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CN105642221A - Phosphorus removal water purifying agent and preparation method thereof - Google Patents

Phosphorus removal water purifying agent and preparation method thereof Download PDF

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Publication number
CN105642221A
CN105642221A CN201610013074.8A CN201610013074A CN105642221A CN 105642221 A CN105642221 A CN 105642221A CN 201610013074 A CN201610013074 A CN 201610013074A CN 105642221 A CN105642221 A CN 105642221A
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sludge
parts
water
phosphorus
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朱新锋
殷世强
郭飞
郭一飞
杨家宽
刘彪
汪潇
郭雨菲
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Henan University of Urban Construction
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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
    • B01J20/0203Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
    • B01J20/0248Compounds of B, Al, Ga, In, Tl
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/0203Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
    • B01J20/0225Compounds of Fe, Ru, Os, Co, Rh, Ir, Ni, Pd, Pt
    • B01J20/0229Compounds of Fe
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/0203Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
    • B01J20/0274Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04 characterised by the type of anion
    • B01J20/0281Sulfates of compounds other than those provided for in B01J20/045
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/0203Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
    • B01J20/0274Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04 characterised by the type of anion
    • B01J20/0288Halides of compounds other than those provided for in B01J20/046
    • 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
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/48Sorbents characterised by the starting material used for their preparation
    • B01J2220/4875Sorbents characterised by the starting material used for their preparation the starting material being a waste, residue or of undefined composition
    • B01J2220/4887Residues, wastes, e.g. garbage, municipal or industrial sludges, compost, animal manure; fly-ashes
    • 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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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
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  • Chemical Kinetics & Catalysis (AREA)
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  • Hydrology & Water Resources (AREA)
  • 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

本发明涉及一种除磷净水剂及其制备方法,它是由下列重量份数的原料制备而成的:粒径小于0.15mm的给水厂铝污泥50份至60份,粒径小于0.15mm污水厂剩余活性污泥35份至45份,粘结剂粘土5份;将上述原料按照配比称量后混合均匀,混合过程中加入水分,湿基含水率控制在18%至25%,混合后得到混合料;将上述混合料制成粒径为0.5mm至1.5mm的污泥颗粒,然后将污泥颗粒干燥,干燥温度为100℃至110℃,干燥后得到干燥污泥颗粒;将上述干燥污泥颗粒在300℃至900℃下烘焙10min至60min,最终得到除磷的改性污泥;避免污泥处理方式对环境造成的危害,节省水厂废弃物处理的成本,成本低、操作简单、环保。The invention relates to a phosphorus-removing water purifying agent and a preparation method thereof, which is prepared from the following raw materials in parts by weight: 50 to 60 parts of aluminum sludge from a water supply plant with a particle size of less than 0.15 mm, and a particle size of less than 0.15 mm 35 to 45 parts of the remaining activated sludge in the mm sewage plant, and 5 parts of the binder clay; the above raw materials are weighed according to the proportion and mixed evenly, and water is added during the mixing process, and the moisture content of the wet basis is controlled at 18% to 25%. After mixing, the mixture is obtained; the above mixture is made into sludge particles with a particle size of 0.5mm to 1.5mm, and then the sludge particles are dried at a drying temperature of 100°C to 110°C, and dried sludge particles are obtained after drying; The above-mentioned dried sludge particles are baked at 300°C to 900°C for 10min to 60min to finally obtain phosphorus-removed modified sludge; avoiding the harm to the environment caused by the sludge treatment method, saving the cost of waste treatment in water plants, low cost, Simple operation and environmental protection.

Description

一种除磷净水剂及其制备方法A kind of phosphorus removal water purification agent and preparation method thereof

技术领域 technical field

本发明涉及净水领域,具体涉及一种利用城市给水厂污泥、污水厂污泥为主要原料制备的轻质多孔净水材料处理含磷废水的方法,特别涉及一种除磷净水剂及其制备方法。 The invention relates to the field of water purification, in particular to a method for treating phosphorus-containing waste water with light porous water purification materials prepared from urban water supply plant sludge and sewage plant sludge as main raw materials, in particular to a phosphorus-removing water purifying agent and its preparation method.

背景技术 Background technique

常规饮用水处理技术普遍采用混凝、沉淀、过滤工艺,混凝单元在整个处理工艺中占有至关重要的作用。近些年来,低分子的硫酸铝和氯化铁逐渐被高分子的聚合氯化铝为代表的新型铝盐混凝剂所取代,净水过程中产生大量污泥,主要来自沉淀池排泥水和滤池反冲洗排水。目前全国城市水厂脱水污泥(含水率70%)年产量接近2200万吨,预计到2015年末,我国脱水污泥年产量将超过2600万吨,2010年的数据显示北京市第九水厂的泥饼(含水率70%)年产量约为六千吨,因此合理处置大量污泥成为国内外亟需解决的问题。脱水铝污泥是自来水厂净水过程中的副产物,其主要成分包括腐殖质、金属氢氧化物、有机质、硅酸盐等。 Conventional drinking water treatment technology generally adopts coagulation, sedimentation, and filtration processes, and the coagulation unit plays a vital role in the entire treatment process. In recent years, low-molecular aluminum sulfate and ferric chloride have been gradually replaced by new aluminum salt coagulants represented by high-molecular polyaluminum chloride. A large amount of sludge is produced in the process of water purification, mainly from sedimentation tank discharge water and Filter backwash drain. At present, the annual output of dewatered sludge (with a moisture content of 70%) in urban water plants across the country is close to 22 million tons. It is estimated that by the end of 2015, the annual output of dewatered sludge in my country will exceed 26 million tons. According to the data in 2010, the No. The annual output of mud cake (moisture content 70%) is about 6,000 tons, so the reasonable disposal of a large amount of sludge has become an urgent problem to be solved at home and abroad. Dehydrated aluminum sludge is a by-product of the water purification process in waterworks, and its main components include humus, metal hydroxides, organic matter, silicate, etc.

生活污水厂污泥,即在城市生活污水处理中,不同处理过程产生的各类沉淀物、漂浮物等的统称。目前我国生活污水处理厂每年排放的污泥量年增长率大于10%,以含固率20%计,全国每年的污泥总产量已经突破3000万吨,据推测在2020~2025年之间每年的污泥总产量更将突破6000万吨大关。污水厂的污泥产生量很大,并含有大量的微生物、病原体以及有机污染物,合理地处理、处置污泥是一项很重要的工作。 Domestic sewage plant sludge is a general term for various sediments and floating objects produced in different treatment processes in urban domestic sewage treatment. At present, the annual growth rate of the amount of sludge discharged by domestic sewage treatment plants in my country is greater than 10%. Based on a solid content of 20%, the total annual sludge output in the country has exceeded 30 million tons. The total output of sludge will exceed 60 million tons. Sewage plants produce a large amount of sludge and contain a large number of microorganisms, pathogens and organic pollutants. Reasonable treatment and disposal of sludge is a very important task.

这些给水厂与污水厂污泥如果不经处理直接排入水体,不但严重污染水体,而且浪费大量的水资源,自来水厂污泥与污水厂污泥处理工作势在必行。现有的污泥处理方法有直接排放、陆上埋弃、卫生填埋、海洋弃投、土地利用和焚烧处理等等。但是这些方法或多或少都会给环境带来一定程度的污染。当前大多数对给水厂污泥中与污水厂污泥的处理方法,并没有将其作为一种资源加以利用。 If the sludge from these water supply plants and sewage plants is directly discharged into the water body without treatment, it will not only seriously pollute the water body, but also waste a lot of water resources. It is imperative to treat the sludge from waterworks plants and sewage plant. The existing sludge treatment methods include direct discharge, land disposal, sanitary landfill, ocean disposal, land use and incineration, etc. However, these methods more or less all bring a certain degree of pollution to the environment. Most of the current treatment methods for water supply plant sludge and sewage plant sludge do not use it as a resource.

目前我国水污染依然严重,湖(库)一个重要问题是富营养化现象,主要污染指数为总氮和总磷,其中磷更是控制性因素,湖泊富营养化问题非常突出。而现在的除磷技术也有很多种,主要有三种方法:分别是化学除磷、生物除磷、物理除磷,其中化学除磷或化学辅助生物除磷应用比较广泛。化学除磷效率可靠,除磷控制过程相对简单,但是需要投加化学药剂,费用较高,并且处理过程中会产生大量污泥,处置费用较高。生物除磷依靠聚磷菌等微生物,对水体中的磷进行净化,作为污水处理厂对污水处理的一种工艺运行。生物除磷不需要投加额外的药剂,成本相对较低可利用污水处理过程中的其他工艺实现对氮及BOD的去除,但微生物对环境的敏感性较强,在运行过程中需要严格控制微生物生长条件,因此限制了整个污水除磷过程及处理效果的稳定性。 At present, my country's water pollution is still serious. An important problem in lakes (reservoirs) is eutrophication. The main pollution indexes are total nitrogen and total phosphorus, of which phosphorus is a controlling factor. The problem of eutrophication in lakes is very prominent. There are also many kinds of phosphorus removal technologies, mainly three methods: chemical phosphorus removal, biological phosphorus removal, and physical phosphorus removal. Among them, chemical phosphorus removal or chemical-assisted biological phosphorus removal are widely used. The efficiency of chemical phosphorus removal is reliable, and the control process of phosphorus removal is relatively simple, but it needs to add chemical agents, which is expensive, and a large amount of sludge will be generated during the treatment process, and the disposal cost is high. Biological phosphorus removal relies on microorganisms such as phosphorus accumulating bacteria to purify phosphorus in water bodies, and is operated as a process for sewage treatment in sewage treatment plants. Biological phosphorus removal does not require additional chemicals, and the cost is relatively low. Other processes in the sewage treatment process can be used to remove nitrogen and BOD. However, microorganisms are highly sensitive to the environment, and microorganisms need to be strictly controlled during operation. growth conditions, thus limiting the stability of the entire sewage phosphorus removal process and treatment effect.

利用污水厂与给水厂污泥制备净水材料净化含磷给水,经济有效,简单实用,而且能够变废为宝,避免二次污染。 Using sludge from sewage plants and water supply plants to prepare water purification materials to purify phosphorus-containing water supply is economical, effective, simple and practical, and can turn waste into wealth and avoid secondary pollution.

因此,生产一种节能环保,节省资源,成本低,吸附能力高效,无再生废弃物,稳定性强,加工和制备方法简单的除磷净水剂及其制备方法,具有广阔的市场前景。 Therefore, the production of an energy-saving and environmental-friendly, resource-saving, low-cost, high-efficiency adsorption capacity, no regeneration waste, strong stability, simple processing and preparation methods for phosphorus removal water purifiers and preparation methods thereof has broad market prospects.

发明内容 Contents of the invention

针对现有技术的不足,本发明提供一种节能环保,节省资源,成本低,吸附能力高效,无再生废弃物,稳定性强,加工和制备方法简单的除磷净水剂及其制备方法,用于弥补现有技术中缺陷。 Aiming at the deficiencies of the prior art, the present invention provides an energy-saving and environment-friendly, resource-saving, low-cost, high-efficiency adsorption capacity, no regeneration waste, strong stability, simple processing and preparation methods, and a preparation method thereof for phosphorus removal and water purification. It is used to make up for the defects in the prior art.

本发明的技术方案是这样实现的:一种除磷净水剂,它是由下列重量份数的原料制备而成的:粒径小于0.15mm的给水厂铝污泥50份至60份,粒径小于0.15mm污水厂剩余活性污泥35份至45份,粘结剂粘土5份。 The technical solution of the present invention is achieved in the following way: a phosphorus removal water purifying agent, which is prepared from the following raw materials in parts by weight: 50 to 60 parts of aluminum sludge from a water supply plant with a particle diameter of less than 0.15 mm, and The diameter is less than 0.15mm sewage plant remaining activated sludge 35 to 45 parts, binder clay 5 parts.

一种如上所述的除磷净水剂的制备方法,其制备方法如下: A kind of preparation method of phosphorus removal water purifying agent as above, its preparation method is as follows:

1)将上述原料按照配比称量后混合均匀,混合过程中加入水分,湿基含水率控制在18%至25%,混合后得到混合料; 1) Weigh the above raw materials according to the proportion and mix them evenly, add water during the mixing process, control the moisture content of the wet basis at 18% to 25%, and obtain the mixture after mixing;

2)将上述混合料制成粒径为0.5mm至1.5mm的污泥颗粒,然后将污泥颗粒干燥,干燥温度为100℃至110℃,干燥后得到干燥污泥颗粒; 2) Make the above mixture into sludge particles with a particle size of 0.5mm to 1.5mm, then dry the sludge particles at a drying temperature of 100°C to 110°C, and obtain dried sludge particles after drying;

3)将上述干燥污泥颗粒在300℃至900℃下烘焙10min至60min,最终得到除磷的改性污泥。 3) The above-mentioned dried sludge particles are baked at 300°C to 900°C for 10min to 60min to finally obtain phosphorus-removed modified sludge.

所述的给水厂污泥来自给水厂使聚合氯化铝絮凝剂、聚合硫酸铁以及铁、铝为主体的混凝剂在沉淀池以及滤池反冲过程中的污泥脱水后获得脱水污泥。 The sludge from the water supply plant comes from the water supply plant to obtain dewatered sludge after dewatering the sludge in the sedimentation tank and filter backwashing process with polyaluminum chloride flocculant, polyferric sulfate, iron and aluminum as the main coagulant .

所述的污水厂剩余活性污泥为生活污水厂的污泥,该污泥有机物含量不小于65%。 The residual activated sludge of the sewage plant is the sludge of the domestic sewage plant, and the organic matter content of the sludge is not less than 65%.

本发明具有如下的积极效果:本发明以给水厂污泥,生活污水厂污泥为主要原料混料、造粒、焙烧制备轻质除磷吸附材料,与现有技术相比,本发明将给水厂污泥与污水厂污泥研磨过筛后与黏合剂及混合并在高温下烘焙,生活污水厂污泥中大量有机物能够在高温下碳化,增强了高温改性污泥的孔隙度,孔隙度高,增加了污泥与含磷化合物接触的表面积,利于污泥对水中含磷化合物的去除,对磷的吸附效果更加理想,高效吸附了富营养化水体中的含磷化合物,起到了水质净化的作用,对水体环境有明显改善;本发明合理利用给水厂污泥与生活污水厂污泥,避免污泥处理方式诸如直接排放、陆上埋弃、卫生填埋、海洋弃投和土地利用对环境造成的危害,节省水厂废弃物处理的成本,相比其他水体除磷方法,本发明所用原料简单易得,价格低廉,制作原理简单,具有成本低、操作简单、环保等优势,具有较大推广前景。 The present invention has the following positive effects: the present invention uses water supply plant sludge and domestic sewage plant sludge as main raw materials for mixing, granulating, and roasting to prepare light-weight phosphorus-removing adsorption materials. Compared with the prior art, the present invention will Plant sludge and sewage plant sludge are ground and sieved, mixed with binder and baked at high temperature. A large amount of organic matter in domestic sewage plant sludge can be carbonized at high temperature, which enhances the porosity and porosity of high-temperature modified sludge. High, increasing the surface area of sludge in contact with phosphorus-containing compounds, which is conducive to the removal of phosphorus-containing compounds in water by sludge, and the adsorption effect on phosphorus is more ideal. It can efficiently adsorb phosphorus-containing compounds in eutrophic water bodies and play a role in water purification. The effect of water body environment is significantly improved; the present invention rationally utilizes water supply plant sludge and domestic sewage plant sludge, and avoids sludge treatment methods such as direct discharge, land burial, sanitary landfill, marine abandonment and land use. The harm caused by the environment saves the cost of waste treatment in water plants. Compared with other water body phosphorus removal methods, the raw materials used in the present invention are simple and easy to obtain, the price is low, the production principle is simple, and it has the advantages of low cost, simple operation, and environmental protection. Great prospects for promotion.

具体实施方式 detailed description

一种除磷净水剂,它是由下列重量份数的原料制备而成的:粒径小于0.15mm的给水厂铝污泥50份至60份,粒径小于0.15mm污水厂剩余活性污泥35份至45份,粘结剂粘土5份。所述的给水厂污泥来自给水厂使聚合氯化铝絮凝剂、聚合硫酸铁以及铁、铝为主体的混凝剂在沉淀池以及滤池反冲过程中的污泥脱水后获得脱水污泥。所述的污水厂剩余活性污泥为生活污水厂的污泥,该污泥有机物含量不小于65%。 A phosphorus-removing water purifier, which is prepared from the following raw materials in parts by weight: 50 to 60 parts of aluminum sludge from water supply plants with a particle size of less than 0.15 mm, and residual activated sludge from sewage plants with a particle size of less than 0.15 mm 35 to 45 parts, 5 parts of binder clay. The sludge from the water supply plant comes from the water supply plant to obtain dewatered sludge after dewatering the sludge in the sedimentation tank and filter backwashing process with polyaluminum chloride flocculant, polyferric sulfate, iron and aluminum as the main coagulant . The residual activated sludge of the sewage plant is the sludge of the domestic sewage plant, and the organic matter content of the sludge is not less than 65%.

一种如上所述的除磷净水剂的制备方法,其制备方法如下: A kind of preparation method of phosphorus removal water purifying agent as above, its preparation method is as follows:

1)将上述原料按照配比称量后混合均匀,混合过程中加入水分,湿基含水率控制在18%至25%,混合后得到混合料; 1) Weigh the above raw materials according to the proportion and mix them evenly, add water during the mixing process, control the moisture content of the wet basis at 18% to 25%, and obtain the mixture after mixing;

2)将上述混合料制成粒径为0.5mm至1.5mm的污泥颗粒,然后将污泥颗粒干燥,干燥温度为100℃至110℃,干燥后得到干燥污泥颗粒; 2) Make the above mixture into sludge particles with a particle size of 0.5mm to 1.5mm, then dry the sludge particles at a drying temperature of 100°C to 110°C, and obtain dried sludge particles after drying;

3)将上述干燥污泥颗粒在300℃至900℃下烘焙10min至60min,最终得到除磷的改性污泥。 3) The above-mentioned dried sludge particles are baked at 300°C to 900°C for 10min to 60min to finally obtain phosphorus-removed modified sludge.

实施例1:原料采用给水厂污泥60份,生活污水厂污泥35份,粘土5份。 Example 1: 60 parts of water supply plant sludge, 35 parts of domestic sewage plant sludge and 5 parts of clay were used as raw materials.

制备方法为:给水厂污泥干燥后破碎,筛分后使用;生活污水厂污泥干燥破碎筛分后使用;将给水厂污泥、污水厂污泥、粘土在搅拌机中搅拌10分钟,加入水,使湿基含水率为21%,搅拌均匀后制成粒径为0.5mm至1.5mm的污泥颗粒,105℃干燥1小时,700℃烘焙30分钟,得到产品轻质除磷吸附材料。 The preparation method is as follows: the sludge from the water supply plant is dried, crushed, and used after sieving; the sludge from the domestic sewage plant is dried, crushed, and sieved before being used; the sludge from the water supply plant, the sludge from the sewage plant, and the clay are stirred in a mixer for 10 minutes, and then added with water , so that the moisture content of the wet basis is 21%, stir evenly, make sludge particles with a particle size of 0.5mm to 1.5mm, dry at 105°C for 1 hour, and bake at 700°C for 30 minutes to obtain the product light phosphorus removal adsorption material.

本实例中的检验产品材料性能情况,在烧杯中加入一定量的高温改性污泥和模拟污水,污水中的总磷浓度为2mg/L,使用溶液为1L,吸附剂的投加量为10g。通过泥和水的充分接触,磷的去除率为95%,出水为0.18mg/L。 In this example, to test the material performance of the product, add a certain amount of high-temperature modified sludge and simulated sewage into the beaker, the total phosphorus concentration in the sewage is 2mg/L, the use solution is 1L, and the dosage of the adsorbent is 10g . Through the full contact of mud and water, the removal rate of phosphorus is 95%, and the effluent is 0.18mg/L.

实施例2:原料采用给水厂污泥55份,生活污水厂污泥40份,粘土5份, Embodiment 2: raw material adopts 55 parts of water supply plant sludge, 40 parts of domestic sewage plant sludge, 5 parts of clay,

制备方法为给水厂污泥破碎,筛分后使用;生活污水厂污泥破碎筛分后使用;将给水厂污泥、污水厂污泥、粘土在搅拌机中搅拌10分钟,加入水,使湿基含水率为18%,搅拌均匀后制成粒径为0.5mm至1.5mm的污泥颗粒,105℃干燥1小时,800℃烘焙20分钟,得到产品轻质除磷吸附材料。 The preparation method is to crush and sieve the water supply plant sludge; use the domestic sewage plant sludge after crushing and sieving; stir the water supply plant sludge, sewage plant sludge, and clay in a mixer for 10 minutes, add water, and make the wet basis The moisture content is 18%, and after stirring evenly, it is made into sludge particles with a particle size of 0.5mm to 1.5mm, dried at 105°C for 1 hour, and baked at 800°C for 20 minutes to obtain the product light phosphorus removal adsorption material.

本实例中的检验产品材料性能情况,在烧杯中加入一定量的高温改性污泥和模拟污水,污水中的总磷浓度为3mg/L,使用溶液为1L,吸附剂的投加量为10g。通过泥和水的充分接触,磷的去除率为90%,出水为0.3mg/L。 In this example, to test the material performance of the product, add a certain amount of high-temperature modified sludge and simulated sewage into the beaker, the total phosphorus concentration in the sewage is 3mg/L, the use solution is 1L, and the dosage of the adsorbent is 10g . Through the full contact of mud and water, the removal rate of phosphorus is 90%, and the effluent is 0.3mg/L.

实施例3:原料采用给水厂污泥50份,生活污水厂污泥45份,粘土5份,制备方法为给水厂污泥破碎,筛分后使用;生活污水厂污泥破碎筛分后使用, Embodiment 3: 50 parts of water supply plant sludge, 45 parts of domestic sewage plant sludge, and 5 parts of clay are used as raw materials. The preparation method is to crush water supply plant sludge and use after screening; use after domestic sewage plant sludge is crushed and sieved,

将给水厂污泥、污水厂污泥、粘土在搅拌机中搅拌10分钟,加入水,使湿基含水率为23%,搅拌均匀后制成粒径为0.5mm至1.5mm的污泥颗粒,105℃干燥1小时,650℃烘焙20分钟。得到产品轻质除磷吸附材料。 Stir water supply plant sludge, sewage plant sludge, and clay in a mixer for 10 minutes, add water to make the moisture content of the wet basis 23%, and mix well to make sludge particles with a particle size of 0.5mm to 1.5mm, 105 ℃ drying for 1 hour, 650 ℃ baking for 20 minutes. The product light phosphorus removal adsorption material is obtained.

本实例中的检验产品材料性能情况,在烧杯中加入一定量的高温改性污泥和模拟污水,污水中的总磷浓度为3mg/L,使用溶液为1L,吸附剂的投加量为10g。通过泥和水的充分接触,出水为0.32mg/L。 In this example, to test the material performance of the product, add a certain amount of high-temperature modified sludge and simulated sewage into the beaker, the total phosphorus concentration in the sewage is 3mg/L, the use solution is 1L, and the dosage of the adsorbent is 10g . Through the full contact of mud and water, the effluent is 0.32mg/L.

Claims (4)

1. a dephosphorization water purification agent, it is characterized in that, it is prepared from by the raw material of following weight part number: particle diameter is less than 50 parts to 60 parts, the water supply plant aluminium mud of 0.15mm, and particle diameter is less than 0.15mm Sewage Plant residual active sludge 35 parts to 45 parts, binding agent clay 5 parts.
2. the preparation method of a dephosphorization water purification agent as claimed in claim 1, it is characterised in that, its preparation method is as follows:
1) mixing after being weighed according to proportioning by above-mentioned raw materials, add moisture in mixing process, wet base moisture control, 18% to 25%, obtains compound after mixing;
2) above-mentioned compound being made the mud granule that particle diameter is 0.5mm to 1.5mm, then that mud granule is dry, drying temperature is 100 DEG C to 110 DEG C, obtains sludge-drying particle after dry;
3) above-mentioned sludge-drying particle is cured 10min to 60min at 300 DEG C at 900 DEG C, finally obtain the modified sewage sludge of dephosphorization.
3. dephosphorization water purification agent according to claim 1, it is characterised in that: described waterworks sludge makes flocculant of polymeric aluminium chloride, bodied ferric sulfate and iron, aluminium be obtain dewatered sludge after the sludge dewatering in settling tank and filter tank recoil process of the coagulating agent of main body from water supply plant.
4. dephosphorization water purification agent according to claim 1, it is characterised in that: described Sewage Plant residual active sludge is the mud of domestic sewage factory, and this mud organic substance content is not less than 65%.
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CN106430537A (en) * 2016-11-14 2017-02-22 兰州交通大学 Tide-type biological contact oxidation treatment process
CN106673164A (en) * 2017-02-08 2017-05-17 合肥智慧龙图腾知识产权股份有限公司 Sewage treatment agent and preparation method thereof
CN107081122A (en) * 2017-06-15 2017-08-22 兰州交通大学 The method that dephosphorization agent is prepared using copper water-supply pipe
CN109621907A (en) * 2018-12-24 2019-04-16 北京建筑大学 A kind of mud granule and the preparation method and application thereof for removing removing heavy metals
CN109908860A (en) * 2019-02-20 2019-06-21 陕西朗正环保科技有限公司 A kind of phosphorus adsorbent and its application using waterworks sludge preparation
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CN110252240A (en) * 2019-06-05 2019-09-20 中国电建集团西北勘测设计研究院有限公司 Method for preparing phosphorus-containing wastewater adsorbent by roasting-free aluminum-containing waste residue and application of method
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CN110540265A (en) * 2019-09-19 2019-12-06 上海城市水资源开发利用国家工程中心有限公司 Method for preparing enhanced phosphorus removal particles by using water supply plant sludge
CN112755954A (en) * 2020-12-29 2021-05-07 湖南工业大学 Preparation method and application of nitrogen and phosphorus removal hydroxy aluminum vermiculite sludge particles

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