CN108017161A - Preparation method of dominant microorganism solid microbial inoculum for river water pollution treatment - Google Patents
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- 239000007787 solid Substances 0.000 title claims abstract description 19
- 238000003903 river water pollution Methods 0.000 title claims abstract description 17
- 238000002360 preparation method Methods 0.000 title claims abstract description 14
- 244000005700 microbiome Species 0.000 title claims abstract description 13
- 239000002068 microbial inoculum Substances 0.000 title abstract 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 45
- 239000001963 growth medium Substances 0.000 claims abstract description 14
- 238000000034 method Methods 0.000 claims description 21
- 239000002609 medium Substances 0.000 claims description 17
- 230000001580 bacterial effect Effects 0.000 claims description 15
- 239000003795 chemical substances by application Substances 0.000 claims description 15
- 235000013882 gravy Nutrition 0.000 claims description 15
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 claims description 12
- 235000015278 beef Nutrition 0.000 claims description 12
- 235000008429 bread Nutrition 0.000 claims description 12
- 230000000813 microbial effect Effects 0.000 claims description 12
- 239000000203 mixture Substances 0.000 claims description 9
- 241000894006 Bacteria Species 0.000 claims description 7
- 238000002791 soaking Methods 0.000 claims description 7
- 229920000742 Cotton Polymers 0.000 claims description 6
- 239000001888 Peptone Substances 0.000 claims description 6
- 108010080698 Peptones Proteins 0.000 claims description 6
- 239000000654 additive Substances 0.000 claims description 6
- 230000000996 additive effect Effects 0.000 claims description 6
- 239000000463 material Substances 0.000 claims description 6
- 235000019319 peptone Nutrition 0.000 claims description 6
- 239000011780 sodium chloride Substances 0.000 claims description 6
- 230000003254 anti-foaming effect Effects 0.000 claims description 4
- 229920001817 Agar Polymers 0.000 claims description 3
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims description 3
- 239000008272 agar Substances 0.000 claims description 3
- 238000001816 cooling Methods 0.000 claims description 3
- 235000013372 meat Nutrition 0.000 claims description 3
- 238000011177 media preparation Methods 0.000 claims description 3
- 235000015097 nutrients Nutrition 0.000 claims description 3
- 230000035755 proliferation Effects 0.000 claims description 3
- 229920002545 silicone oil Polymers 0.000 claims description 3
- 238000003756 stirring Methods 0.000 claims description 3
- 238000010792 warming Methods 0.000 claims description 3
- 238000010170 biological method Methods 0.000 abstract description 2
- 238000003860 storage Methods 0.000 abstract description 2
- 238000012258 culturing Methods 0.000 abstract 1
- 238000005273 aeration Methods 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 230000015271 coagulation Effects 0.000 description 2
- 238000005345 coagulation Methods 0.000 description 2
- 230000006866 deterioration Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 239000013049 sediment Substances 0.000 description 2
- 239000010865 sewage Substances 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- DNJIEGIFACGWOD-UHFFFAOYSA-N ethanethiol Chemical compound CCS DNJIEGIFACGWOD-UHFFFAOYSA-N 0.000 description 1
- 238000009776 industrial production Methods 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 239000002957 persistent organic pollutant Substances 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 230000004083 survival effect Effects 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
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- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
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- C12N1/00—Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/007—Contaminated open waterways, rivers, lakes or ponds
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Abstract
Description
技术领域technical field
本发明涉及污染治理技术领域,具体为一种用于河涌水污染治理的优势微生物固体菌剂制备方法。The invention relates to the technical field of pollution control, in particular to a method for preparing a dominant microbial solid bacterial agent for river water pollution control.
背景技术Background technique
随着社会经济的发展,人们生活水平的提高,人口密集带来生活污水,小工厂散布带来工业废水,这些未经处理的生活污水、未经处理或处理不达标的工业生产废水排放亦随之增多,长时间不间断的排污,当有机污染物超出河涌水体所能容纳的自然净化的限度,水中的溶解氧会迅速被消耗而呈缺氧状态,河涌水体变得富营养化,水体便发黑发臭,由于缺氧,原生态生物的生存直接受到威胁,直至死亡、尸体腐败,进一步污染水体及出现恶臭,如此恶性循环不断,使河涌生态遭到彻底的破坏。With the development of social economy and the improvement of people's living standards, the dense population brings domestic sewage, and the spread of small factories brings industrial wastewater. These untreated domestic sewage, untreated or untreated industrial production wastewater are also discharged with When the organic pollutants exceed the limit of natural purification that the river water body can hold, the dissolved oxygen in the water will be consumed rapidly and become anoxic, and the river water body will become eutrophic. The water body turns black and smelly. Due to the lack of oxygen, the survival of the original ecological organisms is directly threatened, until death, corpse decay, further pollution of the water body and stench, such a vicious cycle continues, completely destroying the ecology of the river.
目前,河涌治理方法主要有截流、疏浚、活水循环(即引水增流)、河道人工增氧曝气、底泥覆盖、混凝、生态修复等方法。这些方法虽在一定程度上缓解了河涌水环境恶化的问题,但存在许多不足之处。At present, the river surge control methods mainly include closure, dredging, running water circulation (that is, water diversion to increase flow), artificial aeration of river channels, sediment covering, coagulation, ecological restoration and other methods. Although these methods have alleviated the problem of the deterioration of the river gushing water environment to a certain extent, there are many shortcomings.
发明内容Contents of the invention
本发明的目的在于提供一种用于河涌水污染治理的优势微生物固体菌剂制备方法,以解决上述背景技术中提出的目前,河涌治理方法主要有截流、疏浚、活水循环(即引水增流)、河道人工增氧曝气、底泥覆盖、混凝、生态修复等方法。这些方法虽在一定程度上缓解了河涌水环境恶化的问题,但存在许多不足之处的问题。The object of the present invention is to provide a kind of preponderant microbial solid bacterial agent preparation method that is used for river water pollution control, to solve the present problem that proposes in the above-mentioned background technology, river surge treatment method mainly contains interception, dredging, running water circulation (being water diversion to increase flow) ), artificial aeration of river channels, sediment covering, coagulation, ecological restoration and other methods. Although these methods have alleviated the problem of the deterioration of the river gushing water environment to a certain extent, there are many deficiencies.
为实现上述目的,本发明提供如下技术方案:一种用于河涌水污染治理的优势微生物固体菌剂制备方法,该用于河涌水污染治理的优势微生物固体菌剂制备方法的具体制备步骤如下:In order to achieve the above object, the present invention provides the following technical solutions: a method for preparing a solid microbial agent for river water pollution control, the specific preparation steps of the solid microbial agent for river water pollution control are as follows:
S1:培养基制备:取500g牛肉,将获取的500g牛肉浸泡在800ml-850ml 的水中,将浸泡的牛肉在20-25摄氏度的温度环境下保持浸泡8-10小时,将浸泡后的肉过滤保留肉汁,在肉汁内每100ml加入300g蛋白胨、4-5gNaCl,将加入蛋白胨和氯化钠的肉汁加热混合,直至肉汁浓缩为浓稠状态,加入苏打继续搅拌,检测肉汁的PH值为7.0-7.2时即可,将调节PH后的培养基底料通过高温蒸汽的方式进行灭菌,灭菌后的培养基底料以每100ml加入2.2g-2.4g 的琼脂,混合均匀;S1: Culture medium preparation: Take 500g of beef, soak the obtained 500g of beef in 800ml-850ml of water, keep the soaked beef at 20-25 degrees Celsius for 8-10 hours, filter the soaked meat For gravy, add 300g of peptone and 4-5g of NaCl per 100ml of the gravy, heat and mix the gravy with peptone and sodium chloride until the gravy is concentrated into a thick state, add soda and continue stirring, and check the pH value of the gravy at 7.0-7.2 That is, the PH-adjusted medium base material is sterilized by high-temperature steam, and 2.2g-2.4g of agar is added to the sterilized medium base material per 100ml, and mixed evenly;
S2:培养微生物:在步骤S1制备完毕的培养基上均匀接种不同种类的菌种,将接种菌种后的培养基放置在温度为25-30摄氏度的范围内培养,培养的天数为15天,培养基上均匀长出菌落,在培养的过程中每隔3天加入酸碱度调节剂,加入酸碱度调节剂K2HPO4时进行PH测量,直至PH值再次恢复至7.0- 7.2时即可;S2: Cultivate microorganisms: uniformly inoculate different types of strains on the culture medium prepared in step S1, place the culture medium after the inoculated strains at a temperature of 25-30 degrees Celsius for cultivation, and the number of days for cultivation is 15 days. Colonies grow evenly on the culture medium, add a pH regulator every 3 days during the cultivation process, and measure the pH when adding the pH regulator K 2 HPO 4 until the pH value returns to 7.0-7.2 again;
S3:注入河道污染的泥水,针对性选择菌种:从需要进行治理的河流段选取河底的泥和底部距离地面20cm范围内的河水,将取出的河水与河泥混合搅拌均匀,将混合均匀的泥水浇入步骤S2中含有菌落的培养基内,150ml的培养基内加入30-35ml的泥水,将注入泥水的培养基继续培养3-5天,培养过程中观察并取出死亡的菌落,培养至8-10天时,将培养后活着的菌落取出;S3: Inject the muddy water polluted by the river, and select the bacteria in a targeted manner: select the mud at the bottom of the river and the river water within 20cm from the bottom of the ground from the river section that needs to be treated, mix the taken out river water with the river mud, and mix evenly Pour the muddy water into the medium containing the colonies in step S2, add 30-35ml of muddy water into the 150ml medium, continue to cultivate the medium injected with muddy water for 3-5 days, observe and take out the dead bacterium colonies during the cultivation, and cultivate At 8-10 days, the living bacterial colonies after cultivation were taken out;
S4:增殖微生物:将剩余的泥水分别按照100ml的量进行等分储放,在泥水中加入步骤S3中取出的活着的菌落,且每100ml中加入4-5组菌落,将菌落分散培养3-5天即可,将培养后的泥水中加入面包,将棉包放置在泥水中浸泡2-3小时,菌落发现营养物质则吸附在面包上,取出面包即可将吸附在面包上的菌落取出,通过降温的方式对菌落冷藏,需要使用将吸附有菌落的棉包取出回暖即可将菌落复活。S4: Proliferation of microorganisms: Store the remaining muddy water in equal parts according to the amount of 100ml, add the living colonies taken out in step S3 to the muddy water, and add 4-5 groups of colonies per 100ml, and disperse and cultivate the colonies for 3- After 5 days, add the cultivated mud water to the bread, put the cotton bag in the mud water and soak for 2-3 hours, the colony finds nutrients and then adsorbs on the bread, take out the bread to remove the colonies adsorbed on the bread, The colony is refrigerated by cooling down, and the colony can be revived by taking out the cotton bag that has adsorbed the colony and warming it up.
优选的,所述步骤S1中培养基制备的过程中还要加入消泡添加剂。Preferably, an antifoaming additive is also added during the preparation of the medium in the step S1.
优选的,所述消泡添加剂为乳化硅油。Preferably, the defoaming additive is emulsified silicone oil.
优选的,所述步骤S1中对牛肉的浸泡温度为25摄氏度,浸泡时间为9.5 小时。Preferably, the soaking temperature of the beef in the step S1 is 25 degrees Celsius, and the soaking time is 9.5 hours.
优选的,所述酸碱度调节剂为K2HPO4或者KH2PO4。Preferably, the pH regulator is K 2 HPO 4 or KH 2 PO 4 .
优选额,所述步骤S4中对菌落冷藏的温度为-5℃-0摄氏度。Preferably, the temperature for refrigerating the colony in the step S4 is -5°C-0°C.
与现有技术相比,本发明的有益效果是:该用于河涌水污染治理的优势微生物固体菌剂制备方法,通过菌种对河道污染的治理,生物法治理绿色环保,能够长期对河道污染进行治理,通过冷藏式的存储方式,使得固体菌剂方便保存和运输。Compared with the prior art, the beneficial effects of the present invention are: the preparation method of the advantageous microbial solid bacterial agent used for the treatment of river water pollution can control the river pollution by the bacteria, and the biological method is green and environmentally friendly, and can prevent the river pollution for a long time. For treatment, through the refrigerated storage method, the solid bacterial agent is conveniently stored and transported.
附图说明Description of drawings
图1为本发明制备工艺流程图。Figure 1 is a flow chart of the preparation process of the present invention.
具体实施方式Detailed ways
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.
请参阅图1,本发明提供一种技术方案:一种用于河涌水污染治理的优势微生物固体菌剂制备方法,该用于河涌水污染治理的优势微生物固体菌剂制备方法的具体制备步骤如下:Please refer to Fig. 1, the present invention provides a kind of technical scheme: a kind of method for preparing the solid bacterial agent of dominant microorganisms used in the treatment of river water pollution, the specific preparation steps of the method for preparing the solid microbial agent of dominant microorganisms for the treatment of river water pollution are as follows :
S1:培养基制备:取500g牛肉,将获取的500g牛肉浸泡在800ml-850ml 的水中,将浸泡的牛肉在20-25摄氏度的温度环境下保持浸泡8-10小时,将浸泡后的肉过滤保留肉汁,在肉汁内每100ml加入300g蛋白胨、4-5gNaCl,将加入蛋白胨和氯化钠的肉汁加热混合,直至肉汁浓缩为浓稠状态,加入苏打继续搅拌,检测肉汁的PH值为7.0-7.2时即可,将调节PH后的培养基底料通过高温蒸汽的方式进行灭菌,灭菌后的培养基底料以每100ml加入2.2g-2.4g 的琼脂,混合均匀;S1: Culture medium preparation: Take 500g of beef, soak the obtained 500g of beef in 800ml-850ml of water, keep the soaked beef at 20-25 degrees Celsius for 8-10 hours, filter the soaked meat For gravy, add 300g of peptone and 4-5g of NaCl per 100ml of the gravy, heat and mix the gravy with peptone and sodium chloride until the gravy is concentrated into a thick state, add soda and continue stirring, and check the pH value of the gravy at 7.0-7.2 That is, the PH-adjusted medium base material is sterilized by high-temperature steam, and 2.2g-2.4g of agar is added to the sterilized medium base material per 100ml, and mixed evenly;
S2:培养微生物:在步骤S1制备完毕的培养基上均匀接种不同种类的菌种,将接种菌种后的培养基放置在温度为25-30摄氏度的范围内培养,培养的天数为15天,培养基上均匀长出菌落,在培养的过程中每隔3天加入酸碱度调节剂,加入酸碱度调节剂K2HPO4时进行PH测量,直至PH值再次恢复至7.0- 7.2时即可;S2: Cultivate microorganisms: evenly inoculate different types of strains on the culture medium prepared in step S1, place the culture medium after inoculating the strains at a temperature of 25-30 degrees Celsius for cultivation, and the number of days for cultivation is 15 days. Colonies grow evenly on the culture medium, add a pH regulator every 3 days during the cultivation process, and measure the pH when adding the pH regulator K 2 HPO 4 until the pH value returns to 7.0-7.2 again;
S3:注入河道污染的泥水,针对性选择菌种:从需要进行治理的河流段选取河底的泥和底部距离地面20cm范围内的河水,将取出的河水与河泥混合搅拌均匀,将混合均匀的泥水浇入步骤S2中含有菌落的培养基内,150ml的培养基内加入30-35ml的泥水,将注入泥水的培养基继续培养3-5天,培养过程中观察并取出死亡的菌落,培养至8-10天时,将培养后活着的菌落取出;S3: Inject the muddy water polluted by the river, and select the bacteria in a targeted manner: select the mud at the bottom of the river and the river water within 20cm from the bottom of the ground from the river section that needs to be treated, mix the taken out river water with the river mud, and mix evenly Pour the muddy water into the medium containing the colonies in step S2, add 30-35ml of muddy water into the 150ml medium, continue to cultivate the medium injected with muddy water for 3-5 days, observe and take out the dead bacterium colonies during the cultivation, and cultivate At 8-10 days, the living bacterial colonies after cultivation were taken out;
S4:增殖微生物:将剩余的泥水分别按照100ml的量进行等分储放,在泥水中加入步骤S3中取出的活着的菌落,且每100ml中加入4-5组菌落,将菌落分散培养3-5天即可,将培养后的泥水中加入面包,将棉包放置在泥水中浸泡2-3小时,菌落发现营养物质则吸附在面包上,取出面包即可将吸附在面包上的菌落取出,通过降温的方式对菌落冷藏,需要使用将吸附有菌落的棉包取出回暖即可将菌落复活。S4: Proliferation of microorganisms: Store the remaining muddy water in equal parts according to the amount of 100ml, add the living colonies taken out in step S3 to the muddy water, and add 4-5 groups of colonies per 100ml, and disperse and cultivate the colonies for 3- After 5 days, add the cultivated mud water to the bread, put the cotton bag in the mud water and soak for 2-3 hours, the colony finds nutrients and then adsorbs on the bread, take out the bread to remove the colonies adsorbed on the bread, The colony is refrigerated by cooling down, and the colony can be revived by taking out the cotton bag that has adsorbed the colony and warming it up.
其中,步骤S1中培养基制备的过程中还要加入消泡添加剂,消泡添加剂为乳化硅油,步骤S1中对牛肉的浸泡温度为25摄氏度,浸泡时间为9.5小时,酸碱度调节剂为K2HPO4或者KH2PO4,步骤S4中对菌落冷藏的温度为-5℃- 0摄氏度。Wherein, during the preparation of the culture medium in step S1, an antifoaming additive is also added, and the antifoaming additive is emulsified silicone oil. In step S1, the soaking temperature of the beef is 25 degrees Celsius, the soaking time is 9.5 hours, and the pH regulator is K 2 HPO 4 or KH 2 PO 4 , the temperature of the refrigerated colony in step S4 is -5°C-0°C.
尽管已经示出和描述了本发明的实施例,对于本领域的普通技术人员而言,可以理解在不脱离本发明的原理和精神的情况下可以对这些实施例进行多种变化、修改、替换和变型,本发明的范围由所附权利要求及其等同物限定。Although the embodiments of the present invention have been shown and described, those skilled in the art can understand that various changes, modifications and substitutions can be made to these embodiments without departing from the principle and spirit of the present invention. and modifications, the scope of the invention is defined by the appended claims and their equivalents.
Claims (6)
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CN110438059A (en) * | 2019-08-01 | 2019-11-12 | 上海环境卫生工程设计院有限公司 | A kind of superior microorganism microbial inoculum of water pollution control and preparation method thereof |
CN114230019A (en) * | 2021-10-25 | 2022-03-25 | 盐城工学院 | Application of a kind of probiotic activated sludge in sewage treatment |
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Publication number | Priority date | Publication date | Assignee | Title |
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CN110438059A (en) * | 2019-08-01 | 2019-11-12 | 上海环境卫生工程设计院有限公司 | A kind of superior microorganism microbial inoculum of water pollution control and preparation method thereof |
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