CN105800824A - Treatment system for waste water containing hydrazine - Google Patents
Treatment system for waste water containing hydrazine Download PDFInfo
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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
- C02F9/00—Multistage treatment of water, waste water or sewage
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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
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/725—Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
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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
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/74—Treatment of water, waste water, or sewage by oxidation with air
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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
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/38—Organic compounds containing nitrogen
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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
- C02F2301/00—General aspects of water treatment
- C02F2301/08—Multistage treatments, e.g. repetition of the same process step under different conditions
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Abstract
本发明公开了一种含肼类废水处理系统,其包括废水进管(1)、连接管(2)、出水管(3)、加药管(4)、曝气管(5)、回水泵(6)、催化反应器(101)、中间隔板102)、出水隔板(103)、沉降罐中心筒(201)、沉降罐(202)、催化剂恢复罐(301)和搅拌器(302),废水进管(1)位于催化反应器(101)左侧中间位置距离顶部200mm,曝气管(5)整体为UPVC且管路是从催化反应器(101)左侧深入进反应器,均布曝气口在反应器左半侧;本发明在其催化反应过程中不断的有与空气接触,并且还在循环翻动过程中液体处于曝气状态和无氧状态的交替,使得催化的效果可以达到最佳,从而将肼类物质充分分解。
The invention discloses a hydrazine-containing wastewater treatment system, which comprises a wastewater inlet pipe (1), a connecting pipe (2), a water outlet pipe (3), a dosing pipe (4), an aeration pipe (5), and a return pump (6), catalytic reactor (101), intermediate partition (102), water outlet partition (103), settling tank center tube (201), settling tank (202), catalyst recovery tank (301) and agitator (302) , the waste water inlet pipe (1) is located in the middle of the left side of the catalytic reactor (101) and is 200 mm from the top, the aeration pipe (5) is UPVC as a whole and the pipeline is deep into the reactor from the left side of the catalytic reactor (101), all The cloth aeration port is on the left half of the reactor; the present invention is constantly in contact with the air during the catalytic reaction process, and the liquid is alternately in the aerated state and anaerobic state during the cyclic turning process, so that the catalytic effect can be achieved To achieve the best, so as to fully decompose the hydrazine substances.
Description
技术领域technical field
本发明属于环保技术领域,尤其涉及一种含肼类废水处理系统。The invention belongs to the technical field of environmental protection, and in particular relates to a hydrazine-containing wastewater treatment system.
背景技术Background technique
随着行业的技术革新及高速发展,越来越多的废水水质具有难生物降解性、高COD等特点,例如,化工行业产生的废水COD可高达数万、乃至数十万毫克每升,传统的活性污泥法已经无法直接处理这些废水;目前,处理高COD废水的方法主要包括:1)生物厌氧处理及其联用技术,例如,上流式厌氧污泥床(UASB)、厌氧-好氧联用技术(A/O)、缺氧-厌氧-好氧联用技术(A2O)等;2)化学氧化处理及其联用技术,例如,电解-好氧联用技术、芬顿-好氧联用技术等,但是上述提及的方法均有不足之处;生物厌氧处理及其联用技术的缺陷在于反应条件苛刻、装置设计及维护复杂、正式装置运行前厌氧污泥驯化过程漫长;化学氧化处理及其联用技术的缺陷在于药剂成本较高、易产生剧毒副产物,如何处理高COD废水一直是污水处理行业的研究热点。With the technological innovation and rapid development of the industry, more and more wastewater has the characteristics of refractory biodegradability and high COD. For example, the COD of wastewater produced by the chemical industry can be as high as tens of thousands or even hundreds of thousands of mg per liter. The activated sludge method has been unable to directly treat these wastewaters; at present, the methods for treating high COD wastewater mainly include: 1) biological anaerobic treatment and its combination technology, for example, upflow anaerobic sludge bed (UASB), anaerobic - Aerobic combined technology (A/O), anoxic-anaerobic-aerobic combined technology (A 2 O), etc.; 2) Chemical oxidation treatment and its combined technology, for example, electrolysis-aerobic combined technology , Fenton-aerobic combination technology, etc., but the above-mentioned methods all have shortcomings; the defects of biological anaerobic treatment and its combination technology are harsh reaction conditions, complicated device design and maintenance, and exhaustion before the formal device operation. The domestication process of oxygen sludge is long; the disadvantage of chemical oxidation treatment and its combination technology is that the cost of chemicals is high and it is easy to produce highly toxic by-products. How to deal with high COD wastewater has always been a research hotspot in the sewage treatment industry.
发明内容Contents of the invention
为了解决现有技术的问题,本发明提供一种含肼类废水处理系统,该系统主要是针对催化剂的再生及循环利用设计的,在其催化反应过程中不断的有与空气接触,并且还在循环翻动过程中液体处于曝气状态和无氧状态的交替,使得催化的效果可以达到最佳,从而将肼类物质充分分解。In order to solve the problems of the prior art, the present invention provides a hydrazine-containing wastewater treatment system, which is mainly designed for the regeneration and recycling of the catalyst, and is constantly in contact with the air during the catalytic reaction process, and is still During the cyclical turning process, the liquid is alternately in the aerated state and the anaerobic state, so that the catalytic effect can be optimized, so that the hydrazine substances can be fully decomposed.
依据本发明的技术方案,提供一种含肼类废水处理系统包括废水进管1、连接管2、出水管3、加药管4、曝气管5、回水泵6、催化反应器101、中间隔板102、出水隔板103、沉降罐中心筒201、沉降罐202、催化剂恢复罐301和搅拌器302。废水进管1位于催化反应器101左侧中间位置距离顶部200mm,曝气管5整体为UPVC其管路是从催化反应器101左侧深入进反应器,均布曝气口在反应器左半侧。According to the technical solution of the present invention, a hydrazine-containing wastewater treatment system is provided, including a wastewater inlet pipe 1, a connecting pipe 2, an outlet pipe 3, a dosing pipe 4, an aeration pipe 5, a return pump 6, a catalytic reactor 101, an intermediate Separator 102 , water outlet separator 103 , settling tank central cylinder 201 , settling tank 202 , catalyst recovery tank 301 and agitator 302 . The waste water inlet pipe 1 is located in the middle of the left side of the catalytic reactor 101 and is 200mm from the top. The aeration pipe 5 is made of UPVC as a whole, and its pipeline is deep into the reactor from the left side of the catalytic reactor 101. side.
其中,曝气口的每个口布置相对间距300mm且曝气口直径为4mm的孔垂直向上,并且其管路最末端底部设置有3mm垂直向下的孔,用于排水;曝气量的确定为单位时间水量的5倍;中间隔板102位于催化反应器101的中间位置,其顶部距离反应器顶部500mm,底部距离反应器底部300mm,出水隔板103位于催化反应器101左侧,距离右边壁面300mm其底部距离反应器底部300mm顶部距离反应器顶部200mm;连接管2左端从催化反应器101右侧中间位置距离其顶部250mm右端进入沉降罐中心筒201且距离中心筒顶面100mm。Among them, each hole of the aeration port is arranged with a relative distance of 300mm and a hole with a diameter of 4mm vertically upward, and the bottom of the most end of the pipeline is provided with a 3mm vertically downward hole for drainage; the determination of the aeration volume It is 5 times of the water volume per unit time; the middle partition 102 is located in the middle of the catalytic reactor 101, its top is 500 mm away from the top of the reactor, and the bottom is 300 mm away from the bottom of the reactor. The wall surface is 300mm, its bottom is 300mm from the bottom of the reactor, and the top is 200mm from the top of the reactor; the left end of the connecting pipe 2 is 250mm from the middle position on the right side of the catalytic reactor 101, and the right end enters the settling tank central cylinder 201 and is 100mm from the top surface of the central cylinder.
进一步地,中心筒位于沉降罐202中间位置,距离顶部200mm距离底部1200mm,底部100mm处设置有导向作用的锥形;出水管3位于沉降罐202右侧距离顶部高度350mm;催化剂恢复罐301顶部设置有搅拌器302,位于催化剂恢复罐的中间位置,搅拌叶片距离催化剂恢复罐301罐底高度为400mm。Further, the central cylinder is located in the middle of the settling tank 202, 200mm from the top and 1200mm from the bottom, and a tapered guiding function is provided at the bottom 100mm; the outlet pipe 3 is located on the right side of the settling tank 202, and the height from the top is 350mm; the top of the catalyst recovery tank 301 is set There is an agitator 302 located in the middle of the catalyst recovery tank, and the height of the stirring blades from the bottom of the catalyst recovery tank 301 is 400 mm.
本发明的一种含肼类废水处理系统相比于现有技术,具有如下技术优势:Compared with the prior art, a kind of hydrazine-containing wastewater treatment system of the present invention has the following technical advantages:
1.催化剂可以反复在线再生重复利用,节约很大的运行成本。1. The catalyst can be regenerated and reused online repeatedly, which saves a lot of operating costs.
2.设备完全自动运行,不用人为控制。2. The equipment operates completely automatically without human control.
3.设备结构紧凑,处理负荷大。3. The equipment has a compact structure and a large processing load.
附图说明Description of drawings
图1为依据本发明的含肼类废水处理系统的工艺示意图。Figure 1 is a process schematic diagram of a hydrazine-containing wastewater treatment system according to the present invention.
具体实施方式detailed description
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的一部分实施例,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 technical solutions in the embodiments of the present invention will be clearly and completely described below in conjunction with the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only part of the embodiments of the present invention, not all of them; 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.
图1为依据本发明的含肼类废水处理系统的工艺示意图,其中附图标记如下:废水进管1、连接管2、出水管3、加药管4、曝气管5、回水泵6、催化反应器101、中间隔板102、出水隔板103、沉降罐中心筒201、沉降罐202、催化剂恢复罐301和搅拌器302;如图1所示,废水进管1位于催化反应器101左侧中间位置距离顶部200mm,曝气管5整体为UPVC其管路是从催化反应器101左侧深入进反应器,均布曝气口在反应器左半侧,曝气口的每个口布置相对间距300mm且曝气口直径为4mm的孔垂直向上,并且其管路最末端底部设置有3mm垂直向下的孔,用于排水。曝气量的确定为单位时间水量的5倍;中间隔板102位于催化反应器101的中间位置,其顶部距离反应器顶部500mm,底部距离反应器底部300mm,出水隔板103位于催化反应器101左侧,距离右边壁面300mm其底部距离反应器底部300mm顶部距离反应器顶部200mm;连接管2左端从催化反应器101右侧中间位置距离其顶部250mm右端进入沉降罐中心筒201且距离中心筒顶面100mm;中心筒位于沉降罐202中间位置,距离顶部200mm距离底部1200mm,底部100mm处设置有导向作用的锥形;出水管3位于沉降罐202右侧距离顶部高度350mm;催化剂恢复罐301顶部设置有搅拌器302,位于催化剂恢复罐的中间位置,搅拌叶片距离催化剂恢复罐301罐底高度为400mm,其顶部靠右侧设置有加药管4,距离右边距离为100mm;回水泵6进水端连接催化剂恢复罐301右侧距离底部高度200mm的管路出水端连接废水进管1。Fig. 1 is the process schematic diagram of the hydrazine-containing wastewater treatment system according to the present invention, wherein the reference signs are as follows: wastewater inlet pipe 1, connecting pipe 2, water outlet pipe 3, dosing pipe 4, aeration pipe 5, return water pump 6, Catalytic reactor 101, intermediate partition 102, water outlet partition 103, settling tank central cylinder 201, settling tank 202, catalyst recovery tank 301 and agitator 302; as shown in Figure 1, waste water inlet pipe 1 is located on the left side of catalytic reactor 101 The middle position of the side is 200mm from the top, the aeration pipe 5 is UPVC as a whole, and its pipeline is deep into the reactor from the left side of the catalytic reactor 101, and the evenly distributed aeration port is on the left half of the reactor, and each port of the aeration port is arranged The holes with a relative spacing of 300mm and aeration port diameter of 4mm are vertically upward, and the bottom of the most end of the pipeline is provided with a 3mm vertically downward hole for drainage. The determination of the aeration rate is 5 times of the water volume per unit time; the middle partition 102 is located in the middle of the catalytic reactor 101, its top is 500 mm away from the top of the reactor, and the bottom is 300 mm away from the bottom of the reactor, and the water outlet partition 103 is located in the catalytic reactor 101 The left side is 300mm away from the right side wall, and its bottom is 300mm away from the bottom of the reactor, and the top is 200mm away from the top of the reactor; The surface is 100mm; the central tube is located in the middle of the settling tank 202, 200mm from the top and 1200mm from the bottom, and a tapered guide is provided at the bottom 100mm; the outlet pipe 3 is located on the right side of the settling tank 202 and the height from the top is 350mm; the top of the catalyst recovery tank 301 is set There is an agitator 302 located in the middle of the catalyst recovery tank, the height of the stirring blade from the bottom of the catalyst recovery tank 301 is 400 mm, and the top is provided with a dosing pipe 4 on the right side, and the distance from the right side is 100 mm; the water inlet of the return pump 6 Connect the outlet end of the pipeline on the right side of the catalyst recovery tank 301 with a height of 200 mm from the bottom to the waste water inlet pipe 1 .
依据本发明的含肼类废水处理系统的催化反应器101,沉降罐202及催化剂恢复罐301并排布置,间距为500mm。According to the catalytic reactor 101 of the hydrazine-containing wastewater treatment system of the present invention, the settling tank 202 and the catalyst recovery tank 301 are arranged side by side with a distance of 500 mm.
此外,在依据本发明的含肼类废水处理系统中,含肼类废水通过1废水进管与催化剂恢复罐来的催化剂混合在一起后进入到101催化反应器中,在催化反应的过程中,受到从底部来的曝气动力,由于气体的进入使得设备左侧的相对密度极大的降低,由于左侧液位和右侧液位的压力平衡关系使得左侧的液位高于右侧较多,从而左侧液体会从顶部流到右侧,从而便可以将反应器内的液体在曝气动力持续推动下而快速转动起来,废水中的肼类物质在催化剂硫酸铜及溶氧的共同作用下分解成小分子物质;处理后的废水通过103出水隔板处流出来,其中废水中会携带大量的催化反应后的硫酸铜的产物氢氧化铜,进入到201沉降罐中心筒内,通过中心筒从其底部流进沉降罐内,由于其流速降低了很多,此时氢氧化铜会逐渐的沉淀到沉降罐底部,沉降下来的氢氧化铜会通过其底部的排泥管路进入到301催化剂恢复罐内,通过向催化剂恢复罐的4加药管向氢氧化铜液体加入硫酸溶液,其在化学反应的过程中为了使其可以反应充分,反应过程中302搅拌器在不停的旋转中,转速60转/分钟,搅拌叶距离罐底30cm,搅拌直径为罐体直径的1/2,搅拌叶面积为罐体截面的1/30,经过反应后便恢复了其催化作用,经过6回水泵将其泵回废水进管处进行催化反应。In addition, in the hydrazine-containing wastewater treatment system according to the present invention, the hydrazine-containing wastewater enters the 101 catalytic reactor after being mixed with the catalyst from the catalyst recovery tank through the waste water inlet pipe 1. During the catalytic reaction, Due to the aeration power from the bottom, the relative density on the left side of the equipment is greatly reduced due to the entry of gas, and the liquid level on the left is higher than that on the right due to the pressure balance relationship between the liquid level on the left and the liquid level on the right. Therefore, the liquid on the left side will flow from the top to the right side, so that the liquid in the reactor can be quickly rotated under the continuous promotion of aeration power, and the hydrazine substances in the wastewater are combined with the catalyst copper sulfate and dissolved oxygen. Under the action of decomposing into small molecular substances; the treated wastewater flows out through the 103 water outlet partition, and the wastewater will carry a large amount of copper hydroxide, the product of copper sulfate after the catalytic reaction, into the central cylinder of the 201 settling tank, and pass through The central cylinder flows into the settling tank from the bottom, and because the flow rate is much lower, the copper hydroxide will gradually settle to the bottom of the settling tank, and the settled copper hydroxide will enter the 301 through the sludge discharge pipeline at the bottom. In the catalyst recovery tank, add sulfuric acid solution to the copper hydroxide liquid through the 4 dosing pipes of the catalyst recovery tank. In order to make it fully react during the chemical reaction, the 302 agitator is constantly rotating during the reaction process. , the rotating speed is 60 rpm, the stirring blade is 30cm away from the bottom of the tank, the stirring diameter is 1/2 of the diameter of the tank body, and the area of the stirring blade is 1/30 of the cross section of the tank body. After the reaction, its catalytic effect is restored. The water pump pumps it back to the waste water inlet pipe for catalytic reaction.
此催化剂可以不断的重复再生,循环使用;处理后的废水可以进入到生物处理的厌氧处理或者好氧处理。The catalyst can be continuously regenerated and recycled; the treated wastewater can enter the anaerobic or aerobic treatment of biological treatment.
显然上述实施例仅为清楚的说明本发明所做的举例,而并非对实施方式的限定。对于所属领域的普通技术人员来说,在上述说明的基础上,还可以做出其他不同形式的变化或变动,这里无需也无法对所有实施方式予以穷举,由此所引申的显而易见的变化或变动仍处于本发明创造的保护范围之中。Apparently, the above-mentioned embodiments are only examples for clearly illustrating the present invention, rather than limiting the implementation. For those of ordinary skill in the art, on the basis of the above description, other changes or changes in different forms can also be made, and it is not necessary and impossible to exhaustively list all the implementation modes here. Changes are still within the protection scope of the present invention.
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CN1590311A (en) * | 2003-10-28 | 2005-03-09 | 第二炮兵工程学院对外技术服务部 | Treatment method of hydrazin containing waste water |
CN104355443A (en) * | 2014-10-30 | 2015-02-18 | 兰州大学 | Treatment method for unsymmetrical dimethylhydrazine-containing wastewater |
CN104556494A (en) * | 2013-10-15 | 2015-04-29 | 中国石油化工股份有限公司 | Advanced sewage treatment technology |
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2016
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JPS55142590A (en) * | 1979-04-23 | 1980-11-07 | Japan Organo Co Ltd | Treating method of water containing hydrazine |
CN1590311A (en) * | 2003-10-28 | 2005-03-09 | 第二炮兵工程学院对外技术服务部 | Treatment method of hydrazin containing waste water |
CN104556494A (en) * | 2013-10-15 | 2015-04-29 | 中国石油化工股份有限公司 | Advanced sewage treatment technology |
CN104355443A (en) * | 2014-10-30 | 2015-02-18 | 兰州大学 | Treatment method for unsymmetrical dimethylhydrazine-containing wastewater |
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