CN107456951A - A kind of rice straw adsorbent of modification and its preparation method and application - Google Patents
A kind of rice straw adsorbent of modification and its preparation method and application Download PDFInfo
- Publication number
- CN107456951A CN107456951A CN201710743317.8A CN201710743317A CN107456951A CN 107456951 A CN107456951 A CN 107456951A CN 201710743317 A CN201710743317 A CN 201710743317A CN 107456951 A CN107456951 A CN 107456951A
- Authority
- CN
- China
- Prior art keywords
- rice straw
- adsorbent
- modified
- add
- water
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Classifications
-
- 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
- B01J20/24—Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
-
- 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
- C02F1/286—Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
-
- 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
- B01J2220/00—Aspects relating to sorbent materials
- B01J2220/40—Aspects relating to the composition of sorbent or filter aid materials
- B01J2220/48—Sorbents characterised by the starting material used for their preparation
- B01J2220/4812—Sorbents characterised by the starting material used for their preparation the starting material being of organic character
- B01J2220/4825—Polysaccharides or cellulose materials, e.g. starch, chitin, sawdust, wood, straw, cotton
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
- C02F2101/22—Chromium or chromium compounds, e.g. chromates
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Analytical Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
本发明公开了一种改性的水稻秸秆吸附剂及其制备方法和应用,吸附剂为通过胺基改性的水稻秸秆;制备方法如下:(1)首先将水稻秸秆去除杂质、清洗、烘干后粉碎或研磨,过筛;(2)称取步骤(1)中经处理的水稻秸秆,加入环氧氯丙烷和二甲基甲酰胺,90‑100℃条件下搅拌1‑2h,使其充分反应;随后加入二亚乙基三胺,继续搅拌1‑2h;最后,加入三乙胺,保持温度继续反应2‑3h;将所得材料过滤分离,并用水冲洗干净;(3)将步骤(2)中冲洗干净的材料烘干,即得。本发明中改性吸附剂原料为水稻秸秆,其价格低廉,获取方便;吸附剂通过物理方法吸附去除水中的铬和镍,吸附效率高,整个吸附去除过程中无二次污染物生成,没有对人身有害的物质产生。The invention discloses a modified rice straw adsorbent and its preparation method and application. The adsorbent is rice straw modified by amine groups; the preparation method is as follows: (1) first remove impurities, wash and dry the rice straw Then crush or grind, and sieve; (2) Weigh the treated rice straw in step (1), add epichlorohydrin and dimethylformamide, and stir at 90-100°C for 1-2h to make it fully reaction; then add diethylenetriamine and continue to stir for 1‑2h; finally, add triethylamine and keep the temperature to continue the reaction for 2‑3h; filter the resulting material and rinse it with water; (3) the step (2 ) and dry the rinsed material, that is. The raw material of the modified adsorbent in the present invention is rice straw, which is cheap and easy to obtain; the adsorbent removes chromium and nickel in water through physical methods, and the adsorption efficiency is high. No secondary pollutants are generated during the entire adsorption removal process, and there is no impact Harmful substances produced.
Description
技术领域technical field
本发明属于水处理技术领域,特别涉及一种改性的水稻秸秆吸附剂及其制备方法和应用。The invention belongs to the technical field of water treatment, in particular to a modified rice straw adsorbent and its preparation method and application.
背景技术Background technique
随着工业生产和人类社会的迅猛发展,环境污染问题日益加重。无数的污染物质被排放到水环境中,其中重金属污染物质具有剧毒性或致癌性,且难以进行生物降解。此外,重金属容易在生物体内富集并进而通过食物链累积在生物体或人体中。With the rapid development of industrial production and human society, the problem of environmental pollution has become increasingly serious. Numerous pollutants are discharged into the water environment, among which heavy metal pollutants are highly toxic or carcinogenic and difficult to biodegrade. In addition, heavy metals are easy to accumulate in organisms and then accumulate in organisms or humans through the food chain.
铬和镍离子广泛应用于皮革、电镀、水泥制造、染料工业等。鉴于铬和镍的危害性和它在各种工业生产、制造过程中的广泛应用,从工业废水中有效的去除铬和镍具有重要的意义。去除水体中铬和镍的常用处理方法主要有两类,一类是传统处理方法,包括化学(还原)沉淀法、电化学法、膜过滤法、离子交换法等;一类是吸附法。传统处理方法处理效率低,投资和处理成本较高,且操作不便。而与众多传统处理方法相比,吸附法通常利用吸附材料的多孔性将污水中的有害物质固定在其表面从而加以去除,同时具有无能耗,无二次污染、易于操作等优点。因而寻求成本低廉且吸附效率高的吸附剂极其重要。Chromium and nickel ions are widely used in leather, electroplating, cement manufacturing, dye industry, etc. In view of the harmfulness of chromium and nickel and its wide application in various industrial production and manufacturing processes, it is of great significance to effectively remove chromium and nickel from industrial wastewater. There are two main types of common treatment methods for removing chromium and nickel in water, one is traditional treatment methods, including chemical (reduction) precipitation, electrochemical methods, membrane filtration, ion exchange methods, etc.; the other is adsorption methods. Traditional treatment methods have low treatment efficiency, high investment and treatment costs, and inconvenient operation. Compared with many traditional treatment methods, the adsorption method usually uses the porosity of the adsorption material to fix the harmful substances in the sewage on its surface to remove them. At the same time, it has the advantages of no energy consumption, no secondary pollution, and easy operation. Therefore, it is extremely important to find an adsorbent with low cost and high adsorption efficiency.
近来年,活性炭、石墨烯等工业原料以及他们的改性材料制备的吸附剂多有报道,粉煤灰、废橡胶等工业废料经过处理后对重金属也有一定的吸附作用,我国是农业生产大国,农业领域的研究者也在思考是否可以利用农业废弃材料制备出吸附效果好、易于操作的吸附剂。申请号CN2012105884866的中国专利申请公开了一种油酸改性花生壳吸附剂,将花生壳预处理后利用油酸、正己烷和硫酸对花生壳改性,即得改性后花生壳吸附剂。本申请主要利用羧酸中的羧基与花生壳中的羟基进行酯化反应,酯化生成物在水中电离出的羧基可对重金属离子形成吸附作用,但该申请对重金属铅的吸附效果更好,对铬和镍的处理并未提及。In recent years, there have been many reports on adsorbents prepared from industrial raw materials such as activated carbon and graphene and their modified materials. Industrial waste such as fly ash and waste rubber can also adsorb heavy metals to a certain extent after treatment. my country is a large agricultural production country. Researchers in the field of agriculture are also thinking about whether it is possible to use agricultural waste materials to prepare adsorbents with good adsorption effect and easy operation. The Chinese patent application with the application number CN2012105884866 discloses an oleic acid modified peanut shell adsorbent. After the peanut shell is pretreated, the peanut shell is modified with oleic acid, n-hexane and sulfuric acid to obtain the modified peanut shell adsorbent. This application mainly uses the carboxyl group in the carboxylic acid to carry out the esterification reaction with the hydroxyl group in the peanut shell. The carboxyl group ionized in the water of the esterification product can form an adsorption effect on heavy metal ions, but this application has a better adsorption effect on heavy metal lead. Treatment of chromium and nickel is not mentioned.
发明内容Contents of the invention
针对现有问题的不足,本发明的目的是提供一种改性的水稻秸秆吸附剂及其制备方法和应用,原料易得,制备工艺简单,所得吸附剂具有良好的吸附效果,对于废水中的污染重金属具有良好的吸附、去除效应,可以用于解决现有技术对废水中铬和镍污染物难处理的问题。In view of the deficiencies of the existing problems, the purpose of the present invention is to provide a modified rice straw adsorbent and its preparation method and application. The raw materials are easy to obtain, the preparation process is simple, and the obtained adsorbent has good adsorption effect. Polluted heavy metals have good adsorption and removal effects, and can be used to solve the problem of difficult treatment of chromium and nickel pollutants in wastewater by existing technologies.
为实现上述目的,本发明采用的技术方案为:To achieve the above object, the technical solution adopted in the present invention is:
一种改性的水稻秸秆吸附剂,先将水稻秸秆经粉碎化预处理,再将预处理后的秸秆与改性剂在高温下进行胺基改性反应,清洗、烘干,即得。A modified rice straw adsorbent is prepared by pulverizing and pretreating rice straw, then subjecting the pretreated straw to a modifying agent for amino group modification reaction at high temperature, washing and drying.
一种改性的水稻秸秆吸附剂的制备方法,包括如下步骤:A preparation method of a modified rice straw adsorbent, comprising the steps of:
(1)水稻秸秆的预处理:首先将水稻秸秆去除杂质、清洗、烘干后粉碎或研磨,过筛;(1) Pretreatment of rice stalks: first remove impurities from the rice stalks, wash and dry them, then crush or grind them, and sieve them;
(2)水稻秸秆的改性:称取步骤(1)中经过处理的水稻秸秆,加入改性剂进行高温改性,改性剂的加入顺序是:先加入环氧氯丙烷和二甲基甲酰胺,90-100℃条件下搅拌1-2h,使其充分反应;随后加入二亚乙基三胺,保温继续搅拌1-2h;最后,加入三乙胺,相同温度条件下搅拌2-3h;将所得材料过滤分离,并用水冲洗干净;(2) Modification of rice stalks: Weigh the treated rice stalks in step (1), add modifiers for high-temperature modification, the order of adding modifiers is: first add epichlorohydrin and dimethyl formaldehyde For amides, stir at 90-100°C for 1-2h to make it fully react; then add diethylenetriamine, keep warm and continue stirring for 1-2h; finally, add triethylamine, stir for 2-3h at the same temperature; The resulting material is separated by filtration and rinsed with water;
(3)将步骤(2)中冲洗干净的材料烘干,即得。(3) drying the material rinsed in step (2) to obtain the product.
作为本申请的一种优选技术方案,所述步骤(1)中,水稻秸秆用蒸馏水冲洗后,置于80-100℃的烘箱中烘20-24h,烘干后的秸秆碾碎、研磨后过40-200目筛。As a preferred technical solution of the present application, in the step (1), after the rice stalks are rinsed with distilled water, they are placed in an oven at 80-100° C. for 20-24 hours, and the dried stalks are crushed and ground and then dried 40-200 mesh sieve.
作为本申请的一种优选技术方案,所述步骤(2)中,每称取水稻秸秆的质量9-10g时加入改性剂31-36mL,其中,环氧氯丙烷与二甲基酰胺、二亚乙基三胺、三乙胺的体积比为3~3.6:2.5~3:1~1.2:2.5~3;冲洗用水为去离子水或蒸馏水。As a preferred technical solution of the present application, in the step (2), 31-36 mL of modifier is added every time 9-10 g of rice straw is weighed, wherein epichlorohydrin and dimethylamide, dimethicone The volume ratio of ethylenetriamine and triethylamine is 3-3.6:2.5-3:1-1.2:2.5-3; the washing water is deionized water or distilled water.
作为本申请的一种优选技术方案,所述步骤(2)中采用磁力搅拌器搅拌。As a preferred technical solution of the present application, a magnetic stirrer is used in the step (2) to stir.
作为本申请的一种优选技术方案,所述步骤(3)中,烘干温度为80-100℃,烘干时间为20-24h。As a preferred technical solution of the present application, in the step (3), the drying temperature is 80-100° C., and the drying time is 20-24 hours.
本发明还提供一种利用上述方法制备的改性的水稻秸秆吸附剂在吸附废水中重金属的应用。The present invention also provides an application of the modified rice straw adsorbent prepared by the above method in adsorbing heavy metals in wastewater.
水稻秸秆由纤维素、半纤维素和木质素等组成,可以在溶液中有效吸附重金属,利用废弃农业材料作为吸附剂,不仅能充分利用废弃的资源,而且可以通过改性提高吸附效果作为水处理中的高效吸附剂应用;胺类在酸性环境中很容易质子化,通过静电吸引和离子交换吸附金属离子提高吸附效率。基于上述优良特性,水稻秸秆可以用于铬和镍的吸附,胺基改性后的水稻秸秆具有更优良的吸附性能。Rice straw is composed of cellulose, hemicellulose and lignin, etc., which can effectively adsorb heavy metals in the solution. Using waste agricultural materials as adsorbents can not only make full use of waste resources, but also improve the adsorption effect through modification as water treatment. The application of high-efficiency adsorbents in China; amines are easily protonated in acidic environments, and adsorb metal ions through electrostatic attraction and ion exchange to improve adsorption efficiency. Based on the above excellent properties, rice straw can be used for the adsorption of chromium and nickel, and the rice straw modified with amine group has better adsorption performance.
与现有技术相比,本发明具有以下有益效果:Compared with the prior art, the present invention has the following beneficial effects:
(1)本发明中作为原料的农业材料水稻秸秆,其价格低廉,获取方便;(1) the agricultural material rice stalk used as raw material in the present invention is cheap and easy to obtain;
(2)改性材料无危险性,无污染性,吸附剂制备方法简单易操作;(2) The modified material is non-hazardous and non-polluting, and the preparation method of the adsorbent is simple and easy to operate;
(3)最终的产物通过物理方法吸附去除水中的铬和镍,对铬和镍的吸附效率高,整个吸附去除过程中无二次污染物的生成,没有对人身有害的物质产生;(3) The final product adsorbs and removes chromium and nickel in water through physical methods, and the adsorption efficiency of chromium and nickel is high, and no secondary pollutants are generated during the entire adsorption removal process, and no substances harmful to the human body are produced;
(4)本发明充分利用材料,物尽其用,达到节能环保的目的。(4) The present invention makes full use of materials, makes the best use of everything, and achieves the purpose of energy saving and environmental protection.
具体实施方式detailed description
以下结合实施例对本发明做进一步详细说明。所用试剂或者仪器设备未注明生产厂商的,均视为可以通过市场购买的常规产品。The present invention is described in further detail below in conjunction with embodiment. The reagents or instruments used are not indicated by the manufacturer, and they are all regarded as conventional products that can be purchased through the market.
实施例1Example 1
一种改性的水稻秸秆吸附剂的制备方法,包括以下步骤:A preparation method of a modified rice straw adsorbent, comprising the following steps:
(1)水稻秸秆的预处理:首先将收集到的水稻秸秆用蒸馏水冲洗,然后至于80℃烘箱中烘24h。再将烘干的秸秆碾碎、研磨后过100目筛;(1) Pretreatment of rice straw: firstly, the collected rice straw was washed with distilled water, and then dried in an oven at 80° C. for 24 hours. Then the dried straw is crushed and ground and passed through a 100-mesh sieve;
(2)水稻秸秆的改性:取10g步骤1中有待改性的水稻秸秆置于圆底烧瓶中,并加入10.8mL环氧氯丙烷和9mL二甲基甲酰胺,然后将烧瓶置于100℃条件下搅拌1h,使其充分反应。随后在烧瓶中加入3.6mL二亚乙基三胺,95℃条件下继续搅拌2h;最后,在烧瓶中加入9mL三乙胺,90℃条件下搅拌3h。然后,将所得材料过滤分离,并用去离子水清洗;(2) Modification of rice straw: Take 10 g of rice straw to be modified in step 1 and place it in a round bottom flask, add 10.8 mL of epichlorohydrin and 9 mL of dimethylformamide, and place the flask at 100 ° C Under the condition of stirring for 1h, it fully reacted. Subsequently, 3.6 mL of diethylenetriamine was added to the flask, and the stirring was continued at 95° C. for 2 h; finally, 9 mL of triethylamine was added to the flask, and stirring was continued at 90° C. for 3 h. Then, the resulting material was separated by filtration and washed with deionized water;
(3)将步骤2所得材料置于100℃烘箱中烘20h,即得。(3) Put the material obtained in step 2 into an oven at 100°C and bake for 20 hours to obtain the product.
上述方法制备的粉末材料即为改性的水稻秸秆吸附剂,将该吸附剂置于干燥器中储存备用。The powder material prepared by the above method is the modified rice straw adsorbent, and the adsorbent is stored in a desiccator for standby.
实施例2Example 2
一种改性的水稻秸秆吸附剂的制备方法,包括以下步骤:A preparation method of a modified rice straw adsorbent, comprising the following steps:
(1)水稻秸秆的预处理:首先将收集到的水稻秸秆用蒸馏水冲洗,然后至于80℃烘箱中烘24h。再将烘干的秸秆碾碎、研磨后过40目筛;(1) Pretreatment of rice straw: firstly, the collected rice straw was washed with distilled water, and then dried in an oven at 80° C. for 24 hours. Then the dried stalks are crushed and ground and passed through a 40-mesh sieve;
(2)水稻秸秆的改性:取9g步骤1中有待改性的水稻秸秆置于圆底烧瓶中,并加入12mL环氧氯丙烷和10mL二甲基甲酰胺,然后将烧瓶置于90℃条件下搅拌2h,使其充分反应。随后在烧瓶中加入4mL二亚乙基三胺,100℃条件下继续搅拌1h;最后,在烧瓶中加入10mL三乙胺,100℃条件下搅拌2h。然后,将所得材料过滤分离,并用去离子水清洗;(2) Modification of rice straw: take 9g of rice straw to be modified in step 1 and place it in a round bottom flask, add 12mL epichlorohydrin and 10mL dimethylformamide, and then place the flask at 90°C Under stirring for 2h, it fully reacted. Then 4 mL of diethylenetriamine was added to the flask, and the stirring was continued for 1 h at 100° C.; finally, 10 mL of triethylamine was added to the flask, and the stirring was continued at 100° C. for 2 h. Then, the resulting material was separated by filtration and washed with deionized water;
(3)将步骤2所得材料置于80℃烘箱中烘24h,即得。(3) Put the material obtained in step 2 in an oven at 80°C for 24 hours to obtain the product.
上述方法制备的粉末材料即为改性的水稻秸秆吸附剂,将该吸附剂置于干燥器中储存备用。The powder material prepared by the above method is the modified rice straw adsorbent, and the adsorbent is stored in a desiccator for standby.
实施例3Example 3
一种改性的水稻秸秆吸附剂的制备方法,包括以下步骤:A preparation method of a modified rice straw adsorbent, comprising the following steps:
(1)水稻秸秆的预处理:首先将收集到的水稻秸秆用蒸馏水冲洗,然后至于100℃烘箱中烘24h。再将烘干的秸秆碾碎、研磨后过200目筛;(1) Pretreatment of rice straw: first, the collected rice straw was rinsed with distilled water, and then dried in an oven at 100° C. for 24 hours. Then the dried stalks are crushed and ground and passed through a 200-mesh sieve;
(2)水稻秸秆的改性:取9.1g步骤1中有待改性的水稻秸秆置于圆底烧瓶中,并加入10mL环氧氯丙烷和8.8mL二甲基甲酰胺,然后将烧瓶置于95℃条件下搅拌1.4h,使其充分反应。随后在烧瓶中加入3.3mL二亚乙基三胺,90℃条件下继续搅拌1.6h;最后,在烧瓶中加入9mL三乙胺,95℃条件下搅拌2.5h。然后,将所得材料过滤分离,并用去离子水清洗;(2) Modification of rice straw: take 9.1 g of rice straw to be modified in step 1 and place it in a round bottom flask, add 10 mL of epichlorohydrin and 8.8 mL of dimethylformamide, and then place the flask at 95 Stir at ℃ for 1.4h to fully react. Then, 3.3 mL of diethylenetriamine was added to the flask, and the stirring was continued at 90° C. for 1.6 h; finally, 9 mL of triethylamine was added to the flask, and the stirring was continued at 95° C. for 2.5 h. Then, the resulting material was separated by filtration and washed with deionized water;
(3)将步骤2所得材料置于95℃烘箱中烘22h,即得。(3) Put the material obtained in step 2 in an oven at 95°C for 22 hours to obtain the product.
上述方法制备的粉末材料即为改性的水稻秸秆吸附剂,将该吸附剂置于干燥器中储存备用。The powder material prepared by the above method is the modified rice straw adsorbent, and the adsorbent is stored in a desiccator for standby.
将实施例1-3中得到的改性的水稻秸秆(MRS)和未改性的水稻秸秆(RS)作为吸附剂做对比试验,验证以上两种吸附剂在水中吸附铬和镍的效果。具体为:The modified rice straw (MRS) obtained in Examples 1-3 and the unmodified rice straw (RS) were used as adsorbents for comparative experiments to verify the effect of the above two adsorbents on the adsorption of chromium and nickel in water. Specifically:
分别配置浓度不同的铬(Ⅵ)、镍(Ⅱ)溶液,测试吸附剂对铬(Ⅵ)、镍(Ⅱ)的吸附效应。分别取吸附剂质量为0.2g、0.3g和0.4g;铬(Ⅵ)溶液浓度为20mg/L、40mg/L和60mg/L;镍(Ⅱ)溶液浓度为20mg/L、40mg/L和60mg/L。铬(Ⅵ)溶液和镍(Ⅱ)溶液体积均为50mL。Chromium (VI) and nickel (II) solutions with different concentrations were respectively prepared to test the adsorption effect of the adsorbent on chromium (VI) and nickel (II). Take the adsorbent quality as 0.2g, 0.3g and 0.4g respectively; the concentration of chromium (Ⅵ) solution is 20mg/L, 40mg/L and 60mg/L; the concentration of nickel (Ⅱ) solution is 20mg/L, 40mg/L and 60mg /L. The volumes of chromium (Ⅵ) solution and nickel (Ⅱ) solution are both 50mL.
在其他条件保持不变的情况下,试验例和对比例中不同质量吸附剂对不同浓度的铬(Ⅵ)溶液、镍(Ⅱ)相应的吸附性能,分别如下表1、表2所示。Under the condition that other conditions remain unchanged, the corresponding adsorption properties of different mass adsorbents for different concentrations of chromium (VI) solutions and nickel (II) in the test examples and comparative examples are shown in Table 1 and Table 2 below, respectively.
表1水稻秸秆吸附剂铬(Ⅵ)处理效果Table 1 Treatment effect of rice straw adsorbent chromium (Ⅵ)
表2水稻秸秆吸附剂镍(Ⅱ)处理效果Table 2 Treatment effect of rice straw adsorbent nickel(Ⅱ)
参考表1和表2,对比改性前后水稻秸秆对铬和镍的相关吸附数据,可以看出改性后的水稻秸秆其吸附性能得到了较大程度的提升,吸附效率也大大增加。Referring to Table 1 and Table 2, comparing the adsorption data of chromium and nickel on rice straw before and after modification, it can be seen that the adsorption performance of modified rice straw has been greatly improved, and the adsorption efficiency has also been greatly increased.
如上述表中所示,铬(Ⅵ)和镍(Ⅱ)初始浓度越高,相应吸附剂的吸附量越多;然而,吸附剂的用量对于吸附质的吸附效果是非线性的,达到一定用量后,即使增加吸附剂用量,吸附效果也增加有限。As shown in the above table, the higher the initial concentration of chromium (VI) and nickel (II), the higher the adsorption capacity of the corresponding adsorbent; , even if the amount of adsorbent is increased, the adsorption effect is limited.
以上所述仅是本发明的优选实施方式,应当指出:对于本技术领域的普通技术人员来说,在不脱离本发明原理的前提下,还可以做出若干改进和润饰,这些改进和润饰也应视为本发明的保护范围。The above is only a preferred embodiment of the present invention, it should be pointed out that for those of ordinary skill in the art, without departing from the principle of the present invention, some improvements and modifications can also be made, and these improvements and modifications are also possible. It should be regarded as the protection scope of the present invention.
Claims (7)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710743317.8A CN107456951A (en) | 2017-08-25 | 2017-08-25 | A kind of rice straw adsorbent of modification and its preparation method and application |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710743317.8A CN107456951A (en) | 2017-08-25 | 2017-08-25 | A kind of rice straw adsorbent of modification and its preparation method and application |
Publications (1)
Publication Number | Publication Date |
---|---|
CN107456951A true CN107456951A (en) | 2017-12-12 |
Family
ID=60549622
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201710743317.8A Pending CN107456951A (en) | 2017-08-25 | 2017-08-25 | A kind of rice straw adsorbent of modification and its preparation method and application |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN107456951A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109174067A (en) * | 2018-11-06 | 2019-01-11 | 齐鲁工业大学 | A method of hexavalent chromium adsorbent is prepared by raw material of Alocasia ordora |
CN109513425A (en) * | 2018-09-25 | 2019-03-26 | 山东大学 | A kind of peanut shell graphene composite aerogel oil absorption material and preparation method thereof |
CN112023889A (en) * | 2020-08-28 | 2020-12-04 | 西安工程大学 | A kind of microwave-assisted method for in-situ one-step modification of activated carbon with oleic acid |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103381357A (en) * | 2013-07-30 | 2013-11-06 | 河海大学 | Preparation method for modified walnut shell cation adsorbent |
CN104014317A (en) * | 2014-06-19 | 2014-09-03 | 山东大学 | Preparation and application of modified magnetic straw anion adsorbent |
CN104772123A (en) * | 2015-04-01 | 2015-07-15 | 南华大学 | Method for preparing amino modified sawdust adsorbent and application of method |
CN105080502A (en) * | 2015-07-29 | 2015-11-25 | 上海沃杉化工有限公司 | Preparation method of wheat straw modified anion adsorbent |
-
2017
- 2017-08-25 CN CN201710743317.8A patent/CN107456951A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103381357A (en) * | 2013-07-30 | 2013-11-06 | 河海大学 | Preparation method for modified walnut shell cation adsorbent |
CN104014317A (en) * | 2014-06-19 | 2014-09-03 | 山东大学 | Preparation and application of modified magnetic straw anion adsorbent |
CN104772123A (en) * | 2015-04-01 | 2015-07-15 | 南华大学 | Method for preparing amino modified sawdust adsorbent and application of method |
CN105080502A (en) * | 2015-07-29 | 2015-11-25 | 上海沃杉化工有限公司 | Preparation method of wheat straw modified anion adsorbent |
Non-Patent Citations (2)
Title |
---|
YUNHAI WU ET AL.: "Functionalized agricultural biomass as a low-cost adsorbent: Utilization of rice straw incorporated with amine groups for the adsorption of Cr(VI) and Ni(II) from single and binary systems", 《BIOCHEMICAL ENGINEERING JOURNAL》 * |
陈素红: "玉米秸秆的改性及其对六价铬离子吸附性能的研究", 《中国博士学位论文全文数据库工程科技Ⅰ辑》 * |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109513425A (en) * | 2018-09-25 | 2019-03-26 | 山东大学 | A kind of peanut shell graphene composite aerogel oil absorption material and preparation method thereof |
CN109513425B (en) * | 2018-09-25 | 2021-08-10 | 山东大学 | Peanut shell graphene composite aerogel oil absorption material and preparation method thereof |
CN109174067A (en) * | 2018-11-06 | 2019-01-11 | 齐鲁工业大学 | A method of hexavalent chromium adsorbent is prepared by raw material of Alocasia ordora |
CN109174067B (en) * | 2018-11-06 | 2021-06-18 | 齐鲁工业大学 | A kind of method for preparing hexavalent chromium ion adsorbent with alocasia as raw material |
CN112023889A (en) * | 2020-08-28 | 2020-12-04 | 西安工程大学 | A kind of microwave-assisted method for in-situ one-step modification of activated carbon with oleic acid |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN106115691B (en) | A kind of preparation method and application method of bamboo shoot shell matrix activated carbon | |
CN106362690A (en) | Magnetic biochar adsorbing material and preparation method thereof | |
CN101091906B (en) | Agricultural waste quaternary ammonium salt cationic adsorbent and its preparation process | |
CN103769058A (en) | Preparation method of carbonized chitosan adsorbent, adsorbent and application method of absorbent | |
CN103752280B (en) | Composite modified walnut shell adsorbent and its preparation method and application | |
CN107744801A (en) | A kind of poly- phenol amine sorbing material of new lignin-base and preparation method | |
CN105148850B (en) | The method of sulfate ion in a kind of composite Adsorption water of layer structure | |
CN106378094A (en) | Preparation method of amino iron-carrying composite modified biochar | |
CN108579684A (en) | A method of being modified spherical porous silica removal heavy metal containing sewage and its organic pollution | |
CN107456951A (en) | A kind of rice straw adsorbent of modification and its preparation method and application | |
CN104785227A (en) | Chitosan-grafting amino acid magnetic composite microsphere as well as preparation method and application | |
CN101486769A (en) | Preparation of amidoxime group bacteria cellulose | |
Qu et al. | Characterization of modified Alternanthera philoxeroides by diethylenetriamine and its application in the adsorption of copper (II) ions in aqueous solution | |
CN105854800A (en) | Method for preparing modified charcoal by utilizing aquatic plant wastes and hydrochloric acid | |
CN106994333A (en) | The preparation method of the cystamine modification biological charcoal of Adsorption of Heavy Metals cadmium ion | |
CN102580698A (en) | Persimmon tannin adsorption material and preparation method thereof | |
CN106362712A (en) | Rice husk base ion-exchange adsorption material, preparation method thereof and application | |
CN101912767A (en) | A kind of preparation method of modified furfural slag heavy metal adsorbent | |
CN103433004B (en) | Method for preparing bio-adsorbent by taking rice bran as raw material | |
CN113617342A (en) | Preparation method of aminated bagasse/graphene composite aerogel and application of aminated bagasse/graphene composite aerogel in wastewater treatment | |
CN109603768B (en) | Preparation method of economic and reproducible biogas residue-based heavy metal adsorbent | |
CN105170107B (en) | A kind of preparation method of green heavy metal chelating agent | |
CN106311187B (en) | A kind of preparation of cyanurotriamide modified magnetic coconut skin adsorbent | |
CN112892486A (en) | Preparation method of inorganic heavy metal waste liquid adsorption material, adsorption material and application | |
CN105195094B (en) | A kind of preparation method for the graphene oxide sorbing material for adsorbing copper ion |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20171212 |
|
RJ01 | Rejection of invention patent application after publication |