CN101343111B - Method for improving efficiency of attached growth wastewater treatment biomembrane reactor - Google Patents
Method for improving efficiency of attached growth wastewater treatment biomembrane reactor Download PDFInfo
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- WPBNNNQJVZRUHP-UHFFFAOYSA-L manganese(2+);methyl n-[[2-(methoxycarbonylcarbamothioylamino)phenyl]carbamothioyl]carbamate;n-[2-(sulfidocarbothioylamino)ethyl]carbamodithioate Chemical compound [Mn+2].[S-]C(=S)NCCNC([S-])=S.COC(=O)NC(=S)NC1=CC=CC=C1NC(=S)NC(=O)OC WPBNNNQJVZRUHP-UHFFFAOYSA-L 0.000 description 1
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Classifications
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- 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
- Y02W10/10—Biological treatment of water, waste water, or sewage
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Abstract
Description
技术领域technical field
本发明涉及提高附着生长废水处理生物膜反应器效能的方法,具体的说,涉及提高以微生物附着生长载体的废水生物膜反应器效能的方法。The invention relates to a method for improving the performance of a biofilm reactor for attaching and growing wastewater, in particular to a method for improving the performance of a wastewater biofilm reactor using microorganisms to attach and grow as a carrier.
背景技术Background technique
生物处理技术包括附着生长的生物膜技术和悬浮生长(污泥)技术两大类,已经成为废水处理的主导技术之一,随着各种废水生物处理技术的大量应用,其中以微生物附着生长的生物膜技术得到了快速发展,附着生长技术是指通过细菌等微生物和原生动物、后生动物等微型动物附着在某些物料载体上进行生长繁殖,形成生物膜,污水通过与生物膜的充分接触,其中的有机污染物作为营养物质被膜中生物摄取或分解从而直到净化污水的作用,由于微生物膜附着生长的生物膜技术具有微生物生态系统食物链长、污染物净化效果好而得到了较为广泛的应用,包括生物移动床、生物转盘、生物滤池、生物流化床、生物栅等以微生物附着生长固定方式的生物膜反应器在废水处理工程中得到了快速的发展和应用,其中决定处理系统是否稳定运行的关键因是反应器能否快速启动和具有较高的处理效果。Biological treatment technology includes two categories: attached growth biofilm technology and suspended growth (sludge) technology, which has become one of the leading technologies for wastewater treatment. Biofilm technology has been developed rapidly. Attachment growth technology refers to the growth and reproduction of microorganisms such as bacteria and micro-animals such as protozoa and metazoans attached to certain material carriers to form biofilms. Sewage is fully contacted with biofilms. Among them, the organic pollutants are taken up or decomposed by the organisms in the nutrient film to purify the sewage. Because the biofilm technology attached to the growth of the microbial film has a long food chain in the microbial ecosystem and a good purification effect of the pollutants, it has been widely used. Biofilm reactors, including biological moving bed, biological turntable, biological filter, biological fluidized bed, biological grid, etc., which are fixed by microbial attachment and growth, have been rapidly developed and applied in wastewater treatment engineering, which determines whether the treatment system is stable or not. The key factors for operation are whether the reactor can start up quickly and have a high treatment effect.
微量元素是维持和促进微生物酶代谢反应的重要基础物质,所有微生物生长都需要金属元素,微量金属的存在和生物有效度会解决大部分的运行问题。目前这方面的研究以铁、钴、镍、铜、锌、锰、钼、钨等元素在低剂量条件下对活性污泥系统中微生物作用效果,并对重金属离子对活性污泥废水处理系统微生物种群活性的促进取得了较理想的研究成果。缺少任何一种常见的微量金属都会造成生物处理反应的抑制甚至完全停止造成运行失败。稀土作为一类金属,是我国特有的丰富资源,自20世纪80年代以来,我国稀土资源开发与应用已遍布工业、农业、医疗和生活各个领域,基于我国丰富的稀土资源和稀土的“高抑低促”的homisis效应,经过多年的研究积累,发现镧、铈等占稀土总量四分之三的轻稀土对废水处理系统中微生物有明显的活性促进效果。Trace elements are important basic substances for maintaining and promoting microbial enzyme metabolic reactions. All microorganisms need metal elements for growth. The existence and bioavailability of trace metals will solve most of the operational problems. The current research in this area is based on the effect of iron, cobalt, nickel, copper, zinc, manganese, molybdenum, tungsten and other elements on the microorganisms in the activated sludge system under low dosage conditions, and the effect of heavy metal ions on the microorganisms in the activated sludge wastewater treatment system. The promotion of population activity has achieved ideal research results. The absence of any one of the common trace metals can cause the inhibition or even stop of the biological treatment reaction and cause the operation to fail. As a class of metals, rare earths are uniquely rich resources in my country. Since the 1980s, the development and application of rare earth resources in my country have spread throughout the fields of industry, agriculture, medical care and life. After years of research and accumulation, it is found that light rare earths such as lanthanum and cerium, which account for three-quarters of the total rare earths, can significantly promote the activity of microorganisms in wastewater treatment systems.
稀土对微生物的作用机理主要包括两个方面,首先是以微生物细胞膜为靶器官,与蛋白质、酶等生物大分子作用,从而影响细胞的某些生物功能和活性。目前的研究结果已发现稀土可以作用于细胞膜上的转运蛋白或磷脂,提高膜的透性。其次,稀土元素活泼的化学性质和强络合能力决定了在一定条件下可能成为微生物体内有害自由基的清除剂。如已有研究结果表明,低浓度稀土对提高生物活性有积极的促进作用,适宜浓度的Ce3+对厌氧微生物比产甲烷活性(SMA)有短期的促进作用,0.05mg/L对稳定培养的厌氧微生物的SMA有明显的促进作用,高达14.29%。截止目前为止,稀土对废水处理反应器中微生物作用未见公开报道。利用稀土促进厌氧污泥活性的方法的专利(公开号CN1654365A)公开了利用稀土促进厌氧污泥活性的方法。但利用稀土制造填料并促进生物膜反应器净化效果的方法未见报道。The mechanism of action of rare earths on microorganisms mainly includes two aspects. First, the microbial cell membrane is used as the target organ to interact with biological macromolecules such as proteins and enzymes, thereby affecting certain biological functions and activities of cells. The current research results have found that rare earths can act on transport proteins or phospholipids on cell membranes to improve membrane permeability. Secondly, the active chemical properties and strong complexing ability of rare earth elements determine that they may become harmful free radical scavengers in microorganisms under certain conditions. For example, the existing research results have shown that low concentrations of rare earths have a positive effect on improving biological activity, an appropriate concentration of Ce 3+ has a short-term effect on the specific methanogenic activity (SMA) of anaerobic microorganisms, and 0.05 mg/L is effective for stable cultivation. The SMA of anaerobic microorganisms has obvious promotion effect, as high as 14.29%. So far, there are no public reports on the effect of rare earths on microorganisms in wastewater treatment reactors. The patent (publication number CN1654365A) of the method for promoting the activity of anaerobic sludge by using rare earth discloses the method for promoting the activity of anaerobic sludge by using rare earth. However, there is no report on the method of using rare earths to make fillers and promote the purification effect of biofilm reactors.
发明内容Contents of the invention
1.发明要解决的技术问题1. The technical problem to be solved by the invention
针对生物膜反应器在废水处理工程中不能稳定运行、快速启动和处理效果欠佳,本发明的目的是提供一种提高微生物附着生长废水处理生物膜反应器效能的方法,可加速废水处理生物膜反应器的启动,提高净化效果和稳定性。Aiming at the unstable operation, fast start-up and poor treatment effect of biofilm reactors in wastewater treatment projects, the purpose of the present invention is to provide a method for improving the efficiency of microbial attachment growth wastewater treatment biofilm reactors, which can accelerate wastewater treatment biofilm The start-up of the reactor improves the purification effect and stability.
2.技术方案2. Technical solution
本发明的目的是通过以下技术方案实现的:The purpose of the present invention is achieved through the following technical solutions:
一种提高微生物附着生长废水处理生物膜反应器效能的方法,包括以下步骤:A method for improving the performance of biofilm reactors for microbial attachment and growth wastewater treatment, comprising the following steps:
步骤A:制造填料或滤料等载体时将1~10mg/kg(填料基料)的可溶性稀土化合物作为添加剂添加到填料或滤料等载体中,形成改性填料或改性滤料载体;Step A: Adding 1 to 10 mg/kg (filler base material) of soluble rare earth compounds as additives to carriers such as fillers or filter materials when manufacturing carriers such as fillers or filter materials to form modified fillers or modified filter materials;
步骤B:将以上改性填料或改性滤料载体填充于生物膜反应器用于废水处理。Step B: filling the above modified filler or modified filter material carrier into a biofilm reactor for wastewater treatment.
适宜的稀土化合物用于生产的改性填料或滤料,在废水处理反应器初期挂膜过程中,接种生长的微生物有一定的刺激生长作用。Appropriate rare earth compounds are used in the production of modified fillers or filter materials. During the initial film formation process of wastewater treatment reactors, the inoculated and grown microorganisms have a certain growth-stimulating effect.
本发明中稀土化合物添加剂可以为单一稀土,也可以为复合稀土。稀土化合物可以为硝酸盐或氯化盐稀土化合物。The rare earth compound additive in the present invention can be a single rare earth or a compound rare earth. The rare earth compound may be a nitrate or chloride rare earth compound.
本发明中填料、滤料等载体可以由聚乙烯、聚氯乙烯、聚苯乙烯、聚丙烯塑料或尼龙、维纶、腈纶、涤纶化纤材料制造。Carriers such as fillers and filter materials in the present invention can be made of polyethylene, polyvinyl chloride, polystyrene, polypropylene plastics or nylon, vinylon, acrylic, polyester chemical fiber materials.
本发明适用的反应器包括生物移动床、生物转盘、生物滤池、生物流化床、生物栅。The reactor applicable to the present invention includes biological moving bed, biological turntable, biological filter, biological fluidized bed and biological barrier.
3.有益效果3. Beneficial effect
本发明提供了一种提高微生物附着生长废水处理生物膜反应器效能的方法,本发明操作简单,通过在填料或滤料等载体的生产制造过程中加入一定浓度的稀土化合物,即可有效地加速了废水处理生物膜反应器的启动,并可明显提高净化效果和稳定性,而稀土投加量少,废水处理成本低,具有广阔的应用前景。使用本发明方法生物的改性微生物附着生长固定化材料,其形成的成熟生物膜时间可以提前5~10天,同时微生物活性与稳定性提高,废水中COD去除率可以提高5%~15%,其他主要污染物去除率可提高5%~10%。The invention provides a method for improving the performance of biofilm reactors for microbial attachment and growth wastewater treatment. The start-up of biofilm reactor for wastewater treatment is guaranteed, and the purification effect and stability can be obviously improved, while the rare earth dosage is small, the cost of wastewater treatment is low, and it has broad application prospects. Using the bio-modified microbial attachment growth immobilization material of the method of the present invention, the mature biofilm time can be advanced by 5 to 10 days, and at the same time the microbial activity and stability can be improved, and the COD removal rate in the wastewater can be increased by 5% to 15%. The removal rate of other major pollutants can be increased by 5% to 10%.
具体实施方式Detailed ways
以下通过实试例对本发明做进一步详述。The present invention will be described in further detail below through practical examples.
实施例1Example 1
添加硝酸稀土生产改性悬浮填料,其加入量为5mg/kg(填料基料)的Ce(NO3)3,将制造的改性聚氯乙烯填料装入移动床生物膜反应器中处理制药废水,以某污水处理厂曝气池污泥作为接种污泥室温(20~30℃)启动开始挂膜,初始进水COD浓度为500mg/L,营养元素正常投加,经过22天的启动运行,达到设计COD容积负荷0.8kg/m3·d,与添加未改性的填料比较,启动减少7天,启动完成后对COD去除率提高5%~8%。Adding rare earth nitrate to produce modified suspension packing, the addition amount is Ce(NO 3 ) 3 of 5 mg/kg (filler base material), and putting the manufactured modified polyvinyl chloride packing into a moving bed biofilm reactor to treat pharmaceutical wastewater , using the sludge from the aeration tank of a sewage treatment plant as the inoculum sludge to start film formation at room temperature (20-30°C), the initial influent COD concentration was 500mg/L, and nutrients were added normally. After 22 days of start-up operation, The designed COD volume load is 0.8kg/m 3 ·d. Compared with the addition of unmodified filler, the start-up is reduced by 7 days, and the COD removal rate is increased by 5% to 8% after the start-up is completed.
实施例2Example 2
添加氯化稀土生产改性生物转盘,其加入量为2mg/kg(填料基料)的CeCl3/LaCl3复合添加剂,将制造的改性聚乙烯和聚丙烯塑料生物转盘用于处理城市污水,以某城市污水处理厂曝气池污泥作为接种污泥室温(20~30℃)启动挂膜,初始进水COD浓度为250-350mg/L,营养元素正常投加,挂膜启动时间为12天,达到设计COD容积负荷1.0-1.2kg/m3·d,与不含稀土填料相比,启动减少5天,启动完成后对基质的去除率提高5%~8%。Add rare earth chloride to produce modified biological turntables, the amount of which is 2mg/kg (filler base material) CeCl 3 /LaCl 3 composite additives, the modified polyethylene and polypropylene plastic biological turntables manufactured are used to treat urban sewage, The sludge from the aeration tank of an urban sewage treatment plant was used as the inoculation sludge to start film formation at room temperature (20-30°C). The initial influent COD concentration was 250-350mg/L, and nutrients were added normally. The start-up time of film formation was 12 day, to reach the design COD volume load of 1.0-1.2kg/m 3 ·d, compared with fillers without rare earths, the start-up is reduced by 5 days, and the removal rate of the matrix is increased by 5%-8% after the start-up is completed.
实施例3Example 3
添加复合稀土化合物生产改性生物绳填料,其加入量为6mg/kg(填料基料)的复合稀土化合物(55%~65%Ce(NO3)3、5%~15%EuCl3、10%~30%Gd(NO3)3)/kg的复合稀土添加剂,将制造的改性尼伦维伦化纤材料生物绳装入厌氧滤池反应器(AF)中用于处理制糖废水,同时加入接种污泥进行中温(33~35℃)启动挂膜,达到COD进水负荷5.5kg/m3·d的时间为35天,与不含稀土载体相比,启动减少12天,启动完成后对COD去除率提高10%~15%。Add compound rare earth compound to produce modified biological rope filler, its addition is 6mg/kg (filler base material) compound rare earth compound (55%~65% Ce(NO 3 ) 3 , 5%~15% EuCl 3 , 10% ~30%Gd(NO 3 ) 3 )/kg compound rare earth additive, the modified Nylen Velen chemical fiber material bio-rope manufactured is packed in the anaerobic filter reactor (AF) for the treatment of sugar wastewater, and at the same time Add inoculated sludge to start film formation at medium temperature (33-35°C), and the time to reach COD influent load 5.5kg/m 3 ·d is 35 days. Compared with the carrier without rare earth, the start-up is reduced by 12 days. The removal rate of COD is increased by 10% to 15%.
实施例4Example 4
添加氯化稀土化合物生产改性填料,其加入量为6mg/kg(填料基料)的CeCl3,将制造的改性塑料填料装入厌氧生物流化床反应器中用于处理制糖废水,同时加入接种污泥进行中温(33~35℃)启动挂膜,达到COD进水负荷5.5kg/m3·d的时间为39天,与不含稀土载体相比,启动减少8天,启动完成后对COD去除率提高8%~15%。Add chlorinated rare earth compounds to produce modified fillers, the amount of which is 6mg/kg (filler base) of CeCl 3 , and put the manufactured modified plastic fillers into an anaerobic biological fluidized bed reactor for the treatment of sugar wastewater At the same time, add inoculation sludge to start film formation at medium temperature (33-35°C), the time to reach COD influent load 5.5kg/m 3 ·d is 39 days, compared with the carrier without rare earth, the start-up is reduced by 8 days, and the start-up After completion, the COD removal rate is increased by 8% to 15%.
实施例5Example 5
添加复合稀土化合物生产改性填料,其加入量为3.5mg/kg(填料基料)的Ce(NO3)3/LaCl3,将制造的改性塑料填料装入好氧生物栅中用于处理城市污水,同时加入接种污泥进行中温(33~35℃)启动挂膜,达到COD进水负荷0.8kg/m3·d的时间为13天,与不含稀土载体相比,启动减少5天,启动完成后对COD去除率提高8%~15%,TN去除率提高5%~12%,TP去除率提高5%~15%。Add composite rare earth compounds to produce modified fillers, the amount of which is 3.5 mg/kg (filler base) Ce(NO 3 ) 3 /LaCl 3 , and the manufactured modified plastic fillers are loaded into an aerobic biobarrier for treatment For urban sewage, add inoculated sludge at the same time to start film formation at medium temperature (33-35°C), and the time to reach the COD influent load of 0.8kg/m 3 ·d is 13 days, which is 5 days less than that without rare earth carrier. , After the startup is completed, the removal rate of COD is increased by 8% to 15%, the removal rate of TN is increased by 5% to 12%, and the removal rate of TP is increased by 5% to 15%.
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