CN101973687A - Sludge treatment method - Google Patents
Sludge treatment method Download PDFInfo
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- CN101973687A CN101973687A CN 201010525075 CN201010525075A CN101973687A CN 101973687 A CN101973687 A CN 101973687A CN 201010525075 CN201010525075 CN 201010525075 CN 201010525075 A CN201010525075 A CN 201010525075A CN 101973687 A CN101973687 A CN 101973687A
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Abstract
The invention relates to the field of sludge treatment, in particular to a sludge treatment method. Aiming at the problems in the prior art, the invention provides a sludge treatment method with good flocculation effect and low treatment cost. The sludge treatment method comprises the following steps of: 1) decomposing, conveying the sludge into a sludge mixing tank, and putting an inorganic polymer water purifying agent into the sludge mixing tank; 2) conveying the sludge treated by the inorganic polymer water purifying agent into a stirring and mixing bucket, adding a cationic flocculant, and stirring for full reaction; and 3) conveying the reacted sludge into a filter press and dewatering. The sludge treated by the process has low water content, and the flocculation effect is good; and then the sludge is treated, so the treatment cost is low.
Description
Technical field
The present invention relates to field of sludge treatment, be specifically related to a kind of method for sludge treatment.
Background technology
Pulping and paper-making is one of important industry of Chinese national economy, and the output of the carton cardboard of China's production at present leaps to the first in the world, and over nearly 3 years, secondary stock proportion in paper making raw material surpasses 56%.But, in paper-making process, produced a large amount of waste sludge from paper mill mud, with the present papermaking scale of China, estimate that the paper mill sludge that produces has reached 2,000 ten thousand tons/year.The improvement of paper mill sludge becomes the main environment protection treating object of China's paper industry.
Paper mill sludge is mainly derived from following three aspects: the one, and chemical pulping alkali reclaims station white clay recycle section, is the product of lotusization reaction, belongs to precipitated chalk; The 2nd, the biological sludge that produces in the paper waste treating processes; Three stones come from the deinked sludge of paper-making process from waste paper deinking workshop section, the non-fiber impurity of screening scavenging process.At present, back two kinds of main sources that mud is China's papermaking weapon.
The prime cost of biological sludge is generally: fiber fines, xylogen and derivative thereof and some organism.The complex chemical composition of waste paper pulp-making waste residue, organism accounts for 70% ~ 90%, inorganics and metallic impurity account for 10% ~ 30%, mainly containing plastics class, fiber fines, rag, cotton yarn, mess-tin, abandoned optical discs in the organism and from the various organic-fuels of printing-ink, tackiness agent etc., mainly is other inorganic salt that add in papermaking filler (as alumina etc.), coating (as kaolin etc.) and the pulping and papermaking processes in the inorganics.The chemical constitution and the characteristic of the solid slag that waste paper pulp-making and deinking process produce also are subjected to many factor affecting.
These biochemistry and materialized mud just carry out conventional processed in treating processes at present, and the dewatering of mud is poor, the water ratio height, the processing cost height.The problem that prior art exists is: have in the conventional sludge dewatering that flocculating effect is poor, water ratio height and a processing cost height.
Summary of the invention
Problem at prior art exists the invention provides the method for sludge treatment that a kind of flocculating effect is good, processing cost is low.
A kind of method for sludge treatment may further comprise the steps:
1) decomposes, mud is transported in the mud mixing pit, in the mud mixing pit, drop into inorganic high molecular water purifier;
2) mud that inorganic high molecular water purifier was handled is sent into and is mixed bucket, adds cationic flocculant simultaneously, stirs, and it is fully reacted;
3) reacted mud is sent into pressure filter, dehydration.
Wherein, described mud is biochemical sludge and materialized mud.
Wherein, among the described step b, the mud that inorganic high molecular water purifier was handled is pumped into through pipeline by sludge pump and mixes in the bucket, adds cationic flocculant in pipeline.
Wherein, inorganic high molecular water purifier be polymerize aluminum chloride, aluminium iron polychloride, aluminium chlorohydroxide, ferrous sulfate, Tai-Ace S 150, bodied ferric sulfate wherein any one.
Wherein, described cationic flocculant be polyacrylamide, polyacrylic acid, sodium polyacrylate, calcium polyacrylate (CPA) wherein any one.
Compared with prior art, advantage of the present invention is as follows:
A kind of method for sludge treatment may further comprise the steps: 1) decompose, mud is transported in the mud mixing pit, drop into inorganic high molecular water purifier in the mud mixing pit; 2) mud that inorganic high molecular water purifier was handled is sent into the bucket that mixes before the water extracter, adds the organic polymer cationic polyacrylamide simultaneously, stirs, and it is fully reacted; 3) mud after the flocculation reaction is sent into pressure filter, dehydration.The sludge moisture content of crossing through art breading of the present invention is very low, and flocculating effect is good, carries out sludge treatment afterwards again, and processing cost is low.
Description of drawings
Fig. 1 is a structural representation of the present invention.
Embodiment
Below in conjunction with embodiment the present invention is done detailed description.
Embodiment 1, referring to Fig. 1, a kind of method for sludge treatment may further comprise the steps:
1) decomposes, mud is transported in the mud mixing pit, in the mud mixing pit, drop into polymerize aluminum chloride;
2) mud that polymerize aluminum chloride was handled is sent into and is mixed bucket, adds polyacrylamide simultaneously, stirs, and it is fully reacted;
3) reacted mud is sent into pressure filter, dehydration.
Wherein, described mud is biochemical sludge and materialized mud.
Wherein, among the described step b, the mud that inorganic high molecular water purifier was handled is pumped into through pipeline by sludge pump and mixes in the bucket, adds polyacrylamide in pipeline.
Embodiment 2, referring to Fig. 1, a kind of method for sludge treatment may further comprise the steps:
1) decomposes, mud is transported in the mud mixing pit, in the mud mixing pit, drop into aluminium iron polychloride;
2) mud that aluminium iron polychloride was handled is sent into and is mixed bucket, adds sodium polyacrylate simultaneously, stirs, and it is fully reacted;
3) reacted mud is sent into pressure filter, dehydration.
Wherein, described mud is biochemical sludge and materialized mud.
Wherein, among the described step b, the mud that inorganic high molecular water purifier was handled is pumped into through pipeline by sludge pump and mixes in the bucket, adds sodium polyacrylate in pipeline.
Embodiment 3, referring to Fig. 1, a kind of method for sludge treatment may further comprise the steps:
1) decomposes, mud is transported in the mud mixing pit, in the mud mixing pit, drop into bodied ferric sulfate;
2) mud that bodied ferric sulfate was handled is sent into and is mixed bucket, adds calcium polyacrylate (CPA) simultaneously, stirs, and it is fully reacted;
3) reacted mud is sent into pressure filter, dehydration.
Wherein, described mud is biochemical sludge and materialized mud.
Wherein, among the described step b, the mud that inorganic high molecular water purifier was handled is pumped into through pipeline by sludge pump and mixes in the bucket, adds calcium polyacrylate (CPA) in pipeline.
Above content is preferred embodiment of the present invention only, and for those of ordinary skill in the art, according to thought of the present invention, the part that all can change in specific embodiments and applications, this description should not be construed as limitation of the present invention.
Claims (5)
1. method for sludge treatment may further comprise the steps:
1) decomposes, mud is transported in the mud mixing pit, in the mud mixing pit, drop into inorganic high molecular water purifier;
2) mud that inorganic high molecular water purifier was handled is sent into and is mixed bucket, adds cationic flocculant simultaneously, stirs, and it is fully reacted;
3) reacted mud is sent into pressure filter, dehydration.
2. a kind of method for sludge treatment as claimed in claim 1 is characterized in that: described mud is biochemical sludge and materialized mud.
3. a kind of method for sludge treatment as claimed in claim 2 is characterized in that: among the described step b, the mud that inorganic high molecular water purifier was handled is pumped into through pipeline by sludge pump and mixes in the bucket, adds cationic flocculant in pipeline.
4. a kind of method for sludge treatment as claimed in claim 3 is characterized in that: described inorganic high molecular water purifier be polymerize aluminum chloride, aluminium iron polychloride, aluminium chlorohydroxide, ferrous sulfate, Tai-Ace S 150, bodied ferric sulfate wherein any one.
5. as claim 3 or 4 described a kind of method for sludge treatment, it is characterized in that: described cationic flocculant be polyacrylamide, polyacrylic acid, sodium polyacrylate, calcium polyacrylate (CPA) wherein any one.
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CN 201010525075 CN101973687A (en) | 2010-10-29 | 2010-10-29 | Sludge treatment method |
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Cited By (17)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102491618A (en) * | 2011-11-29 | 2012-06-13 | 曾秀仪 | Depth dehydration method for residual sludge |
CN102674657A (en) * | 2012-06-11 | 2012-09-19 | 安徽国祯环保节能科技股份有限公司 | Sludge dewatering method for urban sewage plant |
CN102964053A (en) * | 2012-11-09 | 2013-03-13 | 徐渊 | Domestic sludge drying treatment method |
CN103524016A (en) * | 2013-10-22 | 2014-01-22 | 山东省环境保护科学研究设计院 | Stable settling agent and stable settling method of heavy-metal bottom mud |
CN103910444A (en) * | 2012-12-28 | 2014-07-09 | 栗田工业株式会社 | Agglutination treatment method for silt-containing water and device |
CN104671636A (en) * | 2015-01-30 | 2015-06-03 | 深圳市水务(集团)有限公司 | Deep dehydration conditioning medicament for sludge and application method of deep dehydration conditioning medicament |
CN104692610A (en) * | 2015-02-03 | 2015-06-10 | 无锡金园污泥处置新型燃料科技有限公司 | Method for preparing cement raw materials from industrial sludge |
CN105016451A (en) * | 2015-07-16 | 2015-11-04 | 中国轻工业长沙工程有限公司 | Recycling method for iron-enriched sludge of pulping and papermaking factory wastewater |
CN105541081A (en) * | 2016-01-22 | 2016-05-04 | 浙江正洁环境科技有限公司 | Composite conditioner for sludge dewatering and using method thereof |
CN105776815A (en) * | 2016-03-11 | 2016-07-20 | 湖南清和环保技术有限公司 | Agent for deep dehydration of sludge and preparation method for agent |
CN105967484A (en) * | 2015-12-29 | 2016-09-28 | 南京紫鑫汇萃环境科技有限公司 | Sludge deep dehydration method for processing flue gas desulfurization wastewater sludge |
CN106396306A (en) * | 2016-11-02 | 2017-02-15 | 赵青娇 | Sludge deodorant and preparation method thereof |
CN107253812A (en) * | 2017-08-07 | 2017-10-17 | 深圳市海源能源科技有限公司 | The ameliorative way of dewatering performance of sludge after a kind of hydrolysis acidification |
CN108249732A (en) * | 2018-02-12 | 2018-07-06 | 山鹰国际控股股份公司 | A kind of paper mill sludge conditioning, dehydration, desiccation, incineration treatment technology |
CN110436746A (en) * | 2019-07-31 | 2019-11-12 | 克拉玛依市博瑞科技发展有限公司 | Water, mud release agent and preparation method thereof and application method |
CN112028258A (en) * | 2020-08-26 | 2020-12-04 | 江苏建霖环保科技有限公司 | Water purifying agent for rapid treatment of industrial wastewater and preparation method thereof |
CN113149398A (en) * | 2021-04-30 | 2021-07-23 | 玖龙纸业(东莞)有限公司 | Improved papermaking sludge treatment method |
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JPS5323145A (en) * | 1976-07-20 | 1978-03-03 | Kurita Water Ind Ltd | Method of dehydrating sludge |
CN1305976A (en) * | 2000-01-14 | 2001-08-01 | 曾智勇 | Process for treating sludge generated after sewage treatment |
CN101367597A (en) * | 2008-09-17 | 2009-02-18 | 广州绿由工业弃置废物回收处理有限公司 | Flocculating agent for sludge dewatering and sludge dewatering method |
CN101704629A (en) * | 2009-09-18 | 2010-05-12 | 东莞玖龙纸业有限公司 | Method for dynamically controlling continuous feeding in dehydration of papermaking sludge |
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2010
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JPS5323145A (en) * | 1976-07-20 | 1978-03-03 | Kurita Water Ind Ltd | Method of dehydrating sludge |
CN1305976A (en) * | 2000-01-14 | 2001-08-01 | 曾智勇 | Process for treating sludge generated after sewage treatment |
CN101367597A (en) * | 2008-09-17 | 2009-02-18 | 广州绿由工业弃置废物回收处理有限公司 | Flocculating agent for sludge dewatering and sludge dewatering method |
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Non-Patent Citations (1)
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Cited By (21)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102491618A (en) * | 2011-11-29 | 2012-06-13 | 曾秀仪 | Depth dehydration method for residual sludge |
CN102674657A (en) * | 2012-06-11 | 2012-09-19 | 安徽国祯环保节能科技股份有限公司 | Sludge dewatering method for urban sewage plant |
CN102964053A (en) * | 2012-11-09 | 2013-03-13 | 徐渊 | Domestic sludge drying treatment method |
CN102964053B (en) * | 2012-11-09 | 2014-06-04 | 徐渊 | Domestic sludge drying treatment method |
CN103910444A (en) * | 2012-12-28 | 2014-07-09 | 栗田工业株式会社 | Agglutination treatment method for silt-containing water and device |
CN103524016A (en) * | 2013-10-22 | 2014-01-22 | 山东省环境保护科学研究设计院 | Stable settling agent and stable settling method of heavy-metal bottom mud |
CN104671636A (en) * | 2015-01-30 | 2015-06-03 | 深圳市水务(集团)有限公司 | Deep dehydration conditioning medicament for sludge and application method of deep dehydration conditioning medicament |
CN104692610A (en) * | 2015-02-03 | 2015-06-10 | 无锡金园污泥处置新型燃料科技有限公司 | Method for preparing cement raw materials from industrial sludge |
CN105016451A (en) * | 2015-07-16 | 2015-11-04 | 中国轻工业长沙工程有限公司 | Recycling method for iron-enriched sludge of pulping and papermaking factory wastewater |
CN105967484A (en) * | 2015-12-29 | 2016-09-28 | 南京紫鑫汇萃环境科技有限公司 | Sludge deep dehydration method for processing flue gas desulfurization wastewater sludge |
CN105541081A (en) * | 2016-01-22 | 2016-05-04 | 浙江正洁环境科技有限公司 | Composite conditioner for sludge dewatering and using method thereof |
CN105776815A (en) * | 2016-03-11 | 2016-07-20 | 湖南清和环保技术有限公司 | Agent for deep dehydration of sludge and preparation method for agent |
CN105776815B (en) * | 2016-03-11 | 2019-09-06 | 袁锐 | A kind of medicament and preparation method for deeply dehydrating sludge |
CN106396306A (en) * | 2016-11-02 | 2017-02-15 | 赵青娇 | Sludge deodorant and preparation method thereof |
CN107253812A (en) * | 2017-08-07 | 2017-10-17 | 深圳市海源能源科技有限公司 | The ameliorative way of dewatering performance of sludge after a kind of hydrolysis acidification |
CN107253812B (en) * | 2017-08-07 | 2020-12-04 | 深圳市海源能源科技有限公司 | Method for improving dehydration performance of sludge subjected to hydrolytic acidification |
CN108249732A (en) * | 2018-02-12 | 2018-07-06 | 山鹰国际控股股份公司 | A kind of paper mill sludge conditioning, dehydration, desiccation, incineration treatment technology |
CN108249732B (en) * | 2018-02-12 | 2019-01-22 | 山鹰国际控股股份公司 | A kind of paper mill sludge conditioning, dehydration, desiccation, incineration treatment technology |
CN110436746A (en) * | 2019-07-31 | 2019-11-12 | 克拉玛依市博瑞科技发展有限公司 | Water, mud release agent and preparation method thereof and application method |
CN112028258A (en) * | 2020-08-26 | 2020-12-04 | 江苏建霖环保科技有限公司 | Water purifying agent for rapid treatment of industrial wastewater and preparation method thereof |
CN113149398A (en) * | 2021-04-30 | 2021-07-23 | 玖龙纸业(东莞)有限公司 | Improved papermaking sludge treatment method |
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Application publication date: 20110216 |