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 PDFInfo
- 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
Links
- 239000000463 material Substances 0.000 title claims abstract description 15
- 238000002360 preparation method Methods 0.000 title claims abstract description 8
- 238000003911 water pollution Methods 0.000 title claims abstract description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 40
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 claims abstract description 36
- 229920001661 Chitosan Polymers 0.000 claims abstract description 20
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims abstract description 18
- 230000001580 bacterial effect Effects 0.000 claims abstract description 13
- 238000003756 stirring Methods 0.000 claims abstract description 13
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 11
- 239000002244 precipitate Substances 0.000 claims abstract description 9
- 229910000029 sodium carbonate Inorganic materials 0.000 claims abstract description 9
- 239000010865 sewage Substances 0.000 claims abstract description 7
- 238000013268 sustained release Methods 0.000 claims abstract description 4
- 239000012730 sustained-release form Substances 0.000 claims abstract description 4
- 241000894006 Bacteria Species 0.000 claims description 12
- 241000193830 Bacillus <bacterium> Species 0.000 claims description 10
- 238000000034 method Methods 0.000 claims description 10
- 244000005700 microbiome Species 0.000 claims description 8
- 230000000243 photosynthetic effect Effects 0.000 claims description 7
- 150000001875 compounds Chemical class 0.000 claims description 5
- 244000063299 Bacillus subtilis Species 0.000 claims description 4
- 235000014469 Bacillus subtilis Nutrition 0.000 claims description 4
- 241000194108 Bacillus licheniformis Species 0.000 claims description 3
- 241000194103 Bacillus pumilus Species 0.000 claims description 3
- 239000002068 microbial inoculum Substances 0.000 claims description 3
- 238000001035 drying Methods 0.000 claims 1
- 238000001914 filtration Methods 0.000 claims 1
- 230000000813 microbial effect Effects 0.000 claims 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 5
- 239000005416 organic matter Substances 0.000 abstract description 5
- 239000001301 oxygen Substances 0.000 abstract description 5
- 229910052760 oxygen Inorganic materials 0.000 abstract description 5
- 238000000354 decomposition reaction Methods 0.000 abstract description 4
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 abstract description 3
- IOVCWXUNBOPUCH-UHFFFAOYSA-M nitrite group Chemical group N(=O)[O-] IOVCWXUNBOPUCH-UHFFFAOYSA-M 0.000 abstract description 3
- 239000007787 solid Substances 0.000 abstract description 3
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 abstract 1
- BVKZGUZCCUSVTD-UHFFFAOYSA-N carbonic acid Chemical compound OC(O)=O BVKZGUZCCUSVTD-UHFFFAOYSA-N 0.000 abstract 1
- 229910052708 sodium Inorganic materials 0.000 abstract 1
- 239000011734 sodium Substances 0.000 abstract 1
- 239000000243 solution Substances 0.000 description 13
- UHOVQNZJYSORNB-UHFFFAOYSA-N Benzene Chemical compound C1=CC=CC=C1 UHOVQNZJYSORNB-UHFFFAOYSA-N 0.000 description 3
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 description 3
- 239000007864 aqueous solution Substances 0.000 description 2
- 238000002474 experimental method Methods 0.000 description 2
- 239000002574 poison Substances 0.000 description 2
- 231100000614 poison Toxicity 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- SCYULBFZEHDVBN-UHFFFAOYSA-N 1,1-Dichloroethane Chemical compound CC(Cl)Cl SCYULBFZEHDVBN-UHFFFAOYSA-N 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- LSDPWZHWYPCBBB-UHFFFAOYSA-N Methanethiol Chemical compound SC LSDPWZHWYPCBBB-UHFFFAOYSA-N 0.000 description 1
- 230000001133 acceleration Effects 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- -1 alkalis Substances 0.000 description 1
- 229910052785 arsenic Inorganic materials 0.000 description 1
- RQNWIZPPADIBDY-UHFFFAOYSA-N arsenic atom Chemical compound [As] RQNWIZPPADIBDY-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 229910052793 cadmium Inorganic materials 0.000 description 1
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000010949 copper Substances 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 239000003651 drinking water Substances 0.000 description 1
- 235000020188 drinking water Nutrition 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 1
- 229910052753 mercury Inorganic materials 0.000 description 1
- 230000001151 other effect Effects 0.000 description 1
- 239000007800 oxidant agent Substances 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 238000000844 transformation Methods 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
-
- 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
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
- C02F2101/166—Nitrites
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic 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
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
表2投药一周Table 2 Dosing for one week
表3投药两周Table 3 Dosing for two weeks
表4投药三周Table 4 Administration for three weeks
表5投药四周Table 5 Dosing for four weeks
表7投药六周Table 7 Dosing for six weeks
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
表9投药一周Table 9 Dosing for one week
表10投药两周Table 10 Dosing for two weeks
表11投药三周Table 11 Administration for three weeks
表12投药四周Table 12 Dosing for four weeks
表13投药五周Table 13 Dosing for five weeks
表14投药六周Table 14 Dosing for six weeks
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)
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)
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)
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 |
-
2020
- 2020-06-17 CN CN202010554641.7A patent/CN111646580A/en active Pending
Patent Citations (6)
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)
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)
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 |