CN104475063A - Method for preparing heavy metal adsorbent - Google Patents
Method for preparing heavy metal adsorbent Download PDFInfo
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- CN104475063A CN104475063A CN201410781269.8A CN201410781269A CN104475063A CN 104475063 A CN104475063 A CN 104475063A CN 201410781269 A CN201410781269 A CN 201410781269A CN 104475063 A CN104475063 A CN 104475063A
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- 229910001385 heavy metal Inorganic materials 0.000 title claims abstract description 25
- 238000000034 method Methods 0.000 title claims abstract description 5
- 239000003463 adsorbent Substances 0.000 title abstract description 16
- 241000609240 Ambelania acida Species 0.000 claims abstract description 53
- 239000010905 bagasse Substances 0.000 claims abstract description 53
- 229920002678 cellulose Polymers 0.000 claims abstract description 48
- 239000001913 cellulose Substances 0.000 claims abstract description 48
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims abstract description 39
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 22
- SMZOUWXMTYCWNB-UHFFFAOYSA-N 2-(2-methoxy-5-methylphenyl)ethanamine Chemical compound COC1=CC=C(C)C=C1CCN SMZOUWXMTYCWNB-UHFFFAOYSA-N 0.000 claims abstract description 20
- NIXOWILDQLNWCW-UHFFFAOYSA-N 2-Propenoic acid Natural products OC(=O)C=C NIXOWILDQLNWCW-UHFFFAOYSA-N 0.000 claims abstract description 20
- 239000012153 distilled water Substances 0.000 claims abstract description 16
- 238000002360 preparation method Methods 0.000 claims abstract description 13
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims abstract description 6
- 230000004913 activation Effects 0.000 claims abstract description 6
- 238000007334 copolymerization reaction Methods 0.000 claims abstract description 6
- 238000006243 chemical reaction Methods 0.000 claims abstract description 5
- 230000003213 activating effect Effects 0.000 claims abstract 3
- 229920000578 graft copolymer Polymers 0.000 claims description 20
- ROOXNKNUYICQNP-UHFFFAOYSA-N ammonium persulfate Chemical compound [NH4+].[NH4+].[O-]S(=O)(=O)OOS([O-])(=O)=O ROOXNKNUYICQNP-UHFFFAOYSA-N 0.000 claims description 12
- 239000000725 suspension Substances 0.000 claims description 10
- 229910001870 ammonium persulfate Inorganic materials 0.000 claims description 6
- 238000000746 purification Methods 0.000 claims description 5
- 238000003756 stirring Methods 0.000 claims description 5
- USHAGKDGDHPEEY-UHFFFAOYSA-L potassium persulfate Chemical group [K+].[K+].[O-]S(=O)(=O)OOS([O-])(=O)=O USHAGKDGDHPEEY-UHFFFAOYSA-L 0.000 claims description 3
- 239000003431 cross linking reagent Substances 0.000 claims description 2
- 238000010298 pulverizing process Methods 0.000 claims description 2
- 238000002604 ultrasonography Methods 0.000 claims description 2
- 239000002250 absorbent Substances 0.000 claims 2
- 230000002745 absorbent Effects 0.000 claims 2
- 238000006386 neutralization reaction Methods 0.000 claims 2
- 238000011017 operating method Methods 0.000 claims 1
- 235000019394 potassium persulphate Nutrition 0.000 claims 1
- 238000012216 screening Methods 0.000 claims 1
- 238000005406 washing Methods 0.000 claims 1
- 238000001179 sorption measurement Methods 0.000 abstract description 13
- 239000003999 initiator Substances 0.000 abstract description 10
- ZIUHHBKFKCYYJD-UHFFFAOYSA-N n,n'-methylenebisacrylamide Chemical compound C=CC(=O)NCNC(=O)C=C ZIUHHBKFKCYYJD-UHFFFAOYSA-N 0.000 abstract description 8
- 239000000835 fiber Substances 0.000 abstract description 6
- 239000000047 product Substances 0.000 abstract description 4
- 230000009257 reactivity Effects 0.000 abstract description 3
- 239000000126 substance Substances 0.000 abstract description 3
- 230000009286 beneficial effect Effects 0.000 abstract description 2
- 210000002421 cell wall Anatomy 0.000 abstract description 2
- CSCPPACGZOOCGX-UHFFFAOYSA-N Acetone Chemical compound CC(C)=O CSCPPACGZOOCGX-UHFFFAOYSA-N 0.000 abstract 2
- 239000003513 alkali Substances 0.000 abstract 1
- 239000012043 crude product Substances 0.000 abstract 1
- 239000010949 copper Substances 0.000 description 5
- 230000007935 neutral effect Effects 0.000 description 4
- 150000002500 ions Chemical class 0.000 description 3
- JPVYNHNXODAKFH-UHFFFAOYSA-N Cu2+ Chemical compound [Cu+2] JPVYNHNXODAKFH-UHFFFAOYSA-N 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 229910001431 copper ion Inorganic materials 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000000706 filtrate Substances 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 238000009616 inductively coupled plasma Methods 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 230000001902 propagating effect Effects 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 238000004611 spectroscopical analysis Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
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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
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/26—Synthetic macromolecular compounds
- B01J20/264—Synthetic macromolecular compounds derived from different types of monomers, e.g. linear or branched copolymers, block copolymers, graft copolymers
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/285—Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
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- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Analytical Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Graft Or Block Polymers (AREA)
Abstract
本发明公开了一种重金属吸附剂的制备方法。方法步骤是:先对蔗渣进行碱处理制备得到蔗渣纤维素;再对蔗渣纤维素进行超声活化,然后依次加入引发剂、NaOH溶液中和后的丙烯酸和N,N’-亚甲基双丙烯酰胺,进行接枝反应,制备得到接枝共聚产物;依次用蒸馏水、无水乙醇洗涤、干燥、粉碎,得到重金属吸附剂的粗产物;再经丙酮抽提,即可得到纯化的重金属吸附剂。本发明的有益效果是:与现有技术相比,对蔗渣纤维进行超声活化处理,使蔗渣纤维细胞壁外层破碎、脱除,增强了蔗渣纤维的化学反应活性,提高了反应接枝率和产物的吸附性能。The invention discloses a preparation method of a heavy metal adsorbent. The steps of the method are: firstly treating the bagasse with alkali to prepare the bagasse cellulose; then ultrasonically activating the bagasse cellulose, and then sequentially adding an initiator, acrylic acid and N,N'-methylenebisacrylamide neutralized by NaOH solution , carry out grafting reaction to prepare the graft copolymerization product; wash with distilled water and absolute ethanol, dry and pulverize in sequence to obtain the crude product of the heavy metal adsorbent; then extract with acetone to obtain the purified heavy metal adsorbent. The beneficial effect of the present invention is: compared with the prior art, the bagasse fiber is subjected to ultrasonic activation treatment, the outer layer of the bagasse fiber cell wall is broken and removed, the chemical reactivity of the bagasse fiber is enhanced, and the reaction grafting rate and product quality are improved. adsorption properties.
Description
技术领域technical field
本发明涉及一种重金属吸附剂的制备领域,具体是一种重金属吸附剂的制备方法。The invention relates to the field of preparation of a heavy metal adsorbent, in particular to a preparation method of a heavy metal adsorbent.
背景技术Background technique
含有重金属离子的工业废水的排放,对环境造成了严重的污染,对人们的身体健康也构成了威胁,因此,移除废水中的重金属离子十分重要。纤维素价廉、易得、对环境友好,因此,纤维素基的重金属离子吸附材料备受研究者的关注。The discharge of industrial wastewater containing heavy metal ions has caused serious pollution to the environment and a threat to people's health. Therefore, it is very important to remove heavy metal ions in wastewater. Cellulose is cheap, easy to obtain, and environmentally friendly. Therefore, cellulose-based heavy metal ion adsorption materials have attracted the attention of researchers.
天然纤维素中,约有70%的晶型结构,使得纤维素的可及度较低,导致纤维素分子上的接枝率较难提高。超声波可以产生机械作用、热作用和空化作用,在液体中传播时,可产生巨大的压强,使纤维细胞壁外层破碎、脱除,增强纤维的化学反应活性,提高反应接枝率和产物的吸附性能。In natural cellulose, about 70% of the crystalline structure makes the accessibility of cellulose lower, making it difficult to increase the grafting rate on cellulose molecules. Ultrasound can produce mechanical action, thermal action and cavitation action. When propagating in liquid, it can generate huge pressure, break and remove the outer layer of fiber cell wall, enhance the chemical reactivity of fiber, and increase the reaction grafting rate and product stability. Adsorption properties.
发明内容Contents of the invention
本发明的目的是提供一种成本低廉、对环境友好且吸附效果优异的重金属吸附剂的制备方法。The object of the present invention is to provide a method for preparing a heavy metal adsorbent with low cost, environmental friendliness and excellent adsorption effect.
本发明解决上述技术问题的技术方案如下:The technical scheme that the present invention solves the problems of the technologies described above is as follows:
一种重金属吸附剂的制备方法,操作步骤如下:A preparation method of a heavy metal adsorbent, the operation steps are as follows:
1.制备蔗渣纤维素:1. Preparation of bagasse cellulose:
将蔗渣粉碎后,用100目筛网筛选,保留细小部分,在蔗渣中加入80~120ml的质量浓度为15~20%的NaOH,在120℃下处理0.5~1.0h,用蒸馏水洗涤至中性,烘干,得到蔗渣纤维素。After pulverizing the bagasse, screen it with a 100-mesh sieve, keep the small parts, add 80-120ml of NaOH with a mass concentration of 15-20% to the bagasse, treat it at 120°C for 0.5-1.0h, wash with distilled water until neutral , dried to obtain bagasse cellulose.
2.蔗渣纤维素的活化:2. Activation of bagasse cellulose:
取步骤1得到的绝干蔗渣纤维素1.0g置于三口瓶中,加入15-18ml蒸馏水,在功率为150~400W的超声条件下反应15~30min,得到活化后的纤维素悬浮液。Take 1.0 g of the absolute-dried bagasse cellulose obtained in step 1 and place it in a three-necked flask, add 15-18 ml of distilled water, and react for 15-30 minutes under ultrasonic conditions with a power of 150-400 W to obtain an activated cellulose suspension.
3.蔗渣纤维素与丙烯酸的接枝共聚反应:3. Graft copolymerization of bagasse cellulose and acrylic acid:
取步骤2得到活化后的蔗渣纤维素悬浮液,加入中和后的丙烯酸;依次加入引发剂和交联剂;控制蔗渣纤维素:引发剂:N,N’-亚甲基双丙烯酰胺的质量比为2:0.1~0.5:0.0~0.05;在60~70℃的水浴锅中搅拌反应1.5~3.0h,得到接枝共聚物。所述的中和后的丙烯酸是将氢氧化钠溶液加入到丙烯酸中,控制氢氧化钠:丙烯酸的质量比为2:3~7。所述引发剂是过硫酸钾或过硫酸铵。Take step 2 to obtain the activated bagasse cellulose suspension, add neutralized acrylic acid; add initiator and crosslinking agent successively; control the quality of bagasse cellulose: initiator: N,N'-methylenebisacrylamide The ratio is 2:0.1~0.5:0.0~0.05; stir and react in a water bath at 60~70°C for 1.5~3.0h to obtain a graft copolymer. The neutralized acrylic acid is obtained by adding sodium hydroxide solution into acrylic acid, and controlling the mass ratio of sodium hydroxide:acrylic acid to be 2:3-7. The initiator is potassium persulfate or ammonium persulfate.
4.接枝共聚物的提纯:4. Purification of graft copolymer:
将步骤3得到的接枝共聚物,依次分别用蒸馏水、无水乙醇洗涤,干燥,粉碎,再将粉碎后的接枝共聚物在60~75℃下抽提24~48h,烘干,得到纯化后的重金属吸附剂。Wash the graft copolymer obtained in step 3 with distilled water and absolute ethanol in turn, dry, and pulverize, then extract the pulverized graft copolymer at 60-75°C for 24-48 hours, and dry to obtain purified heavy metal adsorbent.
本发明的有益效果:Beneficial effects of the present invention:
采用超声波技术对纤维素进行活化处理,增强蔗渣纤维的化学反应活性,提高反应接枝率和产物的吸附性能,提供了一种廉价的重金属吸附剂制备方法。提高了蔗渣的经济附加值,净化受重金属污染的水体。The cellulose is activated by ultrasonic technology, the chemical reactivity of the bagasse fiber is enhanced, the reaction grafting rate and the adsorption performance of the product are improved, and a cheap heavy metal adsorbent preparation method is provided. The economic added value of bagasse is improved, and water bodies polluted by heavy metals are purified.
具体实施方式Detailed ways
下面结合实施例对本发明作进一步说明。The present invention will be further described below in conjunction with embodiment.
实施例1Example 1
一种重金属吸附剂的制备方法,按以下步骤进行:A kind of preparation method of heavy metal adsorbent, carries out according to the following steps:
1.制备蔗渣纤维素:1. Preparation of bagasse cellulose:
将蔗渣粉碎后,用100目筛网筛选,保留细小部分,在蔗渣中加入80ml的15%的NaOH,在120℃下处理0.5h,蒸馏水洗涤至中性,烘干,得到蔗渣纤维素。After crushing the bagasse, sieve it with a 100-mesh sieve to keep the small parts, add 80ml of 15% NaOH to the bagasse, treat at 120°C for 0.5h, wash with distilled water until neutral, and dry to obtain bagasse cellulose.
2.蔗渣纤维素的活化:2. Activation of bagasse cellulose:
取步骤1得到的绝干蔗渣纤维素1.0g置于三口瓶中,加入15ml蒸馏水,在功率为150W的超声条件下反应30min,得到活化后的纤维素悬浮液。Take 1.0 g of the absolute-dried bagasse cellulose obtained in step 1 and place it in a three-necked flask, add 15 ml of distilled water, and react for 30 minutes under ultrasonic conditions with a power of 150 W to obtain an activated cellulose suspension.
3.蔗渣纤维素与丙烯酸的接枝共聚反应:3. Graft copolymerization of bagasse cellulose and acrylic acid:
取步骤2得到的蔗渣纤维素悬浮液,加入中和后的丙烯酸(氢氧化钠:丙烯酸质量比为2:3);依次加入引发剂过硫酸铵和N,N’-亚甲基双丙烯酰胺;控制蔗渣纤维素:引发剂过硫酸铵:N,N’-亚甲基双丙烯酰胺的质量比为2:0.1:0.01;在60℃的水浴锅中搅拌反应1.5h,得到接枝共聚物。Take the bagasse cellulose suspension obtained in step 2, add neutralized acrylic acid (sodium hydroxide:acrylic acid mass ratio is 2:3); add initiator ammonium persulfate and N,N'-methylenebisacrylamide in sequence ; Control bagasse cellulose: initiator ammonium persulfate: N, N'-methylenebisacrylamide mass ratio is 2:0.1:0.01; Stir and react in a water bath at 60°C for 1.5h to obtain a graft copolymer .
4.接枝共聚物的提纯;4. Purification of graft copolymer;
将步骤3得到的接枝共聚物,依次分别用蒸馏水、无水乙醇洗涤,干燥,粉碎,再将粉碎后的接枝共聚物在75℃下抽提24h,烘干,得到纯化后的重金属吸附剂。The graft copolymer obtained in step 3 was washed successively with distilled water and absolute ethanol, dried, and pulverized, and then the pulverized graft copolymer was extracted at 75°C for 24 hours, and dried to obtain the purified heavy metal adsorption agent.
实施例2Example 2
一种重金属吸附剂的制备方法,按以下步骤进行:A kind of preparation method of heavy metal adsorbent, carries out according to the following steps:
1.制备蔗渣纤维素:1. Preparation of bagasse cellulose:
将蔗渣粉碎后,用100目筛网筛选,保留细小部分,在蔗渣中加入100ml的20%的NaOH,在120℃下处理1.0h,蒸馏水洗涤至中性,烘干,得到蔗渣纤维素。After crushing the bagasse, sieve it with a 100-mesh sieve to keep the fine parts, add 100ml of 20% NaOH to the bagasse, treat at 120°C for 1.0h, wash with distilled water until neutral, and dry to obtain bagasse cellulose.
2.蔗渣纤维素的活化:2. Activation of bagasse cellulose:
取步骤1得到的绝干蔗渣纤维素1.0g置于三口瓶中,加入18ml蒸馏水,在功率为300W的超声条件下反应30min,得到活化后的纤维素悬浮液。Take 1.0 g of the absolute-dried bagasse cellulose obtained in step 1 and place it in a three-necked flask, add 18 ml of distilled water, and react for 30 minutes under ultrasonic conditions with a power of 300 W to obtain an activated cellulose suspension.
3.蔗渣纤维素与丙烯酸的接枝共聚反应:3. Graft copolymerization of bagasse cellulose and acrylic acid:
取步骤2得到的蔗渣纤维素悬浮液,加入中和后的丙烯酸(氢氧化钠:丙烯酸质量比为2:5);依次加入引发剂过硫酸钾和N,N’-亚甲基双丙烯酰胺,控制蔗渣纤维素:引发剂:N,N’-亚甲基双丙烯酰胺的质量比为2:0.3:0.03;在70℃的水浴锅中搅拌反应2.0h,得到接枝共聚物。Take the bagasse cellulose suspension obtained in step 2, add neutralized acrylic acid (sodium hydroxide:acrylic acid mass ratio is 2:5); add initiator potassium persulfate and N,N'-methylenebisacrylamide in sequence , control the mass ratio of bagasse cellulose:initiator:N,N'-methylenebisacrylamide to 2:0.3:0.03; stir and react in a water bath at 70°C for 2.0h to obtain a graft copolymer.
(4)接枝共聚物的提纯;(4) purification of graft copolymer;
将步骤(3)得到的接枝共聚物,依次分别用蒸馏水、无水乙醇洗涤,干燥,粉碎,再将粉碎后的接枝共聚物在70℃下抽提48h,烘干,得到纯化后的重金属吸附剂。The graft copolymer obtained in step (3) was washed successively with distilled water and absolute ethanol, dried, and pulverized, and then the pulverized graft copolymer was extracted at 70° C. for 48 hours, and dried to obtain purified heavy metal adsorbent.
实施例3Example 3
一种重金属吸附剂的制备方法,按以下步骤进行:A kind of preparation method of heavy metal adsorbent, carries out according to the following steps:
1.制备蔗渣纤维素:1. Preparation of bagasse cellulose:
将蔗渣粉碎后,用100目筛网筛选,保留细小部分,在蔗渣中加入120ml的20%的NaOH,在120℃下处理1.0h,蒸馏水洗涤至中性,烘干,得到蔗渣纤维素。After crushing the bagasse, sieve it with a 100-mesh sieve to keep the fine parts, add 120ml of 20% NaOH to the bagasse, treat at 120°C for 1.0h, wash with distilled water until neutral, and dry to obtain bagasse cellulose.
2.蔗渣纤维素的活化:2. Activation of bagasse cellulose:
取步骤1得到的绝干蔗渣纤维素1.0g置于三口瓶中,加入18ml蒸馏水,在功率为400W的超声条件下反应30min,得到活化后的纤维素悬浮液。Take 1.0 g of the absolute-dried bagasse cellulose obtained in step 1 and place it in a three-necked flask, add 18 ml of distilled water, and react for 30 minutes under ultrasonic conditions with a power of 400 W to obtain an activated cellulose suspension.
3.蔗渣纤维素与丙烯酸的接枝共聚反应:3. Graft copolymerization of bagasse cellulose and acrylic acid:
取步骤2得到的蔗渣纤维素悬浮液,加入中和后的丙烯酸(氢氧化钠:丙烯酸质量比为2:7);依次加入引发剂过硫酸铵和N,N’-亚甲基双丙烯酰胺;控制蔗渣纤维素:引发剂过硫酸铵:N,N’-亚甲基双丙烯酰胺的质量比为2:0.5:0.05;在70℃的水浴锅中搅拌反应3.0h,得到接枝共聚物。Take the bagasse cellulose suspension obtained in step 2, add neutralized acrylic acid (sodium hydroxide: acrylic acid mass ratio is 2:7); add initiator ammonium persulfate and N,N'-methylenebisacrylamide successively ; Control bagasse cellulose: the mass ratio of initiator ammonium persulfate: N,N'-methylenebisacrylamide is 2:0.5:0.05; stir and react in a water bath at 70°C for 3.0h to obtain a graft copolymer .
4.接枝共聚物的提纯;4. Purification of graft copolymer;
将步骤3得到的接枝共聚物,依次分别用蒸馏水、无水乙醇洗涤,干燥,粉碎,再将粉碎后的接枝共聚物在70℃下抽提24h,烘干,得到纯化后的重金属吸附剂。The graft copolymer obtained in step 3 was washed with distilled water and absolute ethanol in sequence, dried, and pulverized, and then the pulverized graft copolymer was extracted at 70°C for 24 hours, and dried to obtain the purified heavy metal adsorption agent.
实施例4Example 4
重金属吸附剂的应用:Application of heavy metal adsorbent:
以重金属铜作吸附试验。The heavy metal copper was used for adsorption test.
取0.1000g实施例2制备的重金属吸附剂于250ml锥形瓶中,加入浓度为150mg/L铜离子溶液,在常温下,转速150r/min的水浴振荡器中震荡0.5h,过滤,取30ml清液,用电感耦合等离子光谱法测量溶液中所剩余的铜离子含量,根据以下公式算出吸附量和吸附率:Get 0.1000g of the heavy metal adsorbent prepared in Example 2 in a 250ml Erlenmeyer flask, add a concentration of 150mg/L copper ion solution, shake for 0.5h in a water bath oscillator with a rotating speed of 150r/min at normal temperature, filter, and take 30ml of clear solution, measure the remaining copper ion content in the solution by inductively coupled plasma spectrometry, and calculate the adsorption capacity and adsorption rate according to the following formula:
式中:In the formula:
q——单位质量高吸水树脂对Cu2+的吸附量,mg/g;q——the adsorption capacity of superabsorbent resin on Cu 2+ per unit mass, mg/g;
η——Cu2+的去除率,%;η——Cu 2+ removal rate, %;
C0——Cu2+的初始浓度,mg/L;C 0 ——the initial concentration of Cu 2+ , mg/L;
C——过滤后滤液中Cu2+的浓度,mg/L;C - the concentration of Cu 2+ in the filtrate after filtration, mg/L;
V——溶液的体积,L;V - the volume of the solution, L;
实验结果:吸附量为82.98mg/g,吸附率为98.34%。Experimental results: The adsorption capacity is 82.98mg/g, and the adsorption rate is 98.34%.
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