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CN107475121A - The prevention and controls of harmful bacteria in a kind of microalga cultivation process - Google Patents

The prevention and controls of harmful bacteria in a kind of microalga cultivation process Download PDF

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CN107475121A
CN107475121A CN201710852400.9A CN201710852400A CN107475121A CN 107475121 A CN107475121 A CN 107475121A CN 201710852400 A CN201710852400 A CN 201710852400A CN 107475121 A CN107475121 A CN 107475121A
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bacteria
microalgae
harmful bacteria
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赵鄢鹏
王冰
白雪梅
蔡忠贞
冯倩
刘峰
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ENN Science and Technology Development Co Ltd
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Abstract

The present invention relates to a kind of prevention and controls of harmful bacteria in both culturing microalgae technical field, more particularly to microalga cultivation process.Specific aim improvement can be carried out to there is evil bacterium in microalga cultivation process in time.The prevention and controls of harmful bacteria in a kind of microalga cultivation process, including:Step 1) determines the harmful bacteria that the microalgae has polluted, and the physicochemical property determined by acquisition corresponding to harmful bacteria in microalgae carries out breeding process;Step 2) is cultivated to the microalgae, and in breeding process, the algae solution of the microalgae is monitored, and judges the physicochemical property for whether having corresponding to identified harmful bacteria in the algae solution;If it is determined that having the physicochemical property corresponding to identified harmful bacteria in the algae solution, then, physicochemical property of the step 3) determined by corresponding to harmful bacteria, specific aim improvement is carried out to the harmful bacteria.The embodiment of the present invention is used for both culturing microalgae.

Description

一种微藻养殖过程中有害细菌的防治方法A method for preventing and controlling harmful bacteria in the process of microalgae cultivation

技术领域technical field

本发明涉及微藻养殖技术领域,尤其涉及一种微藻养殖过程中有害细菌的防治方法。The invention relates to the technical field of microalgae cultivation, in particular to a method for preventing and controlling harmful bacteria in the microalgae cultivation process.

背景技术Background technique

目前,全球经济发展受到能源紧缺的制约。为实现经济可持续发展,微藻生物质能源作为可再生能源受到广泛关注。但是,现有的藻类规模化培养通常在开放池或者生物反应器中进行,在养殖过程中,尤其是夏季,可能会出现一系列的污染,例如:细菌污染、原生动物污染等。其中细菌污染在微藻污染过程中会最先发生,其中部分种类的细菌会使微藻产量下降,甚至会导致大规模培养在几天、甚至昼夜之间完全溃败,给藻类的大规模培养带来极大的危害。At present, global economic development is constrained by energy shortage. In order to achieve sustainable economic development, microalgae biomass energy has received extensive attention as a renewable energy source. However, the existing large-scale cultivation of algae is usually carried out in open ponds or bioreactors. During the cultivation process, especially in summer, a series of pollution may occur, such as: bacterial pollution, protozoan pollution, etc. Among them, bacterial pollution will occur first in the process of microalgae pollution, and some types of bacteria will reduce the yield of microalgae, and even cause large-scale cultivation to completely collapse within a few days, or even day and night, bringing serious damage to the large-scale cultivation of algae. to great harm.

为了预防藻类规模化培养过程中产生细菌污染,目前,通常在养殖前的准备时期,对培养液和反应器进行灭菌处理,以避免微藻在养殖过程中污染细菌,并且,现有的规模化培养多采用开放式或者半开放式养殖,在养殖过程中并不能完全避免细菌的污染,并且发生污染之后也没有分辨有害细菌和无害细菌的技术,只能是在微藻生长已经受到影响的时候再进行治理,这个时候杀菌剂所使用的剂量较大,会对生长状态不佳的微藻产生更加不好的影响。In order to prevent bacterial contamination during the large-scale cultivation of algae, at present, the culture medium and reactors are usually sterilized in the preparation period before cultivation, so as to avoid microalgae from contaminating bacteria during the cultivation process, and the existing scale Most of the chemical culture adopts open or semi-open culture. Bacterial pollution cannot be completely avoided during the breeding process, and there is no technology to distinguish harmful bacteria from harmless bacteria after pollution occurs. It can only be affected when the growth of microalgae has been affected At this time, the dose of fungicide used is relatively large, which will have a more adverse impact on microalgae that are not growing well.

因此,亟待寻求一种对微藻培养过程中的有害细菌进行早期治理的方法,对有害细菌进行针对性治理,避免有害细菌治理不及时所带来的微藻产量下降,以及不能对有害细菌进行针对性治理所带来的微藻产量下降的情况发生。Therefore, it is urgent to seek a method for early treatment of harmful bacteria in the microalgae culture process, targeted treatment of harmful bacteria, avoiding the decline in microalgae production caused by untimely treatment of harmful bacteria, and the inability to treat harmful bacteria. The reduction of microalgae production caused by targeted treatment occurs.

发明内容Contents of the invention

本发明的主要目的在于,提供一种微藻养殖过程中有害细菌的治理方法,通过对微藻养殖过程中的有害细菌进行实时监控,能够及时对微藻养殖过程中出现的有害细菌进行针对性治理,从而能够避免有害细菌治理不及时所带来的微藻产量下降,以及不能对有害细菌进行针对性治理所带来的微藻产量下降的情况发生。The main purpose of the present invention is to provide a treatment method for harmful bacteria in the process of microalgae cultivation. By monitoring the harmful bacteria in the process of microalgae cultivation in real time, the harmful bacteria that appear in the process of microalgae cultivation can be targeted in time. Treatment, so as to avoid the decrease of microalgae production caused by untimely treatment of harmful bacteria, and the decrease of microalgae production caused by inability to carry out targeted treatment of harmful bacteria.

为达到上述目的,本发明采用如下技术方案:To achieve the above object, the present invention adopts the following technical solutions:

本发明实施例提供一种微藻养殖过程中有害细菌的防治方法,包括:The embodiment of the present invention provides a method for preventing and controlling harmful bacteria in the microalgae cultivation process, comprising:

步骤1)在微藻进行养殖过程中,确定所述微藻已污染的有害细菌,并获取所确定的有害细菌所对应的理化特性;Step 1) During the microalgae cultivation process, determine the harmful bacteria that the microalgae has polluted, and obtain the physical and chemical characteristics corresponding to the determined harmful bacteria;

步骤2)对所述微藻进行养殖,并在养殖过程中,对所述微藻的藻液进行监控,判断所述藻液中是否具有所确定的有害细菌所对应的理化特性;Step 2) cultivating the microalgae, and monitoring the algae liquid of the microalgae during the cultivation process, and judging whether the algae liquid has the physical and chemical characteristics corresponding to the determined harmful bacteria;

若确定所述藻液中具有所确定的有害细菌所对应的理化特性,则,If it is determined that the algae liquid has the corresponding physical and chemical characteristics of the determined harmful bacteria, then,

步骤3)根据所确定的有害细菌所对应的理化特性,对所述有害细菌进行针对性治理。Step 3) According to the physical and chemical characteristics corresponding to the determined harmful bacteria, carry out targeted treatment on the harmful bacteria.

可选的,所述方法还包括:Optionally, the method also includes:

当监控到所述微藻的藻液中的细菌数量增大,或者,在所述步骤3)之后,增大监控的频率。When it is monitored that the number of bacteria in the algae fluid of the microalgae increases, or, after the step 3), the frequency of monitoring is increased.

可选的,在微藻进行养殖过程中,确定所述微藻已污染的有害细菌;具体包括:Optionally, during the cultivation of microalgae, it is determined that the microalgae has been polluted by harmful bacteria; specifically including:

对所述微藻进行养殖,并在所述微藻污染有细菌,和/或,所述微藻的生物增量开始降低时,对所述微藻的藻液进行取样,并对藻液中出现的细菌进行菌落培养;Cultivate the microalgae, and when the microalgae is contaminated with bacteria, and/or, when the bioincrease of the microalgae begins to decrease, the algae liquid of the microalgae is sampled, and the algae liquid in the algae liquid is Bacteria that emerged were colonized;

将培养所获得的来自不同菌落的细菌分别与无菌微藻在不同的实验组中进行共同养殖,若在养殖过程中第i实验组中的无菌微藻出现生物量下降,藻细胞颜色变白或变黄以及藻细胞发生絮凝中的至少一种现象,则确定所述第i实验组中的细菌为所述微藻已污染的有害细菌,其中,i为大于等于1的自然数,所述第i实验组为所有实验组中的任意一组。Bacteria from different colonies obtained from the culture were co-cultivated with sterile microalgae in different experimental groups. If the biomass of the sterile microalgae in the i-th experimental group decreased during the cultivation process, the color of the algal cells changed. Whitening or yellowing and at least one phenomenon in the flocculation of algal cells, then it is determined that the bacteria in the i-th experimental group are harmful bacteria that have been polluted by the microalgae, wherein, i is a natural number greater than or equal to 1, and the The i-th experimental group is any one of all experimental groups.

可选的,获取所确定的有害细菌所对应的理化特性;具体包括:Optionally, obtain the physical and chemical characteristics corresponding to the identified harmful bacteria; specifically include:

观察所确定的各个有害细菌所对应的菌落形态,以获取各个有害细菌所对应的理化特性;或者,Observing the colony morphology corresponding to each of the identified harmful bacteria to obtain the physicochemical characteristics corresponding to each harmful bacteria; or,

对所确定的各个有害细菌进行革兰氏染色,并观察革兰氏染色后的各个有害细菌的细胞形态以及所呈现的颜色,以获取各个有害细菌所对应的理化特性;或者,Perform Gram staining on each of the identified harmful bacteria, and observe the cell morphology and color of each harmful bacteria after Gram staining, so as to obtain the corresponding physical and chemical characteristics of each harmful bacteria; or,

分别对所确定的每一个有害细菌进行DNA序列测定,并根据各个有害细菌所对应的DNA序列确定各个有害细菌所属的属,以获取各个有害细菌所对应的理化特性。The DNA sequence of each identified harmful bacterium is determined separately, and the genus of each harmful bacterium is determined according to the DNA sequence corresponding to each harmful bacterium, so as to obtain the corresponding physical and chemical characteristics of each harmful bacterium.

可选的,根据各个有害细菌所对应的DNA序列,并通过NCBI数据库查询,以确定各个有害细菌所属的属。Optionally, the genus to which each harmful bacterium belongs can be determined according to the DNA sequence corresponding to each harmful bacterium and querying the NCBI database.

可选的,将培养所获得的来自不同菌落的细菌分别与无菌微藻在不同的实验组中进行共同养殖之前,所述方法还包括:Optionally, before the bacteria from different colonies obtained by the culture are cultured together with the sterile microalgae in different experimental groups, the method also includes:

分别对来自不同菌落的细菌进行DNA序列测定,并根据DNA序列测定结果确定来自不同菌落的细菌是否为同一种细菌,以筛选出所有菌落中与无菌微藻进行共同养殖的不同菌种,并根据筛选出的不同菌种,确定分别对来自不同菌落的细菌与所述无菌微藻进行共同养殖的实验组数。Carry out DNA sequence determination to the bacteria from different colonies, and determine whether the bacteria from different colonies are the same bacteria according to the DNA sequence determination results, to screen out the different bacterial species that are co-cultivated with sterile microalgae in all colonies, and According to the different strains screened out, determine the number of experimental groups for co-culturing bacteria from different colonies and the sterile microalgae.

可选的,对所述微藻的藻液进行监控,并判断所述藻液中是否具有所确定的有害细菌所对应的理化特性;具体包括:Optionally, monitor the algae fluid of the microalgae, and determine whether the algae fluid has the physical and chemical characteristics corresponding to the identified harmful bacteria; specifically include:

对所述微藻的藻液进行取样,并对所述藻液所污染的细菌进行菌落培养,将培养所获得的各个菌落的菌落形态和所确定的有害细菌所对应的菌落形态进行对比;或者,Sampling the algal fluid of the microalgae, and performing colony culture on the bacteria contaminated by the algae fluid, and comparing the colony morphology of each colony obtained from the culture with the colony morphology corresponding to the determined harmful bacteria; or ,

对所述微藻的藻液进行取样,并对所述藻液中的细菌进行革兰氏染色,将革兰氏染色后的各个细菌所对应的细胞形态和所呈现的颜色与所确定的有害细菌进行对比;或者,Sampling the algae fluid of the microalgae, and carrying out Gram staining to the bacteria in the algae fluid, and comparing the cell morphology and the color presented by each bacterium after Gram staining with the determined harmful bacteria for comparison; or,

对所述微藻的藻液进行取样,并对所述藻液中的细菌建立系统发育树,根据所建立的系统发育树对所确定的有害细菌的16SDNA序列设计特异性引物,根据所设计的特异性引物,通过PCR方法对所确定的有害细菌进行跟踪。Sampling the algal liquid of the microalgae, and establishing a phylogenetic tree for the bacteria in the algal liquid, designing specific primers for the 16SDNA sequence of the determined harmful bacteria according to the established phylogenetic tree, and designing specific primers according to the designed phylogenetic tree. Specific primers are used to track the identified harmful bacteria by PCR method.

可选的,通过荧光定量PCR方法对所确定的有害细菌进行标记跟踪。Optionally, the identified harmful bacteria are tagged and tracked by means of fluorescent quantitative PCR.

可选的,所述步骤3)具体包括:Optionally, the step 3) specifically includes:

根据所确定的有害细菌所对应的理化特性,判断所确定的有害细菌的耐酸碱性,以及所述有害细菌和所述养殖微藻的耐酸碱性之间的差异,通过调节藻液的pH值对所确定的有害细菌进行治理;或者,According to the physical and chemical characteristics corresponding to the determined harmful bacteria, judge the acid and alkali resistance of the determined harmful bacteria, and the difference between the acid and alkali resistance of the harmful bacteria and the cultured microalgae, by adjusting the pH to remediate the identified harmful bacteria; or,

直接采用合适剂量的消毒剂对所确定的有害细菌进行杀灭。Directly use the appropriate dose of disinfectant to kill the identified harmful bacteria.

本发明实施例提供一种微藻养殖过程中有害细菌的防治方法,通过事先在养藻养殖过程中确定所述微藻已污染的有害细菌,并相应地获取所确定的各个有害细菌所对应的理化特性,这样一来,通过在对微藻进行养殖的过程中,对所述微藻的藻液进行实时监控,判断所述藻液中是否具有所确定的有害细菌所对应的理化特性,能够对所述藻液中出现的细菌中的有害细菌进行实时监控,这样一来,当监控到所述藻液中具有所确定的有害细菌的理化特性时,根据所确定的有害细菌所对应的理化特性,对所述有害细菌进行针对性治理,能够避免有害细菌治理不及时所带来的微藻产量下降,以及不能对有害细菌进行针对性治理所带来的微藻产量下降的情况发生,从而能够对有害细菌进行早期治理,最大程度上提高微藻的产量。The embodiment of the present invention provides a method for preventing and controlling harmful bacteria in the process of microalgae cultivation, by determining in advance the harmful bacteria that have been contaminated by the microalgae during the algae cultivation process, and correspondingly obtaining the Physicochemical properties, in this way, by monitoring the algae liquid of the microalgae in real time during the process of cultivating the microalgae, judging whether the algae liquid has the physical and chemical properties corresponding to the determined harmful bacteria, can Real-time monitoring of the harmful bacteria in the bacteria appearing in the algae liquid, so that when the physical and chemical characteristics of the determined harmful bacteria are monitored in the algae liquid, according to the corresponding physical and chemical characteristics of the determined harmful bacteria characteristics, the targeted treatment of the harmful bacteria can avoid the decrease in the production of microalgae caused by the untimely treatment of harmful bacteria, and the decrease in the production of microalgae caused by the inability to carry out targeted treatment of harmful bacteria, thereby It can carry out early treatment of harmful bacteria and maximize the production of microalgae.

附图说明Description of drawings

为了更清楚地说明本发明实施例或现有技术中的技术方案,下面将对实施例描述中所需要使用的附图作简单地介绍,显而易见地,下面描述中的附图仅仅是本发明的一些实施例,对于本领域普通技术人员来讲,在不付出创造性劳动的前提下,还可以根据这些附图获得其它的附图。In order to more clearly illustrate the embodiments of the present invention or the technical solutions in the prior art, the following will briefly introduce the accompanying drawings that need to be used in the description of the embodiments. Obviously, the accompanying drawings in the following description are only of the present invention. For some embodiments, those skilled in the art can also obtain other drawings based on these drawings without creative efforts.

图1为本发明实施例提供的一种微藻养殖过程中有害细菌的防治方法的流程示意图;1 is a schematic flow diagram of a method for preventing and controlling harmful bacteria in a microalgae cultivation process provided by an embodiment of the present invention;

图2为本发明实施例提供的一种以100倍倍比稀释的有害细菌基因组为模板的荧光定量PCR的敏感度曲线图;Fig. 2 is the sensitivity curve diagram of a kind of fluorescent quantitative PCR with 100-fold diluted harmful bacterial genome as template provided by the embodiment of the present invention;

图3为本发明实施例提供的一种所设计的特异性引物的特异性分析的曲线图;Fig. 3 is a graph of the specificity analysis of a designed specific primer provided by the embodiment of the present invention;

图4为本发明实施例提供的一种实验组和对照组分别检出有害细菌当天的荧光定量PCR检测结果图。Fig. 4 is a graph of fluorescent quantitative PCR detection results on the day when harmful bacteria were detected in the experimental group and the control group provided by the embodiment of the present invention.

具体实施方式detailed description

下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有做出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。The following will clearly and completely describe the technical solutions in the embodiments of the present invention with reference to the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only some, not all, embodiments of the present invention. Based on the embodiments of the present invention, all other embodiments obtained by persons of ordinary skill in the art without making creative efforts belong to the protection scope of the present invention.

本发明实施例提供一种微藻养殖过程中有害细菌的防治方法,参见图1,包括:The embodiment of the present invention provides a method for preventing and controlling harmful bacteria in the process of microalgae cultivation, as shown in Figure 1, including:

步骤1)在微藻进行养殖过程中,确定所述微藻已污染的有害细菌,并获取所确定的有害细菌所对应的理化特性;Step 1) During the microalgae cultivation process, determine the harmful bacteria that the microalgae has polluted, and obtain the physical and chemical characteristics corresponding to the determined harmful bacteria;

步骤2)对所述微藻进行养殖,并在养殖过程中,对所述微藻的藻液进行监控,判断所述藻液中是否具有所确定的有害细菌所对应的理化特性;Step 2) cultivating the microalgae, and monitoring the algae liquid of the microalgae during the cultivation process, and judging whether the algae liquid has the physical and chemical characteristics corresponding to the determined harmful bacteria;

若确定所述藻液中具有所确定的有害细菌所对应的理化特性,则,If it is determined that the algae liquid has the corresponding physical and chemical characteristics of the determined harmful bacteria, then,

步骤3)根据所确定的有害细菌所对应的理化特性,对所述有害细菌进行针对性治理。Step 3) According to the physical and chemical characteristics corresponding to the determined harmful bacteria, carry out targeted treatment on the harmful bacteria.

有害细菌所对应的理化特性是指有害细菌在物理和化学方面的特性。The physical and chemical properties corresponding to harmful bacteria refer to the physical and chemical characteristics of harmful bacteria.

本发明实施例提供一种微藻养殖过程中有害细菌的防治方法,通过事先在微藻养殖过程中确定所述微藻已污染的有害细菌,并相应地获取所确定的各个有害细菌所对应的理化特性,这样一来,通过在对微藻进行养殖的过程中,对所述微藻的藻液进行实时监控,判断所述藻液中是否具有所确定的有害细菌所对应的理化特性,能够对所述藻液中出现的细菌中的有害细菌进行实时监控,这样一来,当监控到所述藻液中具有所确定的有害细菌的理化特性时,根据所确定的有害细菌所对应的理化特性,对所述有害细菌进行针对性治理,能够避免有害细菌治理不及时所带来的微藻产量下降,以及不能对有害细菌进行针对性治理所带来的微藻产量下降的情况发生,从而能够对有害细菌进行早期治理,最大程度上提高微藻的产量。The embodiment of the present invention provides a method for preventing and controlling harmful bacteria in the microalgae culture process, by determining in advance the harmful bacteria that the microalgae has polluted in the microalgae culture process, and correspondingly obtaining the Physicochemical properties, in this way, by monitoring the algae liquid of the microalgae in real time during the process of cultivating the microalgae, judging whether the algae liquid has the physical and chemical properties corresponding to the determined harmful bacteria, can Real-time monitoring of the harmful bacteria in the bacteria appearing in the algae liquid, so that when the physical and chemical characteristics of the determined harmful bacteria are monitored in the algae liquid, according to the corresponding physical and chemical characteristics of the determined harmful bacteria characteristics, the targeted treatment of the harmful bacteria can avoid the decrease in the production of microalgae caused by the untimely treatment of harmful bacteria, and the decrease in the production of microalgae caused by the inability to carry out targeted treatment of harmful bacteria, thereby It can carry out early treatment of harmful bacteria and maximize the production of microalgae.

本发明的一实施例中,所述方法还包括:In an embodiment of the present invention, the method also includes:

当监控到所述微藻的藻液中的细菌数量增大,或者,在所述步骤3)之后,增大监控的频率。When it is monitored that the number of bacteria in the algae fluid of the microalgae increases, or, after the step 3), the frequency of monitoring is increased.

能够增大对有害细菌的监控频率,从而能够对养殖过程中可能出现的有害细菌进行及时治理。The monitoring frequency of harmful bacteria can be increased, so that harmful bacteria that may appear in the breeding process can be treated in time.

本发明的又一实施例中,在微藻进行养殖过程中,确定所述微藻已污染的有害细菌;具体包括:In yet another embodiment of the present invention, during the cultivation of microalgae, it is determined that the harmful bacteria that have been contaminated by the microalgae; specifically include:

对所述微藻进行养殖,并在所述微藻污染有细菌,和/或,所述微藻的生物增量开始降低时,对所述微藻的藻液进行取样,并对藻液中出现的细菌进行菌落培养;Cultivate the microalgae, and when the microalgae is contaminated with bacteria, and/or, when the bioincrease of the microalgae begins to decrease, the algae liquid of the microalgae is sampled, and the algae liquid in the algae liquid is Bacteria that emerged were colonized;

将培养所获得的来自不同菌落的细菌分别与无菌微藻在不同的实验组中进行共同养殖,若在养殖过程中第i实验组中的无菌微藻出现生物量下降,藻细胞颜色变白或变黄以及藻细胞发生絮凝中的至少一种现象,则确定所述第i实验组中的细菌为所述微藻已污染的有害细菌,其中,i为大于等于1的自然数,所述第i实验组为所有实验组中的任意一组。Bacteria from different colonies obtained from the culture were co-cultivated with sterile microalgae in different experimental groups. If the biomass of the sterile microalgae in the i-th experimental group decreased during the cultivation process, the color of the algal cells changed. Whitening or yellowing and at least one phenomenon in the flocculation of algal cells, then it is determined that the bacteria in the i-th experimental group are harmful bacteria that have been polluted by the microalgae, wherein, i is a natural number greater than or equal to 1, and the The i-th experimental group is any one of all experimental groups.

其中,菌落是由单个细菌细胞在适宜固体培养基表面或内部生长繁殖到一定程度,形成肉眼可见的子细胞群落。Among them, a colony consists of a single bacterial cell growing and multiplying on the surface or inside of a suitable solid medium to a certain extent, forming a sub-cell community visible to the naked eye.

在本发明实施例中,在所述微藻污染有细菌,是指通过显微镜观察可以明显看到有细菌污染,而在所述微藻的生物增量开始降低时,说明所述微藻中污染了细菌,这时,通过对微藻的藻液进行取样,并对藻液中的细菌进行菌落培养,能够获得所述藻液中的所有细菌的菌落,再将菌落培养后的细菌分别与无菌微藻进行共同养殖,能够确定所述微藻已污染的细菌中是否有有害细菌,即,当某一实验组中的所述无菌微藻不生长,藻细胞明显变白变黄和微藻出现明显的絮凝现象中的至少一种现象时,则可以确定该实验组中的细菌为有害细菌,示例性的,当培养所获得的菌落为3个时,来自3个菌落中的细菌分别在在第一实验组、第二实验组和第三实验组与无菌微藻进行共同养殖,其中,当第二实验组中的藻细胞出现藻细胞变白变黄,则说明第二实验组中的细菌为有害细菌。这里,第一、第二、第三是为了区分实验组进行的命名,并不对实验组的设置顺序和具体设置方式造成限定。In the embodiment of the present invention, when the microalgae is contaminated with bacteria, it means that there is obvious bacterial contamination through microscope observation, and when the biological increase of the microalgae begins to decrease, it means that the microalgae is polluted. At this time, by sampling the algae liquid of microalgae and carrying out colony culture to the bacteria in the algae liquid, the colonies of all bacteria in the algae liquid can be obtained, and then the bacteria after the colony culture are compared with those without Bacteria and microalgae are co-cultivated, and it is possible to determine whether there are harmful bacteria in the bacteria contaminated by the microalgae, that is, when the sterile microalgae in a certain experimental group does not grow, the algal cells are obviously white and yellow and the microalgae appear. When there is at least one phenomenon in the obvious flocculation phenomenon, it can be determined that the bacteria in the experimental group are harmful bacteria. Exemplary, when the number of bacterial colonies obtained by cultivating is 3, the bacteria from the 3 bacterial colonies are respectively in the The first experimental group, the second experimental group and the third experimental group are cultured together with sterile microalgae, wherein, when the algal cells in the second experimental group appear to turn white and yellow, it means that the algal cells in the second experimental group Bacteria are harmful bacteria. Here, the first, second, and third names are used to distinguish the experimental groups, and do not limit the setting order and specific setting methods of the experimental groups.

通常情况下,来自不同菌落的细菌为不同菌种的细菌,但是,在藻液进行涂布的过程中,同一种细菌的不同个体可能会被涂布在固体培养基上的不同位置,因此会形成不同的菌落。Usually, the bacteria from different colonies are bacteria of different strains, however, in the process of coating the algae liquid, different individuals of the same bacteria may be coated on different positions on the solid medium, so there will be form different colonies.

因此,本发明的一优选实施例中,将培养所获得的来自不同菌落的细菌分别与无菌微藻在不同的实验组中进行共同养殖之前,所述方法还包括:Therefore, in a preferred embodiment of the present invention, before the bacteria from different colonies obtained by cultivating are respectively cultured with sterile microalgae in different experimental groups, the method also includes:

分别对来自不同菌落的细菌进行DNA序列测定,并根据DNA序列测定结果确定来自不同菌落的细菌是否为同一种细菌,以筛选出所有菌落中与无菌微藻进行共同养殖的不同菌种,并根据筛选出的不同菌种,确定分别对来自不同菌落的细菌与所述无菌微藻进行共同养殖的实验组数。Carry out DNA sequence determination to the bacteria from different colonies, and determine whether the bacteria from different colonies are the same bacteria according to the DNA sequence determination results, to screen out the different bacterial species that are co-cultivated with sterile microalgae in all colonies, and According to the different strains screened out, determine the number of experimental groups for co-culturing bacteria from different colonies and the sterile microalgae.

在本发明实施例中,通过对来自不同菌落的细菌进行DNA序列测定,并根据DNA序列测定结果,能够确定来自不同菌落的细菌是否为同一种细菌,从而能够确定所有的菌落总共包含几种不同的菌种,再分别将不同的菌种与无菌微藻进行共同养殖,能够避免同一菌种重复设置实验组,减少实验组的设置。示例性的,当培养所获得的菌落为5个时,为了方便描述,将来这5个不同的菌落分别记为第一菌落、第二菌落、第三菌落、第四菌落和第五菌落,分别对这5个不同菌落的细菌进行DNA序列测定,当确定第一菌落和第四菌落为同一种细菌,而第三菌落和第五菌落为同一种细菌时,则可以确定来自这5个不同菌落的细菌中有三种不同的菌种,这时,就可以确定对来自不同菌落的细菌与所述无菌微藻进行共同养殖的实验组数为三组,即第一实验组可以为来自第一菌落和第四菌落中的任意一个菌落中的细菌,第二实验组可以为来自第二菌落中的细菌,第三实验组可以为来自第三菌落和第五菌落中的任意一个菌落中的细菌,从而能够避免第一菌落和第四菌落为同一种细菌而重复设置与无菌微藻进行共同养殖的实验组,实验组的数量可以缩减为3个,减少了实验组的设置。这里,第一、第二、第三是为了区分实验组进行的命名,并不对实验组的设置顺序和具体设置方式造成限定。In the embodiment of the present invention, by performing DNA sequence determination on bacteria from different colonies, and according to the results of DNA sequence determination, it can be determined whether the bacteria from different colonies are the same bacteria, so that it can be determined that all the colonies contain a total of several different bacteria. Different strains and sterile microalgae are cultured together, which can avoid repeated setting of experimental groups for the same strain and reduce the number of experimental groups. Exemplarily, when the number of bacterium colonies obtained by cultivating is 5, for the convenience of description, these 5 different bacterium colonies will be respectively recorded as the first bacterium colony, the second bacterium colony, the third bacterium colony, the fourth bacterium colony and the fifth bacterium colony in the future, respectively Carry out DNA sequence determination to the bacteria of these 5 different colonies, when it is determined that the first and fourth bacterial colonies are the same bacterium, and the third and fifth bacterial colonies are the same bacterium, then it can be determined that they are from these 5 different bacterial colonies There are three different bacterial species in the bacterium, at this moment, just can determine that the experimental group number that the bacterium from different bacterial colony and described sterile microalgae are cultured together is three groups, promptly the first experimental group can be from the first Bacteria in any one of the bacterium colony and the fourth bacterium colony, the second experimental group can be bacteria from the second bacterium colony, and the third experimental group can be bacteria from any one of the third bacterium colony and the fifth bacterium colony , so as to avoid repeated setting of the experimental group for co-culturing with sterile microalgae for the first bacterial colony and the fourth bacterial colony for the same bacterium, the number of experimental groups can be reduced to 3, reducing the setting of the experimental group. Here, the first, second, and third names are used to distinguish the experimental groups, and do not limit the setting order and specific setting methods of the experimental groups.

其中,对来自不同菌落的细菌进行DNA序列测定之前,所述方法还包括:Wherein, before DNA sequence determination is carried out to the bacteria from different colonies, the method also includes:

分别对来自不同菌落的细菌进行DNA提取,并采用细菌16S通用引物进行PCR(Polymerase Chain Reaction,聚合酶链式反应)扩增。DNA was extracted from bacteria from different colonies, and PCR (Polymerase Chain Reaction, polymerase chain reaction) amplification was performed using bacterial 16S universal primers.

PCR(Polymerase Chain Reaction,聚合酶链式反应)利用DNA在体外摄氏95°高温时变性会变成单链,低温(经常是60℃左右)时引物与单链按碱基互补配对的原则结合,再调温度至DNA聚合酶最适反应温度(72℃左右),DNA聚合酶沿着磷酸到五碳糖(5'-3')的方向合成互补链。是一种用于放大扩增特定的DNA片段的分子生物学技术。PCR (Polymerase Chain Reaction, Polymerase Chain Reaction) uses DNA to denature in vitro at a high temperature of 95°C and it will become a single strand. Then adjust the temperature to the optimum reaction temperature of DNA polymerase (about 72°C), and DNA polymerase synthesizes complementary chain along the direction from phosphoric acid to five-carbon sugar (5'-3'). It is a molecular biology technique used to amplify specific DNA fragments.

本发明的又一实施例中,获取所确定的有害细菌所对应的理化特性;具体包括:In yet another embodiment of the present invention, the physical and chemical characteristics corresponding to the determined harmful bacteria are obtained; specifically include:

观察所确定的各个有害细菌所对应的菌落形态,以获取各个有害细菌所对应的理化特性。Observe the colony morphology corresponding to each of the identified harmful bacteria, so as to obtain the corresponding physical and chemical characteristics of each harmful bacteria.

其中,菌落形态包括菌落的大小、形状、边缘、光泽、质地、颜色和透明程度等。每一种细菌在一定条件下形成固定的菌落特征。Among them, the colony morphology includes the size, shape, edge, luster, texture, color and degree of transparency of the colony. Each kind of bacteria forms fixed colony characteristics under certain conditions.

通过对各个有害细菌所对应的菌落形态进行观察,能够对各个有害细菌所对应的菌落形态和其他细菌的菌落形态进行区分,从而能够获取各个有害细菌所对应的理化特性。示例性的,当通过对所有的细菌进行菌落培养,并确定其中一种细菌为有害细菌时,若这种细菌所对应的菌落为圆形红色小菌落,且菌落湿润、粘稠、易挑起,而其余的细菌所对应的菌落为,且菌落干燥,有褶皱,则可以获取所确定的有害细菌所对应的理化特性为圆形红色小菌落,且菌落湿润、粘稠、易挑起。By observing the colony form corresponding to each harmful bacterium, the colony form corresponding to each harmful bacterium can be distinguished from the colony form of other bacteria, so that the physical and chemical characteristics corresponding to each harmful bacterium can be obtained. Exemplarily, when all bacteria are colonized and determined to be a harmful bacterium, if the colony corresponding to this bacterium is a small round red colony, and the colony is moist, sticky, and easy to provoke , and the colonies corresponding to the rest of the bacteria are, and the colonies are dry and wrinkled, then the physical and chemical characteristics corresponding to the determined harmful bacteria can be obtained as small round red colonies, and the colonies are moist, sticky, and easy to provoke.

或者,对所确定的各个有害细菌进行革兰氏染色,并观察革兰氏染色后的各个有害细菌的细胞形态以及所呈现的颜色,以获取各个有害细菌所对应的理化特性;Alternatively, perform Gram staining on each of the identified harmful bacteria, and observe the cell morphology and color of each harmful bacteria after Gram staining, so as to obtain the corresponding physical and chemical characteristics of each harmful bacteria;

革兰氏染色是细菌学中广泛使用的一种鉴别染色法,未经染色的细菌,由于其与周围环境折光率差别甚小,故在显微镜下极难观察。染色后细菌与环境形成鲜明对比,可以清楚地观察到细菌的形态、排列及某些结构特征,而用以分类鉴定。示例性的,当确定所有细菌中的一种细菌为有害细菌时,通过对这种细菌进行革兰氏染色,可以在显微镜下观察到这种细菌的形状(如杆状、球状、螺旋状等),以及这种细菌进行革兰氏染色后所显示的颜色,与其他细菌的形状和革兰氏阴阳性形成比对,则可以获取所确定的有害细菌所对应的理化特性为革兰氏阳性或者革兰氏阴性的杆状菌,还是球状菌,或者是螺旋状菌。Gram staining is a differential staining method widely used in bacteriology. Unstained bacteria are extremely difficult to observe under a microscope because of the small difference in refractive index between them and the surrounding environment. After staining, the bacteria are in sharp contrast with the environment, and the shape, arrangement and certain structural features of the bacteria can be clearly observed, which can be used for classification and identification. Exemplarily, when it is determined that a bacterium in all bacteria is a harmful bacterium, by carrying out Gram staining to this bacterium, the shape (such as rod shape, spherical shape, spiral shape, etc.) of this bacterium can be observed under a microscope. ), and the color displayed by this bacterium after Gram staining, compared with the shape of other bacteria and Gram-negative and positive, the physical and chemical characteristics corresponding to the determined harmful bacteria can be obtained as Gram-positive Or Gram-negative rods, or cocci, or spirochetes.

或者,分别对所确定的每一个有害细菌进行DNA序列测定,并根据各个有害细菌所对应的DNA序列确定各个有害细菌所属的属,以获取各个有害细菌所对应的理化特性。Alternatively, the DNA sequence of each identified harmful bacterium is determined, and the genus of each harmful bacterium is determined according to the DNA sequence corresponding to each harmful bacterium, so as to obtain the corresponding physical and chemical characteristics of each harmful bacterium.

通过对所确定的有害细菌进行DNA序列测定,并将DNA序列测定结果与已知的DNA序列进行对比,能够确定所确定的有害细菌所属的属,从而能够根据所确定的有害细菌所属的属具有的共性,获取所确定的有害细菌所对应的理化特性。示例性的,当所确定的有害细菌所属的属为芽孢杆菌,其他细菌所属的属为其他属时,则可以获取所确定的有害细菌具有所属的属所对应的理化特性,例如:当所确定的有害细菌为芽孢杆菌时,其为杆菌科的一属细菌,可以获取该有害细菌对外界有害因子抵抗力强,且为革兰氏阳性菌等。By performing DNA sequence determination on the determined harmful bacteria, and comparing the DNA sequence determination results with known DNA sequences, the genus to which the determined harmful bacteria belongs can be determined, so that according to the genus to which the determined harmful bacteria belong, the commonality, to obtain the physical and chemical properties corresponding to the identified harmful bacteria. Exemplarily, when the genus to which the determined harmful bacteria belongs is Bacillus, and the genus to which other bacteria belong is other genera, it can be obtained that the determined harmful bacteria have the corresponding physical and chemical characteristics of the genus to which they belong, for example: when the determined harmful bacteria When the bacterium is Bacillus, it is a genus of bacteria belonging to the family Bacillus, and it can be obtained that the harmful bacterium is highly resistant to external harmful factors and is a Gram-positive bacterium or the like.

其中,本发明的一优选实施例中,根据各个有害细菌所对应的DNA序列,并通过NCBI数据库查询以确定各个有害细菌所属的属。Wherein, in a preferred embodiment of the present invention, the genus to which each harmful bacterium belongs is determined according to the DNA sequence corresponding to each harmful bacterium and queried through the NCBI database.

NCBI(National Center for Biotechnology Information)是指美国国立生物技术信息中心。NCBI受过分子生物学高级训练的工作人员通过来自各个实验室递交的序列和同国际核酸序列数据库(EMBL和DDBJ)交换数据建立起数据库。同美国专利和商标局的安排使得专利的序列信息也被整合。NCBI (National Center for Biotechnology Information) refers to the National Center for Biotechnology Information in the United States. NCBI's highly trained staff in molecular biology has established a database through sequences submitted by various laboratories and exchanged data with international nucleic acid sequence databases (EMBL and DDBJ). Arrangements with the US Patent and Trademark Office have enabled sequence information on patents to be integrated as well.

本发明的一实施例中,对所述微藻的藻液中的细菌进行监控,并判断所述藻液中的细菌是否具有所确定的有害细菌的理化特性;具体包括:In one embodiment of the present invention, the bacteria in the algae fluid of the microalgae are monitored, and it is judged whether the bacteria in the algae fluid have the determined physical and chemical characteristics of harmful bacteria; specifically include:

对所述微藻的藻液进行取样,并对藻液中的细菌进行菌落培养,将培养所形成的各个菌落的菌落形态和所确定的有害细菌所对应的菌落形态进行对比。Sampling the algae fluid of the microalgae, performing colony culture on the bacteria in the algae fluid, and comparing the colony morphology of each colony formed by the culture with the colony morphology corresponding to the determined harmful bacteria.

通过在培养过程中对藻液中的细菌进行菌落培养,并将所形成的各个菌落的菌落形态与所确定的有害细菌进行比对,能够对所述藻液中的有害细菌进行实时监控,示例性的,当通过比对,发现所有菌落中的一种菌落与所确定的有害细菌的菌落形态相同时,则可以确定所述藻液具有所确定的有害细菌的理化特性。By carrying out colony culture to the bacteria in the algae liquid during the cultivation process, and comparing the colony morphology of each colony formed with the determined harmful bacteria, the harmful bacteria in the algae liquid can be monitored in real time, for example Specifically, when one of the colonies among all the colonies is found to have the same colony morphology as the determined harmful bacteria through comparison, it can be determined that the algae liquid has the physical and chemical characteristics of the determined harmful bacteria.

或者,对所述微藻的藻液进行取样,并对所述藻液中的细菌进行革兰氏染色,对革兰氏染色后的各个细菌的细胞形态和所呈现的颜色与所确定的有害细菌进行对比。Or, sampling the algae fluid of the microalgae, and carrying out Gram staining to the bacteria in the algae fluid, the cell morphology and the presented color of each bacterium after Gram staining and the determined harmful bacteria for comparison.

通过培养过程中对藻液中的细菌进行革兰氏染色,并对革兰氏染色后的各个细菌的细胞形态和所呈现的颜色与所确定的有害细菌进行比对,同样能够对所述藻液中的有害细菌进行实时监控,示例性的,当通过比对发现:有一种革兰氏染色后的细菌的细胞形态和所呈现的颜色与所确定的有害细菌一致时,则可以确定所述藻液中具有所确定的有害细菌的理化特性。By Gram staining the bacteria in the algae liquid during the culture process, and comparing the cell morphology and the presented color of each bacteria after Gram staining with the determined harmful bacteria, it is also possible to treat the algae. Real-time monitoring of harmful bacteria in the liquid, for example, when it is found through comparison: the cell shape and color presented by a Gram-stained bacterium are consistent with the determined harmful bacteria, then it can be determined that the The algae liquid has the physical and chemical properties of the identified harmful bacteria.

或者,对所述微藻的藻液进行取样,并对所述藻液中的细菌建立系统发育树,根据所建立的系统发育树对所确定的有害细菌的16SDNA序列设计特异性引物,根据所设计的特异性引物,通过PCR方法对所确定的有害细菌进行跟踪。Or, sampling the algal fluid of the microalgae, and establishing a phylogenetic tree for the bacteria in the algal fluid, designing specific primers for the 16SDNA sequence of the determined harmful bacteria according to the established phylogenetic tree, and designing specific primers according to the established phylogenetic tree. The designed specific primers are used to track the identified harmful bacteria by PCR method.

通过在培养过程中对所述藻液中的细菌建立系统发育树,并根据所建立的系统发育树对所确定的有害细菌的16SDNA序列设计特异性引物,根据所设计的特异性引物通过PCR方法对所确定的有害细菌进行跟踪,同样能够对所述藻液中的有害细菌进行实时监控。By establishing a phylogenetic tree for the bacteria in the algae liquid during the cultivation process, and designing specific primers for the 16SDNA sequence of the determined harmful bacteria according to the established phylogenetic tree, by PCR method according to the designed specific primers Tracking the determined harmful bacteria can also monitor the harmful bacteria in the algae liquid in real time.

优选的,通过荧光定量PCR方法对所确定的有害细菌进行标记跟踪。荧光定量PCR是(realtime fluores-cence quantitative PCR,RTFQ PCR),是由美国AppliedBiosystems公司推出的一种新定量试验技术,它是通过荧光染料或荧光标记的特异性的探针,对PCR产物进行标记跟踪,实时在线监控反应过程,结合相应的软件可以对产物进行分析,计算待测样品模板的初始浓度。刚开始时,探针结合在DNA任意一条单链上,PCR扩增时,Taq酶的5'端-3'端外切酶活性将探针酶切降解,使报告荧光基团和淬灭荧光基团分离,从而荧光监测系统可接收到荧光信号,即每扩增一条DNA链,就有一个荧光分子形成,实现了荧光信号的累积与PCR产物形成完全同步。实时荧光定量PCR的出现,极大地简化了定量检测的过程,而且真正实现了绝对定量。Preferably, the identified harmful bacteria are tagged and tracked by fluorescent quantitative PCR method. Fluorescent quantitative PCR (realtime fluores-cence quantitative PCR, RTFQ PCR) is a new quantitative test technology introduced by AppliedBiosystems in the United States. It uses fluorescent dyes or fluorescently labeled specific probes to label PCR products. Tracking, real-time online monitoring of the reaction process, combined with the corresponding software can analyze the product and calculate the initial concentration of the sample template to be tested. At the beginning, the probe is bound to any single strand of DNA. During PCR amplification, the 5'-3' end exonuclease activity of Taq enzyme will digest and degrade the probe, making the reporter fluorescent group and quenching fluorescence The group is separated, so that the fluorescence monitoring system can receive the fluorescent signal, that is, every time a DNA strand is amplified, a fluorescent molecule is formed, and the accumulation of the fluorescent signal is completely synchronized with the formation of the PCR product. The emergence of real-time fluorescence quantitative PCR greatly simplifies the process of quantitative detection, and truly realizes absolute quantification.

本发明的又一实施例中,所述步骤3)具体包括:In yet another embodiment of the present invention, the step 3) specifically includes:

根据所确定的有害细菌所对应的理化特性,判断所确定的有害细菌的耐酸碱性,以及所述有害细菌和所述微藻的耐酸碱性之间的差异,通过调节藻液的pH值对所确定的有害细菌进行治理。According to the physical and chemical characteristics corresponding to the determined harmful bacteria, judge the acid and alkali resistance of the determined harmful bacteria, and the difference between the acid and alkali resistance of the harmful bacteria and the microalgae, by adjusting the pH of the algae liquid value to control the identified harmful bacteria.

能够对所确定的有害细菌进行针对性治理,并最大程度上减少对所述微藻的伤害。示例性的,当通过上述革兰氏染色获取到所确定的有害细菌所对应的理化特性为杆状的革兰氏阴性细菌(该有害细菌的酸碱耐受范围在6.5-7.5之间),且所对应的微藻为栅藻时,则可以先调节藻液的pH值为4.0并保持一定的时间,以对所述有害细菌进行杀灭,并在处理完成之后再调节藻液的pH值至所述栅藻的正常生长范围内。The identified harmful bacteria can be controlled in a targeted manner, and the damage to the microalgae can be minimized. Exemplarily, when the physical and chemical properties corresponding to the determined harmful bacteria are rod-shaped Gram-negative bacteria (the acid-base tolerance range of the harmful bacteria is between 6.5-7.5) obtained through the above-mentioned Gram staining, And when the corresponding microalgae is Scenedesmus, the pH value of the algae liquid can be adjusted to 4.0 and kept for a certain period of time to kill the harmful bacteria, and the pH value of the algae liquid can be adjusted after the treatment is completed. To the normal growth range of described Scenedesmus.

或者,直接采用合适剂量的消毒剂对所确定的有害细菌进行杀灭。Or, directly use a suitable dose of disinfectant to kill the identified harmful bacteria.

同样能够对所确定的有害细菌进行针对性治理,并最大程度上减少对所述微藻的伤害。示例性的,当通过上述荧光定量PCR方法对所确定的有害细菌进行标记跟踪,发现藻液中的有害细菌的浓度为初始浓度的103左右,则可以根据该有害细菌的浓度,采用合适剂量的消毒剂对该有害细菌进行杀灭,合适计量的消毒剂是指能够正好将有害细菌杀灭而不对微藻造成伤害的剂量。It is also possible to carry out targeted control on the identified harmful bacteria and reduce the damage to the microalgae to the greatest extent. Exemplarily, when the determined harmful bacteria are marked and tracked by the above-mentioned fluorescent quantitative PCR method, and the concentration of harmful bacteria in the algal liquid is found to be about 103 of the initial concentration, then an appropriate dose can be used according to the concentration of the harmful bacteria A suitable disinfectant is used to kill the harmful bacteria, and a suitable dose of disinfectant refers to the dose that can just kill the harmful bacteria without causing damage to the microalgae.

其中,所述消毒剂可以为次氯酸钠。Wherein, the disinfectant can be sodium hypochlorite.

以下,将通过实施例对本发明进行详细说明,并通过实施例和对照组对本发明所产生的技术效果进行详细说明。Hereinafter, the present invention will be described in detail through examples, and the technical effects produced by the present invention will be described in detail through examples and comparison groups.

实施例1Example 1

所述实施例1以室外0.2m2跑道池养殖拟微绿球藻作为实验组,其中,在以下养殖过程中,保持各个实验组中所述拟微绿球藻的初始接种浓度均为3g/L,养殖天数均为7天,培养基采用海水培养基,光照情况为室外自然光照,微藻培养情况测定采用每24h测定干重的方式。Described embodiment 1 takes outdoor 0.2m 2 runway ponds to cultivate Nannochloropsis as experimental group, wherein, in the following breeding process, keep the initial inoculation concentration of Nannochloropsis described in each experimental group to be 3g/ L, the number of culture days is 7 days, the culture medium is seawater culture medium, the light conditions are outdoor natural light, and the microalgae culture conditions are measured by measuring the dry weight every 24h.

一、确定有害细菌1. Identify harmful bacteria

在室外0.2m2跑道池内接种拟微绿球藻,初始浓度为3g/L,取显微镜下已明显有细菌污染的藻液,取适量样品,使用无菌水采用倍比稀释法进行不同浓度的稀释,调整污染细菌的浓度为200个/ml,使用血球计数板观察细菌浓度。Inoculate Nannochloropsis pseudochloropsis in the outdoor 0.2m 2 raceway pool, the initial concentration is 3g/L, take the algae liquid that has obvious bacterial contamination under the microscope, take an appropriate amount of samples, and use sterile water to carry out different concentrations by doubling dilution method. Dilute, adjust the concentration of contaminating bacteria to 200/ml, and use a hemocytometer to observe the bacterial concentration.

取200微升涂相应的固体细菌营养平板,在33℃下在培养箱内进行细菌菌落培养。Take 200 microliters of the corresponding solid bacterial nutrient plate, and carry out bacterial colony cultivation in an incubator at 33 °C.

挑取上述进行菌落培养后所获得的细菌,并对各个菌落的细菌进行活化,将活化后的细菌分别提取DNA,采用细菌16S通用引物进行PCR方法扩增后进行DNA测序,根据所测得的DNA序列将所有的菌落进行细菌分类,并挑取不同菌种的细菌,分别与无菌拟微绿球藻按照细胞数为1:1的比例混合在33℃下进行共同培养,并观察各组拟微绿球藻的生长情况,若微藻不生长,或者藻细胞明显变白变黄,或者产生微藻絮凝现象,则确定这些细菌为有害细菌。Pick the bacteria obtained after the above-mentioned colony culture, and activate the bacteria in each colony, extract the DNA from the activated bacteria, use the bacterial 16S universal primer to perform PCR amplification, and then perform DNA sequencing. According to the measured The DNA sequence was used to classify all the colonies into bacteria, and bacteria of different species were picked and mixed with sterile Nannochloropsis at a ratio of 1:1 for co-cultivation at 33°C, and the bacteria of each group were observed. For the growth of Nannochloropsis, if the microalgae does not grow, or the algal cells obviously turn white and yellow, or produce microalgae flocculation, these bacteria are determined to be harmful bacteria.

结论:总共获得36个菌落,DNA测序后获得7种不同的菌种,通过将这7种不同的菌种分别与无菌拟微绿球藻进行共同培养,获得有一种细菌在与无菌拟微绿球藻进行共同培养的4天后藻细胞变白。Conclusion: A total of 36 colonies were obtained, and 7 different bacterial species were obtained after DNA sequencing. By co-cultivating these 7 different bacterial species with sterile Nannochloropsis respectively, we obtained a bacterium that was incompatible with sterile Pseudochloropsis The algal cells turned white after 4 days of co-cultivation of Nannochloropsis.

二、荧光定量PCR特异性引物的确定和验证2. Determination and verification of specific primers for fluorescent quantitative PCR

将所有的细菌建立系统发育树,对照所建立的系统发育树对有害细菌的16SDNA设计特异性引物。A phylogenetic tree was established for all bacteria, and specific primers were designed for 16SDNA of harmful bacteria in comparison with the established phylogenetic tree.

分别以100倍倍比稀释的目标DNA为模板确定荧光定量PCR的敏感性,其中,荧光定量PCR体系为25微升,荧光定量PCR酶为12.5微升,引物为1微升,模板分别为2微升,荧光定量PCR的反应条件为:首先在95℃保持30s,之后,95℃保持5s,60℃保持15s为一个循环,循环40次;结果参见图2所示,由图2可知:随着DNA稀释倍比的减小,荧光定量PCR的敏感性越强,循环数越少,越容易检出。因此,可以得出:荧光定量PCR的检测信号与DNA的浓度有关,检测方法敏感可靠,可进行定量分析。The 100-fold diluted target DNA was used as a template to determine the sensitivity of fluorescent quantitative PCR. Among them, the fluorescent quantitative PCR system was 25 microliters, the fluorescent quantitative PCR enzyme was 12.5 microliters, the primer was 1 microliter, and the template was 2 microliters. Microliter, the reaction conditions of fluorescent quantitative PCR are: first keep at 95°C for 30s, then keep at 95°C for 5s, and keep at 60°C for 15s as a cycle, and cycle 40 times; the results are shown in Figure 2, and it can be seen from Figure 2 that: As the DNA dilution ratio decreases, the sensitivity of fluorescent quantitative PCR is stronger, the number of cycles is smaller, and the detection is easier. Therefore, it can be concluded that the detection signal of fluorescent quantitative PCR is related to the concentration of DNA, the detection method is sensitive and reliable, and can be used for quantitative analysis.

分别以系统发育树亲缘关系较近的2个菌液DNA为模板,确定所设计的特异性引物的特异性。其中,荧光定量PCR体系为25微升,荧光定量PCR酶为12.5微升,引物为1微升,模板分别为2微升,荧光定量PCR的反应条件为:首先在95℃保持30s,之后,95℃保持5s,60℃保持15s为一个循环,循环40次;结果参见图3所示,由图3可知:特异基因荧光强度是非特异性基因荧光强度的106倍以上,因此,可以得知所设计的特异性引物具有非常高的特异性,可用于早期有害细菌的检出。The specificity of the designed specific primers was determined by using DNA from two bacterial liquids with close phylogenetic relationship as templates. Among them, the fluorescent quantitative PCR system is 25 microliters, the fluorescent quantitative PCR enzyme is 12.5 microliters, the primer is 1 microliter, and the template is 2 microliters respectively. The reaction conditions of the fluorescent quantitative PCR are: first keep at 95°C for 30s, and then, Keep at 95°C for 5s, keep at 60°C for 15s as a cycle, and cycle 40 times; the results are shown in Figure 3. From Figure 3, it can be seen that the fluorescence intensity of specific genes is more than 10 6 times that of non-specific genes. Therefore, it can be known that The designed specific primers have very high specificity and can be used for early detection of harmful bacteria.

三、微藻养殖过程中有害细菌的监控与治理3. Monitoring and treatment of harmful bacteria in the process of microalgae cultivation

在室外0.2m2跑道池内接种拟微绿球藻,初始浓度为3g/L,对拟微绿球藻进行养殖,并在养殖过程中根据上述确定的特异性引物,通过荧光定量PCR方法对藻液中的有害细菌进行标记跟踪,将其作为实验组对有害细菌进行监控;同时,设置一个同等养殖条件下的对照组,通过在养殖过程中通过显微镜镜检的方式对有害细菌进行监控。Inoculate Nannochloropsis pseudochloropsis in the outdoor 0.2m2 raceway pool, the initial concentration is 3g/L, culture Nannochloropsis, and in the cultivation process, according to the specific primers determined above, through the fluorescent quantitative PCR method. Harmful bacteria in the liquid are marked and tracked, and they are used as the experimental group to monitor the harmful bacteria; at the same time, a control group under the same culture conditions is set up to monitor the harmful bacteria through microscope inspection during the culture process.

通过监控发现,在通过荧光定量PCR的方法对有害细菌进行标记跟踪的过程中,在养殖3天后出现有害细菌的浓度为初始浓度的103倍左右,表明养殖3天后实验组出现了所确定的有害细菌,这时,采用2ppm的次氯酸钠对有害细菌进行治理,而在通过对照组对有害细菌进行监控时,在养殖5天后才观察到有细菌污染,这时,微藻的产量已经出现了下降趋势,并且需要采用10ppm的次氯酸钠对有害细菌进行治理。Through monitoring, it is found that in the process of labeling and tracking harmful bacteria by the method of fluorescence quantitative PCR, the concentration of harmful bacteria after 3 days of cultivation is about 103 times of the initial concentration, indicating that the experimental group has emerged after 3 days of cultivation. Harmful bacteria, at this time, use 2ppm sodium hypochlorite to treat harmful bacteria, and when the harmful bacteria are monitored through the control group, bacterial contamination is only observed after 5 days of cultivation. At this time, the production of microalgae has declined. trend, and need to use 10ppm of sodium hypochlorite to control harmful bacteria.

具体的,实验组和对照组分别在检出有害细菌当天所做的荧光强度和循环数的对应关系如图4所示,可见,对照组与实验组相比,有害细菌的检出具有一定的滞后性,不能及时对有害细菌进行针对性治理,会导致微藻产量的下降。其中,通过对实验组和对照组的微藻干重进行定期检测,可以获得如下表1所示结果。Specifically, the corresponding relationship between the fluorescence intensity and the cycle number of the experimental group and the control group on the day when harmful bacteria were detected is shown in Figure 4. It can be seen that the detection of harmful bacteria in the control group has a certain degree of difference compared with the experimental group. Hysteresis, unable to carry out targeted treatment of harmful bacteria in time, will lead to a decline in the production of microalgae. Among them, the results shown in Table 1 below can be obtained by regularly detecting the dry weight of microalgae in the experimental group and the control group.

表1Table 1

名称name 实验组产量(g/m2/天)Yield of experimental group (g/m 2 /day) 对照组产量(g/m2/天)Output of control group (g/m 2 /day) 养殖1天Breeding 1 day 7.617.61 7.77.7 养殖2天Breeding for 2 days 8.18.1 8.038.03 养殖3天Breeding for 3 days 7.927.92 7.797.79 养殖4天Breeding for 4 days 7.887.88 6.986.98 养殖5天Breeding for 5 days 8.068.06 4.884.88 养殖6天Breeding for 6 days 7.877.87 0.350.35 养殖7天Breeding for 7 days 8.138.13 0.750.75 平均产量average yield 7.947.94 5.215.21

由表1可知:实验组能够及时检出有害细菌,并在采用小剂量的次氯酸钠治理后,使得细菌得到有效控制并不对微藻的产量产生影响,而对照组在检出有害细菌时,细菌的数量已经很大,需要较大剂量的次氯酸钠进行治理,并且微藻的产量已经受到一定程度的影响,在通过较大剂量的次氯酸钠治理之后,会对微藻产生一定程度的伤害,使得微藻的产量急剧下降,且实验组的平均产量大于对照组。It can be seen from Table 1 that the experimental group can detect harmful bacteria in time, and after using a small dose of sodium hypochlorite treatment, the bacteria can be effectively controlled without affecting the production of microalgae, while the control group can detect harmful bacteria. The quantity is already very large, and a large dose of sodium hypochlorite is required for treatment, and the production of microalgae has been affected to a certain extent. After treatment with a large dose of sodium hypochlorite, it will cause a certain degree of damage to the microalgae, making the microalgae The yield dropped sharply, and the average yield of the experimental group was greater than that of the control group.

实施例2Example 2

所述实施例2以室外光程为10cm的板式反应器养殖栅藻作为实验组,其中,在以下养殖过程中,保持各个实验组中所述栅藻的初始接种浓度均为3g/L,养殖天数均为7天,培养基采用BG11,光照情况为室外自然光照,微藻培养情况测定采用每24h测定微藻干重的方式。In said embodiment 2, the plate reactor with an outdoor optical path of 10 cm is used to cultivate Scenedesmus as an experimental group, wherein, in the following cultivation process, the initial inoculation concentration of Scenedesmus in each experimental group is kept at 3 g/L, and the cultured Scenedesmus is 3 g/L. The number of days is 7 days, the medium is BG11, the light is outdoor natural light, and the microalgae culture is measured by measuring the dry weight of microalgae every 24 hours.

一、确定有害细菌1. Identify harmful bacteria

具体方法与实施例1相同,在此不再赘述。The specific method is the same as that in Embodiment 1, and will not be repeated here.

结论:总共获得41个菌落,分别将41个菌落中的细菌与无菌栅藻进行共同培养,可以得出:有两种细菌对栅藻有致害作用,其中一种细菌5天后可使微藻变白,另一种细菌4天后可使微藻细胞出现絮凝现象。Conclusion: A total of 41 colonies were obtained, and the bacteria in the 41 colonies were co-cultured with the sterile Scenedesmus. It can be concluded that there are two kinds of bacteria that are harmful to Scenedesmus, and one of them can kill the microalgae after 5 days. Blanching, another bacterium can flocculate the microalgae cells after 4 days.

二、有害细菌的理化特性的确定2. Determination of the physical and chemical characteristics of harmful bacteria

对上述所确定的有害细菌进行革兰氏染色,并观察所确定的有害细菌所对应的细胞形态和所呈现的颜色。Perform Gram staining on the harmful bacteria identified above, and observe the cell morphology and the color presented corresponding to the harmful bacteria identified above.

革兰氏染色结果:以上两种细菌均为杆状的革兰氏阴性细菌。PH值的耐受范围在6.5-7.5之间。Gram staining results: the above two bacteria are rod-shaped Gram-negative bacteria. The tolerance range of PH value is between 6.5-7.5.

三、微藻养殖过程中有害细菌的监控与治理3. Monitoring and treatment of harmful bacteria in the process of microalgae cultivation

在室外光程为10cm的板式反应器内接种栅藻,初始浓度为3g/L,对栅藻进行养殖,并在养殖过程中对藻液进行取样,并对藻液中的细菌进行革兰氏染色,将其作为实验组对有害细菌进行监控;同时,设置同等养殖条件下的对照组,通过在养殖过程中通过显微镜镜检的方式对有害细菌进行监控。Scenedesmus was inoculated in a plate reactor with an outdoor light path of 10cm, the initial concentration was 3g/L, and the Scenedesmus was cultured, and the algae liquid was sampled during the cultivation process, and the bacteria in the algae liquid were tested for Gram. Staining, it is used as an experimental group to monitor harmful bacteria; at the same time, a control group under the same culture conditions is set up, and harmful bacteria are monitored by means of microscope inspection during the culture process.

通过监控发现,在通过革兰氏染色对有害细菌进行监控的过程中,在养殖第3天就检出藻液中出现了所确定的有害细菌,这时,通过调节pH值至4.0保持0.5h,之后调节pH至微藻正常养殖范围的方法,对有害细菌进行治理。而在通过对照组对有害细菌进行监控时,在养殖第5天时才观察到有细菌污染,这时,微藻的产量已经出现了下降趋势,通过调节pH值至4.0,并每隔10min取样镜检的方式对有害细菌进行治理,当镜检没有存活的细菌时,共保持1.5h,之后调节pH至微藻正常养殖范围内的方法对有害细菌进行治理。It is found through monitoring that in the process of monitoring harmful bacteria by Gram staining, it is detected that the identified harmful bacteria appear in the algae liquid on the 3rd day of cultivation, at this time, by adjusting the pH value to 4.0 to maintain 0.5h , and then adjust the pH to the normal culture range of microalgae to control harmful bacteria. When monitoring harmful bacteria through the control group, bacterial contamination was only observed on the 5th day of cultivation. At this time, the production of microalgae has shown a downward trend. Harmful bacteria are treated by means of microscopic inspection. When there is no surviving bacteria in the microscopic examination, it is kept for 1.5 hours, and then the method of adjusting the pH to the normal culture range of microalgae is used to control harmful bacteria.

可见,对照组与实验组相比,有害细菌的检出具有一定的滞后性,不能及时对有害细菌进行针对性治理,会导致微藻产量的下降。其中,通过对实验组和对照组的微藻干重进行定期检测,可以获得如下表2所示结果。It can be seen that compared with the experimental group, the detection of harmful bacteria has a certain lag in the control group, and the targeted treatment of harmful bacteria cannot be carried out in time, which will lead to a decline in the production of microalgae. Among them, the results shown in Table 2 below can be obtained by regularly detecting the dry weight of microalgae in the experimental group and the control group.

表2Table 2

名称name 实验组产量(g/m2/天)Yield of experimental group (g/m 2 /day) 对照组产量(g/m2/天)Output of control group (g/m 2 /day) 养殖1天Breeding 1 day 8.348.34 8.568.56 养殖2天Breeding for 2 days 8.218.21 8.38.3 养殖3天Breeding for 3 days 7.917.91 7.977.97 养殖4天Breeding for 4 days 7.787.78 6.836.83 养殖5天Breeding for 5 days 7.887.88 4.694.69 养殖6天Breeding for 6 days 7.797.79 0.360.36 养殖7天Breeding for 7 days 8.028.02 0.650.65 平均产量average yield 7.997.99 5.345.34

由表2可知:实验组能够及时检出有害细菌,并使用短时间降低pH的方法进行治理,使得细菌得到有效控制并不对微藻的产量产生影响,而对照组在检出有害细菌时,细菌的数量已经很大,需要长时间降低pH的方法进行治理,并且微藻的产量已经受到一定程度的影响,在通过长时间降低pH的方法进行治理之后,会对微藻产生一定程度的伤害,使得微藻的产量也出现了急剧下降,且所述实验组的平均产量大于对照组。It can be seen from Table 2 that the experimental group can detect harmful bacteria in time, and use the method of lowering the pH for a short time for treatment, so that the bacteria can be effectively controlled without affecting the production of microalgae, while in the control group, when harmful bacteria are detected, the bacteria The quantity is already very large, and the method of lowering the pH for a long time is required for treatment, and the production of microalgae has been affected to a certain extent. After treatment by the method of lowering the pH for a long time, it will cause a certain degree of damage to the microalgae. As a result, the yield of microalgae also decreased sharply, and the average yield of the experimental group was greater than that of the control group.

实施例3Example 3

所述实施例3以室外2m2跑道池养殖小球藻作为实验组,其中,在以下养殖过程中,保持各个实验组中所述小球藻的初始接种浓度均为3g/L,养殖天数均为7天,培养基采用BG11,光照情况为室外自然光照,微藻培养情况测定采用每24h测定微藻干重的方式。Described embodiment 3 takes outdoor 2m 2 runway pond culture chlorella as experimental group, wherein, in following culture process, keep the initial inoculum concentration of described chlorella in each experimental group to be 3g/L, culture days average For 7 days, BG11 was used as the medium, the light was outdoor natural light, and the microalgae culture was measured by measuring the dry weight of microalgae every 24 hours.

一、确定有害细菌1. Identify harmful bacteria

具体方法与实施例1相同,在此不再赘述。The specific method is the same as that in Embodiment 1, and will not be repeated here.

结论:总共获得35个菌落,并分别进行DNA测序获得5种不同种类的细菌,分别将5种不同种类的菌种与无菌小球藻进行共同培养,可以得出:有一种细菌对小球藻有致害作用,4天后可使藻细胞变白。Conclusion: A total of 35 colonies were obtained, and DNA sequencing was carried out to obtain 5 different types of bacteria. The 5 different types of bacteria were co-cultured with sterile Chlorella. Algae are harmful and can turn algae cells white after 4 days.

二、有害细菌的理化特性的确定2. Determination of the physical and chemical characteristics of harmful bacteria

观察上述所确定的有害细菌的菌落形态为湿润、粘稠,易挑起、圆形红色小菌落。Observe that the colony form of the above-mentioned harmful bacteria is moist, sticky, easy to stir up, small round red colonies.

三、微藻养殖过程中有害细菌的监控与治理3. Monitoring and treatment of harmful bacteria in the process of microalgae cultivation

在室外2m2跑道池内接种小球藻,初始浓度为3g/L,对小球藻进行养殖,并在养殖过程中对藻液进行取样,并对藻液中的细菌进行菌落培养,将所有的菌落与所确定的有害细菌的菌落形态进行比对,将其作为实验组对有害细菌进行监控;同时,设置同等养殖条件下的对照组,通过在养殖过程中通过显微镜镜检的方式对有害细菌进行监控。Inoculate Chlorella in the outdoor 2m2 raceway pool, the initial concentration is 3g/L, culture Chlorella, and sample the algae liquid during the cultivation process, and carry out colony culture on the bacteria in the algae liquid, and all the The colony is compared with the colony form of the determined harmful bacteria, and it is used as the experimental group to monitor the harmful bacteria; at the same time, a control group under the same culture conditions is set up, and the harmful bacteria are detected by microscope inspection during the culture process. to monitor.

通过监控发现,在通过实验组对有害细菌进行监控的过程中,在养殖第3天就检出藻液中出现了所确定的有害细菌,这时,通过采用2ppm的次氯酸钠,对有害细菌进行治理。而在通过对照组对有害细菌进行监控时,在养殖第5天时才观察到有细菌污染,这时,微藻的产量已经出现了下降趋势,并且需要采用10ppm的次氯酸钠对有害细菌进行治理。Through monitoring, it was found that in the process of monitoring harmful bacteria through the experimental group, the identified harmful bacteria were detected in the algae liquid on the third day of cultivation. At this time, the harmful bacteria were controlled by using 2ppm sodium hypochlorite . When the harmful bacteria were monitored by the control group, bacterial contamination was observed on the 5th day of cultivation. At this time, the production of microalgae had shown a downward trend, and 10ppm of sodium hypochlorite was needed to control the harmful bacteria.

可见,对照组与实验组相比,有害细菌的检出具有一定的滞后性,不能及时对有害细菌进行针对性治理,会导致微藻产量的下降。其中,通过对实验组和对照组的微藻干重进行定期检测,可以获得如下表3所示结果。It can be seen that compared with the experimental group, the detection of harmful bacteria has a certain lag in the control group, and the targeted treatment of harmful bacteria cannot be carried out in time, which will lead to a decline in the production of microalgae. Among them, by regularly detecting the dry weight of microalgae in the experimental group and the control group, the results shown in Table 3 below can be obtained.

表3table 3

名称name 实验组产量(g/m2/天)Yield of experimental group (g/m 2 /day) 对照组产量(g/m2/天)Output of control group (g/m 2 /day) 养殖1天Breeding 1 day 8.228.22 8.218.21 养殖2天Breeding for 2 days 8.048.04 8.138.13 养殖3天Breeding for 3 days 7.917.91 7.867.86 养殖4天Breeding for 4 days 6.786.78 6.736.73 养殖5天Breeding for 5 days 6.546.54 4.584.58 养殖6天Breeding for 6 days 7.077.07 0.530.53 养殖7天Breeding for 7 days 7.027.02 0.470.47 平均产量average yield 7.377.37 5.225.22

由表3可知:实验组能够及时检出有害细菌,并在采用小剂量的次氯酸钠治理后,使得细菌得到有效控制并不对微藻的产量产生影响,而对照组在检出有害细菌时,细菌的数量已经很大,需要较大剂量的次氯酸钠进行治理,并且微藻的产量已经受到一定程度的影响,在通过较大剂量的次氯酸钠治理之后,会对微藻产生一定程度的伤害,使得微藻的产量急剧下降,且实验组的平均产量大于对照组。It can be seen from Table 3 that the experimental group can detect harmful bacteria in time, and after using a small dose of sodium hypochlorite treatment, the bacteria can be effectively controlled without affecting the production of microalgae, while the control group can detect harmful bacteria. The quantity is already very large, and a large dose of sodium hypochlorite is required for treatment, and the production of microalgae has been affected to a certain extent. After treatment with a large dose of sodium hypochlorite, it will cause a certain degree of damage to the microalgae, making the microalgae The yield dropped sharply, and the average yield of the experimental group was greater than that of the control group.

综上所述,通过事先在微藻养殖过程中确定所述微藻污染的有害细菌,并相应地获取所确定的各个有害细菌所对应的理化特性,这样一来,通过在对微藻进行养殖的过程中,对所述微藻的藻液进行实时监控,判断所述藻液中是否具有所确定的有害细菌所对应的理化特性,能够对所述藻液中出现的细菌中的有害细菌进行实时监控,这样一来,当监控到所述藻液中具有所确定的有害细菌的理化特性时,根据所确定的有害细菌所对应的理化特性,对所述有害细菌进行针对性治理,能够避免有害细菌治理不及时所带来的微藻产量下降,以及不能对有害细菌进行针对性治理所带来的微藻产量下降的情况发生,从而能够对有害细菌进行早期治理,最大程度上提高微藻的产量,同时,与现有技术中在养殖过程中通过镜检对有害细菌进行监控相比,克服了现有技术中通过镜检的滞后性较强的缺陷,在污染的早期就能够检出有害细菌,避免有害细菌对微藻的产量产生影响,同时还能够避免有害细菌数量增大所带来的治理方法容易对微藻产生伤害的缺陷发生。In summary, by determining the harmful bacteria polluted by the microalgae in the process of microalgae cultivation in advance, and correspondingly obtaining the physical and chemical characteristics corresponding to each of the determined harmful bacteria, in this way, by cultivating the microalgae During the process, the algae liquid of the microalgae is monitored in real time to determine whether the algae liquid has the physical and chemical characteristics corresponding to the determined harmful bacteria, and the harmful bacteria in the bacteria that appear in the algae liquid can be detected. Real-time monitoring, in this way, when the physical and chemical characteristics of the determined harmful bacteria are monitored in the algae liquid, the harmful bacteria are targeted according to the corresponding physical and chemical characteristics of the determined harmful bacteria, which can avoid The decrease of microalgae production caused by untimely treatment of harmful bacteria and the decrease of microalgae production caused by the inability to carry out targeted treatment of harmful bacteria occur, so that early treatment of harmful bacteria can be carried out to maximize the improvement of microalgae production. At the same time, compared with the monitoring of harmful bacteria through microscopic examination in the prior art in the breeding process, it overcomes the relatively strong defect of hysteresis through microscopic examination in the prior art, and can be detected in the early stage of pollution Harmful bacteria, avoiding the impact of harmful bacteria on the production of microalgae, and at the same time avoiding the defect that the treatment method caused by the increase in the number of harmful bacteria is easy to cause damage to microalgae.

以上所述,仅为本发明的具体实施方式,但本发明的保护范围并不局限于此,任何熟悉本技术领域的技术人员在本发明揭露的技术范围内,可轻易想到变化或替换,都应涵盖在本发明的保护范围之内。因此,本发明的保护范围应以所述权利要求的保护范围为准。The above is only a specific embodiment of the present invention, but the scope of protection of the present invention is not limited thereto. Anyone skilled in the art can easily think of changes or substitutions within the technical scope disclosed in the present invention. Should be covered within the protection scope of the present invention. Therefore, the protection scope of the present invention should be determined by the protection scope of the claims.

Claims (9)

1.一种微藻养殖过程中有害细菌的防治方法,其特征在于,包括:1. A method for preventing and treating harmful bacteria in the microalgae culture process, characterized in that, comprising: 步骤1)在微藻进行养殖过程中,确定所述微藻已污染的有害细菌,并获取所确定的有害细菌所对应的理化特性;Step 1) During the microalgae cultivation process, determine the harmful bacteria that the microalgae has polluted, and obtain the physical and chemical characteristics corresponding to the determined harmful bacteria; 步骤2)对所述微藻进行养殖,并在养殖过程中,对所述微藻的藻液进行监控,判断所述藻液中是否具有所确定的有害细菌所对应的理化特性;Step 2) cultivating the microalgae, and monitoring the algae liquid of the microalgae during the cultivation process, and judging whether the algae liquid has the physical and chemical characteristics corresponding to the determined harmful bacteria; 若确定所述藻液中具有所确定的有害细菌所对应的理化特性,则,If it is determined that the algae liquid has the corresponding physical and chemical characteristics of the determined harmful bacteria, then, 步骤3)根据所确定的有害细菌所对应的理化特性,对所述有害细菌进行针对性治理。Step 3) According to the physical and chemical characteristics corresponding to the determined harmful bacteria, carry out targeted treatment on the harmful bacteria. 2.根据权利要求1所述的防治方法,其特征在于,2. The control method according to claim 1, characterized in that, 所述方法还包括:The method also includes: 当监控到所述微藻的藻液中的细菌数量增大,或者,在所述步骤3)之后,增大监控的频率。When it is monitored that the number of bacteria in the algae fluid of the microalgae increases, or, after the step 3), the frequency of monitoring is increased. 3.根据权利要求1所述的防治方法,其特征在于,3. The control method according to claim 1, characterized in that, 在微藻进行养殖过程中,确定所述微藻已污染的有害细菌;具体包括:During the microalgae cultivation process, determine the harmful bacteria that the microalgae has polluted; specifically include: 对所述微藻进行养殖,并在所述微藻污染有细菌,和/或,所述微藻的生物增量开始降低时,对所述微藻的藻液进行取样,并对藻液中出现的细菌进行菌落培养;Cultivate the microalgae, and when the microalgae is contaminated with bacteria, and/or, when the bioincrease of the microalgae begins to decrease, the algae liquid of the microalgae is sampled, and the algae liquid in the algae liquid is Bacteria that emerged were colonized; 将培养所获得的来自不同菌落的细菌分别与无菌微藻在不同的实验组中进行共同养殖,若在养殖过程中第i实验组中的无菌微藻出现生物量下降,藻细胞颜色变白或变黄以及藻细胞发生絮凝中的至少一种现象,则确定所述第i实验组中的细菌为所述微藻已污染的有害细菌,其中,i为大于等于1的自然数,所述第i实验组为所有实验组中的任意一组。Bacteria from different colonies obtained from the culture were co-cultivated with sterile microalgae in different experimental groups. If the biomass of the sterile microalgae in the i-th experimental group decreased during the cultivation process, the color of the algal cells changed. Whitening or yellowing and at least one phenomenon in the flocculation of algal cells, then it is determined that the bacteria in the i-th experimental group are harmful bacteria that have been polluted by the microalgae, wherein, i is a natural number greater than or equal to 1, and the The i-th experimental group is any one of all experimental groups. 4.根据权利要求3所述的防治方法,其特征在于,4. The control method according to claim 3, characterized in that, 获取所确定的有害细菌所对应的理化特性;具体包括:Obtain the physicochemical properties corresponding to the identified harmful bacteria; specifically include: 观察所确定的各个有害细菌所对应的菌落形态,以获取各个有害细菌所对应的理化特性;或者,Observing the colony morphology corresponding to each of the identified harmful bacteria to obtain the physicochemical characteristics corresponding to each harmful bacteria; or, 对所确定的各个有害细菌进行革兰氏染色,并观察革兰氏染色后的各个有害细菌的细胞形态以及所呈现的颜色,以获取各个有害细菌所对应的理化特性;或者,Perform Gram staining on each of the identified harmful bacteria, and observe the cell morphology and color of each harmful bacteria after Gram staining, so as to obtain the corresponding physical and chemical characteristics of each harmful bacteria; or, 分别对所确定的每一个有害细菌进行DNA序列测定,并根据各个有害细菌所对应的DNA序列确定各个有害细菌所属的属,以获取各个有害细菌所对应的理化特性。The DNA sequence of each identified harmful bacterium is determined separately, and the genus of each harmful bacterium is determined according to the DNA sequence corresponding to each harmful bacterium, so as to obtain the corresponding physical and chemical characteristics of each harmful bacterium. 5.根据权利要求4所述的防治方法,其特征在于,5. The control method according to claim 4, characterized in that, 根据各个有害细菌所对应的DNA序列,并通过NCBI数据库查询,以确定各个有害细菌所属的属。According to the DNA sequence corresponding to each harmful bacterium, and through the NCBI database query, to determine the genus to which each harmful bacterium belongs. 6.根据权利要求3所述的防治方法,其特征在于,6. The control method according to claim 3, characterized in that, 将培养所获得的来自不同菌落的细菌分别与无菌微藻在不同的实验组中进行共同养殖之前,所述方法还包括:Before the bacteria from different bacterium colonies obtained by culturing are cultured together with sterile microalgae respectively in different experimental groups, the method also includes: 分别对来自不同菌落的细菌进行DNA序列测定,并根据DNA序列测定结果确定来自不同菌落的细菌是否为同一种细菌,以筛选出所有菌落中与无菌微藻进行共同养殖的不同菌种,并根据筛选出的不同菌种,确定分别对来自不同菌落的细菌与所述无菌微藻进行共同养殖的实验组数。Carry out DNA sequence determination to the bacteria from different colonies, and determine whether the bacteria from different colonies are the same bacteria according to the DNA sequence determination results, to screen out the different bacterial species that are co-cultivated with sterile microalgae in all colonies, and According to the different strains screened out, determine the number of experimental groups for co-culturing bacteria from different colonies and the sterile microalgae. 7.根据权利要求1-6任一项所述的防治方法,其特征在于,7. The control method according to any one of claims 1-6, characterized in that, 对所述微藻的藻液进行监控,并判断所述藻液中是否具有所确定的有害细菌所对应的理化特性;具体包括:Monitoring the algae liquid of the microalgae, and judging whether the algae liquid has the physical and chemical characteristics corresponding to the identified harmful bacteria; specifically including: 对所述微藻的藻液进行取样,并对所述藻液所污染的细菌进行菌落培养,将培养所获得的各个菌落的菌落形态和所确定的有害细菌所对应的菌落形态进行对比;或者,Sampling the algal fluid of the microalgae, and performing colony culture on the bacteria contaminated by the algae fluid, and comparing the colony morphology of each colony obtained from the culture with the colony morphology corresponding to the determined harmful bacteria; or , 对所述微藻的藻液进行取样,并对所述藻液中的细菌进行革兰氏染色,将革兰氏染色后的各个细菌所对应的细胞形态和所呈现的颜色与所确定的有害细菌进行对比;或者,Sampling the algae fluid of the microalgae, and carrying out Gram staining to the bacteria in the algae fluid, and comparing the cell morphology and the color presented by each bacterium after Gram staining with the determined harmful bacteria for comparison; or, 对所述微藻的藻液进行取样,并对所述藻液中的细菌建立系统发育树,根据所建立的系统发育树对所确定的有害细菌的16SDNA序列设计特异性引物,根据所设计的特异性引物,通过PCR方法对所确定的有害细菌进行跟踪。Sampling the algal liquid of the microalgae, and establishing a phylogenetic tree for the bacteria in the algal liquid, designing specific primers for the 16SDNA sequence of the determined harmful bacteria according to the established phylogenetic tree, and designing specific primers according to the designed phylogenetic tree. Specific primers are used to track the identified harmful bacteria by PCR method. 8.根据权利要求7所述的防治方法,其特征在于,8. The control method according to claim 7, characterized in that, 通过荧光定量PCR方法对所确定的有害细菌进行标记跟踪。The identified harmful bacteria were tagged and tracked by fluorescent quantitative PCR method. 9.根据权利要1所述的防治方法,其特征在于,9. The control method according to claim 1, characterized in that, 所述步骤3)具体包括:Described step 3) specifically comprises: 根据所确定的有害细菌所对应的理化特性,判断所确定的有害细菌的耐酸碱性,以及所述有害细菌和所述养殖微藻的耐酸碱性之间的差异,通过调节藻液的pH值对所确定的有害细菌进行治理;或者,According to the physical and chemical characteristics corresponding to the determined harmful bacteria, judge the acid and alkali resistance of the determined harmful bacteria, and the difference between the acid and alkali resistance of the harmful bacteria and the cultured microalgae, by adjusting the pH to remediate the identified harmful bacteria; or, 直接采用合适剂量的消毒剂对所确定的有害细菌进行杀灭。Directly use the appropriate dose of disinfectant to kill the identified harmful bacteria.
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EP2292776A1 (en) * 2000-07-31 2011-03-09 Danisco US Inc. Manipulation of genes of the mevalonate and isoprenoid pathways to create novel traits in transgenic organisms
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