CN102180574A - Surplus sludge reduction method combining ultrasonic treatment with microfauna ingestion - Google Patents
Surplus sludge reduction method combining ultrasonic treatment with microfauna ingestion Download PDFInfo
- Publication number
- CN102180574A CN102180574A CN2011100762092A CN201110076209A CN102180574A CN 102180574 A CN102180574 A CN 102180574A CN 2011100762092 A CN2011100762092 A CN 2011100762092A CN 201110076209 A CN201110076209 A CN 201110076209A CN 102180574 A CN102180574 A CN 102180574A
- Authority
- CN
- China
- Prior art keywords
- microfauna
- excess sludge
- sludge
- micro
- animals
- 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
- 239000010802 sludge Substances 0.000 title claims abstract description 76
- 238000000034 method Methods 0.000 title claims abstract description 29
- 230000009467 reduction Effects 0.000 title claims abstract description 17
- 238000009210 therapy by ultrasound Methods 0.000 title abstract description 13
- 230000037406 food intake Effects 0.000 title 1
- 241000700141 Rotifera Species 0.000 claims abstract description 14
- 239000002245 particle Substances 0.000 claims abstract description 12
- 239000010865 sewage Substances 0.000 claims abstract description 7
- 206010015150 Erythema Diseases 0.000 claims abstract description 6
- 231100000321 erythema Toxicity 0.000 claims abstract description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 5
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 5
- 239000001301 oxygen Substances 0.000 claims abstract description 5
- 229920002635 polyurethane Polymers 0.000 claims abstract 2
- 239000004814 polyurethane Substances 0.000 claims abstract 2
- 230000009471 action Effects 0.000 claims description 4
- 230000008569 process Effects 0.000 claims description 3
- 239000000463 material Substances 0.000 claims description 2
- 238000002525 ultrasonication Methods 0.000 claims 5
- 238000005273 aeration Methods 0.000 claims 1
- 230000003247 decreasing effect Effects 0.000 claims 1
- 239000008187 granular material Substances 0.000 claims 1
- 238000011081 inoculation Methods 0.000 claims 1
- 230000000694 effects Effects 0.000 abstract description 6
- 230000008901 benefit Effects 0.000 abstract description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 3
- 241001465754 Metazoa Species 0.000 abstract description 2
- 230000007613 environmental effect Effects 0.000 abstract description 2
- 239000006261 foam material Substances 0.000 abstract 1
- 238000000746 purification Methods 0.000 abstract 1
- 239000000969 carrier Substances 0.000 description 2
- 230000008859 change Effects 0.000 description 2
- 238000005265 energy consumption Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 201000005171 Cystadenoma Diseases 0.000 description 1
- 206010028980 Neoplasm Diseases 0.000 description 1
- 241000242594 Platyhelminthes Species 0.000 description 1
- 229920005830 Polyurethane Foam Polymers 0.000 description 1
- 241000700605 Viruses Species 0.000 description 1
- 244000052616 bacterial pathogen Species 0.000 description 1
- 235000013601 eggs Nutrition 0.000 description 1
- 239000013013 elastic material Substances 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 238000010169 landfilling Methods 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 244000045947 parasite Species 0.000 description 1
- 239000011496 polyurethane foam Substances 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 230000000087 stabilizing effect Effects 0.000 description 1
Images
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/20—Sludge processing
Landscapes
- Treatment Of Sludge (AREA)
Abstract
本发明为一种城市污水处理厂剩余污泥减量方法,属于环境工程技术领域。本发明利用低能量超声波处理使污泥的颗粒粒径减小至适宜微型动物摄食,然后利用微型动物的摄食作用进行剩余污泥减量。本发明采用的微型动物种类为红斑顠体虫和宿轮虫,为了提高微型动物密度以提高微型动物对剩余污泥的摄食效率,采用了适宜这两类微型动物生长的多孔弹性载体(即聚氨酯泡沫材料)并保持一定的溶解氧浓度。采用本发明的方法,红斑顠体虫和宿轮虫的种群密提高了5~6倍、污泥减量效率提高了46.2~60.1%、并且COD去除率提高23.6~41.5%。因此,本方法既能提高微型动物种群密度、有利微型动物对剩余污泥的摄食利用和剩余污泥减量效率的提高,又能改善对水质的净化效果。
The invention relates to a method for reducing excess sludge in an urban sewage treatment plant, which belongs to the technical field of environmental engineering. The invention utilizes low-energy ultrasonic treatment to reduce the particle size of the sludge to be suitable for micro-animals to feed, and then uses the micro-animals' feeding to reduce the excess sludge. The kind of miniature animal that the present invention adopts is erythema erythematosus and rotifer, in order to improve the density of microfauna to improve the feeding efficiency of microfauna to surplus sludge, adopt the porous elastic carrier (being polyurethane that is suitable for the growth of these two types of microfauna foam material) and maintain a certain concentration of dissolved oxygen. By adopting the method of the invention, the population density of the erythema erythema and the rotifer are increased by 5-6 times, the sludge reduction efficiency is increased by 46.2-60.1%, and the COD removal rate is increased by 23.6-41.5%. Therefore, the method can not only increase the population density of micro-animals, but also benefit the micro-animals to feed and utilize excess sludge and increase the efficiency of excess sludge reduction, and can also improve the purification effect on water quality.
Description
技术领域technical field
本发明系一种城市污水处理厂剩余污泥减量方法,属于环境工程技术领域。The invention relates to a method for reducing excess sludge in urban sewage treatment plants, and belongs to the technical field of environmental engineering.
背景技术Background technique
随着城市污水生物处理率和处理量的提高,随之而来的是如何处理处置污水生物处理过程中大量产生的剩余污泥。剩余污泥的含水率一般在95%以上,有机物含量为60~70%,还含有病原菌,寄生虫卵以及病毒及重金属等有害成分。传统的剩余污泥处理处置方法包括填埋和投海,投海法由于严重危害海洋水质已经受到越来越多的国家的禁止,而填埋法不仅可能污染土壤且费用较高,因此,探索经济有效地处理剩余污泥的新方法已得到越来越多的关注。With the improvement of urban sewage biological treatment rate and treatment capacity, how to deal with and dispose of the excess sludge produced in the process of sewage biological treatment. The moisture content of excess sludge is generally above 95%, and the organic matter content is 60-70%. It also contains harmful components such as pathogenic bacteria, parasite eggs, viruses and heavy metals. The traditional disposal methods of surplus sludge include landfill and throwing into the sea. The throwing into the sea has been banned by more and more countries due to the serious harm to ocean water quality, and the landfilling method may not only pollute the soil but also cost a lot. Therefore, exploring New methods for cost-effective disposal of excess sludge have received increasing attention.
有关剩余污泥减量方法的文献和专利已有许多。这些方法大致可分成两大类,一类属于物理化学方法,另一类属于生物学或生态学方法。如中国专利申请号为CN200810180021.0、CN200910227265.4等,均是应用物理化学方法进行剩余污泥减量。There are many literatures and patents related to the reduction method of excess sludge. These methods can be roughly divided into two categories, one belongs to physical and chemical methods, and the other belongs to biological or ecological methods. For example, the Chinese patent application numbers are CN200810180021.0, CN200910227265.4, etc., all of which use physical and chemical methods to reduce excess sludge.
利用微型动物对污泥的摄食来达到剩余污泥减量目的的方法,符合生态学原理,具有低能耗且无二次污染的特色。然而这种方法对剩余污泥进行减量的效果受到一些因素的制约:一是微型动物在剩余污泥体系中生长并不稳定,且种群密度不高;二是微型动物对污泥的摄食效率与污泥粒径大小相关。微型动物对污泥的摄食主要依靠其口器,只有颗粒尺寸小于其口器的污泥才有可能为微型动物所摄食。目前的研究多偏向于稳定微型动物的生长方面,即设计专门的微型动物反应器,如专利CN200310115721.9、CN200610010265.5等。若能对剩余污泥进行预处理,通过减小其粒径以提高微型动物对剩余污泥的利用效率,同时强化微型动物在剩余污泥减量体系中的生长繁殖,可以有效地提高剩余污泥减量效率。The method of using micro-animals to feed on sludge to achieve the purpose of reducing excess sludge is in line with ecological principles, and has the characteristics of low energy consumption and no secondary pollution. However, the effect of this method on excess sludge reduction is restricted by some factors: first, the growth of micro-animals in the excess sludge system is not stable, and the population density is not high; second, the feeding efficiency of micro-animals to sludge related to sludge particle size. Microfauna mainly rely on their mouthparts to feed on sludge, and only sludge with a particle size smaller than its mouthparts can be ingested by microfauna. The current research tends to stabilize the growth of microanimals, that is, to design special microanimal reactors, such as patents CN200310115721.9, CN200610010265.5, etc. If the excess sludge can be pretreated, the utilization efficiency of micro-animals to excess sludge can be improved by reducing its particle size, and at the same time, the growth and reproduction of micro-animals in the excess sludge reduction system can be strengthened, which can effectively improve the residual sludge. Mud reduction efficiency.
发明内容Contents of the invention
本发明的目的是通过对剩余污泥进行超声波处理,使污泥粒径减小,同时在污泥减量系统中添加载体,在稳定微型动物生长、提高微型动物种群密度的同时,强化微型动物对污泥的摄食效率,以达到较高的污泥减量效率的目的,对减少剩余污泥的外排量具有重要的意义。The purpose of the present invention is to reduce the particle size of the sludge by ultrasonic treatment of the excess sludge, and at the same time add a carrier in the sludge reduction system, while stabilizing the growth of micro-animals and increasing the population density of micro-animals, strengthen the micro-animals The feeding efficiency of sludge is of great significance to reduce the amount of excess sludge discharged in order to achieve a higher sludge reduction efficiency.
本发明一种超声波处理与微型动物摄食相结合的剩余污泥减量方法,其特征在于具有以下的过程和步骤:The present invention is a method for reducing the amount of excess sludge combined with ultrasonic treatment and micro-animal feeding, which is characterized in that it has the following processes and steps:
a. 将一定浓度的剩余污泥先利用超声波处理,使污泥颗粒粒径减小至适宜微型动物摄食的程度;剩余污泥的合适浓度为1~12g/L;颗粒粒径5~30μm;超声能量密度为0.05~0.1W/ml;作用时间为5~15min;a. Treat a certain concentration of excess sludge with ultrasonic waves to reduce the particle size of the sludge to a level suitable for micro-animal feeding; the appropriate concentration of excess sludge is 1-12g/L; the particle size is 5-30μm; The ultrasonic energy density is 0.05~0.1W/ml; the action time is 5~15min;
b. 将上述经过处理的污泥引入处理系统中,在所述污泥中接种适宜的微型动物,并放入有利于其附着和生长的多孔弹性载体;同时在系统中的曝气溶解氧浓度控制在2~4mg/L;所述的微型动物为红斑顠体虫和/或宿轮虫。b. Introduce the above-mentioned treated sludge into the treatment system, inoculate suitable micro-animals in the sludge, and put it into a porous elastic carrier that is conducive to its attachment and growth; at the same time, the concentration of aerated dissolved oxygen in the system Controlled at 2-4mg/L; the micro-animals are Cystia erythematosus and/or Rotifer.
所述微型动物附着和生长的多孔弹性载体为聚氨酯泡沫材料,其孔径为1~2mm。The porous elastic carrier on which the miniature animal attaches and grows is a polyurethane foam material with a pore diameter of 1-2mm.
所述的污泥为城市污水处理厂沉淀池的剩余污泥,或者是回流污泥。The sludge is the remaining sludge in the sedimentation tank of the urban sewage treatment plant, or the return sludge.
所述的微型动物也可以为其他蟠虫和周丝轮虫类微型动物。The micro-animals can also be other flatworms and perifilariae micro-animals.
本发明方法的优点如下所述:The advantage of the inventive method is as follows:
本发明是一种城市污水处理厂剩余污泥减量方法,其优点在于:只需对剩余污泥进行超声波处理,强度低,能耗小,选择的载体-多孔弹性材料普遍易得,成本低,效果好,无二次污染,可显著提高微型动物摄食对剩余污泥的减量效果及水质状况。利用本发明的方法,污泥减量效率提高了46.2-60.1%,COD去除率了提高23.6-41.5%。本发明也适用于回流污泥以及其它蠕虫和周丛轮虫类微型动物在污泥减量系统中的运用。The invention is a method for reducing excess sludge in urban sewage treatment plants. Its advantages are: only need to perform ultrasonic treatment on excess sludge, low strength, low energy consumption, and the selected carrier-porous elastic material is generally easy to obtain and low in cost. , good effect, no secondary pollution, can significantly improve the reduction effect of micro-animal feeding on excess sludge and water quality. By using the method of the invention, the sludge reduction efficiency is increased by 46.2-60.1%, and the COD removal rate is increased by 23.6-41.5%. The present invention is also applicable to the use of returning sludge and other micro-animals of worms and rotifers in a sludge reduction system.
附图说明Description of drawings
图1为以本发明的方法经0.05W/ml超声处理后不同污泥中微型动物生长情况。Figure 1 shows the growth of micro-animals in different sludges after ultrasonic treatment at 0.05 W/ml by the method of the present invention.
图2为以本发明的方法经0.1W/ml超声处理后不同污泥中微型动物生长情况。Figure 2 shows the growth of micro-animals in different sludges after ultrasonic treatment at 0.1 W/ml by the method of the present invention.
具体实施方式Detailed ways
现将本发明的具体实施例叙述于后:Specific embodiments of the present invention are now described in the following:
实施例1:处理污泥浓度为9710mg/L,平均粒径为20.13μm的剩余污泥,超声声能密度为0.05W/mL,作用时间为10min。处理后剩余污泥浓度减小为9510mg/L,平均粒径减小为8.32μm。在该污泥中以每5mL污泥中添加3ind微型动物的密度接种红斑顠体虫与宿轮虫,并添加适宜其附着生长的多孔弹性载体,保持溶解氧浓度为2-4mg/L,经过25天的接触反应,期间定期观察红斑顠体虫和宿轮虫生长情况并测定剩余污泥的浓度及污泥COD浓度变化情况。结果表明红斑顠体虫和宿轮虫在经过超声处理并添加载体的剩余污泥中生长良好,种群密度明显高于未经超声处理且未添加载体的对照组,约为其6倍。经超声处理的剩余污泥能更好地被红斑顠体虫及宿轮虫所摄食利用,污泥减量效果明显提高,污泥减量率提高60.1%,同时有机负荷并未受到负面影响,COD去除率提高41.5%。Example 1: Treat excess sludge with a sludge concentration of 9710 mg/L and an average particle size of 20.13 μm, an ultrasonic sound energy density of 0.05 W/mL, and an action time of 10 min. After treatment, the residual sludge concentration was reduced to 9510mg/L, and the average particle size was reduced to 8.32μm. In this sludge, add 3ind micro-animal density in every 5mL sludge to inoculate C. erythematosus and rotifer, and add the poroelastic carrier suitable for its attached growth, keep the dissolved oxygen concentration at 2-4mg/L, through During the 25-day contact reaction, the growth of C. erythematosus and rotifer were observed regularly, and the concentration of remaining sludge and the change of sludge COD concentration were measured. The results showed that C. erythematosus and rotifers grew well in the excess sludge treated with ultrasonic treatment and added with carrier, and the population density was significantly higher than that of the control group without ultrasonic treatment and added carrier, which was about 6 times. The excess sludge after ultrasonic treatment can be better ingested and utilized by the erythema erythematosus and rotifers. The sludge reduction effect is significantly improved, and the sludge reduction rate is increased by 60.1%. At the same time, the organic load has not been negatively affected. The COD removal rate increased by 41.5%.
实施例2:处理污泥浓度为8930mg/L,平均粒径为21.16μm的剩余污泥,超声声能密度为0.1W/mL,作用时间为10min。处理后剩余污泥浓度减小为8620mg/L,平均粒径减小为6.17μm。在该污泥中以3ind/5ml的密度接种红斑顠体虫与宿轮虫,并添加适宜其附着生长的多孔弹性载体,保持溶解氧浓度为2-4mg/L,经过25天的接触反应,期间定期观察红斑顠体虫和宿轮虫生长情况并测定剩余污泥的浓度及污泥COD浓度变化情况。结果表明红斑顠体虫和宿轮虫在经过超声处理并添加载体的剩余污泥中生长良好,种群密度明显高于未经超声处理且未添加载体的对照组,约为其5倍。经超声处理的剩余污泥能更好地被红斑顠体虫及宿轮虫所摄食利用,污泥减量效果明显提高,污泥减量率提高46.2%,同时有机负荷并未受到负面影响,COD去除率提高23.6%。Example 2: To treat excess sludge with a sludge concentration of 8930 mg/L and an average particle size of 21.16 μm, the ultrasonic sound energy density is 0.1 W/mL, and the action time is 10 min. After treatment, the residual sludge concentration was reduced to 8620mg/L, and the average particle size was reduced to 6.17μm. In this sludge with the density of 3ind/5ml to inoculate Cystoma erythematosus and rotifer, and add the porous elastic carrier suitable for its attached growth, keep dissolved oxygen concentration as 2-4mg/L, through 25 days of contact reaction, During the period, the growth of C. erythematosus and rotifer were observed regularly, and the concentration of remaining sludge and the change of sludge COD concentration were measured. The results showed that P. erythematosus and rotifers grew well in the excess sludge treated with ultrasonic treatment and added with carriers, and the population density was significantly higher than that of the control group without ultrasonic treatment and added carriers, which was about 5 times that. The excess sludge after ultrasonic treatment can be better ingested and utilized by the erythema erythematosus and rotifers. The sludge reduction effect is significantly improved, and the sludge reduction rate is increased by 46.2%. At the same time, the organic load has not been negatively affected. COD removal rate increased by 23.6%.
Claims (4)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN2011100762092A CN102180574A (en) | 2011-06-14 | 2011-06-14 | Surplus sludge reduction method combining ultrasonic treatment with microfauna ingestion |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN2011100762092A CN102180574A (en) | 2011-06-14 | 2011-06-14 | Surplus sludge reduction method combining ultrasonic treatment with microfauna ingestion |
Publications (1)
Publication Number | Publication Date |
---|---|
CN102180574A true CN102180574A (en) | 2011-09-14 |
Family
ID=44566900
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN2011100762092A Pending CN102180574A (en) | 2011-06-14 | 2011-06-14 | Surplus sludge reduction method combining ultrasonic treatment with microfauna ingestion |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN102180574A (en) |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102499185A (en) * | 2011-10-26 | 2012-06-20 | 同济大学 | Method for cultivating aeolosoma hemprichi on large scale |
CN103399141A (en) * | 2013-08-20 | 2013-11-20 | 安徽工业大学 | Method for predicting activated sludge state based on microfauna density analysis |
CN109748470A (en) * | 2017-11-02 | 2019-05-14 | 中国石油化工股份有限公司 | A kind of method for microbial treatment of excess sludge |
CN114711174A (en) * | 2022-02-21 | 2022-07-08 | 上海大学 | Aeolosoma hemprichi high-density culture method |
CN114835359A (en) * | 2022-04-08 | 2022-08-02 | 江南大学 | Method for realizing excess sludge reduction by enhancing biological predation |
Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101508513A (en) * | 2009-03-23 | 2009-08-19 | 浙江工业大学 | Sewage sludge decrement process for reinforcing removal of nitrogen and phosphor in sewage water |
-
2011
- 2011-06-14 CN CN2011100762092A patent/CN102180574A/en active Pending
Patent Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101508513A (en) * | 2009-03-23 | 2009-08-19 | 浙江工业大学 | Sewage sludge decrement process for reinforcing removal of nitrogen and phosphor in sewage water |
Non-Patent Citations (2)
Title |
---|
《环境污染治理技术与设备》 20030131 周可新等 利用微型动物削减剩余污泥量的研究 第4卷, 第1期 * |
《环境科学学报》 20090430 喻艳菁等 超声处理对剩余污泥的粒径和溶出物的影响 第29卷, 第4期 * |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102499185A (en) * | 2011-10-26 | 2012-06-20 | 同济大学 | Method for cultivating aeolosoma hemprichi on large scale |
CN103399141A (en) * | 2013-08-20 | 2013-11-20 | 安徽工业大学 | Method for predicting activated sludge state based on microfauna density analysis |
CN109748470A (en) * | 2017-11-02 | 2019-05-14 | 中国石油化工股份有限公司 | A kind of method for microbial treatment of excess sludge |
CN114711174A (en) * | 2022-02-21 | 2022-07-08 | 上海大学 | Aeolosoma hemprichi high-density culture method |
CN114711174B (en) * | 2022-02-21 | 2023-09-29 | 上海大学 | High-density culture method of Helicobacter worms |
CN114835359A (en) * | 2022-04-08 | 2022-08-02 | 江南大学 | Method for realizing excess sludge reduction by enhancing biological predation |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Adams et al. | Research advances in anammox granular sludge: A review | |
Krakat et al. | Methods of ammonia removal in anaerobic digestion: a review | |
Li et al. | Hazardous substances and their removal in recirculating aquaculture systems: A review | |
Saini et al. | Biofilm-mediated wastewater treatment: a comprehensive review | |
Wang et al. | A review of biomass immobilization in anammox and partial nitrification/anammox systems: Advances, issues, and future perspectives | |
Chu et al. | Nitrogen removal using biodegradable polymers as carbon source and biofilm carriers in a moving bed biofilm reactor | |
CN104961306B (en) | A kind of processing method of vaccary breeding wastewater | |
Rong et al. | Towards advanced mariculture wastewater treatment by bacterial-algal symbiosis system with different bacteria and algae inoculation ratios | |
Qiao et al. | High-rate nitrogen removal from livestock manure digester liquor by combined partial nitritation–anammox process | |
US20230382778A1 (en) | Efficient nitrogen and phosphorus removal process system for mariculture tail water treatment | |
CN104787882B (en) | A kind of method of low carbon-nitrogen ratio sewage denitrification advanced nitrogen | |
Chen et al. | Advancements in swine wastewater treatment: Removal mechanisms, influential factors, and optimization strategies | |
CN102070244A (en) | Magnetic carrier biofilm reactor and method thereof used for wastewater sludge reduction treatment | |
CN102180574A (en) | Surplus sludge reduction method combining ultrasonic treatment with microfauna ingestion | |
Lee et al. | Complete reduction of highly concentrated contaminants in piggery waste by a novel process scheme with an algal-bacterial symbiotic photobioreactor | |
CN102432134A (en) | Method for treating wastewater from acrylic fiber production by dry method | |
CN101891356B (en) | Landfill leachate treatment method realizing zero sludge discharge | |
CN107337275B (en) | Aerobic granular sludge with high denitrification capacity at low temperature, culture method and culture device | |
Gao et al. | Recent advances and perspectives of biochar for livestock wastewater: modification methods, applications, and resource recovery | |
CN109279747B (en) | Method for enhancing resistance gene of excess sludge hydrothermal reduction by using zero-valent iron | |
CN104843939A (en) | Process for adopting metal film to cooperatively treat wastewater capable of reaching Class III in water quality | |
JP2008068233A (en) | Nitrogen removing method and nitrogen removing apparatus | |
JP4892917B2 (en) | Biological treatment method and apparatus for organic wastewater | |
CN108751581B (en) | Treatment process of biochemical effluent of landfill leachate | |
CN101928067B (en) | A kind of cultivation method of aerobic denitrification granular sludge |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C02 | Deemed withdrawal of patent application after publication (patent law 2001) | ||
WD01 | Invention patent application deemed withdrawn after publication |
Application publication date: 20110914 |