CN117884095B - A method for preparing composite modified sand-granulated microcrystalline activated carbon - Google Patents
A method for preparing composite modified sand-granulated microcrystalline activated carbon Download PDFInfo
- Publication number
- CN117884095B CN117884095B CN202311827712.6A CN202311827712A CN117884095B CN 117884095 B CN117884095 B CN 117884095B CN 202311827712 A CN202311827712 A CN 202311827712A CN 117884095 B CN117884095 B CN 117884095B
- Authority
- CN
- China
- Prior art keywords
- activated carbon
- microcrystalline
- sand
- reactor
- ammonia 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.)
- Active
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
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/20—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
-
- 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
- B01J20/28—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
- B01J20/28054—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their surface properties or porosity
- B01J20/28057—Surface area, e.g. B.E.T specific surface area
-
- 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
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/3007—Moulding, shaping or extruding
-
- 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
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/3028—Granulating, agglomerating or aggregating
-
- 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
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/3078—Thermal treatment, e.g. calcining or pyrolizing
-
- 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
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/3085—Chemical treatments not covered by groups B01J20/3007 - B01J20/3078
Landscapes
- Chemical & Material Sciences (AREA)
- Analytical Chemistry (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Physics & Mathematics (AREA)
- Thermal Sciences (AREA)
- Inorganic Chemistry (AREA)
- Carbon And Carbon Compounds (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
Description
技术领域Technical Field
本发明属于活性炭改性技术领域,具体涉及一种复合改性砂粒化微晶活性炭的制备方法。The invention belongs to the technical field of activated carbon modification, and in particular relates to a method for preparing composite modified sand-granulated microcrystalline activated carbon.
背景技术Background technique
微晶活性炭是一种具有特殊结构的炭材料,比表面积在70-900m2/g,内部含有大量比较完整的、尺寸在1-3nm之间的类石墨微晶结构,相比普通的活性炭,具有更明显的晶体特性,并保持较大的层间距,石墨微晶的层间距在0.365-0.385nm之间。微晶活性炭具有发达的孔隙结构和较大的比表面积以及较强的吸附性和催化功能,作为一种优良的吸附剂,在水处理领域得到广泛的应用,是去除水中有机污染物的有效手段。Microcrystalline activated carbon is a carbon material with a special structure, with a specific surface area of 70-900m2 /g. It contains a large number of relatively complete graphite-like microcrystalline structures with a size of 1-3nm. Compared with ordinary activated carbon, it has more obvious crystal characteristics and maintains a larger interlayer spacing. The interlayer spacing of graphite microcrystals is between 0.365-0.385nm. Microcrystalline activated carbon has a developed pore structure, a large specific surface area, strong adsorption and catalytic functions. As an excellent adsorbent, it is widely used in the field of water treatment and is an effective means to remove organic pollutants in water.
然而,在利用微晶活性炭对废水进行处理后,由于微晶活性炭本身重量较轻,不易与好氧活性污泥进行分离,另外,由于微晶活性炭表面含有大量的羧基、酚羟基等极性官能团,导致其具有较强的亲水性,废水中水分子和污染物分子产生竞争性吸附,使得微晶活性炭对污染物分子的吸附效果变差,进而加速微晶活性炭的“老化”过程。However, after using microcrystalline activated carbon to treat wastewater, it is not easy to separate from aerobic activated sludge due to its light weight. In addition, since the surface of microcrystalline activated carbon contains a large number of polar functional groups such as carboxyl and phenolic hydroxyl groups, it has strong hydrophilicity. The water molecules and pollutant molecules in the wastewater produce competitive adsorption, which makes the adsorption effect of microcrystalline activated carbon on pollutant molecules worse, thereby accelerating the "aging" process of microcrystalline activated carbon.
此外,在废水处理过程中,生化出水中剩余的难以降解的污染物大都是疏水性的有机物,亲水性较强的微晶活性炭对这类有机物的吸附效果不理想,还需要借助高级氧化法去除有机物,成本较高。另外,污水处理中若采用膜相关技术,则微晶活性炭容易造成膜的堵塞。In addition, in the process of wastewater treatment, the remaining pollutants that are difficult to degrade in the biochemical effluent are mostly hydrophobic organic matter. The hydrophilic microcrystalline activated carbon has an unsatisfactory adsorption effect on such organic matter, and it is necessary to use advanced oxidation methods to remove organic matter, which is costly. In addition, if membrane-related technologies are used in sewage treatment, microcrystalline activated carbon is prone to cause membrane blockage.
发明内容Summary of the invention
针对上述问题,本发明提供一种复合改性砂粒化微晶活性炭的制备方法,包括以下步骤:In view of the above problems, the present invention provides a method for preparing composite modified sand-granulated microcrystalline activated carbon, comprising the following steps:
S1:将原料微晶活性炭和砂粒都清洗干净,在氨水中混合搅拌,进行第一次氨水改性,得到一次改性产物;S1: Clean the raw material microcrystalline activated carbon and sand particles, mix and stir them in ammonia water, perform the first ammonia water modification, and obtain a first modified product;
S2:将一次改性产物和步骤S1剩余的砂粒放入挤压设备中制粒成型,得到砂粒化的微晶活性炭;S2: putting the first modified product and the remaining sand particles in step S1 into an extrusion device for granulation to obtain sand-granulated microcrystalline activated carbon;
S3:将植物生物质、砂粒和水混合至呈糊状,该糊状物与砂粒化的微晶活性炭混合均匀,然后送入马弗炉内高温煅烧,得到再塑活性炭;S3: mixing plant biomass, sand and water into a paste, mixing the paste with the sanded microcrystalline activated carbon evenly, and then calcining at high temperature in a muffle furnace to obtain re-plasticized activated carbon;
S4:将再塑活性炭加入氨水中,进行第二次氨水改性,得到二次改性产物;S4: adding the remolded activated carbon into ammonia water to perform a second ammonia modification to obtain a secondary modified product;
S5:使用聚四氟乙烯溶液均匀喷涂二次改性产物的表面,进行疏水改性,晾干后送入马弗炉内干燥,得到最终的复合改性砂粒化微晶活性炭。S5: Use polytetrafluoroethylene solution to evenly spray the surface of the secondary modified product for hydrophobic modification, and then send it into a muffle furnace for drying after drying to obtain the final composite modified sand-granulated microcrystalline activated carbon.
可选的,步骤S1中,所述将原料微晶活性炭和砂粒都清洗干净,包括微晶活性炭的表面预处理和砂粒的表面预处理;Optionally, in step S1, the raw material microcrystalline activated carbon and sand particles are cleaned, including surface pretreatment of the microcrystalline activated carbon and surface pretreatment of the sand particles;
微晶活性炭的表面预处理包括:(1)用蒸馏水冲洗微晶活性炭,将微晶活性炭表面的灰分冲洗干净,然后过滤;(2)将沥干水分的微晶活性炭浸渍于过量的蒸馏水中,超声清洗2-3h,去除微晶活性炭孔隙中的无机杂质,疏通微晶活性炭孔道;(3)用1-3mol/L氢氧化钠溶液清洗,去除微晶活性炭表面的有机杂质,之后用自来水水洗到中性为止,沥干水分后,烘干,备用;The surface pretreatment of microcrystalline activated carbon includes: (1) washing the microcrystalline activated carbon with distilled water to clean the ash on the surface of the microcrystalline activated carbon, and then filtering; (2) immersing the drained microcrystalline activated carbon in excess distilled water, and ultrasonically cleaning it for 2-3 hours to remove inorganic impurities in the pores of the microcrystalline activated carbon and dredge the microcrystalline activated carbon pores; (3) washing with 1-3 mol/L sodium hydroxide solution to remove organic impurities on the surface of the microcrystalline activated carbon, and then washing with tap water until it is neutral, draining the water, drying, and setting aside;
砂粒的表面预处理包括:用自来水冲洗搓洗砂粒,将砂粒表面的泥土、杂质、灰尘等洗净,再用蒸馏水涮洗,烘干,备用。The surface pretreatment of the sand particles includes: washing and scrubbing the sand particles with tap water to clean the dirt, impurities, dust, etc. on the surface of the sand particles, then rinsing with distilled water, drying, and setting aside.
可选的,步骤S1中,清洗干净之后,微晶活性炭的粒径为0.5-1.2mm,砂粒破碎研磨至300-500目;微晶活性炭与砂粒的质量比为(2-2.5):1。Optionally, in step S1, after cleaning, the particle size of the microcrystalline activated carbon is 0.5-1.2 mm, and the sand is crushed and ground to 300-500 mesh; the mass ratio of the microcrystalline activated carbon to the sand is (2-2.5):1.
可选的,步骤S1中,所述第一次氨水改性具体为:先将微晶活性炭加入反应器内,加入25-28wt%的氨水,微晶活性炭与氨水的质量体积比为1g:(10-20)mL;搅拌使得微晶活性炭充分分散,再加入砂粒,50-80℃搅拌混合;反应器为密封的,且设有排气管,排气管连通反应器的顶部和底部,将挥发的氨气抽出,再返回反应器内部,在反应器底部形成氨气曝气,反应器内的温度有利于氨气重新溶入水中;Optionally, in step S1, the first ammonia modification is specifically as follows: first, add microcrystalline activated carbon into a reactor, add 25-28wt% ammonia water, and the mass volume ratio of microcrystalline activated carbon to ammonia water is 1g:(10-20)mL; stir to fully disperse the microcrystalline activated carbon, then add sand particles, and stir and mix at 50-80°C; the reactor is sealed and provided with an exhaust pipe, which is connected to the top and bottom of the reactor, and the volatilized ammonia gas is extracted and returned to the inside of the reactor, forming ammonia aeration at the bottom of the reactor, and the temperature in the reactor is conducive to the ammonia gas re-dissolving into water;
改性后排出氨水,加入若干次清水,继续搅拌,至反应器内pH为7-8,得到所述一次改性产物和剩余的砂粒。After the modification, the ammonia water is discharged, and clean water is added several times, and stirring is continued until the pH in the reactor is 7-8, thereby obtaining the primary modified product and the remaining sand particles.
微晶活性炭表面经氨水进行初步改性后,表面的酸碱性质会发生改变,表面的还原官能团增多,对非极性物质的吸附性能提高。同时,氨水能改性促进微晶活性炭表面孔道的形成和发育,提高活其比表面积和孔隙度。在反应器内部,微晶活性炭和砂粒处于机械混合状态,有利于粒径较小的砂粒嵌入微晶活性炭的内部孔隙中,使得微晶活性炭的内部具有砂粒,有助于增加微晶活性炭的内部实心重量,使得后续应用时改性后的微晶活性炭与好氧污泥易于分离。After the surface of the microcrystalline activated carbon is initially modified by ammonia water, the acid-base properties of the surface will change, the reducing functional groups on the surface will increase, and the adsorption performance of non-polar substances will be improved. At the same time, ammonia water can promote the formation and development of pores on the surface of the microcrystalline activated carbon, and increase its specific surface area and porosity. Inside the reactor, the microcrystalline activated carbon and sand particles are in a mechanically mixed state, which is conducive to the embedding of sand particles with smaller particle size into the internal pores of the microcrystalline activated carbon, so that the microcrystalline activated carbon has sand particles inside, which helps to increase the internal solid weight of the microcrystalline activated carbon, making it easy to separate the modified microcrystalline activated carbon from aerobic sludge in subsequent applications.
微晶活性炭充分分散后,取样检测微晶活性炭单粒的质量,记为初始质量;第一次氨水改性过程中,对反应器内的微晶活性炭进行取样,并检测样品单粒的质量,直至样品单粒的重量增加到初始质量的120-140%,代表第一次氨水改性结束。After the microcrystalline activated carbon is fully dispersed, the mass of a single microcrystalline activated carbon particle is sampled and detected, which is recorded as the initial mass. During the first ammonia modification process, the microcrystalline activated carbon in the reactor is sampled and the mass of a single sample particle is detected until the weight of the single sample particle increases to 120-140% of the initial mass, indicating that the first ammonia modification is completed.
可选的,步骤S2中,所述一次改性产物和步骤S1剩余的砂粒从反应器排出后,含有一定的水,含水率为10-15wt%,可直接进行制粒,将实心化的微晶活性炭与破碎后的砂粒混合成砂粒化的微晶活性炭,粒径为0.6-2.5mm,自然冷却至室温。Optionally, in step S2, the once modified product and the remaining sand particles of step S1 contain a certain amount of water after being discharged from the reactor, with a water content of 10-15wt%, and can be directly granulated. The solidified microcrystalline activated carbon and the crushed sand particles are mixed into sand-granulated microcrystalline activated carbon with a particle size of 0.6-2.5mm, and then naturally cooled to room temperature.
可选的,步骤S3中,所述植物生物质选自农作物、草本植物、水生植物中的一种或几种,农作物、草本植物、水生植物的根、茎、叶均可;步骤S3使用的砂粒为上述破碎研磨后的砂粒(300-500目),植物生物质破碎后晒干再研磨至粒径为300-500目;Optionally, in step S3, the plant biomass is selected from one or more of crops, herbs, and aquatic plants, and the roots, stems, and leaves of crops, herbs, and aquatic plants may be used; the sand used in step S3 is the above-mentioned crushed and ground sand (300-500 mesh), and the plant biomass is crushed, dried, and then ground to a particle size of 300-500 mesh;
植物生物质与砂粒的质量比为(1.5-2.5):1,砂粒与砂粒化的微晶活性炭的质量比为(0.7-1.3):1,加水量不作限制,能制成糊状即可;The mass ratio of plant biomass to sand is (1.5-2.5):1, and the mass ratio of sand to sand-granulated microcrystalline activated carbon is (0.7-1.3):1. There is no limit on the amount of water added, as long as it can be made into a paste;
将步骤S2得到的砂粒化的微晶活性炭与上述糊状物搅拌混合均匀,使得砂粒化的微晶活性炭的表面均匀覆盖糊状物,然后将混合物整体过筛,筛上留下覆盖糊状物的砂粒化的微晶活性炭,再将筛上物收集后送入马弗炉,马弗炉加热温度为900-1100℃,加热5-7h,加热完取出自然冷却。The granulated microcrystalline activated carbon obtained in step S2 is stirred and mixed evenly with the above-mentioned paste, so that the surface of the granulated microcrystalline activated carbon is evenly covered with the paste, and then the mixture is sieved as a whole, leaving the granulated microcrystalline activated carbon covering the paste on the sieve, and then the sieve material is collected and sent to a muffle furnace. The heating temperature of the muffle furnace is 900-1100°C, and the heating is carried out for 5-7 hours. After heating, it is taken out and cooled naturally.
步骤S3在砂粒化的微晶活性炭的表面均匀涂覆一层生物质与砂粒的混合泥浆,再在马弗炉内高温焙烧,生物质碳化,在活性炭表面及靠近表面处,形成一层碳化物质,且具有微孔及内部孔道结构,比表面积较大,补充了活性炭由于嵌入砂粒而导致的孔隙减少、比表面积减少;同时,混合泥浆中含有砂粒,有利于砂粒嵌入新形成的碳化物质的孔隙内,促进碳化物质与活性炭的结合。所述再塑活性炭的粒径为0.8-3mm,其内部和靠近外部均嵌入了砂粒,使得活性炭的砂粒化改性更为均匀和彻底,在后续应用中,砂粒不易流失。Step S3: uniformly coat a layer of mixed slurry of biomass and sand on the surface of the sand-granulated microcrystalline activated carbon, and then calcine at high temperature in a muffle furnace to carbonize the biomass, forming a layer of carbonized material on the surface and near the surface of the activated carbon, and having micropores and internal pore structure, with a large specific surface area, which makes up for the reduction of pores and specific surface area of the activated carbon due to the embedding of sand particles; at the same time, the mixed slurry contains sand particles, which is conducive to the embedding of sand particles into the pores of the newly formed carbonized material, and promotes the combination of carbonized material and activated carbon. The particle size of the remolded activated carbon is 0.8-3mm, and sand particles are embedded inside and near the outside, so that the sand modification of the activated carbon is more uniform and thorough, and the sand particles are not easy to lose in subsequent applications.
可选的,步骤S4中,使用步骤S1的反应器,将再塑活性炭加入反应器内,加入25-28wt%的氨水,再塑活性炭与氨水的质量体积比为1g:(5-10)mL;50-80℃搅拌使得再塑活性炭充分分散,与氨水充分混合;反应器的排气管将挥发的氨气抽出,再返回反应器内部,在反应器底部形成氨气曝气;Optionally, in step S4, the reactor of step S1 is used, the remolded activated carbon is added into the reactor, 25-28wt% ammonia water is added, and the mass volume ratio of the remolded activated carbon to the ammonia water is 1g:(5-10)mL; the remolded activated carbon is stirred at 50-80°C to fully disperse and mix with the ammonia water; the exhaust pipe of the reactor extracts the volatilized ammonia gas and returns it to the inside of the reactor, forming ammonia aeration at the bottom of the reactor;
混合10-12h,然后排出氨水,加入若干次清水,继续搅拌,至反应器内pH为7-8,得到所述二次改性产物,再在烘箱内100℃干燥5-6h。Mix for 10-12 hours, then drain the ammonia water, add clean water several times, and continue stirring until the pH in the reactor is 7-8 to obtain the secondary modified product, and then dry it in an oven at 100°C for 5-6 hours.
本发明针对再塑活性炭进行第二次氨水改性,使用氨水作为还原改性剂,氨水相比氢氧化钠价格便宜,且氨水在较高温度下可以产生·NH2、·NH和·H等自由基,这些自由基与再塑活性炭表面的酸性基团反应生成氨基衍生物等物质,可以有效去除活性炭表面的酸性含氧基团,同时引入含氮碱性基团,增加活性炭表面的碱性基团数量,从而增强微晶活性炭表面的非极性。同时,氨水能促进再塑活性炭表面孔道的形成和发育,进一步提高其比表面积和孔隙度。The present invention performs a second ammonia modification on the remolded activated carbon, using ammonia as a reducing modifier. Ammonia is cheaper than sodium hydroxide, and can generate free radicals such as · NH2 , ·NH and ·H at a higher temperature. These free radicals react with the acidic groups on the surface of the remolded activated carbon to generate substances such as amino derivatives, which can effectively remove the acidic oxygen-containing groups on the surface of the activated carbon, and introduce nitrogen-containing basic groups to increase the number of basic groups on the surface of the activated carbon, thereby enhancing the non-polarity of the surface of the microcrystalline activated carbon. At the same time, ammonia can promote the formation and development of pores on the surface of the remolded activated carbon, further increasing its specific surface area and porosity.
可选的,步骤S5中,聚四氟乙烯溶液的浓度为30-40wt%,介质为水;二次改性产物与喷涂的用聚四氟乙烯溶液的质量体积比为1g:(0.01-0.25)mL,聚四氟乙烯在二次改性产物表面形成一层疏水层,提高活性炭的疏水性;Optionally, in step S5, the concentration of the polytetrafluoroethylene solution is 30-40wt%, and the medium is water; the mass volume ratio of the secondary modified product to the sprayed polytetrafluoroethylene solution is 1g:(0.01-0.25)mL, and the polytetrafluoroethylene forms a hydrophobic layer on the surface of the secondary modified product to improve the hydrophobicity of the activated carbon;
晾干的标准是活性炭颗粒表面不粘手;The standard for drying is that the surface of activated carbon particles is not sticky;
活性炭颗粒在马弗炉内进行程序升温干燥,以8-10℃升温至80℃,加热40min;以5-7℃升温至150℃,加热20min;以5-7℃升温至200℃,加热20min;加热完后,取出物料,自然冷却。The activated carbon particles are dried in a muffle furnace by programmed temperature increase, from 8-10°C to 80°C for 40 minutes; from 5-7°C to 150°C for 20 minutes; from 5-7°C to 200°C for 20 minutes; after heating, the material is taken out and cooled naturally.
上述加热能够固化聚四氟乙烯涂层,在聚四氟乙烯涂层固化的同时,由于聚四氟乙烯会向二次改性产物的孔隙通道内渗入一部分,程序升温以及加热温度的选择,能使聚四氟乙烯慢些固化,保持流动性,对二次改性产物的孔隙通道进行疏水改性,而不是迅速在颗粒表面固化,堵塞孔隙;上述程序升温的条件。The above heating can cure the polytetrafluoroethylene coating. While the polytetrafluoroethylene coating is curing, since part of the polytetrafluoroethylene will penetrate into the pore channels of the secondary modified product, the programmed temperature increase and the selection of the heating temperature can make the polytetrafluoroethylene cure slowly and maintain fluidity, thereby performing hydrophobic modification on the pore channels of the secondary modified product, rather than quickly curing on the particle surface and blocking the pores; the above programmed temperature increase conditions.
本发明在疏水改性方面,使用聚四氟乙烯,聚四氟乙烯具有耐腐蚀、耐老化、高润滑、不粘附等特性。此外,作为一种低表面能的分散液,表现出性质稳定、无毒害等特点,将其负载在微晶活性炭表面,在提高其表面疏水性的同时,还可以减缓微晶活性炭的“老化”过程。In the aspect of hydrophobic modification, the present invention uses polytetrafluoroethylene, which has the characteristics of corrosion resistance, aging resistance, high lubricity, non-adhesion, etc. In addition, as a dispersion liquid with low surface energy, it exhibits the characteristics of stable properties and non-toxicity, and is loaded on the surface of microcrystalline activated carbon, which can improve its surface hydrophobicity and slow down the "aging" process of the microcrystalline activated carbon.
本发明采用氨水改性和负载聚四氟乙烯疏水涂层的复合改性方法,可以进一步增强微晶活性炭表面的疏水性能,同时经过氨水改性后,可以避免负载在微晶活性炭表面的低表面能物质聚四氟乙烯的流失。制备的疏水活性炭对非极性物质的吸附效果好,吸附性能稳定。The present invention adopts a composite modification method of ammonia water modification and polytetrafluoroethylene hydrophobic coating loading, which can further enhance the hydrophobic property of the surface of microcrystalline activated carbon, and at the same time, after ammonia water modification, the loss of polytetrafluoroethylene, a low surface energy substance loaded on the surface of microcrystalline activated carbon, can be avoided. The prepared hydrophobic activated carbon has a good adsorption effect on non-polar substances and stable adsorption performance.
由于负载聚四氟乙烯涂层会不可避免的损失活性炭原有的部分孔隙,进而导致吸附性能下降。本发明创造性的采用两次氨水改性再配合生物质碳包覆的方法,经过第一次氨水改性,先对微晶活性炭进行处理,促进孔道孔隙生长,提前准备有利条件。再配置植物生物质和砂粒的糊状物,在焙烧条件下,重塑活性炭的结构,增加其整体的比表面积和孔隙孔道。同时,第一次氨水改性促进砂粒进入活性炭内部,提高实心度;挤出制粒成型和糊状物涂覆,都能提高砂粒在活性炭表面或外侧的负载量。再经过第二次氨水改性和疏水性改性,最终得到高比表面积、高孔隙率、高砂粒负载量、疏水性良好的复合改性砂粒化微晶活性炭。Since the loading of polytetrafluoroethylene coating will inevitably lose part of the original pores of activated carbon, the adsorption performance will be reduced. The present invention creatively adopts a method of twice ammonia modification combined with biomass carbon coating. After the first ammonia modification, the microcrystalline activated carbon is first treated to promote the growth of pores and channels, and favorable conditions are prepared in advance. Then, a paste of plant biomass and sand particles is configured, and under roasting conditions, the structure of the activated carbon is reshaped to increase its overall specific surface area and pore channels. At the same time, the first ammonia modification promotes the entry of sand particles into the interior of the activated carbon and improves the solidity; extrusion granulation molding and paste coating can increase the loading amount of sand particles on the surface or outside of the activated carbon. After the second ammonia modification and hydrophobic modification, a composite modified sand-granulated microcrystalline activated carbon with high specific surface area, high porosity, high sand particle loading amount and good hydrophobicity is finally obtained.
具体实施方式Detailed ways
实施例1Example 1
本实施例提供的一种复合改性砂粒化微晶活性炭的制备方法,包括以下步骤:The present embodiment provides a method for preparing a composite modified sand-granulated microcrystalline activated carbon, comprising the following steps:
S1:将原料微晶活性炭(椰壳质活性炭20g)和砂粒都清洗干净,在氨水中混合搅拌,进行第一次氨水改性,得到一次改性产物;S1: Clean the raw material microcrystalline activated carbon (20 g coconut shell activated carbon) and sand, mix and stir in ammonia water, perform the first ammonia water modification, and obtain a first modified product;
S2:将一次改性产物和步骤S1剩余的砂粒放入挤压设备中制粒成型,得到砂粒化的微晶活性炭;S2: putting the first modified product and the remaining sand particles in step S1 into an extrusion device for granulation to obtain sand-granulated microcrystalline activated carbon;
S3:将植物生物质、砂粒和水混合至呈糊状,该糊状物与砂粒化的微晶活性炭混合均匀,然后送入马弗炉内高温煅烧,得到再塑活性炭;S3: mixing plant biomass, sand and water into a paste, mixing the paste with the sanded microcrystalline activated carbon evenly, and then calcining at high temperature in a muffle furnace to obtain re-plasticized activated carbon;
S4:将再塑活性炭加入氨水中,进行第二次氨水改性,得到二次改性产物;S4: adding the remolded activated carbon into ammonia water to perform a second ammonia modification to obtain a secondary modified product;
S5:使用聚四氟乙烯溶液均匀喷涂二次改性产物的表面,进行疏水改性,晾干后送入马弗炉内干燥,得到最终的复合改性砂粒化微晶活性炭。S5: Use polytetrafluoroethylene solution to evenly spray the surface of the secondary modified product for hydrophobic modification, and then send it into a muffle furnace for drying after drying to obtain the final composite modified sand-granulated microcrystalline activated carbon.
步骤S1中,所述将原料微晶活性炭和砂粒都清洗干净,包括微晶活性炭的表面预处理和砂粒的表面预处理;In step S1, the raw material microcrystalline activated carbon and sand particles are cleaned, including surface pretreatment of the microcrystalline activated carbon and surface pretreatment of the sand particles;
微晶活性炭的表面预处理包括:(1)用蒸馏水冲洗微晶活性炭,将微晶活性炭表面的灰分冲洗干净,然后过滤;(2)将沥干水分的微晶活性炭浸渍于过量的蒸馏水中,超声清洗2h,去除微晶活性炭孔隙中的无机杂质,疏通微晶活性炭孔道;(3)用2mol/L氢氧化钠溶液清洗,去除微晶活性炭表面的有机杂质,之后用自来水水洗到中性为止,沥干水分后,烘干,备用;The surface pretreatment of the microcrystalline activated carbon includes: (1) washing the microcrystalline activated carbon with distilled water to clean the ash on the surface of the microcrystalline activated carbon, and then filtering; (2) immersing the drained microcrystalline activated carbon in excess distilled water, and ultrasonically cleaning it for 2 hours to remove inorganic impurities in the pores of the microcrystalline activated carbon and dredge the microcrystalline activated carbon pores; (3) washing with 2 mol/L sodium hydroxide solution to remove organic impurities on the surface of the microcrystalline activated carbon, and then washing with tap water until it is neutral, draining the water, drying it, and setting it aside;
砂粒的表面预处理包括:用自来水冲洗搓洗砂粒,将砂粒表面的泥土、杂质、灰尘等洗净,再用蒸馏水涮洗,烘干,备用。The surface pretreatment of the sand particles includes: washing and scrubbing the sand particles with tap water to clean the dirt, impurities, dust, etc. on the surface of the sand particles, then rinsing with distilled water, drying, and setting aside.
步骤S1中,清洗干净之后,微晶活性炭的粒径为0.5-0.8mm,砂粒破碎研磨至300-500目;微晶活性炭与砂粒的质量比为2:1。In step S1, after cleaning, the particle size of the microcrystalline activated carbon is 0.5-0.8 mm, and the sand is crushed and ground to 300-500 mesh; the mass ratio of the microcrystalline activated carbon to the sand is 2:1.
步骤S1中,所述第一次氨水改性具体为:先将微晶活性炭加入反应器内,加入25wt%的氨水,微晶活性炭与氨水的质量体积比为1g:10mL;搅拌使得微晶活性炭充分分散,再加入砂粒,80℃搅拌混合;反应器为密封的,且设有排气管,排气管连通反应器的顶部和底部,将挥发的氨气抽出,再返回反应器内部,在反应器底部形成氨气曝气,反应器内的温度有利于氨气重新溶入水中;In step S1, the first ammonia modification is specifically as follows: first, add microcrystalline activated carbon into a reactor, add 25wt% ammonia water, and the mass volume ratio of microcrystalline activated carbon to ammonia water is 1g:10mL; stir to fully disperse the microcrystalline activated carbon, then add sand particles, and stir and mix at 80°C; the reactor is sealed and provided with an exhaust pipe, which is connected to the top and bottom of the reactor, and the volatilized ammonia gas is extracted and returned to the reactor, forming ammonia aeration at the bottom of the reactor, and the temperature in the reactor is conducive to the ammonia gas re-dissolving into water;
改性后排出氨水,加入若干次清水,继续搅拌,至反应器内pH为7-8,得到所述一次改性产物和剩余的砂粒。After the modification, the ammonia water is discharged, and clean water is added several times, and stirring is continued until the pH in the reactor is 7-8, thereby obtaining the primary modified product and the remaining sand particles.
微晶活性炭充分分散后,取样检测微晶活性炭单粒的质量,取样检测10次,计算平均值,记为初始质量;第一次氨水改性过程中,对反应器内的微晶活性炭进行取样,并检测样品单粒的质量,直至样品单粒的重量增加到初始质量的120%,代表第一次氨水改性结束。After the microcrystalline activated carbon is fully dispersed, the mass of a single microcrystalline activated carbon particle is tested by sampling. The sampling is tested 10 times, and the average value is calculated and recorded as the initial mass. During the first ammonia modification process, the microcrystalline activated carbon in the reactor is sampled and the mass of a single sample particle is tested until the weight of the single sample particle increases to 120% of the initial mass, indicating that the first ammonia modification is completed.
步骤S2中,所述一次改性产物和步骤S1剩余的砂粒从反应器排出后,含水率为10wt%,可直接进行制粒,将实心化的微晶活性炭与破碎后的砂粒混合成砂粒化的微晶活性炭,平均粒径为1.5mm,自然冷却至室温。In step S2, after the primary modified product and the remaining sand particles in step S1 are discharged from the reactor, the moisture content is 10wt%, and granulation can be directly performed. The solidified microcrystalline activated carbon and the crushed sand particles are mixed into sand-granulated microcrystalline activated carbon with an average particle size of 1.5mm, and then naturally cooled to room temperature.
步骤S3中,所述植物生物质包括秸秆和野草,根、茎、叶都能用;步骤S3使用的砂粒为上述破碎研磨后的砂粒(300-500目),植物生物质破碎后晒干再研磨至粒径为300-500目;In step S3, the plant biomass includes straw and weeds, and roots, stems and leaves can all be used; the sand used in step S3 is the above-mentioned crushed and ground sand (300-500 mesh), and the plant biomass is crushed, dried and then ground to a particle size of 300-500 mesh;
植物生物质与砂粒的质量比为1.5:1,砂粒与砂粒化的微晶活性炭的质量比为0.7:1,加水量不作限制,能制成糊状即可;The mass ratio of plant biomass to sand is 1.5:1, and the mass ratio of sand to sand-granulated microcrystalline activated carbon is 0.7:1. There is no limit on the amount of water added, as long as it can be made into a paste;
将步骤S2得到的砂粒化的微晶活性炭与上述糊状物搅拌混合均匀,使得砂粒化的微晶活性炭的表面均匀覆盖糊状物,然后将混合物整体过筛,筛上留下覆盖糊状物的砂粒化的微晶活性炭,再将筛上物收集后送入马弗炉,马弗炉加热温度为1000℃,加热5h,加热完取出自然冷却。The granulated microcrystalline activated carbon obtained in step S2 is stirred and mixed evenly with the above-mentioned paste, so that the surface of the granulated microcrystalline activated carbon is evenly covered with the paste, and then the mixture is sieved as a whole, leaving the granulated microcrystalline activated carbon covering the paste on the sieve, and then the sieved material is collected and sent to a muffle furnace. The muffle furnace is heated to a temperature of 1000°C for 5 hours, and then taken out and naturally cooled after heating.
步骤S4中,使用步骤S1的反应器,将再塑活性炭加入反应器内,加入25wt%的氨水,再塑活性炭与氨水的质量体积比为1g:5mL;80℃搅拌使得再塑活性炭充分分散,与氨水充分混合;反应器的排气管将挥发的氨气抽出,再返回反应器内部,在反应器底部形成氨气曝气;In step S4, the reactor of step S1 is used, the remolded activated carbon is added into the reactor, 25 wt% ammonia water is added, and the mass volume ratio of the remolded activated carbon to the ammonia water is 1 g:5 mL; the remolded activated carbon is stirred at 80° C. to fully disperse and mix with the ammonia water; the exhaust pipe of the reactor extracts the volatilized ammonia gas and returns it to the reactor, forming ammonia aeration at the bottom of the reactor;
混合10h,然后排出氨水,加入若干次清水,继续搅拌,至反应器内pH为7-8,得到所述二次改性产物,再在烘箱内100℃干燥5-6h。The mixture was mixed for 10 hours, and then the ammonia water was discharged, and clean water was added several times and stirred continuously until the pH in the reactor was 7-8 to obtain the secondary modified product, which was then dried in an oven at 100° C. for 5-6 hours.
步骤S5中,聚四氟乙烯溶液的浓度为30wt%,介质为水;二次改性产物与喷涂的用聚四氟乙烯溶液的质量体积比为1g:0.01mL;In step S5, the concentration of the polytetrafluoroethylene solution is 30wt%, and the medium is water; the mass volume ratio of the secondary modified product to the polytetrafluoroethylene solution used for spraying is 1g:0.01mL;
晾干的标准是活性炭颗粒表面不粘手;The standard for drying is that the surface of activated carbon particles is not sticky;
活性炭颗粒在马弗炉内进行程序升温干燥,以10℃升温至80℃,加热40min;以5℃升温至150℃,加热20min;以5℃升温至200℃,加热20min;加热完后,取出物料,自然冷却,得到最终的复合改性砂粒化微晶活性炭。The activated carbon particles are dried by programmed temperature increase in a muffle furnace, with the temperature increased from 10°C to 80°C for 40 minutes; the temperature increased from 5°C to 150°C for 20 minutes; the temperature increased from 5°C to 200°C for 20 minutes; after heating, the material is taken out and cooled naturally to obtain the final composite modified sand-granulated microcrystalline activated carbon.
本实施例制得的最终的复合改性砂粒化微晶活性炭的总质量为58g,明显增重。The total mass of the final composite modified sand-granulated microcrystalline activated carbon prepared in this embodiment is 58 g, which is a significant increase in weight.
对比例1Comparative Example 1
本对比例提供的一种复合改性砂粒化微晶活性炭的制备方法,与实施例1相同,区别在于,不进行第一次氨水改性、第二次氨水改性,不实施步骤S3,The preparation method of a composite modified sand-granulated microcrystalline activated carbon provided in this comparative example is the same as that in Example 1, except that the first ammonia modification and the second ammonia modification are not performed, and step S3 is not implemented.
步骤S1的原料微晶活性炭和砂粒都清洗干净之后,直接将微晶活性炭和砂粒在水中混合均匀,得到含水率10wt%的混合物料,再放入挤压设备中制粒成型,得到砂粒化的微晶活性炭;再实施步骤S5,使用聚四氟乙烯溶液均匀喷涂砂粒化的微晶活性炭的表面,后续与实施例1相同。After the raw materials of step S1, the microcrystalline activated carbon and sand are cleaned, the microcrystalline activated carbon and sand are directly mixed evenly in water to obtain a mixture with a moisture content of 10wt%, and then put into an extrusion device for granulation to obtain sand-granulated microcrystalline activated carbon; then step S5 is implemented, and the surface of the sand-granulated microcrystalline activated carbon is evenly sprayed with a polytetrafluoroethylene solution, and the subsequent steps are the same as in Example 1.
对比例2Comparative Example 2
本对比例提供的一种复合改性砂粒化微晶活性炭的制备方法,与实施例1相同,区别在于,不进行第一次氨水改性,The preparation method of a composite modified sand-granulated microcrystalline activated carbon provided in this comparative example is the same as that in Example 1, except that the first ammonia modification is not performed.
步骤S1的原料微晶活性炭和砂粒都清洗干净之后,直接将微晶活性炭和砂粒在水中混合均匀,得到含水率10wt%的混合物料,再放入挤压设备中制粒成型,得到砂粒化的微晶活性炭。After the raw materials of the microcrystalline activated carbon and the sand particles in step S1 are cleaned, the microcrystalline activated carbon and the sand particles are directly mixed evenly in water to obtain a mixture with a moisture content of 10 wt%, and then put into an extrusion device for granulation to obtain sand-granulated microcrystalline activated carbon.
对比例3Comparative Example 3
本对比例提供的一种复合改性砂粒化微晶活性炭的制备方法,与实施例1相同,区别在于,不实施步骤S3,将砂粒化的微晶活性炭直接进行第二次氨水改性。The preparation method of a composite modified sand-granulated microcrystalline activated carbon provided in this comparative example is the same as that of Example 1, except that step S3 is not implemented, and the sand-granulated microcrystalline activated carbon is directly subjected to a second ammonia modification.
对比例4Comparative Example 4
本对比例提供的一种复合改性砂粒化微晶活性炭的制备方法,与实施例1相同,区别在于,不进行第二次氨水改性,使用聚四氟乙烯溶液均匀喷涂再塑活性炭,进行疏水改性。The preparation method of a composite modified sand-granulated microcrystalline activated carbon provided in this comparative example is the same as that of Example 1, except that no second ammonia modification is performed, and polytetrafluoroethylene solution is used to evenly spray the re-plasticized activated carbon for hydrophobic modification.
实施例2Example 2
本实施例提供的一种复合改性砂粒化微晶活性炭的制备方法,与实施例1相同,区别在于,步骤S1中微晶活性炭与氨水的质量体积比为1g:20mL。The method for preparing a composite modified sand-granulated microcrystalline activated carbon provided in this embodiment is the same as that in Embodiment 1, except that the mass volume ratio of the microcrystalline activated carbon to the ammonia water in step S1 is 1 g:20 mL.
实施例3Example 3
本实施例提供的一种复合改性砂粒化微晶活性炭的制备方法,与实施例1相同,区别在于,步骤S1中微晶活性炭与氨水的质量体积比为1g:9mL。The preparation method of a composite modified sand-granulated microcrystalline activated carbon provided in this embodiment is the same as that in Embodiment 1, except that the mass volume ratio of the microcrystalline activated carbon to the ammonia water in step S1 is 1 g:9 mL.
实施例4Example 4
本实施例提供的一种复合改性砂粒化微晶活性炭的制备方法,与实施例1相同,区别在于,步骤S3中植物生物质与砂粒的质量比为2.5:1。The method for preparing a composite modified sand-granulated microcrystalline activated carbon provided in this embodiment is the same as that in Embodiment 1, except that the mass ratio of plant biomass to sand in step S3 is 2.5:1.
实施例5Example 5
本实施例提供的一种复合改性砂粒化微晶活性炭的制备方法,与实施例1相同,区别在于,步骤S3中植物生物质与砂粒的质量比为1.4:1。The method for preparing a composite modified sand-granulated microcrystalline activated carbon provided in this embodiment is the same as that in Embodiment 1, except that the mass ratio of plant biomass to sand in step S3 is 1.4:1.
实施例6Example 6
本实施例提供的一种复合改性砂粒化微晶活性炭的制备方法,与实施例1相同,区别在于,步骤S3中砂粒与砂粒化的微晶活性炭的质量比为1.3:1。The method for preparing a composite modified sand-granulated microcrystalline activated carbon provided in this embodiment is the same as that in Embodiment 1, except that in step S3, the mass ratio of sand to sand-granulated microcrystalline activated carbon is 1.3:1.
实施例7Example 7
本实施例提供的一种复合改性砂粒化微晶活性炭的制备方法,与实施例1相同,区别在于,步骤S3中砂粒与砂粒化的微晶活性炭的质量比为0.6:1。The method for preparing a composite modified sand-granulated microcrystalline activated carbon provided in this embodiment is the same as that in Embodiment 1, except that in step S3, the mass ratio of sand to sand-granulated microcrystalline activated carbon is 0.6:1.
实施例8Example 8
本实施例提供的一种复合改性砂粒化微晶活性炭的制备方法,与实施例1相同,区别在于,步骤S4中再塑活性炭与氨水的质量体积比为1g:10mL。The present embodiment provides a method for preparing a composite modified sand-granulated microcrystalline activated carbon, which is the same as that of Embodiment 1, except that the mass volume ratio of the remolded activated carbon to the ammonia water in step S4 is 1 g:10 mL.
实施例9Embodiment 9
本实施例提供的一种复合改性砂粒化微晶活性炭的制备方法,与实施例1相同,区别在于,步骤S4中再塑活性炭与氨水的质量体积比为1g:4mL。The present embodiment provides a method for preparing a composite modified sand-granulated microcrystalline activated carbon, which is the same as that of Embodiment 1, except that the mass volume ratio of the remolded activated carbon to the ammonia water in step S4 is 1 g:4 mL.
实施例10Example 10
本实施例提供的一种复合改性砂粒化微晶活性炭的制备方法,与实施例1相同,区别在于,步骤S5中二次改性产物与喷涂的用聚四氟乙烯溶液的质量体积比为1g:0.25mL。The preparation method of a composite modified sand-granulated microcrystalline activated carbon provided in this embodiment is the same as that in Embodiment 1, except that the mass volume ratio of the secondary modified product to the sprayed polytetrafluoroethylene solution in step S5 is 1 g:0.25 mL.
实施例11Embodiment 11
本实施例提供的一种复合改性砂粒化微晶活性炭的制备方法,与实施例1相同,区别在于,步骤S5中二次改性产物与喷涂的用聚四氟乙烯溶液的质量体积比为1g:0.26mL。The preparation method of a composite modified sand-granulated microcrystalline activated carbon provided in this embodiment is the same as that in Embodiment 1, except that the mass volume ratio of the secondary modified product to the sprayed polytetrafluoroethylene solution in step S5 is 1 g:0.26 mL.
实施例12Example 12
本实施例提供的一种复合改性砂粒化微晶活性炭的制备方法,与实施例1相同,区别在于,步骤S5中马弗炉加热200℃,加热80min。The preparation method of a composite modified sand-granulated microcrystalline activated carbon provided in this embodiment is the same as that in Embodiment 1, except that in step S5, the muffle furnace is heated at 200° C. for 80 min.
表1实施例和对比例的复合改性砂粒化微晶活性炭比表面积比较Table 1 Comparison of specific surface areas of composite modified sand-granulated microcrystalline activated carbon of the embodiment and the comparative example
表2实施例的复合改性砂粒化微晶活性炭的疏水性比较Table 2 Comparison of hydrophobicity of composite modified sand-granulated microcrystalline activated carbon in the examples
由表1和表2可知,本发明提供复合改性砂粒化微晶活性炭的制备方法,在明显增重的基础上,依然具有较大的比表面积,不影响其吸附或催化性能,经过疏水改性,接触角达到170°以上。It can be seen from Table 1 and Table 2 that the present invention provides a method for preparing a composite modified sand-granulated microcrystalline activated carbon, which still has a large specific surface area on the basis of obvious weight gain, does not affect its adsorption or catalytic performance, and after hydrophobic modification, the contact angle reaches more than 170°.
Claims (9)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202311827712.6A CN117884095B (en) | 2023-12-28 | 2023-12-28 | A method for preparing composite modified sand-granulated microcrystalline activated carbon |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202311827712.6A CN117884095B (en) | 2023-12-28 | 2023-12-28 | A method for preparing composite modified sand-granulated microcrystalline activated carbon |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN117884095A CN117884095A (en) | 2024-04-16 |
| CN117884095B true CN117884095B (en) | 2024-07-26 |
Family
ID=90643775
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202311827712.6A Active CN117884095B (en) | 2023-12-28 | 2023-12-28 | A method for preparing composite modified sand-granulated microcrystalline activated carbon |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN117884095B (en) |
Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106807331A (en) * | 2016-12-23 | 2017-06-09 | 镇江华域环保设备制造有限公司 | The preparation of the composite filtering material of natural organic matter in removal drinking water |
| CN111821945A (en) * | 2020-07-07 | 2020-10-27 | 美埃(中国)环境科技股份有限公司 | Active carbon modification method for removing sulfur dioxide and hydrogen sulfide gas in air |
Family Cites Families (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US8555896B2 (en) * | 2007-12-19 | 2013-10-15 | Philip Morris Usa Inc. | Activated carbon from microcrystalline cellulose |
| CN112705166A (en) * | 2021-01-05 | 2021-04-27 | 桂林理工大学 | Preparation method and application of ammonia water modified eucalyptus activated carbon adsorbent |
| CN114044515B (en) * | 2021-11-04 | 2024-04-26 | 中欣环保科技有限公司 | A method for preparing desulfurization and denitrification activated carbon |
| CN117018759A (en) * | 2023-09-25 | 2023-11-10 | 中国电建集团中南勘测设计研究院有限公司 | Alkalescent zinc composite rock extruded carbon filter element and preparation method thereof |
-
2023
- 2023-12-28 CN CN202311827712.6A patent/CN117884095B/en active Active
Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106807331A (en) * | 2016-12-23 | 2017-06-09 | 镇江华域环保设备制造有限公司 | The preparation of the composite filtering material of natural organic matter in removal drinking water |
| CN111821945A (en) * | 2020-07-07 | 2020-10-27 | 美埃(中国)环境科技股份有限公司 | Active carbon modification method for removing sulfur dioxide and hydrogen sulfide gas in air |
Also Published As
| Publication number | Publication date |
|---|---|
| CN117884095A (en) | 2024-04-16 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN111135790B (en) | A kind of phosphorus removal composite adsorbent and its preparation method and application in sewage treatment | |
| CN109534432B (en) | Preparation method of biochar modified material for removing phosphorus in eutrophic water body | |
| CN1272241C (en) | Shaped activated carbon | |
| CN105536704A (en) | Calcium modified biochar and preparation method and application thereof | |
| CN106000334A (en) | Modified reed biomass charcoal and preparing method and application thereof | |
| WO2022088825A1 (en) | Composite treatment and remediation technology for polluted water and soil | |
| CN111701568A (en) | A kind of high adsorption performance eggshell straw biochar composite microsphere phosphorus removal adsorbent and its preparation method and application | |
| CN110523379A (en) | A low-cost preparation method of porous carbon | |
| CN104587960A (en) | Preparation method of dephosphorization high-temperature modified aluminum sludge | |
| CN106861622A (en) | A kind of water treatment agent for processing eutrophication water | |
| KR101931088B1 (en) | Method of preparing activated carbon for filter using biomass and method of preparing filter using the same | |
| CN116850961B (en) | Modified sludge-based porous biochar and preparation method thereof | |
| CN101234332A (en) | A method for preparing active adsorption material by using sludge and waste graphite | |
| CN113198417A (en) | Iron-based biochar sponge composite material and preparation method and application thereof | |
| CN107555521A (en) | A kind of porous biomass microspheres for heavy metal sewage treatment and preparation method thereof | |
| CN114797767A (en) | Modified leaf biochar and preparation method and application thereof | |
| CN107185505B (en) | A kind of modified zeolite-polyurethane composite filler and its modification method and application | |
| CN117884095B (en) | A method for preparing composite modified sand-granulated microcrystalline activated carbon | |
| CN116534856B (en) | A method for preparing biomass charcoal by co-pyrolysis of biomass and biomass charcoal | |
| CN108993393A (en) | A kind of preparation based on fish-bone biomass carbon greasy dirt adsorbent material | |
| CN113457622A (en) | Preparation of aluminum-manganese composite modified biochar and application of aluminum-manganese composite modified biochar in phosphorus removal | |
| KR20180058239A (en) | Method for producing activated carbon for filter using biomass | |
| CN118204062A (en) | Modified biochar, preparation method and application | |
| CN116899566A (en) | Modified biochar and its preparation method and application | |
| CN103663606B (en) | A kind of method utilizing sunflower seed shell biomass charcoal sorbent material to remove waste water Malachite Green |
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 | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant | ||
| CP03 | Change of name, title or address | ||
| CP03 | Change of name, title or address |
Address after: 450047 Henan Province, Zhengzhou Economic and Technological Development Zone, Xunjiang East Road No. 126 Patentee after: Huaxia Bishui Environmental Protection Technology Co.,Ltd. Country or region after: China Address before: No. 906, 9th Floor, Building 2, Xinghua Science and Technology Industrial Park, West of Second Street, South of Jingnan Road, Zhengzhou Area (Jingkai), Free Trade Pilot Zone, Zhengzhou City, Henan Province, 450199 Patentee before: Huaxia Bishui Environmental Protection Technology Co.,Ltd. Country or region before: China |