CN106140105A - A kind of preparation method of waste water mercury-removing adsorbent - Google Patents

A kind of preparation method of waste water mercury-removing adsorbent Download PDF

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CN106140105A
CN106140105A CN201610618496.8A CN201610618496A CN106140105A CN 106140105 A CN106140105 A CN 106140105A CN 201610618496 A CN201610618496 A CN 201610618496A CN 106140105 A CN106140105 A CN 106140105A
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凌雪木
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Guangxi Province Nanning City Guierchuang Environmental Protection Technology Co Ltd
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/24Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/0203Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
    • B01J20/0207Compounds of Sc, Y or Lanthanides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/0203Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
    • B01J20/0274Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04 characterised by the type of anion
    • B01J20/0281Sulfates of compounds other than those provided for in B01J20/045
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/223Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material containing metals, e.g. organo-metallic compounds, coordination complexes
    • 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
    • C02F1/288Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered

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  • Water Treatment By Sorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The invention discloses the preparation method of a kind of waste water mercury-removing adsorbent, it is that Pericarpium Musae is pulverized, add sodium hydroxide solution to soak, it is washed with water and washs Fructus Musae corium farinosum to neutral, in Pericarpium Musae cellulose, add ethyl acrylate, add water, mix homogeneously, at temperature is 60 80 DEG C, it is dried 2 3h, obtains modified Fructus Musae corium farinosum;Take Entermorpha powder and thiourea adds ultrasonic stirrer, add suitable quantity of water and carry out ultrasonic reaction, reacted pastel is placed in heat drying 1 2h in the baking oven of 70 80 DEG C, obtains modified Entermorpha powder;Again modification Fructus Musae corium farinosum, modified Entermorpha powder are added agitator, add cerous sulfate solution and sodium alginate, add water furnishing pasty state, pastel is put into microwave heating equipment heat drying, be cooled to room temperature, grind, obtain waste water mercury-removing adsorbent.The adsorbent of the present invention has the advantages such as raw material sources are extensive, with low cost, specific surface area is big, adsorption capacity is big, adsorption efficiency is high, preparation technology is simple, and waste water mercury ion is had good absorption property.

Description

一种废水除汞吸附剂的制备方法A kind of preparation method of waste water mercury removal adsorbent

技术领域technical field

本发明涉及吸附材料技术领域,具体是一种废水除汞吸附剂的制备方法。The invention relates to the technical field of adsorption materials, in particular to a preparation method of an adsorbent for removing mercury from wastewater.

背景技术Background technique

近年来,随着重金属工业的发展、重金属废水未加处理的任意排放,导致了重金属离子在自然水体中的含量日益增加,由此所导致的水污染事件频频发生。重金属是造成环境污染问题的重要原因之一,当重金属进入到环境中,是不能被生物降解为无害物质的,同时水中的悬浮颗粒通过对重金属离子的吸附和沉淀作用,使得水体重金属长期污染就此产生。更有甚者,存在于生物体内的重金属经过累积、富集,还参与生物圈循环,危害人体健康,是对生态环境危害极大的一类污染物。水体重金属污染已经成为了全社会关注的一个世界性的的环境问题。In recent years, with the development of the heavy metal industry and the arbitrary discharge of heavy metal wastewater without treatment, the content of heavy metal ions in natural water bodies has increased, and water pollution incidents have occurred frequently. Heavy metals are one of the important causes of environmental pollution. When heavy metals enter the environment, they cannot be biodegraded into harmless substances. At the same time, suspended particles in the water absorb and precipitate heavy metal ions, making the water polluted by heavy metals for a long time. And so it came about. What's more, the heavy metals that exist in living organisms are accumulated and enriched, and they also participate in the cycle of the biosphere, endangering human health, and are a type of pollutant that is extremely harmful to the ecological environment. Heavy metal pollution in water has become a worldwide environmental problem of concern to the whole society.

含汞废水主要来源于有色金属冶炼厂、仪表厂和某些化工厂等。汞是一种毒性很强的金属。有机汞的毒性大于金属汞和无机汞化合物,因而更容易发生中毒。有机汞和甲基汞均可通过呼吸道、消化道、皮肤侵入人体。无机汞在人体内蓄积部位主要是肾脏,其次是肝脏和脾脏;甲基汞除蓄积在肝、肾等脏器之外,还可通过血脑屏障蓄积于脑织织内。汞中毒能损伤中枢神经系统,轻者表现为口腔炎、震颤、急躁、易怒和情绪不稳定,重者则精神紊乱、行为支配能力降低、四肢瘫痪、耳聋眼瞎,甚至成为白痴。因此,如何经济有效地处理含汞废水便成为我国重要的研究方向之一。Mercury-containing wastewater mainly comes from non-ferrous metal smelters, instrument factories and some chemical plants. Mercury is a very toxic metal. Organic mercury is more toxic than metallic mercury and inorganic mercury compounds, so poisoning is more likely to occur. Both organic mercury and methylmercury can enter the human body through the respiratory tract, digestive tract, and skin. Inorganic mercury accumulates mainly in the kidneys, followed by the liver and spleen; methylmercury not only accumulates in the liver, kidneys and other organs, but also accumulates in the brain tissue through the blood-brain barrier. Mercury poisoning can damage the central nervous system. In mild cases, it manifests as stomatitis, tremor, impatience, irritability and emotional instability. In severe cases, it causes mental disorders, reduced behavioral control ability, quadriplegia, deafness and blindness, and even becomes an idiot. Therefore, how to treat mercury-containing wastewater economically and effectively has become one of the important research directions in our country.

含汞废水的处理方法较多,硫化物沉淀法、铁氧体法、浮选法、黄原酸酯适用于处理少量含汞废水,大量的含汞废水的处理含汞工业废水的处理方法包括化学沉淀法、混凝沉淀法、离子交换法、吸附法等。由于吸附法具有工艺流程简单、处理效果好、可操作性强等优点,因此在处理废水汞离子中得到广泛的应用。其中活性炭作为一种有效的废水处理吸附剂可用于大多数重金属、有机分子的除去且吸附能力强,只是活性炭资源有限,大批量治理废水造价高,寿命短,再生操作费用高,较难在经济尚不发达的地区得到广泛的应用。现有的高分子吸附剂、利用废弃物制备的吸附剂和复合吸附剂等也存在成本高、吸附效率低、易产生二次污染等问题。因此,如何提高吸附剂的吸附效率,和减少吸附剂使用过程中造成的二次污染问题是当今的研究热点。There are many treatment methods for mercury-containing wastewater. The sulfide precipitation method, ferrite method, flotation method, and xanthate are suitable for treating a small amount of mercury-containing wastewater, and the treatment of a large amount of mercury-containing wastewater. The treatment methods for mercury-containing industrial wastewater include Chemical precipitation, coagulation precipitation, ion exchange, adsorption, etc. Because the adsorption method has the advantages of simple process flow, good treatment effect and strong operability, it has been widely used in the treatment of mercury ions in wastewater. Among them, activated carbon, as an effective adsorbent for wastewater treatment, can be used to remove most heavy metals and organic molecules and has strong adsorption capacity. However, the resource of activated carbon is limited, and the cost of treating wastewater in large quantities is high, the life is short, and the regeneration operation cost is high. It is widely used in underdeveloped areas. Existing polymer adsorbents, adsorbents prepared from waste, and composite adsorbents also have problems such as high cost, low adsorption efficiency, and easy to produce secondary pollution. Therefore, how to improve the adsorption efficiency of the adsorbent and reduce the secondary pollution caused by the use of the adsorbent is a research hotspot today.

发明内容Contents of the invention

本发明针对现有吸附剂存在的问题,提供一种比表面积大、吸附容量大、吸附效率高、成本低、制备工艺简单、安全环保的用于废水除汞的吸附剂。Aiming at the problems existing in the existing adsorbents, the present invention provides an adsorbent for removing mercury from waste water with large specific surface area, large adsorption capacity, high adsorption efficiency, low cost, simple preparation process, safety and environmental protection.

为了实现以上目的,本发明是通过以下技术方案实现:In order to achieve the above object, the present invention is achieved through the following technical solutions:

一种废水除汞吸附剂的制备方法,是以质量比为100:10-15:50-70:6-10:4-6:10-15的香蕉皮、丙烯酸乙酯、浒苔粉、硫脲、硫酸铈和海藻酸钠作为原料,通过微波加热法制成吸附剂,具体操作步骤如下:A preparation method of mercury-removing adsorbent for wastewater, comprising banana peel, ethyl acrylate, enteromorpha powder, sulfur Urea, cerium sulfate and sodium alginate are used as raw materials, and the adsorbent is made by microwave heating method. The specific operation steps are as follows:

(1)将100份香蕉皮粉碎,加入氢氧化钠溶液浸泡3-5h,再用水洗涤香蕉皮粉至中性,得香蕉皮纤维素;在香蕉皮纤维素中加入10-15份丙烯酸乙酯,再加入100-120份水,混合均匀,在温度为60-80℃下干燥2-3h,得改性香蕉皮粉;(1) Crush 100 parts of banana peel, add sodium hydroxide solution to soak for 3-5 hours, then wash the banana peel powder with water until neutral to obtain banana peel cellulose; add 10-15 parts of ethyl acrylate to the banana peel cellulose , then add 100-120 parts of water, mix evenly, and dry at a temperature of 60-80°C for 2-3 hours to obtain modified banana peel powder;

(2)取浒苔粉50-70份和硫脲6-10份加入超声波搅拌器,再加入适量水进行超声反应,将反应后的糊状物置于70-80℃的烘箱中加热干燥1-2h,得改性浒苔粉;(2) Take 50-70 parts of Enteromorpha powder and 6-10 parts of thiourea and add them to an ultrasonic stirrer, then add an appropriate amount of water for ultrasonic reaction, and place the reacted paste in an oven at 70-80°C to heat and dry for 1- 2h, get modified enteromorpha powder;

(3)将上述改性香蕉皮粉、改性浒苔粉加入搅拌器,加入硫酸铈溶液4-6份和海藻酸钠10-15份,再加入水调成糊状,将糊状物放入微波加热设备,在温度为120-140℃下微波30-60min,冷却至室温,研磨,即得废水除汞吸附剂。(3) Add the above-mentioned modified banana peel powder and modified enteromorpha powder into the mixer, add 4-6 parts of cerium sulfate solution and 10-15 parts of sodium alginate, then add water to make a paste, put the paste Put it into a microwave heating equipment, microwave at a temperature of 120-140°C for 30-60min, cool to room temperature, and grind to obtain a mercury-removing adsorbent for wastewater.

优选的,以上所述香蕉皮的含水量为12%。Preferably, the water content of the above-mentioned banana peel is 12%.

优选的,以上步骤(1)是将香蕉皮粉碎至40-60目。Preferably, the above step (1) is to crush the banana peel to 40-60 mesh.

优选的,以上所述氢氧化钠的浓度为3-5mol/L。Preferably, the concentration of the above-mentioned sodium hydroxide is 3-5 mol/L.

优选的,以上所述浒台粉是将新鲜浒台粉洗净,干燥至含水量为10%,再粉碎至80目,即得浒台粉。Preferably, the above-mentioned Hutai powder is washed fresh Hutai powder, dried to a water content of 10%, and then crushed to 80 mesh to obtain Hutai powder.

优选的,以上步骤(2)所述的超声反应是在超声频率为60-80kHz下超声反应20-30min。Preferably, the ultrasonic reaction in the above step (2) is performed at an ultrasonic frequency of 60-80 kHz for 20-30 minutes.

优选的,以上步骤(3)所述微波的功率为200-300W。Preferably, the power of the microwave in the above step (3) is 200-300W.

优选的,以上所述硫酸铈溶液的浓度为5mol/L。Preferably, the concentration of the above-mentioned cerium sulfate solution is 5 mol/L.

优选的,以上步骤(3)所述研磨是将物料研磨至粒径为0.5-1.0mm。Preferably, the grinding in the above step (3) is to grind the material to a particle size of 0.5-1.0 mm.

与现有技术相比,本发明的优点和有益效果为:Compared with prior art, advantage and beneficial effect of the present invention are:

1、本发明制备的吸附剂具有原料来源广泛、成本低廉、比表面积大、吸附容量大、吸附效率高、制备工艺简单、环保易降解等优点,对汞离子具有很好的吸附性能,在工业废水处理中具有广阔的市场前景。1. The adsorbent prepared by the present invention has the advantages of wide source of raw materials, low cost, large specific surface area, large adsorption capacity, high adsorption efficiency, simple preparation process, environmental protection and easy degradation, and has good adsorption performance for mercury ions. Wastewater treatment has broad market prospects.

2、本发明以农作物废弃物香蕉皮作为主要原料,不仅原料来源广泛,价格低廉,还能实现废弃物的资源化回收利用,增加香蕉皮的应用价值。2. The present invention uses the agricultural waste banana peel as the main raw material, which not only has a wide range of raw material sources and low price, but also realizes the recycling and utilization of waste and increases the application value of the banana peel.

3、本方法利用氢氧化钠和丙烯酸乙酯对香蕉皮进行改性,可以去除香蕉皮的色素、木质素和半纤维素等物质,由于丙烯酸乙酯分子链上具有大量的羧基等活性基团,可活化吸附位点,提高吸附剂的吸附性能。3. This method uses sodium hydroxide and ethyl acrylate to modify the banana peel, which can remove the pigment, lignin and hemicellulose of the banana peel, because the molecular chain of ethyl acrylate has a large number of active groups such as carboxyl groups. , which can activate the adsorption sites and improve the adsorption performance of the adsorbent.

4、本发明以分布广泛、繁殖速度快、生长周期短的浒苔作为原料,不但为浒台灾害提供了有效处理途径,浒台的多空结构可为重金属提供有效地吸附位点,同时浒台富含蛋白质、多糖及粗纤维等多种大分子物质,含有大量的羟基、羧基和氨基等官能团,可与汞离子发生较为完全的络合反应,从而达到更好的吸附效果。4. The present invention uses Enteromorpha with wide distribution, fast propagation speed and short growth cycle as raw material, which not only provides an effective treatment approach for the disaster of the Formosa, the porous structure of the Formosa can provide effective adsorption sites for heavy metals, and simultaneously Taiwan is rich in various macromolecular substances such as protein, polysaccharide and crude fiber, and contains a large number of functional groups such as hydroxyl, carboxyl and amino groups, which can undergo a relatively complete complexation reaction with mercury ions, thereby achieving better adsorption effects.

5、本方法采用超声波处理浒苔粉,能够快速破碎植物的细胞壁,使更多的内部功能团暴露出来与金属离子结合,对废水重金属汞离子的吸附效果显著提高。5. This method adopts ultrasonic treatment of Enteromorpha powder, which can quickly break the cell wall of the plant, so that more internal functional groups are exposed to combine with metal ions, and the adsorption effect of heavy metal mercury ions in wastewater is significantly improved.

6、本发明采用硫脲对浒苔粉进行改性,可以使吸附剂赋予更大的比表面积和吸附容量,提高吸附剂对汞离子的吸附性能。6. The present invention adopts thiourea to modify Enteromorpha powder, which can endow the adsorbent with larger specific surface area and adsorption capacity, and improve the adsorption performance of the adsorbent to mercury ions.

7、本方法在吸附剂的制备过程中加入硫酸铈,可提高吸附剂的吸附容量大和吸附效率。7. In this method, cerium sulfate is added in the preparation process of the adsorbent, which can improve the adsorption capacity and adsorption efficiency of the adsorbent.

8、本发明采用微波法加热,具有加热速度快、受热体系温度均匀、耗能低等优点。8. The present invention uses microwave heating, which has the advantages of fast heating speed, uniform temperature of the heating system, and low energy consumption.

9、本发明制备的吸附剂具有良好的吸附性能,其中吸附剂的比表面积为300-350m2/g,对汞离子的吸附率达到98%以上。9. The adsorbent prepared by the present invention has good adsorption performance, wherein the specific surface area of the adsorbent is 300-350m 2 /g, and the adsorption rate for mercury ions is over 98%.

具体实施方式detailed description

下面将结合具体实施例对本发明进一步说明,但不限于本发明的保护范围。The present invention will be further described below in conjunction with specific examples, but not limited to the protection scope of the present invention.

实施例1Example 1

一种废水除汞吸附剂的制备方法,具体操作步骤如下:A kind of preparation method of waste water mercury removal adsorbent, concrete operation steps are as follows:

(1)将100kg含水量为12%的香蕉皮粉碎至40目,加入浓度为5mol/L的氢氧化钠溶液浸泡3h,再用水洗涤香蕉皮粉至中性,得香蕉皮纤维素;在香蕉皮纤维素中加入12kg丙烯酸乙酯,再加入100kg水,混合均匀,在温度为60℃下干燥3h,得改性香蕉皮粉;(1) Crush 100kg of banana peels with a water content of 12% to 40 meshes, add 5mol/L sodium hydroxide solution for soaking for 3 hours, then wash the banana peel powder with water until neutral to obtain banana peel cellulose; Add 12kg of ethyl acrylate to the peel cellulose, then add 100kg of water, mix well, and dry at a temperature of 60°C for 3 hours to obtain modified banana peel powder;

(2)取浒苔粉50kg和硫脲6kg加入超声波搅拌器,再加入100kg水,在超声频率为80kHz下超声反应20min,将反应后的糊状物置于70℃的烘箱中加热干燥2h,得改性浒苔粉;(2) Get 50kg of Enteromorpha powder and 6kg of thiourea into an ultrasonic mixer, then add 100kg of water, and conduct an ultrasonic reaction at an ultrasonic frequency of 80kHz for 20min, place the reacted paste in an oven at 70°C for 2h and heat and dry it to obtain Modified enteromorpha powder;

(3)将上述改性香蕉皮粉、改性浒苔粉加入搅拌器,加入硫酸铈溶液5kg和海藻酸钠10kg,再加入水调成糊状,将糊状物放入微波加热设备,在功率为250W、温度为120℃下微波60min,冷却至室温,将物料研磨至粒径为0.5mm,即得废水除汞吸附剂。(3) Add the above-mentioned modified banana peel powder and modified enteromorpha powder to the stirrer, add 5 kg of cerium sulfate solution and 10 kg of sodium alginate, then add water to adjust to a paste, put the paste into microwave heating equipment, and The power is 250W, the temperature is 120°C, microwave for 60min, cool to room temperature, and grind the material to a particle size of 0.5mm to obtain the mercury-removing adsorbent for wastewater.

实施例2Example 2

一种废水除汞吸附剂的制备方法,具体操作步骤如下:A kind of preparation method of waste water mercury removal adsorbent, concrete operation steps are as follows:

(1)将100kg含水量为12%的香蕉皮粉碎至40目,加入浓度为5mol/L氢氧化钠溶液浸泡3h,再用水洗涤香蕉皮粉至中性,得香蕉皮纤维素;在香蕉皮纤维素中加入10kg丙烯酸乙酯,再加入100kg水,混合均匀,在温度为80℃下干燥2h,得改性香蕉皮粉;(1) Crush 100kg of banana peels with a water content of 12% to 40 meshes, add 5 mol/L sodium hydroxide solution to soak for 3 hours, then wash the banana peel powder with water until neutral to obtain banana peel cellulose; Add 10kg of ethyl acrylate to the cellulose, then add 100kg of water, mix well, and dry at 80°C for 2 hours to obtain modified banana peel powder;

(2)取浒苔粉60kg和硫脲8kg加入超声波搅拌器,再加入120kg水,在超声频率为60kHz下超声反应30min,将反应后的糊状物置于80℃的烘箱中加热干燥1.5h,得改性浒苔粉;(2) Take 60kg of Enteromorpha powder and 8kg of thiourea and add them to an ultrasonic mixer, then add 120kg of water, and conduct an ultrasonic reaction at an ultrasonic frequency of 60kHz for 30min, place the reacted paste in an oven at 80°C and heat and dry it for 1.5h. Obtain modified enteromorpha powder;

(3)将上述改性香蕉皮粉、改性浒苔粉加入搅拌器,加入硫酸铈溶液4kg和海藻酸钠12kg,再加入水调成糊状,将糊状物放入微波加热设备,在功率为200W、温度为130℃下微波45min,冷却至室温,将物料研磨至粒径为0.5mm,即得废水除汞吸附剂。(3) Add the above-mentioned modified banana peel powder and modified enteromorpha powder to the stirrer, add 4 kg of cerium sulfate solution and 12 kg of sodium alginate, then add water to adjust to a paste, put the paste into microwave heating equipment, and The power is 200W, the temperature is 130°C, microwave for 45 minutes, cool to room temperature, and grind the material to a particle size of 0.5mm to obtain the mercury-removing adsorbent for wastewater.

实施例3Example 3

一种废水除汞吸附剂的制备方法,具体操作步骤如下:A kind of preparation method of waste water mercury removal adsorbent, concrete operation steps are as follows:

(1)将100kg含水量为12%的香蕉皮粉碎至60目,加入浓度为3mol/L氢氧化钠溶液浸泡5h,再用水洗涤香蕉皮粉至中性,得香蕉皮纤维素;在香蕉皮纤维素中加入15kg丙烯酸乙酯,再加入120kg水,混合均匀,在温度为80℃下干燥2.5h,得改性香蕉皮粉;(1) Crush 100kg of banana peels with a water content of 12% to 60 mesh, add 3 mol/L sodium hydroxide solution to soak for 5 hours, then wash the banana peel powder with water until neutral to obtain banana peel cellulose; Add 15kg of ethyl acrylate to the cellulose, then add 120kg of water, mix evenly, and dry at 80°C for 2.5h to obtain modified banana peel powder;

(2)取浒苔粉70kg和硫脲10kg加入超声波搅拌器,再加入150kg水,在超声频率为70kHz下超声反应30min,将反应后的糊状物置于80℃的烘箱中加热干燥2h,得改性浒苔粉;(2) Get 70kg of Enteromorpha powder and 10kg of thiourea and add it to an ultrasonic mixer, then add 150kg of water, and conduct an ultrasonic reaction at an ultrasonic frequency of 70kHz for 30min, place the reacted paste in an oven at 80°C for 2h and heat and dry it to obtain Modified enteromorpha powder;

(3)将上述改性香蕉皮粉、改性浒苔粉加入搅拌器,加入硫酸铈溶液6kg和海藻酸钠12kg,再加入水调成糊状,将糊状物放入微波加热设备,在功率为300W、温度为140℃下微波30min,冷却至室温,将物料研磨至粒径为1.0mm,即得废水除汞吸附剂。(3) Add the above-mentioned modified banana peel powder and modified enteromorpha powder to the stirrer, add 6 kg of cerium sulfate solution and 12 kg of sodium alginate, then add water to adjust to a paste, put the paste into microwave heating equipment, and The power is 300W, the temperature is 140°C, microwave for 30min, cool to room temperature, and grind the material to a particle size of 1.0mm to obtain the mercury-removing adsorbent for wastewater.

实施例4Example 4

一种废水除汞吸附剂的制备方法,具体操作步骤如下:A kind of preparation method of waste water mercury removal adsorbent, concrete operation steps are as follows:

(1)将100kg含水量为12%的香蕉皮粉碎至60目,加入浓度为5mol/L氢氧化钠溶液浸泡5h,再用水洗涤香蕉皮粉至中性,得香蕉皮纤维素;在香蕉皮纤维素中加入12kg丙烯酸乙酯,再加入100kg水,混合均匀,在温度为80℃下干燥2h,得改性香蕉皮粉;(1) Crush 100 kg of banana peels with a water content of 12% to 60 mesh, add 5 mol/L sodium hydroxide solution to soak for 5 hours, and then wash the banana peel powder with water until neutral to obtain banana peel cellulose; Add 12kg of ethyl acrylate to the cellulose, then add 100kg of water, mix evenly, and dry at 80°C for 2 hours to obtain modified banana peel powder;

(2)取浒苔粉60kg和硫脲10kg加入超声波搅拌器,再加入120kg水,在超声频率为60kHz下超声反应60min,将反应后的糊状物置于80℃的烘箱中加热干燥1h,得改性浒苔粉;(2) Get 60 kg of Enteromorpha powder and 10 kg of thiourea and add them to an ultrasonic mixer, then add 120 kg of water, and conduct an ultrasonic reaction at an ultrasonic frequency of 60 kHz for 60 min, place the reacted paste in an oven at 80° C. for heating and drying for 1 h to obtain Modified enteromorpha powder;

(3)将上述改性香蕉皮粉、改性浒苔粉加入搅拌器,加入硫酸铈溶液5kg和海藻酸钠15kg,再加入水调成糊状,将糊状物放入微波加热设备,在功率为250W、温度为120℃下微波60min,冷却至室温,将物料研磨至粒径为1.0mm,即得废水除汞吸附剂。(3) Add the above-mentioned modified banana peel powder and modified enteromorpha powder to the agitator, add 5 kg of cerium sulfate solution and 15 kg of sodium alginate, then add water to adjust to a paste, put the paste into microwave heating equipment, and The power is 250W, the temperature is 120°C, microwave for 60min, cool to room temperature, and grind the material to a particle size of 1.0mm to obtain the mercury-removing adsorbent for wastewater.

吸附剂的使用方法为:在室温条件下,将3g的吸附剂投入1L含有汞离子的废水中,控制pH为6,在转速为300r/min下搅拌60min,分离出吸附剂,即可吸附废水中的汞离子。The method of using the adsorbent is: at room temperature, put 3g of the adsorbent into 1L of waste water containing mercury ions, control the pH to 6, stir at a speed of 300r/min for 60min, separate the adsorbent, and the waste water can be adsorbed mercury ions in.

以下对实施例1-4制得的吸附剂进行吸附性能的测定。其中采用比表面积测定吸附剂的比表面积。采用原子吸收分光光度法测定汞离子的浓度,再根据以下公式计算出吸附率,测定结果如下表所示。The adsorption properties of the adsorbents prepared in Examples 1-4 were measured as follows. The specific surface area of the adsorbent is measured by the specific surface area. The concentration of mercury ions was measured by atomic absorption spectrophotometry, and then the adsorption rate was calculated according to the following formula. The measurement results are shown in the table below.

ŋ=(C0-Ci)×100% /C0 ŋ=(C 0 -C i )×100%/C 0

其中C0、Ci为废水中汞离子吸附前后的含量(mg/L),ŋ为吸附率。Among them, C 0 and C i are the content (mg/L) of mercury ions in wastewater before and after adsorption, and ŋ is the adsorption rate.

从测定结果可以看出,本发明制备的吸附剂具有较大的比表面积,对汞离子的吸附率达到98%以上,在工业废水处理中具有广阔的应用前景。It can be seen from the measurement results that the adsorbent prepared by the present invention has a large specific surface area, and the adsorption rate of mercury ions reaches more than 98%, and has broad application prospects in industrial wastewater treatment.

以上内容不能认定本发明具体实施只局限于这些说明,对于本发明所属技术领域的普通技术人员来说,在不脱离本发明构思前提下,还可以做出若干简单推演或替换,都应当视为属于本发明由所提交的权利要求书确定的专利保护范围。The above content cannot be deemed that the specific implementation of the present invention is limited to these descriptions. For those of ordinary skill in the technical field of the present invention, without departing from the concept of the present invention, some simple deduction or replacement can also be made, which should be regarded as Belonging to the scope of patent protection of the present invention determined by the submitted claims.

Claims (9)

1. the preparation method of a waste water mercury-removing adsorbent, it is characterised in that: it is with mass ratio as 100:10-15:50-70:6- The Pericarpium Musae of 10:4-6:10-15, ethyl acrylate, Entermorpha powder, thiourea, cerous sulfate and sodium alginate, as raw material, pass through microwave Heating makes adsorbent, and concrete operation step is as follows:
(1) 100 parts of Pericarpium Musae are pulverized, add sodium hydroxide solution and soak 3-5h, be washed with water and wash Fructus Musae corium farinosum extremely neutrality, Pericarpium Musae cellulose;Adding 10-15 part ethyl acrylate in Pericarpium Musae cellulose, add 100-120 part water, mixing is all Even, at temperature is 60-80 DEG C, it is dried 2-3h, obtains modified Fructus Musae corium farinosum;
(2) take Entermorpha powder 50-70 part and thiourea 6-10 part add ultrasonic stirrer, add suitable quantity of water and carry out ultrasonic reaction, Reacted pastel is placed in heat drying 1-2h in the baking oven of 70-80 DEG C, obtains modified Entermorpha powder;
(3) above-mentioned modified Fructus Musae corium farinosum, modified Entermorpha powder are added agitator, add cerous sulfate solution 4-6 part and sodium alginate 10-15 part, adds water furnishing pasty state, pastel is put into microwave heating equipment, microwave 30-at temperature is 120-140 DEG C 60min, is cooled to room temperature, grinds, obtains waste water mercury-removing adsorbent.
The preparation method of waste water mercury-removing adsorbent the most according to claim 1, it is characterised in that: the water content of described Pericarpium Musae It is 12%.
The preparation method of waste water mercury-removing adsorbent the most according to claim 2, it is characterised in that: step (1) is by Pericarpium Musae It is crushed to 40-60 mesh.
The preparation method of waste water mercury-removing adsorbent the most according to claim 1, it is characterised in that: the concentration of described sodium hydroxide For 3-5mol/L.
The preparation method of waste water mercury-removing adsorbent the most according to claim 1, it is characterised in that: described waterside platform powder is by fresh Waterside platform powder cleaning, drying are 10% to water content, then are crushed to 80 mesh, obtain waterside platform powder.
The preparation method of waste water mercury-removing adsorbent the most according to claim 1, it is characterised in that: ultrasonic described in step (2) Reaction is ultrasonic reaction 20-30min under supersonic frequency is 60-80kHz.
The preparation method of waste water mercury-removing adsorbent the most according to claim 1, it is characterised in that: step (3) described microwave Power is 200-300W.
The preparation method of waste water mercury-removing adsorbent the most according to claim 1, it is characterised in that: described cerous sulfate solution dense Degree is 5mol/L.
The preparation method of waste water mercury-removing adsorbent the most according to claim 1, it is characterised in that: step (3) described grinding is Grinding the material to particle diameter is 0.5-1.0mm.
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