[go: up one dir, main page]

CN111646580A - Preparation method and application of slow-release material for treating water pollution - Google Patents

Preparation method and application of slow-release material for treating water pollution Download PDF

Info

Publication number
CN111646580A
CN111646580A CN202010554641.7A CN202010554641A CN111646580A CN 111646580 A CN111646580 A CN 111646580A CN 202010554641 A CN202010554641 A CN 202010554641A CN 111646580 A CN111646580 A CN 111646580A
Authority
CN
China
Prior art keywords
water
chitosan
release material
solution
bacillus
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202010554641.7A
Other languages
Chinese (zh)
Inventor
邵美涵
王曹甘泓
卞诗倩
郑晓璇
孙慧莹
钱建瑛
周莹
史劲松
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Jiangnan University
Original Assignee
Jiangnan University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Jiangnan University filed Critical Jiangnan University
Priority to CN202010554641.7A priority Critical patent/CN111646580A/en
Publication of CN111646580A publication Critical patent/CN111646580A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • C02F2101/166Nitrites
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Microbiology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

本发明公开了一种用于治理水污染的缓释材料的制备方法及应用,本发明通过将壳聚糖加入用醋酸调整pH为4‑5的水中,搅拌至完全溶解;向其中快速加入碳酸钠溶液,每克壳聚糖加入40‑60mL碳酸钠溶液,充分搅拌,得到壳聚糖溶液;再加入功能菌剂进行包埋;用醋酸调整溶液pH为6.5‑7.5,析出沉淀,搅拌充分后静置,过滤干燥得到缓释材料。本发明的缓释材料包埋菌剂用于治理污水,可以起到长期净化水质、有效降低水中有机物和氨氮含量、加速亚硝酸盐分解、絮凝水中悬浮物、增加水体溶氧等效果。The invention discloses a preparation method and application of a sustained-release material for treating water pollution. In the invention, chitosan is added to water whose pH is adjusted to 4-5 with acetic acid, and stirred until completely dissolved; carbonic acid is rapidly added to the water. Sodium solution, add 40-60mL of sodium carbonate solution per gram of chitosan, fully stir to obtain a chitosan solution; then add functional bacterial agents for embedding; adjust the pH of the solution to 6.5-7.5 with acetic acid, and precipitate out after fully stirring Set aside, filter and dry to obtain a sustained-release material. The slow-release material-embedded bacterial agent of the invention is used for sewage treatment, and can purify water for a long time, effectively reduce the content of organic matter and ammonia nitrogen in water, accelerate the decomposition of nitrite, flocculate suspended solids in water, and increase dissolved oxygen in water.

Description

一种用于治理水污染的缓释材料的制备方法及应用A kind of preparation method and application of slow-release material for controlling water pollution

技术领域technical field

本发明涉及一种用于治理水污染的缓释材料的制备方法及应用,属于微生物技术领域。The invention relates to a preparation method and application of a slow-release material for treating water pollution, and belongs to the technical field of microorganisms.

背景技术Background technique

水污染是由有害化学物质造成水的使用价值降低或丧失,污染环境的水。污水中的酸、碱、氧化剂,以及铜、镉、汞、砷等化合物,苯、二氯乙烷、乙二醇等有机毒物,会毒死水生生物,影响饮用水源、风景区景观。污水中的有机物被微生物分解时消耗水中的氧,影响水生生物的生命,水中溶解氧耗尽后,有机物进行厌氧分解,产生硫化氢、硫醇等难闻气体,使水质进一步恶化。Water pollution is water that pollutes the environment by reducing or losing the use value of water by harmful chemicals. Acids, alkalis, oxidants, copper, cadmium, mercury, arsenic and other compounds in sewage, as well as organic poisons such as benzene, dichloroethane, and ethylene glycol, will poison aquatic organisms and affect drinking water sources and scenic spots. When the organic matter in the sewage is decomposed by microorganisms, the oxygen in the water is consumed, which affects the life of aquatic organisms. After the dissolved oxygen in the water is exhausted, the organic matter undergoes anaerobic decomposition, producing unpleasant gases such as hydrogen sulfide and mercaptan, which further deteriorate the water quality.

随着我国城市化进程的不断加快,大量废水未经处理直接或间接排入城市河道,导致水环境日益恶化,河道水体自净能力下降甚至丧失。水污染的治理可以用生物修复技术,其总是以微生物为先行应用,但投加到水体中的微生物菌剂处于游离状态,致使微生物流失严重,无法长期留存于水体中,严重限制了其对污染水体的净化效果。可以用包埋固定化技术对微生物进行固定。但是现有的包埋固定化技术只能发挥微生物本身的净化作用,而包埋载体无法发挥有效作用,处理效果较弱。With the continuous acceleration of urbanization in my country, a large amount of wastewater is directly or indirectly discharged into urban rivers without treatment, resulting in the deterioration of the water environment and the decline or even loss of the self-purification capacity of river water bodies. The treatment of water pollution can use bioremediation technology, which always uses microorganisms as the first application, but the microbial inoculum added to the water body is in a free state, resulting in serious loss of microorganisms and cannot be retained in the water body for a long time, which seriously limits its use. Purification of polluted water bodies. Microorganisms can be immobilized using immobilization techniques. However, the existing embedding and immobilization technology can only play the role of purifying the microorganism itself, while the embedding carrier cannot play an effective role, and the treatment effect is weak.

发明内容SUMMARY OF THE INVENTION

为解决上述技术问题,本发明提供一种缓释材料包埋菌剂,并用于治理污水,可以起到长期净化水质、有效降低水中有机物和氨氮含量、加速亚硝酸盐分解、絮凝水中悬浮物、增加水体溶氧等效果。In order to solve the above-mentioned technical problems, the present invention provides a slow-release material embedded bacterial agent, which can be used for the treatment of sewage, which can purify water for a long time, effectively reduce the content of organic matter and ammonia nitrogen in water, accelerate the decomposition of nitrite, flocculate suspended solids in water, Increase water dissolved oxygen and other effects.

本发明的第一个目的是提供一种用于治理水污染的缓释材料的制备方法,包括如下步骤:The first object of the present invention is to provide a kind of preparation method of the slow-release material for controlling water pollution, comprises the steps:

S1、将壳聚糖加入用醋酸调整pH为4-5的水中,搅拌至完全溶解;S1, add chitosan into water whose pH is adjusted to 4-5 with acetic acid, and stir until completely dissolved;

S2、按照每克壳聚糖加入40-60mL碳酸钠溶液,向S1步骤中快速加入碳酸钠溶液,充分搅拌,得到壳聚糖溶液;S2, adding 40-60 mL of sodium carbonate solution per gram of chitosan, rapidly adding sodium carbonate solution to step S1, and fully stirring to obtain a chitosan solution;

S3、向S2步骤制备得到的壳聚糖溶液中加入功能菌剂进行包埋;S3, adding functional bacterial agent to the chitosan solution prepared in step S2 for embedding;

S4、用醋酸调整溶液pH为6.5-7.5,析出沉淀,搅拌充分后静置,过滤干燥得到所述的缓释材料。S4, using acetic acid to adjust the pH of the solution to 6.5-7.5, to precipitate a precipitate, stir well and then stand, filter and dry to obtain the slow-release material.

进一步地,所述的碳酸钠溶液的浓度为0.08~0.12mol/L。Further, the concentration of the sodium carbonate solution is 0.08-0.12 mol/L.

进一步地,在S1步骤中,壳聚糖与水的质量体积比g/mL为1:100-200。Further, in step S1, the mass-volume ratio g/mL of chitosan and water is 1:100-200.

进一步地,所述的功能菌剂为改善水质的功能微生物。Further, the functional bacterial agent is a functional microorganism for improving water quality.

进一步地,S3步骤中,所述的功能菌剂的添加量为每克壳聚糖加入4~6g功能菌剂。Further, in step S3, the added amount of the functional bacterial agent is 4-6 g of functional bacterial agent per gram of chitosan.

进一步地,所述的功能菌剂为光合细菌、复合芽孢杆菌中的一种或多种组合。Further, the functional bacterial agent is one or more combinations of photosynthetic bacteria and complex Bacillus.

进一步地,所述的光合细菌的活菌含量为5×108cfu/mL-5×109cfu/mL。Further, the viable bacteria content of the photosynthetic bacteria is 5×10 8 cfu/mL-5×10 9 cfu/mL.

进一步地,所述的复合芽孢杆菌为地衣芽孢杆菌、枯草芽孢杆菌、侧孢芽孢杆菌或短小芽孢杆菌中的两种及两种以上,活菌含量为100×108cfu/mL-200×109cfu/mL。Further, the compound Bacillus is two or more of Bacillus licheniformis, Bacillus subtilis, Bacillus lateralis or Bacillus pumilus, and the viable bacteria content is 100×10 8 cfu/mL-200×10 9 cfu/mL.

本发明的第二个目的是提供所述的方法制备得到的缓释材料。The second object of the present invention is to provide the sustained-release material prepared by the method.

本发明的第三个目的是提供所述的缓释材料在污水处理中的应用。The third object of the present invention is to provide the application of the slow-release material in sewage treatment.

本发明的有益效果:Beneficial effects of the present invention:

本发明的缓释材料包埋菌剂用于治理污水,可以起到长期净化水质、有效降低水中有机物和氨氮含量、加速亚硝酸盐分解、絮凝水中悬浮物、增加水体溶氧等效果。The slow-release material-embedded bacterial agent of the invention is used for sewage treatment, and can purify water for a long time, effectively reduce the content of organic matter and ammonia nitrogen in water, accelerate the decomposition of nitrite, flocculate suspended solids in water, and increase dissolved oxygen in water.

具体实施方式Detailed ways

下面结合具体实施例对本发明作进一步说明,以使本领域的技术人员可以更好地理解本发明并能予以实施,但所举实施例不作为对本发明的限定。The present invention will be further described below with reference to specific embodiments, so that those skilled in the art can better understand the present invention and implement it, but the embodiments are not intended to limit the present invention.

实施例1:Example 1:

按本发明技术方案包埋市售光合细菌,该菌剂活菌含量5×108cfu/mL-5×109cfu/mL,原商品使用说明的用量为每亩水面1米水深泼洒100g,每10-15天使用一次。将壳聚糖按质量体积比g/mL为1:100加入用醋酸调整pH为4-5的水中,搅拌至完全溶解;总共称取壳聚糖20g,加入2L醋酸水溶液中;快速加入1L 0.1mol/L的碳酸钠溶液,充分搅拌;加入光合细菌100g;用醋酸调整溶液pH为6.5-7.5,溶液中渐渐析出沉淀,搅拌充分后静置4℃冷藏半小时,布氏漏斗抽滤,将沉淀滤出,摊量至基本干燥,称重,约120g。According to the technical scheme of the present invention, commercially available photosynthetic bacteria are embedded, and the viable bacteria content of the bacterial agent is 5×10 8 cfu/mL-5×10 9 cfu/mL. Use every 10-15 days. Add chitosan at a mass-to-volume ratio of g/mL of 1:100 to water adjusted to pH 4-5 with acetic acid, and stir until completely dissolved; weigh 20 g of chitosan in total and add it to 2L of acetic acid aqueous solution; quickly add 1L of 0.1 mol/L sodium carbonate solution, stir well; add 100 g of photosynthetic bacteria; adjust the pH of the solution to 6.5-7.5 with acetic acid, and precipitate gradually precipitates out of the solution. The precipitate was filtered off, weighed to be substantially dry, and weighed, about 120 g.

选两块面积约为1亩水深1米的池塘进行实验,分别抛洒光合细菌100g和制备好的包埋物120g,定期检测水质指标,结果见下表1-7。Two ponds with an area of about 1 mu and a water depth of 1 meter were selected for the experiment, and 100 g of photosynthetic bacteria and 120 g of the prepared embedded material were sprinkled respectively, and the water quality indicators were regularly tested. The results are shown in Table 1-7 below.

表1初始水质Table 1 Initial water quality

Figure BDA0002543854730000031
Figure BDA0002543854730000031

表2投药一周Table 2 Dosing for one week

Figure BDA0002543854730000041
Figure BDA0002543854730000041

表3投药两周Table 3 Dosing for two weeks

Figure BDA0002543854730000042
Figure BDA0002543854730000042

表4投药三周Table 4 Administration for three weeks

Figure BDA0002543854730000043
Figure BDA0002543854730000043

表5投药四周Table 5 Dosing for four weeks

Figure BDA0002543854730000044
Figure BDA0002543854730000044

Figure BDA0002543854730000045
Figure BDA0002543854730000045

Figure BDA0002543854730000046
Figure BDA0002543854730000046

表7投药六周Table 7 Dosing for six weeks

Figure BDA0002543854730000051
Figure BDA0002543854730000051

实施例2:Example 2:

按本发明技术方案包埋市售复合芽孢杆菌(包含地衣芽孢杆菌、枯草芽孢杆菌、侧孢芽孢杆菌、短小芽孢杆菌,活菌含量100×108cfu/mL-200×109cfu/mL),原商品使用说明的用量为每10-12亩水面1米水深,投量0.5-1kg,每10-15天使用一次。将壳聚糖按质量体积比g/mL为1:200加入用醋酸调整pH为4-5的水中,搅拌至完全溶解;总共称取壳聚糖100g,加入20L醋酸水溶液中;快速加入5L 0.1mol/L的碳酸钠溶液,充分搅拌;加入复合芽孢杆菌500g;用醋酸调整溶液pH为6.5-7.5,溶液中渐渐析出沉淀,搅拌充分后静置4℃冷藏半小时,布氏漏斗抽滤,将沉淀滤出,摊量至基本干燥,称重,约600g。According to the technical solution of the present invention, commercially available Bacillus complexes (including Bacillus licheniformis, Bacillus subtilis, Bacillus lateralis, and Bacillus pumilus, with a viable bacterial content of 100×10 8 cfu/mL-200×10 9 cfu/mL) are encapsulated , the dosage of the original product instructions for use is 1 meter water depth per 10-12 mu of water surface, the input amount is 0.5-1kg, and it is used once every 10-15 days. Add chitosan to water whose pH is adjusted to 4-5 with acetic acid at a mass-to-volume ratio of g/mL of 1:200, and stir until completely dissolved; weigh 100 g of chitosan in total and add it to 20 L of acetic acid aqueous solution; quickly add 5 L of 0.1 mol/L sodium carbonate solution, stir well; add 500 g of Bacillus compound; adjust the pH of the solution to 6.5-7.5 with acetic acid, and precipitate gradually precipitates out of the solution, stir well and leave it to stand at 4°C for half an hour, filter with suction on a Buchner funnel, The precipitate was filtered off, weighed to substantial dryness, and weighed, approximately 600 g.

选两块面积约为10亩水深1米的池塘进行实验,分别抛洒复合芽孢杆菌500g和制备好的包埋物600g,定期检测水质指标,结果见下表8-14。Two ponds with an area of about 10 mu and a water depth of 1 meter were selected for the experiment, and 500 g of Bacillus compound and 600 g of the prepared embedded material were sprinkled respectively, and the water quality indicators were regularly tested. The results are shown in Table 8-14 below.

表8初始水质Table 8 Initial water quality

Figure BDA0002543854730000052
Figure BDA0002543854730000052

表9投药一周Table 9 Dosing for one week

Figure BDA0002543854730000061
Figure BDA0002543854730000061

表10投药两周Table 10 Dosing for two weeks

Figure BDA0002543854730000062
Figure BDA0002543854730000062

表11投药三周Table 11 Administration for three weeks

Figure BDA0002543854730000063
Figure BDA0002543854730000063

表12投药四周Table 12 Dosing for four weeks

Figure BDA0002543854730000064
Figure BDA0002543854730000064

表13投药五周Table 13 Dosing for five weeks

Figure BDA0002543854730000065
Figure BDA0002543854730000065

表14投药六周Table 14 Dosing for six weeks

Figure BDA0002543854730000071
Figure BDA0002543854730000071

以上所述实施例仅是为充分说明本发明而所举的较佳的实施例,本发明的保护范围不限于此。本技术领域的技术人员在本发明基础上所作的等同替代或变换,均在本发明的保护范围之内。本发明的保护范围以权利要求书为准。The above-mentioned embodiments are only preferred embodiments for fully illustrating the present invention, and the protection scope of the present invention is not limited thereto. Equivalent substitutions or transformations made by those skilled in the art on the basis of the present invention are all within the protection scope of the present invention. The protection scope of the present invention is subject to the claims.

Claims (10)

1. A preparation method of a slow-release material for treating water pollution is characterized by comprising the following steps:
s1, adding chitosan into water with pH adjusted to 4-5 by acetic acid, and stirring until the chitosan is completely dissolved;
s2, adding 40-60mL of sodium carbonate solution into each gram of chitosan, quickly adding the sodium carbonate solution into the step S1, and fully stirring to obtain a chitosan solution;
s3, adding a functional microbial inoculum into the chitosan solution prepared in the step S2 for embedding;
s4, adjusting the pH value of the solution to 6.5-7.5 by using acetic acid, separating out a precipitate, fully stirring, standing, filtering and drying to obtain the slow-release material.
2. The method according to claim 1, wherein the concentration of the sodium carbonate solution is 0.08-0.12 mol/L.
3. The method as set forth in claim 1, wherein the mass-to-volume ratio g/mL of chitosan to water in the step S1 is 1: 100-200.
4. The method according to claim 1, wherein the functional microbial agent is a functional microorganism for improving water quality.
5. The preparation method according to claim 1, wherein in the step S3, the addition amount of the functional microbial inoculum is 4-6 g per gram of chitosan.
6. The method for preparing the compound bacterial preparation as claimed in claim 5, wherein the functional bacterial preparation is one or more of photosynthetic bacteria and bacillus compositus.
7. The method according to claim 6, wherein the photosynthetic bacteria have a viable bacteria content of 5 × 108cfu/mL-5×109cfu/mL。
8. The method according to claim 6, wherein the Bacillus subtilis complex is Bacillus licheniformis, Bacillus subtilis, or Bacillus laterosporusTwo or more of Bacillus or Bacillus pumilus with viable bacteria content of 100 × 108cfu/mL-200×109cfu/mL。
9. A sustained release material prepared by the method of any one of claims 1 to 8.
10. Use of the slow release material of claim 9 in sewage treatment.
CN202010554641.7A 2020-06-17 2020-06-17 Preparation method and application of slow-release material for treating water pollution Pending CN111646580A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202010554641.7A CN111646580A (en) 2020-06-17 2020-06-17 Preparation method and application of slow-release material for treating water pollution

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202010554641.7A CN111646580A (en) 2020-06-17 2020-06-17 Preparation method and application of slow-release material for treating water pollution

Publications (1)

Publication Number Publication Date
CN111646580A true CN111646580A (en) 2020-09-11

Family

ID=72344086

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202010554641.7A Pending CN111646580A (en) 2020-06-17 2020-06-17 Preparation method and application of slow-release material for treating water pollution

Country Status (1)

Country Link
CN (1) CN111646580A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112978937A (en) * 2021-02-08 2021-06-18 谷尚昆 Lozenge for purifying organic pollution of water body and preparation method thereof
CN113321319A (en) * 2021-06-07 2021-08-31 广州市清沃生物科技有限公司 Sewage purification active bacteria sustained-release product

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104313004A (en) * 2014-10-20 2015-01-28 内蒙古阜丰生物科技有限公司 Preparation for treating sewage produced by production of xanthan gum
CN105885118A (en) * 2014-12-08 2016-08-24 北京服装学院 Chitosan film and method for adsorbing and desorbing hexavalent chromium using chitosan film
CN108178325A (en) * 2017-12-22 2018-06-19 中山市小榄企业服务有限公司 A kind of biological agent for handling glutamic acid fermentation waste water
CN109456421A (en) * 2018-10-30 2019-03-12 江南大学 A kind of preparation of water soluble chitosan material and application method
CN109876780A (en) * 2019-02-02 2019-06-14 杭州师范大学 A kind of phosphorus removal adsorbent and preparation method thereof
CN111039415A (en) * 2019-11-18 2020-04-21 天津大学 A kind of preparation method of immobilized slow-release microorganisms that can be used for in-situ remediation of water bodies

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104313004A (en) * 2014-10-20 2015-01-28 内蒙古阜丰生物科技有限公司 Preparation for treating sewage produced by production of xanthan gum
CN105885118A (en) * 2014-12-08 2016-08-24 北京服装学院 Chitosan film and method for adsorbing and desorbing hexavalent chromium using chitosan film
CN108178325A (en) * 2017-12-22 2018-06-19 中山市小榄企业服务有限公司 A kind of biological agent for handling glutamic acid fermentation waste water
CN109456421A (en) * 2018-10-30 2019-03-12 江南大学 A kind of preparation of water soluble chitosan material and application method
CN109876780A (en) * 2019-02-02 2019-06-14 杭州师范大学 A kind of phosphorus removal adsorbent and preparation method thereof
CN111039415A (en) * 2019-11-18 2020-04-21 天津大学 A kind of preparation method of immobilized slow-release microorganisms that can be used for in-situ remediation of water bodies

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
李保强 等: "《壳聚糖生物材料》", 30 June 2017, 哈尔滨工业大学出版社 *
黄玉媛 等: "《精细化工配方常用原料手册》", 30 March 1998, 广东科技出版社 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112978937A (en) * 2021-02-08 2021-06-18 谷尚昆 Lozenge for purifying organic pollution of water body and preparation method thereof
CN112978937B (en) * 2021-02-08 2023-11-14 谷尚昆 Lozenge for purifying organic pollution of water body and preparation method thereof
CN113321319A (en) * 2021-06-07 2021-08-31 广州市清沃生物科技有限公司 Sewage purification active bacteria sustained-release product

Similar Documents

Publication Publication Date Title
CN110563162B (en) Sewage treatment agent and preparation method and application thereof
CN108793433B (en) High-turbidity water quality emergency treatment technology
CN109956563B (en) Preparation method and application of high-efficiency aerobic denitrifying phosphorus-accumulating bacteria immobilized pellets
CN113788549B (en) Urban sewage treatment agent, preparation method and application thereof
CN110683657A (en) Culture sewage treatment method based on microbial degradation
CN107434303A (en) The processing method of eutrophication aquiculture waste water
CN105923759A (en) Biological treatment method and application thereof for removing new type organic pollutants in water
CN111646580A (en) Preparation method and application of slow-release material for treating water pollution
CN111499000B (en) A kind of artificial wetland filler and preparation method thereof
CN108913623A (en) A kind of preparation method of sulphur autotrophic denitrification bacteria immobilized particle
CN103214084B (en) A kind of compound formulation for environment water reparation and its preparation method and application
CN111925965B (en) Biological sewage treatment composite microbial inoculum and preparation method thereof
CN106986455A (en) A kind of dystopy purifying of the hypertrophic water system method based on carrier organism membranous system
CN107285455A (en) A kind of method for culturing aerobic granular sludge for handling electroplating wastewater
CN115490341A (en) Microbial agent particle, preparation method and application thereof
CN101638268A (en) Preparation method of fossilized active sludge and micro-sewage treatment method
CN116354494A (en) Composite slow-release carbon material coupled aerobic denitrifying bacteria and application thereof in water treatment
CN108546699A (en) The preparation and application of nitrifying bacteria community immobilized spherule
CN109928518B (en) Efficient water purifying agent
CN109928451B (en) Preparation method of efficient wetting purifying agent and application of efficient wetting purifying agent in environmental purification
CN117466430B (en) Sewage treatment agent based on COD degrading bacteria and preparation method thereof
CN111439845A (en) Composition for optimizing water body structure and preparation method thereof
CN101367576A (en) A method for removing Cr(VI) in water
CN112279455A (en) Microbial treatment method for landscape water body eutrophication
CN118458963B (en) Water treatment agent and preparation method thereof

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20200911

RJ01 Rejection of invention patent application after publication