CN108650918A - The method for improveing soil using composite enzyme - Google Patents
The method for improveing soil using composite enzyme Download PDFInfo
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- CN108650918A CN108650918A CN201810397530.2A CN201810397530A CN108650918A CN 108650918 A CN108650918 A CN 108650918A CN 201810397530 A CN201810397530 A CN 201810397530A CN 108650918 A CN108650918 A CN 108650918A
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- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01B—SOIL WORKING IN AGRICULTURE OR FORESTRY; PARTS, DETAILS, OR ACCESSORIES OF AGRICULTURAL MACHINES OR IMPLEMENTS, IN GENERAL
- A01B79/00—Methods for working soil
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- C—CHEMISTRY; METALLURGY
- C09—DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
- C09K—MATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
- C09K17/00—Soil-conditioning materials or soil-stabilising materials
- C09K17/14—Soil-conditioning materials or soil-stabilising materials containing organic compounds only
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Abstract
The invention discloses a kind of methods improveing soil using composite enzyme, it is included in the first fermentation raw material containing malt sugar and carries out the first fermentation using plant enzyme, obtain the first zymotic fluid, then the second fermentation is carried out using first zymotic fluid in the second fermentation raw material containing malt sugar and wheat bran, obtains composite enzyme；Total bacteria count is 3 × 10 in the composite enzyme5~3 × 109CFU/ml, lactic acid bacteria account for 80% of total bacteria count or more, and actinomyces, photosynthetic bacteria, nitrogen-fixing bacteria, bacillus subtilis and saccharomycete account for 10~20%；It is formed and is discharged using composite enzyme treated sewage, water outlet is filtered, composite enzyme nutrient solution is obtained；Composite enzyme nutrient solution is diluted with water, salinization of soil farmland is irrigated.The reclamation result of the present invention is good.
Description
Technical field
The present invention relates to a kind of method of improvement soil more particularly to a kind of methods improveing soil using composite enzyme.
Background technology
With the quickening of urbanization process, the municipal sewage of generation is consequently increased.In addition, country sewage is also constantly increasing
Add.Country is increasingly strict for the standard of environmental requirement, this puts forward higher requirements the technology of sewage disposal.Traditional activity
Sludge includes the following steps：Sewage disinfection treatment, sludge seeding, sludge for agricultural use (appropriateness aeration) are first gradually intake three points
Start together be aerated, and progressively reach design water level, start secondary settling tank, secondary settling tank water inlet starts sedimentation basin, and sludge timing is fixed
Amount reflux.Regurgitant volume and time are adjusted according to state, extra-nutrition object decomposes sewage ability to cultivate micro organism quantity and improve,
Follow-up sewage-treatment plant is started, such as sludge settling pond plus chemicals, sanitizer and sludge treatment equipment.Activated sludge front end
For biological treatment, the mode for taking aerobic-anaerobic to ferment decomposes harmful substance in water, in order to reach settled sludge and disinfection mesh
, centre uses chemicals, such as flocculant, rear end that the modes such as carbon granule filtering is taken to make water qualified discharge.Traditional activity
There are problems for sludge.For example, processing rear end uses chemical agent, disinfection also to kill dirt while removing harmful substance
Beneficial microbe in mud makes the reduction of returned sludge microbial activity, and cannot fully ferment decomposing harmful substances.The water of discharge is without battalion
It supports, it is impossible to be used in agricultural irrigation especially cannot be used for improvement soil.
Therefore, a kind of method of improvement soil is present needed exist for, can directly be gone out using what is obtained after sewage disposal
Water.
Invention content
In view of this, the purpose of the present invention is to provide a kind of method improveing soil using composite enzyme, it can be straight
The water outlet that is obtained using after sewage disposal is connect as nutrient solution.Specifically, the present invention includes the following contents.
The method for improveing soil using composite enzyme of the present invention includes the following steps：
Composite enzyme preparation process：The first fermentation is carried out using plant enzyme in the first fermentation raw material containing malt sugar,
The first zymotic fluid is obtained, then carries out second using first zymotic fluid in the second fermentation raw material containing malt sugar and wheat bran
Fermentation, obtains composite enzyme；Total bacteria count is 3 × 10 in the composite enzyme5~3 × 109CFU/ml, lactic acid bacteria account for total bacteria count
80% or more, actinomyces, photosynthetic bacteria, nitrogen-fixing bacteria, bacillus subtilis and saccharomycete account for 10~20%；With
Sewage treatment step：It is formed and is discharged using the composite enzyme treated sewage, the water outlet is filtered, is obtained compound
Enzyme nutrient solution；
Soil improvement step is selected from one of following steps：
(1) water of the composite enzyme nutrient solution based on 5~500 times of composite enzyme nutrient solution weight is diluted, is irrigated
Salinization of soil farmland；Or
(2) mixture of the composite enzyme nutrient solution and the composite enzyme is used and is based on composite enzyme nutrient solution weight
5~500 times of water dilution, irrigates salinization of soil farmland；Wherein, the weight ratio of composite enzyme and composite enzyme nutrient solution is 1:5~
30。
In the composite enzyme preparation process of the present invention, it is preferable that the first fermentation raw material includes 3~8 parts by weight of leaf, water
3~8 parts by weight of fruit, 0.5~2 parts by weight of pine nut, 0.5~2 parts by weight of soybean residue, 0.5~2 parts by weight of soya-bean cake, vegetable oil residue 0.5
0.5~2 parts by weight of~2 parts by weight, 0.5~2 parts by weight of rice bran and malt sugar；Second fermentation raw material include 2~9 parts by weight of malt sugar,
1~5 parts by weight of rice bran, 0.5~5 parts by weight of 1~5 parts by weight of soya-bean cake, 1~5 parts by weight of soybean residue and wheat bran.In certain embodiment party
In case, the first fermentation raw material includes 6~7.5 parts by weight of leaf, 6~7.5 parts by weight of fruit, 1~1.5 parts by weight of pine nut, bean curd
1~1.5 parts by weight of slag, 1~1.5 parts by weight of soya-bean cake, 1~1.5 parts by weight of vegetable oil residue, 1~1.5 parts by weight of rice bran and malt sugar 1
~1.5 parts by weight.It is further preferred that the first fermentation raw material includes leaf and each 6 parts by weight of fruit, other raw material (pine nut, beans
Rotten slag, soya-bean cake, vegetable oil residue, rice bran, malt sugar) it is respectively 1 parts by weight.In certain embodiments, the second fermentation raw material includes
5~8 parts by weight of malt sugar, 2~3 parts by weight of rice bran, 0.8~2 weight of 2~3 parts by weight of soya-bean cake, 2~3 parts by weight of soybean residue and wheat bran
Part.It is further preferred that malt sugar is 5 parts by weight, rice bran is 2 parts by weight, other each ingredients (soya-bean cake, soybean residue, wheat bran) are respectively
For 1 parts by weight.
In the composite enzyme preparation process of the present invention, it is preferable that when first ferments, the dosage of plant enzyme is 2~6
Parts by weight, preferably 3~5 parts by weight, such as 4 parts by weight.First ferment when, be aerated 20~150 minutes, fermentation time be 30~
50 days.When second ferments, the dosage of the first zymotic fluid is 5~15 parts by weight, preferably 6~10 parts by weight, more preferable 7~8 weight
Measure part.The fermentation time of second fermentation can be 20~50 days, such as 30~40 days.According to embodiment of the present invention,
The time of first fermentation is 30~50 days；The time of second fermentation is 20~50 days.
In the composite enzyme preparation process of the present invention, it is preferable that 10~15 days fermentation temperatures before the first fermentation
It it is 30~40 DEG C, subsequent fermentation temperature is 20~30 DEG C；Need stirring 10~50 daily within 20~25 days before the first fermentation
Minute.According to embodiment of the present invention, 10~15 days fermentation temperatures are 35~38 DEG C before the first fermentation, then
Fermentation temperature be 20~28 DEG C, first 20~25 days need daily stirring 20~30 minutes.Using above-mentioned steps, be conducive to ferment
Process generates more beneficial bacteriums.
In the composite enzyme preparation process of the present invention, it is preferable that 10~15 days fermentation temperatures before the second fermentation
It it is 35~40 DEG C, subsequent fermentation temperature is 10~40 DEG C；Need stirring 10~50 daily within 15~20 days before the second fermentation
Minute.According to embodiment of the present invention, 10~15 days fermentation temperatures are 35~38 DEG C before the second fermentation, then
Fermentation temperature be 15~30 DEG C；Need within first 15~20 days stirring 20~30 minutes daily.Using above-mentioned steps, be conducive to ferment
Process generates more beneficial bacteriums.
The present invention composite enzyme preparation process in, it is preferable that plant enzyme may be used it is those of known in the art,
For example, by using fruit ferment, pectase etc..Commercially available plant enzyme may be used, or use existing method system
It is standby.For example, CN103609985A, CN104012896A, CN104473170A disclose the preparation method of some fruit ferment,
Its full text is incorporated herein by this.
The present invention composite enzyme preparation process in, leaf may include Poplar leaves, pine tree leaf, Folium Pterocaryae, peach leaves,
Apple leaf and loguat leaf.Preferably, leaf is made of Poplar leaves, pine tree leaf, Folium Pterocaryae, peach leaves, apple leaf and loguat leaf.On
It states leaf and is provided with meaning known in the art, which is not described herein again.In the present invention, Poplar leaves, pine tree leaf, Folium Pterocaryae, peach
The weight ratio of leaf, apple leaf and loguat leaf is 1~1.5:1~1.5:1~1.5:1~1.5:1~1.5:1~1.5；Preferably
1~1.3:1~1.3:1~1.3:1~1.3:1~1.3:1~1.3.
The present invention composite enzyme preparation process in, fruit may include pears, apple, hawthorn, blueberry, orange, apricot and
Lichee.Preferably, fruit is made of pears, apple, hawthorn, blueberry, orange, apricot and lichee.In the present invention, pears, apple, mountain
Short, bristly hair or beard, blueberry, orange, apricot and lichee weight ratio be 1~1.5:1~1.5:1~1.5:1~1.5:1~1.5:1~1.5:1~
1.5；Preferably 1~1.3:1~1.3:1~1.3:1~1.3:1~1.3:1~1.3:1~1.3.
In the sewage treatment step of the present invention, is formed and be discharged using the composite enzyme treated sewage, by the water outlet
Filtering, obtains composite enzyme nutrient solution.The dosage of composite enzyme can be sewage weight 0.05~5wt%, preferably 0.1~
1wt%.Using the dosage of above range, be conducive to save composite enzyme, while improving wastewater treatment efficiency.It is according to the present invention
Composite enzyme is divided into multiple batches, is separately added into multiple fermentation vats, is then connect successively with sewage by one embodiment
It touches.Wastewater treatment efficiency can further be improved in this way.Water outlet indicates obtaining after treated sewage, by be further processed can be with
The water of discharge.The mode of filtering is not particularly limited, and for example, carbon granule filters.
In one embodiment of the present invention, the composite enzyme, which is directly added into sewage, carries out aerated fermentation.Namely
It says, the composite enzyme can be contacted directly with sanitary sewage, to carry out fermentation decomposition to sewage.In the another kind of the present invention
In embodiment, the composite enzyme and the waste water after fermentation.For example, the composite enzyme is directly connect with sewage first
The sewage after being fermented is touched, then by the waste water after the composite enzyme and the fermentation.
The sewage of the present invention is not particularly limited, and can be trade effluent, sanitary sewage, livestock and poultry cultivation sewage or urine
Liquid.But for wastewater treatment efficiency, sanitary sewage, livestock and poultry cultivation sewage or urine are preferred.According to the present invention one
A embodiment, the sewage are sanitary sewage.
In the method for the present invention, each microorganism in composite enzyme generates utility and secretion during growth
The matrix mutually grown and raw material are formed, stable structure, an energy are formed extensively with a variety of more by mutual Relationship With Proliferation
The biological flora of sample microbe colony, collaboration play a role, realize coexist, symbiosis, common prosperity environment purification target.
In the soil improvement step of the present invention, composite enzyme nutrient solution is diluted with water, irrigates salinization of soil farmland.At certain
A little embodiment weights, the mixture of composite enzyme nutrient solution and composite enzyme is diluted with water, and irrigates salinization of soil farmland.Compound ferment
The weight ratio of element and composite enzyme nutrient solution can be 1:5~30, preferably 1:10~15.Compound ferment may be used in composite enzyme
The composite enzyme that plain preparation process obtains.Their hybrid mode is not particularly limited.For example, composite enzyme nutrient solution is added
Water dilutes, and composite enzyme is then added.For another example, composite enzyme nutrient solution and composite enzyme are mixed, is then diluted with water.
In the soil improvement step of the present invention, for pouring, the dosage of water is the 50 of the weight of composite enzyme nutrient solution
~500 times, preferably 100~300 times.For spray cans, the dosage of water is 5~20 times of the weight of composite enzyme nutrient solution, excellent
It is selected as 8~15 times.Be conducive to improve reclamation result in this way, salt alkali number declines, and alleviates soil hardening degree.The number of irrigation
Can be 1 year more than twice, preferably three times more than.Pass through above-mentioned irrigation so that the water soluble salt total amount slippage 20 of soil
~70%.The water soluble salt total amount of soil may be used《The 16th part of NY/T1121.16-2006 Soil K+adsorptions：Soil is water-soluble
The measurement of salt total amount》It is measured.Above-mentioned irrigation includes but not limited to pouring and/or spray cans, is preferably poured.In addition, pouring
Sprinkling irrigation, such effect can be coordinated more preferable.For example, using 5~20 times, the water-reducible composite enzyme of preferably 8~15 times of weight
Nutrient solution is sprayed.
According to embodiment of the present invention, soil improvement step is：By composite enzyme nutrient solution and composite enzyme
Mixture is diluted with the water based on 50~500 times of composite enzyme nutrient solution weight, irrigates salinization of soil farmland；Wherein, composite enzyme
Weight ratio with composite enzyme nutrient solution is 1:10~15.
The present invention carries out soil improvement by the nutrient solution that composite enzyme technical finesse sewage generates.The fermentation of the present invention
The cheap raw materials such as Cheng Caiyong leaves, cost reduction.Composite enzyme treated sewage need not add chemical reagent.Gained water outlet is used
In irrigated farmland, soil can be effectively improved.Therefore, method of the invention is advantageously implemented green organic healthy benign cycle
The agricultural and animal products new era.
Specific implementation mode
With reference to specific embodiment, the present invention is further illustrated, but protection scope of the present invention is not limited to
This.
Total bacteria count is measured using GB 20287-2006.Lactic acid bacteria is measured using GB4789.35-2016.Using GB/
T26428 measures other bacterial populations such as bacillus subtilis.
Fruit ferment is prepared using the method for CN103609985A disclosed embodiments 1.
Embodiment 1
<Composite enzyme preparation process>
First fermentation required various leaves and fruit, pine nut, soybean residue, soya-bean cake, vegetable oil residue, rice bran are cleaned, sugar
Dilute 38 DEG C of warm water dilute, spare.Raw material, which is weighed, according to the formula of table 1 carries out dispensing.By 38 DEG C of water and fruit ferment, leaf
(Poplar leaves, pine tree leaf, Folium Pterocaryae, peach leaves, apple leaf and loguat leaf), fruit (pears, apple, hawthorn, blueberry, orange, apricot and
Lichee), pine nut, soybean residue, soya-bean cake, vegetable oil residue, rice bran and malt sugar (being diluted with water, but the total amount of water is constant) mixing, aeration
60 minutes or so, obtain the first fermentation raw material.By the first fermentation raw material in closed fermentation cylinder for fermentation 30 days or so, is obtained
One zymotic fluid.Preceding 15 days fermentation temperatures are 35 DEG C or so, and subsequent 15 days fermentation temperatures are 25 DEG C or so.It needs within first 25 days every
Its opening fermentation tank stirs 30 minutes or so, then covers tightly fermentation tank.First successfully outstanding feature of fermenting is：Fermented liquid has
Acetic acid taste, the distribution of zymotic fluid surface filiform.After testing, the total bacteria count in the first zymotic fluid is 3 × 108~3 × 109CFU/ml,
Lactic acid bacteria is 80% or more, other probiotics such as actinomyces, photosynthetic bacteria, nitrogen-fixing bacteria, bacillus subtilis, saccharomycete account for 5~
20%.
Table 1, the first fermentating formula
Rice bran, soya-bean cake, soybean residue and wheat bran needed for second fermentation is cleaned, malt sugar is diluted with 38 DEG C of warm water, spare.It presses
Raw material progress dispensing is weighed according to the formula of table 2.By 38 DEG C of water and the first zymotic fluid, malt sugar, rice bran, soya-bean cake, soybean residue and bran
Skin mixes, and is aerated 60 minutes or so, obtains the second fermentation raw material in closed fermentation cylinder for fermentation 30 days or so, obtains the second hair
Zymotic fluid.Preceding 15 days fermentation temperatures are 38 DEG C or so, and subsequent fermentation temperature is 25 DEG C or so；It needs within first 20 days to open hair daily
Fermentation tank stirs 30 minutes or so, then covers tightly fermentation tank.After testing, the total bacteria count in the second zymotic fluid is 3 × 105~3 ×
109CFU/ml, lactic acid bacteria are 80wt% or more, other benefits such as actinomyces, photosynthetic bacteria, nitrogen-fixing bacteria, bacillus subtilis, saccharomycete
Raw bacterium accounts for 10~20%.By the second zymotic fluid directly as composite enzyme.
Table 2, the second fermentating formula
| Title | First zymotic fluid | Malt sugar | Rice bran | Soya-bean cake | Soybean residue | Wheat bran | Water |
| Dosage (kg) | 10 | 8 | 2 | 2 | 2 | 1 | 75 |
<Sewage treatment step>
Second zymotic fluid is used for sewage disposal directly as composite enzyme, sewage day output is 500 ton days.
1. influent quality
The water inlet of this item purpose is the sanitary sewage of resident, and water quality is shown in Table 3.
Table 3, influent quality table
| pH | Total phosphorus content TP (mg/L) | NH3-N(mg/L) | COD(mg/L) | BOD(mg/L) |
| 6-9 | 15-4 | 100-55 | 400-200 | 200-100 |
2. effluent quality controls standard
According to the country of table 4《Urban wastewater treatment firm pollutant emission standard》(GB18918-2002) level-one A is marked in table
Accurate and table 5 field irrigation standard (GB5084-2005) index qualified as water outlet.
Table 4, water outlet contamination index numerical value list
| pH | Total phosphorus content TP (mg/L) | NH3-N(mg/L) | COD(mg/L) | BOD(mg/L) |
| 6-9 | 1 | 5 | 50 | 10 |
Table 5, field irrigation water quality list
3. sewage disposal process
Sewage is discharged through former pond, the first fermentation vat, second fermentation vat etc. successively, and water outlet is obtained by filtration multiple through carbon granule
Close enzyme nutrient solution.The dosage and putting mode of composite enzyme are as shown in table 6 below, and sewage disposal result is as shown in table 7 below.
Table 6, composite enzyme add situation list
Testing result compares before and after table 7, sewage disposal
<Soil improvement step>
Composite enzyme nutrient solution is added into 100 times of water dilutions, pours salinization of soil farmland, 1 year three times.The water in salinization of soil farmland
Soluble total amount declines 56% (NY/T1121.16-2006).
It sprays with the use of the water-reducible composite enzyme nutrient solution of 10 times of weight, 1 year twice, salinization of soil farmland
Water soluble salt total amount decline 60% (NY/T1121.16-2006).
Embodiment 2
First fermentating formula of embodiment 1 is replaced with and is formulated shown in table 8, remaining condition is same as Example 1 (to be needed
Sprinkling irrigation).The water soluble salt total amount in salinization of soil farmland declines 55%.
Table 8, the first fermentating formula
Embodiment 3
First fermentating formula of embodiment 1 is replaced with and is formulated shown in table 9, remaining condition is same as Example 1 (to be not required to
It sprays).The water soluble salt total amount in salinization of soil farmland declines 50%.
Table 9, the first fermentating formula
Embodiment 4
Second fermentating formula of embodiment 1 is replaced with and is formulated shown in table 10, remaining condition is same as Example 1 (no
It needs to spray).The water soluble salt total amount in salinization of soil farmland declines 38%.
Table 10, the second fermentating formula
| Title | One time fermentation liquid | Malt sugar | Rice bran | Soya-bean cake | Soybean residue | Wheat bran | Water |
| Dosage (kg) | 8 | 9 | 2 | 2 | 2 | 1 | 76 |
Embodiment 5
By composite enzyme (composite enzyme and the composite enzyme nutrient solution of the composite enzyme nutrient solution of embodiment 1 and embodiment 1
Weight ratio be 1:10) it mixes, adds 100 times of water dilutions, pour salinization of soil farmland, 1 year three times.The water solubility in salinization of soil farmland
Salt total amount declines 58% (NY/T1121.16-2006).
It sprays with the use of the water-reducible composite enzyme nutrient solution of 10 times of weight, 1 year twice, salinization of soil farmland
Water soluble salt total amount decline 63% (NY/T1121.16-2006).
Present invention is not limited to the embodiments described above, without departing from the essence of the present invention, this field skill
Any deformation, improvement, the replacement that art personnel are contemplated that each fall within the scope of the present invention.
Claims (10)
1. a kind of method improveing soil using composite enzyme, which is characterized in that include the following steps：
Composite enzyme preparation process：The first fermentation is carried out using plant enzyme in the first fermentation raw material containing malt sugar, is obtained
Then first zymotic fluid carries out the second hair in the second fermentation raw material containing malt sugar and wheat bran using first zymotic fluid
Ferment obtains composite enzyme；Total bacteria count is 3 × 10 in the composite enzyme5~3 × 109CFU/ml, lactic acid bacteria account for total bacteria count
80% or more, actinomyces, photosynthetic bacteria, nitrogen-fixing bacteria, bacillus subtilis and saccharomycete account for 10~20%；With
Sewage treatment step：It is formed and is discharged using the composite enzyme treated sewage, the water outlet is filtered, composite enzyme is obtained
Nutrient solution；
Soil improvement step is selected from one of following steps：
(1) water of the composite enzyme nutrient solution based on 5~500 times of composite enzyme nutrient solution weight is diluted, is irrigated saline and alkaline
Change farmland；Or
(2) by the mixture of the composite enzyme nutrient solution and the composite enzyme use based on composite enzyme nutrient solution weight 5~
500 times of water dilution, irrigates salinization of soil farmland；Wherein, the weight ratio of composite enzyme and composite enzyme nutrient solution is 1:5~30.
2. according to the method described in claim 1, it is characterized in that, in composite enzyme preparation process, first proferment
Material include 3~8 parts by weight leaves, 3~8 weight fruits, 0.5~2 parts by weight pine nut, 0.5~2 parts by weight soybean residue, 0.5~
2 parts by weight soya-bean cakes, 0.5~2 parts by weight vegetable oil residue, 0.5~2 parts by weight rice bran and 0.5~2 parts by weight malt sugar；Described second
Fermentation raw material include 2~9 parts by weight malt sugars, 1~5 parts by weight rice bran, 1~5 parts by weight soya-bean cake, 1~5 parts by weight soybean residue and
0.5~5 parts by weight wheat bran.
3. according to the method described in claim 2, it is characterized in that, in composite enzyme preparation process, the time of the first fermentation
It is 30~50 days；The time of second fermentation is 20~50 days.
4. according to the method described in claim 3, it is characterized in that, in composite enzyme preparation process, before the first fermentation
10~15 days fermentation temperatures are 30~40 DEG C, and subsequent fermentation temperature is 10~40 DEG C；20~25 days before the first fermentation
It needs to stir 10~50 minutes daily.
5. according to the method described in claim 3, it is characterized in that, in composite enzyme preparation process, before the second fermentation
10~15 days fermentation temperatures are 35~40 DEG C, and subsequent fermentation temperature is 20~30 DEG C；15~20 days before the second fermentation
It needs to stir 20~50 minutes daily.
6. according to the method described in claim 1, it is characterized in that, in composite enzyme preparation process, the leaf includes poplar
Leaf, pine tree leaf, Folium Pterocaryae, peach leaves, apple leaf and loguat leaf；The fruit include pears, apple, hawthorn, blueberry, orange,
Apricot and lichee.
7. according to the method described in claim 6, it is characterized in that, in composite enzyme preparation process, Poplar leaves, pine tree leaf,
Folium Pterocaryae, peach leaves, apple leaf and loguat leaf weight ratio be 1~1.5:1~1.5:1~1.5:1~1.5:1~1.5:1~
1.5；Pears, apple, hawthorn, blueberry, orange, apricot and lichee weight ratio be 1~1.5:1~1.5:1~1.5:1~1.5:1~
1.5:1~1.5:1~1.5.
8. according to the method described in claim 1, it is characterized in that, in composite enzyme preparation process, the second fermentation raw material packet
Include 5~8 parts by weight malt sugars, 2~3 parts by weight rice brans, 2~3 parts by weight soya-bean cakes, 2~3 parts by weight soybean residues and 0.8~2 parts by weight
Wheat bran.
9. according to claim 1~8 any one of them method, which is characterized in that in sewage treatment step, the compound ferment
The dosage of element is 0.1~1wt% of sewage weight.
10. according to the method described in claim 9, it is characterized in that, soil improvement step is：By the composite enzyme nutrient solution
It is diluted with the water of the mixture of the composite enzyme based on 50~500 times of composite enzyme nutrient solution weight, irrigates salinization of soil agriculture
Field；Wherein, the weight ratio of composite enzyme and composite enzyme nutrient solution is 1:10~15.
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| CN109368771A (en) * | 2018-11-29 | 2019-02-22 | 北京市畜牧总站 | It continuously returns fraction activated sludge and quickly handles high concentrated organic wastewater technique and device |
Citations (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002361273A (en) * | 2001-06-12 | 2002-12-17 | Hitoshi Tofun | Environment purifying material and producing method therefor |
| CN101066898A (en) * | 2007-04-21 | 2007-11-07 | 刘奋安 | Organic soil conditioner prepared with city sludge and its usage |
| CN102888427A (en) * | 2011-07-19 | 2013-01-23 | 博赐康生物科技有限公司 | Preparation method of natural environmentally-friendly functional enzyme and application |
| CN104445642A (en) * | 2014-12-09 | 2015-03-25 | 武汉绿阳环保有限责任公司 | Urban sewage treatment composite material as well as preparation method and application thereof |
| CN105349471A (en) * | 2015-12-15 | 2016-02-24 | 金龙 | Preparation method of microbial flora preparation and application thereof |
| CN105409377A (en) * | 2015-11-17 | 2016-03-23 | 仇颖超 | Method using poultry cultivation waste water to process soil hardening |
| CN106135884A (en) * | 2015-03-23 | 2016-11-23 | 孙文彬 | Utilize agricultural wastes produced environment friendly function ferment and preparation method thereof |
| CN106277366A (en) * | 2016-09-29 | 2017-01-04 | 中国科学院水生生物研究所 | A kind of pig-breeding wastewater treatment microbial microbial inoculum and preparation method and application |
-
2018
- 2018-04-28 CN CN201810397530.2A patent/CN108650918A/en active Pending
Patent Citations (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002361273A (en) * | 2001-06-12 | 2002-12-17 | Hitoshi Tofun | Environment purifying material and producing method therefor |
| CN101066898A (en) * | 2007-04-21 | 2007-11-07 | 刘奋安 | Organic soil conditioner prepared with city sludge and its usage |
| CN102888427A (en) * | 2011-07-19 | 2013-01-23 | 博赐康生物科技有限公司 | Preparation method of natural environmentally-friendly functional enzyme and application |
| CN104445642A (en) * | 2014-12-09 | 2015-03-25 | 武汉绿阳环保有限责任公司 | Urban sewage treatment composite material as well as preparation method and application thereof |
| CN106135884A (en) * | 2015-03-23 | 2016-11-23 | 孙文彬 | Utilize agricultural wastes produced environment friendly function ferment and preparation method thereof |
| CN105409377A (en) * | 2015-11-17 | 2016-03-23 | 仇颖超 | Method using poultry cultivation waste water to process soil hardening |
| CN105349471A (en) * | 2015-12-15 | 2016-02-24 | 金龙 | Preparation method of microbial flora preparation and application thereof |
| CN106277366A (en) * | 2016-09-29 | 2017-01-04 | 中国科学院水生生物研究所 | A kind of pig-breeding wastewater treatment microbial microbial inoculum and preparation method and application |
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| CN109368771A (en) * | 2018-11-29 | 2019-02-22 | 北京市畜牧总站 | It continuously returns fraction activated sludge and quickly handles high concentrated organic wastewater technique and device |
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