CN107285309A - A kind of oily sludge and the biomass combined method for preparing multistage mesoporous activated carbon - Google Patents
A kind of oily sludge and the biomass combined method for preparing multistage mesoporous activated carbon Download PDFInfo
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- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 title claims abstract description 114
- 239000002028 Biomass Substances 0.000 title claims abstract description 50
- 239000010802 sludge Substances 0.000 title claims abstract description 48
- 238000000034 method Methods 0.000 title claims abstract description 36
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- 239000011148 porous material Substances 0.000 claims abstract description 26
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 25
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- 229910052593 corundum Inorganic materials 0.000 claims description 17
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- 238000001994 activation Methods 0.000 abstract description 16
- 238000002360 preparation method Methods 0.000 abstract description 10
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- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 28
- 239000000203 mixture Substances 0.000 description 27
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- RBTBFTRPCNLSDE-UHFFFAOYSA-N 3,7-bis(dimethylamino)phenothiazin-5-ium Chemical compound C1=CC(N(C)C)=CC2=[S+]C3=CC(N(C)C)=CC=C3N=C21 RBTBFTRPCNLSDE-UHFFFAOYSA-N 0.000 description 7
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- C01—INORGANIC CHEMISTRY
- C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
- C01P2004/00—Particle morphology
- C01P2004/01—Particle morphology depicted by an image
- C01P2004/03—Particle morphology depicted by an image obtained by SEM
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
- C01P2006/00—Physical properties of inorganic compounds
- C01P2006/12—Surface area
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
- C01P2006/00—Physical properties of inorganic compounds
- C01P2006/14—Pore volume
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
- C01P2006/00—Physical properties of inorganic compounds
- C01P2006/16—Pore diameter
- C01P2006/17—Pore diameter distribution
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Abstract
本发明公开了一种含油污泥与生物质复合制备多级孔活性炭的方法,包括以下步骤:将含油污泥离心取上层油相,与生物质颗粒混合后放入管式炉中,在惰性气氛保护下以2‑5℃/min升温至350‑450℃并保温90‑120min,冷却至室温完成碳化过程;然后将固体与KOH均匀混合,在惰性气氛保护下升温至800‑850℃保温60‑90min,自然冷却完成活化工艺;将所得固体洗涤烘干研磨得到所述多级孔活性炭。制备得到的活性炭比表面积超过1800m2/g,平均孔径3nm左右。本发明以生物质和高粘度、成分复杂的含油污泥为原料,具有原料来源广、成本低、设备简单、无污染,制备过程中的副产物能够回收利用的优点。
The invention discloses a method for compounding oily sludge and biomass to prepare multi-level porous activated carbon, which comprises the following steps: centrifuging the oily sludge to take the upper oil phase, mixing it with biomass particles, putting it into a tube furnace, Under the protection of the atmosphere, the temperature was raised to 350-450°C at 2-5°C/min and kept for 90-120min, cooled to room temperature to complete the carbonization process; then the solid and KOH were evenly mixed, and the temperature was raised to 800-850°C under the protection of an inert atmosphere and kept for 60 minutes. ‑90min, natural cooling to complete the activation process; the resulting solids were washed, dried and ground to obtain the hierarchically porous activated carbon. The prepared activated carbon has a specific surface area of more than 1800m 2 /g and an average pore diameter of about 3nm. The invention uses biomass and oily sludge with high viscosity and complex components as raw materials, and has the advantages of wide source of raw materials, low cost, simple equipment, no pollution, and the by-products in the preparation process can be recycled.
Description
技术领域technical field
本发明涉及石油化工行业含油污泥有毒有害固体废弃物和农业生产过程中生物质废弃物资源化利用技术领域,特别涉及一种含油污泥与生物质复合制备多级孔活性炭的方法。The invention relates to the technical field of oily sludge toxic and harmful solid waste in the petrochemical industry and the resource utilization of biomass waste in the agricultural production process, in particular to a method for preparing multi-level porous activated carbon by compounding oily sludge and biomass.
背景技术Background technique
含油污泥是在原油勘探、开采、运输、储存、清罐、炼制等过程中产生的一种水、油、渣高度乳化的粘稠状固体废弃物。含油污泥成分复杂,含有大量原油、沥青质、蜡质、水分、固体颗粒以及各种药剂,具有难降解、有毒、有害等特点,不易处理且污染环境,属于国家危险废物名录中危险废物类别HW08。通常,含油污泥含有30-50%的水,10-12%的固体颗粒和30-50%的油,而油相又由饱和烃、芳香烃、胶质和沥青质组成。胶质和沥青质的存在促进了含油污泥中乳化物的稳定性,大大增加了含油污泥的处理难度。目前,焚烧法是含油污泥无害化处理方法之一,但是存在着成本高、易产生二次污染的问题。而资源化处理方法主要包括:机械分离、化学萃取和热转化方法,但是由于含油污泥的高粘度和高毒性,也存在效果不理想、操作复杂等不足。Oily sludge is a kind of viscous solid waste with highly emulsified water, oil and slag produced in the process of crude oil exploration, mining, transportation, storage, tank cleaning and refining. The composition of oily sludge is complex, containing a large amount of crude oil, asphaltene, wax, moisture, solid particles and various chemicals. It is difficult to degrade, toxic, harmful, etc. It is not easy to handle and pollutes the environment. It belongs to the category of hazardous waste in the national hazardous waste list. HW08. Generally, oily sludge contains 30-50% water, 10-12% solid particles and 30-50% oil, and the oil phase is composed of saturated hydrocarbons, aromatic hydrocarbons, colloids and asphaltenes. The presence of colloids and asphaltene promotes the stability of the emulsion in oily sludge, which greatly increases the difficulty of oily sludge treatment. At present, the incineration method is one of the harmless treatment methods for oily sludge, but there are problems of high cost and easy to produce secondary pollution. The resource treatment methods mainly include: mechanical separation, chemical extraction and thermal conversion methods, but due to the high viscosity and high toxicity of oily sludge, there are also shortcomings such as unsatisfactory results and complicated operations.
生物质作为一种农业废弃物,具有来源广泛、产量高、价格低廉、生长周期短等优势,而且与原料煤相比,生物质无粘结性、无需破黏等特殊处理。我国作为一个农业大国,每年的生物质如秸秆、稻壳、玉米芯等产量极大。传统的生物质处置方法,如焚烧法,容易造成资源浪费和环境污染。目前生物质的资源化利用方法主要为热转化方法,但是也存在着产物品质不高、设备复杂等问题。As a kind of agricultural waste, biomass has the advantages of wide sources, high output, low price, and short growth cycle. Compared with raw coal, biomass has no cohesiveness and does not need special treatment such as breaking sticks. As a large agricultural country, our country produces a huge amount of biomass such as straw, rice husk, and corn cob every year. Traditional biomass disposal methods, such as incineration, are prone to waste of resources and environmental pollution. At present, the resource utilization method of biomass is mainly thermal conversion method, but there are also problems such as low product quality and complicated equipment.
活性炭是一种比表面积高,表面具有多孔结构的材料。由于其具有独特的吸附表面结构特性和表面化学性能,活性炭具有较强的吸附性能和催化性能,活性炭制备原料充足且安全性高、耐酸碱、耐热、不溶于水和有机溶剂、易再生,是一种环境友好型吸附剂。目前,活性炭已广泛应用于化工、环保、食品加工、冶金、药物精制、军事化学防护等各个领域。普通活性炭材料是由煤、椰壳、果壳、木屑等原料经过加工处理所得的无定形碳,比表面积通常小于1100m2/g且多以介孔为主。而用于特殊用途的活性炭是由昂贵的沥青质和高分子聚合材料制得,比表面积大于2000m2/g。多级孔活性炭指的是活性炭中同时分布有大量的介孔和微孔,对气体分子和液相中的离子及有机物污染物具有很高的吸附能力。Activated carbon is a material with a high specific surface area and a porous structure on the surface. Due to its unique adsorption surface structure characteristics and surface chemical properties, activated carbon has strong adsorption performance and catalytic performance. The raw materials for the preparation of activated carbon are sufficient and safe, acid and alkali resistance, heat resistance, insoluble in water and organic solvents, and easy to regenerate , is an environmentally friendly adsorbent. At present, activated carbon has been widely used in chemical industry, environmental protection, food processing, metallurgy, drug refining, military chemical protection and other fields. Ordinary activated carbon materials are amorphous carbon obtained by processing raw materials such as coal, coconut shells, fruit shells, and wood chips. The specific surface area is usually less than 1100m 2 /g and mostly mesoporous. The activated carbon used for special purposes is made of expensive asphaltene and high molecular polymer materials, with a specific surface area greater than 2000m 2 /g. Hierarchical activated carbon refers to a large number of mesopores and micropores distributed in activated carbon at the same time, which has a high adsorption capacity for gas molecules and ions and organic pollutants in the liquid phase.
以含油污泥和生物质混合料的多级孔活性炭制备技术属于危险固体废弃物的资源化利用领域。本发明以原油生产加工过程中产生的含油污泥和农业生产中产生的生物质混合料为对象,按照“无害化、减量化、资源化”的原则,针对含油污泥本身难处理、沥青质含量高,生物质产量大等特点,研究含油污泥和生物质混合料制备多级孔活性炭技术。为含油污泥和生物质的资源化利用及其工业化生产提供了新思路和新方法,具有重要现实意义。The preparation technology of multi-level porous activated carbon from oily sludge and biomass mixture belongs to the field of resource utilization of hazardous solid waste. The present invention takes the oily sludge produced in the process of crude oil production and processing and the biomass mixture produced in agricultural production as objects, and according to the principle of "harmless, reduced, resourceful", aims at oily sludge itself which is difficult to handle, Due to the characteristics of high asphaltene content and large biomass output, the technology of preparing hierarchical porous activated carbon from oily sludge and biomass mixture is studied. It provides new ideas and new methods for resource utilization and industrial production of oily sludge and biomass, and has important practical significance.
中国专利CN201611234477.1公开了一种生物质-渣油共炼焦活性炭的制备方法,在惰性气体保护下将生物质和渣油进行共焦化反应,得到共炼焦;对共炼焦依次进行亲水性预处理和除灰分预处理,得到预处理后的共炼焦;在惰性气体保护条件下,将预处理后的共炼焦焙烧,得到生物基炭材料;在惰性气体保护下,将生物基碳材料与活化剂进行活化反应,得到生物质-渣油共炼焦活性炭具有高比表面积、高孔容特性。Chinese patent CN201611234477.1 discloses a preparation method of biomass-residue co-coking activated carbon. Under the protection of inert gas, biomass and residue are subjected to co-coking reaction to obtain co-coking; treatment and ash removal pretreatment to obtain pretreated co-coking; under the protection of inert gas, roast the pre-treated co-coking to obtain bio-based carbon materials; Activated carbon with high specific surface area and high pore volume.
发明内容Contents of the invention
本发明的目的在于一种含油污泥与生物质复合制备多级孔活性炭的方法,为含油污泥和生物质废弃物的资源化利用提供一种新思路。本发明的优点在于:成本低、易操作、无污染、设备简单投入少,并且制备过程中的副产物能够回收再利用,能够充分回收利用储运油泥和生物质的各个组分。The purpose of the present invention is a method for compounding oily sludge and biomass to prepare hierarchical porous activated carbon, and provides a new idea for resource utilization of oily sludge and biomass waste. The invention has the advantages of low cost, easy operation, no pollution, simple equipment and low investment, and by-products in the preparation process can be recycled and reused, and various components of oil sludge and biomass can be fully recycled and utilized.
为了达到上述目的,本发明采用的技术方案包括:In order to achieve the above object, the technical scheme adopted in the present invention comprises:
一种含油污泥和生物质复合制备多级孔活性炭的方法,所述活性炭的比表面积在1800m2/g以上,孔径分布主要在0.5-4nm之间,平均孔径在3nm左右,孔容积大于1.5cm3/g;包括以下步骤:A method for preparing hierarchically porous activated carbon by compounding oily sludge and biomass, the specific surface area of the activated carbon is above 1800m 2 /g, the pore size distribution is mainly between 0.5-4nm, the average pore size is about 3nm, and the pore volume is greater than 1.5 cm 3 /g; including the following steps:
步骤(1)、将含油污泥离心分离后,去除中层的水分和底层的固体渣,得到上层油相产物;Step (1), after centrifuging the oily sludge, removing the moisture in the middle layer and the solid slag in the bottom layer to obtain an oil phase product in the upper layer;
步骤(2)、将生物质破碎研磨,得到生物质颗粒;Step (2), crushing and grinding the biomass to obtain biomass particles;
步骤(3)、将步骤(1)所得的油相产物和步骤(2)所得的生物质颗粒以质量比1:(0.2-1)均匀混合后,放入刚玉坩埚中,在惰性气氛保护下以2-5℃/min升温至350-450℃并保温90-120min,自然冷却到室温后得到块状固体,研磨成颗粒;Step (3), after uniformly mixing the oil phase product obtained in step (1) and the biomass particles obtained in step (2) at a mass ratio of 1: (0.2-1), put them into a corundum crucible, and under the protection of an inert atmosphere Raise the temperature at 2-5°C/min to 350-450°C and keep it warm for 90-120min, cool down to room temperature naturally to obtain blocky solids, and grind them into granules;
步骤(4)、将步骤(3)得到固体颗粒与KOH粉末均匀混合后放入刚玉坩埚中,在惰性气氛保护下升温至800-850℃,保温60-90min,自然冷却到室温,取出后用去离子水冲洗至滤液呈中性,干燥研磨得到所述多级孔活性炭。Step (4), uniformly mix the solid particles obtained in step (3) with KOH powder and put them into a corundum crucible, raise the temperature to 800-850°C under the protection of an inert atmosphere, keep it warm for 60-90min, cool naturally to room temperature, take it out and use Rinse with deionized water until the filtrate is neutral, dry and grind to obtain the hierarchically porous activated carbon.
所述的含油污泥为原油生产加工过程中产生的一种高粘度、成分复杂的黑色乳状物。The oily sludge is a black emulsion with high viscosity and complex components produced during crude oil production and processing.
所述的生物质为农业生产过程中产生的如秸秆、稻壳、等固体废弃物。The biomass is solid waste such as straw, rice husk, etc. produced in the agricultural production process.
步骤(1)所述的离心参数为:3000-4000rpm,离心10-20min,过程温度为15-20℃。The centrifugation parameters described in step (1) are: 3000-4000rpm, centrifugation for 10-20min, and the process temperature is 15-20°C.
步骤(2)所述的生物质颗粒为60-80目左右。The biomass particles described in step (2) are about 60-80 mesh.
步骤(3)所述的研磨颗粒大小为1.5-2mmThe grinding particle size described in step (3) is 1.5-2mm
步骤(4)所述固体颗粒与KOH粉末的混合质量比为1:(3-5)。The mixing mass ratio of solid particles and KOH powder in step (4) is 1:(3-5).
本发明含油污泥与生物质复合制备多级孔活性炭的方法具有以下优点:The method for preparing hierarchically porous activated carbon by compounding oily sludge and biomass of the present invention has the following advantages:
1.制备工艺简单:通过含油污泥离心、生物质破碎、原料混合、碳化、活化、洗涤、干燥、研磨等一系列方法,对含油污泥和生物质进行处理,制备得到多级孔活性炭,制备工艺简单,装置易得,操作步骤少,可行性高;1. The preparation process is simple: through a series of methods such as oily sludge centrifugation, biomass crushing, raw material mixing, carbonization, activation, washing, drying, grinding, etc., the oily sludge and biomass are treated to prepare hierarchical porous activated carbon. The preparation process is simple, the device is easy to obtain, the operation steps are few, and the feasibility is high;
2.原材料和添加剂易得:制备所需的含油污泥为原油生产加工过程中产生的危险固体废弃物;制备所需的生物质是农业生产过程中产生的固体废弃物,产量大;制备过程中所需的添加剂易得;2. Raw materials and additives are easy to obtain: the oily sludge required for preparation is hazardous solid waste generated during crude oil production and processing; the biomass required for preparation is solid waste generated during agricultural production, and the output is large; the preparation process The required additives are readily available;
3.原料充分利用:含油污泥和生物质混合料碳化过程中产生油产品粘度低、分子量小,经处理后可作为优质油产品回收。3. Full utilization of raw materials: The oil product produced during the carbonization process of oily sludge and biomass mixture has low viscosity and small molecular weight, and can be recycled as high-quality oil product after treatment.
4.制备的多级孔活性炭品质高:比表面积不小于1800m2/g,孔径分布主要在0.5-4nm之间,平均孔径在3nm左右,孔容积大于1.5cm3/g。4. The prepared hierarchical porous activated carbon is of high quality: the specific surface area is not less than 1800m 2 /g, the pore size distribution is mainly between 0.5-4nm, the average pore size is about 3nm, and the pore volume is greater than 1.5cm 3 /g.
附图说明Description of drawings
图1是本发明含油污泥与生物质复合制备多级孔活性炭的方法流程图。Fig. 1 is a flow chart of the method for preparing hierarchically porous activated carbon by compounding oily sludge and biomass in the present invention.
图2是本发明实施例1所得活性炭的扫描电镜图。Figure 2 is a scanning electron micrograph of the activated carbon obtained in Example 1 of the present invention.
图3是本发明实施例1所得活性炭的氮吸附-脱附等温线图。Fig. 3 is a nitrogen adsorption-desorption isotherm diagram of the activated carbon obtained in Example 1 of the present invention.
图4是本发明实施例1所得活性炭的孔径分布图。Fig. 4 is the pore size distribution diagram of the activated carbon obtained in Example 1 of the present invention.
具体实施方式detailed description
下面,本发明将用实施例进一步说明,但不局限于以下实施例中的任一个。图1是本发明含油污泥与生物质复合制备多级孔活性炭的方法流程图。Hereinafter, the present invention will be further illustrated by examples, but not limited to any one of the following examples. Fig. 1 is a flow chart of the method for preparing hierarchically porous activated carbon by compounding oily sludge and biomass in the present invention.
实施例1Example 1
以沥青质质量含量为6%的含油污泥作为原料,在20℃下经过3000rpm、10min的离心处理后去除底部固体颗粒和水分,取上层油相。以稻壳作为生物质原料,经过破碎研磨后得到60-80目的稻壳颗粒。将上层油相和稻壳颗粒以质量比1:0.25均匀混合。将混合物放入刚玉坩埚中在管式炉中以氮气为气氛加热碳化,加热条件为4℃/min,升温至400℃后保温120min,自然冷却至室温后得到固体产物。将固体产物研磨至2mm左右的固体颗粒,并与KOH粉末以质量比1:4均匀混合后放入刚玉坩埚中,并置于管式炉中加热活化,活化过程中以氮气为保护气氛,加热温度为800℃,保温60min后自然冷却至室温。得到的产物经过去离子水冲洗至滤液呈中性后,烘干研磨得到所述多级孔活性炭,活性炭扫描电镜如图2所示。所制备的活性炭比表面积为1849m2/g,孔容积为1.58cm3/g,如图3可见所制备的活性炭在相对压力低于0.1以及0.1-0.9之间的吸附量均有明显增加,说明活性炭中同时存在微孔和介孔。如图4可见活性炭孔径分布在0.8-4.1nm之间,平均孔径为2.81nm,对水体中亚甲基蓝的吸附量为931mg/g。Oily sludge with a mass content of asphaltene of 6% was used as a raw material, and after centrifugation at 20° C. at 3000 rpm for 10 min, the solid particles and moisture at the bottom were removed, and the upper oil phase was taken. Rice husks are used as biomass raw materials, and rice husk particles of 60-80 meshes are obtained after crushing and grinding. Mix the upper oil phase and rice husk particles evenly at a mass ratio of 1:0.25. The mixture was put into a corundum crucible and heated and carbonized in a tube furnace with nitrogen as an atmosphere, the heating condition was 4°C/min, the temperature was raised to 400°C and kept for 120 minutes, and the solid product was obtained after natural cooling to room temperature. Grind the solid product to a solid particle of about 2mm, and mix it with KOH powder at a mass ratio of 1:4, put it into a corundum crucible, and place it in a tube furnace for heating and activation. During the activation process, nitrogen is used as a protective atmosphere and heated The temperature is 800°C, and after 60 minutes of heat preservation, it is naturally cooled to room temperature. The obtained product was washed with deionized water until the filtrate was neutral, then dried and ground to obtain the hierarchically porous activated carbon. The activated carbon scanning electron microscope is shown in FIG. 2 . The specific surface area of the prepared activated carbon is 1849m 2 /g, and the pore volume is 1.58cm 3 /g. As can be seen in Figure 3, the adsorption capacity of the prepared activated carbon increases significantly when the relative pressure is lower than 0.1 and between 0.1 and 0.9, indicating that Both micropores and mesopores exist in activated carbon. As shown in Figure 4, the pore size distribution of activated carbon is between 0.8-4.1nm, the average pore size is 2.81nm, and the adsorption capacity of methylene blue in water is 931mg/g.
实施例2Example 2
以沥青质质量含量为11%的含油污泥作为原料,在20℃下经过3500rpm、10min的离心处理后去除底部固体颗粒和水分,取上层油相。以稻壳作为生物质原料,经过破碎研磨后得到60-80目的稻壳颗粒。将上层油相和稻壳颗粒以质量比1:0.25均匀混合。将混合物放入刚玉坩埚中在管式炉中以氮气为气氛加热碳化,加热条件为4℃/min,升温至400℃后保温120min,自然冷却至室温后得到固体产物。将固体产物研磨至2mm左右的固体颗粒,并与KOH粉末以质量比1:4均匀混合后放入刚玉坩埚中,并置于管式炉中加热活化,活化过程中以氮气为保护气氛,加热温度为800℃,保温60min后自然冷却至室温。得到的产物经过去离子水冲洗至滤液呈中性后,烘干研磨得到所述多级孔活性炭。所制备的活性炭比表面积为2142m2/g,孔容积为1.85cm3/g,平均孔径为3.04nm,对水体中亚甲基蓝的吸附量为1038mg/g。Oily sludge with an asphaltene mass content of 11% was used as a raw material, and after centrifugation at 3500 rpm for 10 min at 20°C, the solid particles and water at the bottom were removed, and the upper oil phase was taken. Rice husks are used as biomass raw materials, and rice husk particles of 60-80 meshes are obtained after crushing and grinding. Mix the upper oil phase and rice husk particles evenly at a mass ratio of 1:0.25. The mixture was put into a corundum crucible and heated and carbonized in a tube furnace with nitrogen as an atmosphere. The heating condition was 4°C/min. After the temperature was raised to 400°C, it was kept for 120 minutes, and a solid product was obtained after natural cooling to room temperature. Grind the solid product to a solid particle of about 2mm, and mix it with KOH powder at a mass ratio of 1:4, put it into a corundum crucible, and place it in a tube furnace for heating and activation. During the activation process, use nitrogen as a protective atmosphere and heat The temperature is 800°C, and after 60 minutes of heat preservation, it is naturally cooled to room temperature. The obtained product is washed with deionized water until the filtrate is neutral, then dried and ground to obtain the hierarchically porous activated carbon. The prepared activated carbon has a specific surface area of 2142m 2 /g, a pore volume of 1.85cm 3 /g, an average pore diameter of 3.04nm, and an adsorption capacity of methylene blue in water of 1038mg/g.
实施例3Example 3
以沥青质质量含量为11%的含油污泥作为原料,在20℃下经过4000rpm、15min的离心处理后去除底部固体颗粒和水分,取上层油相。以稻壳作为生物质原料,经过破碎研磨后得到60-80目的稻壳颗粒。将上层油相和稻壳颗粒以质量比1:1均匀混合。将混合物放入刚玉坩埚中在管式炉中以氮气为气氛加热碳化,加热条件为4℃/min,升温至400℃后保温120min,自然冷却至室温后得到固体产物。将固体产物研磨至2mm左右的固体颗粒,并与KOH粉末以质量比1:4均匀混合后放入刚玉坩埚中,并置于管式炉中加热活化,活化过程中以氮气为保护气氛,加热温度为800℃,保温60min后自然冷却至室温。得到的产物经过去离子水冲洗至滤液呈中性后,烘干研磨得到所述多级孔活性炭。所制备的活性炭比表面积为1976m2/g,孔容积为1.68cm3/g,平均孔径为2.74nm,对水体中亚甲基蓝的吸附量为891mg/g。Oily sludge with an asphaltene mass content of 11% was used as a raw material, and after centrifugation at 20°C at 4000 rpm for 15 minutes, the solid particles and water at the bottom were removed, and the upper oil phase was taken. Rice husks are used as biomass raw materials, and rice husk particles of 60-80 meshes are obtained after crushing and grinding. Mix the upper oil phase and rice husk particles evenly at a mass ratio of 1:1. The mixture was put into a corundum crucible and heated and carbonized in a tube furnace with nitrogen as an atmosphere. The heating condition was 4°C/min. After the temperature was raised to 400°C, it was kept for 120 minutes, and a solid product was obtained after natural cooling to room temperature. Grind the solid product to a solid particle of about 2mm, and mix it with KOH powder at a mass ratio of 1:4, put it into a corundum crucible, and place it in a tube furnace for heating and activation. During the activation process, use nitrogen as a protective atmosphere and heat The temperature is 800°C, and after 60 minutes of heat preservation, it is naturally cooled to room temperature. The obtained product is washed with deionized water until the filtrate is neutral, then dried and ground to obtain the hierarchically porous activated carbon. The prepared activated carbon has a specific surface area of 1976m 2 /g, a pore volume of 1.68cm 3 /g, an average pore diameter of 2.74nm, and an adsorption capacity of methylene blue in water of 891mg/g.
实施例4Example 4
以沥青质质量含量为11%的含油污泥作为原料,在20℃下经过3000rpm、15min的离心处理后去除底部固体颗粒和水分,取上层油相。以稻壳作为生物质原料,经过破碎研磨后得到60-80目的稻壳颗粒。将上层油相和稻壳颗粒以质量比1:0.3均匀混合。将混合物放入刚玉坩埚中在管式炉中以氮气为气氛加热碳化,加热条件为4℃/min,升温至400℃后保温120min,自然冷却至室温后得到固体产物。将固体产物研磨至2mm左右的固体颗粒,并与KOH粉末以质量比1:4均匀混合后放入刚玉坩埚中,并置于管式炉中加热活化,活化过程中以氮气为保护气氛,加热温度为800℃,保温60min后自然冷却至室温。得到的产物经过去离子水冲洗至滤液呈中性后,烘干研磨得到所述多级孔活性炭。所制备的活性炭比表面积为2254m2/g,孔容积为1.87cm3/g,平均孔径为3.12nm,对水体中亚甲基蓝的吸附量为1044mg/g。Oily sludge with an asphaltene mass content of 11% was used as a raw material, and after centrifugation at 20°C at 3000 rpm for 15 minutes, the solid particles and water at the bottom were removed, and the upper oil phase was taken. Rice husks are used as biomass raw materials, and rice husk particles of 60-80 meshes are obtained after crushing and grinding. Mix the upper oil phase and rice husk particles evenly at a mass ratio of 1:0.3. The mixture was put into a corundum crucible and heated and carbonized in a tube furnace with nitrogen as an atmosphere. The heating condition was 4°C/min. After the temperature was raised to 400°C, it was kept for 120 minutes, and a solid product was obtained after natural cooling to room temperature. Grind the solid product to a solid particle of about 2mm, and mix it with KOH powder at a mass ratio of 1:4, put it into a corundum crucible, and place it in a tube furnace for heating and activation. During the activation process, use nitrogen as a protective atmosphere and heat The temperature is 800°C, and after 60 minutes of heat preservation, it is naturally cooled to room temperature. The obtained product is washed with deionized water until the filtrate is neutral, then dried and ground to obtain the hierarchically porous activated carbon. The prepared activated carbon has a specific surface area of 2254m 2 /g, a pore volume of 1.87cm 3 /g, an average pore diameter of 3.12nm, and an adsorption capacity of methylene blue in water of 1044mg/g.
实施例5Example 5
以沥青质质量含量为6%的含油污泥作为原料,在15℃下经过4000rpm、20min的离心处理后去除底部固体颗粒和水分,取上层油相。以稻壳作为生物质原料,经过破碎研磨后得到60-80目的稻壳颗粒。将上层油相和稻壳颗粒以质量比1:0.2均匀混合。将混合物放入刚玉坩埚中在管式炉中以氮气为气氛加热碳化,加热条件为4℃/min,升温至400℃后保温120min,自然冷却至室温后得到固体产物。将固体产物研磨至2mm左右的固体颗粒,并与KOH粉末以质量比1:4均匀混合后放入刚玉坩埚中,并置于管式炉中加热活化,活化过程中以氮气为保护气氛,加热温度为800℃,保温60min后自然冷却至室温。得到的产物经过去离子水冲洗至滤液呈中性后,烘干研磨得到所述多级孔活性炭。所制备的活性炭比表面积为1985m2/g,孔容积为1.61cm3/g,平均孔径为2.95nm,对水体中亚甲基蓝的吸附量为895mg/g。Oily sludge with a mass content of asphaltene of 6% was used as a raw material, and after centrifugation at 15°C at 4000rpm for 20min, the solid particles and water at the bottom were removed, and the upper oil phase was taken. Rice husks are used as biomass raw materials, and rice husk particles of 60-80 meshes are obtained after crushing and grinding. Mix the upper oil phase and rice husk particles evenly at a mass ratio of 1:0.2. The mixture was put into a corundum crucible and heated and carbonized in a tube furnace with nitrogen as an atmosphere. The heating condition was 4°C/min. After the temperature was raised to 400°C, it was kept for 120 minutes, and a solid product was obtained after natural cooling to room temperature. Grind the solid product to a solid particle of about 2mm, and mix it with KOH powder at a mass ratio of 1:4, put it into a corundum crucible, and place it in a tube furnace for heating and activation. During the activation process, use nitrogen as a protective atmosphere and heat The temperature is 800°C, and after 60 minutes of heat preservation, it is naturally cooled to room temperature. The obtained product is washed with deionized water until the filtrate is neutral, then dried and ground to obtain the hierarchically porous activated carbon. The prepared activated carbon has a specific surface area of 1985m 2 /g, a pore volume of 1.61cm 3 /g, an average pore diameter of 2.95nm, and an adsorption capacity of methylene blue in water of 895mg/g.
实施例6Example 6
以沥青质质量含量为6%的含油污泥作为原料,在20℃下经过4000rpm、10min的离心处理后去除底部固体颗粒和水分,取上层油相。以稻壳作为生物质原料,经过破碎研磨后得到60-80目的稻壳颗粒。将上层油相和稻壳颗粒以质量比1:0.2均匀混合。将混合物放入刚玉坩埚中在管式炉中以氮气为气氛加热碳化,加热条件为2℃/min,升温至350℃后保温120min,自然冷却至室温后得到固体产物。将固体产物研磨至2mm左右的固体颗粒,并与KOH粉末以质量比1:3均匀混合后放入刚玉坩埚中,并置于管式炉中加热活化,活化过程中以氮气为保护气氛,加热温度为850℃,保温90min后自然冷却至室温。得到的产物经过去离子水冲洗至滤液呈中性后,烘干研磨得到所述多级孔活性炭。所制备的活性炭比表面积为1885m2/g,孔容积为1.78cm3/g,平均孔径为2.90nm,对水体中亚甲基蓝的吸附量为845mg/g。Oily sludge with a mass content of asphaltene of 6% was used as a raw material, and after centrifugation at 20°C at 4000rpm for 10min, the solid particles and water at the bottom were removed, and the upper oil phase was taken. Rice husks are used as biomass raw materials, and rice husk particles of 60-80 meshes are obtained after crushing and grinding. Mix the upper oil phase and rice husk particles evenly at a mass ratio of 1:0.2. The mixture was put into a corundum crucible and heated and carbonized in a tube furnace with nitrogen as an atmosphere, the heating condition was 2°C/min, the temperature was raised to 350°C and kept for 120 minutes, and the solid product was obtained after natural cooling to room temperature. Grind the solid product to a solid particle of about 2mm, and mix it with KOH powder at a mass ratio of 1:3, put it into a corundum crucible, and place it in a tube furnace for heating and activation. During the activation process, nitrogen is used as a protective atmosphere and heated The temperature is 850°C, and after 90 minutes of heat preservation, it is naturally cooled to room temperature. The obtained product is washed with deionized water until the filtrate is neutral, then dried and ground to obtain the hierarchically porous activated carbon. The prepared activated carbon has a specific surface area of 1885m 2 /g, a pore volume of 1.78cm 3 /g, an average pore diameter of 2.90nm, and an adsorption capacity of methylene blue in water of 845mg/g.
实施例7Example 7
以沥青质质量含量为11%的含油污泥作为原料,在17℃下经过4000rpm、10min的离心处理后去除底部固体颗粒和水分,取上层油相。以稻壳作为生物质原料,经过破碎研磨后得到60-80目的稻壳颗粒。将上层油相和稻壳颗粒以质量比1:0.5均匀混合。将混合物放入刚玉坩埚中在管式炉中以氮气为气氛加热碳化,加热条件为5℃/min,升温至450℃后保温90min,自然冷却至室温后得到固体产物。将固体产物研磨至2mm左右的固体颗粒,并与KOH粉末以质量比1:5均匀混合后放入刚玉坩埚中,并置于管式炉中加热活化,活化过程中以氮气为保护气氛,加热温度为820℃,保温70min后自然冷却至室温。得到的产物经过去离子水冲洗至滤液呈中性后,烘干研磨得到所述多级孔活性炭。所制备的活性炭比表面积为2112m2/g,孔容积为1.83cm3/g,平均孔径为3.08nm,对水体中亚甲基蓝的吸附量为1103mg/g。Oily sludge with an asphaltene content of 11% was used as a raw material, and after centrifugation at 17°C at 4000rpm for 10min, the solid particles and water at the bottom were removed, and the upper oil phase was taken. Rice husks are used as biomass raw materials, and rice husk particles of 60-80 meshes are obtained after crushing and grinding. Mix the upper oil phase and rice husk particles evenly at a mass ratio of 1:0.5. The mixture was put into a corundum crucible and heated and carbonized in a tube furnace with nitrogen as an atmosphere. The heating condition was 5°C/min. After the temperature was raised to 450°C, it was kept for 90 minutes, and a solid product was obtained after natural cooling to room temperature. Grind the solid product to a solid particle of about 2mm, and mix it with KOH powder at a mass ratio of 1:5, put it into a corundum crucible, and place it in a tube furnace for heating and activation. During the activation process, nitrogen is used as a protective atmosphere and heated The temperature is 820°C, after 70 minutes of heat preservation, it is naturally cooled to room temperature. The obtained product is washed with deionized water until the filtrate is neutral, then dried and ground to obtain the hierarchically porous activated carbon. The prepared activated carbon has a specific surface area of 2112m 2 /g, a pore volume of 1.83cm 3 /g, an average pore diameter of 3.08nm, and an adsorption capacity of methylene blue in water of 1103mg/g.
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Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108773840A (en) * | 2018-06-07 | 2018-11-09 | 广西壮族自治区环境保护科学研究院 | A kind of method that destructive distillation oily sludge prepares charcoal |
CN109174063A (en) * | 2018-10-17 | 2019-01-11 | 肇庆市珈旺环境技术研究院 | A kind of sludge base adsorbent and preparation method thereof |
CN110479209A (en) * | 2019-09-03 | 2019-11-22 | 邓晖 | A kind of natural minerals/absorbent charcoal composite material and preparation method thereof |
CN111533126A (en) * | 2020-05-22 | 2020-08-14 | 东华大学 | A kind of preparation method of high compressive strength, high porosity formed sludge activated carbon |
CN112408390A (en) * | 2020-11-20 | 2021-02-26 | 西北化工研究院有限公司 | Method for preparing activated carbon adsorbent from kerosene co-refining residues |
CN113772671A (en) * | 2021-10-27 | 2021-12-10 | 西安交通大学 | A kind of improved coal-based activated carbon and its preparation method and application |
CN114073932A (en) * | 2020-08-14 | 2022-02-22 | 中国石油天然气集团有限公司 | Oil product adsorbing material and preparation method thereof |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103553040A (en) * | 2013-11-15 | 2014-02-05 | 中国石油大学(华东) | Method for preparing porous carbon through co-pyrolysis of petroleum coke and oily sludge |
CN105502390A (en) * | 2015-12-27 | 2016-04-20 | 历清伟 | Method for preparing activated carbon from rice husks and sludge in sewage plant |
-
2017
- 2017-06-27 CN CN201710499400.5A patent/CN107285309B/en active Active
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103553040A (en) * | 2013-11-15 | 2014-02-05 | 中国石油大学(华东) | Method for preparing porous carbon through co-pyrolysis of petroleum coke and oily sludge |
CN105502390A (en) * | 2015-12-27 | 2016-04-20 | 历清伟 | Method for preparing activated carbon from rice husks and sludge in sewage plant |
Non-Patent Citations (3)
Title |
---|
JUN WANG ET AL.: "Production and characterization of high quality activated carbon from oily sludge", 《FUEL PROCESSING TECHNOLOGY》 * |
YUPENG GUO ET AL.: "The preparation and mechanism studies of rice husk based porous carbon", 《MATERIALS CHEMISTRY AND PHYSICS》 * |
邓皓等: "含油污泥制备高比表面积活性炭", 《山东大学学报(工学版)》 * |
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CN108773840A (en) * | 2018-06-07 | 2018-11-09 | 广西壮族自治区环境保护科学研究院 | A kind of method that destructive distillation oily sludge prepares charcoal |
CN109174063A (en) * | 2018-10-17 | 2019-01-11 | 肇庆市珈旺环境技术研究院 | A kind of sludge base adsorbent and preparation method thereof |
CN110479209A (en) * | 2019-09-03 | 2019-11-22 | 邓晖 | A kind of natural minerals/absorbent charcoal composite material and preparation method thereof |
CN111533126A (en) * | 2020-05-22 | 2020-08-14 | 东华大学 | A kind of preparation method of high compressive strength, high porosity formed sludge activated carbon |
CN114073932A (en) * | 2020-08-14 | 2022-02-22 | 中国石油天然气集团有限公司 | Oil product adsorbing material and preparation method thereof |
CN114073932B (en) * | 2020-08-14 | 2024-04-30 | 中国石油天然气集团有限公司 | Oil adsorption material and preparation method thereof |
CN112408390A (en) * | 2020-11-20 | 2021-02-26 | 西北化工研究院有限公司 | Method for preparing activated carbon adsorbent from kerosene co-refining residues |
CN113772671A (en) * | 2021-10-27 | 2021-12-10 | 西安交通大学 | A kind of improved coal-based activated carbon and its preparation method and application |
CN113772671B (en) * | 2021-10-27 | 2024-03-29 | 西安交通大学 | Improved coal-based activated carbon and preparation method and application thereof |
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