CN103566899A - Comprehensive treatment method for agricultural straws - Google Patents
Comprehensive treatment method for agricultural straws Download PDFInfo
- Publication number
- CN103566899A CN103566899A CN201310563383.9A CN201310563383A CN103566899A CN 103566899 A CN103566899 A CN 103566899A CN 201310563383 A CN201310563383 A CN 201310563383A CN 103566899 A CN103566899 A CN 103566899A
- Authority
- CN
- China
- Prior art keywords
- solid
- straw
- reaction
- water
- product
- 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.)
- Granted
Links
Images
Landscapes
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
Abstract
本发明公开了一种农业秸秆的综合处理方法,将农业秸秆通过前处理、预处理、碳化处理后得到液相产物和固相产物,其中液相产物经过缩合、磺化反应后制得水煤浆分散剂产品,固相产物经过改性后得到固体吸附剂产品。本发明能够有效的避免现有技术中处理秸秆产生的废液污染问题,将富含木质素的液相产物进行缩合、磺化反应后用作水煤浆分散剂,取得了良好的技术效果;同时,本发明的方法得到的固体吸附剂产品,由于反应过程精确控制,选择最优的工艺参数,具有良好的吸附效果,能够对废水中的阴离子、阳离子污染物进行有效的净化。
The invention discloses a comprehensive treatment method for agricultural straws. The agricultural straws are subjected to pretreatment, pretreatment, and carbonization to obtain liquid-phase products and solid-phase products, wherein the liquid-phase products undergo condensation and sulfonation reactions to produce water coal Slurry dispersant products, solid-phase products are modified to obtain solid adsorbent products. The invention can effectively avoid the pollution of waste liquid produced by straw treatment in the prior art, and use the lignin-rich liquid phase product as a coal-water slurry dispersant after condensation and sulfonation reactions, achieving good technical effects; At the same time, the solid adsorbent product obtained by the method of the present invention has a good adsorption effect due to precise control of the reaction process and selection of optimal process parameters, and can effectively purify anion and cation pollutants in wastewater.
Description
技术领域 technical field
本发明涉及一种秸秆的处理方法,尤其涉及一种农业秸秆的综合处理方法,以制备得到固体吸附剂产品和水煤浆分散剂产品。 The invention relates to a straw processing method, in particular to a comprehensive processing method of agricultural straw to prepare solid adsorbent products and coal-water slurry dispersant products. the
背景技术 Background technique
2006年以来,全国上下加强了节能减排工作,国务院发布了加强节能工作的决定,制定了促进节能减排的一系列政策措施,各地区、各部门相继做出了工作部署,节能减排工作取得了积极进展。但是,2006年全国没有实现年初确定的节能降耗和污染减排的目标,加大了“十一五”后四年节能减排工作的难度。更为严峻的是,2007年一季度,工业特别是高耗能、高污染行业增长过快,占全国工业能耗和二氧化硫排放近70%的电力、钢铁、有色、建材、石油加工、化工等六大行业增长20.6%,同比加快6.6个百分点。与此同时,各方面工作仍存在认识不到位、责任不明确、措施不配套、政策不完善、投入不落实、协调不得力等问题。 Since 2006, the whole country has strengthened energy conservation and emission reduction work. The State Council issued a decision to strengthen energy conservation work and formulated a series of policies and measures to promote energy conservation and emission reduction. Various regions and departments have made work arrangements one after another. Positive progress has been made. However, in 2006, the whole country failed to achieve the goals of energy saving and pollution reduction determined at the beginning of the year, which increased the difficulty of energy saving and emission reduction in the four years after the "Eleventh Five-Year Plan". What is more serious is that in the first quarter of 2007, industries, especially those with high energy consumption and high pollution, grew too fast, accounting for nearly 70% of the national industrial energy consumption and sulfur dioxide emissions, such as electricity, steel, non-ferrous metals, building materials, petroleum processing, and chemicals The six major industries grew by 20.6%, an acceleration of 6.6 percentage points year-on-year. At the same time, there are still problems such as insufficient understanding, unclear responsibilities, unsuitable measures, imperfect policies, unrealized investment, and ineffective coordination in all aspects of work. the
国家“十二五规划”明确提出了节能减排的目标,即到2015年,单位GDP二氧化碳排放降低17%;单位GDP能耗下降16%;非化石能源占一次能源消费比重提高3.1个百分点,从8.3%到11.4%;主要污染物排放总量减少8到10%的目标。此外,十二五”规划中还明确了主要污染物控制总类,在“十一五”化学需氧量、二氧化碳这两个类别基础上,增加了氨氮和氮氧化物两个类别的污染物控制指标。“十二五”规划提出的约束性指标更加明确了国家节能减排的决心。国务院确定了5个方面的主要污染物减排重点工程:一是以城镇污水处理设施及配套管网建设、现有设施升级改造、污泥处理处置设施建设为重点,提升脱氮除磷能力。二是以制浆造纸、印染、食品加工、农副产品加工等行业 为重点,继续加大水污染深度治理和工艺技术改造。三是推进脱硫脱硝工程建设。四是开展农业源污染防治。五是控制机动车污染物排放。 The national "Twelfth Five-Year Plan" clearly puts forward the goal of energy conservation and emission reduction, that is, by 2015, carbon dioxide emissions per unit of GDP will be reduced by 17%; energy consumption per unit of GDP will be reduced by 16%; the proportion of non-fossil energy in primary energy consumption will increase by 3.1 percentage points, From 8.3% to 11.4%; the goal of reducing the total discharge of major pollutants by 8 to 10%. In addition, the 12th Five-Year Plan also clarified the general categories of major pollutants to be controlled. On the basis of the two categories of chemical oxygen demand and carbon dioxide in the "Eleventh Five-Year Plan", two categories of pollutants, ammonia nitrogen and nitrogen oxides, were added. Control indicators. The binding indicators proposed in the "Twelfth Five-Year Plan" further clarified the country's determination to save energy and reduce emissions. The State Council has identified five key projects for the reduction of major pollutants: First, urban sewage treatment facilities and supporting pipe networks Focus on construction, upgrading and reconstruction of existing facilities, and construction of sludge treatment and disposal facilities to improve the capacity of nitrogen and phosphorus removal. Second, focus on pulp and paper, printing and dyeing, food processing, agricultural and sideline product processing and other industries to continue to increase the depth of water pollution Governance and technological transformation. The third is to promote the construction of desulfurization and denitrification projects. The fourth is to carry out the prevention and control of agricultural source pollution. The fifth is to control the discharge of motor vehicle pollutants.
农业秸秆是成熟农作物茎叶(穗)部分的总称,通常指小麦、水稻、玉米、薯类、油料、棉花、甘蔗在收获籽实后的剩余部分。农作物光合作用的产物有一半以上存在于秸秆中。据联合国环境规划署(UNEP)统计,世界上种植的各种农作物每年所产生的秸秆多达17亿吨。 Agricultural straw is the general term for the stems and leaves (ears) of mature crops, and usually refers to the remaining parts of wheat, rice, corn, potatoes, oilseeds, cotton, and sugarcane after harvesting the seeds. More than half of the photosynthetic products of crops exist in straw. According to the statistics of the United Nations Environment Program (UNEP), various crops grown in the world produce up to 1.7 billion tons of straw every year. the
秸秆作为我国农村常见的农业废弃物,具有分布广、资源量大的特点。按照其化学组成,秸秆主要由纤维素、半纤维素和木质素组成,此外还含有少量的能够被水、乙醇、苯等中性溶剂或稀酸、碱溶液抽提的灰分、可提取有机物等。 As a common agricultural waste in rural my country, straw has the characteristics of wide distribution and large amount of resources. According to its chemical composition, straw is mainly composed of cellulose, hemicellulose and lignin, and also contains a small amount of ash that can be extracted by neutral solvents such as water, ethanol, benzene, or dilute acid and alkaline solutions, and extractable organic matter, etc. . the
秸秆不仅是农作物重要副产品,同时也是工农业生产的重要生产资源。然而目前,对秸秆的处理仍主要停留在传统的燃烧、还田、饲料等方面。其中,秸秆焚烧近年来越发为人们重视。据统计,全世界每年秸秆产量约29亿吨,其中约有66%直接还田或作为生活能源而被烧掉。秸秆焚烧不但会产生CO、SO2等有毒有害气体,还会产生大量的可吸入颗粒物,给人类健康带来危害。实际上,焚烧秸秆不仅带来了环境污染,也是一种严重的资源浪费。充分发掘秸秆的潜在价值,将秸秆用作工业原料,是近年来秸秆利用的主要发展方向,也该是贯彻国家十二五规划的节能减排任务的重要方面。 Straw is not only an important by-product of crops, but also an important production resource for industrial and agricultural production. However, at present, the treatment of straw is still mainly in the traditional aspects of burning, returning to the field, and feeding. Among them, straw burning has attracted more and more attention in recent years. According to statistics, the world's annual output of straw is about 2.9 billion tons, of which about 66% is directly returned to the field or burned as a living energy. Straw incineration will not only produce CO, SO 2 and other toxic and harmful gases, but also produce a large amount of inhalable particulate matter, which is harmful to human health. In fact, straw burning not only brings environmental pollution, but also a serious waste of resources. Fully exploring the potential value of straw and using straw as industrial raw materials is the main development direction of straw utilization in recent years, and it should also be an important aspect of implementing the energy-saving and emission-reduction tasks of the national 12th Five-Year Plan.
现有技术中,CN102614853A以碳质材料为原料制备了一种吸附剂,首先将碳质材料浸渍在金属氯化物溶液中,待浸渍充分后进行干燥,然后将干燥后的混合物放入管式炉进行炭化活化造孔制备复合吸附剂;将炭化活化后的复合吸附剂与金属粉末锡粉和铝粉混合均匀,加入粘结剂搅拌均匀,然后填充进金属翅片管的翅片间,干燥;将带有吸附剂和金属粉末的金属翅片管放入管式炉 中进行烧结,通过金属粉末将吸附剂和金属翅片管烧结在一起。 In the prior art, CN102614853A prepared a kind of adsorbent with carbonaceous material as raw material, first impregnated the carbonaceous material in the metal chloride solution, dried after the impregnation was sufficient, and then put the dried mixture into the tube furnace Carry out carbonization and activation to make pores to prepare composite adsorbent; mix the carbonized and activated composite adsorbent with metal powder tin powder and aluminum powder evenly, add binder and stir evenly, then fill it into the fins of the metal finned tube, and dry; The metal finned tube with adsorbent and metal powder is put into a tube furnace for sintering, and the adsorbent and metal finned tube are sintered together by metal powder. the
CN102815699A公开了一种新型雪松树枝碳质材料的制备方法,为采用水热碳化法制备所述雪松树枝碳质材料,包括如下步骤:收集雪松树掉落在地的树枝,去皮;将去皮后的树枝切成小段,放入溶有适量柠檬酸的水中进行水热碳化反应,其中水热碳化反应的温度为180~220℃,反应时间为28~32小时;将反应后的含有碳化物的溶液自然冷却后并滤去溶液,将碳化物洗涤后真空干燥;将干燥后的碳化物进行研磨后获得所述雪松树枝碳质材料。 CN102815699A discloses a preparation method of a novel cedar branch carbonaceous material. In order to prepare the cedar branch carbonaceous material by hydrothermal carbonization, the method comprises the following steps: collecting the fallen branches of cedar trees and peeling them; The final branch is cut into small sections, put into the water that is dissolved with appropriate amount of citric acid to carry out hydrothermal carbonization reaction, wherein the temperature of hydrothermal carbonization reaction is 180~220 ℃, and the reaction time is 28~32 hours; After the solution is naturally cooled, the solution is filtered off, the carbide is washed and then vacuum-dried; the dried carbide is ground to obtain the cedar branch carbonaceous material. the
同时,现有技术中还公开了将秸秆进行过处理后用作环境保护材料,例如石油吸附剂、重金属吸附剂等。但是,现有技术中存在的处理秸秆的方法产生的废液中存在大量的木质素,导致难以治理,形成二次污染,制备的吸附剂吸附效果不好等技术缺陷,现有技术中并没有一种综合处理秸秆的方法。 At the same time, the prior art also discloses that the treated straw is used as an environmental protection material, such as petroleum adsorbent, heavy metal adsorbent and the like. However, there is a large amount of lignin in the waste liquid produced by the method of processing straw in the prior art, which makes it difficult to treat, forms secondary pollution, and has technical defects such as poor adsorption effect of the prepared adsorbent. A method for comprehensively treating straw. the
发明内容 Contents of the invention
针对现有技术的不足,本发明提供一种农业秸秆的综合处理方法,以克服现有技术中存在的产生废液污染的问题,而是变废为宝,制备得到水煤浆分散剂和高效的固体吸附剂产品。 Aiming at the deficiencies of the prior art, the present invention provides a comprehensive treatment method for agricultural stalks to overcome the problem of waste liquid pollution in the prior art, and to turn waste into treasure, and to prepare a coal-water slurry dispersant and high-efficiency solid adsorbent products. the
一种农业秸秆的综合处理方法,其特征在于,包括如下步骤: A comprehensive processing method for agricultural stalks, characterized in that it comprises the following steps:
(1)预处理:将农业秸秆进行干燥处理,将干燥的农业秸秆剪成小段后用搅拌机进一步磨碎,然后过100目分样筛,取分样筛筛下秸秆使用去离子水清洗2—3次,之后使用真空泵抽滤直至滤液变澄清,得到的秸秆粉末在烘干箱中于55℃干燥24—48h后得到预处理后的秸秆粉末; (1) Pretreatment: dry the agricultural stalks, cut the dried agricultural stalks into small sections and grind them further with a mixer, then pass through a 100-mesh sampling sieve, take the stalks under the sampling sieve and wash them with deionized water for 2— 3 times, then use a vacuum pump to filter until the filtrate becomes clear, and dry the obtained straw powder in a drying oven at 55°C for 24-48 hours to obtain the pretreated straw powder;
(2)前处理:将步骤(1)得到的预处理后的秸秆粉末使用0.01-0.09mol/L的氢氧化钠溶液润胀处理,润胀时间为48-64小时,润胀结束后,调节pH至6.6—7.4,离心过滤后,使用去离子水清洗2—3次,然后置于烘干箱中于65℃ 干燥24—48h;得到前处理后的秸秆粉末; (2) Pretreatment: Swell the pretreated straw powder obtained in step (1) with 0.01-0.09mol/L sodium hydroxide solution. The swelling time is 48-64 hours. After swelling, adjust pH to 6.6-7.4, after centrifugal filtration, wash with deionized water for 2-3 times, and then place in a drying oven at 65°C for 24-48h; obtain pre-treated straw powder;
(3)碳化处理:称取步骤(2)得到的前处理后的秸秆粉末、去离子水、以及环氧丙烷加入反应釜中,密封,通入氮气20—60min将反应釜内部残余气体排出,再将进气和出气阀门拧紧后,开启磁力搅拌装置进行搅拌,并通冷却水保护磁力搅拌装置,通过电子炉将反应釜加热到220—250℃;达到反应温度后,停止加热,先自然冷却至180℃,后通入冷凝水,直至反应釜冷却至常温;然后打开反应釜,将反应产物经抽滤后得到液相产物和固相产物;固相产物在110—120℃干燥26—36h,得到碳化处理后的固体材料;其中步骤(2)得到的前处理后的秸秆粉末、去离子水、以及环氧丙烷的质量用量比例为5—20:500—1500:3—5; (3) Carbonization treatment: Weigh the pretreated straw powder, deionized water, and propylene oxide obtained in step (2) and add them to the reactor, seal it, and feed nitrogen gas for 20-60 minutes to discharge the residual gas inside the reactor. After tightening the air inlet and outlet valves, turn on the magnetic stirring device for stirring, and pass cooling water to protect the magnetic stirring device, and heat the reactor to 220-250°C through an electronic furnace; after reaching the reaction temperature, stop heating and let it cool naturally to 180°C, then pour in condensed water until the reactor cools down to room temperature; then open the reactor, and filter the reaction product to obtain a liquid-phase product and a solid-phase product; dry the solid-phase product at 110-120°C for 26-36 hours , to obtain the solid material after carbonization treatment; wherein the mass dosage ratio of the pretreated straw powder, deionized water, and propylene oxide obtained in step (2) is 5-20:500-1500:3-5;
(4)改性处理:将3-氯-2-羟丙基三甲基氯化铵溶于异丙醇-水混合溶液中,形成混合溶液A,然后将步骤(3)得到的固体材料加入到上述混合溶液A中,其中,3-氯-2-羟丙基三甲基氯化铵、异丙醇与水的质量比为5—10:16—23:200—230,3-氯-2-羟丙基三甲基氯化铵与步骤(3)得到的固体材料的质量比为1-3:5—10,所得混合物在30—65℃下,反应12—20h,反应结束后将反应体系的pH调节至6.5—7;然后对所得到的溶液过滤,过滤后的固体产物使用去离子水清洗2—3次,然后在110—120℃干燥26-48h,得到3-氯-2-羟丙基三甲基氯化铵改性的固体产物; (4) Modification treatment: 3-chloro-2-hydroxypropyltrimethylammonium chloride is dissolved in isopropanol-water mixed solution to form mixed solution A, and then the solid material obtained in step (3) is added In the above mixed solution A, wherein, the mass ratio of 3-chloro-2-hydroxypropyltrimethylammonium chloride, isopropanol to water is 5-10:16-23:200-230, 3-chloro- The mass ratio of 2-hydroxypropyltrimethylammonium chloride to the solid material obtained in step (3) is 1-3:5-10, and the resulting mixture is reacted for 12-20h at 30-65°C, and after the reaction finishes, the The pH of the reaction system was adjusted to 6.5-7; then the obtained solution was filtered, and the filtered solid product was washed 2-3 times with deionized water, and then dried at 110-120°C for 26-48h to obtain 3-chloro-2 -The solid product of hydroxypropyltrimethylammonium chloride modification;
将氯乙酸溶于乙醇-水混合溶液中,形成混合溶液B,其中,氯乙酸、乙醇与水的质量比为4—9:20—100:20—98,将3-氯-2-羟丙基三甲基氯化铵改性的固体产物加入到混合溶液B中,其中,3-氯-2-羟丙基三甲基氯化铵改性的固体产物与氯乙酸的质量比为5—10:6-12;在40—80℃下搅拌反应13—24h;反应结束后将上述体系的pH调节至6.6—7.5;然后对所得到的溶液过滤,过滤后的固体 产物使用去离子水清洗5—9次,然后在110—115℃干燥30—72h,得到固体吸附剂产品; Dissolve chloroacetic acid in ethanol-water mixed solution to form mixed solution B, wherein the mass ratio of chloroacetic acid, ethanol and water is 4-9:20-100:20-98, and 3-chloro-2-hydroxypropyl The solid product modified by trimethyl ammonium chloride is added in the mixed solution B, wherein, the mass ratio of the solid product modified by 3-chloro-2-hydroxypropyl trimethyl ammonium chloride to chloroacetic acid is 5— 10: 6-12; Stir and react at 40-80°C for 13-24h; after the reaction, adjust the pH of the above system to 6.6-7.5; then filter the obtained solution, and wash the filtered solid product with deionized water 5-9 times, then dry at 110-115°C for 30-72 hours to obtain solid adsorbent products;
(5)制备水煤浆分散剂:将步骤(3)得到的液相产物的pH调至12-12.8,边搅拌边升温至75℃,滴加甲醛进行缩合反应1-2h,然后将温度升至90℃,加入亚硫酸钠进行磺化反应2—3h,反应结束后冷却至常温出料,得到水煤浆分散剂产品。 (5) Preparation of coal water slurry dispersant: adjust the pH of the liquid phase product obtained in step (3) to 12-12.8, raise the temperature to 75°C while stirring, add formaldehyde dropwise for condensation reaction for 1-2h, and then raise the temperature To 90°C, add sodium sulfite to carry out sulfonation reaction for 2-3 hours, after the reaction is completed, cool to normal temperature and discharge to obtain the coal water slurry dispersant product. the
进一步地,所述的农业秸秆是小麦秸秆、水稻秸秆、玉米秸秆、棉花秸秆、或者甘蔗秸秆。 Further, the agricultural straw is wheat straw, rice straw, corn straw, cotton straw, or sugarcane straw. the
本发明公开的一种农业秸秆的综合处理方法,能够有效的避免现有技术中处理秸秆产生的废液污染问题,本发明将富含木质素的液相产物进行缩合、磺化反应后用作水煤浆分散剂,取得了良好的技术效果;同时,本发明的方法得到的固体吸附剂产品,由于反应过程精确控制,选择最优的工艺参数,具有良好的吸附效果,能够对废水中的阴离子、阳离子污染物进行有效的净化。 The comprehensive treatment method for agricultural stalks disclosed by the invention can effectively avoid the problem of waste liquid pollution caused by the treatment of stalks in the prior art. The coal water slurry dispersant has achieved good technical effects; meanwhile, the solid adsorbent product obtained by the method of the present invention has a good adsorption effect due to the precise control of the reaction process and the selection of optimal process parameters, and can treat the waste water. Effective purification of anion and cation pollutants. the
附图说明 Description of drawings
图1为本发明的流程示意图。 Fig. 1 is a schematic flow chart of the present invention. the
具体实施方式 Detailed ways
下面结合具体实施例对本发明进行进一步详细说明。 The present invention will be further described in detail below in conjunction with specific embodiments. the
实施例1 Example 1
一种农业秸秆的综合处理方法,其特征在于,包括如下步骤: A comprehensive processing method for agricultural stalks, characterized in that it comprises the following steps:
(1)预处理:将小麦秸秆进行干燥处理,将干燥的小麦秸秆剪成小段后用搅拌机进一步磨碎,然后过100目分样筛,取分样筛筛下秸秆使用去离子水清洗2次,之后使用真空泵抽滤直至滤液变澄清,得到的秸秆粉末在烘干箱中于55℃干燥48h后得到预处理后的秸秆粉末; (1) Pretreatment: dry the wheat straw, cut the dry wheat straw into small pieces and grind it further with a mixer, then pass through a 100-mesh sampling sieve, take the straw under the sampling sieve and wash it twice with deionized water , and then use a vacuum pump to filter until the filtrate becomes clear, and the obtained straw powder is dried in an oven at 55°C for 48 hours to obtain a pretreated straw powder;
(2)前处理:将步骤(1)得到的预处理后的秸秆粉末使用0.01mol/L的氢氧化钠溶液润胀处理,润胀时间为48小时,润胀结束后,调节pH至6.6,离心过滤后,使用去离子水清洗2次,然后置于烘干箱中于65℃干燥24h;得到前处理后的秸秆粉末; (2) Pretreatment: Swell the pretreated straw powder obtained in step (1) with 0.01mol/L sodium hydroxide solution, the swelling time is 48 hours, after the swelling is completed, adjust the pH to 6.6, After centrifugal filtration, wash twice with deionized water, and then place in a drying oven at 65°C for 24 hours to obtain pretreated straw powder;
(3)碳化处理:称取步骤(2)得到的前处理后的秸秆粉末、去离子水、以及环氧丙烷加入反应釜中,密封,通入氮气20min将反应釜内部残余气体排出,再将进气和出气阀门拧紧后,开启磁力搅拌装置进行搅拌,并通冷却水保护磁力搅拌装置,通过电子炉将反应釜加热到220℃;达到反应温度后,停止加热,先自然冷却至180℃,后通入冷凝水,直至反应釜冷却至常温;然后打开反应釜,将反应产物经抽滤后得到液相产物和固相产物;固相产物在110℃干燥26h,得到碳化处理后的固体材料;其中步骤(2)得到的前处理后的秸秆粉末、去离子水、以及环氧丙烷的质量用量比例为5:1500:5; (3) Carbonization treatment: Weigh the pretreated straw powder, deionized water, and propylene oxide obtained in step (2) and add them to the reactor, seal it, and feed nitrogen gas for 20 minutes to discharge the residual gas inside the reactor, and then put the After the air inlet and outlet valves are tightened, turn on the magnetic stirring device for stirring, and pass cooling water to protect the magnetic stirring device, and heat the reactor to 220°C through an electronic furnace; after reaching the reaction temperature, stop heating, and first cool down to 180°C naturally. Finally, pour condensed water until the reactor is cooled to normal temperature; then open the reactor, and filter the reaction product to obtain a liquid-phase product and a solid-phase product; dry the solid-phase product at 110°C for 26 hours to obtain a carbonized solid material ; Wherein the mass dosage ratio of the pretreated stalk powder, deionized water, and propylene oxide obtained in step (2) is 5:1500:5;
(4)改性处理:将3-氯-2-羟丙基三甲基氯化铵溶于异丙醇-水混合溶液中,形成混合溶液A,然后将步骤(3)得到的固体材料加入到上述混合溶液A中,其中,3-氯-2-羟丙基三甲基氯化铵、异丙醇与水的质量比为5:23:230,3-氯-2-羟丙基三甲基氯化铵与步骤(3)得到的固体材料的质量比为1:10,所得混合物在30℃下,反应12h,反应结束后将反应体系的pH调节至6.5;然后对所得到的溶液过滤,过滤后的固体产物使用去离子水清洗2次,然后在110℃干燥26h,得到3-氯-2-羟丙基三甲基氯化铵改性的固体产物; (4) Modification treatment: 3-chloro-2-hydroxypropyltrimethylammonium chloride is dissolved in isopropanol-water mixed solution to form mixed solution A, and then the solid material obtained in step (3) is added Into the above mixed solution A, wherein the mass ratio of 3-chloro-2-hydroxypropyltrimethylammonium chloride, isopropanol to water is 5:23:230, 3-chloro-2-hydroxypropyltrimethylammonium The mass ratio of methyl ammonium chloride to the solid material obtained in step (3) is 1:10, and the resulting mixture is reacted for 12 hours at 30° C., and the pH of the reaction system is adjusted to 6.5 after the reaction; then the obtained solution is Filtration, the filtered solid product was washed twice with deionized water, and then dried at 110°C for 26 hours to obtain a solid product modified with 3-chloro-2-hydroxypropyltrimethylammonium chloride;
将氯乙酸溶于乙醇-水混合溶液中,形成混合溶液B,其中,氯乙酸、乙醇与水的质量比为4:100:98,将3-氯-2-羟丙基三甲基氯化铵改性的固体产物加入到混合溶液B中,其中,3-氯-2-羟丙基三甲基氯化铵改性的固体产物与氯乙酸的质量比为5:12;在40℃下搅拌反应13h;反应结束后将上述体系的pH调 节至6.6;然后对所得到的溶液过滤,过滤后的固体产物使用去离子水清洗5次,然后在110℃干燥30h,得到固体吸附剂产品; Dissolve chloroacetic acid in an ethanol-water mixed solution to form a mixed solution B, wherein the mass ratio of chloroacetic acid, ethanol and water is 4:100:98, and chlorinated 3-chloro-2-hydroxypropyl trimethyl The ammonium-modified solid product was added to the mixed solution B, wherein the mass ratio of the 3-chloro-2-hydroxypropyltrimethylammonium chloride-modified solid product to chloroacetic acid was 5:12; at 40°C Stir the reaction for 13 hours; after the reaction, adjust the pH of the above system to 6.6; then filter the obtained solution, wash the filtered solid product with deionized water for 5 times, and then dry it at 110°C for 30 hours to obtain a solid adsorbent product ;
(5)制备水煤浆分散剂:将步骤(3)得到的液相产物的pH调至12,边搅拌边升温至75℃,滴加甲醛进行缩合反应1h,然后将温度升至90℃,加入亚硫酸钠进行磺化反应2h,反应结束后冷却至常温出料,得到水煤浆分散剂产品。 (5) Preparation of coal water slurry dispersant: adjust the pH of the liquid phase product obtained in step (3) to 12, raise the temperature to 75°C while stirring, add dropwise formaldehyde for condensation reaction for 1 hour, then raise the temperature to 90°C, Sodium sulfite was added for sulfonation reaction for 2 hours, and after the reaction was completed, the mixture was cooled to room temperature and discharged to obtain a coal-water slurry dispersant product. the
实施例2 Example 2
一种玉米秸秆的综合处理方法,其特征在于,包括如下步骤: A comprehensive treatment method for corn stalks, characterized in that it comprises the steps of:
(1)预处理:将玉米秸秆进行干燥处理,将干燥的玉米秸秆剪成小段后用搅拌机进一步磨碎,然后过100目分样筛,取分样筛筛下秸秆使用去离子水清洗3次,之后使用真空泵抽滤直至滤液变澄清,得到的秸秆粉末在烘干箱中于55℃干燥48h后得到预处理后的秸秆粉末; (1) Pretreatment: Dry the corn stalks, cut the dried corn stalks into small pieces and grind them further with a mixer, then pass through a 100-mesh sampling sieve, take the straw under the sampling sieve and wash it with deionized water for 3 times , and then use a vacuum pump to filter until the filtrate becomes clear, and the obtained straw powder is dried in an oven at 55°C for 48 hours to obtain a pretreated straw powder;
(2)前处理:将步骤(1)得到的预处理后的秸秆粉末使用0.09mol/L的氢氧化钠溶液润胀处理,润胀时间为64小时,润胀结束后,调节pH至7.4,离心过滤后,使用去离子水清洗3次,然后置于烘干箱中于65℃干燥48h;得到前处理后的秸秆粉末; (2) Pretreatment: Swell the pretreated straw powder obtained in step (1) with 0.09 mol/L sodium hydroxide solution. The swelling time is 64 hours. After swelling, adjust the pH to 7.4. After centrifugal filtration, wash with deionized water for 3 times, then place in a drying box and dry at 65°C for 48 hours; obtain the pretreated straw powder;
(3)碳化处理:称取步骤(2)得到的前处理后的秸秆粉末、去离子水、以及环氧丙烷加入反应釜中,密封,通入氮气60min将反应釜内部残余气体排出,再将进气和出气阀门拧紧后,开启磁力搅拌装置进行搅拌,并通冷却水保护磁力搅拌装置,通过电子炉将反应釜加热到250℃;达到反应温度后,停止加热,先自然冷却至180℃,后通入冷凝水,直至反应釜冷却至常温;然后打开反应釜,将反应产物经抽滤后得到液相产物和固相产物;固相产物在120℃干燥36h,得到碳化处理后的固体材料;其中步骤(2)得到的前处理后的秸 秆粉末、去离子水、以及环氧丙烷的质量用量比例为20:500:3; (3) Carbonization treatment: Weigh the pretreated straw powder, deionized water, and propylene oxide obtained in step (2) and add them to the reactor, seal it, and feed nitrogen gas for 60 minutes to discharge the residual gas inside the reactor, and then put the After the air inlet and outlet valves are tightened, turn on the magnetic stirring device for stirring, and pass cooling water to protect the magnetic stirring device, and heat the reactor to 250°C through an electronic furnace; after reaching the reaction temperature, stop heating, and first cool down to 180°C naturally. Finally, pour condensed water until the reactor is cooled to normal temperature; then open the reactor, and filter the reaction product to obtain a liquid-phase product and a solid-phase product; dry the solid-phase product at 120°C for 36 hours to obtain a carbonized solid material ; Wherein the mass consumption ratio of the pretreated stalk powder, deionized water and propylene oxide obtained in step (2) is 20:500:3;
(4)改性处理:将3-氯-2-羟丙基三甲基氯化铵溶于异丙醇-水混合溶液中,形成混合溶液A,然后将步骤(3)得到的固体材料加入到上述混合溶液A中,其中,3-氯-2-羟丙基三甲基氯化铵、异丙醇与水的质量比为10:16:200,3-氯-2-羟丙基三甲基氯化铵与步骤(3)得到的固体材料的质量比为3:5,所得混合物在65℃下,反应20h,反应结束后将反应体系的pH调节至7;然后对所得到的溶液过滤,过滤后的固体产物使用去离子水清洗3次,然后在120℃干燥48h,得到3-氯-2-羟丙基三甲基氯化铵改性的固体产物; (4) Modification treatment: 3-chloro-2-hydroxypropyltrimethylammonium chloride is dissolved in isopropanol-water mixed solution to form mixed solution A, and then the solid material obtained in step (3) is added Into the above mixed solution A, wherein the mass ratio of 3-chloro-2-hydroxypropyltrimethylammonium chloride, isopropanol to water is 10:16:200, 3-chloro-2-hydroxypropyltrimethylammonium The mass ratio of methyl ammonium chloride to the solid material obtained in step (3) is 3:5, and the resulting mixture is reacted for 20 h at 65° C., and the pH of the reaction system is adjusted to 7 after the reaction; Filtration, the filtered solid product was washed 3 times with deionized water, and then dried at 120°C for 48h to obtain a solid product modified with 3-chloro-2-hydroxypropyltrimethylammonium chloride;
将氯乙酸溶于乙醇-水混合溶液中,形成混合溶液B,其中,氯乙酸、乙醇与水的质量比为9:20:20,将3-氯-2-羟丙基三甲基氯化铵改性的固体产物加入到混合溶液B中,其中,3-氯-2-羟丙基三甲基氯化铵改性的固体产物与氯乙酸的质量比为10:6;在80℃下搅拌反应24h;反应结束后将上述体系的pH调节至7.5;然后对所得到的溶液过滤,过滤后的固体产物使用去离子水清洗9次,然后在115℃干燥72h,得到固体吸附剂产品; Dissolve chloroacetic acid in ethanol-water mixed solution to form mixed solution B, wherein the mass ratio of chloroacetic acid, ethanol and water is 9:20:20, and chlorinated 3-chloro-2-hydroxypropyl trimethyl Add the ammonium-modified solid product to the mixed solution B, wherein the mass ratio of the 3-chloro-2-hydroxypropyltrimethylammonium chloride-modified solid product to chloroacetic acid is 10:6; at 80°C Stir the reaction for 24 hours; after the reaction, adjust the pH of the above system to 7.5; then filter the obtained solution, wash the filtered solid product with deionized water for 9 times, and then dry it at 115°C for 72 hours to obtain a solid adsorbent product;
(5)制备水煤浆分散剂:将步骤(3)得到的液相产物的pH调至12.8,边搅拌边升温至75℃,滴加甲醛进行缩合反应2h,然后将温度升至90℃,加入亚硫酸钠进行磺化反应3h,反应结束后冷却至常温出料,得到水煤浆分散剂产品。 (5) Preparation of coal water slurry dispersant: adjust the pH of the liquid phase product obtained in step (3) to 12.8, raise the temperature to 75°C while stirring, add dropwise formaldehyde for condensation reaction for 2 hours, then raise the temperature to 90°C, Sodium sulfite was added for sulfonation reaction for 3 hours, and after the reaction was completed, the mixture was cooled to room temperature and discharged to obtain a coal-water slurry dispersant product. the
实施例3 Example 3
一种甘蔗秸秆的综合处理方法,其特征在于,包括如下步骤: A comprehensive processing method for sugarcane stalks, characterized in that it comprises the following steps:
(1)预处理:将甘蔗秸秆进行干燥处理,将干燥的甘蔗秸秆剪成小段后用搅拌机进一步磨碎,然后过100目分样筛,取分样筛筛下秸秆使用去离子水清洗3次,之后使用真空泵抽滤直至滤液变澄清,得到的秸秆粉末在烘干箱中于 55℃干燥48h后得到预处理后的秸秆粉末; (1) Pretreatment: dry the sugarcane stalks, cut the dried sugarcane stalks into small pieces and grind them further with a mixer, then pass through a 100-mesh sampling sieve, take the straw under the sampling sieve and wash it with deionized water for 3 times , and then use a vacuum pump to filter until the filtrate becomes clear, and the obtained straw powder is dried in an oven at 55°C for 48 hours to obtain a pretreated straw powder;
(2)前处理:将步骤(1)得到的预处理后的秸秆粉末使用0.08mol/L的氢氧化钠溶液润胀处理,润胀时间为50小时,润胀结束后,调节pH至7,离心过滤后,使用去离子水清洗3次,然后置于烘干箱中于65℃干燥40h;得到前处理后的秸秆粉末; (2) Pretreatment: Swell the pretreated straw powder obtained in step (1) with 0.08 mol/L sodium hydroxide solution, and the swelling time is 50 hours. After swelling, adjust the pH to 7. After centrifugal filtration, wash with deionized water for 3 times, and then place in a drying box and dry at 65°C for 40 hours; obtain the pretreated straw powder;
(3)碳化处理:称取步骤(2)得到的前处理后的秸秆粉末、去离子水、以及环氧丙烷加入反应釜中,密封,通入氮气40min将反应釜内部残余气体排出,再将进气和出气阀门拧紧后,开启磁力搅拌装置进行搅拌,并通冷却水保护磁力搅拌装置,通过电子炉将反应釜加热到240℃;达到反应温度后,停止加热,先自然冷却至180℃,后通入冷凝水,直至反应釜冷却至常温;然后打开反应釜,将反应产物经抽滤后得到液相产物和固相产物;固相产物在114℃干燥30h,得到碳化处理后的固体材料;其中步骤(2)得到的前处理后的秸秆粉末、去离子水、以及环氧丙烷的质量用量比例为15:600:4; (3) Carbonization treatment: Weigh the pretreated straw powder, deionized water, and propylene oxide obtained in step (2) and add them to the reactor, seal it, and feed nitrogen gas for 40 minutes to discharge the residual gas inside the reactor, and then put the After the air inlet and outlet valves are tightened, turn on the magnetic stirring device for stirring, and pass cooling water to protect the magnetic stirring device, and heat the reaction kettle to 240°C through an electronic furnace; after reaching the reaction temperature, stop heating, and first cool down to 180°C naturally. After that, condensed water was introduced until the reactor was cooled to normal temperature; then the reactor was opened, and the reaction product was filtered with suction to obtain a liquid-phase product and a solid-phase product; the solid-phase product was dried at 114°C for 30 hours to obtain a carbonized solid material ; Wherein the mass dosage ratio of the pretreated stalk powder, deionized water, and propylene oxide obtained in step (2) is 15:600:4;
(4)改性处理:将3-氯-2-羟丙基三甲基氯化铵溶于异丙醇-水混合溶液中,形成混合溶液A,然后将步骤(3)得到的固体材料加入到上述混合溶液A中,其中,3-氯-2-羟丙基三甲基氯化铵、异丙醇与水的质量比为8:20:210,3-氯-2-羟丙基三甲基氯化铵与步骤(3)得到的固体材料的质量比为2:6,所得混合物在50℃下,反应16h,反应结束后将反应体系的pH调节至6.8;然后对所得到的溶液过滤,过滤后的固体产物使用去离子水清洗3次,然后在115℃干燥30h,得到3-氯-2-羟丙基三甲基氯化铵改性的固体产物; (4) Modification treatment: 3-chloro-2-hydroxypropyltrimethylammonium chloride is dissolved in isopropanol-water mixed solution to form mixed solution A, and then the solid material obtained in step (3) is added Into the above mixed solution A, wherein the mass ratio of 3-chloro-2-hydroxypropyltrimethylammonium chloride, isopropanol to water is 8:20:210, 3-chloro-2-hydroxypropyltrimethylammonium The mass ratio of methyl ammonium chloride to the solid material obtained in step (3) is 2:6, and the resulting mixture is reacted for 16 hours at 50° C., and the pH of the reaction system is adjusted to 6.8 after the reaction; then the obtained solution is Filtration, the filtered solid product was washed 3 times with deionized water, and then dried at 115°C for 30h to obtain a solid product modified with 3-chloro-2-hydroxypropyltrimethylammonium chloride;
将氯乙酸溶于乙醇-水混合溶液中,形成混合溶液B,其中,氯乙酸、乙醇与水的质量比为8:50:60,将3-氯-2-羟丙基三甲基氯化铵改性的固体产物加入到混合溶液B中,其中,3-氯-2-羟丙基三甲基氯化铵改性的固体产物与氯乙酸 的质量比为7:10;在70℃下搅拌反应20h;反应结束后将上述体系的pH调节至7;然后对所得到的溶液过滤,过滤后的固体产物使用去离子水清洗8次,然后在112℃干燥30—72h,得到固体吸附剂产品; Dissolve chloroacetic acid in ethanol-water mixed solution to form mixed solution B, wherein the mass ratio of chloroacetic acid, ethanol and water is 8:50:60, and chlorinated 3-chloro-2-hydroxypropyl trimethyl The ammonium-modified solid product was added to the mixed solution B, wherein the mass ratio of the 3-chloro-2-hydroxypropyltrimethylammonium chloride-modified solid product to chloroacetic acid was 7:10; at 70°C Stir the reaction for 20 hours; after the reaction, adjust the pH of the above system to 7; then filter the obtained solution, wash the filtered solid product with deionized water for 8 times, and then dry it at 112°C for 30-72 hours to obtain a solid adsorbent product;
(5)制备水煤浆分散剂:将步骤(3)得到的液相产物的pH调至12.6,边搅拌边升温至75℃,滴加甲醛进行缩合反应2h,然后将温度升至90℃,加入亚硫酸钠进行磺化反应1.6h,反应结束后冷却至常温出料,得到水煤浆分散剂产品。 (5) Preparation of coal-water slurry dispersant: adjust the pH of the liquid phase product obtained in step (3) to 12.6, raise the temperature to 75°C while stirring, add formaldehyde dropwise for condensation reaction for 2 hours, and then raise the temperature to 90°C, Sodium sulfite was added to carry out sulfonation reaction for 1.6 hours. After the reaction was completed, it was cooled to room temperature and discharged to obtain a coal-water slurry dispersant product. the
将实施例1-3得到的固体吸附剂产品对废水中的铜离子进行吸附测试,吸附测试后的结果如表1所示。表1是实施例1-3对废水中铜离子的吸附测试结果。 The solid adsorbent product obtained in Examples 1-3 was subjected to an adsorption test on copper ions in wastewater, and the results after the adsorption test are shown in Table 1. Table 1 is the adsorption test results of Examples 1-3 to copper ions in wastewater. the
由表1可知,本发明实施例1-3制备得到的固体吸附剂产品对废水中铜离子的均具有良好的吸附效果。 It can be seen from Table 1 that the solid adsorbent products prepared in Examples 1-3 of the present invention have good adsorption effects on copper ions in wastewater. the
尽管上述实施例对本发明做出了详尽的描述,但它仅仅是本发明一部分实施例,而不是全部实施例,人们还可以根据本实施例在不经创造性前提下获得其他实施例,这些实施例都属于本发明的保护范围。 Although the foregoing embodiment has described the present invention in detail, it is only a part of the embodiments of the present invention, rather than all embodiments, and people can also obtain other embodiments according to the present embodiment without inventive step, these embodiments All belong to the protection scope of the present invention. the
Claims (2)
Priority Applications (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201310563383.9A CN103566899B (en) | 2013-11-06 | 2013-11-06 | A kind of integrated conduct method of agricultural stalk |
CN201510543570.XA CN105148849B (en) | 2013-11-06 | 2013-11-06 | It is a kind of that the application that solid absorbent handles waste water is prepared by wheat stalk |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201310563383.9A CN103566899B (en) | 2013-11-06 | 2013-11-06 | A kind of integrated conduct method of agricultural stalk |
Related Child Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201510543570.XA Division CN105148849B (en) | 2013-11-06 | 2013-11-06 | It is a kind of that the application that solid absorbent handles waste water is prepared by wheat stalk |
Publications (2)
Publication Number | Publication Date |
---|---|
CN103566899A true CN103566899A (en) | 2014-02-12 |
CN103566899B CN103566899B (en) | 2015-08-12 |
Family
ID=50040127
Family Applications (2)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201310563383.9A Expired - Fee Related CN103566899B (en) | 2013-11-06 | 2013-11-06 | A kind of integrated conduct method of agricultural stalk |
CN201510543570.XA Expired - Fee Related CN105148849B (en) | 2013-11-06 | 2013-11-06 | It is a kind of that the application that solid absorbent handles waste water is prepared by wheat stalk |
Family Applications After (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201510543570.XA Expired - Fee Related CN105148849B (en) | 2013-11-06 | 2013-11-06 | It is a kind of that the application that solid absorbent handles waste water is prepared by wheat stalk |
Country Status (1)
Country | Link |
---|---|
CN (2) | CN103566899B (en) |
Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104741083A (en) * | 2015-03-30 | 2015-07-01 | 安徽理工大学 | Method for preparing composite magnetic adsorption material |
CN104986822A (en) * | 2015-06-19 | 2015-10-21 | 华东理工大学 | Preparation method and regeneration method for chemical-modified iron-carrying peanut shell phosphorous removal material |
CN105272389A (en) * | 2015-06-04 | 2016-01-27 | 浙江科技学院 | Pig manure carbon-based fertilizer development method based on soil improvement |
CN105396556A (en) * | 2015-11-12 | 2016-03-16 | 广州逸仙环境保护科技有限公司 | Method for preparing efficient formaldehyde adsorbent by pinecone |
CN105950251A (en) * | 2016-05-12 | 2016-09-21 | 华南理工大学 | Garden rubbish utilization method based on hydrothermal carbonization and solid biomass fuel |
CN106281514A (en) * | 2016-08-31 | 2017-01-04 | 郭迎庆 | A kind of long-acting preparation method stablizing effective dispersant additive |
CN110760323A (en) * | 2019-09-24 | 2020-02-07 | 中国石油天然气集团有限公司 | Magnetic coupling seal transmission structure and thermal reaction furnace |
CN111057568A (en) * | 2019-12-25 | 2020-04-24 | 华南理工大学 | A method for improving the yield of lignin pyrolysis oil and its application |
CN111087068A (en) * | 2019-12-24 | 2020-05-01 | 南京公诚节能新材料研究院有限公司 | Preparation method of biological filter material for water purification treatment |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109078612B (en) * | 2018-08-28 | 2021-08-03 | 山东科技大学 | A kind of carbon-based-nano zero-valent iron composite material and method prepared by using low-rank coal |
CN119488878B (en) * | 2024-11-27 | 2025-05-20 | 辽宁辽河金宇能源集团有限公司科研分公司 | Recyclable sewage treatment agent and preparation method thereof |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2009215285A (en) * | 2008-02-14 | 2009-09-24 | Japan Conservation Engineers Co Ltd | Foreign plant extermination technique |
US20110056125A1 (en) * | 2008-04-17 | 2011-03-10 | Csl Carbon Solutions Ltd. | Process for converting biomass to coal-like material using hydrothermal carbonisation |
CN103058313A (en) * | 2013-01-11 | 2013-04-24 | 中国科学院南京土壤研究所 | Method for removing oxytetracycline from livestock and poultry breeding wastewater by biomass charcoal of straws |
Family Cites Families (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US8414664B2 (en) * | 2009-03-02 | 2013-04-09 | HydoChar LLC | Algal coal and process for preparing same |
CN102626608A (en) * | 2012-04-16 | 2012-08-08 | 南京大学 | Straw modified into amphiprotic adsorbent and preparation method thereof |
-
2013
- 2013-11-06 CN CN201310563383.9A patent/CN103566899B/en not_active Expired - Fee Related
- 2013-11-06 CN CN201510543570.XA patent/CN105148849B/en not_active Expired - Fee Related
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2009215285A (en) * | 2008-02-14 | 2009-09-24 | Japan Conservation Engineers Co Ltd | Foreign plant extermination technique |
US20110056125A1 (en) * | 2008-04-17 | 2011-03-10 | Csl Carbon Solutions Ltd. | Process for converting biomass to coal-like material using hydrothermal carbonisation |
CN103058313A (en) * | 2013-01-11 | 2013-04-24 | 中国科学院南京土壤研究所 | Method for removing oxytetracycline from livestock and poultry breeding wastewater by biomass charcoal of straws |
Cited By (13)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104741083A (en) * | 2015-03-30 | 2015-07-01 | 安徽理工大学 | Method for preparing composite magnetic adsorption material |
CN105272389A (en) * | 2015-06-04 | 2016-01-27 | 浙江科技学院 | Pig manure carbon-based fertilizer development method based on soil improvement |
CN104986822B (en) * | 2015-06-19 | 2017-03-08 | 华东理工大学 | Preparation and regeneration method of chemically modified iron-loaded peanut shell phosphorus removal material |
CN104986822A (en) * | 2015-06-19 | 2015-10-21 | 华东理工大学 | Preparation method and regeneration method for chemical-modified iron-carrying peanut shell phosphorous removal material |
CN105396556A (en) * | 2015-11-12 | 2016-03-16 | 广州逸仙环境保护科技有限公司 | Method for preparing efficient formaldehyde adsorbent by pinecone |
CN105396556B (en) * | 2015-11-12 | 2017-10-31 | 广州逸仙环境保护科技有限公司 | A kind of method that efficient formaldehyde adsorbent is prepared with the pinecone |
CN105950251A (en) * | 2016-05-12 | 2016-09-21 | 华南理工大学 | Garden rubbish utilization method based on hydrothermal carbonization and solid biomass fuel |
CN106281514A (en) * | 2016-08-31 | 2017-01-04 | 郭迎庆 | A kind of long-acting preparation method stablizing effective dispersant additive |
CN106281514B (en) * | 2016-08-31 | 2018-07-13 | 佛山市南海海丰化工有限公司 | A kind of preparation method of long-acting stable effective dispersant additive |
CN110760323A (en) * | 2019-09-24 | 2020-02-07 | 中国石油天然气集团有限公司 | Magnetic coupling seal transmission structure and thermal reaction furnace |
CN111087068A (en) * | 2019-12-24 | 2020-05-01 | 南京公诚节能新材料研究院有限公司 | Preparation method of biological filter material for water purification treatment |
CN111057568A (en) * | 2019-12-25 | 2020-04-24 | 华南理工大学 | A method for improving the yield of lignin pyrolysis oil and its application |
CN111057568B (en) * | 2019-12-25 | 2020-12-22 | 华南理工大学 | A method for improving the yield of lignin pyrolysis oil and its application |
Also Published As
Publication number | Publication date |
---|---|
CN105148849A (en) | 2015-12-16 |
CN103566899B (en) | 2015-08-12 |
CN105148849B (en) | 2017-11-07 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN103566899A (en) | Comprehensive treatment method for agricultural straws | |
CN105170091A (en) | Preparation method of iron-modified reed biological carbon, and application of iron-modified reed biological carbon in treatment of phosphorus wastewater | |
CN107096500A (en) | A kind of utilization Chinese medicine slag prepares the method for magnetic bio charcoal, magnetic bio charcoal and application | |
CN110773123A (en) | Biochar/zeolite composite adsorbent material and preparation method thereof | |
CN107970891B (en) | One kind being based on malic acid and KMnO4The preparation method of the combined modified hot charcoal of cow dung biogas pulp water | |
CN102107872A (en) | A process for preparing activated carbon by adding fruit shells to chemical sludge | |
CN106115691A (en) | The preparation method of a kind of bamboo shell matrix activated carbon and using method | |
CN104084128A (en) | Kitchen waste residue modified sludge activated carbon for sweater treatment | |
CN104785207B (en) | High-adsorption performance biochar for heavy metal ions and preparation method for high-adsorption-performance biochar | |
CN105854800A (en) | Method for preparing modified charcoal by utilizing aquatic plant wastes and hydrochloric acid | |
CN107570115A (en) | A kind of preparation method of crab shell charcoal | |
CN106732361A (en) | A kind of preparation method of the sludge base charcoal of the paper powder that adulterates | |
CN110684647A (en) | System and method for realizing biogas residue drying heat balance by virtue of synergistic digestion of kitchen waste, kitchen waste and municipal sludge | |
CN104801271A (en) | Method for preparing modified rice hull biochar and conditioning urban sludge through modified rice hull biochar | |
CN102658083B (en) | Modified sludge activated carbon for removing multiple heavy metals in sewage and sludge simultaneously | |
CN106512947A (en) | Preparation method of sludge-based charcoal doped with bamboo and wood powder | |
CN103272566B (en) | Method for preparing ammonia nitrogen adsorbent by using banana peel and application of ammonia nitrogen adsorbent | |
CN106221849A (en) | Stalk fuel containing biomass sludge and preparation method thereof | |
CN106111060A (en) | A kind of modification biological carbon composite and preparation thereof and application | |
CN115722190B (en) | A method for preparing hydrothermal biochar using eggshell-modified crop straw | |
CN103803735A (en) | Combined process for cutting down heavy metals in biogas slurry | |
CN106000416A (en) | Method for preparing ozone catalyst by using agricultural waste straw as raw material and application thereof | |
CN102134072A (en) | Process for preparing activated carbon by using excess sludge from pesticide chemical industry sewage treatment | |
CN103332690A (en) | Food residue activated carbon for wastewater treatment, and preparation method of food residue activated carbon | |
CN105080482A (en) | Production method for biomass charcoal adsorbents |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20150812 Termination date: 20161106 |
|
CF01 | Termination of patent right due to non-payment of annual fee |