CN101898836B - Complex enzyme preparation for sludge removal and in-situ remediation of organisms in eutrophic water areas and application method thereof - Google Patents

Complex enzyme preparation for sludge removal and in-situ remediation of organisms in eutrophic water areas and application method thereof Download PDF

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CN101898836B
CN101898836B CN2010101645922A CN201010164592A CN101898836B CN 101898836 B CN101898836 B CN 101898836B CN 2010101645922 A CN2010101645922 A CN 2010101645922A CN 201010164592 A CN201010164592 A CN 201010164592A CN 101898836 B CN101898836 B CN 101898836B
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water
enzymic preparation
compound enzymic
ecosystem
prozyme
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CN101898836A (en
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麦广鸿
郑丽军
彭韬
马丹
陈雯
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HANGZHOU JINGKANG ENVIRONMENT ENGINEERING Co Ltd
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Abstract

The invention relates to a complex enzyme preparation for sludge removal and in-situ ecological remediation of organisms in eutrophic water areas, which is prepared by mixing complex enzyme and mineral water, wherein the weight ratio of the complex enzyme to the mineral water is 1:9-50. The complex enzyme comprises the following components in volume content: 50-80mg/L of bromelain, 50-80mg/L of papain, 15-30mg/L of L-aspartase and 15-30mg/L of glutathione. The invention improves the water quality of water bodies, decomposes the organic sludge deposited at the water bottom, forms dynamic balance with the continuously input pollution sources, basically solves the problem of eutrophication of water bodies, and simultaneously solves the problem of secondary pollution of sludge removal of river channels and lakes.

Description

Compound enzymic preparation and applying method that the biological desilting original position of eutrophic water is repaired
(1) technical field
The invention belongs to the environmental treatment field, be specifically related to a kind of compound enzymic preparation and applying method that is used for the restoration of the ecosystem of the biological desilting original position of eutrophic water.
(2) background technology
The investigation of more than 200 lake, the whole nation being carried out according to " National urban drinking water safety ensure planning " establishment group in 2009 shows that eutrophication has taken place in eighty per cant lake, and the algae raised growth has had a strong impact on the water quality of tap water.In the time of 1991, in 122 lakes of China, also have only 51% to be the eutrophication state, by 2005, in 133 lakes of China, 88.6% eutrophication is arranged, wherein 61% state control emphasis lake (storehouse) water quality is five classes and bad five classes.In 27 state control emphasis lakes (storehouse), it is elementary five classes and bad five classes that 18 lakes (storehouse) are arranged, and in the lake of 13 bad five class water quality (storehouse), breaks out Taihu Lake, Chaohu, the Dian Chi of blue-green algae and is listed.Thereby being called as " the blue-green algae year " of China in 2007, Taihu Lake, Wuxi, Chaohu, Anhui, Dian Chi, Yunnan, Wuhan East Lake are broken out blue-green algae in succession.The exhausted major part of the water body of urban river is five classes and bad five classes, we can say that " water pollution " had influence on human existence.Yet, still do not have the easy-operating technology of mature and reliable to solve water pollution problems at present.
The waters eutrophication problem, be the speed that the decomposition rate of microorganism does not catch up with the input pollution source of water body in the water body after all, thereby the accumulation that causes a large number of nutrients forms water-bed organic sludge, thereby remove water-bed organic sludge, and make the decomposition of microorganism and the lasting input of source of pollution reach dynamic balance, could fundamentally solve the body eutrophication problem.The present common artificial desilting way of taking, not only to the effect that improves unable to get up essence of water quality, and the disposal of a large amount of mud is serious problems, can bring secondary pollution.
Chinese patent CN1646982A discloses a kind of water quality cleansing agent that utilizes catalyzed reaction, with be supplied in the postactivated microorganism of polluted water, and objectionable impurities such as microbiological degradation mud and organic compound, sulfide and the natural enzyme that purifies water thus, combine with the mixture of microorganism activatory catalysis in can promoting this polluted water.By activating microorganism, when water quality being purified, easily supply with river, lakes and marhshes or water processing establishment with the objectionable impuritiess such as organic compound in this microbiological degradation mud and the water with natural enzyme.By in polluted water, dripping water quality cleansing agent, microorganism in the activation polluted water, utilize this action of microorganisms to purify the water quality of this polluted water, wherein, water quality cleansing agent for will be supplied in the polluted water activation microorganism, and objectionable impurities such as microbiological degradation mud and organic compound, sulfide and the natural enzyme that purifies water thus, the water quality cleansing agent that combines with the mixture of microorganism activatory catalysis in can promoting this polluted water.
Chinese patent CN1974436 discloses a kind of method that adopts the biological promotor of prozyme polluted-water to be carried out the biology in situ reparation, add dosage and dosing method according to what the quantity discharged of sewage reservoir capacity and the total amount of pollutant and external source sanitary sewage and trade effluent was determined the biological promotor of prozyme, its workflow comprises: investigate polluted-water, analyze sewage reservoir capacity and the total amount of pollutant, formulation rehabilitation plan, set up service platform, the remediation intensification phase, repair consolidation and rebuild maintenance phase.Advantage of the present invention is: administer sewage by the self-purification capacity of recovering water body, recover natural ecological environment; Because the biological promotor of prozyme does not contain microorganism, and is nontoxic to water body, thereby ecological risk is low; Need not the artificial aeration in the reparation, need not to allocate renovation agent again, execute-in-place is simple, need not the instrument of complex and expensive; Comprehensive regulation expense is low, is suitable for the environmental improvement in city unhurried current type, the black smelly river course of dead front type or eutrophication river course and the contaminated waters of big area.
(3) summary of the invention
Technical problem to be solved by this invention organic sludge at the bottom of the water of decomposition is provided to provide under a kind of situation that does not change existing waters overall situation, improves the self purification of water body function, repairs aquatic ecosystem, compound enzymic preparation and the applying method thereof of radical cure blue-green algae.
A kind of compound enzymic preparation that is used for the restoration of the ecosystem of the biological desilting original position of eutrophic water, described compound enzymic preparation mixes composite forming by prozyme and mineral water, and the weight ratio of prozyme and mineral water is 1: 9~50; The component that contains following volume content in the described prozyme: Traumanase 50~80mg/L; Papain 50~80mg/L; L-L-Aspartase 15~30mg/L; Sweet 15~the 30mg/L of paddy Guang; The trace element that contains following volume content in the described mineral water: silicon 0.1~0.3ug/L; Sodium 50~100mg/L; Calcium 60~120mg/L; Magnesium 150~250mg/L; Potassium 50~100mg/L; Iodine 5~12ug/L; Selenium 0.1~0.8ug/L; Iron 0.1~0.8ug/L.
Preferably, the component that contains following volume content in the described prozyme: Traumanase 65mg/L; Papain 70mg/L; L-L-Aspartase 25mg/L; Gsh 23mg/L.
Preferably, the trace element that contains following volume content in the described mineral water: silicon 0.20ug/L; Sodium 74mg/L; Calcium 71mg/L; Magnesium 200mg/L; Potassium 69mg/L; Iodine 9ug/L; Selenium 0.5ug/L; Iron 0.4ug/L.
Preferably, the component that also contains following volume content in the described prozyme: L-glutamic acid 30~50mg/L; Aspartic acid 5~20mg/L; Synanthrin 15~30mg/L; Pyruvic acid 10~30mg/L.
Preferably, the component that also contains following volume content in the described prozyme: N,O-Diacetylmuramidase 5~20mg/L; ATP enzyme 10~30ml/L; Cellulase 10~20mg/L.
Preferably, the component that contains following volume content in the described prozyme: Traumanase 65mg/L; Papain 70mg/L; L-L-Aspartase 25mg/L; Gsh 23mg/L; L-glutamic acid 35mg/L; Aspartic acid 15mg/L; Synanthrin 23mg/L; Pyruvic acid 25mg/L; N,O-Diacetylmuramidase 15mg/L; ATP enzyme 21ml/L; Cellulase 14mg/L.
A kind of described constructional method that is used for the compound enzymic preparation of the biological desilting original position of eutrophic water restoration of the ecosystem, comprise the steps: compound enzymic preparation and water are diluted by 1: 400~1: 6000 weight ratio, and drip or add in the ratio of eutrophic water volumetric quantity 6~10ppm.
Preferably, the constructional method of the compound enzymic preparation of the biological desilting original position of described eutrophic water restoration of the ecosystem, comprise the steps: compound enzymic preparation and water are diluted by 1: 3000 weight ratio, and drip or add in the ratio of eutrophic water volumetric quantity 8ppm.
The present invention is organic sludge, raising self purification of water body function, reparation aquatic ecosystem, radical cure blue-green algae at the bottom of water of decomposition under the situation that does not change existing waters overall situation.After adding compound enzymic preparation, make microorganism in the water body be the raising of how much orders of magnitude to nutraceutical decomposition rate, the content of BOD, COD and ammonia nitrogen, phosphorus in the body in reducing rapidly changes into active sludge with organic sludge and progressively decomposes, improves water quality and finally reach the organism that difficulty is decomposed and decompose within a short period of time.The present invention has not only improved the water quality of water body, and decomposed the organic sludge of subaqueous deposit, and form running balance with the source of pollution that continue input, and fundamentally solve the body eutrophication problem, also solved the secondary pollution problem of river course and lake dredging up simultaneously.
The decomposition object such as the following table of each component among the present invention:
Figure GSB00000605684400031
Compound enzymic preparation of the present invention only need splash in the water body by certain dosage according to water quality, source of pollution, settled sludge amount and get final product.For current water, according to flow velocity in the upstream and mounting points drip apparatus along the line; For impounded body, according to water surface area mounting points drip apparatus and join mechanism and promote water body to flow or manually evenly be sprayed into water body.
The biological dredging method of eutrophic water prozyme is divided into two stages usually:
1 biological desilting stage: the water-bed organic sludge thickness of eutrophic water can reach 0.5~2 meter usually, forms by depositing year in year out, thoroughly decompose usually and also can need six months to 24 months.After the prozyme diluent is added drop-wise in the eutrophication water, can will originally be present in the water body microbic activity be how much order of magnitude ground and increase because the Decomposition of microorganism can make water-bed mud organically combine the generation qualitative change, form the loosening of bed mud, water quality can temporarily become muddy variation.After one month (need two months winter), water-bed organic sludge more can become loose, and produce a large amount of carbonic acid gas and methane gas, the thread mud of loose one-tenth also can be easy to naked-eye observation along with the phenomenon of the agglomerating come-up of bubble, thread mud is blended in the water and progressively decomposes, and part becomes the food of metazoan and fish.Along with the continuous enhancing of microorganism active and the decomposition of water-bed organic sludge, the part organic sludge can transfer active sludge to, whole waters can become a natural sewage work, at this moment, the self-purification function of water body is strengthened greatly, the transparency of water body can be improved, and water quality can be greatly improved.
2 original position restoration of the ecosystem stages: water-bed organic sludge major part obtains decomposing, and formation active sludge, the sedimentary source of pollution of water body reduce in a large number, prescription, extension rate, the dripping quantity that then need to adjust prozyme according to the source of pollution that the external world continues to import this moment are come the controlling microbial capacity of decomposition, and make the two form running balance, repair ecological purpose thereby reach, and water quality is safeguarded and kept long-term good order and condition.
3 quality recovery processes
3.1 quality recovery phase I
Along with the amount of compound enzymic preparation with 6~10ppm (preferred 8ppm) splashed in the contaminated sewage continuously, its distinctive anti-oxidant, anti-microbial effect can improve useful microbic activity (katalysis) and reduce the activity (negative catalysis) of spoilage organism, assorted bacterium.Organism decomposer, nitrifier, sulfation bacterium, the denitrifier isoreactivity of aerobic zone are improved, promote organic decomposition fully, ammonia is to the transformation of nitrate ion, and hydrogen sulfide is to the transformation of sulfate ion.Thereby the turbidity of aerobic zone is reduced.In addition, " prozyme " can also make the organism decomposer of anaerobic zone, the activity of photosynthetic bacterium (green sulfur bacteria, red thiobacterium, red non-thiobacterium) improve, make the green sulfur bacteria of aerobic area, red thiobacterium begin to carry out light compositing, consume hydrogen sulfide; Make red non-thiobacterium also begin to carry out light compositing, decomposing organic matter.Promote the decomposition of settled sludge, the mud after being decomposed begins the floating water surface of going up.The required DO of useful microorganism that increases at aerobic zone, DO by repressed spoilage organism, assorted consumption that bacterium subtracts is replenished, but owing to along with the rolling up of aerobic useful microorganism, DO is consumed in large quantities, aerobic zone can temporarily shoal, and turbidity also increases thereupon.
This shows, owing to promoted the organic decomposition of aerobic zone and anaerobic zone, ammonia, hydrogen sulfide in the anaerobic zone generation, decomposed by nitrifier, sulfur oxidizing bacterium and double oxygen photosynthetic bacterium, be released to (stench alleviates) in the atmosphere after concentration reduces significantly, the methane that aerobic area produces directly is released in the atmosphere.Can also see the atomic little bubble that produces because of denitrogenation at the water surface.
Can't carry out in the photosynthetic facility, photosynthetic bacterium is substituted by sulfur oxidizing bacterium and utilizes organism to consume hydrogen sulfide.
3.2 quality recovery phase II
Still the dosage according to 6~10ppm (preferred 8ppm) adds compound enzymic preparation continuously, the useful microbic activity of living at aerobic zone and anaerobic zone further improves, and the active of spoilage organism, assorted bacterium further reduces, and impels organism to decompose fully, aerobic zone further enlarges, and turbidity reduces.Meanwhile, the photosynthetic bacterium of aerobic area comes to life, and the consumption of hydrogen sulfide increases, and promotes organic decomposition.At this moment, the ammonia that discharges in the atmosphere, the concentration of hydrogen sulfide reduce significantly, and foul smell disappears.The generation of methane still continues, and the small bubbles that produce because of deamination increase, and sedimentary mud further decomposes, and the floating water surface of going up of mud is arranged.The second half in this stage begins to occur blue-green algae at aerobic zone, produces oxygen under photosynthesis, and DO increases substantially.
3.3 quality recovery phase III
In order to have kept oxygen condition, also need in water, splash into compound enzymic preparation by the amount of 6~10ppm (preferred 8ppm).In this stage, useful microbic activity further improves, spoilage organism, assorted bacterium keep and are subjected to holddown, further promote cyanophycear growth, under photosynthesis, DO further improves, organism is decomposed by complete oxidation, turbidity reduces significantly, and settled sludge reduces significantly, and settled sludge is in the state of double oxygen, aerobic coexistence.The ammonia and the hydrogen sulfide that produce under the oxygen condition of holding concurrently through in the nitrifier of aerobic zone, the decomposition of sulfur oxidizing bacterium, are converted into nitrate ion and sulfate ion, and stink disappears.Along with the minimizing of settled sludge, the methane bubble also reduces thereupon, and final settled sludge is decomposed fully, and methane, ammonia, hydrogen sulfide also disappear thereupon, and the natural, ecological in waters is recovered, and aquatic organism is survived.
After polluted waters is purified fully, as continue to have sewage to enter continuously,, need to continue in water, to instil continuously compound enzymic preparation by the amount of 3ppm in order to have kept oxygen condition.
After purifying fully,, must press the amount continuous drip compound enzymic preparation of 8ppm in some facility, carrying out under the photosynthetic situation.
Beneficial effect of the present invention is: 1, prozyme is not a biological bacteria, does not have the risk ecological out of control of external bacterial classification; 2, fundamentally solve body eutrophication, and form running balance, reach the purpose of restoration of the ecosystem with the source of pollution that continue input; 3, realize the organic sludge biological decomposition, solved the problem of organic sludge harmless treatment effectively; 4, can reduce colibacillary quantity in the improvement waters effectively; 5, operation and simple to operate, the polluted waters that only needs to administer at need increases compound enzymic preparation storage and Dropping feeder, has debugged rate of addition and has got final product, and implements based technique for in-situ remediation; 6, the technology implementation comprehensive cost is low.Traditional relatively artificial desilting, plant ecological pasture and water, the summation cost that repeats to construct of engineering such as accent is low in artificial aeration, the outer water.
(4) embodiment
Below by embodiment the present invention is preferably specified, but protection scope of the present invention is not limited to this.
Embodiment 1
A kind of compound enzymic preparation that is used for the restoration of the ecosystem of the biological desilting original position of eutrophic water, described compound enzymic preparation mixes composite forming by prozyme and mineral water, and the weight ratio of prozyme and mineral water is 1: 9~50; The component that contains following volume content in the described prozyme: Traumanase 65mg/L; Papain 65mg/L; L-L-Aspartase 20mg/L; Gsh 26mg/L; The trace element that contains following volume content in the described mineral water: silicon 0.20ug/L; Sodium 74mg/L; Calcium 71mg/L; Magnesium 200mg/L; Potassium 69mg/L; Iodine 9ug/L; Selenium 0.5ug/L; Iron 0.4ug/L.
Present embodiment is used for garden, Guangzhou man-made lake landscape water and carries out biological desilting, and applying method comprises the steps: compound enzymic preparation and water are diluted by 1: 2000 weight ratio, and drips or add in the ratio of eutrophic water volumetric quantity 8ppm.Before the processing: the serious eutrophication of water body, water body muddiness (transparency is<10 centimetres), water-bed organic sludge is thick reaches 20 centimetres; Frowziness, water quality are bad five classes; Handle back (six months): stink is eliminated, water transparency is brought up to>and 80 centimetres, water-bed organic sludge is decomposed fully, and water quality is four classes.
Embodiment 2
A kind of compound enzymic preparation that is used for the restoration of the ecosystem of the biological desilting original position of eutrophic water, described compound enzymic preparation mixes composite forming by prozyme and mineral water, and the weight ratio of prozyme and mineral water is 1: 20; The component that contains following volume content in the described prozyme: Traumanase 65mg/L; Papain 70mg/L; L-L-Aspartase 25mg/L; Gsh 23mg/L; The trace element that contains following volume content in the described mineral water: silicon 0.15ug/L; Sodium 74mg/L; Calcium 100mg/L; Magnesium 210mg/L; Potassium 100mg/L; Iodine 8ug/L; Selenium 0.6ug/L; Iron 0.6ug/L.
Present embodiment is used for Hangzhou park landscape water and carries out biological desilting, and applying method comprises the steps: compound enzymic preparation and water are diluted by 1: 3000 weight ratio, and drips or add in the ratio of eutrophic water volumetric quantity 9ppm.Before the processing: water transparency is less than 10 centimetres, and summer, blue-green algae broke out, and water-bed organic sludge is thick to reach 30 centimetres; Handle back (four months): blue-green algae disappears, and water-bed organic sludge is decomposed fully, and water transparency reaches 1 meter.
Embodiment 3
A kind of compound enzymic preparation that is used for the restoration of the ecosystem of the biological desilting original position of eutrophic water, described compound enzymic preparation mixes composite forming by prozyme and mineral water, and the weight ratio of prozyme and mineral water is 1: 20; The component that contains following volume content in the described prozyme: Traumanase 65mg/L; Papain 70mg/L; L-L-Aspartase 25mg/L; Gsh 23mg/L; L-glutamic acid 35mg/L; Aspartic acid 15mg/L; Synanthrin 23mg/L; Pyruvic acid 25mg/L; N,O-Diacetylmuramidase 15mg/L; ATP enzyme 21ml/L; Cellulase 14mg/L.The trace element that contains following volume content in the described mineral water: silicon 0.25ug/L; Sodium 74mg/L; Calcium 71mg/L; Magnesium 200mg/L; Potassium 69mg/L; Iodine 9ug/L; Selenium 0.5ug/L; Iron 0.4ug/L.
Present embodiment is used for the aquatic organism desilting of river, Hangzhou, and applying method comprises the steps: compound enzymic preparation and water are diluted by 1: 5000 weight ratio, and drips or add in the ratio of eutrophic water volumetric quantity 8ppm.Before the processing: by severe contamination, it is smelly to turn black, and water-bed organic sludge is the thickest to reach 2 meters; Handle back (five months): water-bed organic sludge major part is decomposed, and inorganic content improves, and the water body foul smell is eliminated, and the downstream water transparency reaches 60 centimetres.

Claims (8)

1. a compound enzymic preparation that is used for the restoration of the ecosystem of the biological desilting original position of eutrophic water is characterized in that described compound enzymic preparation mixes composite forming by prozyme and mineral water, and the weight ratio of prozyme and mineral water is 1: 9~50;
The component that contains following volume content in the described prozyme: Traumanase 50~80mg/L; Papain 50~80mg/L; L-L-Aspartase 15~30mg/L; Gsh 15~30mg/L;
The trace element that contains following volume content in the described mineral water: silicon 0.1~0.30ug/L; Sodium 50~100mg/L; Calcium 60~120mg/L; Magnesium 150~250mg/L; Potassium 50~100mg/L; Iodine 5~12ug/L; Selenium 0.1~0.8ug/L; Iron 0.1~0.8ug/L.
2. the compound enzymic preparation that is used for the restoration of the ecosystem of the biological desilting original position of eutrophic water according to claim 1 is characterized in that containing in the described prozyme component of following volume content: Traumanase 65mg/L; Papain 70mg/L; L-L-Aspartase 25mg/L; Gsh 23mg/L.
3. the compound enzymic preparation that is used for the restoration of the ecosystem of the biological desilting original position of eutrophic water according to claim 1 is characterized in that containing in the described mineral water trace element of following volume content: silicon 0.20ug/L; Sodium 74mg/L; Calcium 71mg/L; Magnesium 200mg/L; Potassium 69mg/L; Iodine 9ug/L; Selenium 0.5ug/L; Iron 0.4ug/L.
4. according to the described compound enzymic preparation that is used for the restoration of the ecosystem of the biological desilting original position of eutrophic water of one of claim 1~3, it is characterized in that also containing in the described prozyme component of following volume content: L-glutamic acid 30~50mg/L; Aspartic acid 5~20mg/L; Synanthrin 15~30mg/L; Pyruvic acid 10~30mg/L.
5. the compound enzymic preparation that is used for the restoration of the ecosystem of the biological desilting original position of eutrophic water according to claim 4 is characterized in that also containing in the described prozyme component of following volume content: N,O-Diacetylmuramidase 5~20mg/L; ATP enzyme 10~30ml/L; Cellulase 10~20mg/L.
6. the compound enzymic preparation that is used for the restoration of the ecosystem of the biological desilting original position of eutrophic water according to claim 5 is characterized in that containing in the described prozyme component of following volume content: Traumanase 65mg/L; Papain 70mg/L; L-L-Aspartase 25mg/L; Gsh 23mg/L; L-glutamic acid 35mg/L; Aspartic acid 15mg/L; Synanthrin 23mg/L; Pyruvic acid 25mg/L; N,O-Diacetylmuramidase 15mg/L; ATP enzyme 21ml/L; Cellulase 14mg/L.
7. the described applying method that is used for the compound enzymic preparation of the biological desilting original position of eutrophic water restoration of the ecosystem of a claim 1, it is characterized in that comprising the steps: compound enzymic preparation and water are diluted by 1: 400~1: 6000 weight ratio, and drip or add in the ratio of eutrophic water volumetric quantity 6~10ppm.
8. according to the described applying method that is used for the compound enzymic preparation of the biological desilting original position of eutrophic water restoration of the ecosystem of claim 7, it is characterized in that comprising the steps: compound enzymic preparation and water are diluted by 1: 3000 weight ratio, and drip or add in the ratio of eutrophic water volumetric quantity 8ppm.
CN2010101645922A 2010-05-05 2010-05-05 Complex enzyme preparation for sludge removal and in-situ remediation of organisms in eutrophic water areas and application method thereof Expired - Fee Related CN101898836B (en)

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