CN101077817A - Method for processing paper-making waste water of regenerative paper - Google Patents
Method for processing paper-making waste water of regenerative paper Download PDFInfo
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- CN101077817A CN101077817A CN 200610010918 CN200610010918A CN101077817A CN 101077817 A CN101077817 A CN 101077817A CN 200610010918 CN200610010918 CN 200610010918 CN 200610010918 A CN200610010918 A CN 200610010918A CN 101077817 A CN101077817 A CN 101077817A
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Abstract
The process of treating effluent from making paper with waste paper belongs to the field of industrial effluent treating technology, and aims at lowering the harmful matter content in the effluent from making paper with waste paper to reach the exhaust standard. The process includes the first passing the effluent through grating to filter out fiber and suspended matter, the subsequent settling in a sloping plate settling tank to eliminate granular impurity, flocculating in an air floating tank with flocculant and fishing out the resultant suspended matter, anaerobic reaction in an anaerobic settling tank, treating with introduced air and active sludge in an aeration tank and eliminating suspended matter and colloidal matter, clarifying in a settling tank, and treating in artificial wetland to eliminate nitrogen and phosphate and obtain clear water. The process can reduce SS, BOD5 and CODcr of the effluent obviously and make the effluent reach draining standard.
Description
Technical field
The invention belongs to the industrial sewage treatment technology field, particularly a kind of paper waste treatment process.
Background technology
Regenerated papermaking is a main raw material with useless paperboard, disregard message paper, useless book paper etc., products such as the white board of production plurality of specifications, boxboard, fluting board.Mainly contain pollutents such as hemicellulose, xylogen, inorganic acid salt, fiber fines, mineral filler and printing ink, dyestuff in the waste paper making wastewater.Xylogen, hemicellulose mainly form the COD and the BOD of waste water
5The main SS that forms such as fiber fines, mineral filler; Main colourity and the COD of forming such as printing ink, dyestuff.It is all higher that these pollutent concentrated expressions go out SS, the COD index of waste water.
The waste water treatment technology technologies that adopt to regenerated papermaking are more at present:
(1), with pitch grid or nylon wire to papermaking after effusive waste water filter, reclaim the fiber in the waste water;
(2), again waste water is flowed into inclined-plate clarifying basin, the granular impurity in the precipitation removal waste water;
(3), the waste water in the inclined-plate clarifying basin is flowed into air flotation pool, adding flocculation agent, the fine-fibered in the cohesion water;
(4), the reacted suspended substance of waste water in the air flotation pool and flocculation agent salvaged to the pond, removes, then the waste water in the pond is flowed into the precipitation anaerobic pond, carry out biochemical anaerobic reaction, remove objectionable constituent;
After the aforesaid method processing, can remove SS, remove most of non-solubility COD and being partly dissolved property COD and BOD simultaneously
5
Show that yet research and analyse generally, each Pollutant levels is in the treated waste water: SS approximately is 62mg/l, BOD
5Approximately be 180mg/l, CODcr approximately is 460mg/l, as seen, though be greatly improved by the waste water water quality after the aforesaid method processing, but still do not reach national environmental protection emission standards and requirement.
Summary of the invention
Objectionable impurities exceeds standard in the present regeneration paper mill wastewater processing in order to solve, and can not reach the problem of emission standard, the invention provides a kind of method for processing paper-making waste water of regenerative paper, and its technical scheme is as follows:
The paper waste treatment process, this method comprises the steps:
(1), filtered and recycled: with pitch be 0.15mm~0.25mm grid or 60 orders~70 order nylon wires to papermaking after effusive waste water filter, the waste water after the filtration flows into the fiber recovery pond, reclaims fiber and other suspended substance in the waste water;
(2), precipitation purifies: the waste water in the fiber recovery pond is flowed into inclined-plate clarifying basin, and precipitation is removed the granular impurity in the waste water;
(3), air supporting removes fine: the waste water in the inclined-plate clarifying basin is flowed into air flotation pool, add flocculation agent in air flotation pool, with flocculation agent and waste water uniform mixing, condense the fine-fibered in the water;
(4), anaerobic treatment: waste water in the air flotation pool and the reacted suspended substance of flocculation agent are salvaged to the pond, then the waste water in the pond is flowed into the precipitation anaerobic pond;
(5), aerobic is handled: the waste water that will precipitate in the anaerobic pond flows into the aeration tank, in the aeration tank, add and contain microbic activity mud, carry out aeration from the bottom bubbling air of aeration tank, the blast inlet mean number of bottom, aeration tank is to be no less than 2 in 1 square metre;
(6), secondary sedimentation: the waste water in the aeration tank is flowed into secondary sedimentation basins, and the secondary sedimentation basins bottom is a gravel bed system;
(7), wetland purification: the primary purifying water in the secondary sedimentation basins is flowed into the artificial swamp pond, the bottom in artificial swamp pond and be the antiseep wall all around, kind is implanted with plant in the pond;
(8), water purification reclaims: artificial swamp is not held the effusive inflow clean water basin of purifying waste water, recycle.
After the aforesaid method processing, SS, BOD in the waste water
5, CODcr obviously reduces, clearance is: SS is 98.95%, BOD
5Be 95.11%, CODcr is 93.51%, emission concentration all meets " paper industry pollution discharge standard " requirement.
Description of drawings
Fig. 1 is a process flow sheet of the present invention.
Embodiment
Method for processing paper-making waste water of regenerative paper, this method comprises the steps:
(1), with pitch be the 0.22mm grid to papermaking after effusive waste water filter, waste water after the filtration flows into the fiber recovery pond, reclaims fiber and other suspended substance in the waste water; Also can filter with 70 order nylon wires;
(2), the waste water in the fiber recovery pond is flowed into inclined-plate clarifying basin, precipitation is removed the granular impurity in the waste water, and sedimentation time is 8 hours;
(3), the waste water in the inclined-plate clarifying basin is flowed into air flotation pool, in air flotation pool, add flocculation agent,, condense the fine-fibered in the water flocculation agent and waste water uniform mixing;
(4), remove suspended substance, the reacted suspended substance of waste water in the air flotation pool and flocculation agent is salvaged to the pond, with the inflow of the waste water in pond anaerobic pond, carry out anaerobic treatment then;
(5), the waste water that will precipitate in the anaerobic pond flows into the aeration tank, adds in the aeration tank and contains microbic activity mud, carries out aeration from the bottom bubbling air of aeration tank, the blast inlet mean number of bottom, aeration tank is to have 4 in 1 square metre; In the aeration tank, 1 hour processing wastewater flow rate is 4 cubic metres in 1 cubic metre of volume, and 1 hour the air blast amount of carrying out is 150 cubic metres in 1 cubic metre the waste water, sneaks into 0.1 cubic metre of active mud content average out in 1 cubic metre of waste water;
(6), the waste water in the aeration tank is flowed into secondary sedimentation basins, the secondary sedimentation basins bottom is a gravel bed system;
(7), the primary purifying water in the secondary sedimentation basins is flowed into the artificial swamp pond, the bottom in artificial swamp pond and be the antiseep wall of concrete structure all around, kind is implanted with plant in the pond; The depth of water in the artificial swamp pond is between 0.6 meter, and 1 square metre of artificial swamp per hour purifies the water yield and is no more than 2 cubic metres, plants in the pond to be implanted with fishscale bamboo, cattail, reed, Herba Eichhorniae, big wooden dipper.
(8), artificial swamp is not held the effusive inflow clean water basin of purifying waste water, recycle.
Claims (3)
1, paper waste treatment process, this method comprises the steps:
(1), with pitch be 0.15mm~0.25mm grid or 60 orders~70 order nylon wires to papermaking after effusive waste water filter, the waste water after the filtration flows into the fiber recovery pond, reclaims fiber and other suspended substance in the waste water;
(2), the waste water in the fiber recovery pond is flowed into inclined-plate clarifying basin, the granular impurity in the precipitation removal waste water;
(3), the waste water in the inclined-plate clarifying basin is flowed into air flotation pool, in air flotation pool, add flocculation agent,, condense the fine-fibered in the water flocculation agent and waste water uniform mixing;
(4), waste water in the air flotation pool and the reacted suspended substance of flocculation agent are salvaged to the pond, then with the inflow of the waste water in pond precipitation anaerobic pond;
It is characterized in that: handle through following several steps again from the effusive waste water of precipitation anaerobic pond
(5), the waste water that will precipitate in the anaerobic pond flows into the aeration tank, adds in the aeration tank and contains microbic activity mud, carries out aeration from the bottom bubbling air of aeration tank, the blast inlet mean number of bottom, aeration tank is to be no less than 2 in 1 square metre;
(6), the waste water in the aeration tank is flowed into secondary sedimentation basins, the secondary sedimentation basins bottom is a gravel bed system;
(7), the primary purifying water in the secondary sedimentation basins is flowed into the artificial swamp pond, the bottom in artificial swamp pond and be the antiseep wall all around, kind is implanted with plant in the pond;
(8), artificial swamp is not held the effusive inflow clean water basin of purifying waste water, recycle.
2, paper waste treatment process as claimed in claim 1, it is characterized in that: in the aeration tank, per hour handle wastewater flow rate in 1 cubic metre of volume between 1 cubic metre to 8 cubic metres, air blast air input hourly is sneaked into active mud content between 0.05 cubic metre to 0.2 cubic metre in 1 cubic metre the waste water in 1 cubic metre of waste water between 50 cubic metres to 400 cubic metres.
3, paper waste treatment process as claimed in claim 1 is characterized in that: the depth of water in the artificial swamp pond is between 0.4 meter to 0.8 meter, and 1 square metre of artificial swamp per hour purifies the water yield and is no more than 4 cubic metres, and the plant variety of plantation is no less than 2 kinds in the pond.
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CN 200610010918 CN101077817A (en) | 2006-05-24 | 2006-05-24 | Method for processing paper-making waste water of regenerative paper |
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CN 200610010918 CN101077817A (en) | 2006-05-24 | 2006-05-24 | Method for processing paper-making waste water of regenerative paper |
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Cited By (24)
Publication number | Priority date | Publication date | Assignee | Title |
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CN101767918A (en) * | 2010-02-10 | 2010-07-07 | 泉州华祥纸业有限公司 | Synusiologic processing method of paper manufacturing waste water |
CN101708916B (en) * | 2009-09-14 | 2012-06-27 | 陕西科技大学 | Closed circulation and zero emission processes for papermaking wastewater |
CN102874985A (en) * | 2012-10-17 | 2013-01-16 | 中国科学院亚热带农业生态研究所 | Method for treating waste pollutants in pig farm |
CN103028285A (en) * | 2012-12-17 | 2013-04-10 | 中国核电工程有限公司 | Filter system for built-in containment refueling water storage tank |
CN103408202A (en) * | 2013-08-30 | 2013-11-27 | 中水珠江规划勘测设计有限公司 | High-density sedimentation internal circulating integrated sewage treatment equipment |
CN103496823A (en) * | 2009-11-04 | 2014-01-08 | 大亚有限公司 | Method for comprehensive treatment on domestic sewage and organic garbage and equipment thereof |
CN103723855A (en) * | 2013-12-13 | 2014-04-16 | 云南中烟昆船瑞升科技有限公司 | Pre-treatment technology for sewage produced during production of paper-making reconstituted tobaccos |
CN103964613A (en) * | 2014-05-27 | 2014-08-06 | 浙江华川实业集团有限公司 | Wastewater treatment process for paper mill |
CN103964653A (en) * | 2014-05-27 | 2014-08-06 | 浙江华川实业集团有限公司 | Wastewater recovery processing process of paper mill |
CN104692593A (en) * | 2015-02-28 | 2015-06-10 | 江苏高科物流科技股份有限公司 | Treatment method applied to industrial wastewater |
CN104986924A (en) * | 2015-08-03 | 2015-10-21 | 富阳鸿祥技术服务有限公司 | Industrial waste-water treating system for paper making factory |
CN105060641A (en) * | 2015-08-11 | 2015-11-18 | 怀宁县天元纸业有限公司 | Paper-making wastewater treatment method |
CN105084659A (en) * | 2015-08-11 | 2015-11-25 | 浙江惠同纸业有限公司 | Paper mill wastewater treatment technology and treatment equipment thereof |
CN105152450A (en) * | 2015-08-18 | 2015-12-16 | 杭州启澄科技有限公司 | Physical pretreatment system for paper mill wastewater |
CN105239448A (en) * | 2015-10-14 | 2016-01-13 | 泉州华祥纸业有限公司 | Method for preparing tissue paper by reuse water |
CN105399284A (en) * | 2015-12-23 | 2016-03-16 | 沈晓笑 | Papermaking wastewater and sludge ecological recycling system and ecological recycling method |
CN106517641A (en) * | 2016-10-17 | 2017-03-22 | 南京大学 | Papermaking waste water deep processing and safe ecological utilization integrated technology based on toxicity reduction |
CN107265796A (en) * | 2017-08-18 | 2017-10-20 | 安徽国能亿盛环保科技有限公司 | A kind of device for processing papermaking wastewater |
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CN111472185A (en) * | 2020-04-08 | 2020-07-31 | 石河子市国力源环保制浆有限公司 | Recycling method in straw pulping and papermaking process |
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CN114804354A (en) * | 2022-06-24 | 2022-07-29 | 北京涞澈科技发展有限公司 | Biological rotary drum denitrification filter tank and denitrification treatment system based on sulfur autotrophy |
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2006
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Cited By (31)
Publication number | Priority date | Publication date | Assignee | Title |
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CN101708916B (en) * | 2009-09-14 | 2012-06-27 | 陕西科技大学 | Closed circulation and zero emission processes for papermaking wastewater |
CN103496823A (en) * | 2009-11-04 | 2014-01-08 | 大亚有限公司 | Method for comprehensive treatment on domestic sewage and organic garbage and equipment thereof |
CN101767918A (en) * | 2010-02-10 | 2010-07-07 | 泉州华祥纸业有限公司 | Synusiologic processing method of paper manufacturing waste water |
CN102874985A (en) * | 2012-10-17 | 2013-01-16 | 中国科学院亚热带农业生态研究所 | Method for treating waste pollutants in pig farm |
CN102874985B (en) * | 2012-10-17 | 2014-01-15 | 中国科学院亚热带农业生态研究所 | Method for treating waste pollutants in pig farm |
CN103028285A (en) * | 2012-12-17 | 2013-04-10 | 中国核电工程有限公司 | Filter system for built-in containment refueling water storage tank |
CN103028285B (en) * | 2012-12-17 | 2015-04-22 | 中国核电工程有限公司 | Filter system for built-in containment refueling water storage tank |
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CN103723855A (en) * | 2013-12-13 | 2014-04-16 | 云南中烟昆船瑞升科技有限公司 | Pre-treatment technology for sewage produced during production of paper-making reconstituted tobaccos |
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