CN101781056A - Treatment method of waste papermaking water - Google Patents
Treatment method of waste papermaking water Download PDFInfo
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- CN101781056A CN101781056A CN200910001270A CN200910001270A CN101781056A CN 101781056 A CN101781056 A CN 101781056A CN 200910001270 A CN200910001270 A CN 200910001270A CN 200910001270 A CN200910001270 A CN 200910001270A CN 101781056 A CN101781056 A CN 101781056A
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Abstract
The invention relates to a treatment method of waste papermaking water, which comprises the steps of filtration, flocculation and sedimentation, QA2O treatment and deep treatment. Because the QA2O treatment process is adopted in the treatment method of the invention for replacing the conventional biochemical treatment method, the treatment cost is greatly reduced, in addition, the treatment effect is perfect, and the technical process is simple and can be implemented easily. The method of the invention can be used for treating various kinds of waste papermaking water, particularly the middle section waste water with high load. The waste water treated by the method of the invention can reach the national specified discharge standard, or can be reused in the papermaking process.
Description
Technical field
The present invention relates to a kind of technological process for the treatment of papermaking method, particularly relate to a kind of purifying treatment method of papermaking midcourse wastewater.
Background technology
The whole process of production of pulp and paper industry needs a large amount of water, these water have compiled a large amount of industrial objectionable impuritiess in process of production, both can't directly utilize, directly discharging pollutes the environment again, therefore, the waste water that each stage of pulping and papermaking processes is produced carries out recycling, and remarkable economical and social value are arranged, and is determining the survival and development of papermaking enterprise.
In paper industry, adopt treatment process centering water such as chemical precipitation, air supporting processing and bio-oxidation to handle usually.
Papermaking environmental protection one-level processing traditional technology is just heavy or materialization flocculation sediment at present, the flocculation process clearance is higher, especially can remove the organic pollutant of a large amount of polymer difficult degradations, this lays a good foundation for next step carries out biochemical treatment, yet such processing is only applicable to the lower waste water of loading.European countries are the most advanced on materialization is handled, and eliminated horizontal sedimentation tank substantially, adopt the advanced precipitation technology of plusator, sludge blanket clarifier and highly dense settling pond or the like.
Microbial film ultra-filtration technique, reverse osmosis, electrodialysis, ion exchange treatment means constantly occur in recent years.In paper industry, because processing cost is too high, owing to the paper waste complicated component, the treatment technology difficulty is very big, therefore, does not still have industrialized ripe treatment technology to use so far on the other hand on the one hand.
For example, CN101186418A has disclosed a kind of recoverying and utilizing method of paper-making industrial waste water, and this method is with membrane technique and the combination of Treatment of Industrial Water technology, and concrete grammar comprises: micro-filtration process section, ultrafiltration technology section and reverse osmosis membrane process section.Owing to needed at first to carry out biochemical treatment before the micro-filtration process section, the ultrafiltration technology section need adopt ultra-filtration membrane, and the reverse osmosis process section need adopt reverse osmosis membrane.Therefore, cost of water treatment is too high, and in addition, the requirement to water in the implementation process of this method is quite strict, therefore, for the paper waste complicated component is changeable, is difficult to industrialization.
CN1255340C has disclosed the decoloring method of water in a kind of papermaking, adopts oxygen, dioxide peroxide, and flocculation agent handles the middle water through biochemical treatment respectively, with obtain can reuse purify waste water.Yet this method need be used dioxide peroxide, itself is exactly a kind of chemical agent of forbidding gradually at present.This method needs long sedimentation, long processing period in addition.
CN101050044A has disclosed and a kind of papermaking wastewater has been carried out the method for advanced treatment, comprises chemical coagulation, gravitational settling, and composite filtering material filters, and the biological adsorption agent absorption degradation purifies or the oxygenant oxidation, etc. step.Wherein chemical coagulation has adopted traditional flocculation agent such as aluminium salt and/or molysite, and polyacrylamide (PAM).Owing to do not carry out desalting treatment, therefore, increased the composite filtering material filtration in this method, and purification of biological adsorption agent absorption degradation or oxygenant oxidation, not only increased processing cost, but also made complex disposal processization, operability variation in implementation process, treatment effect is undesirable.
CN1203231C has disclosed a kind of method of papermaking straw pulp sewage disposal, comprises that interpolation flocculation agent (compound aluminum chloride) and coagulant aids (polyacrylamide) carry out flocculation sediment and handle, and carries out air supporting then and handles, and clear water directly discharges or reuse.Because soluble salt content is very high in the waste water, adopts simple flocculation sediment not remove, therefore, certainly, the middle water of handling through this method does not reach the direct discharging of present national regulation or the standard of reuse.
CN100357191C has disclosed the decoloring method of water in a kind of papermaking, comprises adding white clay and flocculation agent among the Xiang Zhongshui, adsorbs to reach by slag then and reduces the COD and the purpose of decolouring.This method is not still handled water-soluble salts a large amount of in the waste water, therefore, is difficult to reach the emission standards of present national regulation.
CN1057512C has disclosed a kind of improvement method of paper waste, comprises being acidified with acid to isolate xylogen; Utilize coal grain and iron dust filtration organism and solid particulate; Add milk of lime and carry out flocculation sediment; Adding flocculation agent again carries out flocculation sediment with milk of lime and separates.Because black liquor and middle water are mixed, therefore, this method needs a large amount of acid to carry out the acidifying separating lignin, has lost a large amount of bronsted lowry acids and bases bronsted lowries artificially.In addition, used a large amount of coal grain and iron filings, and milk of lime, will produce a large amount of secondary pollutions.Moreover, owing to water-soluble salt is not wherein handled, make final process result undesirable, be difficult to reach national specified discharge standard.
In the above-mentioned prior art, quite a few adopts simple flocculation sediment to handle, isolate throw out then, clear water directly discharges or reuse, still can use for the lower waste water of load, higher for load, for example, by the middle-stage wastewater that pulping process of straw pulp produces, above-mentioned treatment process is difficult to reach national specified discharge standard.Also have some treatment processs to adopt flocculation sediments, (biology) adsorption filtration, or the like step, will produce a large amount of secondary pollutions in the treating processes, in addition, treating processes is too complicated, therefore, cost will improve greatly.The prior art that has has adopted ultrafiltration membrane technique and reverse osmosis membrane to combine with the method for wastewater treatment of routine, in theory should thoroughly decontamination problem.But owing to the cost reason, and technical reason, be that the papermaking midcourse wastewater complicated component is changeable, not only brought the high problem of cost for ultrafiltration membrane technique and reverse osmosis membrane technology on Processing Paper Wastewater, technical meeting runs into beyond thought trouble when handling but also make.Therefore, solve the cost height that exists in the prior art, processing means complexity causes serious secondary pollution problem again, is the cardinal task that current paper waste is handled, and can paper waste be handled and be finished smoothly, determined the survival and development of papermaking enterprise.
Summary of the invention
At the problems referred to above of prior art, the inventor has finished the present invention through concentrating on studies.Promptly the present invention proposes and a kind ofly can reduce processing cost effectively, simplify technological process greatly, and can handle various paper wastes, the particularly treatment process of high loading middle-stage wastewater.
Specifically, the invention provides a kind of technological process for the treatment of papermaking method, comprising: filter, flocculation sediment, biochemical treatment and advanced treatment step is characterized in that, QA is adopted in biochemical treatment
2The O treatment process.
Wherein, described QA
2The O treatment process comprises complex reaction aeration, the multistage AO aeration of time-delay and pulse water distribution upwelling anaerobic reaction.
In addition, treatment process of the present invention also comprises handling the advanced treatment step of waste water.
In addition, the described micro-filtration that is filtered into, the order number of filter screen is from the 80-120 order.
Also comprise in addition QA
2The mud that O produces carries out sludge dewatering treatment.
QA
2O mainly comprises three sections of A1, A2, O, but it is bigger with traditional A2O process distinction, because of its A1, A2, three sections independent settings of O, and every section is respectively A1 (complex reaction aeration tank), A2 (pulse water distribution upwelling anaerobic reactor), O (the multistage AO aeration tank of delaying time), this technology has the removal ability of pollutents such as extremely strong SS, COD, BOD, the circulation of traditional A2O mud all runs through whole technology, and the Aerobic Pond mixed solution circulates in a large number in A2 section and O section, and main purpose is to realize denitrogenation dephosphorizing.
1, technical process contrast
QA2O technology: see Fig. 2 for details
Tradition A2O technology: see Fig. 3 for details
QA2O technology and traditional A2O process distinction are bigger as can be seen by above-mentioned two artworks, mud is circulation in three sections of A1, A2, O in traditional A2O technology, settling tank is not established in the centre, and the mixed solution circulation is arranged in that A2, O two are intersegmental, and A1 is that anaerobism A2 is that the oxygen O that holds concurrently is aerobic in these three sections.The A1 section is based on the oxygen bacterium of holding concurrently in QA2O technology, simultaneously met physical reaction again, and this section is provided with settling tank separately, the independently mud recycle system is arranged, the A2 section is based on obligatory anaerobic bacteria, be anaerobic technique completely, the independently mixed solution recycle system is arranged, do not rely on A1 and O section mud and reflux, the O section is then based on aerobic bacteria, alternately oxygen supply by aerator realizes that the series connection of a plurality of oxygen enrichment anoxic sections is multistage AO, and the biological pond of selecting is set before the O section, to reach the purpose of optimizing bacterial classification.
This technology mainly contains five effects greatly: remove SS, denitrogenation, dephosphorization, raising biodegradability, degraded COD and BOD.
(1) in the A1 section to remove SS, the nitration denitrification reaction takes place simultaneously, realize denitrification dephosphorization function (seeing complex reaction aeration tank part for details)
(2) in the A2 section mainly based on anaerobic digestion, simultaneously play the effect that certain larger molecular organics chain rupture is decomposed into small organic molecule again, improved the clearance of follow-up O section, and realized the release of phosphorus.(seeing acoustic streaming anaerobic reactor part on the pulse water distribution for details).
(3) then bring into play the advantage of aerobic bacteria fully in the O section, and realize that simultaneously multistage AO alternately, makes microorganism have more activity, to reach higher removal efficient.Under the time-delay underload, move for a long time in addition and generated a large amount of aerobic particle muds.
The complex reaction aeration tank
The complex reaction aeration tank is the A1 section in this technology.
The selection of waste water treatment process is directly connected to effect, running cost and the total investment of engineering of wastewater treatment, so the suitable waste water treatment process of careful selection is the key of this engineering.The selection of waste water treatment process should be taken all factors into consideration according to multiple factors such as design Inlet and outlet water water quality, degree of treatment requirement, floor space, project scales, and various technologies all have its applicable elements, should fit actual conditions and decides.
China's pulp and paper industry output has occupied the third place in the world, and paper technology upgrades day by day.The paper-making industrial waste water quantity discharged is big, and is seriously polluted, and ecological damage is big, is puzzlement countries in the world paper industry and the hot issue of environmental protection organization and the emphasis of research for many years always.My company furthers investigate paper waste from putting into practice the engineering point of view of application, has developed the feasible suitable process program of a cover.
The waste water of papermaking enterprise discharging mainly contains middle-stage wastewater and paper machine white water.Plain boiled water can be handled all or part of slurrying workshop section that is back in back; Middle section water is mainly from the waste water that produces in pulping, screening, the floatation process, its main component is tiny suspension fiber, papermaking filler, waste paper impurity and a small amount of pectin, wax, carbohydrate, and all kinds of organic and mineral compound that adds in the paper process.The characteristics of waste water are that SS and COD are all higher; And non-solubility COD is higher, accounts for more than 60%; When SS is removed, but non-dissolubility COD simultaneously also major part be lowered.The ratio of B/C in the paper waste is generally not high, but most BOD and solubility COD also want the applying biological method to remove, and is more difficult.
And determine to adopt combined chemistry reaction aeration tank-precipitator method (QA at last through test in place repeatedly
2The A of O technology
1Section) as pre-treating technology, can obtain good ss, cod treatment effect.
One, this technology is the novel technique that biological absorption-degrading activity mud method combines with the materialization flocculation reaction, be in the conventional activated sludge method, (the AB method is the absorption biological degradation method for two sections activated sludge processes, materialization flocculence, AB methods, form by A section B section two portions, the A section is based on bacterium absorption propagation, belong to the high loading biochemical processing process, the B section can be traditional aerobic biological treatment process) the basis on the sewage treatment process that grows up.This technology belongs to the high loading activated sludge process, and sewage is introduced into the A1 section of high loading, and then enters the A2 section of low anaerobism load, is entering the series operation of ultra-low load O section.A1 section mud has very strong adsorptive power and good sedimentation function.The A1 section is flocculation adsorption based on bacterium to organic removal, with materialization flocculation adsorption as strengthening and replenishing.A1 segment process sludge loading height, mud age and hydraulic detention time are short, so the investment of A segment process and working cost are low, the enhanced primary that belongs to the high loading Sludge System is handled.This technology has following characteristics in paper waste is handled:
(1) capacity of resisting impact load is strong, and water quality, the water yield of intaking had huge self-regulated ability, can not make the treatment system paralysis because of the rapid variation of water quality and quantity, stop transport, and loses processing power; When coming water water-quality COD, SS by normal variation water quality to 2 times, water outlet still can keep higher clearance even higher clearance, if in time adjust operating parameter even can keep effluent quality constant, or slightly raises.Strong like this anti impulsion load is for the steady running of whole integrated technique provides assurance.
(2) mud has very strong adsorptive power and good sedimentation function, and process sludge load height reaches as high as 7kg/kgmlss.d, mud age and the water conservancy residence time short (30min-60min), and investment and working cost are low, clearance height (40%--65%).
(3) used technology has bigger biochemical reaction impellent, has stronger adsorption-flocculation and decomposing oxidation to improve the biodegradability ability to the pollution substance of difficult for biological degradation in the paper waste; Because this pond is based on oxygen bacterium and the aerobic bacteria of holding concurrently, the oxygen effect of especially holding concurrently makes waste water B: C behind this pond can improve 2%-5%.
(4) transfer efficiency of oxygen is higher, saves aeration energy consumption; Move owing to adopt under the low dissolved axygen condition, this has just improved gas-liquid mass transfer efficient greatly, uses coefficient of oxygen utilization to improve greatly, can use dissolved oxygen efficiency to reach more than 40%, and dynamic efficiency reaches more than 4.
(5) technical process is simple, and structures are few, simple and convenient operation and maintenance;
(6) treatment effect is stable;
(7) biochemistry is combined with materialization, obtain higher removal efficient and more stable effect of settling.
Commercially available aerator commonly used can be adopted in the complex reaction aeration tank, is conspicuous to those skilled in the art for the selection of equipment, need not to make creative work.
A large amount of microorganism (bacterium) is generally all surviving in the waste water, these bacterial growth reproduction speeds are very fast, can realize a generation cycle in general 20 minutes, that is to say one day and can breed for 72 generations, and the general vitality of these bacteriums is more intense, and is not high to environmental requirement.Can utilize the excess sludge of aerobic activated sludge to improve concentration and the population density of microorganism such as bacterium and primary metazoan in the aeration tank in addition, to reach high efficiency operation.
Three, processing parameter
After waste water entered into the complex reaction aeration tank, this pond main control parameters was as follows:
Flow Q=MAX120000M
3/ d
Temperature T=20---35 ℃
Hydraulic detention time HTR=30min---60min
Sludge concentration MLSS=3000---10000mg/L
Dissolved oxygen DO=0.1---1.0
Ph＝6——8
30 fens SV of settling ratio
30=30---90
Sludge index SVI=150---350
Sludge age SRT=20---40min
Reflux ratio R=40%---200%
Through behind the aeration, enter the settling tank precipitate and separate, for example adding in right amount between aeration tank and settling tank according to separating effect, PAM regulates.Before entering the complex reaction aeration tank, for example can add PAC commonly used.In the operational process of settling tank, must control sludge interface, surface load and reflux ratio.Belong to the scope of conventional design for these parameter control, those of ordinary skills can carry out suitable adjusting according to the particular case of waste water.Usually, sludge interface is suitable to be controlled at more than 3 meters, and surface load should be lower than 1.2m
3/ m
2.h, reflux ratio is controlled according to sludge interface and excess sludge output.Can improve the service efficiency of settling tank like this, improve sludge loading and also increased removal efficient simultaneously.
This technology is compound physical-chemical reaction and biochemical reaction makes the flco density, adsorptive power etc. of physical reaction obtain great enhancing, and the settleability that has promoted biochemical action is arranged simultaneously, makes it be easier to mud-water separation, is that water outlet is more clear.
Pulse water distribution upwelling anaerobic reactor
This reactor is the A2 section in the QA2O technology, and mainly based on anaerobic reaction, sewage hydrolysis reaction, fermentative acidification reaction mainly takes place, produce acetic acidreaction and methanation reaction in this section.
One, this reactor principal feature has:
1, without triphase separator.This is this anaerobic reactor and one of difference of traditional reactor maximum, by bigger diameter/height ratio (5: 1), has reduced the flow velocity of waste water, thereby has reached the purpose of solid-liquid separation.
2, adopt the pulse water distribution system, to store in the water distributor 3～5 minutes A1 section water outlet rushes at the pond with very fast flow velocity in the short period of time (several seconds to tens seconds) at the bottom of by syphonic effect, sludge blanket at the bottom of the pond risen to upper punch be suspended state, thereby make the muddy water uniform mixing in the pond, guaranteed the efficient of anaerobic reaction.
3, be particularly useful for (but being not limited only to) wheat straw chemical pulp middle-stage wastewater.Mierocrystalline cellulose in this waste water, hemicellulose, polysaccharide, reducing sugar, treated starch, part lignin and the derivative thereof etc. of joining in the coating waste-water there is good specific aim, well brought into play acidication these macromole size degradations have been become small molecules, for follow-up aerobic treatment creates conditions.
4, anerobe is granule sludge and floc sludge.The tradition anaerobism is mostly because diameter is too small, and the flow velocity height makes floc sludge run off seriously; and to cultivate the granulating anaerobic sludge, this reactor then can make the coexistence of granule sludge and floc sludge, simultaneously effect; to reach higher removal effect, also improved the removal ability of ss simultaneously.
5, single pond processing power is big, owing to adopt big blade diameter length ratio, makes single pond processing power improve greatly.
This reactor mainly be with the organism in the waste water under the acting in conjunction of a large amount of microorganisms, be converted into methane, carbonic acid gas, water, hydrogen sulfide and ammonia, different anerobes, the oxygen bacterium of holding concurrently interact, condition each other in this process, are very complicated coenosiss.The process of its degradation of organic substances can be divided into four sections:
1, the macromolecular organism of hydrolysis stage is decomposed into small molecules in this stage by the bacterium extracellular enzyme, is chain rupture, and micromolecular hydrolysate is easy to dissolving.For example: the Mierocrystalline cellulose in this stage paper waste is cellobiose, glucose etc. by cellulase hydrolysis; Pectin and degradation product thereof be by the pectin enzymic hydrolysis, and then better degraded by bacterium.
2, souring stage is converted into voltaile fatty acid, alcohols, carbonic acid gas, hydrogen, ammonia, hydrogen sulfide etc. by dissolved organic matter such as disaccharides, the glucose etc. that hydrolysis section generates under the effect of fermenting bacteria.
3, produce the acetate stage under the effect of acetogen, the product of souring stage is converted into acetate, hydrogen, carbonic acid gas and other new cell etc.
4, produce methane phase under the effect of methanogen, acetate, hydrogen, carbonic acid, formic acid, methyl alcohol etc. are converted into methane, carbonic acid gas, new cell etc.Thereby reach the purpose of degradation of organic substances.
Waste water through adjusting the proportioning of C: N: P, for example is adjusted to 200: 5: 1 after handling through the A1 section, flows automatically to the A2 section, enters for example about 300m of volume
3The pulse water distribution jar, the pulse water distribution device water distribution cycle is 8 minutes, be that per 8 minutes pulse water distribution devices are finished water-filling water distribution process one time, waste water is sent into the anaerobic sludge layer uniformly by the water distributor of cloth at the bottom of the pond, under the effect of obligatory anaerobic bacteria, organic hydrolysis takes place, fermentation, produce acetate, DeRs such as methanation, the general stop 16 hours, these reactions are all finished, sewage progressively rises in reactor, for example finish mud-water separation in 2.5-1.0 rice at the distance rising pipe at last, sludge settling continues to fall after rise to sludge blanket, and continues to rise through the gas of sewage behind the anaerobic reaction and anaerobism generation, at the rising pipe place, sewage overflow goes out reactor, and aerogenesis (methane, hydrogen sulfide, carbonic acid gas etc.) gather gas collection district, top, pond, and be collected into the biogas cabinet at this top gas collection tube place, district.
The main technical details of this system is as follows:
1, the water yield: single pond maximum amount of water Q
MAX60000M
3/ d.
2, influent load: COD
CR1000---4000mg/L.
3, water distribution: effect and water distribution that acid is produced in hydrolysis have much relations, this section adopts the high-efficiency pulse water distribution system, it is will to have stored in the water distributor 3～7 minutes A1 section water outlet rushes at the pond with very fast flow velocity in the short period of time (several seconds to tens seconds) at the bottom of by syphonic effect, sludge blanket at the bottom of the pond risen to upper punch be suspended state, thereby make the muddy water uniform mixing in the pond.
4, temperature: this parameter directly affects growth velocity and activity, the physico-chemical property etc. of bacterium, tackles this and carries out strictness control.Have a liking for the warm type microorganism because the microorganism in this system belongs to, the temperature of system is controlled at 20～39 ℃.
5, pH: because hydrolysis bacterium and acid-producing bacteria have in a big way adaptability to pH, methanogen then requires relatively harsher to pH, and the pH of system of therefore controlling well influence system for anaerobic treatment to move one of fine or not important factor.By test of many times, this value is controlled at 6.5---between 7.5.
6, sludge concentration: require to have very high sludge concentration in the normal postrun hydrolysis acidification pool, general controlledly be made as 6000---25000mg/L, the best is 18000mg/L
7, hydraulic detention time: 16h
8, the sludge retention time in the reactor: 15---60d, preferred 45d.
9, sludge volume index: 50---150, preferred 70
10, system sludge internal recycle amount: determine according to the water yield and water distribution situation, can be controlled in 0---between 40%.
11, O section return sludge ratio: need a large amount of O section mud to tame during debugging, need add certain anaerobic species simultaneously.Can add on a small quantity during normal the operation,, increase sludge concentration, improve the anerobe rate of growth to improve clearance.
12, nutritive substance:, therefore must maintain good bacterial growth state because the anaerobic treatment process of waste water is finished by bacterium fully.Except the carbon source of necessity, nitrogenous source, also need to replenish necessary nutritive element in the paper waste.The characteristics of actual waste water are arranged and determine it to add ratio, the COD in operational process of assurance system: N: P is 150～500: 5: 1.Preferred 200: 5: 1.Those of ordinary skills can suitably adjust above-mentioned parameter according to the particular case of waste water, and these adjustment are conspicuous to those skilled in the art, need not to make creative work.
The multistage AO aeration tank explanation of delaying time
The multistage AO aeration tank of delaying time is an O section in the QA2O technology, and waste water mainly is based on aerobic in this section, realizes the series connection of a plurality of oxygen enrichment anoxic sections the nitrification and denitrification reaction taking place by the alternately oxygen supply of aerator.
One, principal feature:
1, more reasonable to the utilization of oxygen
Multistage A/O process using is interrupted aeration, and active sludge is in " aerobic-anoxic " alternative environment.That active sludge is in is this " hungry full " alternative state can be brought into play self potential, accelerates the degradation speed to pollutent under good oxygen condition, improves processing efficiency, especially improves the utilization ratio to oxygen.
2, more effective to the removal of NH4-N
Repeatedly nitrated-anti-nitration reaction stack, to the removal effect of NH4-N be better than tradition single nitrated-anti-nitration reaction.Nitrated with tradition-the denitrification technology (clearance of NH4-N is generally 60%～70%) compares, and multistage A/O technology has shortened nitrated-anti-nitration reaction time, has increased progression; The experiment proved that: after the controlling reaction time, each cycle can obtain 20%～30% NH4-N clearance, can obtain clearance greater than 85% through for example 8 cycles.
3, effectively avoided the generation of sludge bulking phenomenon
The most direct sludge index SVI that shows as of sludge bulking raises.Cause the reason of sludge bulking a lot (as the variation of water temperature and quality etc.), with regard to the high sludge loading in aeration tank itself, high sludge concentration, single operation scheme all when water quality worsens suddenly sludge bulking takes place easily.Because multistage A/O process using is interrupted aeration, mixed solution is through the alternating action of aerobic zone and oxygen-starved area repeatedly, and the low sludge loading of whole process using, can effectively avoid the generation of sludge bulking phenomenon.
4, surplus sludge volume is few
This process sludge quantity of reflux is big, sludge concentration height (sludge concentration of design aeration tank is 3000-4000mg/L), and biomass is big.The residence time of mud in the aeration tank is long, and pollutants in waste water can fully be degraded.
Waste water from the A2 section in the QA2O technology at first enters biological selector, by preaeration, carries out the domestication of dominant bacteria.Enter the aeration zone then, under the aeration zone is in aerobic condition, aerobic cenobium (nitrobacteria, nitrite bacteria etc.) is preponderated, make itrogenous organic substance be decomposed by bacteria to ammonia, under the effect of nitrite bacteria, further be converted into nitrite then, be converted into nitrate through the nitrobacteria effect again; Nitrate enters into the district that stops the supple of gas or steam, facultative cenobium is preponderated gradually, under the effect of facultative different oxygen bacterium, utilize or part utilizes that original organism carbon source is electron donor in the waste water, substitute molecular oxygen with nitrate and make electron acceptor(EA), decompose organic matter, simultaneously, nitrogen in the nitrate is reduced to gaseous nitrogen (N, NO2 etc.); When entering into the aeration zone again, aerobic cenobium is preponderated again and ability strengthens; In like manner enter into when stopping the supple of gas or steam the district, facultative cenobium is preponderated again and ability strengthens; The carrying out of going round and beginning again, nutritive substance reduce and the cenobium quality and quantity is all increasing, and reach " balance between supply and demand " state very soon; Be " supply-less-than-demand " state afterwards, nutritive substance is by thoroughly clean decomposition, and the material of some difficult degradations is also decomposed by the mud cenobium of excellent performance at this moment.
Sewage is through biological selector, carry out the optimization of bacterial classification after, enter the multistage AO of time-delay aeration tank, under the effect of nitrifier, nitrococcus, facultative heterotrophic bacteria, the nitrification and denitrification reaction is taking place, thereby degradation of organic substances.The main technical details of this system has:
1, mud organic loading: the mud organic loading in the native system is about 0.05-0.1kgBOD5/kg (MLSS), preferred 0.05, this has also demonstrated fully characteristics---the underload activated sludge process of multistage A/O, it has made full use of microorganism and the metabolic whole process of microorganism that mud provides, and pollutants in waste water is fully degraded.
2, mixed solution sludge concentration: in real work, adopt this index to measure the quantity of active sludge microorganism indirectly, the operation of Controlling System.Usually be controlled between the 3000-4000mg/L preferred 3500mg/L.
3, hydraulic detention time: native system belongs to extended aeration, and general hydraulic detention time is between 50-65 hour, and is best between the 52-57.So the Chang residence time makes pollutent obtain the more purifying treatment of the degree of depth for good treatment effect provides the prerequisite assurance.Make the excess sludge very stable difficult corruption that becomes because nitration reaction has taken place, excess sludge has obvious minimizing simultaneously.
4, sludge index (SVI): this parameter has reflected the loosening degree of mud, is to judge that sludge settling concentrates a parameter commonly used of performance, can judge whether to take place sludge bulking by this parameter in daily administration, and the control sludge volume.According to service experience, this parameter generally is controlled between the 150-200, and sludge settling property is bad when too high, the sludge dewatering weak effect, though it is good to cross low settling property, but absorption property is poor.
5, reflux ratio: this system sludge quantity of reflux is big, adopts 100% to reflux.Surplus sludge volume is little, because action of microorganisms makes that mud can be not smelly, the processing of mud is also than being easier to simultaneously.
6, dissolved oxygen: the demand difference of the DO of different bacterial classifications, at this system of multistage A/O, we control DO between 0.2-2.0, preferred 0.5-1.0, thus realize the decarburization denitrogenation better.
7, sludge age: the sludge age of system is long more, and the nitrogen and phosphorus content in the mud is just low more, organic matter removal thorough more.Generally be controlled at 18-22 days the bests 15-25 days.
8, nutritive element: carbon, nitrogen, phosphorus are the important elements that constitutes the sludge microbe body, and they provide the energy for the existence of bacterium, and native system is regulated three's ratio at any time according to the variation of water quality, and generally with COD: N: P was controlled at 100: 5: 1.
Can be through the waste water after this system handles by reducing in the 100mg/L about former water COD5000mg/L.
In filtration step of the present invention, can adopt filtering technique conventional in the prior art, so that remove silt particle, fiber, part xylogen, pigment or the like, when removing a large amount of solid substances (SS), can also reclaim slurry.
Preferably, adopt rotary Microfilter to filter, select 80-120 purpose steel mesh or nylon wire for use, the slurry that recovery obtains preferably is concentrated into 2% (weight) and returns pulping system, and waste water is after filtering controlled its SS less than 800mg/L.
Waste water after filtering still contains silt, for reducing the reuse cost, improves quality of reused water, guarantees the normal operation of follow-up equipment, preferably waste water is carried out desanding and handles.Can adopt desanding means commonly used in the prior art, this is conspicuous for those of ordinary skills.
Usually adopt settling pit to carry out sand setting and handle, the sediment outflow at intermittence is carried out in the bottom, and supernatant liquor carries out step of flocculation precipitation.
It in the present invention, has no particular limits, can adopt flocculation agent commonly used in the prior art, as long as can reach the purpose of flocculation sediment for the flocculation agent that is adopted.For example, can adopt ferro-aluminum composite salt salt flocculation agent well known in the prior art.
In the present invention,, can also add coagulant aids in order to reach better flocculation sediment effect, same, have no particular limits for the use of coagulant aids, as long as can reaching, it helps the purpose of coagulating.For example can adopt polyacrylamide coagulant aids commonly used or the like.Its consumption is had no particular limits, and those of ordinary skills can carry out appropriate selection as required.
By method of wastewater treatment of the present invention, the reclamation rate of waste water reaches more than 60%.
Description of drawings
Below in conjunction with accompanying drawing technical process of the present invention is described:
Fig. 1 is the synoptic diagram of method of wastewater treatment of the present invention.
Fig. 2 is the synoptic diagram of Q2AO.
Fig. 3 is the synoptic diagram of traditional A2O technology.
Embodiment
Embodiment 1
08 year July 15---22 because pulping process is changed the former water COD5300mg/L of middle section water, the water 2530mg/L that just settles out, A after this system handles
1Water outlet 1550mg/L, A
2Water outlet 900 second pond water outlet 80---105mg/L, SS＜50mg/L.
Embodiment 2
08 year October 3---10 days, the former water COD3500mg/L of middle section water, the water 1800mg/L that after this system handles, just settles out, A
1Water outlet 1150mg/L, A
2Water outlet 705 second pond water outlet 70---55mg/L, SS＜50mg/L.
Embodiment 3
08 year July 10---November 10, the equal COD3800mg/L of the former level of middle section water, the equal 1900mg/L of level that after this system handles, just settles out, A
1Water outlet 1280mg/L, A
2Water outlet 730 second pond water outlet 85mg/L, SS＜50mg/L.
Comparative Examples:
Certain pulping and paper-making factory adopts traditional materialization+aerobic biochemical process to handle, the about COD2500mg/L of former water, and materialization adds flocculation agent PAC800ppm, PAM5ppm, about water outlet COD1850,96 hours water outlet COD350mg/L of aerobic biochemical hydraulic detention time.Processing cost is higher than this technology, and go out water unstable can not be up to standard.
Below with accompanying drawing the present invention has been carried out more detailed explanation in conjunction with the embodiments.For simplicity, only water in the papermaking is carried out among the embodiment.Yet those of ordinary skills should be understood that, so long as the waste water salt content is higher, in the time of should not passing through simply to handle reuse, all can adopt method of the present invention to handle.Therefore, the processing of water during treatment process of the present invention is not limited only to.Under spirit of the present invention, those of ordinary skills can carry out suitable change or change to method of the present invention as required, and these changes and change all fall within the scope of the present invention.Protection scope of the present invention is as the criterion with appending claims.
Claims (5)
1. technological process for the treatment of papermaking method comprises: filters, and flocculation sediment, biochemical treatment and advanced treatment step is characterized in that, QA is adopted in biochemical treatment
2The O treatment process.
2. method according to claim 1, wherein said QA
2The O treatment process comprises complex reaction aeration, the multistage AO aeration of time-delay and pulse water distribution upwelling anaerobic reaction.
3. method according to claim 1 and 2 also comprises in addition to handling the advanced treatment step of waste water.
4. method according to claim 3, the described micro-filtration that is filtered into, the order number of filter screen is from the 80-120 order.
5. method according to claim 4 also comprises QA in addition
2The mud that O produces carries out sludge dewatering treatment.
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| CN2009100012703A CN101781056B (en) | 2009-01-16 | 2009-01-16 | Treatment method of waste papermaking water |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| CN102225827A (en) * | 2011-05-24 | 2011-10-26 | 青岛理工大学 | Treatment method for wastewater from straw pulp papermaking intermediate section |
| CN102515427A (en) * | 2011-12-07 | 2012-06-27 | 浙江省环境保护科学设计研究院 | Printing and dyeing waste water treatment system and process with low yield of sludge |
| CN102515425A (en) * | 2011-12-07 | 2012-06-27 | 浙江省环境保护科学设计研究院 | High efficiency town sewage treatment system and process with low yield of sludge |
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| CN105239438A (en) * | 2015-10-13 | 2016-01-13 | 新疆国力源投资有限公司 | Circulating reuse method for white water in paper machine |
| CN106145569A (en) * | 2014-10-24 | 2016-11-23 | 吴小再 | A kind of method of work of the Multistage settling processing system of paper waste |
| CN107746159A (en) * | 2017-11-27 | 2018-03-02 | 青岛城投娄山河水务有限公司 | A kind of New Type of Sewage Treatment System and technique |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102225827A (en) * | 2011-05-24 | 2011-10-26 | 青岛理工大学 | Treatment method for wastewater from straw pulp papermaking intermediate section |
| CN102225827B (en) * | 2011-05-24 | 2012-09-05 | 青岛理工大学 | Treatment method for wastewater from straw pulp papermaking intermediate section |
| CN102515427A (en) * | 2011-12-07 | 2012-06-27 | 浙江省环境保护科学设计研究院 | Printing and dyeing waste water treatment system and process with low yield of sludge |
| CN102515425A (en) * | 2011-12-07 | 2012-06-27 | 浙江省环境保护科学设计研究院 | High efficiency town sewage treatment system and process with low yield of sludge |
| CN103224309A (en) * | 2013-04-25 | 2013-07-31 | 西华大学 | Leather waste water treatment system and treatment process |
| CN103224309B (en) * | 2013-04-25 | 2014-06-25 | 西华大学 | Leather waste water treatment system and treatment process |
| CN106145569A (en) * | 2014-10-24 | 2016-11-23 | 吴小再 | A kind of method of work of the Multistage settling processing system of paper waste |
| CN106186590A (en) * | 2014-10-24 | 2016-12-07 | 吴小再 | The Multistage settling processing system of paper waste |
| CN106186588A (en) * | 2014-10-24 | 2016-12-07 | 吴小再 | A kind of Multistage settling processing system of paper waste |
| CN106277635A (en) * | 2014-10-24 | 2017-01-04 | 吴小再 | The method of work of the Multistage settling processing system of paper waste |
| CN105239438A (en) * | 2015-10-13 | 2016-01-13 | 新疆国力源投资有限公司 | Circulating reuse method for white water in paper machine |
| CN107746159A (en) * | 2017-11-27 | 2018-03-02 | 青岛城投娄山河水务有限公司 | A kind of New Type of Sewage Treatment System and technique |
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| CN101781056B (en) | 2012-01-04 |
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