WO2022166187A1 - Attapulgite surface modification method - Google Patents

Attapulgite surface modification method Download PDF

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WO2022166187A1
WO2022166187A1 PCT/CN2021/115776 CN2021115776W WO2022166187A1 WO 2022166187 A1 WO2022166187 A1 WO 2022166187A1 CN 2021115776 W CN2021115776 W CN 2021115776W WO 2022166187 A1 WO2022166187 A1 WO 2022166187A1
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attapulgite
modification
alkali
aluminum chloride
modified
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董良飞
孙俊杰
叶天宝
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南京公诚节能新材料研究院有限公司
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    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B33/00Silicon; Compounds thereof
    • C01B33/20Silicates
    • C01B33/36Silicates having base-exchange properties but not having molecular sieve properties
    • C01B33/38Layered base-exchange silicates, e.g. clays, micas or alkali metal silicates of kenyaite or magadiite type
    • C01B33/40Clays
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • C02F1/5245Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron

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  • Embodiment 5 is a diagrammatic representation of Embodiment 5:

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  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
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  • Engineering & Computer Science (AREA)
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  • Water Supply & Treatment (AREA)
  • Dispersion Chemistry (AREA)
  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)

Abstract

Provided is an attapulgite surface modification method, comprising: S3: putting attapulgite into a sodium hydroxide solution, and performing hot alkali modification on natural attapulgite to obtain alkali-modified attapulgite, optionally, performing heat modification on the attapulgite before alkali modification; and S4: adding aluminum chloride to the alkali-modified attapulgite for reaction and polymerization. The attapulgite surface modification method further comprises: S1: replacing magnesium in an attapulgite crystal with aluminum ions to improve the treatment performance of the attapulgite crystal on algae; and S2: polymerizing the aluminum ions on the surface of the attapulgite, so that the surface of the attapulgite is rich in positive charges, and the coagulation effect of the attapulgite is enhanced. According to the attapulgite surface modification method, the attapulgite is first subjected to the heat and alkali modification and then subjected to the aluminum chloride modification, so that the spatial structure of the attapulgite is improved, the adsorption performance of the algae is enhanced, the effect of the attapulgite in the algae treatment is further improved, both economy and environmental protection are achieved, and the modified attapulgite has obvious advantages in the field of water treatment.

Description

一种凹土表面改性方法A kind of surface modification method of attapulgite 技术领域technical field
本发明涉及水处理技术领域,具体为一种凹土表面改性方法。The invention relates to the technical field of water treatment, in particular to a method for modifying the surface of attapulgite.
背景技术Background technique
随着社会发展及工业化进程加快,河流湖泊等环境压力日益增大,很多湖泊河流富营养化问题加剧,甚至污染严重,导致水体生态环境失衡,以藻类为代表的微生物种群爆发性增殖,其恶劣的感官影响及释放的藻毒素,不仅严重影响了水体环境景观,更对河道湖泊水生生物及人类生活生产安全造成了严重威胁。With the acceleration of social development and industrialization, the pressure on the environment such as rivers and lakes is increasing day by day. The eutrophication problem of many lakes and rivers is intensified, and even serious pollution has caused the imbalance of the water ecological environment. The microbial population represented by algae exploded and proliferated. The sensory impact of algal toxins and the release of algal toxins not only seriously affect the water environment and landscape, but also pose a serious threat to the safety of rivers, lakes, aquatic organisms and human life and production.
近年来,国内外的许多学者发展出大量的技术手段减少或去除河道湖泊水体中的藻类,进而控制藻类爆发。目前对于河道湖泊藻类爆发的防治主要为预防和直接治理。其中直接治理方法包括物理法、化学法、微生物法以及这些方法的联合应用。物理法包括机械打捞除藻、直接过滤除藻、微滤机过滤除藻、气浮法除藻、超声波除藻等方法,通过利用杀菌或过滤设备直接消除水体中的藻类,其原理简单,可直接降低水中藻类生物量,无二次污染,但此方法需要消耗大量的人力物力,且对于大范围水体而言应用范围较窄。化学法是利用化学杀菌剂对藻类进行杀灭,通常应用于藻类治理的杀菌剂有硫酸铜、二氧化氯、过氧化氢戊二醛等,虽然此方法除藻速度快,效果明显,但同时也具有一定的危险性,容易造成二次污染,这些化合物在水体中扩散,对水生生物具有直接的毒害作用,且藻类死亡后释放的藻毒素是肝癌的主要诱因。微生物法主要利用光合细菌、芽孢杆菌等微生物作为除 藻剂,通过其生命代谢,将水中污染物进行转化、降解及转移作用,从而使水体获得净化的方法,这种方法成本高,周期长,很难大规模适用,而且还会带来外来生物入侵等问题。凹凸棒石黏土(以下简称凹土)由于其特殊的纤维状棒晶结构以及多空的空间结构,藻类在凹土的表面吸附、富集并沉淀,使得藻类得以去除。但未改性的凹土本身溶胶性较差,絮凝、沉降速率低,使得藻处理效率低下,量少时难以达到良好的去除效果,量大时容易造成原料量和淤渣量过大等问题。因此,本发明利用凹土的除藻特性,以氯化铝为主要改性剂对凹土表面进行改性修饰,增强凹土除藻性能,制备出除藻剂。In recent years, many scholars at home and abroad have developed a large number of technical means to reduce or remove algae in water bodies of rivers and lakes, thereby controlling algal blooms. At present, the prevention and control of algal blooms in rivers and lakes are mainly prevention and direct control. The direct treatment methods include physical method, chemical method, microbial method and the combined application of these methods. Physical methods include mechanical salvage algae removal, direct filtration algae removal, microfiltration algae removal, air flotation algae removal, ultrasonic algae removal and other methods. The algae in the water body can be directly eliminated by using sterilization or filtration equipment. The principle is simple and can be used. Directly reduce algal biomass in water without secondary pollution, but this method requires a lot of manpower and material resources, and has a narrow application range for a large range of water bodies. The chemical method uses chemical fungicides to kill algae. The fungicides usually used in algae treatment include copper sulfate, chlorine dioxide, hydrogen peroxide, glutaraldehyde, etc. It is also dangerous and easy to cause secondary pollution. These compounds diffuse in the water body and have a direct toxic effect on aquatic organisms, and the algal toxins released after the death of algae are the main causes of liver cancer. Microbial method mainly uses photosynthetic bacteria, Bacillus and other microorganisms as algaecide, and through its life metabolism, it transforms, degrades and transfers pollutants in water, so as to purify water body. This method has high cost and long cycle. It is difficult to apply on a large scale, and it will also bring problems such as alien biological invasion. Attapulgite clay (hereinafter referred to as attapulgite) due to its special fibrous rod crystal structure and hollow space structure, algae adsorb, enrich and precipitate on the surface of attapulgite, so that algae can be removed. However, the unmodified attapulgite itself has poor sol property, low flocculation and sedimentation rates, which makes the algae treatment efficiency low, and it is difficult to achieve a good removal effect when the amount is small. . Therefore, the present invention utilizes the algae removal properties of attapulgite, uses aluminum chloride as the main modifier to modify the surface of the attapulgite, enhances the algae removal performance of the attapulgite, and prepares the algae removal agent.
凹土是一种天然的含水富镁铝的硅酸盐矿物,对环境无危害,且具有独特的纳米级链层状分子结构,晶体呈棒状或纤维状。较大的比表面积和微细孔隙结构使之具有良好的吸附性,众多纳米尺寸的孔道存在大量活性中心,加之较强的机械性能和热稳定性,是优良的载体。本发明利用氯化铝使得凹土表面附载大量正电荷离子,中和藻类表面负电荷离子,使得藻类脱稳,最终实现藻类去除,净化水体,达到水质改善和提升的目的。因此我们对此做出改进,提出一种凹土表面改性方法。Attapulgite is a natural silicate mineral rich in magnesium and aluminum, which is not harmful to the environment, and has a unique nano-scale chain layered molecular structure, and the crystals are rod-shaped or fibrous. The large specific surface area and fine pore structure make it have good adsorption, many nano-sized pores have a large number of active centers, coupled with strong mechanical properties and thermal stability, it is an excellent carrier. The invention uses aluminum chloride to make the surface of attapulgite carry a large number of positively charged ions, neutralize the negatively charged ions on the surface of algae, destabilize the algae, and finally realize the removal of algae, purify the water body, and achieve the purpose of improving and improving water quality. Therefore, we improved this and proposed a method for surface modification of attapulgite.
实用发明内容Practical Invention Content
为了解决上述技术问题,本发明提供了如下的技术方案:In order to solve the above-mentioned technical problems, the present invention provides the following technical solutions:
本发明一种凹土表面改性方法,包括以下步骤:A kind of attapulgite surface modification method of the present invention comprises the following steps:
S1:以铝离子对凹土晶体中镁进行取代,改善其对藻类的处理性能;S1: Substitute magnesium in attapulgite crystals with aluminum ions to improve its treatment performance against algae;
S2:铝离子在凹土表面进行聚合,使得凹土表面富含正电荷,加强其混凝效果;S2: The aggregation of aluminum ions on the surface of attapulgite makes the surface of attapulgite rich in positive charges and enhances its coagulation effect;
S3:将凹土投入至氢氧化钠溶液中,对天然凹土进行热碱改性,获得碱改性凹土;S3: put the attapulgite into the sodium hydroxide solution, and perform thermal alkali modification on the natural attapulgite to obtain the alkali-modified attapulgite;
S4:在碱改性凹土中加入氯化铝进行反应并聚合,采用氯化铝对凹土表面进行无机改性,获得改性凹土;S4: adding aluminum chloride to the alkali-modified attapulgite for reaction and polymerization, and using aluminum chloride to perform inorganic modification on the surface of the attapulgite to obtain modified attapulgite;
在上述技术方案中,凹土的热碱改性和氯化铝改性的步骤顺序有限定,在实施中需要对凹土首先实行热、碱改性,然后进一步对凹土进行氯化铝无机改性。In the above technical solution, the step sequence of the thermal alkali modification of attapulgite and the modification of aluminum chloride is limited. In the implementation, it is necessary to first perform thermal and alkali modification on the attapulgite, and then further perform the aluminum chloride inorganic modification on the attapulgite. modified.
作为本发明的一种优选技术方案,所述热改性的具体步骤为:根据S4步骤中,将开采的原矿凹土在0℃-500℃下烘培1-3小时,制得热改性凹土。As a preferred technical solution of the present invention, the specific steps of thermal modification are as follows: according to step S4, the mined attapulgite is baked at 0°C-500°C for 1-3 hours to obtain thermally modified Attapulgite.
作为本发明的一种优选技术方案,所述碱改性的具体步骤为,根据S4步骤中,使热改性后凹土、氢氧化钠和溶剂的混合反应体系于常温条件下反应1-3小时,混合反应体系应于搅拌条件下进行。As a preferred technical solution of the present invention, the specific step of the alkali modification is, according to step S4, the mixed reaction system of the thermally modified attapulgite, sodium hydroxide and solvent is reacted at room temperature for 1-3 hours, the mixed reaction system should be carried out under stirring conditions.
作为本发明的一种优选技术方案,所述搅拌条件转速应为200-500r/min,所述溶剂为去离子水,所述热改性后凹土与氢氧化钠的质量比为(5-10):1。As a preferred technical solution of the present invention, the rotational speed of the stirring condition should be 200-500 r/min, the solvent is deionized water, and the mass ratio of the thermally modified attapulgite to sodium hydroxide is (5- 10): 1.
作为本发明的一种优选技术方案,所述氯化铝改性的具体步骤为:根据S3步骤中,将热碱改性后凹土、氯化铝和溶剂的混合反应体系于60℃-90℃条件下反应6-10小时。As a preferred technical solution of the present invention, the specific steps of the aluminum chloride modification are: according to step S3, the mixed reaction system of attapulgite, aluminum chloride and solvent after thermal alkali modification is heated at 60℃-90℃ The reaction is carried out under the condition of ℃ for 6-10 hours.
作为本发明的一种优选技术方案,所述混合反应体系应于搅拌条 件下进行,所述搅拌条件转速应为200-500r/min,所述溶剂为去离子水。As a preferred technical solution of the present invention, the mixed reaction system should be carried out under stirring conditions, and the rotating speed of the stirring conditions should be 200-500 r/min, and the solvent is deionized water.
作为本发明的一种优选技术方案,所述氯化铝与溶剂的质量比为(10-30):100,所述碱改性凹土与氯化铝的质量比为(1-3):1。As a preferred technical solution of the present invention, the mass ratio of the aluminum chloride to the solvent is (10-30): 100, and the mass ratio of the alkali-modified attapulgite to the aluminum chloride is (1-3): 1.
本发明的有益效果是:The beneficial effects of the present invention are:
1、热改性可以去除凹土内部多余结合水,打开内部结构,增加凹土比表面积;碱改性可以活化凹土内部基团,使得凹土表面附着众多羟基结构,增加凹土的化学活性;带正电荷的铝离子在水中具有一定的混凝作用,其与凹土可以增强藻类絮凝效果;1. Thermal modification can remove excess bound water inside attapulgite, open the internal structure, and increase the specific surface area of attapulgite; alkali modification can activate the internal groups of attapulgite, so that many hydroxyl structures are attached to the surface of attapulgite, increasing the chemical activity of attapulgite ; Positively charged aluminum ions have a certain coagulation effect in water, and attapulgite can enhance the flocculation effect of algae;
2、对凹土采用热、碱及氯化铝等表面改性,改善了凹土的空间结构,增强了藻类吸附性能,进一步提高了凹土在藻类处理中的效果;2. The surface modification of attapulgite by heat, alkali and aluminum chloride improves the spatial structure of attapulgite, enhances the adsorption performance of algae, and further improves the effect of attapulgite in algae treatment;
凹土相对于其他除藻剂在水处理领域来说,价格低廉,适用成本低,且对于环境来说,凹土本身对环境没有危害,添加的氯化铝和其他改性物质对环境影响也微乎其微,从经济及环保角度来说,改性凹土在水处理领域具有明显的优势。Compared with other algaecides in the field of water treatment, attapulgite has low price and low applicable cost, and for the environment, attapulgite itself is not harmful to the environment, and the added aluminum chloride and other modified substances have no impact on the environment. Very little, from the perspective of economy and environmental protection, modified attapulgite has obvious advantages in the field of water treatment.
附图说明Description of drawings
附图用来提供对本发明的进一步理解,并且构成说明书的一部分,与本发明的实施例一起用于解释本发明,并不构成对本发明的限制。在附图中:The accompanying drawings are used to provide a further understanding of the present invention, and constitute a part of the specification, and are used to explain the present invention together with the embodiments of the present invention, and do not constitute a limitation to the present invention. In the attached image:
图1是本发明一种凹土表面改性方法的流程图。Fig. 1 is a flow chart of a method for modifying the surface of attapulgite according to the present invention.
具体实施方式Detailed ways
以下结合附图对本发明的优选实施例进行说明,应当理解,此处 所描述的优选实施例仅用于说明和解释本发明,并不用于限定本发明。The preferred embodiments of the present invention will be described below with reference to the accompanying drawings. It should be understood that the preferred embodiments described herein are only used to illustrate and explain the present invention, but not to limit the present invention.
实施例一:Example 1:
s1:将凹土原矿磨成细粉状过200目筛得凹土粉;得凹土粉末。s1: Grind the attapulgite raw ore into fine powder and pass through a 200-mesh sieve to obtain attapulgite powder; obtain attapulgite powder.
s2:将凹土粉末与氢氧化钠按照5:1的质量比投入少量去离子水中,在常温条件下搅拌1小时,得碱改性凹土。s2: put attapulgite powder and sodium hydroxide in a small amount of deionized water in a mass ratio of 5:1, and stir for 1 hour at normal temperature to obtain alkali-modified attapulgite.
s3:在pH为5左右条件下,将碱改性凹土与氯化铝按照1:1的质量比投入少量去离子水中,在60℃,200r/min条件下搅拌6小时使之分散,烘干,粉碎,得成品。s3: Under the condition that the pH is about 5, put the alkali-modified attapulgite and aluminum chloride into a small amount of deionized water according to the mass ratio of 1:1, and stir them for 6 hours at 60 ° C and 200 r/min to disperse them. Dried, crushed to get the finished product.
实施例二:Embodiment 2:
s1:将凹土原矿磨成细粉状过200目筛得凹土粉;凹土粉在200℃的温度下烘培1小时,得热改性凹土。s1: Grind the attapulgite raw ore into fine powder and pass through a 200-mesh sieve to obtain attapulgite powder; bake the attapulgite powder at a temperature of 200° C. for 1 hour to obtain heat-modified attapulgite.
s2:将热改性凹土与氢氧化钠按照5:1的质量比投入少量去离子水中,在常温条件下搅拌1小时,得碱改性凹土。s2: Put the heat-modified attapulgite and sodium hydroxide into a small amount of deionized water at a mass ratio of 5:1, and stir at room temperature for 1 hour to obtain alkali-modified attapulgite.
s3:在pH为5左右条件下,将热碱改性凹土与氯化铝按照1:1的质量比投入少量去离子水中,在60℃,200r/min条件下搅拌6小时使之分散,烘干,粉碎,得成品。s3: Under the condition that the pH is about 5, the hot alkali modified attapulgite and aluminum chloride are put into a small amount of deionized water according to the mass ratio of 1:1, and stirred for 6 hours at 60 ° C and 200 r/min to disperse them. Dry, pulverize, and get the finished product.
实施例三:Embodiment three:
s1:将凹土原矿磨成细粉状过200目筛得凹土粉;凹土粉在500℃的温度下烘培1小时,得热改性凹土。s1: Grind the attapulgite raw ore into fine powder and pass through a 200-mesh sieve to obtain attapulgite powder; bake the attapulgite powder at a temperature of 500° C. for 1 hour to obtain heat-modified attapulgite.
s2:将热改性凹土与氢氧化钠按照5:1的质量比投入少量去离子水中,在常温条件下搅拌1小时,得碱改性凹土。s2: Put the heat-modified attapulgite and sodium hydroxide into a small amount of deionized water at a mass ratio of 5:1, and stir at room temperature for 1 hour to obtain alkali-modified attapulgite.
s3:在pH为5左右条件下,将热碱改性凹土与氯化铝按照1:1 的质量比投入少量去离子水中,在60℃,200r/min条件下搅拌6小时使之分散,烘干,粉碎,得成品。s3: Under the condition of pH of about 5, put the hot alkali modified attapulgite and aluminum chloride into a small amount of deionized water according to the mass ratio of 1:1, and stir for 6 hours at 60 ° C and 200 r/min to disperse them. Dry, pulverize, and get the finished product.
实施例四:Embodiment 4:
s1:将凹土原矿磨成细粉状过200目筛得凹土粉;得凹土粉末。s1: Grind the attapulgite raw ore into fine powder and pass through a 200-mesh sieve to obtain attapulgite powder; obtain attapulgite powder.
s2:将凹土粉末与氢氧化钠按照10:1的质量比投入少量去离子水中,在常温条件下搅拌1小时,得碱改性凹土。s2: put the attapulgite powder and sodium hydroxide in a small amount of deionized water in a mass ratio of 10:1, and stir for 1 hour at normal temperature to obtain alkali-modified attapulgite.
s3:在pH为6左右条件下,将碱改性凹土与氯化铝按照1:1的质量比投入少量去离子水中,在80℃,200r/min条件下搅拌6小时使之分散,烘干,粉碎,得成品。s3: Under the condition that the pH is about 6, put the alkali-modified attapulgite and aluminum chloride into a small amount of deionized water according to the mass ratio of 1:1, stir for 6 hours at 80 ° C and 200 r/min to disperse them, and dry them. Dried, crushed to get the finished product.
实施例五:Embodiment 5:
s1:将凹土原矿磨成细粉状过200目筛得凹土粉;凹土粉在200℃的温度下烘培1小时,得热改性凹土。s1: Grind the attapulgite raw ore into fine powder and pass through a 200-mesh sieve to obtain attapulgite powder; bake the attapulgite powder at a temperature of 200° C. for 1 hour to obtain heat-modified attapulgite.
s2:将热改性凹土与氢氧化钠按照10:1的质量比投入少量去离子水中,在常温条件下搅拌1小时,得碱改性凹土。s2: Put the heat-modified attapulgite and sodium hydroxide into a small amount of deionized water in a mass ratio of 10:1, and stir at room temperature for 1 hour to obtain alkali-modified attapulgite.
s3:在pH为6左右条件下,将热碱改性凹土与氯化铝按照1:1的质量比投入少量去离子水中,在80℃,200r/min条件下搅拌6小时使之分散,烘干,粉碎,得成品。s3: Under the condition of pH of about 6, put the hot alkali modified attapulgite and aluminum chloride into a small amount of deionized water according to the mass ratio of 1:1, and stir for 6 hours at 80 ° C and 200 r/min to disperse them. Dry, pulverize, and get the finished product.
实施例六:Embodiment 6:
s1:将凹土原矿磨成细粉状过200目筛得凹土粉;凹土粉在500℃的温度下烘培1小时,得热改性凹土。s1: Grind the attapulgite raw ore into fine powder and pass through a 200-mesh sieve to obtain attapulgite powder; bake the attapulgite powder at a temperature of 500° C. for 1 hour to obtain heat-modified attapulgite.
s2:将热改性凹土与氢氧化钠按照10:1的质量比投入少量去离子水中,在常温条件下搅拌1小时,得碱改性凹土。s2: Put the heat-modified attapulgite and sodium hydroxide into a small amount of deionized water in a mass ratio of 10:1, and stir at room temperature for 1 hour to obtain alkali-modified attapulgite.
s3:在pH为6左右条件下,将热碱改性凹土与氯化铝按照1:1的质量比投入少量去离子水中,在80℃,200r/min条件下搅拌6小时使之分散,烘干,粉碎,得成品s3: Under the condition of pH of about 6, put the hot alkali modified attapulgite and aluminum chloride into a small amount of deionized water according to the mass ratio of 1:1, and stir for 6 hours at 80 ° C and 200 r/min to disperse them. Dry, pulverize, get the finished product
对比例1:Comparative Example 1:
单独使用未进行任何改性的天然凹土作为除藻剂应用于藻类治理。The natural attapulgite without any modification was used alone as an algaecide for algae control.
对比例2:Comparative Example 2:
将热改性凹土与氢氧化钠按照5:1质量比投入少量去离子水中,在常温条件下搅拌1小时,得碱改性凹土,应用于藻类治理(对凹土单独进行热碱改性)。Put thermally modified attapulgite and sodium hydroxide in a small amount of deionized water in a mass ratio of 5:1, and stir at room temperature for 1 hour to obtain alkali-modified attapulgite, which is used in algae treatment (heat-alkaline modification is performed on attapulgite alone. sex).
对比例3:Comparative Example 3:
将热改性凹土与氯化铝按照1:1质量比投入少量去离子水中,在80℃,200r/min条件下搅拌6小时,得氯化铝改性凹土,应用于藻类治理(对凹土单独进行氯化铝改性)。The thermally modified attapulgite and aluminum chloride were put into a small amount of deionized water at a mass ratio of 1:1, and stirred at 80 ° C and 200 r/min for 6 hours to obtain aluminum chloride-modified attapulgite, which was used in algae treatment (for algae treatment). Attapulgite is modified with aluminum chloride alone).
取蓝藻叶绿素含量为100-110μg/,pH控制在7.0±1.0的模拟水体,在实施例1-6及对比例1-3所得材料分别投入相同重量的模拟测试水体中,投量为1g/L,投入30分钟后,进行测试,下表为测试结果。Take the simulated water body with cyanobacterial chlorophyll content of 100-110 μg/, pH controlled at 7.0±1.0, and put the materials obtained in Examples 1-6 and Comparative Examples 1-3 into the simulated test water body of the same weight, and the dosage is 1g/L , 30 minutes later, the test is carried out. The following table shows the test results.
Figure PCTCN2021115776-appb-000001
Figure PCTCN2021115776-appb-000001
Figure PCTCN2021115776-appb-000002
Figure PCTCN2021115776-appb-000002
经过分析,对比例1至对比例3中分别采用未改性、单独热碱改性、单独氯化铝改性,所得产物应用于藻类治理中,其藻类去除率与实施例1-6相比,数值明显偏低,及对于藻类治理的效果远不如本申请中的产物对藻类处理的效果,因此可以得出结论,即通过本申请的方法制得的改性凹土,在藻类治理中相比现有技术具有相对较好的应用效果。After analysis, in Comparative Example 1 to Comparative Example 3, unmodified, single thermal alkali modification, and single aluminum chloride modification were respectively used, and the obtained products were used in algae treatment, and the algae removal rate was compared with that of Examples 1-6. , the value is obviously low, and the effect on algae treatment is far less than the effect of the product in this application on algae treatment, so it can be concluded that the modified attapulgite prepared by the method of this application is comparable in algae treatment. It has a relatively better application effect than the prior art.
经过对比实施例1-6,可以看出虽然对凹土进行改性的材料比例和温度有些许差异,但其应用于藻类治理所取得的效果都很接近。By comparing Examples 1-6, it can be seen that although the material ratio and temperature of the modified attapulgite are slightly different, the effects obtained when applied to algae treatment are very similar.
综上所述,采用本申请的凹土改性方法对凹土进行改性,使得改性后的凹土在藻类治理领域相比现有技术具有较优的应用效果。且凹土的价格低廉,适用成本低;本方法中的改性试剂对于环境来说,也不会造成污染,在藻类治理领域具有明显的优势。To sum up, the attapulgite modification method of the present application is used to modify the attapulgite, so that the modified attapulgite has a better application effect in the field of algae treatment than the prior art. In addition, the attapulgite has low price and low applicable cost; the modification reagent in this method does not cause pollution to the environment, and has obvious advantages in the field of algae treatment.
对于本领域技术人员而言,显然本发明不限于上述示范性实施例的细节,而且在不背离本发明的精神或基本特征的情况下,能够以其他的具体形式实现本发明。因此,无论从哪一点来看,均应将实施例看作是示范性的,而且是非限制性的,本发明的范围由所附权利要求而不是上述说明限定,因此旨在将落在权利要求的等同要件的含义和范围内的所有变化囊括在本发明内。不应将权利要求中的任何附图标 记视为限制所涉及的权利要求。It will be apparent to those skilled in the art that the present invention is not limited to the details of the above-described exemplary embodiments, but that the present invention may be embodied in other specific forms without departing from the spirit or essential characteristics of the invention. Therefore, the embodiments are to be regarded in all respects as illustrative and not restrictive, and the scope of the invention is to be defined by the appended claims rather than the foregoing description, which are therefore intended to fall within the scope of the claims. All changes within the meaning and range of the equivalents of , are included in the present invention. Any reference signs in the claims shall not be construed as limiting the involved claim.
此外,应当理解,虽然本说明书按照实施例加以描述,但并非每个实施例仅包含一个独立的技术方案,说明书的这种叙述方式仅仅是为清楚起见,本领域技术人员应当将说明书作为一个整体,各实施例中的技术方案也可以经适当组合,形成本领域技术人员可以理解的其他实施方式In addition, it should be understood that although this specification is described in terms of embodiments, not every embodiment only includes an independent technical solution, and this description in the specification is only for the sake of clarity, and those skilled in the art should take the specification as a whole , the technical solutions in each embodiment can also be appropriately combined to form other embodiments that can be understood by those skilled in the art
最后应说明的是:在本发明的描述中,需要说明的是,术语“竖直”、“上”、“下”、“水平”等指示的方位或位置关系为基于附图所示的方位或位置关系,仅是为了便于描述本发明和简化描述,而不是指示或暗示所指的装置或元件必须具有特定的方位、以特定的方位构造和操作,因此不能理解为对本发明的限制。Finally, it should be noted that: in the description of the present invention, it should be noted that the orientations or positional relationships indicated by the terms "vertical", "upper", "lower", "horizontal", etc. are based on the orientations shown in the accompanying drawings Or the positional relationship is only for the convenience of describing the present invention and simplifying the description, rather than indicating or implying that the indicated device or element must have a specific orientation, be constructed and operated in a specific orientation, and therefore should not be construed as a limitation of the present invention.
在本发明的描述中,还需要说明的是,除非另有明确的规定和限定,术语“设置”、“安装”、“相连”、“连接”应做广义理解,例如,可以是固定连接,也可以是可拆卸连接,或一体地连接;可以是机械连接,也可以是电连接;可以是直接相连,也可以通过中间媒介间接相连,可以是两个元件内部的连通。对于本领域的普通技术人员而言,可以根据具体情况理解上述术语在本发明中的具体含义。In the description of the present invention, it should also be noted that, unless otherwise expressly specified and limited, the terms "arranged", "installed", "connected" and "connected" should be understood in a broad sense, for example, it may be a fixed connection, It can also be a detachable connection, or an integral connection; it can be a mechanical connection or an electrical connection; it can be a direct connection, or an indirect connection through an intermediate medium, or the internal communication between the two components. For those of ordinary skill in the art, the specific meanings of the above terms in the present invention can be understood according to specific situations.
以上所述仅为本发明的优选实施例而已,并不用于限制本发明,尽管参照前述实施例对本发明进行了详细的说明,对于本领域的技术人员来说,其依然可以对前述各实施例所记载的技术方案进行修改,或者对其中部分技术特征进行等同替换。凡在本发明的精神和原则之内,所作的任何修改、等同替换、改进等,均应包含在本发明的保护 范围之内。The above descriptions are only preferred embodiments of the present invention, and are not intended to limit the present invention. Although the present invention has been described in detail with reference to the foregoing embodiments, those skilled in the art can still understand the foregoing embodiments. The technical solutions described are modified, or some technical features thereof are equivalently replaced. Any modification, equivalent replacement, improvement, etc. made within the spirit and principle of the present invention shall be included within the protection scope of the present invention.

Claims (7)

  1. 一种凹土表面改性方法,其特征在于,包括以下步骤:A method for modifying the surface of attapulgite, comprising the following steps:
    S1:以铝离子对凹土晶体中镁进行取代,改善其对藻类的处理性能;S1: Substitute magnesium in attapulgite crystals with aluminum ions to improve its treatment performance against algae;
    S2:铝离子在凹土表面进行聚合,使得凹土表面富含正电荷,加强其混凝效果;S2: The aggregation of aluminum ions on the surface of attapulgite makes the surface of attapulgite rich in positive charges and enhances its coagulation effect;
    S3:将凹土投入至氢氧化钠溶液中,对天然凹土进行热碱改性,获得碱改性凹土;S3: put the attapulgite into the sodium hydroxide solution, and perform thermal alkali modification on the natural attapulgite to obtain the alkali-modified attapulgite;
    S4:在碱改性凹土中加入氯化铝进行反应并聚合,采用氯化铝对凹土表面进行无机改性,获得改性凹土;S4: adding aluminum chloride to the alkali-modified attapulgite for reaction and polymerization, and using aluminum chloride to perform inorganic modification on the surface of the attapulgite to obtain modified attapulgite;
    在上述技术方案中,凹土的热碱改性和氯化铝改性的步骤顺序有限定,在实施中需要对凹土首先实行热、碱改性,然后进一步对凹土进行氯化铝无机改性。In the above technical solution, the step sequence of the thermal alkali modification of attapulgite and the modification of aluminum chloride is limited. In the implementation, it is necessary to first perform thermal and alkali modification on the attapulgite, and then further perform the aluminum chloride inorganic modification on the attapulgite. modified.
  2. 根据权利要求1所述的一种凹土表面改性方法,其特征在于:A kind of attapulgite surface modification method according to claim 1, is characterized in that:
    所述热改性的具体步骤为:根据S4步骤中,将开采的原矿凹土在0℃-500℃下烘培1-3小时,制得热改性凹土。The specific steps of the thermal modification are: according to step S4, the mined raw ore attapulgite is baked at 0°C-500°C for 1-3 hours to prepare thermally modified attapulgite.
  3. 根据权利要求1所述的一种凹土表面改性方法,其特征在于:A kind of attapulgite surface modification method according to claim 1, is characterized in that:
    所述碱改性的具体步骤为,根据S4步骤中,使热改性后凹土、氢氧化钠和溶剂的混合反应体系于常温条件下反应1-3小时,混合反应体系应于搅拌条件下进行。The specific steps of the alkali modification are, according to step S4, the mixed reaction system of the thermally modified attapulgite, sodium hydroxide and solvent is reacted under normal temperature conditions for 1-3 hours, and the mixed reaction system should be stirred under the condition of stirring. conduct.
  4. 根据权利要求3所述的一种凹土表面改性方法,其特征在于:A kind of attapulgite surface modification method according to claim 3, is characterized in that:
    所述搅拌条件转速应为200-500r/min,所述溶剂为去离子水,所述热改性后凹土与氢氧化钠的质量比为(5-10):1。The rotational speed of the stirring conditions should be 200-500 r/min, the solvent is deionized water, and the mass ratio of the thermally modified attapulgite to sodium hydroxide is (5-10):1.
  5. 根据权利要求1所述的一种凹土表面改性方法,其特征在于:A kind of attapulgite surface modification method according to claim 1, is characterized in that:
    所述氯化铝改性的具体步骤为:根据S3步骤中,将热碱改性后凹土、氯化铝和溶剂的混合反应体系于60℃-90℃条件下反应6-10小时。The specific steps of the aluminum chloride modification are: according to step S3, the mixed reaction system of attapulgite, aluminum chloride and solvent after thermal alkali modification is reacted at 60°C-90°C for 6-10 hours.
  6. 根据权利要求5所述的一种凹土表面改性方法,其特征在于:A kind of attapulgite surface modification method according to claim 5, is characterized in that:
    所述混合反应体系应于搅拌条件下进行,所述搅拌条件转速应为200-500r/min,所述溶剂为去离子水。The mixed reaction system should be carried out under stirring conditions, the rotational speed of the stirring conditions should be 200-500 r/min, and the solvent is deionized water.
  7. 根据权利要求5所述的一种凹土表面改性方法,其特征在于:A kind of attapulgite surface modification method according to claim 5, is characterized in that:
    所述氯化铝与溶剂的质量比为(10-30):100,所述碱改性凹土与氯化铝的质量比为(1-3):1。The mass ratio of the aluminum chloride to the solvent is (10-30):100, and the mass ratio of the alkali-modified attapulgite to the aluminum chloride is (1-3):1.
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Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4386010A (en) * 1980-09-02 1983-05-31 Engelhard Corporation Treated attapulgite clay composition
CN102531089A (en) * 2010-12-10 2012-07-04 北京师范大学 Method for treating oxytetracycline waste water with aluminum-modified attapulgite adsorbent
CN109126690A (en) * 2018-10-09 2019-01-04 淮阴工学院 A kind of modification of attapulgite and its denitrification and dephosphorization method
CN112794337A (en) * 2021-02-02 2021-05-14 南京公诚节能新材料研究院有限公司 Attapulgite surface modification method

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102690535A (en) * 2012-06-07 2012-09-26 复旦大学 Organic modified nano-attapulgite particles and preparation method thereof
CN108002472A (en) * 2017-12-25 2018-05-08 芜湖皖江知识产权运营中心有限公司 A kind of preparation method of domestic sewage treating compound
CN108706604B (en) * 2018-07-04 2021-11-23 福建工程学院 Method for preparing modified bentonite by wet method
CN108793178B (en) * 2018-07-28 2022-01-11 塔里木大学 Method for improving vermiculite expansion performance
CN111087068B (en) * 2019-12-24 2022-03-29 南京公诚节能新材料研究院有限公司 Preparation method of biological filter material for water purification treatment

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4386010A (en) * 1980-09-02 1983-05-31 Engelhard Corporation Treated attapulgite clay composition
CN102531089A (en) * 2010-12-10 2012-07-04 北京师范大学 Method for treating oxytetracycline waste water with aluminum-modified attapulgite adsorbent
CN109126690A (en) * 2018-10-09 2019-01-04 淮阴工学院 A kind of modification of attapulgite and its denitrification and dephosphorization method
CN112794337A (en) * 2021-02-02 2021-05-14 南京公诚节能新材料研究院有限公司 Attapulgite surface modification method

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
BAO, XIANG : "Removal of Total Phosphorus from Water by Aluminum Salt Adsorbent Modified by Modified Concave and Convex Rods", ANHUI AGRICULTURAL SCIENCE BULLETIN, vol. 22, no. 19, 15 October 2016 (2016-10-15), pages 28 - 31, XP009538773, ISSN: 1007-7731 *

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