CN106396073B - Water treatment device and method for removing pollutants by using ozone-OH - Google Patents
Water treatment device and method for removing pollutants by using ozone-OH Download PDFInfo
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- CN106396073B CN106396073B CN201610805104.9A CN201610805104A CN106396073B CN 106396073 B CN106396073 B CN 106396073B CN 201610805104 A CN201610805104 A CN 201610805104A CN 106396073 B CN106396073 B CN 106396073B
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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
- C02F1/78—Treatment of water, waste water, or sewage by oxidation with ozone
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Abstract
本发明涉及一种利用臭氧‑OH·去除污染物的水处理装置及方法,装置包括圆柱状壳体,在壳体的顶部左侧安装有出水口,在壳体的右侧自上而下依次安装有加药口、上层取样口、中层取样口及下层取样口,在壳体的底端通过法兰连接有臭氧曝气口管道,在曝气口管道的侧壁上安装有进水口,在壳体内的中下部安置有活性炭填装柱,方法包括:第一步,根据试验数据和拟合模型,确定活性炭、臭氧和对氯苯甲酸的反应体系用量配方,第二步,控制污水流速。本发明所用试剂配方及用量可以促进臭氧在反应过程中分解产生大量的OH·,通过产生大量OH·高效地去除污染物。
The invention relates to a water treatment device and method for removing pollutants by using ozone-OH. The device includes a cylindrical shell, and a water outlet is installed on the left side of the top of the shell. The dosing port, the upper sampling port, the middle sampling port and the lower sampling port are installed, and the bottom of the shell is connected with the ozone aeration port pipe through the flange, and the water inlet is installed on the side wall of the aeration port pipe. The middle and lower part of the casing is equipped with an activated carbon packed column. The method includes: the first step is to determine the dosage formula of the reaction system of activated carbon, ozone and p-chlorobenzoic acid according to the test data and the fitting model; the second step is to control the flow rate of the sewage. The reagent formula and dosage used in the present invention can promote the decomposition of ozone to generate a large amount of OH in the reaction process, and efficiently remove pollutants by generating a large amount of OH.
Description
技术领域technical field
本发明属于水处理技术领域,特别是一种利用臭氧-OH·去除污染物的水处理装置及方法。The invention belongs to the technical field of water treatment, in particular to a water treatment device and method for removing pollutants by using ozone-OH·.
背景技术Background technique
不同pH条件下,多相臭氧催化氧化的反应过程分为三步:Under different pH conditions, the reaction process of heterogeneous ozone catalytic oxidation is divided into three steps:
第一步过程,臭氧均相分解The first step process, the homogeneous decomposition of ozone
O3In→O3 ·-+In+ (1-3)O 3 In→O 3 ·- +In + (1-3)
第二步过程,活性炭表面多相分解The second step process, multiphase decomposition on the surface of activated carbon
2<pH<6:2<pH<6:
pH>6:pH>6:
第二步过程,自由基均相扩散和终止反应The second step process, homogeneous diffusion of free radicals and termination reaction
上述式中S为催化剂表面,In为促进臭氧分解的基团,P为羟基自由基捕获剂,第二步过程,公式(1-5)至公式(1-11),为活性炭表面化学反应,涉及吸附、表面反应和解吸等过程,第3步过程,公式(1-12)至公式(1-15),在液相反应体系中进行。In the above formula, S is the catalyst surface, In is a group that promotes the decomposition of ozone, and P is a hydroxyl radical scavenger. The second step process, formula (1-5) to formula (1-11), is the surface chemical reaction of activated carbon, Involving processes such as adsorption, surface reaction, and desorption, the third step process, formula (1-12) to formula (1-15), is carried out in a liquid phase reaction system.
发明内容Contents of the invention
本发明的目的是针对现有技术的不足,而提出一种利用臭氧-OH·去除污染物的水处理装置及方法。The purpose of the present invention is to propose a water treatment device and method that utilizes ozone-OH· to remove pollutants against the deficiencies of the prior art.
本发明解决其技术问题是采取以下技术方案实现的:The present invention solves its technical problem and realizes by taking the following technical solutions:
一种利用臭氧-OH·去除污染物的水处理装置,包括装置的圆柱状壳体,在壳体的顶部左侧安装有出水口,在壳体的右侧自上而下依次安装有加药口、上层取样口、中层取样口及下层取样口,在壳体的底端通过法兰连接有臭氧曝气口管道,在曝气口管道的侧壁上安装有进水口,在壳体内的中下部安置有活性炭填装柱。A water treatment device that uses ozone-OH to remove pollutants, including a cylindrical shell of the device, a water outlet is installed on the left side of the top of the shell, and a dosing device is installed sequentially on the right side of the shell from top to bottom Port, upper sampling port, middle sampling port and lower sampling port, the bottom end of the housing is connected with the ozone aeration port pipe through the flange, the water inlet is installed on the side wall of the aeration port pipe, and the middle part in the housing The lower part is equipped with an activated carbon packed column.
而且,所述活性炭填装柱的直径为壳体直径的三分之一至二分之一,活性炭填装柱距壳体底端法兰的距离为活性炭填装柱直径的0.5倍至1.0倍,活性炭填装柱的高度为其自身直径的5倍至8倍,是壳体高度的0.4倍至0.5倍。Moreover, the diameter of the activated carbon packed column is 1/3 to 1/2 of the shell diameter, and the distance between the activated carbon filled column and the bottom flange of the shell is 0.5 to 1.0 times the diameter of the activated carbon filled column. , the height of the activated carbon packed column is 5 to 8 times its own diameter, and 0.4 to 0.5 times the height of the shell.
而且,所述壳体高1.5m,直径0.3m。Also, the shell is 1.5m high and 0.3m in diameter.
一种利用臭氧-OH·去除污染物的水处理装置的方法,方法内容包括:A method for a water treatment device utilizing ozone-OH to remove pollutants, the method comprising:
第一步,根据试验数据和拟合模型,确定活性炭、臭氧和对氯苯甲酸的反应体系用量配方,The first step is to determine the dosage formula of the reaction system of activated carbon, ozone and p-chlorobenzoic acid according to the experimental data and the fitting model,
其中,拟合模型包括:Among them, the fitting model includes:
一次多项式模型: A polynomial model of degree one:
二次多项式模型: Quadratic polynomial model:
其中,反应体系用量配方为:选用活性炭为固相催化剂,活性炭体系用量为5g,在臭氧曝气口臭氧浓度为16mg/L,臭氧气体流速为60L/h的曝气条件下,加入的对氯苯甲酸用量为3g/L;Among them, the dosage formula of the reaction system is: select activated carbon as the solid-phase catalyst, the dosage of activated carbon system is 5g, under the aeration conditions where the ozone concentration at the ozone aeration port is 16mg/L, and the ozone gas flow rate is 60L/h, the added p-chlor The dosage of benzoic acid is 3g/L;
第二步,控制污水流速,控制污水由装置壳体底部流入,由装置壳体顶部流出,被处理污水在装置壳体内停留时间为2.5h至3.5h。The second step is to control the sewage flow rate, control the sewage to flow in from the bottom of the device shell, and flow out from the top of the device shell. The residence time of the treated sewage in the device shell is 2.5h to 3.5h.
本发明的优点和积极效果是:Advantage and positive effect of the present invention are:
1、本发明方法所用试剂配方及用量可以促进臭氧分解产生OH·在反应过程中产生大量的OH·。1, the used reagent formula and consumption of the inventive method can promote ozonolysis to produce OH. Produce a large amount of OH in the reaction process.
2、本发明装置通过可以通过产生大量OH·高效地去除污染物。2. The device of the present invention can efficiently remove pollutants by generating a large amount of OH.
附图说明Description of drawings
图1是本发明装置的结构示意图。Fig. 1 is a structural schematic diagram of the device of the present invention.
具体实施方式Detailed ways
以下对本发明实施例做进一步详述:需要强调的是,本发明所述的实施例是说明性的,而不是限定性的,因此本发明并不限于具体实施方式中所述的实施例,凡是由本领域技术人员根据本发明的技术方案得出的其它实施方式,同样属于本发明保护的范围。The embodiments of the present invention are described in further detail below: It should be emphasized that the embodiments of the present invention are illustrative rather than limiting, so the present invention is not limited to the embodiments described in the specific implementation methods. Other implementations obtained by those skilled in the art according to the technical solution of the present invention also belong to the protection scope of the present invention.
一种利用臭氧-OH·去除污染物的水处理装置,包括装置的圆柱状壳体2,在壳体的顶部左侧安装有出水口1,在壳体的右侧自上而下依次安装有加药口3、上层取样口4、中层取样口6及下层取样口7,在壳体的底端通过法兰8连接有臭氧曝气口管道9,在曝气口管道的侧壁上安装有进水口10,在壳体内的中下部安置有活性炭填装柱5。A water treatment device that uses ozone-OH to remove pollutants, including a cylindrical housing 2 of the device, a water outlet 1 is installed on the left side of the top of the housing, and a water outlet is installed on the right side of the housing from top to bottom. The dosing port 3, the upper sampling port 4, the middle sampling port 6 and the lower sampling port 7 are connected with an ozone aeration port pipe 9 through a flange 8 at the bottom end of the housing, and installed on the side wall of the aeration port pipe The water inlet 10 is provided with an activated carbon packing column 5 in the middle and lower part of the housing.
在本发明的具体实施中,所述活性炭填装柱的直径为壳体直径的三分之一至二分之一,活性炭填装柱距壳体底端法兰的距离为活性炭填装柱直径的0.5倍至1.0倍,活性炭填装柱的高度为其自身直径的5倍至8倍,是壳体高度的0.4倍至0.5倍。In the specific implementation of the present invention, the diameter of the activated carbon packing column is 1/3 to 1/2 of the housing diameter, and the distance between the activated carbon filling column and the shell bottom flange is the diameter of the activated carbon filling column. The height of the activated carbon packed column is 5 to 8 times its own diameter, and 0.4 to 0.5 times the height of the shell.
在本发明的具体实施中,所述壳体高1.5m,直径0.3m。In the specific implementation of the present invention, the housing is 1.5m high and 0.3m in diameter.
一种利用臭氧-OH·去除污染物的水处理装置的方法,方法内容包括:A method for a water treatment device utilizing ozone-OH to remove pollutants, the method comprising:
第一步,根据试验数据和拟合模型,确定活性炭、臭氧和对氯苯甲酸的反应体系用量配方,其中,拟合模型包括:The first step is to determine the dosage formula of the reaction system of activated carbon, ozone and p-chlorobenzoic acid according to the experimental data and the fitting model, wherein the fitting model includes:
一次多项式模型: A polynomial model of degree one:
二次多项式模型: Quadratic polynomial model:
其中,反应体系用量配方为:选用活性炭为固相催化剂,活性炭体系用量为5g,在臭氧曝气口臭氧浓度为16mg/L,臭氧气体流速为60L/h的曝气条件下,加入对氯苯甲酸作为辅助药剂时促进臭氧氧化过程,对氯苯甲酸用量为3g/L。可以促进臭氧在活性炭表面分解,产生羟基自由基释放到液相体系中,改变O3/OH·的链式反应,增强处理效果。Among them, the dosage formula of the reaction system is: select activated carbon as the solid-phase catalyst, the dosage of the activated carbon system is 5g, and under the aeration conditions where the ozone concentration at the ozone aeration port is 16mg/L and the ozone gas flow rate is 60L/h, add p-chlorobenzene When formic acid is used as an auxiliary agent to promote the ozone oxidation process, the dosage of p-chlorobenzoic acid is 3g/L. It can promote the decomposition of ozone on the surface of activated carbon, generate hydroxyl radicals and release them into the liquid phase system, change the chain reaction of O3/OH·, and enhance the treatment effect.
第二步,控制污水流速,控制污水由装置壳体底部流入,由装置壳体顶部流出,被处理污水在装置壳体内停留时间为2.5h至3.5h,处理后的污水满足国家污水排放标准。The second step is to control the sewage flow rate, control the sewage to flow in from the bottom of the device shell, and flow out from the top of the device shell. The residence time of the treated sewage in the device shell is 2.5h to 3.5h. The treated sewage meets the national sewage discharge standard.
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Citations (5)
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JPS5385948A (en) * | 1977-01-05 | 1978-07-28 | Toshiba Corp | Method of treating organic waste liquid |
CN1305439A (en) * | 1998-06-18 | 2001-07-25 | 底格里蒙公司 | Method for mineralization of organic pollutants in water by catalytic ozonization |
CN1446757A (en) * | 2003-04-26 | 2003-10-08 | 清华大学 | Method for purifying pollutant in water by using biological activity carbon-catalysis or activated carbon and oxidation of ozone |
CN103466780A (en) * | 2013-09-26 | 2013-12-25 | 南京大学 | Strengthening method for pollution removing by ozone acidic oxidation |
CN203938513U (en) * | 2014-06-13 | 2014-11-12 | 合肥宏士达环保科技有限责任公司 | A kind of novel ozone and the activated carbon combined device of disposing of sewage |
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Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5385948A (en) * | 1977-01-05 | 1978-07-28 | Toshiba Corp | Method of treating organic waste liquid |
CN1305439A (en) * | 1998-06-18 | 2001-07-25 | 底格里蒙公司 | Method for mineralization of organic pollutants in water by catalytic ozonization |
CN1446757A (en) * | 2003-04-26 | 2003-10-08 | 清华大学 | Method for purifying pollutant in water by using biological activity carbon-catalysis or activated carbon and oxidation of ozone |
CN103466780A (en) * | 2013-09-26 | 2013-12-25 | 南京大学 | Strengthening method for pollution removing by ozone acidic oxidation |
CN203938513U (en) * | 2014-06-13 | 2014-11-12 | 合肥宏士达环保科技有限责任公司 | A kind of novel ozone and the activated carbon combined device of disposing of sewage |
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