CN105777258A - Method for making sludge into nutrient soil through anaerobic fermentation - Google Patents
Method for making sludge into nutrient soil through anaerobic fermentation Download PDFInfo
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- CN105777258A CN105777258A CN201610137187.9A CN201610137187A CN105777258A CN 105777258 A CN105777258 A CN 105777258A CN 201610137187 A CN201610137187 A CN 201610137187A CN 105777258 A CN105777258 A CN 105777258A
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
- C05D9/00—Other inorganic fertilisers
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F5/00—Fertilisers from distillery wastes, molasses, vinasses, sugar plant or similar wastes or residues, e.g. from waste originating from industrial processing of raw material of agricultural origin or derived products thereof
- C05F5/002—Solid waste from mechanical processing of material, e.g. seed coats, olive pits, almond shells, fruit residue, rice hulls
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F9/00—Fertilisers from household or town refuse
- C05F9/04—Biological compost
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
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- Environmental & Geological Engineering (AREA)
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- Treatment Of Sludge (AREA)
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Abstract
The invention relates to a method for making sludge into nutrient soil through anaerobic fermentation. Through a reasonable compounding ratio and reasonable arrangement of substrates in a fermentation tank, step-by-step purification layers of an odor substrate adsorption layer, a microbial decomposition layer and a plant absorption layer are formed, so that less odor is given off into air, or the odor is prevented from being given off into the air; in addition, a methane collecting system is paved at the upper part of the anaerobic fermentation tank, so that recycling of sludge energy resources can also be realized. Through 12-month long-time anaerobic fermentation, organic matters which are easy to decompose in sludge can be converted into stable humus type substances, and the content of humus is increased by about 25%. The high-temperature stage duration in the anaerobic fermentation process is long, so that original pathogenic bacteria in the sludge can be killed. The sludge is mixed with alkali soil, so that curing and passivating effects on original heavy metal can be achieved, the validity of the heavy metal is reduced by about 50%, besides, the decomposition effect on antibiotics and durable organic compounds contained in the sludge can be achieved, and the harmfulness of the sludge is reduced.
Description
Technical field
The present invention relates to solid wastes recycling processing technology field, the method for a kind of sludge anaerobic fermentation Nutrition Soil processed.
Background technology
Dewatered sludge of urban sewage plant is that municipal wastewater treatment plant processes solid-state castoff produced by waste water.Along with China is building the increase of Sewage Plant number, sludge yield still can increase.Containing plant desired nutritional elements such as a large amount of organic matters and N, P and K in municipal sludge, it is to realize this type of solid waste reducing that sludge fermentation is used as vegetables matrix after processing, the innoxious and effective way of resource.The outdoor aerobic fermentation generally used, air pollution is relatively big, uses advanced fermentation cabin technique then to need to put into large number quipments and power, and for Nutrition Soil produced by aerobic fermentation, processing cost is higher.
Summary of the invention
Processing for sludge fermentation in above-mentioned prior art and there is the problems such as air pollution is relatively big, processing cost is higher, the present invention provides a kind of method that sludge anaerobic ferments Nutrition Soil processed.
For solving above-mentioned technical problem, the technical solution used in the present invention is:
The method of a kind of sludge anaerobic fermentation Nutrition Soil processed, comprises the following steps:
Step one: selection is barren away from the nutrition of residential block, thicker soil hillside fields, excavation length is the anaerobic fermentating groove of 4m, and wherein the topsoil of 20cm is collected respectively with subsoil；If having sandstone in the soil of excavation, need to sieve, soil and sandstone after sieving retain respectively；
Step 2: the anaerobic fermentation trench bottom dug in step one and surrounding sidewall lay antiseepage film, stops the pollution to Soil Surrounding of zymotic fluid that sludge fermentation produces；
Step 3, taking the dewatered sludge that water content is 75% ~ 85%, the subsoil stirring after then sieving with step one excavation mix, the stalk pulverized by addition or peanut shell with regulate fermentation substrate C/N than as 15:1 ~ 17:1；Spray containing lactic acid bacteria, photosynthetic bacteria, acidifying bacterium during mud mixes with subsoil, produce hydrogen acid-producing bacteria, amonifying bacteria and and the mix bacterium agent of methane backeria, forced fermentation process；
Step 4: take the matrix of becoming thoroughly decomposed utilizing peanut shell and mud to prepare and fill in the orlop 30cm thickness of anaerobic fermentating groove, then the mixed-matrix of step 3 gained is inserted anaerobic fermentating groove at the 80cm of top, insert the Activated Carbon Made from Peanut Shells matrix adsorption layer of 10cm thickness, the thick above-mentioned matrix of becoming thoroughly decomposed of 30cm, the thick above-mentioned matrix composite soil with the topsoil of step one gained that becomes thoroughly decomposed of 40cm the most successively, the most above-mentioned matrix of becoming thoroughly decomposed is mixed by 2:1 with topsoil, forms plant absorption layer at top layer long-term cropping the most again；
Step 5: after the mud mixed-matrix step 4 filled in ferments 12 months, topsoil is removed, the sludge substrate that excavation ferments, pulverize, cross 2mm sieve after i.e. can be used as Nutrition Soil and carry out forest, flower seedling raising, improvement of soil fertility or land reclamation in mining area；The topsoil of excavation is covered on the sandstone of step one gained simultaneously, planting trees and grass can be carried out.
In described step 4, the crop of plantation is the plant variety that can absorb foul smell produced by anaerobic fermentation；
Hillside fields in described step one is away from river course, water source, and level of ground water is deeper；
In described step 3, fermentation substrate C/N is than for 16:1；
In described step 3, the water content of dewatered sludge is 80%, and the water content of lower soil is 20%；
In described step 4, the preparation method of Activated Carbon Made from Peanut Shells matrix is: use peanut shell and the mixing of 25% sulfuric acid, wherein mixed proportion is 1g peanut shell/2ml sulfuric acid, then stand overnight, 2h is activated under the conditions of 450 ~ 500 DEG C, finally cool down, wash, dry, pulverize, obtain Activated Carbon Made from Peanut Shells base；
The preparation method utilizing matrix of becoming thoroughly decomposed prepared by peanut shell and mud in described step 4 is: peanut shell and mud 2:1 in mass ratio being mixed, water content control is 60%, then becomes thoroughly decomposed 18 days under the conditions of maximum temperature 80 DEG C；
Methane collection system is also laid on described anaerobic fermentating groove top.
Beneficial effects of the present invention:
The method of the sludge anaerobic fermentation Nutrition Soil processed that the present invention provides, power consumption is few, it is not necessary to special processing equipment；For the stabilisation of city dehydrated sludge, mud quantifies, and innoxious and recycling treatment provides theory and technology support；This method not only efficiently solves the process handling problems of municipal sludge, and foster and apply fertilizer for waste hillside, land reclamation in mining area, woods tree flower growth provides a kind of efficient nutrient matrix；
The method of the sludge anaerobic fermentation Nutrition Soil processed that the present invention provides, it is possible to achieve sludge stabilizing, innoxious, minimizing and the process of resource.The long anaerobic fermentation through 12 months, can make labile organic matter in mud be changed into stable Humus material, and humus content improves about 25%；The hot stage duration in anaerobic fermentation process is longer, can kill original pathogen in mud；Being mixed by mud and basic soil, can play the solidification passivation effect to original heavy metal, the validity of heavy metal reduces about 50%, and antibiotic and persistent organism to containing in mud play decomposition simultaneously, reduce the harmfulness of mud；By the product acid of anaerobism, produce alkali process, original sludge volume amount and weight minimizing about about 20%；Nutrition Soil after having fermented can be reclaimed as improvement lean soil, deserted mountain, seedling medium etc. uses；Compared with processing with traditional aerobic sludge, expense is relatively low, saves aeration and turns over the input power costs such as plane；Produced by anaerobic fermentation, foul smell is effectively controlled, and by the rational substrate composition in fermentation tank top and arrangement, forms the purifying layer step by step such as foul smell matrix adsorption layer-microbial decomposition layer-plant absorption, less or avoid foul smell distribute with air in the middle of；It addition, by laying methane collection system at anaerobic fermentating groove, the recycling of sludge energy also can be realized.
Detailed description of the invention
Below in conjunction with detailed description of the invention, the present invention is further elaborated.
Embodiment 1
The method of a kind of sludge anaerobic fermentation Nutrition Soil processed, comprises the following steps:
Step one: selection is barren away from the nutrition of residential block, thicker soil hillside fields, and this hillside fields is away from river course, water source, level of ground water is relatively deep, and excavation length is the anaerobic fermentating groove of 4m, and wherein the topsoil of 20cm is collected respectively with lower soil；If having sandstone in the soil of excavation, need to sieve, soil and sandstone after sieving retain respectively；
Step 2: the anaerobic fermentation trench bottom dug in step one and surrounding sidewall lay antiseepage film, stops the pollution to Soil Surrounding of zymotic fluid that sludge fermentation produces；
Step 3, take the dewatered sludge that water content is 80%, after then sieving with step one excavation water content be 20% lower soil stirring mix, the stalk pulverized by addition or peanut shell are to regulate fermentation substrate C/N ratio as 16:1；Spray containing lactic acid bacteria, photosynthetic bacteria, acidifying bacterium during mud mixes with soil, produce hydrogen acid-producing bacteria, amonifying bacteria and and the mix bacterium agent of methane backeria, forced fermentation process；
Step 4: take the matrix of becoming thoroughly decomposed utilizing peanut shell and mud to prepare and fill in the orlop 30cm thickness of anaerobic fermentating groove, then the mixed-matrix of step 3 gained is inserted anaerobic fermentating groove at the 80cm of top, insert the Activated Carbon Made from Peanut Shells matrix adsorption layer adsorption layer as foul smell of 10cm thickness, the thick above-mentioned matrix of becoming thoroughly decomposed of 30cm the most successively as microbial decomposition layer, the thick above-mentioned matrix composite soil with the topsoil of step one gained that becomes thoroughly decomposed of 40cm, the most above-mentioned matrix of becoming thoroughly decomposed is mixed by 2:1 with topsoil, forms plant absorption layer at top layer long-term cropping the most again；The preparation method of matrix that prepared by described peanut shell and mud become thoroughly decomposed is: peanut shell and mud 2:1 in mass ratio being mixed, water content control is 60%, then becomes thoroughly decomposed 18 days under the conditions of maximum temperature 80 DEG C；The preparation method of described Activated Carbon Made from Peanut Shells matrix is: use peanut shell and the mixing of 25% sulfuric acid, wherein mixed proportion is 1g peanut shell/2ml sulfuric acid, then stands overnight, and activates 2h under the conditions of 500 DEG C, finally cool down, wash, dry, pulverize, obtain Activated Carbon Made from Peanut Shells base；
Step 5: after the mud mixed-matrix step 4 filled in ferments 12 months, topsoil is removed, the sludge substrate that excavation ferments, pulverize, cross 2mm sieve after i.e. can be used as Nutrition Soil and carry out forest, flower seedling raising, improvement of soil fertility or land reclamation in mining area；The topsoil of excavation is covered on the sandstone of step one gained simultaneously, planting trees and grass can be carried out.
Embodiment 2
The method of a kind of sludge anaerobic fermentation Nutrition Soil processed, comprises the following steps:
Step one: selection is barren away from the nutrition of residential block, thicker soil hillside fields, and this hillside fields is away from river course, water source, level of ground water is relatively deep, and excavation length is the anaerobic fermentating groove of 4m, the wherein topsoil of 20cm and lower soil separate collection；If having sandstone in the soil of excavation, need to sieve, soil and sandstone after sieving are reserved separately；
Step 2: the anaerobic fermentation trench bottom dug in step one and surrounding sidewall lay antiseepage film, stops the pollution to Soil Surrounding of zymotic fluid that sludge fermentation produces；
Step 3, take the dewatered sludge that water content is 75%, after then sieving with step one excavation water content be 20% lower soil stirring mix, the stalk pulverized by addition or peanut shell are to regulate fermentation substrate C/N ratio as 15:1；Spray containing lactic acid bacteria, photosynthetic bacteria, acidifying bacterium during mud mixes with soil, produce hydrogen acid-producing bacteria, amonifying bacteria and and the mix bacterium agent of methane backeria, forced fermentation process；
Step 4: take the matrix of becoming thoroughly decomposed utilizing peanut shell and mud to prepare and fill in the orlop 30cm thickness of anaerobic fermentating groove, then the mixed-matrix of step 3 gained is inserted anaerobic fermentating groove at the 80cm of top, insert the Activated Carbon Made from Peanut Shells matrix adsorption layer adsorption layer as foul smell of 10cm thickness, the thick above-mentioned matrix of becoming thoroughly decomposed of 30cm the most successively as microbial decomposition layer, the thick above-mentioned matrix composite soil with the topsoil of step one gained that becomes thoroughly decomposed of 40cm, the most above-mentioned matrix of becoming thoroughly decomposed is mixed by 2:1 with topsoil, forms plant absorption layer at top layer long-term cropping the most again；The preparation method of matrix that prepared by described peanut shell and mud become thoroughly decomposed is: peanut shell and mud 2:1 in mass ratio being mixed, water content control is 60%, then becomes thoroughly decomposed 18 days under the conditions of maximum temperature 80 DEG C；The preparation method of described Activated Carbon Made from Peanut Shells matrix is: use peanut shell and the mixing of 25% sulfuric acid, wherein mixed proportion is 1g peanut shell/2ml sulfuric acid, then stands overnight, and activates 2h under the conditions of 450 DEG C, finally cool down, wash, dry, pulverize, obtain Activated Carbon Made from Peanut Shells base；
Step 5: after the mud mixed-matrix step 4 filled in ferments 12 months, topsoil is removed, the sludge substrate that excavation ferments, pulverize, cross 2mm sieve after i.e. can be used as Nutrition Soil and carry out forest, flower seedling raising, improvement of soil fertility or land reclamation in mining area；The topsoil of excavation is covered on the sandstone of step one gained simultaneously, planting trees and grass can be carried out.
Embodiment 3
The method of a kind of sludge anaerobic fermentation Nutrition Soil processed, comprises the following steps:
Step one: selection is barren away from the nutrition of residential block, thicker soil hillside fields, and this hillside fields is away from river course, water source, level of ground water is relatively deep, and excavation length is the anaerobic fermentating groove of 4m, the wherein topsoil of 20cm and lower soil separate collection；If having sandstone in the soil of excavation, need to sieve, soil and sandstone after sieving are reserved separately；
Step 2: the anaerobic fermentation trench bottom dug in step one and surrounding sidewall lay antiseepage film, stops the pollution to Soil Surrounding of zymotic fluid that sludge fermentation produces；
Step 3, take the dewatered sludge that water content is 85%, after then sieving with step one excavation water content be 20% lower soil stirring mix, the stalk pulverized by addition or peanut shell are to regulate fermentation substrate C/N ratio as 17:1；Spray containing lactic acid bacteria, photosynthetic bacteria, acidifying bacterium during mud mixes with soil, produce hydrogen acid-producing bacteria, amonifying bacteria and and the mix bacterium agent of methane backeria, forced fermentation process；
Step 4: take the matrix of becoming thoroughly decomposed utilizing peanut shell and mud to prepare and fill in the orlop 30cm thickness of anaerobic fermentating groove, then the mixed-matrix of step 3 gained is inserted anaerobic fermentating groove at the 80cm of top, insert the Activated Carbon Made from Peanut Shells matrix adsorption layer adsorption layer as foul smell of 10cm thickness, the thick above-mentioned matrix of becoming thoroughly decomposed of 30cm the most successively as microbial decomposition layer, the thick above-mentioned matrix composite soil with the topsoil of step one gained that becomes thoroughly decomposed of 40cm, the most above-mentioned matrix of becoming thoroughly decomposed is mixed by 2:1 with topsoil, forms plant absorption layer at top layer long-term cropping the most again；The preparation method of matrix that prepared by described peanut shell and mud become thoroughly decomposed is: peanut shell and mud 2:1 in mass ratio being mixed, water content control is 60%, then becomes thoroughly decomposed 18 days under the conditions of maximum temperature 80 DEG C；The preparation method of described Activated Carbon Made from Peanut Shells matrix is: use peanut shell and the mixing of 25% sulfuric acid, wherein mixed proportion is 1g peanut shell/2ml sulfuric acid, then stands overnight, and activates 2h under the conditions of 480 DEG C, finally cool down, wash, dry, pulverize, obtain Activated Carbon Made from Peanut Shells base；
Step 5: after the mud mixed-matrix step 4 filled in ferments 12 months, topsoil is removed, the sludge substrate that excavation ferments, pulverize, cross 2mm sieve after i.e. can be used as Nutrition Soil and carry out forest, flower seedling raising, improvement of soil fertility or land reclamation in mining area；The topsoil of excavation is covered on the sandstone of step one gained simultaneously, planting trees and grass can be carried out.
The method of the sludge anaerobic fermentation Nutrition Soil processed that the present invention provides, power consumption is few, it is not necessary to special processing equipment；Quantify for the stabilisation of city dehydrated sludge, mud, innoxious and recycling treatment provides theory and technology support；This method not only efficiently solves the process handling problems of municipal sludge, and foster and apply fertilizer for waste hillside, land reclamation in mining area, woods tree flower growth provides a kind of efficient nutrient matrix；
The method of the sludge anaerobic fermentation Nutrition Soil processed that the present invention provides, it is possible to achieve sludge stabilizing, innoxious, minimizing and the process of resource.The long anaerobic fermentation through 12 months, can make labile organic matter in mud be changed into stable Humus material, and humus content improves about 25%；The hot stage duration in anaerobic fermentation process is longer, can kill original pathogen in mud；Being mixed by mud and basic soil, can play the solidification passivation effect to original heavy metal, the validity of heavy metal reduces about 50%, and antibiotic and persistent organism to containing in mud play decomposition simultaneously, reduce the harmfulness of mud；By the product acid of anaerobism, produce alkali process, original sludge volume amount and weight minimizing about about 20%；Nutrition Soil after having fermented can be reclaimed as improvement lean soil, deserted mountain, seedling medium etc. uses；Compared with processing with traditional aerobic sludge, expense is relatively low, saves aeration and turns over the input power costs such as plane；Produced by anaerobic fermentation, foul smell is effectively controlled, and by the rational substrate composition in fermentation tank top and arrangement, forms the purifying layer step by step such as foul smell matrix adsorption layer-microbial decomposition layer-plant absorption, less or avoid foul smell distribute with air in the middle of；It addition, by laying methane collection system at anaerobic fermentating groove, the recycling of sludge energy also can be realized.
Claims (8)
1. the method for a sludge anaerobic fermentation Nutrition Soil processed, it is characterised in that comprise the following steps:
Step one: selection is barren away from the nutrition of residential block, thicker soil hillside fields, excavation length is the anaerobic fermentating groove of 4m, and wherein the topsoil of 20cm is collected respectively with subsoil；If having sandstone in the soil of excavation, need to sieve, soil and sandstone after sieving retain respectively；
Step 2: the anaerobic fermentation trench bottom dug in step one and surrounding sidewall lay antiseepage film, stops the pollution to Soil Surrounding of zymotic fluid that sludge fermentation produces；
Step 3, taking the dewatered sludge that water content is 75% ~ 85%, the subsoil stirring after then sieving with step one excavation mix, the stalk pulverized by addition or peanut shell with regulate fermentation substrate C/N than as 15:1 ~ 17:1；Spray containing lactic acid bacteria, photosynthetic bacteria, acidifying bacterium during mud mixes with subsoil, produce hydrogen acid-producing bacteria, amonifying bacteria and and the mix bacterium agent of methane backeria, forced fermentation process；
Step 4: take the matrix of becoming thoroughly decomposed utilizing peanut shell and mud to prepare and fill in the orlop 30cm thickness of anaerobic fermentating groove, then the mixed-matrix of step 3 gained is inserted anaerobic fermentating groove at the 80cm of top, insert the Activated Carbon Made from Peanut Shells matrix adsorption layer of 10cm thickness, the thick above-mentioned matrix of becoming thoroughly decomposed of 30cm, the thick above-mentioned matrix composite soil with the topsoil of step one gained that becomes thoroughly decomposed of 40cm the most successively, the most above-mentioned matrix of becoming thoroughly decomposed is mixed by 2:1 with topsoil, forms plant absorption layer at top layer long-term cropping the most again；
Step 5: after the mud mixed-matrix step 4 filled in ferments 12 months, topsoil is removed, the sludge substrate that excavation ferments, pulverize, cross 2mm sieve after i.e. can be used as Nutrition Soil and carry out forest, flower seedling raising, improvement of soil fertility or land reclamation in mining area；The topsoil of excavation is covered on the sandstone of step one gained simultaneously, planting trees and grass can be carried out.
2. the method for sludge anaerobic fermentation Nutrition Soil processed as claimed in claim 1, it is characterised in that: in described step 4, the crop of plantation is the plant variety that can absorb foul smell produced by anaerobic fermentation.
3. the method for sludge anaerobic fermentation Nutrition Soil processed as claimed in claim 1, it is characterised in that: the hillside fields in described step one is away from river course, water source, and level of ground water is deeper.
4. sludge anaerobic as claimed in claim 1 ferments the method for Nutrition Soil processed, it is characterised in that: in described step 3, fermentation substrate C/N ratio is for 16:1.
5. the method for sludge anaerobic fermentation Nutrition Soil processed as claimed in claim 1, it is characterised in that: in described step 3, the water content of dewatered sludge is 80%, and the water content of lower soil is 20%.
6. the method for sludge anaerobic fermentation Nutrition Soil processed as claimed in claim 1, it is characterized in that: in described step 4, the preparation method of Activated Carbon Made from Peanut Shells matrix is: use peanut shell and the mixing of 25% sulfuric acid, wherein mixed proportion is 1g peanut shell/2ml sulfuric acid, then stand overnight, 2h is activated under the conditions of 450 ~ 500 DEG C, finally cool down, wash, dry, pulverize, obtain Activated Carbon Made from Peanut Shells base.
7. the method for sludge anaerobic fermentation Nutrition Soil processed as claimed in claim 1, it is characterized in that: the preparation method of the matrix of becoming thoroughly decomposed utilizing peanut shell and mud to prepare in described step 4 is: peanut shell and mud 2:1 in mass ratio are mixed, water content control is 60%, then becomes thoroughly decomposed 18 days under the conditions of maximum temperature 80 DEG C.
8. the method for sludge anaerobic fermentation Nutrition Soil processed as claimed in claim 1, it is characterised in that: methane collection system is also laid on described anaerobic fermentating groove top.
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| CN201610137187.9A CN105777258A (en) | 2016-03-11 | 2016-03-11 | Method for making sludge into nutrient soil through anaerobic fermentation |
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| CN201610137187.9A CN105777258A (en) | 2016-03-11 | 2016-03-11 | Method for making sludge into nutrient soil through anaerobic fermentation |
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Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106472280A (en) * | 2016-10-14 | 2017-03-08 | 安徽格义循环经济产业园有限公司 | Nursery matrix and preparation method thereof |
| CN107056552A (en) * | 2017-06-10 | 2017-08-18 | 陕西理工学院 | A kind of utilization excess sludge and agriculture and forestry organic waste material prepare the device of fertilizer |
| CN107488065A (en) * | 2017-08-25 | 2017-12-19 | 洛阳茂生生物技术有限公司 | A kind of preparation of sludge organic substrate and the mobile method for culturing seedlings based on the matrix |
| CN109618866A (en) * | 2018-12-17 | 2019-04-16 | 安徽省巢湖铸造厂有限责任公司 | A method of utilizing phosphatization sludge Nutrition Soil |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101381072A (en) * | 2008-10-15 | 2009-03-11 | 云南师范大学 | Hydrogen production method by sweet sorghum stalk anaerobic fermentation |
| CN103664255A (en) * | 2012-09-03 | 2014-03-26 | 厦门绿标生物科技有限公司 | Organic waste facultative aerobic fermentation composting treatment process |
| CN103833426A (en) * | 2014-02-28 | 2014-06-04 | 河南科技大学 | Method for preparing matrix of raw winter vegetables with municipal sludge |
| CN104418613A (en) * | 2013-08-31 | 2015-03-18 | 陈亮亮 | Method for preparing organic fertilizer by using sewage sludge |
| CN105000924A (en) * | 2015-06-26 | 2015-10-28 | 张小平 | Method for wet composting of bio-organic fertilizer from rural garbage |
-
2016
- 2016-03-11 CN CN201610137187.9A patent/CN105777258A/en active Pending
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101381072A (en) * | 2008-10-15 | 2009-03-11 | 云南师范大学 | Hydrogen production method by sweet sorghum stalk anaerobic fermentation |
| CN103664255A (en) * | 2012-09-03 | 2014-03-26 | 厦门绿标生物科技有限公司 | Organic waste facultative aerobic fermentation composting treatment process |
| CN104418613A (en) * | 2013-08-31 | 2015-03-18 | 陈亮亮 | Method for preparing organic fertilizer by using sewage sludge |
| CN103833426A (en) * | 2014-02-28 | 2014-06-04 | 河南科技大学 | Method for preparing matrix of raw winter vegetables with municipal sludge |
| CN105000924A (en) * | 2015-06-26 | 2015-10-28 | 张小平 | Method for wet composting of bio-organic fertilizer from rural garbage |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106472280A (en) * | 2016-10-14 | 2017-03-08 | 安徽格义循环经济产业园有限公司 | Nursery matrix and preparation method thereof |
| CN107056552A (en) * | 2017-06-10 | 2017-08-18 | 陕西理工学院 | A kind of utilization excess sludge and agriculture and forestry organic waste material prepare the device of fertilizer |
| CN107488065A (en) * | 2017-08-25 | 2017-12-19 | 洛阳茂生生物技术有限公司 | A kind of preparation of sludge organic substrate and the mobile method for culturing seedlings based on the matrix |
| CN109618866A (en) * | 2018-12-17 | 2019-04-16 | 安徽省巢湖铸造厂有限责任公司 | A method of utilizing phosphatization sludge Nutrition Soil |
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