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CN110052241A - A kind of preparation and application of cubic spinel type Mn/Al oxysome sludge organism Carbon Materials - Google Patents

A kind of preparation and application of cubic spinel type Mn/Al oxysome sludge organism Carbon Materials Download PDF

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CN110052241A
CN110052241A CN201910341910.9A CN201910341910A CN110052241A CN 110052241 A CN110052241 A CN 110052241A CN 201910341910 A CN201910341910 A CN 201910341910A CN 110052241 A CN110052241 A CN 110052241A
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sludge
solution
cubic spinel
spinel type
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彭广飞
王利平
蒋善庆
张秋亚
曹宇
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Changzhou University
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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
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • 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
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • B01J20/08Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04 comprising aluminium oxide or hydroxide; comprising bauxite
    • 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
    • B01J20/20Solid 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
    • 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
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/105Phosphorus compounds

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  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Water Treatment By Sorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

本发明属于环境功能材料与生物质资源化利用领域,特别涉及一种一步水热法制备立方尖晶石型Mn/Al氧体‑污泥生物炭材料及其应用。所述制备方法包括以下步骤:(1)将污泥加入到去离子水中使其均匀分散在溶液中。(2)然后将氯化锰和氯化铝溶解到含有污泥粉末的溶液中并持续搅拌,在搅拌过程中,将NaOH滴加到混合溶液中。(3)随后,将混合溶液移至不锈钢水热反应釜中反应。(4)待反应结束自然冷却后,所过滤得到的沉淀用去离子水清洗至中性,干燥即得。本发明工艺简单,制备原料具有来源稳定、成本低等优点,同时也为污泥的资源化利用提供了新途径,而且提供了一种新的磷吸附剂,具有良好的环境效应和社会效应。

The invention belongs to the field of environmental functional materials and biomass resource utilization, and particularly relates to a one-step hydrothermal method for preparing cubic spinel-type Mn/Al oxygen body-sludge biochar material and its application. The preparation method includes the following steps: (1) adding the sludge to deionized water to make it evenly dispersed in the solution. (2) The manganese chloride and aluminum chloride are then dissolved into the solution containing the sludge powder and continuously stirred. During the stirring process, NaOH is added dropwise to the mixed solution. (3) Subsequently, the mixed solution was moved to a stainless steel hydrothermal reactor for reaction. (4) After the reaction is finished and naturally cooled, the filtered precipitate is washed with deionized water until neutral, and dried. The method has the advantages of simple process, stable source and low cost for preparing raw materials, and also provides a new way for the resource utilization of sludge, and provides a new phosphorus adsorbent, which has good environmental effect and social effect.

Description

一种立方尖晶石型Mn/Al氧体污泥生物炭材料的制备与应用Preparation and application of a cubic spinel-type Mn/Al oxygen body sludge biochar material

技术领域technical field

本发明属于环境功能材料与生物质资源化利用领域,具体涉及一种立方尖晶石型Mn/Al氧体-污泥生物炭材料及其制备方法与应用。The invention belongs to the field of environmental functional materials and biomass resource utilization, and in particular relates to a cubic spinel type Mn/Al oxygen body-sludge biochar material and a preparation method and application thereof.

背景技术Background technique

随着城市化的发展和人口的空前增长,大量含磷废水的排放使水体富营养化现象日益严重,导致水生态系统物种分布失衡,引起水华、鱼类死亡等现象。因此,迫切需要开发一种有效和环保的方法从水体中将磷去除。With the development of urbanization and the unprecedented growth of the population, the discharge of a large amount of phosphorus-containing wastewater has made the eutrophication of water bodies increasingly serious, resulting in an imbalance in the distribution of species in the aquatic ecosystem, causing algal blooms and fish deaths. Therefore, there is an urgent need to develop an efficient and environmentally friendly method to remove phosphorus from water bodies.

近年来,生物炭作为一种新型生物质吸附材料,获得国内外各处研究者的关注。生物炭是一种通过生物质原料缺氧热解碳化制备的多孔含炭物质,其形态结构相对稳定且含炭丰富。迄今为止,常用于制备生物炭的生物质原料主要包括多种农作物废弃物及副产品、废弃木料、粪便和市政污泥等。然而,废弃木料的低产率及农作物废弃物的季节性因素等会在一定程度上限制生物炭的制备及其大规模推广。相比较而言,选择市政污泥作为原料制备污泥基生物炭,具有来源稳定、成本低等优点,同时也为污泥的资源化利用提供了一种新途径,具有良好的环境效应和社会效应。通常生物炭能够表现出对阳离子较好的吸附性能,但是对NO3 -、PO4 3-等阴离子的吸附效果却不理想,这归因于生物炭表面通常带负电荷,限制了其对带负电荷离子的吸附引力。为了提高生物炭对磷酸盐的吸附能力,通常将金属元素加入到生物炭中,以提高生物炭的零净电荷点。立方尖晶石型Mn/Al氧体分别由Mn2+和Al3+占据四面体和八面体的阳离子位点所构成,具有较高的零净电荷点。目前,立方尖晶石型氧体及其衍生物复合材料由于具有较高的稳定性和大的比表面积已被用于吸附去除各种污染物,如重金属,抗生素和染料等,但将其用于对水中磷的吸附还鲜有报道。本发明以污水厂污泥为原料,复合AlCl3、MnCl2水热碳化合成立方尖晶石型Mn/Al氧体-污泥生物炭 (MA-BC),考察其对磷的吸附性能和机制,为提高对水中磷酸盐吸附去除的生物炭的制备提供新方式,而且实现了污泥的资源化利用。In recent years, as a new type of biomass adsorption material, biochar has attracted the attention of researchers at home and abroad. Biochar is a porous carbon-containing material prepared by anoxic pyrolysis carbonization of biomass raw materials. Its morphological structure is relatively stable and carbon-rich. So far, the biomass raw materials commonly used in the preparation of biochar mainly include a variety of crop wastes and by-products, waste wood, manure and municipal sludge. However, the low yield of waste wood and the seasonality of crop waste will limit the preparation and large-scale promotion of biochar to a certain extent. In comparison, selecting municipal sludge as raw material to prepare sludge-based biochar has the advantages of stable source and low cost, and also provides a new way for the resource utilization of sludge, which has good environmental effects and social benefits. effect. Generally, biochar can show good adsorption performance for cations, but the adsorption effect for anions such as NO 3 - and PO 4 3- is not ideal. This is due to the fact that the surface of biochar is usually negatively charged, which limits its adsorption capacity. Adsorption attraction of negatively charged ions. In order to improve the adsorption capacity of biochar to phosphate, metal elements are usually added to the biochar to increase the zero net charge point of the biochar. The cubic spinel-type Mn/Al oxobody is composed of Mn 2+ and Al 3+ occupying tetrahedral and octahedral cation sites, respectively, and has a high zero net charge point. At present, the cubic spinel-type oxygen body and its derivative composites have been used for adsorption and removal of various pollutants, such as heavy metals, antibiotics and dyes, due to their high stability and large specific surface area. There are few reports on the adsorption of phosphorus in water. The invention uses sewage sludge as raw material, composites AlCl 3 and MnCl 2 hydrothermal carbon to synthesize cubic spinel type Mn/Al oxygen body-sludge biochar (MA-BC), and investigates its adsorption performance and mechanism to phosphorus. , which provides a new way to improve the preparation of biochar by adsorption and removal of phosphate in water, and realizes the resource utilization of sludge.

发明内容SUMMARY OF THE INVENTION

针对上述存在问题和技术分析,本发明的一个目的是提供一种立方尖晶石型Mn/Al氧体-污泥生物炭材料(MA-BC)的制备方法,该方法操作简单,原料易得,制备出的MA-BC具有较大的比表面积和总孔体积。本发明的另一目的是提供MA-BC的应用,不但实现了污泥的资源化利用,而且提供了一种新的磷吸附剂。In view of the above-mentioned existing problems and technical analysis, an object of the present invention is to provide a preparation method of cubic spinel type Mn/Al oxygen body-sludge biochar material (MA-BC), which is simple to operate and easy to obtain raw materials , the prepared MA-BCs have larger specific surface area and total pore volume. Another object of the present invention is to provide the application of MA-BC, which not only realizes the resource utilization of sludge, but also provides a new phosphorus adsorbent.

为实现上述的第一个目的,本发明采用了以下的技术方案:For realizing above-mentioned first purpose, the present invention has adopted following technical scheme:

一种立方尖晶石型Mn/Al氧体-污泥生物炭材料的制备方法,包括以下步骤:A method for preparing a cubic spinel-type Mn/Al oxygen body-sludge biochar material, comprising the following steps:

(1)将2.5 g粉末状污泥加入到50 mL去离子水中并搅拌1 h使其均匀分散在溶液中。(1) Add 2.5 g of powdered sludge to 50 mL of deionized water and stir for 1 h to make it evenly dispersed in the solution.

(2)向步骤(1)所述溶液中添加0.01 mol四水合氯化锰(MnCl2·4H2O)和0.02 mol六水合氯化铝(AlCl3·6H2O),并用磁力搅拌器持续搅拌30 min。(2) Add 0.01 mol of manganese chloride tetrahydrate (MnCl 2 ·4H 2 O) and 0.02 mol of aluminum chloride hexahydrate (AlCl 3 ·6H 2 O) to the solution described in step (1), and continue with a magnetic stirrer Stir for 30 min.

(3)向步骤(2)所述溶液中逐滴加入5 M NaOH,直至溶液pH大于等于10。(3) 5 M NaOH is added dropwise to the solution in step (2) until the pH of the solution is greater than or equal to 10.

(4)将步骤(3)所述溶液移至100 ml的聚四氟乙烯内衬的不锈钢水热反应釜中,在453 K下反应12 h。(4) Transfer the solution described in step (3) to a 100 ml PTFE-lined stainless steel hydrothermal reactor, and react at 453 K for 12 h.

(5)待步骤(4)中所述的反应结束后,得到的沉淀用去离子水清洗至中性,最后在333 K下干燥24 h,所得样品即为立方尖晶石型Mn/Al氧体污泥生物炭(MA-BC)。(5) After the reaction described in step (4) is completed, the obtained precipitate is washed with deionized water until neutral, and finally dried at 333 K for 24 h, the obtained sample is cubic spinel type Mn/Al oxygen Body Sludge Biochar (MA-BC).

为实现上述的另一个目的,本发明采用了以下的技术方案:For realizing the above-mentioned another purpose, the present invention has adopted the following technical scheme:

一种所制备的立方尖晶石型Mn/Al氧体污泥生物炭的应用,作为磷吸附剂用于高效吸附磷。An application of the prepared cubic spinel-type Mn/Al oxygen body sludge biochar as a phosphorus adsorbent for efficiently adsorbing phosphorus.

本发明的有益效果:利用简单的一步水热法,以城市污泥为原料,复合AlCl3、MnCl2合成MA-BC,该材料具有化学稳定性好、比表面积大等优点。本发明工艺简单,制备原料具有来源稳定、成本低等优点,同时也为污泥的资源化利用提供了新途径,具有良好的环境效应和社会效应。The beneficial effects of the invention are as follows: using a simple one-step hydrothermal method, using municipal sludge as a raw material, and compounding AlCl 3 and MnCl 2 to synthesize MA-BC, the material has the advantages of good chemical stability and large specific surface area. The method has the advantages of simple process, stable source and low cost for preparing raw materials, and also provides a new way for the resource utilization of sludge, and has good environmental effect and social effect.

附图说明:Description of drawings:

图1是本发明MA-BC吸附材料的场发射扫描电镜图(FESEM)。FIG. 1 is a field emission scanning electron microscope (FESEM) image of the MA-BC adsorption material of the present invention.

图2是本发明MA-BC吸附材料的XRD图谱。Fig. 2 is the XRD pattern of the MA-BC adsorption material of the present invention.

图3是本发明MA-BC吸附材料在不同pH值条件下对磷的吸附效果影响图。3 is a graph showing the influence of the MA-BC adsorption material of the present invention on the adsorption effect of phosphorus under different pH conditions.

图4是本发明MA-BC吸附材料对磷吸附去除的动力学研究图。Fig. 4 is a kinetic study diagram of the adsorption and removal of phosphorus by the MA-BC adsorbent of the present invention.

图5是本发明MA-BC吸附材料对不同浓度磷的吸附效果图。FIG. 5 is a graph showing the adsorption effect of the MA-BC adsorption material of the present invention on phosphorus with different concentrations.

具体实施方式:Detailed ways:

下面结合实施例对本发明进行详细说明,以使本领域技术人员更好地理解本发明,但本发明并不局限于以下实施例。The present invention will be described in detail below in conjunction with the examples, so that those skilled in the art can better understand the present invention, but the present invention is not limited to the following examples.

实施例 1:Example 1:

立方尖晶石型Mn/Al氧体-污泥生物炭的制备:首先,将脱水污泥在105 ℃的条件下烘至恒重,研磨过200目筛。然后将2.5 g粉末状污泥加入到50 mL去离子水中并搅拌1 h使其均匀分散在溶液中,再将0.01 mol四水合氯化锰(MnCl2·4H2O)和0.02 mol六水合氯化铝(AlCl3·6H2O)溶解到含有污泥粉末的溶液中并用磁力搅拌器持续搅拌30 min。在搅拌过程中,将5 M NaOH逐滴加入到混合溶液中直至pH大于等于10。随后,将混合溶液移至100 ml的聚四氟乙烯内衬的不锈钢水热反应釜中,在453 K下反应12 h。待反应结束自然冷却后,所过滤得到的沉淀用去离子水清洗至中性,最后在333 K下干燥24 h,所得样品即为立方尖晶石型Mn/Al氧体生物炭(MA-BC)。Preparation of cubic spinel-type Mn/Al oxygen body-sludge biochar: First, the dewatered sludge was dried at 105 °C to constant weight, and ground through a 200-mesh sieve. Then 2.5 g of powdered sludge was added to 50 mL of deionized water and stirred for 1 h to make it evenly dispersed in the solution, and then 0.01 mol of manganese chloride tetrahydrate (MnCl 2 ·4H 2 O) and 0.02 mol of chlorine hexahydrate were added. Aluminium (AlCl 3 ·6H 2 O) was dissolved into the solution containing the sludge powder and stirred continuously for 30 min with a magnetic stirrer. During the stirring process, 5 M NaOH was added dropwise to the mixed solution until the pH was greater than or equal to 10. Subsequently, the mixed solution was transferred to a 100 ml PTFE-lined stainless steel hydrothermal reactor and reacted at 453 K for 12 h. After the reaction was finished and cooled naturally, the filtered precipitate was washed with deionized water until neutral, and finally dried at 333 K for 24 h. The obtained sample was the cubic spinel-type Mn/Al oxide biochar (MA-BC ).

MA-BC吸附材料的SEM分析结果(图1)表明MA-BC表面不规则且多孔,具有稠密生长的片状物质。MA-BC的XRD分析结果见图2,在2θ为30.09°、36.56°、42.68°、56.56°、63.04°处均有衍射峰,其分别对应立方尖晶石结构中(220)、(222)、(400)、(333)和(440)晶面的主要特征峰,表明立方尖晶石型Mn/Al氧体成功地生长在了污泥生物质的表面上。The SEM analysis results of the MA-BC adsorbent (Fig. 1) showed that the surface of the MA-BC was irregular and porous, with densely grown sheet-like substances. The XRD analysis results of MA-BC are shown in Figure 2. There are diffraction peaks at 2θ of 30.09°, 36.56°, 42.68°, 56.56°, and 63.04°, which correspond to (220) and (222) in the cubic spinel structure, respectively. The main characteristic peaks of , (400), (333) and (440) crystal planes, indicating that the cubic spinel-type Mn/Al oxygen bodies were successfully grown on the surface of sludge biomass.

实施例 2:Example 2:

不同pH值对实施例1中MA-BC吸附去除磷的影响:称取0.1 g MA-BC加入到含有100 mL浓度为50 mg/L的磷酸盐溶液的锥形瓶中,用0.1M HCl和NaOH调节溶液pH为2-10,间隔为1,然后将锥形瓶置于温度为298 K的恒温振荡器中震荡24 h。吸附完成后,取上层清液,用0.45 μm的膜过滤后用UV-vis分光光度计检测磷酸盐浓度。结果如图3所示,在pH等于3时,吸附量最大,为28.2 mg/g。在pH等于2时,吸附量最小,约为0.2 mg/g,在pH大于3时,随着pH的增加,吸附量呈递减趋势。The effect of different pH values on the adsorption and removal of phosphorus by MA-BC in Example 1: Weigh 0.1 g of MA-BC into a conical flask containing 100 mL of a phosphate solution with a concentration of 50 mg/L, and add 0.1 M HCl and The pH of the solution was adjusted to 2-10 with NaOH, and the interval was 1, and then the conical flask was placed in a constant temperature shaker with a temperature of 298 K for 24 h. After the adsorption was completed, the supernatant was taken, filtered with a 0.45 μm membrane, and the phosphate concentration was detected with a UV-vis spectrophotometer. The results are shown in Fig. 3, when the pH is equal to 3, the adsorption capacity is the largest, which is 28.2 mg/g. When the pH was equal to 2, the adsorption amount was the smallest, about 0.2 mg/g. When the pH was greater than 3, the adsorption amount showed a decreasing trend with the increase of pH.

实施例 3:Example 3:

实施例1中所制备得到的MA-BC用于吸附去除磷的动力学研究:称取0.1 g MA-BC加入到含有100 mL浓度为50 mg/L的磷酸盐溶液的锥形瓶中,调节溶液pH为3,然后将锥形瓶置于温度为298 K的恒温振荡器中震荡48 h,并于不同时间段(1 min、5 min、10 min、30 min、1 h、2 h、5 h、12 h、24 h、36 h、48 h)取上层清液,用0.45 μm的膜过滤后用UV-vis分光光度计检测磷酸盐浓度。结果如图4所示,吸附速率在10 min前较快,然后吸附速率开始降低,最后在36 h左右达到平衡,平衡时的吸附量为31.2 mg/g。The kinetic study of the MA-BC prepared in Example 1 for adsorption and removal of phosphorus: Weigh 0.1 g of MA-BC into a conical flask containing 100 mL of a phosphate solution with a concentration of 50 mg/L, adjust The pH of the solution was 3, and then the conical flask was placed in a constant temperature shaker with a temperature of 298 K for 48 h, and the flask was shaken for 48 h at different time periods (1 min, 5 min, 10 min, 30 min, 1 h, 2 h, 5 h, 12 h, 24 h, 36 h, 48 h) Take the supernatant, filter it with a 0.45 μm membrane, and use a UV-vis spectrophotometer to detect the phosphate concentration. The results are shown in Fig. 4. The adsorption rate was faster before 10 min, then began to decrease, and finally reached equilibrium at about 36 h, and the adsorption amount at equilibrium was 31.2 mg/g.

实施例 4:Example 4:

将实施例1中所制备得到的MA-BC用于不同磷浓度溶液的吸附:将0.1 g MA-BC加入到含有100 mL规定磷酸盐浓度溶液(20 mg/L、50 mg/L、80 mg/L、150 mg/L、200 mg/L、300mg/L)的锥形瓶中,调节溶液pH为3,然后将锥形瓶置于温度为298 K的恒温振荡器中震荡24h。吸附完成后,取上层清液,用0.45 μm的膜过滤后用UV-vis分光光度计检测磷酸盐浓度。结果如图5所示,MA-BC的平衡吸附量随磷酸盐初始浓度的增加呈现先增大后平缓的趋势,最大吸附量为58.77 mg/g。The MA-BC prepared in Example 1 was used for the adsorption of solutions with different phosphorus concentrations: 0.1 g MA-BC was added to a solution containing 100 mL of the specified phosphate concentration (20 mg/L, 50 mg/L, 80 mg /L, 150 mg/L, 200 mg/L, 300 mg/L), adjust the pH of the solution to 3, and then place the conical flask in a constant temperature shaker with a temperature of 298 K for 24 h. After the adsorption was completed, the supernatant was taken, filtered with a 0.45 μm membrane, and the phosphate concentration was detected with a UV-vis spectrophotometer. The results are shown in Figure 5. With the increase of the initial concentration of phosphate, the equilibrium adsorption capacity of MA-BC showed a trend of first increasing and then flattening, and the maximum adsorption capacity was 58.77 mg/g.

Claims (2)

1. a kind of preparation method of cubic spinel type Mn/Al oxysome sludge organism Carbon Materials, which is characterized in that including following step It is rapid: (1) the powdered sludge of 2.5 g to be added in 50 mL deionized waters and stirring 1 h keeps its evenly dispersed in the solution; (2) 0.01 mol, tetra- chloride hydrate manganese (MnCl is added into step (1) described solution2·4H2O) and 0.02 mol six is hydrated chlorine Change aluminium (AlCl3·6H2O 30 min), and with magnetic stirring apparatus are persistently stirred;(3) 5 are added dropwise into step (2) described solution M NaOH, until pH value of solution is more than or equal to 10;(4) step (3) described solution is moved to the polytetrafluoroethyllining lining of 100 ml In stainless steel hydrothermal reaction kettle, 12 h are reacted at 453 K;(5) heavy to what is after reaction, obtained described in step (4) Shallow lake is cleaned with deionized water to neutrality, 24 h is finally dried at 333 K, gained sample is cubic spinel type Mn/Al oxygen Body sludge organism charcoal (MA-BC).
2. the application of cubic spinel type Mn/Al oxysome sludge organism charcoal prepared by a kind of claim 1, it is characterised in that: Efficient absorption phosphorus is used for as phosphorus adsorbent.
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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111229161A (en) * 2020-01-22 2020-06-05 青岛农业大学 Using CuFeO2Method for adsorbing oxytetracycline by/BC composite magnetic material
CN111617739A (en) * 2020-05-09 2020-09-04 齐鲁工业大学 A kind of Al-Mn modified biomass carbon and its preparation method and application
CN111889072A (en) * 2020-07-23 2020-11-06 江苏大学 Preparation of magnesium-aluminum bimetallic oxide-modified straw-biochar composites and its application in removing phosphorus from wastewater
CN113457622A (en) * 2021-06-09 2021-10-01 南京融众环境工程研究院有限公司 Preparation of aluminum-manganese composite modified biochar and application of aluminum-manganese composite modified biochar in phosphorus removal

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20160256851A1 (en) * 2011-07-25 2016-09-08 Leidos, Inc. Reactive Self-Indicating Absorbent Materials, Methods, and Systems
CN107032438A (en) * 2017-06-07 2017-08-11 北京工业大学 The method that sludge based biomass hydro-thermal carbon adsorbent removes Crystal Violet Dye in water removal
CN107413296A (en) * 2017-07-21 2017-12-01 浙江省农业科学院 A kind of charcoal ferrojacobsite composite for being used to adsorb heavy metal antimony cadmium

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20160256851A1 (en) * 2011-07-25 2016-09-08 Leidos, Inc. Reactive Self-Indicating Absorbent Materials, Methods, and Systems
CN107032438A (en) * 2017-06-07 2017-08-11 北京工业大学 The method that sludge based biomass hydro-thermal carbon adsorbent removes Crystal Violet Dye in water removal
CN107413296A (en) * 2017-07-21 2017-12-01 浙江省农业科学院 A kind of charcoal ferrojacobsite composite for being used to adsorb heavy metal antimony cadmium

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
KYUNG-WON JUNG等: "Facile one-pot hydrothermal synthesis of cubic spinel-type manganese ferrite/biochar composites for environmental remediation of heavy metals from aqueous solutions", 《BIORESOURCE TECHNOLOGY》 *
KYUNG-WON JUNG等: "Synthesis of novel magnesium ferrite (MgFe2O4)/biochar magnetic composites and its adsorption behavior for phosphate in aqueous solutions", 《BIORESOURCE TECHNOLOGY》 *
SHISUO FAN等: "Removal of methylene blue from aqueous solution by sewage sludge-derived biochar: Adsorption kinetics, equilibrium,thermodynamics and mechanism", 《JOURNAL OF ENVIRONMENTAL CHEMICAL ENGINEERING》 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111229161A (en) * 2020-01-22 2020-06-05 青岛农业大学 Using CuFeO2Method for adsorbing oxytetracycline by/BC composite magnetic material
CN111617739A (en) * 2020-05-09 2020-09-04 齐鲁工业大学 A kind of Al-Mn modified biomass carbon and its preparation method and application
CN111889072A (en) * 2020-07-23 2020-11-06 江苏大学 Preparation of magnesium-aluminum bimetallic oxide-modified straw-biochar composites and its application in removing phosphorus from wastewater
CN113457622A (en) * 2021-06-09 2021-10-01 南京融众环境工程研究院有限公司 Preparation of aluminum-manganese composite modified biochar and application of aluminum-manganese composite modified biochar in phosphorus removal

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