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CN102125819A - Iron-loaded cotton fiber material and preparation method thereof - Google Patents

Iron-loaded cotton fiber material and preparation method thereof Download PDF

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CN102125819A
CN102125819A CN 201110051205 CN201110051205A CN102125819A CN 102125819 A CN102125819 A CN 102125819A CN 201110051205 CN201110051205 CN 201110051205 CN 201110051205 A CN201110051205 A CN 201110051205A CN 102125819 A CN102125819 A CN 102125819A
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iron
loaded
fiber
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fiber material
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CN102125819B (en
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赵亮
张小转
黄做华
沙保峰
赵东
韩福娇
曹继红
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Institute of Chemistry Henan Academy of Sciences Co Ltd
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Abstract

本发明公开了一种以脱脂棉纤维为基础骨架的载铁棉纤维材料及其制备方法,属于高分子材料技术领域。该纤维材料的结构中含有以无定形态存在的铁的氢氧化物。其制备方法:以脱脂棉纤维做为基础骨架,三价铁盐溶液经过分散、水解载入,使纤维结构中含有以无定形态存在的铁的氢氧化物。反应过程简单,条件温和,所用反应试剂无毒,环境友好。该纤维材料保持了脱脂棉纤维的纤维状形态,在空气中性能稳定,作为吸附剂在水中使用时不会引起水体的pH值变化,吸附剂载铁形态稳定,能够有效地吸附水体中的亚砷酸根离子。

The invention discloses an iron-loaded wool fiber material with absorbent cotton fiber as the basic skeleton and a preparation method thereof, belonging to the technical field of polymer materials. The structure of the fibrous material contains iron hydroxide in an amorphous state. The preparation method is as follows: the absorbent cotton fiber is used as the basic skeleton, and the trivalent iron salt solution is dispersed and hydrolyzed, so that the fiber structure contains iron hydroxide in an amorphous form. The reaction process is simple, the conditions are mild, the reaction reagents used are non-toxic, and the environment is friendly. The fiber material maintains the fibrous shape of absorbent cotton fibers, and has stable performance in the air. When used as an adsorbent in water, it will not cause changes in the pH value of the water body. The adsorbent has a stable form of iron and can effectively adsorb arsenic in water Acid ion.

Description

一种载铁棉纤维材料及其制备方法A kind of iron wool fiber material and preparation method thereof

技术领域technical field

本发明涉及一种纤维状材料,尤其涉及一种载铁棉纤维材料及其制备方法,属于高分子材料技术领域。The invention relates to a fibrous material, in particular to an iron-loaded wool fiber material and a preparation method thereof, belonging to the technical field of polymer materials.

背景技术Background technique

由于某些金属氧化物或者氢氧化物对砷和氟等无机离子具有较强的吸附去除能力,因此,将这些金属氧化物或者氢氧化物负载在一些载体上,从而制备出一些负载金属氧化物或者氢氧化物的无机阴离子吸附材料已成为本领域研究热点。目前,用于载铁吸附剂的载体材料基本上可以分为:(1)天然矿物和无机材料。如CN200610078899“一种用于除砷的四方硫酸盐纤铁矿吸附剂的制备方法”,CN200610008135“一种铁锰复合氧化物/硅藻土吸附剂的制备、使用及再生方法”及闫英桃等报道了一种载铁硅胶的制备方法(长安大学学报,2004年03期);(2)活性炭及活性炭纤维。如CN200510110226“载铁活性炭除砷吸附剂的制备方法”,HRISTOVSKI etc. (Journal of Environmental Science and Health, Part A (2009) 44, 354–361) 和Zhang etc. (Carbon,Volume 48, Issue 1, January 2010, Pages 60-67) 文献涉及以活性炭纤维为载体制备载铁吸附剂如KIM etc. (Journal of Environmental Science and Health, Part A (2010) 45, 177–182), 涉及以粒状活性炭为载体制备吸附剂。(3)天然高分子材料。如CN1593745A“载铁球形纤维素吸附剂及其制备和应用”,CN1589959A“高选择性的载铁配位体交换棉纤维吸附剂的制备方法”,Guo etc.(Environ. Sci. Technol., 2005, 39 (17), pp 6808–6818),研究了以棉纤维素为基体材料制备吸附剂,Altundogan etc. (Process Biochemistry.,Volume 40, Issues 3-4, March 2005, Pages 1443-1452 ) 将铁负载在甜菜碱浆上,制备载铁吸附剂,Dupont etc. (Environmental Chemistry Letters, Volume 5, Number 3 / 2007年8月) 以木质纤维素为载体制备吸附剂,Katsutoshi etc.(Kagaku Kogaku Ronbunshu, VOL.29;NO.3;PAGE.389-394(2003)) 以交联的果胶酸为载体制备吸附剂。(4)改性后的高分子材料。如CN200910028414“载铁系双金属纳米复合阳离子交换树脂及其制备方法和应用”;Rau etc. (Journal of Radioanalytical and Nuclear Chemistry,Volume 246, Number 3 / 2000年12月),Shao etc. (Hydrometallurgy, Volume 91, Issues 1-4, March 2008, Pages 138-143),Pan etc. (Water Research, 44 (2010) 815–824)以树脂材料为载体制备了吸附剂;Lin etc. (Environmental Engineering Science, Volume 26, Number 11, 2009), Vatutsina etc. (Reactive & Functional Polymers 67 (2007) 184–201), 以功能性高分子纤维材料为载体制备了吸附剂等。Because certain metal oxides or hydroxides have strong adsorption and removal capabilities for inorganic ions such as arsenic and fluorine, these metal oxides or hydroxides are loaded on some carriers to prepare some supported metal oxides. Or the inorganic anion adsorption material of hydroxide has become a research hotspot in this field. At present, the carrier materials used for iron-loaded adsorbents can basically be divided into: (1) natural minerals and inorganic materials. For example, CN200610078899 "a preparation method of tetragonal sulfate lepidosite adsorbent for arsenic removal", CN200610008135 "preparation, use and regeneration method of an iron-manganese composite oxide/diatomite adsorbent" and reports by Yan Yingtao, etc. A preparation method of iron-loaded silica gel (Journal of Chang'an University, Issue 03, 2004); (2) Activated carbon and activated carbon fiber. Such as CN200510110226 "preparation method of iron-loaded activated carbon arsenic removal adsorbent", HRISTOVSKI etc. (Journal of Environmental Science and Health, Part A (2009) 44, 354–361) and Zhang etc. (Carbon, Volume 48, Issue 1, January 2010, Pages 60-67) The literature involves the preparation of iron-loaded adsorbents such as KIM etc. (Journal of Environmental Science and Health, Part A (2010) 45, 177–182) with activated carbon fibers as the carrier Prepare the sorbent. (3) Natural polymer materials. Such as CN1593745A "iron-loaded spherical cellulose adsorbent and its preparation and application", CN1589959A "preparation method of highly selective iron-loaded ligand exchange cotton fiber adsorbent", Guo etc. (Environ. Sci. Technol., 2005 , 39 (17), pp 6808–6818), studied the preparation of adsorbents based on cotton cellulose, Altundogan etc. (Process Biochemistry.,Volume 40, Issues 3-4, March 2005, Pages 1443-1452 ) will Iron loaded on betaine pulp, preparation of iron-loaded sorbent, Dupont etc. (Environmental Chemistry Letters, Volume 5, Number 3 / August 2007) Preparation of sorbent with lignocellulose as carrier, Katsutoshi etc. (Kagaku Kogaku Ronbunshu , VOL.29;NO.3;PAGE.389-394(2003)) Preparation of adsorbent with cross-linked pectinic acid as carrier. (4) Modified polymer materials. Such as CN200910028414 "iron-loaded bimetallic nanocomposite cation exchange resin and its preparation method and application"; Rau etc. (Journal of Radioanalytical and Nuclear Chemistry, Volume 246, Number 3 / December 2000), Shao etc. (Hydrometallurgy, Volume 91, Issues 1-4, March 2008, Pages 138-143), Pan etc. (Water Research, 44 (2010) 815–824) prepared adsorbents with resin materials as carriers; Lin etc. (Environmental Engineering Science, Volume 26, Number 11, 2009), Vatutsina etc. (Reactive & Functional Polymers 67 (2007) 184–201), prepared adsorbents with functional polymer fiber materials as carriers.

在上述载体材料中,由于棉纤维是一种天然、可再生材料,该载体亲水性好,孔隙度大,已经广泛用作生物活性材料。以棉纤维作为载铁材料载铁,在目前的研究中,多通过交联,以球状纤维素为载体载铁,如CN1593745A,CN1589959A,Guo etc.(Environ. Sci. Technol., 2005, 39 (17), pp 6808–6818)等中所报道。而对于以棉纤维为载体,不改变棉纤维材料的纤维状态,将铁负载在棉纤维材料上的研究比较少。目前,由于纤维状材料的蓬勃发展和明显的独特优势如比表面积大、流通阻力小、可以多种形式应用等,使得载铁纤维状吸附材料将具有较大的应用开发潜力。Among the above-mentioned carrier materials, since cotton fiber is a natural and renewable material, the carrier has good hydrophilicity and large porosity, and has been widely used as a bioactive material. Cotton fiber is used as the iron-carrying material to carry iron. In the current research, iron is carried by spherical cellulose as the carrier, such as CN1593745A, CN1589959A, Guo etc. (Environ. Sci. Technol., 2005, 39 ( 17), pp 6808–6818) et al. However, there are relatively few studies on loading iron on cotton fiber materials without changing the fiber state of cotton fiber materials. At present, due to the vigorous development of fibrous materials and obvious unique advantages such as large specific surface area, small flow resistance, and application in various forms, iron-carrying fibrous adsorbent materials will have great potential for application and development.

发明内容Contents of the invention

本发明目的在于提供一种不改变棉纤维材料的纤维状态兼有亲水性强、机械性能好、吸附效果好的载铁纤维吸附剂;本发明另一目的在于提供其制备方法。The purpose of the present invention is to provide an iron-loaded fiber adsorbent that does not change the fiber state of the cotton fiber material and has strong hydrophilicity, good mechanical properties and good adsorption effect; another purpose of the present invention is to provide its preparation method.

为实现本发明目的,以天然高分子材料棉纤维为载体,通过简单、温和、环境友好的合成路线,制备一种铁含量高的载铁纤维吸附剂以实现本发明技术方案。In order to realize the object of the present invention, a kind of iron-loaded fiber adsorbent with high iron content is prepared to realize the technical scheme of the present invention by using natural polymer material cotton fiber as a carrier through a simple, mild and environment-friendly synthetic route.

本发明载铁纤维吸附剂以脱脂棉纤维作为基础骨架,含有以无定形态存在的氢氧化铁,并且保持了脱脂棉纤维的纤维状形态。The iron-carrying fiber adsorbent of the present invention uses the absorbent cotton fiber as a basic skeleton, contains iron hydroxide existing in an amorphous state, and maintains the fibrous shape of the absorbent cotton fiber.

其合成方法为:将脱脂棉纤维水洗,浸泡在质量百分比为2%~10%、温度为10~50℃的三价铁水溶液中,经过1~3小时后,搅拌,逐滴加入0.5~2M的碱溶液,三价铁盐经分散、水解载入脱脂棉,在空气中静置3~8小时后,用水洗至中性,于30~80℃烘干。铁含量随着载铁次数的增加而增加,纤维增重控制在10%~40%。The synthesis method is as follows: wash the absorbent cotton fiber with water, soak it in the ferric iron aqueous solution with a mass percentage of 2%~10% and a temperature of 10~50°C, stir after 1~3 hours, and add 0.5~2M Alkali solution and ferric salt are dispersed and hydrolyzed, loaded into absorbent cotton, left to stand in the air for 3-8 hours, washed with water until neutral, and dried at 30-80°C. The iron content increases with the increase of iron loading times, and the fiber weight gain is controlled at 10%~40%.

本发明所采用的脱脂棉纤维是市售商品级脱脂棉,单丝长度在3~7cm,抗拉强力为0.021~0.054N。所用三价铁溶液为氯化铁、硫酸铁、硝酸铁溶液等。所用碱溶液为氢氧化钠、氨水等。三价铁水溶液与碱溶液最大体积比为1:3。The absorbent cotton fiber used in the present invention is a commercially available commercial grade absorbent cotton, the length of the monofilament is 3-7cm, and the tensile strength is 0.021-0.054N. The ferric iron solution used is ferric chloride, ferric sulfate, ferric nitrate solution and the like. The alkali solution used is sodium hydroxide, ammonia water, etc. The maximum volume ratio of ferric iron solution to alkali solution is 1:3.

本发明有益效果在于:(1)原材料脱脂棉纤维来源广泛,性能质量稳定。(2)反应过程简便易控制,反应条件温和,无需增加压力和太高的反应温度,便于工业化生产。(3)不使用有机交联剂,避免了有毒试剂的污染;所用反应试剂便宜易得、无毒。(4)反应所得产品是载铁的纤维状吸附材料。纤维吸附材料与颗粒状或球状吸附材料相比,具有比表面积大,流通阻力小,机械强度好,容易洗脱再生,可加工成多种形式(纤维束、无纺布、织物等)等优点。(5)该材料中含有较多的无定形态铁的氢氧化物,具有较多的活性吸附位点,对于水体中的亚砷酸污染物具有较强的吸附能力,饱和容量为13~25 mg/g纤维。(6)该材料在空气中性能稳定,无需要特殊的保存方法,使用时不会影响水体的pH变化。The beneficial effects of the present invention are: (1) The raw material absorbent cotton fiber has a wide range of sources and stable performance and quality. (2) The reaction process is simple and easy to control, the reaction conditions are mild, there is no need to increase pressure and too high reaction temperature, and it is convenient for industrial production. (3) No organic cross-linking agent is used to avoid the pollution of toxic reagents; the reagents used are cheap, easy to obtain and non-toxic. (4) The product obtained from the reaction is a fibrous adsorption material loaded with iron. Compared with granular or spherical adsorption materials, fiber adsorption materials have the advantages of large specific surface area, small flow resistance, good mechanical strength, easy elution and regeneration, and can be processed into various forms (fiber bundles, non-woven fabrics, fabrics, etc.) . (5) The material contains more hydroxides of amorphous iron, has more active adsorption sites, and has a strong adsorption capacity for arsenous acid pollutants in water bodies, with a saturation capacity of 13-25 mg/g fiber. (6) The material is stable in the air, no special storage method is required, and the pH change of the water body will not be affected when used.

附图说明:Description of drawings:

图1为本发明载铁棉纤维材料与原材料脱脂棉纤维的XRD光谱对比。其中曲线1为载铁棉纤维;曲线2为原脱脂棉纤维。Fig. 1 is the comparison of the XRD spectra of the iron-loaded wool fiber material of the present invention and the raw material absorbent cotton fiber. Among them, curve 1 is the iron-loaded cotton fiber; curve 2 is the original absorbent cotton fiber.

图2为本发明载铁棉纤维材料与原材料脱脂棉纤维的显微镜照片(×400)。其中a图为原脱脂棉纤维;b图为载铁棉纤维。Fig. 2 is a microscope photo (×400) of iron-loaded wool fiber material and raw material absorbent cotton fiber of the present invention. Among them, the picture a is the original absorbent cotton fiber; the picture b is the iron-loaded cotton fiber.

图3 为经本发明载铁棉纤维材料处理后出水中砷(III)浓度与处理水量的吸附曲线。Figure 3 is the adsorption curve of the arsenic (III) concentration in the effluent water and the amount of treated water after being treated with the iron-loaded wool fiber material of the present invention.

图4 为经本发明载铁棉纤维材料处理后出水中砷(III)浓度与处理水量的吸附曲线。Figure 4 is the adsorption curve of the arsenic (III) concentration in the effluent and the amount of treated water after being treated with the iron-loaded wool fiber material of the present invention.

具体实施方式Detailed ways

为更好地对本发明进行详细说明,举实施例如下:For better describing the present invention in detail, give examples as follows:

实施例1Example 1

将6g脱脂棉纤维浸没在100mL5%的氯化铁溶液中,升温至30℃,2小时后,搅拌下逐滴加入1M的氢氧化钠溶液 105mL,加入速度控制在1ml/min。当溶液的pH值升至4时,停止氢氧化钠的加入,倾倒出溶液,用水清洗纤维数次后,重复上述氢氧化钠的加入过程6次。载铁结束后,静置5小时,然后取出,用水洗至中性,在45℃的烘箱中烘干,称重后纤维增重27.8%。其XRD光谱和显微镜照片分别如附图1和附图2所示。从图1可以看出,载铁纤维中的铁以无定形的氢氧化物形式存在;从图2可以看出,脱脂棉载铁之后,仍然保持原纤维状形态。Submerge 6g of absorbent cotton fibers in 100mL of 5% ferric chloride solution, raise the temperature to 30°C, and after 2 hours, add 105mL of 1M sodium hydroxide solution dropwise with stirring, and the adding speed is controlled at 1ml/min. When the pH value of the solution rose to 4, the addition of sodium hydroxide was stopped, the solution was poured out, and the fiber was washed with water several times, and the above-mentioned addition process of sodium hydroxide was repeated 6 times. After loading the iron, let it stand for 5 hours, then take it out, wash it with water until it is neutral, and dry it in an oven at 45°C. After weighing, the weight of the fiber increases by 27.8%. Its XRD spectrum and micrograph are shown in accompanying drawing 1 and accompanying drawing 2 respectively. It can be seen from Figure 1 that the iron in the iron-loaded fiber exists in the form of amorphous hydroxide; it can be seen from Figure 2 that after the absorbent cotton is loaded with iron, it still maintains a fibril shape.

实施例2Example 2

将350g脱脂棉纤维浸没在2000mL 10%的硫酸铁溶液中,升温至25℃,3小时后,搅拌下逐滴加入0.5M的氢氧化钠溶液2050 mL,加入速度控制在20ml/min。当溶液的pH值升至4时,停止氢氧化钠的加入,倾倒出溶液,用水清洗纤维数次后,重复上述氢氧化钠的加入过程6次。载铁结束后,静置5小时,然后取出,用水洗至中性,在60℃的烘箱中烘干,称重后纤维增重16.9%。其XRD光谱和显微镜照片如实施例1。Submerge 350g of absorbent cotton fibers in 2000mL of 10% ferric sulfate solution, raise the temperature to 25°C, and after 3 hours, add 2050mL of 0.5M sodium hydroxide solution dropwise under stirring, and the adding speed is controlled at 20ml/min. When the pH value of the solution rose to 4, the addition of sodium hydroxide was stopped, the solution was poured out, and the fiber was washed with water several times, and the above-mentioned addition process of sodium hydroxide was repeated 6 times. After loading the iron, let it stand for 5 hours, then take it out, wash it with water until neutral, and dry it in an oven at 60°C. After weighing, the weight of the fiber increases by 16.9%. Its XRD spectrum and micrograph are as embodiment 1.

应用例1Application example 1

称取实施例1中制得的纤维材料0.1g,放入50ml用亚砷酸钠配制的砷浓度为100mg/L的水样中,于25℃振荡吸附12小时,测得溶液中的砷浓度降为50.6mg/L,计算得该纤维材料对砷的吸附量为24.7mg/g纤维。Weigh 0.1 g of the fiber material prepared in Example 1, put it into 50 ml of water sample with an arsenic concentration of 100 mg/L prepared with sodium arsenite, shake and adsorb at 25° C. for 12 hours, and measure the arsenic concentration in the solution Reduced to 50.6mg/L, the calculated arsenic adsorption of the fiber material is 24.7mg/g fiber.

应用例2Application example 2

称取实施例2中制得的纤维材料0.1g,放入50ml用亚砷酸钠配制的砷浓度为100mg/L的水样中,于25℃振荡吸附12小时,测得溶液中的砷浓度降为59.3mg/L,计算得该纤维材料对砷的吸附量为20.3mg/g纤维。Weigh 0.1 g of the fiber material prepared in Example 2, put it into 50 ml of water sample with arsenic concentration of 100 mg/L prepared with sodium arsenite, and shake and adsorb for 12 hours at 25 ° C to measure the arsenic concentration in the solution Reduced to 59.3mg/L, the calculated arsenic adsorption of the fiber material is 20.3mg/g fiber.

应用例3Application example 3

称取实施例1中制得的纤维材料2g,填装成高度为10cm、直径为1cm的吸附柱,将砷(III)浓度为1mg/L的水样以1mL/min的流速通过吸附柱,进水pH=6.96,监测出水的砷浓度,当处理水量在40.3L以内时,出水的砷浓度低于50mg/L,出水pH=6.93。吸附曲线如附图3。并通过检测进出水中铁离子浓度,表明该载铁吸附剂载铁形态稳定。Take by weighing 2 g of the fiber material prepared in Example 1, fill it into an adsorption column with a height of 10 cm and a diameter of 1 cm, and a water sample with an arsenic (III) concentration of 1 mg/L passes through the adsorption column at a flow rate of 1 mL/min. Influent pH=6.96, monitor the arsenic concentration in the effluent, when the treated water volume is within 40.3L, the arsenic concentration in the effluent is lower than 50mg/L, and the effluent pH=6.93. The adsorption curve is shown in Figure 3. And by detecting the concentration of iron ions in the influent and effluent water, it is shown that the iron-carrying adsorbent is stable in form.

应用例4Application example 4

称取实施例2中制得的纤维材料2g,填装成高度为10cm、直径为1cm的吸附柱,将砷(III)浓度为1mg/L的水样以1mL/min的流速通过吸附柱,进水pH=6.96,监测出水的砷浓度,当处理水量在35.8L以内时,出水的砷浓度低于50mg/L,出水pH=6.92。吸附曲线如附图4。并通过检测进出水中铁离子浓度,表明该载铁吸附剂载铁形态稳定。Take by weighing 2 g of the fiber material obtained in Example 2, fill it into an adsorption column with a height of 10 cm and a diameter of 1 cm, and a water sample with arsenic (III) concentration of 1 mg/L passes through the adsorption column at a flow rate of 1 mL/min. Influent pH=6.96, monitor the arsenic concentration in the effluent, when the treated water volume is within 35.8L, the arsenic concentration in the effluent is lower than 50mg/L, and the effluent pH=6.92. The adsorption curve is shown in Figure 4. And by detecting the concentration of iron ions in the influent and effluent water, it is shown that the iron-carrying adsorbent is stable in form.

Claims (5)

1.一种载铁棉纤维材料,其特征在于:以脱脂棉纤维作为基础骨架,含有以无定形态存在的氢氧化铁,并且保持了脱脂棉纤维的纤维状形态。1. An iron-loaded cotton fiber material is characterized in that: take the absorbent cotton fiber as the basic skeleton, contain iron hydroxide existing in an amorphous state, and keep the fibrous form of the absorbent cotton fiber. 2.如权利要求1所述的载铁棉纤维材料,其特征在于:所用脱脂棉单丝长度为 3~7 cm,抗拉强力为0.021~0.054N。2. The iron-loaded wool fiber material as claimed in claim 1, characterized in that: the monofilament length of the absorbent cotton used is 3-7 cm, and the tensile strength is 0.021-0.054N. 3.如权利要求1或2所述的载铁棉纤维材料的制备方法,其特征在于:通过如下步骤实现:将脱脂棉纤维水洗,浸泡在质量百分比为2%~10%、温度为10~50℃的三价铁水溶液中,经过1~3小时后,搅拌,逐滴加入0.5~2M的碱溶液,三价铁盐经分散、水解载入脱脂棉,在空气中静置3~8小时后,用水洗至中性,于30~80℃烘干。3. the preparation method of iron-loaded wool fiber material as claimed in claim 1 or 2, is characterized in that: realize by the following steps: the degreasing cotton fiber is washed, soaked in the mass percentage is 2%~10%, temperature is 10~50 After 1~3 hours in the aqueous solution of ferric iron at ℃, stir, and add 0.5~2M alkali solution drop by drop. Wash with water until neutral, and dry at 30~80°C. 4.如权利要求3所述的载铁棉纤维材料的制备方法,其特征在于:三价铁水溶液与碱溶液最大体积比为 1:3。4. The preparation method of iron-loaded wool fiber material as claimed in claim 3, characterized in that: the maximum volume ratio of the ferric iron solution to the alkali solution is 1:3. 5.如权利要求3所述的载铁棉纤维材料的制备方法,其特征在于:纤维增重控制在10%~40%。5. The preparation method of iron-loaded wool fiber material as claimed in claim 3, characterized in that: fiber weight gain is controlled at 10%-40%.
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CN105344332A (en) * 2015-11-04 2016-02-24 苏州书瑞环保科技有限公司 Water treatment arsenic adsorption material and preparation method thereof
CN105797782A (en) * 2016-03-11 2016-07-27 河南师范大学 Iron-loaded cotton fiber-doped nanometer titanium dioxide composite fiber material and preparation method thereof
CN109231280A (en) * 2018-10-12 2019-01-18 山东理工大学 A kind of preparation method of rice-shaped di-iron trioxide composite cotton fabric carbon fibre material
CN115400502A (en) * 2022-09-20 2022-11-29 西安兴晟生态环境有限公司 SPF fiber filter cake material for direct cleaning filter and preparation method thereof

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CN1593745A (en) * 2004-07-05 2005-03-16 南开大学 Ferrum carried spherical cellulose adsorbent, preparation and application thereof
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JP2005058955A (en) * 2003-08-19 2005-03-10 Nippon Steel Chem Co Ltd Treatment method of acid mine wastewater containing arsenic and iron
CN1589959A (en) * 2003-08-28 2005-03-09 王军锋 Preparation method of high selectivity iron carrier ligand exchange cotton fiber adsorbent
CN1593745A (en) * 2004-07-05 2005-03-16 南开大学 Ferrum carried spherical cellulose adsorbent, preparation and application thereof
CN101569854A (en) * 2009-06-05 2009-11-04 河南省科学院化学研究所有限公司 Arsenic adsorbing fiber and synthesizing method thereof

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104084140A (en) * 2014-07-04 2014-10-08 淮海工学院 Adsorbent for heavy metal copper ions in high-salinity wastewater and preparation method of adsorbent
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CN105344332A (en) * 2015-11-04 2016-02-24 苏州书瑞环保科技有限公司 Water treatment arsenic adsorption material and preparation method thereof
CN105797782A (en) * 2016-03-11 2016-07-27 河南师范大学 Iron-loaded cotton fiber-doped nanometer titanium dioxide composite fiber material and preparation method thereof
CN109231280A (en) * 2018-10-12 2019-01-18 山东理工大学 A kind of preparation method of rice-shaped di-iron trioxide composite cotton fabric carbon fibre material
CN115400502A (en) * 2022-09-20 2022-11-29 西安兴晟生态环境有限公司 SPF fiber filter cake material for direct cleaning filter and preparation method thereof

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