CN101289244A - A method for natural photocatalytic degradation of chlorophenol pollutants - Google Patents
A method for natural photocatalytic degradation of chlorophenol pollutants Download PDFInfo
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Abstract
本发明涉及一种用于自然光催化降解氯酚类污染物的方法。首先于质量浓度为10-2-300mg/L的氯酚类污染物水溶液中加入催化剂,所述催化剂由组分A和B组成,A为二价或三价可溶性铁盐,B为碱金属的可溶性盐;A、B的物质的量之比为0.01~1;催化剂与氯酚类物质的量之比为0.01~1。本发明反应条件为室外太阳光照射,价格低廉,降解率高,没有二次污染,适用于分布广、浓度较低的氯酚类污染物及有氯酚类污染物产生的废水的降解,工业化应用前景大。The invention relates to a method for natural photocatalytic degradation of chlorophenol pollutants. First, a catalyst is added to an aqueous solution of chlorophenol pollutants with a mass concentration of 10-2-300mg /L. The catalyst is composed of components A and B. A is a divalent or trivalent soluble iron salt, and B is an alkali metal Soluble salt; the ratio of the amount of substances A and B is 0.01-1; the ratio of the amount of catalyst to chlorophenols is 0.01-1. The reaction condition of the present invention is outdoor sunlight irradiation, low price, high degradation rate, no secondary pollution, suitable for the degradation of chlorophenol pollutants with wide distribution and low concentration and waste water produced by chlorophenol pollutants, industrialization The application prospect is great.
Description
技术领域 technical field
本发明涉及氯酚污染物的光降解去除方法,具体地说是一种太阳照射下催化降解氯酚类污染物的方法。The invention relates to a method for photodegradation and removal of chlorophenol pollutants, in particular to a method for catalytically degrading chlorophenol pollutants under sunlight.
背景技术 Background technique
自20世纪30年代以来,氯酚类化合物(CPs)被广泛用作木材防腐剂、防锈剂、杀菌剂和除草剂等,并且在纸浆漂白工艺中也会产生大量的氯酚类的废水,在亚洲、非洲和南美洲还用于血吸虫病的防治,因此在许多工业化国家CPs的生产规模非常庞大。同时,2-氯酚、2,4-二氯酚、2,4,6-三氯酚和五氯酚都是毒性很高的物质,被美国EPA列入优先控制污染物的黑名单。氯酚类化合物的大量使用,使得大量的CPs污染物进入了环境,给自然环境造成很大的危害。因此,清除环境中的该类化合物是人类面临的一大挑战。Since the 1930s, chlorophenols (CPs) have been widely used as wood preservatives, rust inhibitors, fungicides and herbicides, etc., and a large amount of chlorophenols wastewater is also produced in the pulp bleaching process, It is also used in the control of schistosomiasis in Asia, Africa and South America, so the production scale of CPs in many industrialized countries is very large. At the same time, 2-chlorophenol, 2,4-dichlorophenol, 2,4,6-trichlorophenol and pentachlorophenol are highly toxic substances, and are included in the blacklist of priority pollutants by the US EPA. The extensive use of chlorophenol compounds has caused a large number of CPs pollutants to enter the environment, causing great harm to the natural environment. Therefore, removing such compounds from the environment is a major challenge for humans.
目前处理含氯酚类废水的方法很多,常用的方法为生物降解法、吸附法、萃取法、液膜分离法。但生物法需要的时间特别长,并且对于高浓度氯酚废水的处理不适用。此外,生物降解氯酚类废水还会产生毒性更大的二恶英类污染物(L.G.Oeberg,Chemosphere,1992)。高级氧化技术是20世纪80年代发展起来的处理难降解的有机污染物的技术,其主要特点是通过化学反应产生羟基自由基,使有机污染物有效地降解成水,二氧化碳和无机离子;主要包括臭氧氧化,光催化氧化,湿式氧化,H2O2/UV,Fenton,O3/UV等方法。在高级氧化法处理氯苯酚的方法中,光催化氧化法由于成本较低,条件温和,引起了人们的广泛关注。在氯酚类的降解中,最有代表性的是Meunier的催化氧化体系(Science 1996),用双氧水为氧化剂,铁酞菁为催化剂,处理氯酚类有机污染物,三氯苯酚中碳的矿化率为14%,氯的矿化率为70%。世界专利申请(S.Muriel,WO0059836,2000)发明了金属酞菁催化剂,用双氧水为氧化剂,用来处理三氯苯酚废水。另外,在Collins的催化体系中(Science 2002)中,用四氨基铁大环化合物为催化剂,双氧水为氧化剂,三氯苯酚的矿化率是35%,氯的矿化率是83%。目前存在的问题主要是所用的氧化剂如H2O2和O3价格昂贵,使处理成本相对较高,并且在催化氧化过程中,铁酞菁催化剂等的合成成本也相对较高,另外,一些过渡金属催化剂不稳定,容易失活,这些问题的存在使得对于氯酚类废水的处理可工业化前景很小。At present, there are many methods for treating chlorophenol-containing wastewater, and the commonly used methods are biodegradation, adsorption, extraction, and liquid membrane separation. However, the biological method takes a long time and is not suitable for the treatment of high-concentration chlorophenol wastewater. In addition, biodegradation of chlorophenol wastewater will also produce more toxic dioxin-like pollutants (LGOeberg, Chemosphere, 1992). Advanced oxidation technology is a technology developed in the 1980s to deal with refractory organic pollutants. Its main feature is to generate hydroxyl radicals through chemical reactions, so that organic pollutants can be effectively degraded into water, carbon dioxide and inorganic ions; mainly including Ozone oxidation, photocatalytic oxidation, wet oxidation, H2O2/UV, Fenton, O3/UV and other methods. Among advanced oxidation methods for treating chlorophenols, photocatalytic oxidation has attracted widespread attention due to its low cost and mild conditions. In the degradation of chlorophenols, the most representative one is Meunier's catalytic oxidation system (Science 1996), which uses hydrogen peroxide as oxidant and iron phthalocyanine as catalyst to deal with chlorophenols organic pollutants and the mineralization of carbon in trichlorophenols. The mineralization rate of chlorine is 14%, and the mineralization rate of chlorine is 70%. The world patent application (S.Muriel, WO0059836, 2000) invented a metal phthalocyanine catalyst, which uses hydrogen peroxide as an oxidant to treat trichlorophenol wastewater. In addition, in Collins' catalytic system (Science 2002), using tetraaminoiron macrocyclic compound as catalyst and hydrogen peroxide as oxidant, the mineralization rate of trichlorophenol is 35%, and the mineralization rate of chlorine is 83%. The existing problems are mainly that the used oxidants such as H 2 O 2 and O 3 are expensive, so that the processing cost is relatively high, and in the process of catalytic oxidation, the synthesis cost of iron phthalocyanine catalyst, etc. is also relatively high. In addition, some Transition metal catalysts are unstable and easy to deactivate. The existence of these problems makes the industrialization prospect of chlorophenol wastewater treatment very small.
发明内容 Contents of the invention
为了克服上述降解氯酚类方法中存在的一些不足,本发明的目的在于提供一种催化活性高,处理效果好,反应条件温和,处理成本低,工业化应用前景大,可实现原位处理的光催化降解氯酚类污染物的方法。In order to overcome some deficiencies in the above-mentioned methods for degrading chlorophenols, the purpose of the present invention is to provide a photocatalyst with high catalytic activity, good treatment effect, mild reaction conditions, low treatment cost, great industrial application prospect, and in-situ treatment. A method for catalytically degrading chlorophenol pollutants.
为实现上述目的,本发明采用的技术方案为:To achieve the above object, the technical solution adopted in the present invention is:
一种自然光催化降解氯酚类污染物的方法,A method for natural photocatalytic degradation of chlorophenol pollutants,
首先于质量浓度为10-2-300mg/L的氯酚类污染物水溶液中加入催化剂;First, a catalyst is added to the aqueous solution of chlorophenol pollutants with a mass concentration of 10-2-300mg /L;
所述催化剂由组分A和B组成,A为二价或三价可溶性铁盐,B为碱金属的可溶性盐;A、B的物质的量之比为0.01~1;催化剂与氯酚类物质的量之比为0.01~1。The catalyst is composed of components A and B, A is a divalent or trivalent soluble iron salt, B is a soluble salt of an alkali metal; the ratio of the amounts of A and B is 0.01 to 1; the catalyst and chlorophenols The amount ratio is 0.01-1.
所述三价可溶性铁盐为三氯化铁、硝酸铁和/或硫酸铁;碱金属的可溶性盐为硝酸盐,这些可溶性盐以NO3 -和/或NO2 -为活性阴离子组分;催化剂与氯酚的物质的量之比最好为0.4~1。The trivalent soluble iron salt is ferric chloride, ferric nitrate and/or ferric sulfate; the soluble salt of alkali metal is nitrate, and these soluble salts use NO 3 - and/or NO 2 - as active anion components; catalyst The ratio of the amount of substance to chlorophenol is preferably 0.4-1.
所述自然环境是指环境温度在-25℃至45℃,每天太阳光的照射时间为8-16小时的自然环境。本方法反应条件温和,完全暴露在自然环境中,实验在实验室楼顶完成,采用纯自然天气,白天黑夜交替循环。The natural environment refers to a natural environment with an ambient temperature of -25°C to 45°C and a daily sunlight exposure time of 8-16 hours. This method has mild reaction conditions and is completely exposed to the natural environment. The experiment is completed on the roof of the laboratory building, using pure natural weather, and alternating day and night.
本发明具有如下优点:The present invention has the following advantages:
1.催化剂活性高,反应条件温和。本发明是在带有磨口的小试管中,加入三价可溶性铁盐与非过渡金属的盐溶液组成的催化剂,以空气为氧化剂,可将氯酚氧化降解为二氧化碳,水及一些无毒的小分子羧酸。该法处理氯酚溶液可以达到100%的降解率,在降解过程中没有二次污染。1. The catalyst has high activity and mild reaction conditions. In the present invention, a catalyst composed of trivalent soluble iron salt and non-transition metal salt solution is added to a small test tube with a ground mouth, and air is used as an oxidant to oxidize and degrade chlorophenol into carbon dioxide, water and some non-toxic small molecule carboxylic acid. The method can achieve 100% degradation rate in treating chlorophenol solution, and there is no secondary pollution in the degradation process.
2.处理成本低,工业化前景大。由于本发明所用的氧化剂和催化剂用量小,且便宜易得,处理过程简便,因此本发明所述的催化氧化法具有可工业化处理氯酚类污染物的应用前景,适用于分布广、浓度较低的氯酚类污染物的降解;该方法处理氯酚废水反应条件温和,价格低廉,降解率高。3.环境友好。本发明所述的反应体系简单,方便实用,催化剂反应活性高,对污染物的去除彻底。催化剂在所用的浓度范围内对环境不会造成二次污染。2. The processing cost is low, and the industrialization prospect is great. Because the amount of oxidizing agent and catalyst used in the present invention is small, cheap and easy to obtain, and the treatment process is simple and convenient, the catalytic oxidation method of the present invention has the application prospect of industrially treating chlorophenol pollutants, and is suitable for wide distribution and low concentration Degradation of chlorophenol pollutants; this method has mild reaction conditions, low price and high degradation rate for treating chlorophenol wastewater. 3. Environmental friendly. The reaction system of the invention is simple, convenient and practical, has high catalyst reactivity and can completely remove pollutants. The catalyst will not cause secondary pollution to the environment within the concentration range used.
4.适用范围广。本发明适用于氯酚废水及一些有关氯酚生长厂的废水的处理,常见的需被处理的氯酚的结构式举例如下:4. Wide application range. The present invention is applicable to the treatment of chlorophenol wastewater and some wastewater related to chlorophenol growth plants. The structural formula of common chlorophenols to be treated is exemplified as follows:
n=1~5。n=1-5.
总之,本发明反应条件为室外太阳光照射,价格低廉,降解率高,没有二次污染,适用于分布广、浓度较低的氯酚类污染物及有氯酚类污染物产生的废水的降解,工业化应用前景大。In a word, the reaction condition of the present invention is outdoor sunlight irradiation, low price, high degradation rate, no secondary pollution, suitable for the degradation of chlorophenol pollutants with wide distribution and low concentration and waste water produced by chlorophenol pollutants , and has great prospects for industrial application.
具体实施方式Detailed ways
下面通过实例对本发明给予进一步的说明,当然,本发明不仅限于下述的实施例。The present invention is given further description by examples below, of course, the present invention is not limited to following examples.
实施例1Example 1
首先配制200mg/L的三氯酚溶液,再用纯水稀释10倍,15ml溶液装入20ml带磨口塞的玻璃试管中,并向试管中加入催化剂,盖上盖子,并用封口膜密封,放入实验室楼顶,定时采样检测,同时做了对照反应及放大反应,反应后三氯酚的去除率见表1。环境温度在-25℃至10℃,每天太阳光的照射时间为8-10小时。First prepare a 200mg/L trichlorophenol solution, then dilute it 10 times with pure water, put 15ml of the solution into a 20ml glass test tube with a ground stopper, add a catalyst to the test tube, cover the lid, seal it with a parafilm, and put Enter the roof of the laboratory building, regularly sample and detect, and do a control reaction and an amplification reaction at the same time, and the removal rate of trichlorophenol after the reaction is shown in Table 1. The ambient temperature is -25°C to 10°C, and the daily sunlight exposure time is 8-10 hours.
表1自然条件下光催化降解三氯酚的结果Table 1 The results of photocatalytic degradation of trichlorophenol under natural conditions
mol%为催化剂与三氯酚的比例mol% is the ratio of catalyst to trichlorophenol
实施例2Example 2
按照上述实施例1的操作步骤,用FeCl3/NaNO2为催化剂,在同样的条件下处理20mg/L邻氯酚污染物,结果见表2。环境温度在-25℃至10℃,每天太阳光的照射时间为8-10小时。According to the operation procedure of the above-mentioned Example 1, FeCl 3 /NaNO 2 was used as a catalyst, and 20 mg/L o-chlorophenol pollutant was treated under the same conditions, and the results are shown in Table 2. The ambient temperature is -25°C to 10°C, and the daily sunlight exposure time is 8-10 hours.
表2自然条件下光催化降解邻氯酚的结果Table 2 The results of photocatalytic degradation of o-chlorophenol under natural conditions
实施例3Example 3
按照上述实施例1的操作步骤,用FeCl3/NaNO2为催化剂,在同样的条件下处理20mg/L对氯酚污染物,结果见表3。环境温度在-25℃至10℃,每天太阳光的照射时间为8-10小时。According to the operation procedure of the above-mentioned Example 1, FeCl 3 /NaNO 2 was used as a catalyst to treat 20 mg/L p-chlorophenol pollutants under the same conditions, and the results are shown in Table 3. The ambient temperature is -25°C to 10°C, and the daily sunlight exposure time is 8-10 hours.
表3自然条件下光催化降解对氯酚的结果Table 3 The results of photocatalytic degradation of p-chlorophenol under natural conditions
实施例4Example 4
按照上述实施例1的操作步骤,用FeCl3/NaNO2为催化剂,在同样的条件下处理20mg/L 2,4-二氯酚污染物,结果见表4。环境温度在-25℃至10℃,每天太阳光的照射时间为8-10小时。According to the operation steps of the above-mentioned Example 1, FeCl 3 /NaNO 2 was used as a catalyst to treat 20 mg/L 2,4-dichlorophenol pollutants under the same conditions, and the results are shown in Table 4. The ambient temperature is -25°C to 10°C, and the daily sunlight exposure time is 8-10 hours.
表4自然条件下光催化降解2,4-二氯酚的结果The results of photocatalytic degradation of 2,4-dichlorophenol under natural conditions in table 4
实施例5Example 5
按照上述实施例1的操作步骤,用FeCl3/NaNO2为催化剂,在同样的条件下处理20mg/L五氯酚污染物,结果见表5。环境温度在-25℃至10℃,每天太阳光的照射时间为8-10小时。According to the operation steps of the above-mentioned Example 1, FeCl 3 /NaNO 2 was used as a catalyst to treat 20 mg/L pentachlorophenol pollutants under the same conditions, and the results are shown in Table 5. The ambient temperature is -25°C to 10°C, and the daily sunlight exposure time is 8-10 hours.
表5自然条件下光催化降解五氯酚的结果The results of photocatalytic degradation of pentachlorophenol under natural conditions in table 5
实施例6Example 6
按照上述实施例1的操作步骤,用FeCl3/NaNO2为催化剂,在环境温度在20℃至35℃,每天太阳光的照射时间为12-14小时的条件下,处理20mg/L三氯酚污染物,结果见表6。According to the operation steps of the above-mentioned Example 1, using FeCl 3 /NaNO 2 as a catalyst, at an ambient temperature of 20°C to 35°C, and under the conditions of 12-14 hours of sunlight irradiation time per day, 20mg/L trichlorophenol was treated Pollutants, the results are shown in Table 6.
表6自然条件下光催化降解三氯酚的结果The results of photocatalytic degradation of trichlorophenol under natural conditions in table 6
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CN110683637A (en) * | 2019-10-14 | 2020-01-14 | 临沂大学 | A method for domesticating aerobic microorganisms capable of degrading 2-chlorophenol using phenol as an inducer |
CN112408660A (en) * | 2020-12-11 | 2021-02-26 | 辽宁大学 | Method for degrading 1-chloronaphthalene-containing wastewater by using nitrite based on light conversion |
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CN1569676A (en) * | 2003-07-25 | 2005-01-26 | 中国科学院大连化学物理研究所 | Method for eliminating aqueous solution pollution from halo-phenol compounds |
CN100387334C (en) * | 2005-09-20 | 2008-05-14 | 中国科学院大连化学物理研究所 | A method for treating chlorophenol pollutants by catalytic oxidation |
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CN112408660A (en) * | 2020-12-11 | 2021-02-26 | 辽宁大学 | Method for degrading 1-chloronaphthalene-containing wastewater by using nitrite based on light conversion |
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