CN106984258A - A kind of preparation and application of hypochlorite intercalation layered composite metal hydroxides - Google Patents
A kind of preparation and application of hypochlorite intercalation layered composite metal hydroxides Download PDFInfo
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- WQYVRQLZKVEZGA-UHFFFAOYSA-N hypochlorite Chemical compound Cl[O-] WQYVRQLZKVEZGA-UHFFFAOYSA-N 0.000 title claims abstract description 78
- 239000002131 composite material Substances 0.000 title claims abstract description 52
- 229910000000 metal hydroxide Inorganic materials 0.000 title claims abstract description 45
- 150000004692 metal hydroxides Chemical class 0.000 title claims abstract description 45
- 238000009830 intercalation Methods 0.000 title claims abstract description 19
- 230000002687 intercalation Effects 0.000 title claims abstract description 19
- 238000002360 preparation method Methods 0.000 title claims abstract description 18
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 63
- 229910052785 arsenic Inorganic materials 0.000 claims abstract description 39
- RQNWIZPPADIBDY-UHFFFAOYSA-N arsenic atom Chemical compound [As] RQNWIZPPADIBDY-UHFFFAOYSA-N 0.000 claims abstract description 39
- 239000008367 deionised water Substances 0.000 claims abstract description 25
- 229910021641 deionized water Inorganic materials 0.000 claims abstract description 25
- 238000006243 chemical reaction Methods 0.000 claims abstract description 22
- 239000007788 liquid Substances 0.000 claims abstract description 11
- 238000000926 separation method Methods 0.000 claims abstract description 11
- 238000003756 stirring Methods 0.000 claims abstract description 10
- 239000000463 material Substances 0.000 claims abstract description 9
- 238000001035 drying Methods 0.000 claims abstract description 6
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims abstract 4
- 229910000029 sodium carbonate Inorganic materials 0.000 claims abstract 3
- 230000002195 synergetic effect Effects 0.000 claims abstract 2
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 42
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 14
- SUKJFIGYRHOWBL-UHFFFAOYSA-N sodium hypochlorite Chemical compound [Na+].Cl[O-] SUKJFIGYRHOWBL-UHFFFAOYSA-N 0.000 claims description 14
- 239000011777 magnesium Substances 0.000 claims description 13
- 239000007787 solid Substances 0.000 claims description 13
- 150000003839 salts Chemical class 0.000 claims description 12
- 238000000034 method Methods 0.000 claims description 9
- 239000002002 slurry Substances 0.000 claims description 8
- 230000032683 aging Effects 0.000 claims description 6
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 4
- 238000001354 calcination Methods 0.000 claims description 4
- 239000003814 drug Substances 0.000 claims description 3
- 230000003647 oxidation Effects 0.000 claims description 3
- 238000007254 oxidation reaction Methods 0.000 claims description 3
- 229910002651 NO3 Inorganic materials 0.000 claims 3
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 claims 3
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 claims 1
- 238000010521 absorption reaction Methods 0.000 claims 1
- 239000000356 contaminant Substances 0.000 claims 1
- 230000029087 digestion Effects 0.000 claims 1
- 229910052742 iron Inorganic materials 0.000 claims 1
- 229910052749 magnesium Inorganic materials 0.000 claims 1
- 239000013049 sediment Substances 0.000 claims 1
- 239000002957 persistent organic pollutant Substances 0.000 abstract description 24
- 239000002244 precipitate Substances 0.000 abstract description 14
- 241000894006 Bacteria Species 0.000 abstract description 11
- 238000001179 sorption measurement Methods 0.000 abstract description 8
- 239000003344 environmental pollutant Substances 0.000 abstract description 4
- 231100000719 pollutant Toxicity 0.000 abstract description 4
- 239000000203 mixture Substances 0.000 abstract description 2
- 239000000417 fungicide Substances 0.000 abstract 1
- 239000007800 oxidant agent Substances 0.000 abstract 1
- 230000001590 oxidative effect Effects 0.000 abstract 1
- 239000005708 Sodium hypochlorite Substances 0.000 description 12
- 239000000047 product Substances 0.000 description 10
- 239000011734 sodium Substances 0.000 description 8
- 150000001450 anions Chemical class 0.000 description 6
- 230000007935 neutral effect Effects 0.000 description 6
- 239000006228 supernatant Substances 0.000 description 6
- 239000002384 drinking water standard Substances 0.000 description 5
- 239000003651 drinking water Substances 0.000 description 4
- 235000020188 drinking water Nutrition 0.000 description 4
- 229910052787 antimony Inorganic materials 0.000 description 3
- WATWJIUSRGPENY-UHFFFAOYSA-N antimony atom Chemical compound [Sb] WATWJIUSRGPENY-UHFFFAOYSA-N 0.000 description 3
- 150000001768 cations Chemical class 0.000 description 3
- 230000007613 environmental effect Effects 0.000 description 3
- 239000011229 interlayer Substances 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 150000001875 compounds Chemical class 0.000 description 2
- 229940079593 drug Drugs 0.000 description 2
- 239000000598 endocrine disruptor Substances 0.000 description 2
- 231100000049 endocrine disruptor Toxicity 0.000 description 2
- 239000003673 groundwater Substances 0.000 description 2
- 231100001240 inorganic pollutant Toxicity 0.000 description 2
- 238000005342 ion exchange Methods 0.000 description 2
- 239000010410 layer Substances 0.000 description 2
- YIXJRHPUWRPCBB-UHFFFAOYSA-N magnesium nitrate Chemical group [Mg+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O YIXJRHPUWRPCBB-UHFFFAOYSA-N 0.000 description 2
- 239000002243 precursor Substances 0.000 description 2
- 238000005406 washing Methods 0.000 description 2
- 229910002492 Ce(NO3)3·6H2O Inorganic materials 0.000 description 1
- 229910019440 Mg(OH) Inorganic materials 0.000 description 1
- 150000001495 arsenic compounds Chemical class 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 229910052599 brucite Inorganic materials 0.000 description 1
- 230000000711 cancerogenic effect Effects 0.000 description 1
- 125000005587 carbonate group Chemical group 0.000 description 1
- 231100000315 carcinogenic Toxicity 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 238000000975 co-precipitation Methods 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- MVFCKEFYUDZOCX-UHFFFAOYSA-N iron(2+);dinitrate Chemical group [Fe+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O MVFCKEFYUDZOCX-UHFFFAOYSA-N 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 229910044991 metal oxide Inorganic materials 0.000 description 1
- 150000004706 metal oxides Chemical class 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 230000000474 nursing effect Effects 0.000 description 1
- 238000011017 operating method Methods 0.000 description 1
- 230000035945 sensitivity Effects 0.000 description 1
- 239000002352 surface water Substances 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
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- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/04—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium
- B01J20/046—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium containing halogens, e.g. halides
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- A01N59/00—Biocides, pest repellants or attractants, or plant growth regulators containing elements or inorganic compounds
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- C02F1/00—Treatment of water, waste water, or sewage
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Abstract
本发明涉及一种用于去除水中污染物的次氯酸根插层层状复合金属氢氧化物及其制备与应用,通过将含有Mg2+、Fe3+、Ce3+的溶液与氢氧化钠和碳酸钠溶液混合在去离子水中,搅拌反应,陈化、固液分离、干燥煅烧后在次氯酸盐溶液中进行插层反应,得到的沉淀物干燥后即为次氯酸根插层层状复合金属氢氧化物,该材料可用于用于对水中砷的吸附去除,在吸附砷的同时可释放出次氯酸根,进而氧化水中的有机污染物、杀灭细菌。与现有技术相比,本发明合成了新颖的次氯酸根插层层状复合金属氢氧化物,该材料在有效吸附水中砷同时,可释放出次氯酸根,实现对水中有机污染物、细菌的协同去除,具有利用效率高、不需额外投加氧化剂、杀菌剂等优点。The invention relates to a hypochlorite intercalated layered composite metal hydroxide for removing pollutants in water and its preparation and application. Mix with sodium carbonate solution in deionized water, stir for reaction, age, solid-liquid separation, dry and calcined, then perform intercalation reaction in hypochlorite solution, and the obtained precipitate is hypochlorite intercalation layered after drying Composite metal hydroxide, this material can be used for the adsorption and removal of arsenic in water, and hypochlorite can be released while adsorbing arsenic, thereby oxidizing organic pollutants in water and killing bacteria. Compared with the prior art, the present invention synthesizes a novel hypochlorite-intercalated layered composite metal hydroxide, which can release hypochlorite while effectively adsorbing arsenic in water, so as to realize the treatment of organic pollutants and bacteria in water. The synergistic removal has the advantages of high utilization efficiency, no need to add additional oxidants, fungicides, etc.
Description
技术领域technical field
本发明涉及水处理领域,具体涉及一种次氯酸根插层层状复合金属氢氧化物的制备与应用。The invention relates to the field of water treatment, in particular to the preparation and application of a hypochlorite intercalated layered composite metal hydroxide.
背景技术Background technique
砷是自然界中普遍存在的一种具有毒性和致癌性的元素,饮用水源中的砷污染问题是受到全球关注的环境问题,目前世界上有十几个国家存在大区域的砷污染问题,我国也是砷污染较为严重的国家之一。我国部分地区地下水及河流中的砷污染非常严重,目前,对水中砷的去除方法包括混凝、共沉淀、膜分离、吸附等。吸附法以其经济高效、操作方便等优点在饮用水工程中得到广泛应用。同时,许多国家和地区的地表和地下水环境都受到了有机污染物质的污染,浓度范围为ng·L-1~μg·L-1,并且随着地理位置和季节而变化,如水中药物和个人护理品、内分泌干扰物等有机污染物已成为全球范围内人们普遍面临的环境问题。更为严重的是,我国的许多地区的作为饮用水源的河流和湖泊中已经检测到了砷及各类有机污染物形成的复合污染,在这类水污染治理过程中,必然会涉及砷、有机污染物的同步去除问题。Arsenic is a toxic and carcinogenic element ubiquitous in nature. Arsenic pollution in drinking water sources is an environmental problem that has attracted global attention. At present, there are arsenic pollution problems in large areas in more than a dozen countries in the world. my country It is also one of the countries with serious arsenic pollution. The arsenic pollution in groundwater and rivers in some areas of my country is very serious. At present, the removal methods of arsenic in water include coagulation, coprecipitation, membrane separation, adsorption and so on. The adsorption method has been widely used in drinking water engineering due to its advantages of cost-effectiveness, high efficiency and convenient operation. At the same time, the surface and groundwater environments in many countries and regions are polluted by organic pollutants, the concentration ranges from ng·L -1 to μg·L -1 , and changes with geographical location and seasons, such as water drugs and personal Nursing products, endocrine disruptors and other organic pollutants have become a common environmental problem faced by people all over the world. What's more serious is that the combined pollution of arsenic and various organic pollutants has been detected in rivers and lakes used as drinking water sources in many areas of our country. Simultaneous removal of pollutants.
层状复合金属氢氧化物(LDHs)是由带正电荷的主体层板和层间阴离子通过非共价键的相互作用组装而成的化合物。其结构类似于水镁石Mg(OH)2,化学组成具有如下通式[M2+ 1-xM3+ x(OH)2]x+(An-)x/n·mH2O,其中,M2+和M3+分别为二价和三价阳离子,X为三价金属阳离子与阳离子总量的摩尔比,即M3+/(M2++M3+)。A为层间的阴离子,n为其电荷数。由于LDHs的层间阴离子可与外界的阴离子进行离子交换,因此在环境领域,可用于水中阴离子污染物的吸附去除。如何将层状复合金属氧化物应用在有机污染物与砷元素复合污染的同步去除的处理中,是非常值得研究的课题。Layered composite metal hydroxides (LDHs) are compounds assembled from positively charged host laminates and interlayer anions through non-covalent interactions. Its structure is similar to brucite Mg(OH) 2 , and its chemical composition has the following general formula [M 2+ 1-x M 3+ x (OH) 2 ] x+ (A n- ) x/n mH 2 O, where , M 2+ and M 3+ are divalent and trivalent cations respectively, and X is the molar ratio of trivalent metal cations to the total amount of cations, that is, M 3+ /(M 2+ +M 3+ ). A is an anion between layers, and n is its charge number. Since the interlayer anions of LDHs can ion-exchange with external anions, they can be used for the adsorption and removal of anion pollutants in water in the environmental field. How to apply layered composite metal oxides to the simultaneous removal of organic pollutants and arsenic compound pollution is a topic worthy of research.
发明内容Contents of the invention
本发明的目的就是为了克服上述现有技术存在的缺陷而提供一种兼具吸附砷、催化氧化有机污染物能力和杀菌能力的次氯酸根插层层状复合金属氢氧化物的制备与应用。The purpose of the present invention is to overcome the defects of the above-mentioned prior art and provide a preparation and application of a hypochlorite intercalated layered composite metal hydroxide with the ability to adsorb arsenic, catalyze the oxidation of organic pollutants and sterilize.
本发明的目的可以通过以下技术方案来实现:一种次氯酸根插层层状复合金属氢氧化物,该次氯酸根插层层状复合金属氢氧化物的通式为[Mg2+ 0.75Fe3+ 0.25kCe3+ 0.25(1-k)(OH)2]0.25+(ClO-)0.25·mH2O,其中k=0.95~1。The object of the present invention can be achieved through the following technical scheme: a kind of hypochlorite intercalation layered composite metal hydroxide, the general formula of this hypochlorite intercalation layered composite metal hydroxide is [Mg 2+ 0.75 Fe 3+ 0.25k Ce 3+ 0.25(1-k) (OH) 2 ] 0.25+ (ClO - ) 0.25 ·mH 2 O, where k=0.95~1.
一种如上所述次氯酸根插层层状复合金属氢氧化物的制备方法,所述方法包括以下几个步骤:A kind of preparation method of hypochlorite intercalation layered composite metal hydroxide as above, described method comprises the following steps:
(1)将Mg2+盐、Ce3+盐和Fe3+盐按比例溶于去离子水中,得到第一溶液;将NaOH和Na2CO3混合并溶于去离子水中得到第二溶液;将次氯酸盐溶于去离子水中,得到第三溶液;(1) Mg 2+ salt, Ce 3+ salt and Fe 3+ salt are dissolved in deionized water in proportion to obtain the first solution; NaOH and Na 2 CO 3 are mixed and dissolved in deionized water to obtain the second solution; Dissolving hypochlorite in deionized water to obtain a third solution;
(2)将第一溶液和第二溶液按Mg2+、Ce3+、Fe3+的物质的量之和与第二溶液中的NaOH的物质的量之比为1:(2~4)进行混合,搅拌得到浆液,陈化后固液分离,并将固体沉淀物清洗至中性,烘干并煅烧,得到煅烧产物;(2) The ratio of the sum of the amount of substances of Mg 2+ , Ce 3+ , and Fe 3+ to the amount of NaOH in the second solution is 1: (2~4) Mixing and stirring to obtain a slurry, separating the solid and liquid after aging, washing the solid precipitate to neutrality, drying and calcining to obtain a calcined product;
(3)将煅烧产物加入至第三溶液中,反应后进行固液分离,得到的固体进行清洗及干燥,即得所述次氯酸根插层层状复合金属氢氧化物。(3) adding the calcined product into the third solution, performing solid-liquid separation after the reaction, and washing and drying the obtained solid to obtain the hypochlorite-intercalated layered composite metal hydroxide.
所述Mg2+盐为镁的硝酸盐或盐酸盐,所述Fe3+盐为铁的硝酸盐或盐酸盐,所述Ce3+盐为Ce(NO3)3·6H2O,,所述第一溶液中,Mg2+的浓度为150~900mmol·L-1,Mg2+与Fe3+和Ce3+总摩尔浓度的比例为3:1,Ce3+占Fe3+和Ce3+总摩尔浓度的0~5%。The Mg 2+ salt is magnesium nitrate or hydrochloride, the Fe 3+ salt is iron nitrate or hydrochloride, and the Ce3+ salt is Ce(NO 3 ) 3 ·6H 2 O, so In the above first solution, the concentration of Mg 2+ is 150-900mmol·L -1 , the ratio of Mg 2+ to the total molar concentration of Fe 3+ and Ce 3+ is 3:1, and Ce 3+ accounts for Fe 3+ and Ce 3+ 3+ 0-5% of the total molar concentration.
所述第二溶液中,NaOH浓度为400~4800mmol·L-1,Na2CO3与NaOH的摩尔浓度比为0.25:1。In the second solution, the concentration of NaOH is 400˜4800 mmol·L −1 , and the molar concentration ratio of Na 2 CO 3 to NaOH is 0.25:1.
所述次氯酸盐为NaClO,第三溶液中ClO-的浓度为20~100mmol·L-1。The hypochlorite is NaClO, and the concentration of ClO - in the third solution is 20-100 mmol·L -1 .
步骤(2)中所述搅拌过程中保持溶液pH为9~11,这样可以使金属离子沉淀完全。Keep the pH of the solution at 9-11 during the stirring process described in step (2), so that the metal ions can be completely precipitated.
步骤(2)所述陈化的处理温度为60~80℃,陈化时间为20~36h,所述煅烧时间为400~500℃,控制陈化时间和温度为了使前驱体的具有更佳的层状结构,400~500℃煅烧可以保持前驱体的层板不塌陷并充分去除层间的碳酸根。The aging treatment temperature in step (2) is 60-80°C, the aging time is 20-36h, and the calcination time is 400-500°C, the aging time and temperature are controlled in order to make the precursor have a better Layered structure, calcination at 400-500 °C can keep the laminates of the precursor from collapsing and fully remove the carbonate groups between the layers.
步骤(3)所述干燥温度为-20~-10℃,防止干燥过程中次氯酸根分解。The drying temperature in step (3) is -20 to -10° C. to prevent the decomposition of hypochlorite radicals during the drying process.
一种如上所述次氯酸根插层层状复合金属氢氧化物的应用,可用于水中砷元素的吸附去除或砷元素与有机污染物的协同氧化降解。The application of the above-mentioned hypochlorite intercalation layered composite metal hydroxide can be used for the adsorption and removal of arsenic in water or the coordinated oxidation degradation of arsenic and organic pollutants.
所述有机污染物包括溶于水中的药物及个人护理品、内分泌干扰物或持久性有机污染物。The organic pollutants include drugs and personal care products, endocrine disruptors or persistent organic pollutants dissolved in water.
当将层状复合金属氢氧化物用于吸附去除水中的砷、锑并协同氧化降解有机污染物时,将所述的层状复合金属氢氧化物加入到含有砷、锑和有机污染物的水中,使水中的无机污染物吸附在层状复合金属氢氧化物上,由于合成的材料层板间阴离子是次氯酸根离子,具有较好的离子交换能力,因而吸附污染物的能力更强,并且在吸附砷、锑等无机污染物的同时,由于层间置换作用置换出次氯酸根,可以协同杀灭水中的有机污染物。When the layered composite metal hydroxide is used to adsorb and remove arsenic and antimony in water and synergistically oxidize and degrade organic pollutants, the layered composite metal hydroxide is added to the water containing arsenic, antimony and organic pollutants , so that the inorganic pollutants in the water are adsorbed on the layered composite metal hydroxide. Since the anion between the laminates of the synthesized material is hypochlorite ion, it has a good ion exchange capacity, so the ability to adsorb pollutants is stronger, and While adsorbing inorganic pollutants such as arsenic and antimony, hypochlorite is replaced by interlayer replacement, which can synergistically kill organic pollutants in water.
与现有技术相比,本发明的有益效果体现在以下几方面:Compared with the prior art, the beneficial effects of the present invention are reflected in the following aspects:
(1)对砷元素的处理灵敏度高;(1) The processing sensitivity to arsenic is high;
(2)能有效除去砷元素及各类有机物形成的复合污染,适用范围广;(2) It can effectively remove compound pollution formed by arsenic and various organic substances, and has a wide range of applications;
(3)本发明的高锰酸根插层层状复合金属氢氧化物制备简单,成本低。(3) The permanganate intercalation layered composite metal hydroxide of the present invention is simple to prepare and low in cost.
具体实施方式detailed description
下面对本发明的实施例作详细说明,本实施例在以本发明技术方案为前提下进行实施,给出了详细的实施方式和具体的操作过程,但本发明的保护范围不限于下述的实施例。The embodiments of the present invention are described in detail below. This embodiment is implemented on the premise of the technical solution of the present invention, and detailed implementation methods and specific operating procedures are provided, but the protection scope of the present invention is not limited to the following implementation example.
实施例1Example 1
一种用于协同去除水中复合污染的次氯酸根插层层状复合金属氢氧化物,其制备方法包括以下步骤:A hypochlorite intercalated layered composite metal hydroxide for synergistically removing composite pollution in water, the preparation method of which comprises the following steps:
(1)配制100ml的第一溶液,含有150mmol·L-1的Mg2+、50mmol·L-1的Fe3+;另配制100ml的第二溶液,含有400mmol·L-1的NaOH和100mmol·L-1的Na2CO3;另配制20mmol·L-1的次氯酸钠溶液。(1) Prepare 100ml of the first solution, containing 150mmol·L -1 of Mg 2+ , 50mmol·L -1 of Fe 3+ ; prepare another 100ml of the second solution, containing 400mmol·L -1 of NaOH and 100mmol·L -1 L -1 of Na 2 CO 3 ; another 20 mmol·L -1 of sodium hypochlorite solution was prepared.
(2)将上述配置好的第一溶液和第二溶液同时滴加到含有100ml的去离子水的烧杯中,滴加过程中进行剧烈搅拌,同时控制反应过程的pH值保持在9,将反应得到的浆液在60℃下陈化36小时,然后进行固液分离,将得到的固体沉淀物用去离子水清洗至上清液呈中性,然后在60℃下烘干,并在400℃下煅烧,得到的煅烧产物加入到次氯酸钠溶液中进行反应。(2) Add the above-mentioned configured first solution and second solution dropwise to a beaker containing 100ml of deionized water at the same time, stir vigorously during the dropwise addition, and control the pH value of the reaction process to remain at 9, and react The obtained slurry was aged at 60°C for 36 hours, and then solid-liquid separation was performed, and the obtained solid precipitate was washed with deionized water until the supernatant was neutral, then dried at 60°C, and calcined at 400°C , The obtained calcined product is added into the sodium hypochlorite solution for reaction.
(3)反应后离心分离,并用去离子水冲洗沉淀物,在-10℃下干燥,即得次氯酸根插层层状复合金属氢氧化物。(3) Centrifuge after the reaction, wash the precipitate with deionized water, and dry at -10°C to obtain the hypochlorite-intercalated layered composite metal hydroxide.
将制备得到的层状复合金属氢氧化物用于水中砷的去除,含1.0mg·L-1五价砷水样,经材料吸附处理后砷的浓度小于0.01mg·L-1,低于国家饮用水标准限值。The prepared layered composite metal hydroxide was used for the removal of arsenic in water, and the concentration of arsenic in the water sample containing 1.0mg·L -1 pentavalent arsenic was less than 0.01mg·L -1 after material adsorption treatment, lower than the national Standard limits for drinking water.
实施例2Example 2
一种用于协同去除水中复合污染的次氯酸根插层层状复合金属氢氧化物,其制备方法包括以下步骤:A hypochlorite intercalated layered composite metal hydroxide for synergistically removing composite pollution in water, the preparation method of which comprises the following steps:
(1)配制100ml的第一溶液,含有900mmol·L-1的Mg2+、285mmol·L-1的Fe3+和15mmol·L-1的Ce3+,另配制100ml的第二溶液,含有4800mmol·L-1的NaOH和1200mmol·L-1的Na2CO3,另配制100mmol·L-1的次氯酸钠溶液。(1) Prepare 100ml of the first solution containing 900mmol·L -1 of Mg 2+ , 285mmol·L -1 of Fe 3+ and 15mmol·L -1 of Ce 3+ , and prepare 100ml of the second solution containing 4800mmol·L -1 of NaOH and 1200mmol·L -1 of Na 2 CO 3 , and another 100mmol·L -1 of sodium hypochlorite solution was prepared.
(2)将上述配置好的第一溶液和第二溶液同时滴加到含有100ml的去离子水的烧杯中,滴加过程中进行剧烈搅拌,同时控制反应过程的pH值保持在10,将反应得到的浆液在70℃下陈化24小时,然后进行固液分离,将得到的固体沉淀物用去离子水清洗至上清液呈中性,然后在60℃下烘干,并在500℃下煅烧,得到的煅烧产物加入到次氯酸钠溶液中进行反应。(2) Add the above-mentioned configured first solution and the second solution dropwise to a beaker containing 100ml of deionized water at the same time, stir vigorously during the dropwise addition, and simultaneously control the pH value of the reaction process to remain at 10. The obtained slurry was aged at 70°C for 24 hours, and then solid-liquid separation was performed, and the obtained solid precipitate was washed with deionized water until the supernatant was neutral, then dried at 60°C, and calcined at 500°C , The obtained calcined product is added into the sodium hypochlorite solution for reaction.
(3)反应后离心分离,并用去离子水冲洗沉淀物,在-20℃下干燥,即得次氯酸根插层层状复合金属氢氧化物。(3) Centrifuge after the reaction, wash the precipitate with deionized water, and dry at -20°C to obtain the hypochlorite-intercalated layered composite metal hydroxide.
将制备得到的层状复合金属氢氧化物用于水中的砷的去除,含0.5mg·L-1五价砷和0.5mg·L-1三价砷的水样,经材料吸附处理后总砷的浓度小于0.01mg·L-1,低于国家饮用水标准限值。The prepared layered composite metal hydroxide is used for the removal of arsenic in water. For water samples containing 0.5mg·L -1 pentavalent arsenic and 0.5mg·L -1 trivalent arsenic, the total arsenic after material adsorption treatment The concentration is less than 0.01mg·L -1 , lower than the national drinking water standard limit.
实施例3Example 3
一种用于协同去除水中复合污染的次氯酸根插层层状复合金属氢氧化物,其制备方法包括以下步骤:A hypochlorite intercalated layered composite metal hydroxide for synergistically removing composite pollution in water, the preparation method of which comprises the following steps:
(1)配制100ml的第一溶液,含有300mmol·L-1的Mg2+、95mmol·L-1的Fe3+和5mmol·L-1的Ce3+,另配制100ml的第二溶液,含有800mmol·L-1的NaOH和200mmol·L-1的Na2CO3,另配制100mmol·L-1的次氯酸钠溶液。(1) Prepare 100ml of the first solution containing 300mmol·L -1 of Mg 2+ , 95mmol·L -1 of Fe 3+ and 5mmol·L -1 of Ce 3+ , and prepare 100ml of the second solution containing 800mmol·L -1 of NaOH and 200mmol·L -1 of Na 2 CO 3 , and another 100mmol·L -1 of sodium hypochlorite solution was prepared.
(2)将上述配置好的第一溶液和第二溶液同时滴加到含有100ml的去离子水的烧杯中,滴加过程中进行剧烈搅拌,同时控制反应过程的pH值保持在11,将反应得到的浆液在80℃下陈化20小时,然后进行固液分离,将得到的固体沉淀物用去离子水清洗至上清液呈中性,然后在60℃下烘干,并在500℃下煅烧,得到的煅烧产物加入到次氯酸钠溶液中进行反应。(2) Add the above-mentioned configured first solution and second solution dropwise to a beaker containing 100ml of deionized water at the same time, stir vigorously during the dropwise addition, and simultaneously control the pH value of the reaction process to remain at 11, and react The obtained slurry was aged at 80°C for 20 hours, and then solid-liquid separation was performed, and the obtained solid precipitate was washed with deionized water until the supernatant was neutral, then dried at 60°C, and calcined at 500°C , The obtained calcined product is added into the sodium hypochlorite solution for reaction.
(3)反应后离心分离,并用去离子水冲洗沉淀物,在-10℃下真空冷冻干燥,即得次氯酸根插层层状复合金属氢氧化物。(3) Centrifuge after the reaction, wash the precipitate with deionized water, and vacuum freeze-dry at -10°C to obtain the hypochlorite-intercalated layered composite metal hydroxide.
将制备得到的层状复合金属氢氧化物用于含砷及有机污染物水的净化,含0.5mg·L-1五价砷的水样,经材料吸附处理后总砷的浓度小于0.01mg·L-1,低于国家饮用水标准限值,释放出的次氯酸根可氧化有机污染物。The prepared layered composite metal hydroxide is used to purify water containing arsenic and organic pollutants. For water samples containing 0.5 mg·L -1 pentavalent arsenic, the concentration of total arsenic after material adsorption treatment is less than 0.01 mg· L -1 , lower than the national drinking water standard limit, the released hypochlorite can oxidize organic pollutants.
实施例4Example 4
一种用于协同去除水中复合污染的次氯酸根插层层状复合金属氢氧化物,其制备方法包括以下步骤:A hypochlorite intercalated layered composite metal hydroxide for synergistically removing composite pollution in water, the preparation method of which comprises the following steps:
(1)配制100ml的第一溶液,含有600mmol·L-1的Mg2+、190mmol·L-1的Fe3+和10mmol·L-1的Ce3+,另配制100ml的第二溶液,含有1600mmol·L-1的NaOH和400mmol·L-1的Na2CO3,另配制100mmol·L-1的次氯酸钠溶液。(1) Prepare 100ml of the first solution containing 600mmol·L -1 of Mg 2+ , 190mmol·L -1 of Fe 3+ and 10mmol·L -1 of Ce 3+ , and prepare 100ml of the second solution containing 1600mmol·L -1 of NaOH and 400mmol·L -1 of Na 2 CO 3 , and another 100mmol·L -1 of sodium hypochlorite solution was prepared.
(2)将上述配置好的第一溶液和第二溶液同时滴加到含有100ml的去离子水的烧杯中,滴加过程中进行剧烈搅拌,同时控制反应过程的pH值保持在10.5,将反应得到的浆液在70℃下陈化36小时,然后进行固液分离,将得到的固体沉淀物用去离子水清洗至上清液呈中性,然后在60℃下烘干,并在500℃下煅烧,得到的煅烧产物加入到次氯酸钠溶液中进行反应。(2) Add the above-mentioned configured first solution and the second solution dropwise to a beaker containing 100ml of deionized water at the same time, stir vigorously during the dropwise addition, and control the pH value of the reaction process to remain at 10.5, and react The obtained slurry was aged at 70°C for 36 hours, and then solid-liquid separation was performed, and the obtained solid precipitate was washed with deionized water until the supernatant was neutral, then dried at 60°C, and calcined at 500°C , The obtained calcined product is added into the sodium hypochlorite solution for reaction.
(3)反应后离心分离,并用去离子水冲洗沉淀物,在-10℃下干燥,即得次氯酸根插层层状复合金属氢氧化物。(3) Centrifuge after the reaction, wash the precipitate with deionized water, and dry at -10°C to obtain the hypochlorite-intercalated layered composite metal hydroxide.
将制备得到的层状复合金属氢氧化物用于含砷及微量有机污染物、细菌水的净化,含1.0mg·L-1五价砷、微量有机污染物和细菌的水样,经材料吸附处理后总砷的浓度小于0.01mg·L-1,低于国家饮用水标准限值,释放出的次氯酸根可氧化水中有机污染物、杀灭细菌。The prepared layered composite metal hydroxide is used to purify water containing arsenic and trace organic pollutants and bacteria. Water samples containing 1.0mg·L -1 pentavalent arsenic, trace organic pollutants and bacteria are adsorbed by the material The concentration of total arsenic after treatment is less than 0.01mg·L -1 , which is lower than the national drinking water standard limit, and the released hypochlorite can oxidize organic pollutants in water and kill bacteria.
实施例5Example 5
一种用于协同去除水中复合污染的次氯酸根插层层状复合金属氢氧化物,其制备方法包括以下步骤:A hypochlorite intercalated layered composite metal hydroxide for synergistically removing composite pollution in water, the preparation method of which comprises the following steps:
(1)配制100ml的第一溶液,含有450mmol·L-1的Mg2+、142.5mmol·L-1的Fe3+和7.5mmol·L-1的Ce3+,另配制100ml的第二溶液,含有1200mmol·L-1的NaOH和300mmol·L-1的Na2CO3,另配制100mmol·L-1的次氯酸钠溶液。(1) Prepare 100ml of the first solution, containing 450mmol·L -1 of Mg 2+ , 142.5mmol·L -1 of Fe 3+ and 7.5mmol·L -1 of Ce 3+ , and prepare 100ml of the second solution , containing 1200mmol·L -1 NaOH and 300mmol·L -1 Na 2 CO 3 , and another 100mmol·L -1 sodium hypochlorite solution was prepared.
(2)将上述配置好的第一溶液和第二溶液同时滴加到含有100ml的去离子水的烧杯中,滴加过程中进行剧烈搅拌,同时控制反应过程的pH值保持在9.5,将反应得到的浆液在80℃下陈化24小时,然后进行固液分离,将得到的固体沉淀物用去离子水清洗至上清液呈中性,然后在60℃下烘干,并在500℃下煅烧,得到的煅烧产物加入到次氯酸钠溶液中进行反应。(2) Add the above-mentioned configured first solution and second solution dropwise to a beaker containing 100ml of deionized water at the same time, stir vigorously during the dropwise addition, and control the pH value of the reaction process to remain at 9.5, and react The obtained slurry was aged at 80°C for 24 hours, and then solid-liquid separation was performed, and the obtained solid precipitate was washed with deionized water until the supernatant was neutral, then dried at 60°C, and calcined at 500°C , The obtained calcined product is added into the sodium hypochlorite solution for reaction.
(3)反应后离心分离,并用去离子水冲洗沉淀物,在-10℃下干燥,即得次氯酸根插层层状复合金属氢氧化物。(3) Centrifuge after the reaction, wash the precipitate with deionized water, and dry at -10°C to obtain the hypochlorite-intercalated layered composite metal hydroxide.
将制备得到的层状复合金属氢氧化物用于含砷及微量有机污染物、细菌水的净化,含0.5mg·L-1五价砷、微量有机污染物和细菌的水样,经材料吸附处理后总砷的浓度小于0.01mg·L-1,低于国家饮用水标准限值,释放出的次氯酸根可氧化水中有机污染物、杀灭细菌。The prepared layered composite metal hydroxide is used to purify water containing arsenic, trace organic pollutants, and bacteria. Water samples containing 0.5mg·L -1 pentavalent arsenic, trace organic pollutants, and bacteria are adsorbed by the material The concentration of total arsenic after treatment is less than 0.01mg·L -1 , which is lower than the national drinking water standard limit, and the released hypochlorite can oxidize organic pollutants in water and kill bacteria.
实施例6Example 6
一种用于协同去除水中复合污染的次氯酸根插层层状复合金属氢氧化物,其制备方法包括以下步骤:A hypochlorite intercalated layered composite metal hydroxide for synergistically removing composite pollution in water, the preparation method of which comprises the following steps:
(1)配制100ml的第一溶液,含有100mmol·L-1的Mg2+、285mmol·L-1的Fe3+和15mmol·L-1的Ce3+,另配制100ml的第二溶液,含有900mmol·L-1的NaOH和900mmol·L-1的Na2CO3,另配制100mmol·L-1的次氯酸钠溶液。(1) Prepare 100ml of the first solution containing 100mmol·L -1 of Mg 2+ , 285mmol·L -1 of Fe 3+ and 15mmol·L -1 of Ce 3+ , and prepare 100ml of the second solution containing 900mmol·L -1 of NaOH and 900mmol·L -1 of Na 2 CO 3 , and another 100mmol·L -1 of sodium hypochlorite solution was prepared.
(2)将上述配置好的第一溶液和第二溶液同时滴加到含有100ml的去离子水的烧杯中,滴加过程中进行剧烈搅拌,同时控制反应过程的pH值保持在9,将反应得到的浆液在65℃下陈化24小时,然后进行固液分离,将得到的固体沉淀物用去离子水清洗至上清液呈中性,然后在60℃下烘干,并在500℃下煅烧,得到的煅烧产物加入到次氯酸钠溶液中进行反应。(2) Add the above-mentioned configured first solution and second solution dropwise to a beaker containing 100ml of deionized water at the same time, stir vigorously during the dropwise addition, and control the pH value of the reaction process to remain at 9, and react The obtained slurry was aged at 65°C for 24 hours, and then solid-liquid separation was performed, and the obtained solid precipitate was washed with deionized water until the supernatant was neutral, then dried at 60°C, and calcined at 500°C , The obtained calcined product is added into the sodium hypochlorite solution for reaction.
(3)反应后离心分离,并用去离子水冲洗沉淀物,在-10℃下干燥,即得次氯酸根插层层状复合金属氢氧化物。(3) Centrifuge after the reaction, wash the precipitate with deionized water, and dry at -10°C to obtain the hypochlorite-intercalated layered composite metal hydroxide.
将制备得到的层状复合金属氢氧化物用于含砷及微量有机污染物、细菌水的净化,含0.8mg·L-1五价砷、微量有机污染物和细菌的水样,经材料吸附处理后总砷的浓度小于0.01mg·L-1,低于国家饮用水标准限值,释放出的次氯酸根可氧化水中有机污染物、杀灭细菌。The prepared layered composite metal hydroxide is used to purify water containing arsenic and trace organic pollutants and bacteria. Water samples containing 0.8 mg·L -1 pentavalent arsenic, trace organic pollutants and bacteria are adsorbed by the material The concentration of total arsenic after treatment is less than 0.01mg·L -1 , which is lower than the national drinking water standard limit, and the released hypochlorite can oxidize organic pollutants in water and kill bacteria.
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| CN118847076A (en) * | 2024-07-01 | 2024-10-29 | 北京化工大学 | A layered hydroxide composite material for chemical poison decontamination and preparation method thereof |
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Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
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| CN110078186A (en) * | 2019-05-17 | 2019-08-02 | 上海大学 | A kind of dual-functional nanometer removes the preparation method and application of algae material |
| CN118847076A (en) * | 2024-07-01 | 2024-10-29 | 北京化工大学 | A layered hydroxide composite material for chemical poison decontamination and preparation method thereof |
| CN118847076B (en) * | 2024-07-01 | 2025-06-06 | 北京化工大学 | Layered hydroxide composite material for decontamination of chemical poison and preparation method thereof |
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