 5 is a diagram of the inter-batch stability test of molecular marker 1-38 fluorescent PCR.

图6为分子标记3-53荧光PCR批间稳定性试验图。Fig. 6 is a diagram of the inter-batch stability test of molecular marker 3-53 fluorescent PCR.

具体实施方式detailed description

下面结合附图对本发明的具体实施方式做一个详细的说明。The specific implementation manner of the present invention will be described in detail below in conjunction with the accompanying drawings.

实施例1特异性猪-肠道微生物互作基因的富集筛选Example 1 Enrichment screening of specific pig-intestinal microorganism interaction genes

1.1共采集6个物种145个粪便样品,其中包括猪粪便样品34个、奶牛牛粪便样品20份、山羊粪便样品12份、绵羊粪便样品8份,鸡粪便样品7份、鸭粪便样品20份、鹅粪便样品5份和人粪便样品13份。将样品置于无菌容器中,每200mg(湿重)样品中加入3mL GITC缓冲液(5M异硫氰酸胍、100Mm EDTA(pH 8.0)、十二烷基肌氨酸钠),低温保存。粪样DNA的提取按 Fast DNA Stool Kit(Qiagen,Valencia,CA)说明书进行。并在紫外分光光度计NanoDrop ND-2000UV上测定其浓度和纯度(NanoDrop Technologies,Thermofisher)。1.1 A total of 145 feces samples from 6 species were collected, including 34 swine feces samples, 20 cow feces samples, 12 goat feces samples, 8 sheep feces samples, 7 chicken feces samples, 20 duck feces samples, Five goose feces samples and 13 human feces samples were collected. Place the sample in a sterile container, add 3mL GITC buffer (5M guanidine isothiocyanate, 100Mm EDTA (pH 8.0), sodium lauryl sarcosine) to every 200mg (wet weight) sample, and store it at low temperature. DNA extraction from feces Fast DNA Stool Kit (Qiagen, Valencia, CA) instructions. And its concentration and purity were determined on a UV spectrophotometer NanoDrop ND-2000UV (NanoDrop Technologies, Thermofisher).

1.2宿主(猪)特异性基因组富集(GFE)1.2 Host (pig) specific genome enrichment (GFE)

将所有单个猪源样品基因组DNA混合形成基因组混合库以增加基因组的多样性(待富集组),以牛、羊、鸡、鸭、鹅等其它物种样品基因组混合库作为对照组。Genomic DNA of all single pig source samples was mixed to form a genomic mixed library to increase the diversity of the genome (group to be enriched), and the genomic mixed library of cattle, sheep, chicken, duck, goose and other species samples was used as a control group.

1.2.1富集组DNA的准备1.2.1 Preparation of enriched DNA

将待富集组又分为两个组(待富集组A和B)。The group to be enriched was further divided into two groups (groups to be enriched A and B).

A组DNA的准备:将DNA声波震荡裂解后以Klenow I聚合酶标记上K9标签;被K9标签标记的DNA片段用 Multiwell PCR Purification Kit(Qiagen,Valencia,CA)纯化并扩增以获得足够量的带有K9随机引物的DNA片段。Preparation of group A DNA: After the DNA was cleaved by sonic shock, the K9 tag was labeled with Klenow I polymerase; the DNA fragment labeled with the K9 tag was used Multiwell PCR Purification Kit (Qiagen, Valencia, CA) was purified and amplified to obtain a sufficient amount of DNA fragments with K9 random primers.

B组DNA的准备(生物素标记DNA片段):将DNA经声波降解后标记生物素(PAB,Sigma-Aldrich,Atlanta,GA)。Preparation of group B DNA (biotin-labeled DNA fragments): DNA was labeled with biotin (PAB, Sigma-Aldrich, Atlanta, GA) after sonication.

1.2.2DNA预杂交及竞争性杂交1.2.2 DNA prehybridization and competitive hybridization

将待富集组B与对照组DNA分别变性后进行预杂交,随后将此预杂交混合液与A组猪源DNA竞争性杂交后,形成各种组合的DNA双链。经生物素-链亲和素(Streptavidin)酶联免疫吸附捕获试验,将标记有生物素的杂交双链DNA(即至少含一条待富集组单链的双链DNA)捕获并扩增富集。终将获得高丰度的猪源特异性粪样基因组DNA样品。The DNA of the enriched group B and the control group were denatured and then pre-hybridized, and then the pre-hybridized mixture was competitively hybridized with the pig-derived DNA of group A to form DNA double strands in various combinations. Biotin-streptavidin (Streptavidin) ELISA capture assay captures biotin-labeled hybrid double-stranded DNA (that is, double-stranded DNA containing at least one single strand to be enriched) and amplifies and enriches . Ultimately, high-abundance porcine source-specific fecal genomic DNA samples will be obtained.

1.3构建宏基因组文库1.3 Construction of metagenomic library

将上述富集过程中每一轮的PCR产物经 Multiwel l PCRPurification Kit(Qiagen,Valencia,CA)进行纯化,按照pCR TOPO 4.0(Invitrogen)说明书将PCR纯化产物克隆至载体,并转入感受态大肠杆菌DH5α中。阳性克隆用含有有氨苄青霉素(50μg/mL)的LB固体培养基筛选获得,鉴定后随机挑选500个重组菌送上海生工股份有限公司进行测序。利用DNAstar对每轮所得序列进行拼接、筛选出382条猪源特异性非冗余序列,以构建宏基因组文库。The PCR products of each round in the above enrichment process were subjected to Multiwell l PCRPurification Kit (Qiagen, Valencia, CA) was used for purification, and the PCR purified product was cloned into a vector according to the instructions of pCR TOPO 4.0 (Invitrogen), and transformed into competent Escherichia coli DH5α. Positive clones were obtained by screening with LB solid medium containing ampicillin (50 μg/mL). After identification, 500 recombinant bacteria were randomly selected and sent to Shanghai Sangon Co., Ltd. for sequencing. DNAstar was used to assemble the sequences obtained in each round, and 382 pig-specific non-redundant sequences were screened to construct a metagenomic library.

1.4DNA序列分析1.4 DNA sequence analysis

在GeneBank数据库中利用BLASTX比对分析,根据相似序列的生物功能对每条非冗余序列进行蛋白质功能预测,其中E值≤10-3,识别率≥30%的序列被认为是相似蛋白序列。通过蛋白相邻类聚簇(COG)数据库将所得DNA序列进行功能基因分类。根据在GeneBank数据库BLASTX比对的结果(最小E值)对富集的非冗余序列进行菌群分类。最终筛选出60条与信息贮存与加工、细胞信息传导和代谢有关基因等可能的猪特异性互作靶点。In the GeneBank database, BLASTX analysis was used to predict the protein function of each non-redundant sequence according to the biological function of the similar sequence. Among them, sequences with E value ≤ 10 -3 and recognition rate ≥ 30% were considered similar protein sequences. The resulting DNA sequences were classified into functional genes by the clustering of neighboring classes (COG) database. The enriched non-redundant sequences were classified according to the results of BLASTX alignment in the GeneBank database (minimum E value). Finally, 60 possible pig-specific interaction targets related to information storage and processing, cell information transduction and metabolism were screened out.

1.5猪-微生物特异性互作基因的鉴定1.5 Identification of pig-microbe-specific interaction genes

分别针对60条可能的特异性互作靶点设计引物进行鉴定,结果表明其中基因1-38和基因3-53具有猪源特异性,而不能扩增其它物种的粪便DNA。The primers were designed for 60 possible specific interaction targets, and the results showed that genes 1-38 and genes 3-53 were pig-specific, but could not amplify fecal DNA of other species.

基因1-38:Genes 1-38:

AAATACTAATGGATAAAATAGAAATAATCTCCGGCAAACTCGGAATTGAGCACCGGAAGGTAGCCAACACCGTAAAACTGCTTGAAGATGGCGCTACAGTGCCATTTATCTCGCGATACCGCAAAGAAGCAACCGGCTCACTCGATGAAGTTGCCATCATGAATATCAGCACGCTCTTGGGACAACTCGAAGAATTGGACAAGAGGCGTCGTTACATCCTCGAAAGCATTGAGGCAAGCGGTGCCTTGACTCCGGAATTGAATTCACGCATTATGGTGTGCGATGATGCAACGACACTCGAGGATATCTACCTCCCATTCAAGCCCAAACGCCGCACCAAGGCGGAAGTGGCACGAAACAACGGTCTCGAACCGTTGGCAAAAATAATTATGGCACAAAAATCGATCGATATTCATTCTCAAGCCGGTCGTTTTATTGGGGAAAATGTGCCTGACGAA。AAATACTAATGGATAAAATAGAAATAATCTCCGGCAAACTCGGAATTGAGCACCGGAAGGTAGCCAACACCGTAAAACTGCTTGAAGATGGCGCTACAGTGCCATTTATCTCGCGATACCGCAAAGAAGCAACCGGCTCACTCGATGAAGTTGCCATCATGAATATCAGCACGCTCTTGGGACAACTCGAAGAATTGGACAAGAGGCGTCGTTACATCCTCGAAAGCATTGAGGCAAGCGGTGCCTTGACTCCGGAATTGAATTCACGCATTATGGTGTGCGATGATGCAACGACACTCGAGGATATCTACCTCCCATTCAAGCCCAAACGCCGCACCAAGGCGGAAGTGGCACGAAACAACGGTCTCGAACCGTTGGCAAAAATAATTATGGCACAAAAATCGATCGATATTCATTCTCAAGCCGGTCGTTTTATTGGGGAAAATGTGCCTGACGAA。

基因3-53:Gene 3-53:

AAATACTAATGGATAAAATAGAAATAATCTCCGGCAAACTCGGAATTGAGCACCGGAAGGTAGCCAACACCGTAAAACTGCTTGAAGATGGCGCTACAGTGCCATTTATCTCGCGATACCGCAAAGAAGCAACCGGCTCACTCGATGAAGTTGC CATCATGAATATCAGCACGCTCTTGGGACAACTCGAAGAATTGGACAAGAGGCGTCGTTACATCCTCGAAAGCATTGAGGCAAGCGGTGCCTTGACTCCGGAATTGAATTCACGCATTATGGTGTGCGATGATGCAACGACACTCGAGGATATCTACCTCCCATTCAAGCCCAAACGCCGCACCAAGGCGGAAGTGGCACGAAACAACGGTCTCGAACCGTTGGCAAAAATAATTATGGCACAAAAATCGATCGATATTCATTCTCAAGCCGGTCGTTTTATTGGGGAAAATGTGCCTGACGAA。AAATACTAATGGATAAAATAGAAATAATCTCCGGCAAACTCGGAATTGAGCACCGGAAGGTAGCCAACACCGTAAAA CTGCTTGAAGATGGCGCTACAGTGCCATTTATCTCGCGATACCGCAAAGAAGCAACCGGCTCACTCGATGAAGTTGC CATCATGAATATCAGCACGCTCTTGGGACAACTCGAAGAATTGGACA AGAGGCGTCGTTACATCCTCGAAAGCATTGAGGCAAGCGGTGCCTTGACTCCGGAATTGAATTCACGCATTATGGTGTGCGATGATGCAACGACACTCGAGGATATCTACCTCCCATTCAAGCCCAAACGCCGCACCAAGGCGGAAGTGGCACGAAACAACGGTCTCGAACCGTTGGCAAAAATAATTATGGCACAAAAATCGATCGATATTCATTCTCAAGCCGGTCGTTTTATTGGGGAAAATGTGCCTGACGAA。

实施例2分子标记的筛选和反应条件Screening and reaction conditions of embodiment 2 molecular markers

采用竞争性杂交基因片段富集(GFE)方法建立猪特异性DNA基因文库。将文库克隆至pCR TOPO 4.0后,随机选取500个克隆进行测序分析,共获得382条非冗余猪源特异性序列。经BLAXTS比对分析发现其中60条非冗余序列与拟杆菌群(Bacteroidetes)、梭状杆菌群(Clostridials)等表面蛋白、膜分泌蛋白及碳水化合物代谢蛋白等宿主-微生物互作蛋白有关,可作为猪特异性分子标记筛选的靶点。针对这60条基因设计分子标记,经筛选后发现其中两套可作为猪源粪便污染失踪的分子标记(表1)。A porcine-specific DNA gene library was established by competitive hybrid gene fragment enrichment (GFE). After the library was cloned into pCR TOPO 4.0, 500 clones were randomly selected for sequencing analysis, and a total of 382 non-redundant porcine-specific sequences were obtained. BLAXTS analysis found that 60 non-redundant sequences were related to host-microbe interaction proteins such as surface proteins such as Bacteroidetes and Clostridials, membrane secreted proteins, and carbohydrate metabolism proteins. As a target for porcine-specific molecular marker screening. Molecular markers were designed for these 60 genes, and after screening, two sets of molecular markers were found to be missing from pig-derived fecal contamination (Table 1).

表1分子标记序列Table 1 Molecular marker sequence

以阳性DNA为模板,多次重复性试验发现,分子标记1-38引物和探针浓度分别为0.2μM和0.3μM、3-53引物和探针浓度分别为0.25μM和0.3μM时,两套检测体系分别具有较高的扩增效率和敏感性。因此,20荧光PCR反应体系如下:Using positive DNA as a template, repeated experiments found that when the concentrations of molecular markers 1-38 primers and probes were 0.2 μM and 0.3 μM, and 3-53 primers and probes were respectively 0.25 μM and 0.3 μM, two sets of The detection system has high amplification efficiency and sensitivity respectively. Therefore, the 20 fluorescent PCR reaction system is as follows:

荧光PCR反应条件为:95℃预变性30s,40个循环的95℃变性5s和60℃退火延伸30s,在每个循环延伸结束后读数。图1为分子标记1-38荧光PCR检测图谱,图2为分子标记3-53荧光PCR检测图谱。样品无Ct值并且无扩增曲线,表示样品中无猪粪便污染;样品扩增Ct值≤35,且出现典型的扩增曲线,表示样品中存在猪粪便污染;样品Ct值>35的样本建议重做,重做结果无Ct值者为阴性,否则为阳性。The fluorescent PCR reaction conditions were: 95°C pre-denaturation for 30s, 40 cycles of 95°C denaturation for 5s and 60°C annealing extension for 30s, and read after each cycle of extension. Figure 1 is a fluorescent PCR detection map of molecular marker 1-38, and Figure 2 is a fluorescent PCR detection map of molecular marker 3-53. The sample has no Ct value and no amplification curve, indicating that there is no pig feces contamination in the sample; the sample amplification Ct value ≤ 35, and a typical amplification curve appears, indicating that there is pig feces contamination in the sample; samples with a Ct value > 35 are recommended Redo, redo result without Ct value is negative, otherwise it is positive.

实施例3标准曲线和体系重复性Example 3 standard curve and system repeatability

将1-38和分子标记3-53两种阳性DNA标准10倍倍比稀释至1.2×108至1.2×101拷贝/μl后分别进行荧光PCR反应,每个稀释度3个重复,绘制标准曲线计算扩增效率。结果表明两套分子标记均有较广的扩增线性范围和高扩增效率,分别为1.07和0.95(图3和图4)。同时,分子标记1-38和3-53的最低检测限分别为600拷贝/反应和60拷贝/反应,表明两套检测体系均具有良好的检测灵敏度。Dilute the two positive DNA standards 1-38 and molecular markers 3-53 10 times to 1.2×10 8 to 1.2×10 1 copies/μl, and then perform fluorescent PCR reactions respectively, with 3 repetitions for each dilution, and draw the standards The curve calculates the amplification efficiency. The results showed that the two sets of molecular markers had wide amplification linear ranges and high amplification efficiencies, which were 1.07 and 0.95, respectively (Fig. 3 and Fig. 4). At the same time, the minimum detection limits of molecular markers 1-38 and 3-53 were 600 copies/reaction and 60 copies/reaction, respectively, indicating that both detection systems had good detection sensitivity.

对倍比稀释的两种阳性标准DNA按荧PCR分别进行10个重复检测,分子标记1-38和3-53反应体系的Ct值标准差分别在0.01-0.28和0.03-0.76之间,变异系数均低于2.17%(表2),表明两套基于特异性分子标记的荧光PCR均具有很高的重复性。Perform 10 repeated detections on the two positive standard DNAs with multiple dilutions by fluorescent PCR. The standard deviations of the Ct values of the molecular marker 1-38 and 3-53 reaction systems were between 0.01-0.28 and 0.03-0.76, and the coefficient of variation Both are lower than 2.17% (Table 2), indicating that the two sets of fluorescent PCR based on specific molecular markers have high reproducibility.

表2两种分子标记荧光PCR体系重复性试验Table 2 Repeatability test of two molecular marker fluorescent PCR systems

实施例4批间稳定性试验Stability test between batches of embodiment 4

为分析两套分子标记荧光PCR方法的稳定性,分别进行4次独立检测,每次试验时将阳性标准DNA倍比稀释至1.2×108至1.2×101拷贝/μl,每个稀释度设置4个重复,计算不同稀释度平均CT值及4次独立试验的标准差。结果表明分子标记1-38和3-53荧光PCR体系均具有良好的检测稳定性,其不同批次间检测Ct值标准差分别仅为0.32-1.56和0.07-0.51(图5和图6)。In order to analyze the stability of the two sets of molecular marker fluorescent PCR methods, four independent tests were carried out, and the positive standard DNA was diluted to 1.2×10 8 to 1.2×10 1 copies/μl in each test, and each dilution was set Four repetitions were performed, and the average CT value of different dilutions and the standard deviation of four independent experiments were calculated. The results showed that the molecular markers 1-38 and 3-53 fluorescent PCR systems had good detection stability, and the standard deviations of the detection Ct values between different batches were only 0.32-1.56 and 0.07-0.51 (Figure 5 and Figure 6).

实施例5实际样品检测的宿主特异性和敏感性The host specificity and sensitivity of embodiment 5 actual sample detection

采集猪、奶牛、山羊、绵羊、鸡、鸭、鹅、狗和人粪便,提取DNA后对本发明中的猪特异性分子标记及其检测体系进行特异性(S)和敏感性验证(R)。荧光PCR反应体系和条件同上。并对检测结果按公式R=a/(a+b)和S=c/(c+d)计算,其中a和b分别代表分子标记针对特异性宿主的阳性样品数和假阴性样品数,c和d分别代表分子标记针对其它物种检测的阴性样品数和假阳性样品数。结果表明针对72份猪粪便样品或养殖场污水以及79份其它物种的粪便样品,分子标记1-38荧光PCR检测体系具有85%的宿主特异性和94%的宿主敏感性;3-53检测体系具有90%的宿主特异性和99%的宿主敏感性(表3),表明两套分子标记在实际应用中能高效特异的检测样品中是否含有猪粪便污染。Pig, cow, goat, sheep, chicken, duck, goose, dog and human feces are collected, DNA is extracted, and the specificity (S) and sensitivity verification (R) of the pig-specific molecular marker and its detection system in the present invention are performed. The fluorescent PCR reaction system and conditions are the same as above. And the detection result is calculated by the formula R=a/(a+b) and S=c/(c+d), wherein a and b represent the number of positive samples and the number of false negative samples of the molecular marker for the specific host respectively, and c and d represent the number of negative samples and false positive samples detected by molecular markers against other species, respectively. The results showed that the molecular marker 1-38 fluorescent PCR detection system had 85% host specificity and 94% host sensitivity for 72 pig feces samples or farm sewage and 79 other species of feces samples; 3-53 detection system It has a host specificity of 90% and a host sensitivity of 99% (Table 3), indicating that the two sets of molecular markers can efficiently and specifically detect whether a sample contains pig feces contamination in practical applications.

表3分子标记对实际样品检测的宿主特异性和敏感性Table 3 Host specificity and sensitivity of molecular markers to actual sample detection

<110>浙江省检验检疫科学技术研究院;浙江工商大学<110> Zhejiang Institute of Inspection and Quarantine Science and Technology; Zhejiang Gongshang University

<120>一种基于宿主-肠道微生物互作基因的猪粪便污染特异性分子标记1-38及其检测方法<120> A specific molecular marker 1-38 based on host-gut microbe interaction gene and its detection method

<160>8<160>8

<210>1<210>1

<211>458<211>458

<212>DNA<212>DNA

<213>猪-肠道微生物<213> Pig - Gut Microbiome

<400>1<400>1

AAATACTAAT GGATAAAATA GAAATAATCT CCGGCAAACT CGGAATTGAG CACCGGAAGG 60AAATACTAAT GGATAAAATA GAAATAATCT CCGGCAAACT CGGAATTGAG CACCGGAAGG 60

TAGCCAACAC CGTAAAACTG CTTGAAGATG GCGCTACAGT GCCATTTATC TCGCGATACC 120TAGCCAACAC CGTAAAACTG CTTGAAGATG GCGCTACAGT GCCATTTATC TCGCGATACC 120

GCAAAGAAGC AACCGGCTCA CTCGATGAAG TTGCCATCAT GAATATCAGC ACGCTCTTGG 180GCAAAGAAGC AACCGGCTCA CTCGATGAAG TTGCCATCAT GAATATCAGC ACGCTCTTGG 180

GACAACTCGA AGAATTGGAC AAGAGGCGTC GTTACATCCT CGAAAGCATT GAGGCAAGCG 240GACAACTCGA AGAATTGGAC AAGAGGCGTC GTTACATCCT CGAAAGCATT GAGGCAAGCG 240

GTGCCTTGAC TCCGGAATTG AATTCACGCA TTATGGTGTG CGATGATGCA ACGACACTCG 300GTGCCTTGAC TCCGGAATTG AATTCACGCA TTATGGTGTG CGATGATGCA ACGACACTCG 300

AGGATATCTA CCTCCCATTC AAGCCCAAAC GCCGCACCAA GGCGGAAGTG GCACGAAACA 360AGGATATCTA CCTCCCATTC AAGCCCCAAAC GCCGCACCAA GGCGGAAGTG GCACGAAACA 360

ACGGTCTCGA ACCGTTGGCA AAAATAATTA TGGCACAAAA ATCGATCGAT ATTCATTCTC 420ACGGTCTCGA ACCGTTGGCA AAAATAATTA TGGCACAAAA ATCGATCGAT ATTCATTCTC 420

AAGCCGGTCG TTTTATTGGG GAAAATGTGC CTGACGAA 458AAGCCGGTCG TTTTATTGGG GAAAATGTGC CTGACGAA 458

<210>2<210>2

<211>458<211>458

<212>DNA<212>DNA

<213>猪-肠道微生物<213> Pig - Gut Microbiome

<400>2<400>2

AAATACTAAT GGATAAAATA GAAATAATCT CCGGCAAACT CGGAATTGAG CACCGGAAGG 60AAATACTAAT GGATAAAATA GAAATAATCT CCGGCAAACT CGGAATTGAG CACCGGAAGG 60

TAGCCAACAC CGTAAAACTG CTTGAAGATG GCGCTACAGT GCCATTTATC TCGCGATACC 120TAGCCAACAC CGTAAAACTG CTTGAAGATG GCGCTACAGT GCCATTTATC TCGCGATACC 120

GCAAAGAAGC AACCGGCTCA CTCGATGAAG TTGCCATCAT GAATATCAGC ACGCTCTTGG 180GCAAAGAAGC AACCGGCTCA CTCGATGAAG TTGCCATCAT GAATATCAGC ACGCTCTTGG 180

GACAACTCGA AGAATTGGAC AAGAGGCGTC GTTACATCCT CGAAAGCATT GAGGCAAGCG 240GACAACTCGA AGAATTGGAC AAGAGGCGTC GTTACATCCT CGAAAGCATT GAGGCAAGCG 240

GTGCCTTGAC TCCGGAATTG AATTCACGCA TTATGGTGTG CGATGATGCA ACGACACTCG 300GTGCCTTGAC TCCGGAATTG AATTCACGCA TTATGGTGTG CGATGATGCA ACGACACTCG 300

AGGATATCTA CCTCCCATTC AAGCCCAAAC GCCGCACCAA GGCGGAAGTG GCACGAAACA 360AGGATATCTA CCTCCCATTC AAGCCCCAAAC GCCGCACCAA GGCGGAAGTG GCACGAAACA 360

ACGGTCTCGA ACCGTTGGCA AAAATAATTA TGGCACAAAA ATCGATCGAT ATTCATTCTC 420ACGGTCTCGA ACCGTTGGCA AAAATAATTA TGGCACAAAA ATCGATCGAT ATTCATTCTC 420

AAGCCGGTCG TTTTATTGGG GAAAATGTGC CTGACGAA 458AAGCCGGTCG TTTTATTGGG GAAAATGTGC CTGACGAA 458

<210>3<210>3

<211>23<211>23

<212>DNA<212>DNA

<213>人工序列<213> Artificial sequence

<400>3<400>3

GGAGGTGGTT AAGCCGATAT GTT 23GGAGGTGGTT AAGCCGATAT GTT 23

<210>4<210>4

<211>22<211>22

<212>DNA<212>DNA

<213>人工序列<213> Artificial sequence

<400>4<400>4

GCCCCTTTCT TGATACTTTG GA 22GCCCCTTTCT TGATACTTTG GA 22

<210>5<210>5

<211>26<211>26

<212>DNA<212>DNA

<213>人工序列<213> Artificial sequence

<400>5<400>5

AAACTGATTG GAGAAGAATA CAGGCG 26AAACTGATTGGAGAAGAATACAGGCG26

<210>6<210>6

<211>21<211>21

<212>DNA<212>DNA

<213>人工序列<213> Artificial sequence

<400>6<400>6

GCGTCGTTAC ATCCTCGAAA G 21GCGTCGTTAC ATCCTCGAAA G 21

<210>7<210>7

<211>18<211>18

<212>DNA<212>DNA

<213>人工序列<213> Artificial sequence

<400>7<400>7

GCGTTTGGGC TTGAATGG 18GCGTTTGGGCTTGAATGG 18

<210>8<210>8

<211>29<211>29

<212>DNA<212>DNA

<213>人工序列<213> Artificial sequence

<400>8<400>8

TTCACGCATT ATGGTGTGCG ATGATGCAA 29TTCACGCATT ATGGTGTGCG ATGATGCAA 29

Claims (4)

1. a kind of swine excrement pollution specific molecular marker 1-38 based on host-enteric microorganism interacting genes, its feature exists It is made up of following primer and probe in this molecular labeling:
Upstream primer:GGAGGTGGTTAAGCCGATATGTT
Downstream primer:GCCCCTTTCTTGATACTTTGGA
Probe:Fam-AAACTGATTGGAGAAGAATACAGGCG-Tam.
2. a kind of based on host-enteric microorganism interacting genes swine excrement pollution detection method it is characterised in that:The method Using the primer described in claim 1 and probe and detected sample mix, carry out Fluorescence PCR, extend in each circulation Reading after end;Sample no Ct value and no amplification curve, represent no swine excrement pollution in sample;Sample amplification Ct value≤35, And typical amplification curve occurs, represent in sample, there is swine excrement pollution;Sample Ct value>35 sample suggestion is reformed, and reforms Result no Ct value person is feminine gender, otherwise for the positive.
3. detection method according to claim 2 it is characterised in that:Primer and concentration and probe concentration are respectively 0.2 μM and 0.3 μM.
4. detection method according to claim 2 is it is characterised in that Fluorescence PCR condition is:95 DEG C of denaturation 30 s, 5 s and 60 DEG C of annealing of 95 DEG C of denaturation of 40 circulations extend 30 s.
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