Movatterモバイル変換


[0]ホーム

URL:


CN111977873A - Method for using photoactivated sepiolite Si-OH for adsorption and photodegradation of water-soluble organic pollutants - Google Patents

Method for using photoactivated sepiolite Si-OH for adsorption and photodegradation of water-soluble organic pollutants
Download PDF

Info

Publication number
CN111977873A
CN111977873ACN202010899140.2ACN202010899140ACN111977873ACN 111977873 ACN111977873 ACN 111977873ACN 202010899140 ACN202010899140 ACN 202010899140ACN 111977873 ACN111977873 ACN 111977873A
Authority
CN
China
Prior art keywords
sepiolite
organic pollutants
adsorption
photoactive
adsorbing
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.)
Granted
Application number
CN202010899140.2A
Other languages
Chinese (zh)
Other versions
CN111977873B (en
Inventor
阳海
张雪婷
胡倩
易兵
刘华杰
张帆
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Hunan Institute of Engineering
Original Assignee
Hunan Institute of Engineering
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Hunan Institute of EngineeringfiledCriticalHunan Institute of Engineering
Priority to CN202010899140.2ApriorityCriticalpatent/CN111977873B/en
Publication of CN111977873ApublicationCriticalpatent/CN111977873A/en
Application grantedgrantedCritical
Publication of CN111977873BpublicationCriticalpatent/CN111977873B/en
Activelegal-statusCriticalCurrent
Anticipated expirationlegal-statusCritical

Links

Classifications

Landscapes

Abstract

Translated fromChinese

本发明公开了一种光活海泡石Si‑OH用于水溶性有机污染物吸附与光降解的方法。在常温下,向含有有机污染物的废水中加入海泡石,搅拌使得有机污染物分子在海泡石内腔和表面达到吸附脱附平衡后,采用离心或者过滤的方式固液分离,得到吸附有机物的海泡石并进行干燥,然后进行光源照射,海泡石在光源的作用下发生Si‑OH的断裂产生羟基自由基,羟基自由基和空气中氧气等进一步反应转化氧负离自由基等活性氧物种,进而对吸附在海泡石矿内腔和表面的有机污染物进行降解,起到矿化或者部分矿化有机污染物的作用。本发明加入水溶液中的海泡石稳定性好,易于回收,可重复循环使用。本发明成本低、常温下处理效率高、操作简单,有良好的工业应用价值。The invention discloses a method for the adsorption and photodegradation of water-soluble organic pollutants by photoactive sepiolite Si-OH. At room temperature, add sepiolite to the wastewater containing organic pollutants, stir to make the organic pollutant molecules reach the equilibrium of adsorption and desorption in the inner cavity and surface of the sepiolite, and then separate solid-liquid by centrifugation or filtration to obtain adsorption. The organic sepiolite is dried and then irradiated with a light source. Under the action of the light source, the sepiolite undergoes the cleavage of Si-OH to generate hydroxyl radicals, and the hydroxyl radicals and oxygen in the air are further reacted to convert oxygen anion radicals, etc. Reactive oxygen species, and then degrade the organic pollutants adsorbed on the cavity and surface of sepiolite mines, and play the role of mineralization or partial mineralization of organic pollutants. The sepiolite added into the aqueous solution has good stability, is easy to recover, and can be used repeatedly. The invention has low cost, high processing efficiency at normal temperature, simple operation and good industrial application value.

Description

Translated fromChinese
一种光活海泡石Si-OH用于水溶性有机污染物吸附与光降解 的方法A method for photoactive sepiolite Si-OH for adsorption and photodegradation of water-soluble organic pollutants

技术领域technical field

本发明涉及水溶性有机物的处理,特别涉及一种光活海泡石Si-OH用于水溶性有机污染物吸附与光降解的方法。The invention relates to the treatment of water-soluble organic matter, in particular to a method for the adsorption and photodegradation of water-soluble organic pollutants by photoactive sepiolite Si-OH.

背景技术Background technique

海泡石等粘土矿物资源的开发是国家经济发展的重大需求,也是湖南、江西和河北等地方省份经济和社会发展的重要支撑。近年来,基于比表面积和表面活性方面的突出优势,海泡石已经广泛地运用于土壤治理、空气净化和水体吸附等领域。土壤治理方面,海泡石对砷、镉和铅等重金属具有吸附和螯合作用,通过复配其他功能添加剂,使其相互作用形成的固化网,进一步将重金属封闭在晶格网中,从而实现砷、镉和铅等重金属的固化稳定化。空气净化方面,海泡石和改性后的海泡石不仅能高效滤除VOCs、SO2或H2S、NOx等有害气体,同时具备强大持久的抗菌功能,对PM2.5的一次过滤效率能够高达99%。水体吸附方面,海泡石由于具有极强的吸附性能和离子交换性能,主要运用于水体中重金属Cd和Pb的吸附和去除,然而随着水体中染料、抗生素、有机农药、微塑料等痕量有机污染物的出现,海泡石在有机物污染物的去除领域也出现了相关的科学研究。然而海泡石在土壤重金属污染治理、空气净化和污水处理等领域的应用往往局限于其较大的比表面积和较高的表面活性,而对其Si-OH基的光化学反应活性则尚未开发利用。特别是在有机污染物控制领域,吸附在海泡石表面的有机污染物不能有效地进行矿化降解则大大限制了其应用范围。海泡石Si-OH基在外在光源的作用下能发生Si-O键均裂而产生具有高氧化还原电位的•OH等活性氧物种,并进一步导致有机污染物矿化降解。The development of clay mineral resources such as sepiolite is a major demand for national economic development, and also an important support for the economic and social development of local provinces such as Hunan, Jiangxi and Hebei. In recent years, based on the outstanding advantages of specific surface area and surface activity, sepiolite has been widely used in soil treatment, air purification and water adsorption. In terms of soil treatment, sepiolite has adsorption and chelation effects on heavy metals such as arsenic, cadmium and lead. By compounding other functional additives, the solidified network formed by their interaction further seals the heavy metals in the lattice network, thereby realizing Solidification stabilization of heavy metals such as arsenic, cadmium and lead. In terms of air purification, sepiolite and modified sepiolite can not only efficiently filter harmful gases such as VOCs, SO2 or H2 S, NOx, but also have strong and lasting antibacterial functions, and the primary filtration efficiency of PM2. up to 99%. In terms of water adsorption, sepiolite is mainly used for the adsorption and removal of heavy metals Cd and Pb in water due to its strong adsorption performance and ion exchange performance. With the emergence of organic pollutants, sepiolite has also appeared in relevant scientific research in the field of removal of organic pollutants. However, the application of sepiolite in the fields of soil heavy metal pollution control, air purification and sewage treatment is often limited to its large specific surface area and high surface activity, while its photochemical reactivity of Si-OH group has not been exploited yet. . Especially in the field of organic pollutant control, the organic pollutants adsorbed on the surface of sepiolite cannot be effectively mineralized and degraded, which greatly limits its application range. Under the action of an external light source, the Si-OH group of sepiolite can homogenize the Si-O bond to generate reactive oxygen species such as • OH with high redox potential, and further lead to the mineralization and degradation of organic pollutants.

因此,如何有效地激活海泡石Si-OH基产生•OH等活性氧物种并运用于有机污染物控制领域是整合海泡石矿产资源和拓宽其应用范围的主要技术瓶颈点,也是促使基础研究成果走向应用必须解决的核心科学问题。Therefore, how to effectively activate the sepiolite Si-OH groups to generate OH and other reactive oxygen species and apply them in the field of organic pollutant control is the main technical bottleneck for integrating sepiolite mineral resources and broadening its application scope, and it is also the impetus for basic research. The core scientific problems that must be solved in order for the results to be applied.

发明内容SUMMARY OF THE INVENTION

本发明是针对现有技术的不足,提供一种光活海泡石Si-OH用于水溶性有机污染物吸附与光降解的方法,在100-800 nm光源作用下固/液界面吸附和固/气界面光催化下降解水溶液中有机污染物,即采用100-800 nm光源照射在海泡石内腔和表面达到吸附脱附平衡的海泡石,海泡石被光源激活发生Si-OH健断裂并形成羟基自由基等活性氧物种,从而达到氧化降解抗生素的目的。Aiming at the deficiencies of the prior art, the invention provides a method for the adsorption and photodegradation of water-soluble organic pollutants by photoactive sepiolite Si-OH. Degradation of organic pollutants in aqueous solution by photocatalysis at the /gas interface, that is, using a 100-800 nm light source to irradiate the sepiolite in the cavity and surface of the sepiolite to reach the equilibrium of adsorption and desorption, and the sepiolite is activated by the light source to generate Si-OH bonds. It breaks and forms reactive oxygen species such as hydroxyl radicals, so as to achieve the purpose of oxidative degradation of antibiotics.

为了达到上述目的,本发明采用了以下技术方案:In order to achieve the above object, the present invention adopts the following technical solutions:

一种光活海泡石Si-OH用于水溶性有机污染物吸附与光降解的方法,包括以下步骤:A method for photoactive sepiolite Si-OH for adsorption and photodegradation of water-soluble organic pollutants, comprising the following steps:

(1)在常温下,向含有有机污染物的水溶液中加入海泡石粉末,搅拌使得溶液中有机污染物在海泡石固/液界面,包括海泡石的内腔和表面达到吸附脱附平衡;(1) At room temperature, add sepiolite powder to the aqueous solution containing organic pollutants, and stir to make the organic pollutants in the solution adsorb and desorb at the sepiolite solid/liquid interface, including the inner cavity and surface of the sepiolite. balance;

(2)水溶液中有机污染物在海泡石固/液界面吸附脱附平衡后,采用过滤或者离心的方式固液分离,得吸附了有机污染物的海泡石粉末,并进行干燥;(2) After the organic pollutants in the aqueous solution are balanced by adsorption and desorption at the sepiolite solid/liquid interface, solid-liquid separation is performed by means of filtration or centrifugation to obtain sepiolite powder with organic pollutants adsorbed and dried;

(3)开启光强为5-50 mW cm-2,波长为100-800 nm的光源,照射吸附了有机污染物的海泡石粉末,海泡石以分子筛形式存在的Si-OH基在太阳光光源的作用下发生Si-OH健断裂产生羟基自由基等活性氧物种,从而对有机污染物氧化降解。(3) Turn on the light source with a light intensity of 5-50 mW cm-2 and a wavelength of 100-800 nm, and irradiate the sepiolite powder adsorbed with organic pollutants. Under the action of the light source, the Si-OH bond is broken to generate reactive oxygen species such as hydroxyl radicals, thereby oxidatively degrading organic pollutants.

进一步地,所述的光源优选模拟太阳光光源,光强为5-50 mW cm-2,更优选光强为50 mW cm-2;波长为100-800 nm,更优选为400 nm。Further, the light source is preferably a simulated sunlight light source, the light intensity is 5-50 mW cm-2 , more preferably 50 mW cm-2 ; the wavelength is 100-800 nm, more preferably 400 nm.

进一步地,步骤(1)中,所述的海泡石为海泡石原矿、α-海泡石粉体和β-海泡石粉体中的一种或两种以上,优选为α-海泡石粉体。Further, in step (1), the sepiolite is one or more of sepiolite ore, α-sepiolite powder and β-sepiolite powder, preferably α-sepiolite Fossil powder.

进一步地,步骤(1)中,海泡石在水溶液中的质量体积比为1~50 g/L。Further, in step (1), the mass-volume ratio of sepiolite in the aqueous solution is 1-50 g/L.

进一步地,有机污染物主要是指水溶性有机污染物,包括有机染料、农药、抗生素等有机物,所述的有机污染物的尺寸小于100×500×100 nm。Further, organic pollutants mainly refer to water-soluble organic pollutants, including organic dyes, pesticides, antibiotics and other organic substances, and the size of the organic pollutants is less than 100×500×100 nm.

进一步地,步骤(1)中,搅拌时间为30~120分钟。Further, in step (1), the stirring time is 30-120 minutes.

进一步地,步骤(2)中,干燥温度为40~60℃,干燥时间为2~3小时。Further, in step (2), the drying temperature is 40-60° C., and the drying time is 2-3 hours.

进一步地,步骤(3)中,照射时间为2-36小时。Further, in step (3), the irradiation time is 2-36 hours.

进一步地,还包括海泡石的回收,具体为:吸附了有机污染物的海泡石在固/气界面光催化反应后,100-200℃活化后再次作为吸附剂和催化剂重复利用。Further, it also includes the recovery of sepiolite, specifically: the sepiolite adsorbed with organic pollutants is reused as adsorbent and catalyst after photocatalytic reaction at the solid/gas interface and activation at 100-200°C.

本发明与现有技术相比具有以下优点和有益的效果:Compared with the prior art, the present invention has the following advantages and beneficial effects:

1) 与现有海泡石对有机物污染物的处理技术相比,本发明在海泡石完成吸附后利用光源活化海泡石Si-OH基,使其产生羟基自由基等活性氧物种,从而对水体环境中有机污染物的降解起到吸附和氧化降解的协同作用,大大提高了有机污染物的处理效率,拓宽了海泡石的应用范围。1) Compared with the existing technology for treating organic pollutants by sepiolite, the present invention utilizes a light source to activate the Si-OH group of sepiolite after the adsorption of sepiolite is completed, so as to generate active oxygen species such as hydroxyl radicals, thereby It has a synergistic effect of adsorption and oxidative degradation on the degradation of organic pollutants in the water environment, which greatly improves the treatment efficiency of organic pollutants and broadens the application range of sepiolite.

2) 本发明提供的海泡石主要针对水环境中有机污染物的去除,有机污染物包括有机染料、农药、抗生素等。海泡石对水溶性有机污染物适应性强,广谱性好,分子尺寸小于100×500×100 nm有机污染物,均具有较好的吸附和氧化降解的效果。2) The sepiolite provided by the present invention is mainly aimed at the removal of organic pollutants in the water environment, and the organic pollutants include organic dyes, pesticides, antibiotics and the like. Sepiolite has strong adaptability to water-soluble organic pollutants, good broad-spectrum, and molecular size is less than 100 × 500 × 100 nm of organic pollutants, all of which have good adsorption and oxidative degradation effects.

3) 本发明所采用的海泡石在水溶液中结构稳定,易于回收,经过活化处理后可以重复循环利用,且活性能在多次循环中基本保持不变。3) The sepiolite used in the present invention has a stable structure in an aqueous solution, is easy to recycle, and can be recycled repeatedly after being activated, and its active energy remains basically unchanged in multiple cycles.

4) 本发明工艺流程简单,便于操作,且非常绿色环保,不会产生二次污染,具备广阔的应用前景。4) The technological process of the present invention is simple, easy to operate, very green and environmentally friendly, does not produce secondary pollution, and has broad application prospects.

具体实施方式Detailed ways

下面结合具体实施例对本发明作进一步的描述,但本发明并不限于此。The present invention will be further described below in conjunction with specific embodiments, but the present invention is not limited thereto.

实施例1Example 1

一种光活海泡石Si-OH用于水溶性有机污染物吸附与光降解的方法,具体步骤如下:A method for photoactive sepiolite Si-OH for adsorption and photodegradation of water-soluble organic pollutants, the specific steps are as follows:

(1) 室温下配置100 μmol/L的酸性红37溶液,取100 ml溶液于250 ml反应器内,加入2g α-海泡石粉末,搅拌1 h,使得酸性红37在海泡石固/液界面达到吸附脱附平衡;(1) Prepare 100 μmol/L acid red 37 solution at room temperature, take 100 ml of the solution in a 250 ml reactor, add 2 g of α-sepiolite powder, and stir for 1 h to make acid red 37 solid in sepiolite/ The liquid interface reaches the equilibrium of adsorption and desorption;

(2) 采用过滤的方式固液分离,得到吸附了酸性红37的海泡石粉末,在50℃条件下干燥3小时;(2) solid-liquid separation by filtration to obtain sepiolite powder adsorbed with acid red 37, and dried at 50°C for 3 hours;

(3) 开启氙灯模拟太阳光光源,照射干燥后的海泡石粉末,使有机污染物在海泡石固/气界面其发生氧化降解反应6小时;(3) Turn on the xenon lamp to simulate the sunlight light source, irradiate the dried sepiolite powder, and make the organic pollutants undergo oxidative degradation reaction at the sepiolite solid/gas interface for 6 hours;

(4) 反应结束,收集海泡石粉末,150℃活化后循环利用。(4) At the end of the reaction, the sepiolite powder was collected, activated at 150°C and recycled.

实施例2至4Examples 2 to 4

将酸性红37分别替换为酸性黄17、媒染橙1或茜素黄GG。Acid Red 37 was replaced by Acid Yellow 17, Mordant Orange 1 or Alizarin Yellow GG, respectively.

对步骤(1)中有机污染物吸附脱附平衡后水溶液进行有机污染物含量的测试得海泡石对有机污染物的吸附率,吸附率 = ( C0-C1) /C0×100%,其中C0有机污染物溶液初始浓度,C1是吸附平衡后溶液中有机污染物的浓度。对步骤(3)中光催化反应后的海泡石样品进行有机污染物的含量测试得最终的有机污染物的降解率,降解率 = ( C0-C1-C2) /( C0-C1)×100%,其中C2是光催化反应以后残留在海泡石界面有机污染物的折合浓度,实验结果如表1所示。表1结果表明酸性红37、酸性黄17、媒染橙1和茜素黄GG等有机染料在海泡石表面体现了均有较好的吸附效果,吸附率在85%-91%之间,而吸附了有机污染物的海泡石粉末在以氙灯模拟太阳光源的照射下,反应4-8小时,有机染料的降解率均可以达到80%以上。The adsorption rate of sepiolite to organic pollutants is obtained by testing the content of organic pollutants in the aqueous solution after the equilibrium of adsorption and desorption of organic pollutants in step (1). Adsorption rate = ( C0 -C1 ) /C0 ×100% , where C0 is the initial concentration of organic pollutants in the solution, and C1 is the concentration of organic pollutants in the solution after adsorption equilibrium. The content of organic pollutants is tested on the sepiolite sample after the photocatalytic reaction in step (3) to obtain the final degradation rate of organic pollutants, degradation rate=( C0 -C1 -C2 ) /( C0 - C1 )×100%, where C2 is the equivalent concentration of organic pollutants remaining at the sepiolite interface after the photocatalytic reaction. The experimental results are shown in Table 1. The results in Table 1 show that organic dyes such as acid red 37, acid yellow 17, mordant orange 1 and alizarin yellow GG have good adsorption effect on the surface of sepiolite, and the adsorption rate is between 85% and 91%. When the sepiolite powder adsorbed with organic pollutants is irradiated with a xenon lamp to simulate a solar light source, and reacts for 4-8 hours, the degradation rate of organic dyes can reach more than 80%.

表1有机染料在光活化海泡石Si-OH反应体系下的吸附率和降解率实施例有机染料吸附率降解率实施例1酸性红3785%85%实施例2酸性黄1788%85%实施例3媒染橙190%82%实施例4茜素黄GG91%81%Table 1 Adsorption rate and degradation rate of organic dyes under photoactivated sepiolite Si-OH reaction system Example organic dye Adsorption rate Degradation rate Example 1 Acid Red 37 85% 85% Example 2 Acid Yellow 17 88% 85% Example 3 Mordant Orange 1 90% 82% Example 4 Alizarin Yellow GG 91% 81%

对比现有海泡石对有机染料的处理技术,仅仅停留在对有机染料的吸附去除方面,而本发明则在原有吸附技术的基础上,进一步发明了海泡石Si-OH的活化方法,吸附了有机污染物的海泡石在光源的照射下发生氧化反应,有机污染物获得了较好的去除效果。Compared with the existing sepiolite treatment technology for organic dyes, it only stays in the adsorption and removal of organic dyes, while the present invention further invents the activation method of sepiolite Si-OH on the basis of the original adsorption technology. The sepiolite with organic pollutants undergoes an oxidation reaction under the irradiation of the light source, and the organic pollutants have a good removal effect.

实施例5Example 5

一种光活海泡石Si-OH用于水溶性有机污染物吸附与光降解的方法,具体步骤如下:A method for photoactive sepiolite Si-OH for adsorption and photodegradation of water-soluble organic pollutants, the specific steps are as follows:

(1) 室温下配置100 μmol/L的噻虫嗪溶液,取100 ml溶液于250 ml反应器内,加入2 gα-海泡石粉末,搅拌1 h,使得噻虫嗪在海泡石固/液界面达到吸附脱附平衡;(1) Prepare 100 μmol/L thiamethoxam solution at room temperature, take 100 ml of the solution in a 250 ml reactor, add 2 g α-sepiolite powder, and stir for 1 h, so that thiamethoxam is solid in sepiolite/ The liquid interface reaches the equilibrium of adsorption and desorption;

(2) 采用过滤的方式固液分离,得到吸附了噻虫嗪的海泡石粉末,在60℃条件下干燥2小时;(2) Solid-liquid separation by filtration to obtain sepiolite powder adsorbed with thiamethoxam, and drying at 60°C for 2 hours;

(3) 开启氙灯模拟太阳光光源,照射干燥后的海泡石粉末,使有机污染物在海泡石固/气界面其发生氧化降解反应6小时;(3) Turn on the xenon lamp to simulate the sunlight light source, irradiate the dried sepiolite powder, and make the organic pollutants undergo oxidative degradation reaction at the sepiolite solid/gas interface for 6 hours;

(4) 反应结束,收集海泡石粉末,100-200 ℃活化后循环利用。(4) After the reaction, the sepiolite powder is collected, activated at 100-200 °C and recycled.

实施例6至8Examples 6 to 8

将噻虫嗪分别替换为噻虫胺、克百威或敌草隆。Substitute thiamethoxam with clothianidin, carbofuran, or diuron, respectively.

对步骤(1)中有机污染物吸附脱附平衡后水溶液进行有机污染物含量的测试得海泡石对有机污染物的吸附率,吸附率 = ( C0-C1) /C0×100%,其中C0有机污染物溶液初始浓度,C1是吸附平衡后溶液中有机污染物的浓度。对步骤(3)中光催化反应后的海泡石样品进行有机污染物的含量测试得最终的有机污染物的降解率,降解率 = ( C0-C1-C2) /( C0-C1)×100%,其中C2是光催化反应以后残留在海泡石界面的有机污染物折合浓度,实验结果如表2所示。表2结果表明噻虫嗪、噻虫胺、克百威和敌草隆等有机农药在海泡石表面体现了均有较好的吸附效果,吸附率在85%以上,而吸附了有机污染物的海泡石粉末在以氙灯模拟太阳光源的照射下,反应4-8小时,有机农药的降解率均可以达到80%左右。The adsorption rate of sepiolite to organic pollutants is obtained by testing the content of organic pollutants in the aqueous solution after the equilibrium of adsorption and desorption of organic pollutants in step (1). Adsorption rate = ( C0 -C1 ) /C0 ×100% , where C0 is the initial concentration of organic pollutants in the solution, and C1 is the concentration of organic pollutants in the solution after adsorption equilibrium. The content of organic pollutants is tested on the sepiolite sample after the photocatalytic reaction in step (3) to obtain the final degradation rate of organic pollutants, degradation rate=( C0 -C1 -C2 ) /( C0 - C1 )×100%, where C2 is the equivalent concentration of organic pollutants remaining on the sepiolite interface after the photocatalytic reaction. The experimental results are shown in Table 2. The results in Table 2 show that organic pesticides such as thiamethoxam, clothianidin, carbofuran and diuron have good adsorption effects on the surface of sepiolite, and the adsorption rate is above 85%, while the organic pollutants are adsorbed. The sepiolite powder is irradiated with a xenon lamp to simulate the sun light source, and the degradation rate of organic pesticides can reach about 80% for 4-8 hours.

表2有机农药在光活化海泡石Si-OH反应体系下的吸附率和降解率实施例有机农药吸附率降解率实施例5噻虫嗪85%78%实施例6噻虫胺86%80%实施例7克百威85%82%实施例8敌草隆86%81%Table 2 Adsorption rate and degradation rate of organic pesticides under photoactivated sepiolite Si-OH reaction system Example Organic Pesticides Adsorption rate Degradation rate Example 5 Thiamethoxam 85% 78% Example 6 clothianidin 86% 80% Example 7 Budweiser 85% 82% Example 8 Diuron 86% 81%

对比现有海泡石对有机农药的处理技术,仅仅停留在对有机农药的吸附去除方面,而本发明则在原有吸附技术的基础上,进一步发明了海泡石Si-OH的活化方法,吸附了有机污染物的海泡石在光源的照射下,发生氧化反应,有机污染物获得了较好的去除效果。Compared with the existing sepiolite treatment technology for organic pesticides, it only stays in the adsorption and removal of organic pesticides, while the present invention further invents the activation method of sepiolite Si-OH on the basis of the original adsorption technology. Under the irradiation of the light source, the sepiolite with organic pollutants undergoes an oxidation reaction, and the organic pollutants obtain a good removal effect.

实施例9Example 9

一种光活海泡石Si-OH用于水溶性有机污染物吸附与光降解的方法,具体步骤如下:A method for photoactive sepiolite Si-OH for adsorption and photodegradation of water-soluble organic pollutants, the specific steps are as follows:

(1) 室温下配置100 μmol/L的阿替洛尔溶液,取100 ml溶液于250 ml反应器内,加入2g α-海泡石粉末,搅拌1 h,使得阿替洛尔在海泡石固/液界面达到吸附脱附平衡;(1) Prepare a 100 μmol/L atenolol solution at room temperature, take 100 ml of the solution in a 250 ml reactor, add 2 g of α-sepiolite powder, and stir for 1 h to make atenolol in the sepiolite The solid/liquid interface reaches the equilibrium of adsorption and desorption;

(2) 采用过滤的方式固液分离,得到吸附了阿替洛尔的海泡石粉末,在40-60 ℃条件下干燥1-2小时;(2) Solid-liquid separation by filtration to obtain atenolol-adsorbed sepiolite powder, which is dried at 40-60 °C for 1-2 hours;

(3) 开启氙灯模拟太阳光光源,照射干燥后的海泡石粉末,使有机污染物在海泡石固/气界面其发生氧化降解反应4-8小时;(3) Turn on the xenon lamp to simulate the sunlight light source, irradiate the dried sepiolite powder, and cause the organic pollutants to undergo oxidative degradation reaction at the sepiolite solid/gas interface for 4-8 hours;

(4) 反应结束,收集海泡石粉末,100-200 ℃活化后循环利用。(4) After the reaction, the sepiolite powder is collected, activated at 100-200 °C and recycled.

实施例10至12Examples 10 to 12

将阿替洛尔分别替换为磺胺氯哒嗪、环丙沙星或拉夫米定。Replace atenolol with sulfachloropyridazine, ciprofloxacin, or lavimidine, respectively.

对步骤(1)中有机污染物吸附脱附平衡后水溶液进行有机污染物含量的测试得海泡石对有机污染物的吸附率,吸附率 = ( C0-C1) /C0×100%,其中C0有机污染物溶液初始浓度,C1是吸附平衡后溶液中有机污染物的浓度。对步骤(3)中光催化反应后的海泡石样品进行有机污染物的含量测试得最终的有机污染物的降解率,降解率 = ( C0-C1-C2) /( C0-C1)×100%,其中C2是光催化反应以后残留在海泡石界面的有机污染物折合浓度,实验结果如表3所示。表3结果表明阿替洛尔、磺胺氯哒嗪、环丙沙星和拉夫米定等有机农药在海泡石表面体现了均有较好的吸附效果,吸附率在85%以上,而吸附了有机污染物的海泡石粉末在以氙灯模拟太阳光源的照射下,反应4-8小时,抗生素的降解率均可以达到80%左右。The adsorption rate of sepiolite to organic pollutants is obtained by testing the content of organic pollutants in the aqueous solution after the equilibrium of adsorption and desorption of organic pollutants in step (1). Adsorption rate = ( C0 -C1 ) /C0 ×100% , where C0 is the initial concentration of organic pollutants in the solution, and C1 is the concentration of organic pollutants in the solution after adsorption equilibrium. The content of organic pollutants is tested on the sepiolite sample after the photocatalytic reaction in step (3) to obtain the final degradation rate of organic pollutants, degradation rate=( C0 -C1 -C2 ) /( C0 - C1 )×100%, where C2 is the equivalent concentration of organic pollutants remaining on the sepiolite interface after the photocatalytic reaction. The experimental results are shown in Table 3. The results in Table 3 show that organic pesticides such as atenolol, sulfachloropyridazine, ciprofloxacin and lavimidine have good adsorption effects on the surface of sepiolite, and the adsorption rate is above 85%, while the adsorption The sepiolite powder with organic pollutants is irradiated with a xenon lamp to simulate the sun light source and reacts for 4-8 hours, and the degradation rate of antibiotics can reach about 80%.

表3抗生素在光活化海泡石Si-OH反应体系下的吸附率和降解率实施例有机农药吸附率降解率实施例9阿替洛尔85%78%实施例10磺胺氯哒嗪86%80%实施例11环丙沙星85%82%实施例12拉夫米定86%81%Table 3 Adsorption rate and degradation rate of antibiotics under photoactivated sepiolite Si-OH reaction system Example Organic Pesticides Adsorption rate Degradation rate Example 9 atenolol 85% 78% Example 10 Sulfachloropyridazine 86% 80% Example 11 Ciprofloxacin 85% 82% Example 12 Lavmidine 86% 81%

对比现有海泡石对抗生素的处理技术,仅仅停留在对抗生素的吸附去除方面,而本发明则在原有吸附技术的基础上,进一步发明了海泡石Si-OH的活化方法,吸附了有机污染物的海泡石在光源的照射下,发生氧化反应,有机污染物获得了较好的去除效果。Compared with the existing treatment technology of sepiolite for antibiotics, it only stays in the adsorption and removal of antibiotics, and the present invention further invents the activation method of sepiolite Si-OH on the basis of the original adsorption technology, which adsorbs organic Under the irradiation of the light source, the pollutant sepiolite undergoes an oxidation reaction, and the organic pollutants obtain a better removal effect.

实施例13Example 13

一种光活海泡石Si-OH用于水溶性有机污染物吸附与光降解的方法,具体步骤如下:A method for photoactive sepiolite Si-OH for adsorption and photodegradation of water-soluble organic pollutants, the specific steps are as follows:

(1) 室温下配置100 μmol/L的阿替洛尔溶液,取100 ml溶液于250 ml反应器内,加入2g α-海泡石粉末,搅拌1 h,使得阿替洛尔在海泡石固/液界面达到吸附脱附平衡;(1) Prepare a 100 μmol/L atenolol solution at room temperature, take 100 ml of the solution in a 250 ml reactor, add 2 g of α-sepiolite powder, and stir for 1 h to make atenolol in the sepiolite The solid/liquid interface reaches the equilibrium of adsorption and desorption;

(2) 采用过滤的方式固液分离,得到吸附了阿替洛尔的海泡石粉末,在40-60 ℃条件下干燥1-2小时;(2) Solid-liquid separation by filtration to obtain atenolol-adsorbed sepiolite powder, which is dried at 40-60 °C for 1-2 hours;

(3) 开启氙灯模拟太阳光光源,照射干燥后的海泡石粉末,使有机污染物在海泡石固/气界面其发生氧化降解反应4-8小时;(3) Turn on the xenon lamp to simulate the sunlight light source, irradiate the dried sepiolite powder, and cause the organic pollutants to undergo oxidative degradation reaction at the sepiolite solid/gas interface for 4-8 hours;

(4) 反应结束,收集海泡石粉末,100-200 ℃活化后用于下一批反应。表4是海泡石对100 μmol/L阿替洛尔4次循环后吸附率和降解率的变化情况,海泡石对阿替洛尔的吸附率和降解率均保持不变。(4) At the end of the reaction, collect the sepiolite powder and activate it at 100-200 °C for the next batch of reactions. Table 4 shows the changes of the adsorption rate and degradation rate of sepiolite to 100 μmol/L atenolol after 4 cycles. The adsorption rate and degradation rate of sepiolite to atenolol remained unchanged.

表4海泡石循环使用对阿替洛尔吸附率和降解率的影响循环次数吸附率降解率185%78%285%75%381%72%480%72%Table 4 The effect of sepiolite recycling on the adsorption rate and degradation rate of atenolol Cycles Adsorption rate Degradation rate 1 85% 78% 2 85% 75% 3 81% 72% 4 80% 72%

以上实施例表明,利用海泡石对有机污染物的吸附并激活海泡石Si-OH产生羟基自由基对有机污染物进行降解,两者协同发挥作用,从而达到氧化降解水溶液中有机污染物的目的,针对大部分有机污染物吸附率在85%以上,而降解率则80%左右。此外,海泡石易于回收,循环使用效果好。The above examples show that the adsorption of organic pollutants by sepiolite and the activation of sepiolite Si-OH to generate hydroxyl radicals to degrade organic pollutants, the two work synergistically, so as to achieve the oxidative degradation of organic pollutants in the aqueous solution. For most organic pollutants, the adsorption rate is above 85%, while the degradation rate is about 80%. In addition, sepiolite is easy to recycle and has good recycling effect.

Claims (9)

CN202010899140.2A2020-08-312020-08-31Method for using photoactivated sepiolite Si-OH for adsorption and photodegradation of water-soluble organic pollutantsActiveCN111977873B (en)

Priority Applications (1)

Application NumberPriority DateFiling DateTitle
CN202010899140.2ACN111977873B (en)2020-08-312020-08-31Method for using photoactivated sepiolite Si-OH for adsorption and photodegradation of water-soluble organic pollutants

Applications Claiming Priority (1)

Application NumberPriority DateFiling DateTitle
CN202010899140.2ACN111977873B (en)2020-08-312020-08-31Method for using photoactivated sepiolite Si-OH for adsorption and photodegradation of water-soluble organic pollutants

Publications (2)

Publication NumberPublication Date
CN111977873Atrue CN111977873A (en)2020-11-24
CN111977873B CN111977873B (en)2023-04-07

Family

ID=73446836

Family Applications (1)

Application NumberTitlePriority DateFiling Date
CN202010899140.2AActiveCN111977873B (en)2020-08-312020-08-31Method for using photoactivated sepiolite Si-OH for adsorption and photodegradation of water-soluble organic pollutants

Country Status (1)

CountryLink
CN (1)CN111977873B (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication numberPriority datePublication dateAssigneeTitle
CN113683247A (en)*2021-08-312021-11-23湖南工程学院 A method for synergistic activation of sepiolite by light and heat for the treatment of reverse osmosis concentrated water of grinding wastewater
CN114573086A (en)*2022-02-252022-06-03湖南工程学院Method for catalytically degrading low-concentration antibiotics in water body by SEP @ CTFs composite material under visible light

Citations (4)

* Cited by examiner, † Cited by third party
Publication numberPriority datePublication dateAssigneeTitle
JP2005161205A (en)*2003-12-022005-06-23Asahi Kasei Chemicals Corp Photocatalyst composition
JP2011068726A (en)*2009-09-242011-04-07Daihatsu Motor Co LtdCoating composition
CN102614827A (en)*2012-04-202012-08-01哈尔滨工业大学Preparation method of modified sepiolite supported nano iron material
CN103318984A (en)*2013-07-012013-09-25中国地质大学(武汉) A method for organically modified sepiolite to treat polymer flooding oil production wastewater

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication numberPriority datePublication dateAssigneeTitle
JP2005161205A (en)*2003-12-022005-06-23Asahi Kasei Chemicals Corp Photocatalyst composition
JP2011068726A (en)*2009-09-242011-04-07Daihatsu Motor Co LtdCoating composition
CN102614827A (en)*2012-04-202012-08-01哈尔滨工业大学Preparation method of modified sepiolite supported nano iron material
CN103318984A (en)*2013-07-012013-09-25中国地质大学(武汉) A method for organically modified sepiolite to treat polymer flooding oil production wastewater

Non-Patent Citations (5)

* Cited by examiner, † Cited by third party
Title
RUIJUAN QU等: "Hydroxyl Radical Based Photocatalytic Degradation of Halogenated Organic Contaminants and Paraffinon Silica Gel", 《ENVIROMENTAL SCIENCE&TECHNOLOGY》*
朱洪法: "《催化剂手册》", 31 August 2008, 金盾出版社*
李红霞等: "天然海泡石对染料酸性蓝62的吸附研究", 《安徽化工》*
董颖博等: "《环境矿物材料》", 31 March 2020, 冶金工业出版社*
雷乐成等: "《水处理高级氧化技术》", 31 August 2001, 化学工业出版社*

Cited By (3)

* Cited by examiner, † Cited by third party
Publication numberPriority datePublication dateAssigneeTitle
CN113683247A (en)*2021-08-312021-11-23湖南工程学院 A method for synergistic activation of sepiolite by light and heat for the treatment of reverse osmosis concentrated water of grinding wastewater
CN114573086A (en)*2022-02-252022-06-03湖南工程学院Method for catalytically degrading low-concentration antibiotics in water body by SEP @ CTFs composite material under visible light
CN114573086B (en)*2022-02-252022-11-29湖南工程学院Method for catalytically degrading low-concentration antibiotics in water body by SEP @ CTFs composite material under visible light

Also Published As

Publication numberPublication date
CN111977873B (en)2023-04-07

Similar Documents

PublicationPublication DateTitle
CN204880408U (en)Air purifier
CN205288013U (en)Volatile organic compounds adsorbs integrated device of concentration and plasma decomposition in air
CN105521705A (en)Method for treating organic waste gas through low-temperature plasma concerted catalysis
CN202983486U (en)Integration purification device for processing complex industrial organic waste gas
CN106642487A (en)Fresh air and indoor air purification integrated device and purification method
CN104226240B (en)Preparation method with catalysis/adsorbing material that kieselguhr is carrier
CN107935102A (en)A kind of method that water removal moderate resistance life element is removed using persulfuric acid hydrogen salt and magnetic bismuth oxyiodide visible light catalytic
CN113648825B (en)Technical method for purifying VOCs and peculiar smell tail gas of high-humidity chemical medicine
CN106064101A (en)A kind of iron-based MOFs catalysis material and preparation and application thereof
CN104307473B (en)A kind of preparation method of the absorption visible light catalytic material for air pollution treatment
CN110252316B (en) Ferrihydrite heterogeneous Fenton-like catalyst supported by hollow ceria microspheres and its preparation method and application
CN111977873B (en)Method for using photoactivated sepiolite Si-OH for adsorption and photodegradation of water-soluble organic pollutants
CN107434852A (en)A kind of method of amino benzenes compounds in the super crosslinked resin and its adsorption recovery industrial wastewater of cyclo-dextrin-modified
CN113244962A (en)Preparation method and application of singlet oxygen generating zirconium porphyrin-based MOF-graphene composite photocatalyst
CN114570340B (en) Application of a graphene oxide/metal organic framework composite material in light-controlled desorption of volatile organic compounds
CN115608322B (en) Preparation and application method of a type of regenerable adsorbent for collaborative removal of heavy metals and new organic pollutants in water
CN104667869B (en)A kind of single persulfate and load ferro-cobalt two-phase combined oxidation Graphene is utilized to remove the method for incretion interferent in water
EP2558194A2 (en)Use of granulated natural minerals as gas adsorbents for removing gaseous pollutant components
CN116272904A (en)MOFs composite VOCs adsorbent and preparation method thereof
CN102872796A (en)Preparation method of medical stone purifying agent for adsorbing and decomposing formaldehyde
CN110201661A (en)A kind of manganese base charcoal of porous array structure and its preparation method and application
CN104628211B (en)A kind of method of utilizing the collaborative magnetic oxygenated reduced graphene catalyzing activation persulfate of metallic cerium to remove incretion interferent in water
CN104689701B (en)A kind of purification method of acetone waste gas
Yu et al.Regeneration of Rhodamine B Loaded Modified Biosorbent by a Self‐Cleaning Eluent: TiO2 Hydrosol
CN107754807A (en)A kind of method that estrogen in water removal is removed using sodium peroxydisulfate and magnetic photocatalyst

Legal Events

DateCodeTitleDescription
PB01Publication
PB01Publication
SE01Entry into force of request for substantive examination
SE01Entry into force of request for substantive examination
GR01Patent grant
GR01Patent grant

[8]ページ先頭

©2009-2025 Movatter.jp