CN106431580A - Method and apparatus for treating fecal contamination and producing organic fertilizer at same time through simulation forest surface ecological system - Google Patents
Method and apparatus for treating fecal contamination and producing organic fertilizer at same time through simulation forest surface ecological system Download PDFInfo
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- 238000000034 method Methods 0.000 title claims abstract description 48
- 239000003895 organic fertilizer Substances 0.000 title abstract description 12
- 230000002550 fecal effect Effects 0.000 title abstract description 6
- 238000011109 contamination Methods 0.000 title abstract description 5
- 238000004088 simulation Methods 0.000 title abstract 2
- 239000000706 filtrate Substances 0.000 claims abstract description 264
- 238000000855 fermentation Methods 0.000 claims abstract description 182
- 230000004151 fermentation Effects 0.000 claims abstract description 181
- 238000002156 mixing Methods 0.000 claims abstract description 163
- 239000000463 material Substances 0.000 claims abstract description 90
- 239000007788 liquid Substances 0.000 claims abstract description 49
- 238000001914 filtration Methods 0.000 claims abstract description 47
- 210000003608 fece Anatomy 0.000 claims abstract description 45
- 239000000203 mixture Substances 0.000 claims abstract description 38
- 241000894006 Bacteria Species 0.000 claims abstract description 30
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 25
- 239000011368 organic material Substances 0.000 claims abstract description 21
- 239000007787 solid Substances 0.000 claims abstract description 18
- 238000001704 evaporation Methods 0.000 claims abstract description 16
- 239000002002 slurry Substances 0.000 claims abstract description 15
- 239000004576 sand Substances 0.000 claims abstract description 13
- 239000010902 straw Substances 0.000 claims description 196
- 239000010865 sewage Substances 0.000 claims description 120
- 238000013327 media filtration Methods 0.000 claims description 109
- 239000003337 fertilizer Substances 0.000 claims description 73
- 239000002245 particle Substances 0.000 claims description 48
- 229910010272 inorganic material Inorganic materials 0.000 claims description 31
- 239000011147 inorganic material Substances 0.000 claims description 31
- 239000007921 spray Substances 0.000 claims description 24
- 229910000278 bentonite Inorganic materials 0.000 claims description 23
- 239000000440 bentonite Substances 0.000 claims description 23
- SVPXDRXYRYOSEX-UHFFFAOYSA-N bentoquatam Chemical compound O.O=[Si]=O.O=[Al]O[Al]=O SVPXDRXYRYOSEX-UHFFFAOYSA-N 0.000 claims description 23
- 230000008569 process Effects 0.000 claims description 22
- 238000007599 discharging Methods 0.000 claims description 15
- 230000008020 evaporation Effects 0.000 claims description 15
- 238000011049 filling Methods 0.000 claims description 13
- 239000004927 clay Substances 0.000 claims description 12
- 238000004332 deodorization Methods 0.000 claims description 12
- 235000013312 flour Nutrition 0.000 claims description 12
- 239000002023 wood Substances 0.000 claims description 12
- 239000010881 fly ash Substances 0.000 claims description 11
- 238000000746 purification Methods 0.000 claims description 10
- 239000000126 substance Substances 0.000 claims description 10
- 239000002689 soil Substances 0.000 claims description 8
- 238000005273 aeration Methods 0.000 claims description 7
- 230000009286 beneficial effect Effects 0.000 claims description 7
- 238000010521 absorption reaction Methods 0.000 claims description 6
- 230000008859 change Effects 0.000 claims description 6
- 150000001875 compounds Chemical class 0.000 claims description 6
- 239000000843 powder Substances 0.000 claims description 6
- 238000001816 cooling Methods 0.000 claims description 5
- 238000012423 maintenance Methods 0.000 claims description 5
- 239000010802 sludge Substances 0.000 claims description 5
- 238000004659 sterilization and disinfection Methods 0.000 claims description 4
- 239000011248 coating agent Substances 0.000 claims description 3
- 238000000576 coating method Methods 0.000 claims description 3
- 239000004033 plastic Substances 0.000 claims description 3
- 229920003023 plastic Polymers 0.000 claims description 3
- 238000001179 sorption measurement Methods 0.000 abstract description 2
- 238000005507 spraying Methods 0.000 abstract 3
- 244000144972 livestock Species 0.000 description 22
- 244000144977 poultry Species 0.000 description 20
- 238000004519 manufacturing process Methods 0.000 description 15
- 238000012271 agricultural production Methods 0.000 description 7
- 238000005516 engineering process Methods 0.000 description 7
- 241000196324 Embryophyta Species 0.000 description 6
- 241001465754 Metazoa Species 0.000 description 6
- 235000013339 cereals Nutrition 0.000 description 6
- 230000008901 benefit Effects 0.000 description 5
- 230000007613 environmental effect Effects 0.000 description 5
- 239000010871 livestock manure Substances 0.000 description 5
- 230000008961 swelling Effects 0.000 description 5
- 238000009360 aquaculture Methods 0.000 description 4
- 244000144974 aquaculture Species 0.000 description 4
- 238000009395 breeding Methods 0.000 description 4
- 230000001488 breeding effect Effects 0.000 description 4
- 229910052751 metal Inorganic materials 0.000 description 4
- 239000002184 metal Substances 0.000 description 4
- 239000005416 organic matter Substances 0.000 description 4
- 238000004140 cleaning Methods 0.000 description 3
- 239000002361 compost Substances 0.000 description 3
- 239000012141 concentrate Substances 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 239000003344 environmental pollutant Substances 0.000 description 3
- 239000007789 gas Substances 0.000 description 3
- 231100000719 pollutant Toxicity 0.000 description 3
- 239000000047 product Substances 0.000 description 3
- 241000244203 Caenorhabditis elegans Species 0.000 description 2
- 206010059410 Faecaluria Diseases 0.000 description 2
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 2
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 238000010276 construction Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000011010 flushing procedure Methods 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 229910052757 nitrogen Inorganic materials 0.000 description 2
- 235000015097 nutrients Nutrition 0.000 description 2
- 239000010815 organic waste Substances 0.000 description 2
- 229910052700 potassium Inorganic materials 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 230000001105 regulatory effect Effects 0.000 description 2
- 239000002912 waste gas Substances 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- 241000208340 Araliaceae Species 0.000 description 1
- 239000002028 Biomass Substances 0.000 description 1
- 235000016936 Dendrocalamus strictus Nutrition 0.000 description 1
- 241000233866 Fungi Species 0.000 description 1
- 235000005035 Panax pseudoginseng ssp. pseudoginseng Nutrition 0.000 description 1
- 235000003140 Panax quinquefolius Nutrition 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- 241000607479 Yersinia pestis Species 0.000 description 1
- 210000001015 abdomen Anatomy 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 238000013459 approach Methods 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000004566 building material Substances 0.000 description 1
- 108010066057 cabin-1 Proteins 0.000 description 1
- 108010066114 cabin-2 Proteins 0.000 description 1
- YYRMJZQKEFZXMX-UHFFFAOYSA-L calcium bis(dihydrogenphosphate) Chemical compound [Ca+2].OP(O)([O-])=O.OP(O)([O-])=O YYRMJZQKEFZXMX-UHFFFAOYSA-L 0.000 description 1
- 229910000389 calcium phosphate Inorganic materials 0.000 description 1
- 239000004202 carbamide Substances 0.000 description 1
- 235000013877 carbamide Nutrition 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 239000010883 coal ash Substances 0.000 description 1
- 238000009264 composting Methods 0.000 description 1
- 230000001276 controlling effect Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 238000005108 dry cleaning Methods 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 238000009313 farming Methods 0.000 description 1
- -1 feces Substances 0.000 description 1
- 235000008434 ginseng Nutrition 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 239000003864 humus Substances 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 238000011835 investigation Methods 0.000 description 1
- 239000003621 irrigation water Substances 0.000 description 1
- 235000021374 legumes Nutrition 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 235000019691 monocalcium phosphate Nutrition 0.000 description 1
- 239000010813 municipal solid waste Substances 0.000 description 1
- 239000005445 natural material Substances 0.000 description 1
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 description 1
- 235000021049 nutrient content Nutrition 0.000 description 1
- 238000005457 optimization Methods 0.000 description 1
- 238000012856 packing Methods 0.000 description 1
- 239000000575 pesticide Substances 0.000 description 1
- 239000010900 piggery waste Substances 0.000 description 1
- 238000012805 post-processing Methods 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- OTYBMLCTZGSZBG-UHFFFAOYSA-L potassium sulfate Chemical compound [K+].[K+].[O-]S([O-])(=O)=O OTYBMLCTZGSZBG-UHFFFAOYSA-L 0.000 description 1
- 229910052939 potassium sulfate Inorganic materials 0.000 description 1
- 235000011151 potassium sulphates Nutrition 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 230000000384 rearing effect Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 239000010907 stover Substances 0.000 description 1
- 235000013619 trace mineral Nutrition 0.000 description 1
- 239000011573 trace mineral Substances 0.000 description 1
- 238000010792 warming Methods 0.000 description 1
Classifications
-
- 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
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D36/00—Filter circuits or combinations of filters with other separating devices
- B01D36/02—Combinations of filters of different kinds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
- C02F1/32—Treatment of water, waste water, or sewage by irradiation with ultraviolet light
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- 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
-
- 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
- C05F17/90—Apparatus therefor
- C05F17/989—Flow sheets for biological or biochemical treatment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/20—Nature of the water, waste water, sewage or sludge to be treated from animal husbandry
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
- C02F2301/08—Multistage treatments, e.g. repetition of the same process step under different conditions
-
- 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
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
-
- 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
Landscapes
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Organic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Health & Medical Sciences (AREA)
- Microbiology (AREA)
- Water Supply & Treatment (AREA)
- Environmental & Geological Engineering (AREA)
- Hydrology & Water Resources (AREA)
- Molecular Biology (AREA)
- Biochemistry (AREA)
- Biotechnology (AREA)
- General Chemical & Material Sciences (AREA)
- Inorganic Chemistry (AREA)
- Toxicology (AREA)
- Biodiversity & Conservation Biology (AREA)
- Fertilizers (AREA)
- Treatment Of Sludge (AREA)
Abstract
The invention relates to a simulation forest surface ecological system, and relates to a method and apparatus where organic coarse stalks are used to preliminarily filter fecal contamination, high-adsorption organic and inorganic mixture is further used as a filter material to adsorb and filter contaminated water, organic material is fermented to evaporate the contaminated water, the used filter material and the preliminarily filtered solid feces are mixed and stirred and fermented into organic fertilizer; the method comprises: conveying liquid fecal contamination (<5% of solid) to a coarse stalk filter material filter chamber for preliminary filtration, adding fermenting bacteria to filtrate, spraying the filtrate into a first mixed filter material filter chamber for filtration, further spraying obtained filtrate to a second mixed filter material filter chamber for filtration, and delivering the filtrate into a quick seepage sand filter tank to act as reclaimed water for reuse after being purified; or conveying semi-solid fecal contamination and thick fecal slurry (solid being >/=5% and <30%) to the coarse stalk filter material filter chamber for filtration, adding fermenting bacteria to filtrate, spraying the filtrate to multiple mixed filter material fermenting chambers, fermenting the contaminated water adsorbed filter material at high temperature, evaporating the contaminated water at high temperature for the purpose of 'zero discharge' of contaminated water; mixing the filter material of the coarse stalk filter material filter chamber, the filter material fermented in the mixed filter fermenting chambers and the solid feces on the coarse stalk filter material, and feeding the mixture to an organic fertilizer main fermenting chamber for high-temperature fermentation.
Description
Technical field
The present invention relates to environmental technology field, it is related to organic fertilizer production and organic sewage process field, relates more specifically to
Process the dirty method simultaneously producing fertilizer of excrement and its device using stalk.
Background technology
Since reform and opening-up, China's agricultural production there occurs great variety, has liberated agricultural productive force, improves product
Amount, but agricultural production also brings agricultural pollution problem.A large amount of straw refuses of planting industry, the substantial amounts of feces of aquaculture are dirty
Water, is the big polluter of agricultural production two, and crop straw burning, feces are piled up, sewage crossing current, seriously pollute environment, endanger people
Health.
1st, the dirty pollution of aquaculture excrement and treatment status
Aquaculture integrated production capacity significantly increases, and livestock products total output is substantially improved, animal products structure successive optimization,
Livestock rearing pattern raises the intensive culture Mode change to high productivity for the pattern scattered from the peasant household of the low productivity, defines area
The Production of Livestock and Poultry layout in domain.But in Pollution from livestock and poultry preventing and controlling starting evening, starting point is low, and the fundamentals of management is weak, with scale
The fast-developing serious of livestock and poultry cultivation disconnects.Contradiction between animal husbandry and environmental conservation, Pollution from livestock and poultry becomes
Important content for widespread pollution from the overuse of fertilizers and pesticides in rural area and water environment pollution.
Livestock and poultry cultivation is specialized to concentrate feeding manner with scale, is conducive to improving breeding technology, pest resistance and management
Level, be peasant household's dispersion raising with traditional approach compared with, large-scale breeding is greatly improved production efficiency and feed conversion rate, fall
Low production cost, increases economic benefit.But poultry large-scale breeding also results in fecaluria concentrations and flushing water substantial increase, gives
Ecological environment brings enormous pressure.Dirty to 23, whole nation province (area), city's scale animal and poultry cultivation industry according to State Environmental Protection Administration
Dye status investigation shows, feces of livestock and poultry yield is 2.4 times of industrial solid castoff yield, feces of livestock and poultry COD
(COD) considerably beyond China's industrial wastewater and sanitary sewage COD discharge capacity sum.At present, the scale ginseng of livestock and poultry cultivation
Difference is uneven, and on a small scale and raise cultivation scattered and still occupy sizable proportion, the difficulty polluting improvement increases.Between time domain
Greatly, the animal number in existing soil is extremely uneven for livestock and poultry cultivation amount diversity.The pollution that many areas livestock and poultry cultivation brings is
Through or becoming local environment primary pollution source.
Prevent and treat aspect in Pollution from livestock and poultry, taken the lead by Chinese Ministry of Environmental Protection and put into effect many standards and norms texts, such as《Poultry
Aquaculture pollutant emission standard (GB18596-2001)》《Livestock and poultry breeding industry waste treatment project technical specification (HJ497-
2009)》Deng, specify that discharge standard and feces of farm treatment technology technique of Pollution from livestock and poultry thing etc., but still scarce
Weary practical, operating cost is low, high treating effect, Pollution from livestock and poultry Prevention Technique applied widely or pattern.
And from the point of view of according to various places excrement dirt administration project, treatment for cow manure Facilities Construction many with biogas engineering, three separate one purify,
Fermentation bed is main contents, but all there is limitation it is impossible to thoroughly solve excrement dirt problem.As biogas engineering lacks post processing, have
If biogas slurry and the biogas residue improving soil beneficial to crop growth utilize improper meeting severe contamination farmland and soil, and most cultivation
Field rebuilds light pipe, and facility operation easily sends out fault;Cleaning equipment needs 24h to run, and power consumption is big, and operating cost is high;Fermentation bed takes up an area face
Long-pending big, it is not suitable for nervous area in soil etc..Meanwhile, the construction of Pollution treatment installation and operating cost make most plants powerless
Undertake, " qualified discharge " pattern is not only difficult to solve the problems, such as Livestock Production Pollution, also feces of livestock and poultry resource can be caused to waste.
2nd, the pollution of straw and utilize present situation;
According to 16.5 hundred million mu of statistics China grain acreage, 4.67 hundred million tons of total output of grain, compare 1: 1.2 by grain stalk
Estimation, along with other crop materials, produces nearly 600,000,000 tons of straw, Chinese farmers are long using having to crop material in national year
History, only because the past level of agricultural production is low, yield poorly, straw quantity is few, and straw removes and is used for packing ring on a small quantity, feeds domestic animal
Poultry, partly makes compost outer, major part is all burnt as fuel for heap.With the development of agricultural production, China was from 80 years 20th century
Since generation, grain yield is greatly improved, and straw quantity increases therewith, adds the popularization of firewood-saving and coal-saving technology, burns coal, electricity consumption and makes
With the popularization of liquefied gas, make in rural area, there is straw of having more than needed in a large number.Rural area is reduced to the demand of straw, being treated as of a large amount of straws
One serious social problem is although law bans, but much local peasant still direct burning straws in the fields, cause
Air pollution, fire, aircraft cannot the consequence such as Normal Take-Off And Landing.The progress of science and technology simultaneously, the raising of level of farming mechanization,
Make straw is changed into straw directly returning to field using being made compost by original heap.
Numerous scientific workers have carried out fruitful research, straw Edible Fungi, biomass fuel to straw utilization
The modes such as material, straw building materials make use of a large amount of straws.But straw-returning is main aspect, straw-returning has compost also field, crosses abdomen
Also field, the various ways such as direct returning to farmland.Substantial amounts of organic matter, N P and K and trace element is contained, according to Zhang Fudao et al. in straw
Statistics, legume straw is nitrogenous more, and gramineous crop straw contains that potassium is abundanter, during the nutrient that crop material provides accounts for
The 13%~19% of state's fertilizer total nutrient, is the important organic fertilizer resource of agricultural production.From existing straw Production rate, 600,000,000
In ton straw, npk nutrient content is equivalent to more than 400 ten thousand tons of carbamide, more than 700 ten thousand tons of calcium superphosphate, more than 700 ten thousand tons of potassium sulfate.
But because peasant cultivates custom, geographical conditions, using reasons such as costs, a large amount of straws are not obtained by existing mode.
Invent new excrement dirt Treatment process pattern, inexpensive, simple and practical equipment, by the two of agricultural production big polluter
Combined Treatment, produces the high-quality organic fertilizer of planting industry while pollution administration, realizes the recycling of garbage, have
Necessity and urgency.
Content of the invention
In forest surface ecosystems, forest earth's surface self-assembling formation dry branches and fallen leaves, soil, the ecosystem of microbial bacteria
System, the fecaluria of animal, rainwater is by the ecosystem absorption of earth's surface, filtration, fermentative degradation, moisture evaporation.
Not enough problem for above-mentioned existing treatment for cow manure technology devises the present invention, and it is ecological that the present invention imitates forest earth's surface
System, tentatively filters excrement dirt using the thick straw of Organic substance, selects the strong Organic substance of adsorptivity and mixture of inorganic substance material further
Do filtrate, adsorption filtration sewage, organic materials fermentation evaporation sewage, the filtrate after use and the preliminary solid-state feces filtering and obtaining
The method and apparatus being fermented into fertilizer.The method includes for liquid excrement dirt (solidss < 5%) being transported to thick straw filtrate mistake
Tentatively filter in filter position, filtrate adds zymocyte, then spray in the first mixing media filtration storehouse and filter, gained filtrate enters one
Step spray is filtered in the second thin mixing media filtration storehouse, and gained filtrate is transported to ooze soon and purifies in sand filter as middle water
Reuse;Or dirty for semisolid excrement and sticky excrement slurry (30% >=solidss >=5%) is transported to filtration in thick straw media filtration storehouse,
Filtrate adds zymocyte, then filtrate is sprayed multiple mixing filtrate fermentation cabin, the filtrate hot fermentation of absorption effluent, sewage
By high temperature evaporation, sewage " zero-emission ";By thick straw media filtration storehouse filtrate, mixing filtrate fermentation cabin fermentation after filtrate and
Solid-state feces mixing on thick straw filtrate, sends into fertilizer main fermentation storehouse and carries out hot fermentation.
According to one embodiment of the invention, provide a kind of utilization with straw for main Feedstock treating liquid excrement dirt simultaneously
The method producing fertilizer, the method comprises the following steps:
(A) by solid contents<The liquid excrement dirt of 5 mass % is transported to the thick straw media filtration using thick straw filtrate
In storehouse, filtered using the thick straw filtrate in thick straw media filtration storehouse, filtrate is collected in the first sewage collecting pool, its
In the particle diameter of thick straw be 1-5cm, the thickness of straw filtering layer is 10-150cm (preferably 30-100cm, more preferably 40-60cm);
(B) add fermentation in the first sewage collecting pool with biological bacteria (such as sewage EM compound biological bacterium, effective viable bacteria
≥5.0×109Cfu), then spray (for example utilizing sludge pump), on the mixing filtrate in the first mixing media filtration storehouse, utilizes
Mixing media filtration, filtrate is collected in the second sewage collecting pool,
Described first mixing filtrate includes organic materials and inorganic material, and described organic materials can be selected for dry branches and fallen leaves, straw
Stalk or wood flour, preferably straw, described organic materials particle diameter<1cm (such as particle size range 0.01-0.99cm);Described inorganic material
From clay, bentonite, native flyash, preferably bentonite, described inorganic material particle diameter 80 300 mesh, preferably 200 mesh;Described
Inorganic material volume accounts for the 5%--20% of total volume of material, and preferably 10%;Described first mixing filtrate thickness is 100-300cm,
Preferably 150cm-250cm;
(C) sewage collecting step (B) sprays on the mixing filtrate in the second mixing media filtration storehouse, using mixing filter
Material filters, and filtrate is collected in the 3rd sewage collecting pool,
Described second mixing filtrate is identical with the described first mixing filtrate component;
(D) by the sewage transport collected in the 3rd sewage collecting pool to oozing purification in sand filter soon, after purification, sewage is through disappearing
Malicious (such as disinfection by ultraviolet light) is as Treated sewage reusing;
(E) by the thick straw filtrate in thick straw media filtration storehouse, the first mixing media filtration storehouse and the second mixing filtrate
Solid-state feces mixing on mixing filtrate and thick straw filtrate in filtering cabin, sends into fertilizer main fermentation storehouse and carries out 50-80 DEG C
Hot fermentation, after fermentation pack pile up (for example in greenhouse or hot house, ambient temperature 20-40 DEG C), ferment in second time, obtain
Obtain fertilizer.
In the present embodiment, for the preliminary mistake in liquid excrement dirt (solidss < 5%) liquid excrement soiled ends thick straw filtrate storehouse
Filter, two mixing filtrate storehouses are filtered further, and sewage purification is as Treated sewage reusing.Mainly utilize fracture filtration between filtering material particle dirty
Water.
Preferably, thick straw media filtration storehouse is often filtered 12 hours and is changed 1/2nd materials, the first thin mixing filtrate
Filtering cabin and the second thin every 12 hours in media filtration storehouse that mix change 1/5th materials.
Preferably, using sludge pump respectively to thick straw media filtration storehouse, the first mixing media filtration storehouse and the second mixing
Coating liquid excrement dirty or sewage flow in media filtration storehouse is 2-20 cube m/h, more preferably 5-10 cube m/h.
Preferably, add 1kg/m for the first time to the first sewage collecting pool3Sewage, adds 0.1kg/m later daily3Sewage EM
Compound biological bacterium, effective viable bacteria >=5.0 × 109cfu.
Described hot fermentation be solid-state feces with filter after filtrate by volume 1:0.3-10, preferably 1:0.5-5, more preferably
1:1-4, such as 1:1 mix and blend, is warmed up to 50-60 DEG C for 1-2 days, e.g., from about 55 DEG C, air blast cooling when reaching more than 70 DEG C, dimension
Hold 5-10 days, e.g., from about 7 days.The preferred 30-80% of humidity, more preferably 50%-60% in fermentation cabin, ph value in 6.5-8.5, preferably
Between 7-8.
Described ferment in second time:30-50 days, preferably from about 40 days, intermittent aeration, temperature no longer raises, and fermentation finishes.
The middle water of step (D) meets COD150-300mg/ liter, BOD80-150mg/ liter, SS100-200mg/ liter, ammonia nitrogen
12-30mg/ liter, TP5-10mg/ liter, 1000/100ml of excrement colibacillus group <, roundworm egg < 2/liter.
Gained fertilizer meets organic fertilizer (NY525-2002) standard:
Organic >=30%,
N+P2O5+K >=5, moisture<20%, pH value 5.5 8.0,
Content of beary metal in organic fertilizer, induced worm egg death rate and colititre index should meet wanting of GB8172
Ask.
According to the second embodiment of the present invention, a kind of imitative forest surface ecosystems are provided to process liquid excrement dirt simultaneously
Produce the device of fertilizer, this device includes:
Thick straw media filtration storehouse, the particle diameter of the thick straw of thick straw media filtration storehouse filling is 1-5cm, straw filtering layer
Thickness be 10-150cm (preferably 30-100cm, more preferably 40-60cm),
The first sewage collecting pool connecting with thick straw media filtration storehouse bottom filtrate (liquid,
Mix media filtration storehouse by pipeline is connected with the first sewage collecting pool first,
The second sewage collecting pool connecting with the first mixing media filtration storehouse bottom filtrate (liquid,
Mix media filtration storehouse by pipeline is connected with the second sewage collecting pool second,
First mixing media filtration storehouse and the filtrate of the second mixing media filtration storehouse filling;Described first mixing filtrate includes
Organic materials and inorganic material, described organic materials can be selected for dry branches and fallen leaves, straw or wood flour, preferably straw, described Organic substance
Material particle diameter<1cm (such as particle size range 0.01-0.99cm);Described inorganic material selects clay, bentonite, native flyash, preferably
Bentonite, described inorganic material particle diameter 80 300 mesh, preferably 200 mesh;Described inorganic material volume accounts for total volume of material
5%--20%, preferably 10%;Described first mixing filtrate thickness is 100-300cm, preferably 150cm-250cm;
Described second mixing filtrate is identical with the described first mixing filtrate component;
The 3rd sewage collecting pool connecting with the second mixing media filtration storehouse bottom filtrate (liquid,
Sand filter is oozed soon with the 3rd sewage collecting pool is connected by pipeline,
The clear water reserviors being connected with the lower part outlet oozing sand filter soon,
For by the solid-state feces on thick straw filtrate and thick straw filtrate, the fertilizer main fermentation mixing filtrate fermentation
Storehouse.
Further preferably include greenhouse or the hot house for material after the fermentation of main fermentation storehouse is carried out with ferment in second time.
The structure in thick straw media filtration storehouse includes a warehouse, and the straw filtrate charging port positioned at warehouse top and excrement are dirty
Charging aperture, and optionally it is provided with overfall, positioned at upper strata V-arrangement filter plate and lower floor's V-arrangement filter plate of warehouse bottom, positioned at the filter of upper strata V-arrangement
Filter material layer between plate and lower floor's V-arrangement filter plate, warehouse bottom is the Lower Hold of closing, and is provided with filtrate (liquid, in addition under warehouse
Portion is provided with spiral discharging machine.
Main fermentation storehouse, first mixing media filtration storehouse, second mixing media filtration storehouse (filtrate fermentation fermentation cabin) structure can
With identical, including a warehouse, warehouse top is provided with deodorization cover, is optionally provided with shower (main fermentation storehouse below deodorization cover
Due to not using sewage to spray, shower therefore can not be set), it is material bed below shower, material bed is down V-arrangement filter plate, V
It is the Lower Hold of closing below shape filter plate, below V-arrangement filter plate, is additionally provided with blast pipe, for lowering the temperature to air blast in warehouse, in V-arrangement filter
The bottom of plate, material bed lower section are provided with spiral discharging machine, are provided with straw charging aperture on warehouse top, are provided with the Lower Hold of closing
Filtrate (liquid.
According to the third embodiment the present invention, provide a kind of imitative forest surface ecosystems process semisolid excrement dirty and
The method that sticky excrement slurry produces fertilizer simultaneously, the method comprises the following steps:
(A) by 5 mass %≤solid contents<The sticky excrement slurry of 10 mass % and 10 mass %≤solids content≤30 matter
The semisolid excrement dirt of amount % is transported to using in the thick straw media filtration storehouse of thick straw filtrate, using thick straw media filtration storehouse
In thick straw filtrate filtered, the particle diameter of wherein thick straw is 1-5cm, and the thickness of straw filtering layer is that 10-150cm is (excellent
Select 30-100cm, more preferably 40-60cm);
(B) filtrate that step (A) obtains introducing biofermentation bacterium, (live by such as fertilizer specific complex beneficial bacteria powder
Bacterium sum >=1.0 × 109Cfu/g) to the mixing filter material layer spray in filtrate fermentation cabin, in filtrate fermentation cabin, organic matter fermentation produces
Raw biological heat energy evaporation and concentration sewage, this sewage also sprays to filter material layer in filtrate fermentation cabin after leachate collection pool collection,
Described mixing filtrate include organic materials and inorganic material, described organic materials can be selected for dry branches and fallen leaves, straw or
Wood flour, preferably straw, described organic materials particle diameter<1cm (such as particle size range 0.01-0.99cm);Described inorganic material is selected
Clay, bentonite, native flyash, preferably bentonite, described inorganic material particle diameter 80 300 mesh, preferably 200 mesh;Described inorganic
Volume of material accounts for the 5%--20% of total volume of material, and preferably 10%;Described first mixing filtrate thickness is 100-300cm, preferably
150cm-250cm;
Described second mixing filtrate is identical with the described first mixing filtrate component;
(C) by the mixing filtrate in thick straw filtering storehouse, filtrate fermentation cabin, the solid-state feces mixing on thick straw, enter
Main fermentation storehouse, carries out 50-80 DEG C of hot fermentation, packs accumulation at ambient temperature (for example big in greenhouse or plastics after fermentation
In canopy, ambient temperature 20-40 DEG C), ferment in second time, obtain fertilizer.
In the present embodiment, (5 mass %≤solids content≤30 mass %) are starched for semisolid excrement is dirty with excrement, excrement is dirty
Tentatively filter through thick straw filtrate storehouse, filter the sewage obtaining and spray multiple mixing filtrate fermentation cabin fermentations, heat of fermentation steams
Send out and concentrate sewage, sewage " zero-emission ".The main internal surface area absorption effluent larger using mixing filtrate itself, mixing filtrate is inhaled
Attached height (N) concentration sewage, in fermentation cabin, can maintain 50- for example under 70-99%, preferably more than 80% high humidity
60 DEG C, such as 55 DEG C of hot fermentation 20-40 days, e.g., from about 28 days, 20--30 kilogram of sewage of every cubic metre of evaporation daily.Mixing
Filtrate has this feature and could evaporate sewage.
Preferably, described hot fermentation be solid-state feces with filter after filtrate by volume 1:0.3-10, preferably 1:0.5-
8, more preferably 1:3-5, such as 1:4 mix and blends, are warmed up to 50-60 DEG C for 1-2 days, e.g., from about 55 DEG C, reach drum when more than 70 DEG C
Wind is lowered the temperature, maintenance 5-10 days, e.g., from about 7 days.The preferred 30-80% of humidity, more preferably 50%-60% in fermentation cabin, ph value exists
Between 6.5-8.5, preferably 7-8.
Preferably, the filtrate fermentation in described filtrate fermentation cabin is to be warmed up within 12 days more than 55 DEG C, rouses when more than 70 DEG C
Wind is lowered the temperature.Stalk fermentation preferably under the conditions of humidity 60-90%, preferably 70%-80% maintain 20-40 days, preferably from about 28 days
Hot fermentation.Often found 20 30 liters of sewage of the daily evaporation process of straw.
Preferably, disposably add 3kg fertilizer specific complex beneficial bacteria powder to filter sewage collecting pit, total viable count >=
1.0 × 109cfu/g, adds 0.1kg later daily.
Described ferment in second time:30-50 days, preferably from about 40 days, intermittent aeration, temperature no longer raises, and fermentation finishes.
Gained fertilizer meets fertilizer (NY525-200) standard:
Organic matter >=30%, N+P2O5+K >=5.Moisture<20%, pH value 5.5 8.0;
Content of beary metal in organic fertilizer, induced worm egg death rate and colititre index should meet wanting of GB8172
Ask.
According to the 4th embodiment of the present invention, provide a kind of imitative forest surface ecosystems process semisolid excrement dirty and
Sticky excrement slurry produces the device of fertilizer simultaneously, and this device includes:
Thick straw media filtration storehouse, the particle diameter of the thick straw of thick straw media filtration storehouse filling is 1-5cm, straw filtering layer
Thickness be 10-150cm (preferably 30-100cm, more preferably 40-60cm),
The filtrate collecting pit connecting with thick straw media filtration storehouse bottom filtrate (liquid,
The one or more mixing filtrate fermentation cabin being connected with filtrate collecting pit by pipeline,
The leachate collection pool connecting with one or more mixing filtrate fermentation cabin bottoms filtrate (liquid, leachate collection pool
It is provided with the pipeline for percolate in leachate collection pool being sprayed one or more mixing filtrate fermentation cabin,
The mixing filtrate of filling in mixing filtrate fermentation cabin:Wherein mixing filtrate Organic substance select dry branches and fallen leaves, straw,
Wood flour etc., preferably straw, particle diameter<1cm (such as particle size range 0.01-0.99cm);Inorganic matters select clay, swelling, native fine coal
Ash etc., preferably bentonite, particle diameter 80 300 mesh, preferably 200 mesh;Inorganic material volume accounts for the 5%--20% of total volume of material,
Preferably 10%;Mixing filtrate thickness is 100-300cm, preferably 150cm-250cm;
For by the solid-state feces on thick straw filtrate and thick straw filtrate, the fertilizer master that mixes the fermentation of filtrate filtrate sends out
Ferment storehouse.
Further preferably include greenhouse or the plastics for material after the fermentation of fertilizer main fermentation storehouse is carried out with ferment in second time
Booth.
The structure in thick straw media filtration storehouse includes a warehouse, positioned at straw filtrate charging port and the overflow on warehouse top
Mouthful, positioned at upper strata V-arrangement filter plate and lower floor's V-arrangement filter plate of warehouse bottom, between upper strata V-arrangement filter plate and lower floor's V-arrangement filter plate
Filter material layer, warehouse bottom is the Lower Hold of closing, and is provided with filtrate (liquid, is in addition provided with spiral discharging machine in warehouse bottom.
Fertilizer main fermentation storehouse, mixing filtrate fermentation chamber structure can be identical, including a warehouse, warehouse top is provided with removes
Smelly cover, (main fermentation storehouse, due to not using sewage to spray, therefore can not set spray to be optionally provided with shower below deodorization cover
Pipe), it is material bed below shower, the material bed lower Lower Hold being V-arrangement filter plate, being closing below V-arrangement filter plate, under V-arrangement filter plate
Side is additionally provided with blast pipe, for lowering the temperature to air blast in warehouse, is provided with spiral discharging in the bottom of V-arrangement filter plate, material bed lower section
Machine, is provided with mixing filtrate charging aperture on warehouse top, is provided with filtrate (liquid in the Lower Hold of closing.
Instant invention overcomes the deficiency of prior art pattern, with cheap natural material as raw material, there is provided a kind of thick straw
Media filtration storehouse, mixes filtrate fermentation cabin, fertilizer main fermentation storehouse combined system, using Treated sewage reusing and sewage " zero-emission " two
The pattern of kind, produces high-quality fertilizer while processing excrement dirt.The present invention has disposal organic waste and realizes minimizing, stablizes
Change, innoxious, resource feature, fermentation cabin closed-loop operation, floor space is less, and this system has and can automatically be entered simultaneously
Discharging, forced aeration, temperature control, the feature of vent gas treatment.
Compared with prior art pattern, the invention has the advantages that:
(I) present invention realizes comprehensive utilization of resources, and straw, feces, sewage organic waste pollutant are converted into humus,
The composting production producing is as Fertilizer application it is achieved that recycling.The pollutant combined greatly improvement in rural area two, has preferably
Environmental benefit, Social benefit and economic benefit, promising in big-and-middle-sized livestock and poultry cultivation night soil sewage disposal.
(2) while organic solid waste gurry stover is fertilizer by the present invention, and using generation in course of reaction
Biological heat energy evaporates sewage, realizes " the zero-emission of sewage.”
(3) present invention employs airtight fermentation cabin, reduce foul waste gas and produce, and purified by emission-control equipment useless
Gas, qualified discharge, reduces the impact to surrounding.
(4) production process of the present invention is carried out in hot house, make use of warming solar energy heat, energy saving same
When, closure designs reduce the pollution to environment for the foul waste gas.
(5) low cost of the present invention, combination flexibly, is suitable for various treatment for cow manure and requires, result is preferable, easily promote.
Brief description
Fig. 1 is that a kind of imitative forest surface ecosystems of the present invention process the dirty device simultaneously producing fertilizer of liquid excrement
Schematic diagram.
1st, thick straw media filtration storehouse;2nd, the first mixing media filtration storehouse;3rd, the second mixing media filtration storehouse;4th, ooze sand soon
Filter tank;5th, clear water reserviors;6th, the first sewage collecting pool;7th, the second sewage collecting pool, the 8, the 3rd sewage collecting pool;9th, main fermentation storehouse;
10th, main fermentation storehouse;11st, spiral discharging machine, 12, excrement dirt charging aperture;13rd, overfall;14th, shower;15th, water regulating valve.
Fig. 2 is that a kind of imitative forest surface ecosystems process semisolid excrement dirty and sticky excrement slurry production simultaneously of the present invention has
The schematic diagram of the fertile device of machine.
30th, thick straw media filtration storehouse;31st, mix filtrate fermentation cabin;32;Mixing filtrate fermentation cabin;33rd, leachate collection
Pond;34th, fertilizer main fermentation storehouse;35th, fertilizer main fermentation storehouse;36th, filtrate collecting pit;37th, excrement dirt (or excrement slurry) charging aperture;
38th, overfall;39th, spiral discharging machine;40th, liquid measure regulating valve;41st, Back Water Valve.
Fig. 3 is thick straw filter material filtering basin structural representation.
100th, thick straw media filtration storehouse warehouse;101st, excrement pollution layer;102nd, upper strata V-arrangement filter plate;103rd, straw filter material layer;
104th, lower floor's V-arrangement filter plate;105th, the Lower Hold of closing;106th, filtrate (liquid;107th, spiral discharging machine;108th, straw filtrate filling
Mouthful;109 excrement dirt charging apertures.
Fig. 4 be mixing filtrate fermentation cabin (fertilizer main fermentation storehouse or first mixing media filtration storehouse or second mixing filter
Material filtering cabin) structural representation.
200th, mix filtrate fermentation cabin warehouse;201st, deodorization cover;202nd, shower;203rd, mix filtrate charging aperture;204、
Mixing filtrate fermentation layer;205th, V-arrangement filter plate;206th, blast pipe;207th, the Lower Hold of closing;208th, filtrate (liquid;209th, spiral goes out
Material machine.
Fig. 5 is that the mixing filtrate fermentation cabin of the 4th embodiment of the present invention arranges schematic diagram.
31st, mix filtrate fermentation cabin;32;Mixing filtrate fermentation cabin;45th, mix filtrate charging aperture;46th, heliogreenhouse aerofluxuss
Mouthful;201st, deodorization cover;202nd, shower;206th, blast pipe;208th, filtrate (liquid.
Specific embodiment
To describe the specific embodiment of the present invention below in conjunction with accompanying drawing in detail.
Fig. 1 show a kind of utilization stalk and processes the dirty device simultaneously producing fertilizer of liquid excrement, and this device includes:
Thick straw media filtration storehouse 1, the particle diameter of the thick straw of thick straw media filtration storehouse filling is 1-5cm, straw filtering
The thickness of layer is 10-150cm (preferably 30-100cm, more preferably 40-60cm),
The first sewage collecting pool 6 connecting with thick straw media filtration storehouse bottom filtrate (liquid,
Mix media filtration storehouse 2 by pipeline is connected with the first sewage collecting pool 6 first,
The second sewage collecting pool 7 connecting with the first mixing media filtration storehouse bottom filtrate (liquid,
The second thin mixing media filtration storehouse 3 being connected with the second sewage collecting pool 7 by pipeline,
First mixing media filtration storehouse 2 and the mixing filtrate of the second mixing media filtration storehouse 3 filling:Wherein mix filtrate
Organic substance selects dry branches and fallen leaves, straw, wood flour etc., preferably straw, particle diameter<1cm (such as particle size range 0.01-0.99cm);No
Machine thing selects clay, swelling, native flyash etc., preferably bentonite, particle diameter 80 300 mesh, preferably 200 mesh;Inorganic material volume
Account for the 5%--20% of total volume of material, preferably 10%;Mixing filtrate thickness is 100-300cm, preferably 150cm-250cm;
The 3rd sewage collecting pool 8 connecting with the second mixing media filtration storehouse bottom filtrate (liquid,
Sand filter 4 is oozed soon with the 3rd sewage collecting pool 8 is connected by pipeline,
The clear water reserviors 5 being connected with the lower part outlet oozing sand filter soon,
For by the solid-state feces on thick straw filtrate and thick straw filtrate, the fertilizer main fermentation storehouse mixing filtrate fermentation
9、10.
Further preferably include greenhouse or the hot house (figure for material after the fermentation of main fermentation storehouse is carried out with ferment in second time
Not shown in).
Straw filter as shown in figure 3, the structure in thick straw media filtration storehouse includes a warehouse 100, positioned at warehouse top
Material charging port 108 and excrement dirt charging aperture 109, positioned at upper strata V-arrangement filter plate 102 and lower floor's V-arrangement filter plate 104 of warehouse bottom, are located at
Straw filter material layer 103 between upper strata V-arrangement filter plate and lower floor's V-arrangement filter plate, is excrement pollution layer 101 on upper strata V-arrangement filter plate 102, storehouse
Body bottom is the Lower Hold 105 of closing, and is provided with filtrate (liquid 106, is in addition provided with spiral discharging machine 107 in warehouse bottom.
As shown in figure 4, mixing filtrate fermentation cabin can serve as fertilizer main fermentation storehouse, first mixing media filtration storehouse or
Second mixing media filtration storehouse, including a warehouse 200, warehouse top is provided with deodorization cover 201, optionally sets below deodorization cover
There is shower 202 (main fermentation storehouse, due to not using sewage to spray, therefore can not set shower), be material bed below shower
204, the material bed lower Lower Hold 207 being V-arrangement filter plate 205, below V-arrangement filter plate being closing, it is additionally provided with blast pipe below V-arrangement filter plate
206, for lowering the temperature to air blast in warehouse, it is provided with spiral discharging machine 209 in the bottom of V-arrangement filter plate, material bed lower section, in warehouse
Top is provided with straw charging aperture 203, is provided with filtrate (liquid 208 in the Lower Hold of closing.
Process the dirty side simultaneously producing fertilizer of liquid excrement using a kind of imitative forest surface ecosystems of Fig. 1 shown device
Method comprises the following steps:
(A) by solid contents<The liquid excrement dirt of 5 mass % is transported to the thick straw media filtration using thick straw filtrate
In storehouse, filtered using the thick straw filtrate in thick straw media filtration storehouse, filtrate is collected in the first sewage collecting pool, its
In the particle diameter of thick straw be 1-5cm, the thickness of straw filtering layer is 10-150cm (preferably 30-100cm, more preferably 40-60cm);
(B) add fermentation in the first sewage collecting pool with biological bacteria (such as sewage EM compound biological bacterium, effective viable bacteria
≥5.0×109Cfu), then spray (for example utilizing sludge pump) to the mixing filtrate in the first mixing filtrate media filtration storehouse,
Using mixing media filtration, filtrate is collected in the second sewage collecting pool, mixes filtrate filtrate:Wherein mix the Organic substance of filtrate
From dry branches and fallen leaves, straw, wood flour etc., preferably straw, particle diameter<1cm (such as particle size range 0.01-0.99cm);Inorganic matters select
With clay, swelling, native flyash etc., preferably bentonite, particle diameter 80 300 mesh, preferably 200 mesh;Inorganic material volume accounts for total thing
The 5%--20% of material volume, preferably 10%;Mixing filtrate thickness is 100-300cm, preferably 150cm-250cm
(C) sewage collecting step (B) sprays on the thin straw filtrate in the second thin mixing media filtration storehouse, using mixed
Close media filtration, filtrate is collected in the 3rd sewage collecting pool;
(D) by the sewage transport collected in the 3rd sewage collecting pool to oozing purification in sand filter soon, after purification, sewage is through disappearing
Malicious (such as disinfection by ultraviolet light) is as Treated sewage reusing;
(E) by the thick straw in thick straw media filtration storehouse, the first mixing media filtration storehouse and the second mixing media filtration storehouse
Solid-state feces mixing on stalk filtrate and mixing filtrate and thick straw filtering storehouse, sends into fertilizer main fermentation storehouse and carries out 50-80 DEG C
Hot fermentation, after fermentation pack pile up (for example in greenhouse or hot house, ambient temperature 20-40 DEG C), ferment in second time, obtain
Obtain fertilizer.
In the above-mentioned methods, tentatively filter for liquid excrement dirt (solidss < 5%) liquid excrement soiled ends thick straw filtrate storehouse,
Two mixing media filtration storehouses are filtered further, and sewage purification is as Treated sewage reusing.Hole between the main filtering material particle using mixing
Filter sewage.
Preferably, thick straw media filtration storehouse is often filtered 12 hours and is changed 1/2nd materials, the first thin straw filtrate
Every 12 hours of filtering cabin and the second thin straw media filtration storehouse change 1/5th materials.
Preferably, using sludge pump respectively to thick straw media filtration storehouse, the first mixing media filtration storehouse and the second mixing
Coating liquid excrement dirty or sewage flow in media filtration storehouse is 2-20 cube m/h, more preferably 5-10 cube m/h.
Preferably, add 1kg/m for the first time to the first sewage collecting pool3Sewage, adds 0.1kg/m later daily3Sewage EM
Compound biological bacterium, effective viable bacteria >=5.0 × 109cfu.
Described hot fermentation be solid-state feces with filter after mix filtrate by volume 1:0.3-10, preferably 1:0.5-5, more
Preferably 1:1-4, such as 1:1 mix and blend, is warmed up to 50-60 DEG C for 1-2 days, e.g., from about 55 DEG C, air blast fall when reaching more than 70 DEG C
Temperature, maintenance 5-10 days, e.g., from about 7 days.The preferred 30-80% of humidity, more preferably 50%-60% in fermentation cabin, ph value is in 6.5-
8.5, between preferably 7-8.
Described ferment in second time:30-50 days, preferably from about 40 days, intermittent aeration, temperature no longer raises, and fermentation finishes.
The middle water of step (D) meets COD150-300mg/ liter, BOD80-150mg/ liter, SS100-200mg/ liter, ammonia nitrogen
12-30mg/ liter, TP5-10mg/ liter, 1000/100ml of excrement colibacillus group <, roundworm egg < 2/liter.
Gained fertilizer meets organic fertilizer (NY525-2002) standard:
Organic >=30%,
N+P2O5+K >=5, moisture<20%, pH value 5.5 8.0,
Content of beary metal in organic fertilizer, induced worm egg death rate and colititre index should meet wanting of GB8172
Ask.
Fig. 2 shows that a kind of imitative forest surface ecosystems process semisolid excrement dirty and sticky excrement slurry and produce fertilizer simultaneously
Device, this device includes:
Thick straw media filtration storehouse 30, the particle diameter of the thick straw of thick straw media filtration storehouse filling is 1-5cm, straw filtering
The thickness of layer is 10-150cm (preferably 30-100cm, more preferably 40-60cm),
The filtrate collecting pit 36 connecting with thick straw media filtration storehouse bottom filtrate (liquid,
The one or more straw fermenting cabins 31,32 being connected with filtrate collecting pit by pipeline,
The leachate collection pool 33 connecting with one or more mixing filtrate fermentation cabin bottoms filtrate (liquid, leachate collection
Pond is provided with the pipeline for percolate in leachate collection pool sprays one or more mixing filtrate fermentation cabin, and this pipeline sets
There is Back Water Valve 41,
The mixing filtrate of filling in mixing filtrate fermentation cabin 31,32:Wherein mixing filtrate Organic substance select dry branches and fallen leaves,
Straw, wood flour etc., preferably straw, particle diameter<1cm (such as particle size range 0.01-0.99cm);Inorganic matters select clay, swelling, soil
Flyash etc., preferably bentonite, particle diameter 80 300 mesh, preferably 200 mesh;Inorganic material volume accounts for the 5%-- of total volume of material
20%, preferably 10%;Mixing filtrate thickness is 100-300cm, preferably 150cm-250cm;
For by the solid-state feces on thick straw filtrate and thick straw filtrate, the fertilizer main fermentation storehouse mixing filtrate fermentation
34、35.
Further preferably include greenhouse or the hot house (figure for material after the fermentation of main fermentation storehouse is carried out with ferment in second time
Not shown in).
Thick straw media filtration storehouse is identical with discussed above.
Fertilizer main fermentation storehouse, mixing filtrate fermentation chamber structure can be identical, a warehouse 200, warehouse top is provided with removes
Smelly cover 201, is optionally provided with shower 202 (fertilizer main fermentation storehouse due to not using sewage to spray, therefore below deodorization cover
Shower can not be set), it is material bed 204 below shower, material bed is V-arrangement filter plate 205 down, is closing below V-arrangement filter plate
Lower Hold 207, be additionally provided with blast pipe 206 below V-arrangement filter plate, for lowering the temperature to air blast in warehouse, the bottom of V-arrangement filter plate,
Material bed lower section is provided with spiral discharging machine 209, is provided with mixing filtrate charging aperture 203 on warehouse top, sets in the Lower Hold of closing
There is filtrate (liquid 208.
As shown in figure 5, mixing filtrate fermentation cabin can be arranged in heliogreenhouse.
Process semisolid excrement dirty and sticky excrement slurry using a kind of imitative forest surface ecosystems of the device of Fig. 2 to produce simultaneously
The method of fertilizer comprises the following steps:
(A) by 5 mass %≤solid contents<The sticky excrement slurry of 10 mass % and 10 mass %≤solids content≤30 matter
The semisolid excrement dirt of amount % is transported to using in the thick straw media filtration storehouse of thick straw filtrate, using thick straw media filtration storehouse
In thick straw filtrate filtered, the particle diameter of wherein thick straw is 1-5cm, and the thickness of straw filtering layer is that 10-150cm is (excellent
Select 30-100cm, more preferably 40-60cm);
(B) filtrate that step (A) obtains introducing biofermentation bacterium, (live by such as fertilizer specific complex beneficial bacteria powder
Bacterium sum >=1.0 × 109Cfu/g) to the filter material layer spray in mixing filtrate fermentation cabin, mixing filtrate in mixing filtrate fermentation cabin
Fermentation produces biological heat energy evaporation and concentration sewage, and this sewage is also thin in filtrate fermentation cabin to mixing after leachate collection pool collection
Filter material layer sprays, and mixes filtrate:The Organic substance of wherein mixing filtrate selects dry branches and fallen leaves, straw, wood flour etc., preferably straw, grain
Footpath<1cm (such as particle size range 0.01-0.99cm);Inorganic matters select clay, swelling, native flyash etc., preferably bentonite, grain
Footpath 80 300 mesh, preferably 200 mesh;Inorganic material volume accounts for the 5%--20% of total volume of material, and preferably 10%;Mixing filter material layer
Thick is 100-300cm, preferably 150cm-250cm;
(C) by the mixing filtrate in thick straw filtering storehouse, mixing filtrate fermentation cabin, the solid-state feces mixing on thick straw,
Enter fertilizer main fermentation storehouse, carry out 50-80 DEG C of hot fermentation, pack after fermentation and pile up (for example in temperature at ambient temperature
In room or hot house, ambient temperature 20-40 DEG C), ferment in second time, obtain fertilizer.
In the above-mentioned methods, (5 mass %≤solids content≤30 mass %) are starched for semisolid excrement is dirty with excrement, excrement soiled ends
Thick straw filtrate storehouse is tentatively filtered, and filters the sewage obtaining and sprays multiple mixing filtrate fermentation cabin fermentations, heat of fermentation evaporates
Concentrate sewage, sewage " zero-emission ".The main internal surface area absorption effluent larger using mixing filtrate itself, filtrate absorption is high
(N) concentration sewage, in fermentation cabin, can maintain 50-60 DEG C under preferably more than 80% high humidity, example in 70-99%
As 55 DEG C of hot fermentation 20-40 days, e.g., from about 28 days, 20--30 kilogram of sewage of every cubic metre of evaporation daily.Filtrate has this
The feature of kind could evaporate sewage.
Preferably, described hot fermentation be solid-state feces with filter after filtrate by volume 1:0.3-10, preferably 1:0.5-
8, more preferably 1:3-5, such as 1:4 mix and blends, are warmed up to 50-60 DEG C for 1-2 days, e.g., from about 55 DEG C, reach drum when more than 70 DEG C
Wind is lowered the temperature, maintenance 5-10 days, e.g., from about 7 days.The preferred 30-80% of humidity, more preferably 50%-60% in fermentation cabin, ph value exists
Between 6.5-8.5, preferably 7-8.
Preferably, the filtrate fermentation in described mixing filtrate fermentation cabin is to be warmed up within 12 days more than 55 DEG C, more than 70 DEG C
When air blast cooling.Filtrate ferments in maintenance 20-40 days preferably under the conditions of humidity 60-90%, preferably 70%-80%, preferably from about
28 days hot fermentations.Often found 20 30 liters of sewage of the daily evaporation process of filtrate.
Preferably, disposably add 3kg fertilizer specific complex beneficial bacteria powder to filter sewage collecting pit, total viable count >=
1.0 × 109cfu/g, adds 0.1kg later daily.
Described ferment in second time:30-50 days, preferably from about 40 days, intermittent aeration, temperature no longer raises, and fermentation finishes.
Gained fertilizer meets fertilizer (NY525-200) standard:
Organic matter >=30%, N+P2O5+K >=5.Moisture<20%, pH value 5.5 8.0;
Content of beary metal in organic fertilizer, induced worm egg death rate and colititre index should meet wanting of GB8172
Ask.
By the following specific examples further illustrate the invention.
Embodiment 1
200 pig farm treatment for cow manure of livestock on hand.Using the dry cleaning up excrement mode of production, every pig often produces solid-state feces round the clock
2.5 kilograms, urinate 3 liters, 4.5 liters of flushing water, 10 liters of excrement dirt mixed materials altogether, 200 vertical excrement of pig farm generation daily 2 are dirty, its
In 0.5 vertical solid-state feces, 1.5 vertical sewage, by often standing, mixing filtrate is daily to be processed 20 30 liters of sewage and calculates, and needs 50 75 to stand
Mixing filtrate ferments simultaneously.Using the device shown in Fig. 2, each feed bin 10 stands, and arranges filtering cabin 1, mixes filtrate fermentation cabin 7
Individual, feces filtrate mixing fertilizer fermentation cabin 2.Mixing filtrate fermentation cabin is disposably filled, and fermentation changed one in every 4 days after 28 days
Individual fermentation cabin filtrate, 28 days is a circulation, changes a fermentation cabin filtrate within every 4 days after 7 days.The filtrate changed and filtering cabin
Solid-state feces press 4:1 volume ratio mix and blend enters fertilizer main fermentation storehouse and carries out 55 DEG C of high temperature above fermentations in 7 days, thing after fermentation
Material dress woven bag is sent into hot house and is carried out ferment in second time.Consume straw 10 within every 4 days to stand, 1 vertical bentonite, consume straw daily
2.5 stand, and bentonite 0.25 stands, about 0.37 ton of straw, 0.3 ton of bentonite, and daily evaporation process sewage 1.5 stands.By 10 vertical fermentations
3 tons of material production fertilizer (moisture < 20%), averagely produces about 0.7 ton of fertilizer daily.
Embodiment 2
1000 pig farm treatment for cow manure of livestock on hand.
1st, adopt the first embodiment tupe:Rush the excrement mode of production for water, produce a large amount of liquid excrement dirts, adopted
Filtering method is processed, and mixing filtrate obtains solid-state feces mixed fermentation with filtering, and produces fertilizer.
Every pig often produces 2.5 kilograms of solid-state feces round the clock, urinates 3 liters, and pig farm rushes the excrement mode of production using water, 1000
Pig farm produces 50 vertical left and right excrement dirt (solid contents about 4%).For piggery waste situation, dirty using filtration excrement, Treated sewage reusing
Mode treatment.Using the device shown in Fig. 1,1, the thick straw filtering storehouse of setting, mix 2, media filtration storehouse, fertilizer (leading) is sent out
4, ferment storehouse.By rate of filtration 7.8m3/ h, daily filtration 6 hours about, the sewage filtering out is purified by rapid sand filter,
After water disinfection by ultraviolet light after purification, colony house is rinsed in reuse.By scheme one method, change within every two days filtrate, filtrate is obtained with filtration
Solid-state feces press 2:1 volume ratio mix and blend enters 7 days 55 DEG C of high temperature above fermentation fertilizers of fermentation cabin.Averagely consume straw daily
Stalk 2.5 stands, about 0.37 ton, and bentonite 0.25 stands, about 0.3 ton, filters excrement dirty 50 and stands, produces fertilizer (moisture < 20%) 1.5
Ton.
2nd, adopt the second embodiment tupe:For manually or mechanically do the cleaning up excrement mode of production, produce semisolid and
Excrement is starched, and is tentatively percolated using thick straw, filtrate in percolate spray mixing filtrate fermentation cabin, filtrate fermentation evaporation and concentration sewage,
Sewage " zero-emission " pattern.
Every pig often produces 2.5 kilograms of solid-state feces round the clock, urinates 3 liters, and 1 produces 10 liters of mixing excrement dirts, 1000 pig farms
The daily 10 vertical excrement that produce are dirty, wherein 2.5 vertical solid-state feces, and 7.5 vertical sewage process 20 30 liters of dirts daily by often founding mixing filtrate
Water calculates, and needs 250--375 to found mixing filtrate and ferments simultaneously.Using the device shown in Fig. 2, each feed bin 10 stands, configurating filtered
1, storehouse, 7, feces filtrate mixing fertilizer main fermentation storehouse, mix filtrate fermentation cabin 28.Mixing filtrate fermentation cabin is disposably filled out
Fill, fermentation changes a fermentation cabin filtrate after 28 days daily, be within 28 days a circulation, after feces and fermentation, filtrate presses 1:2 volumes
It is sequentially filled than mixed fermentation storehouse, after 7 days, changes a fermentation cabin material daily, be within 7 days a circulation.Daily consumption straw 10
Make treaty 1.5 tons, bentonite 1 stands, about 1.3 tons, produce 3 tons of fertilizer (moisture < 20%), daily evaporation process sewage 7.5 stands.
Embodiment 3
Small towns treatment for cow manure center.Livestock on hand live pig 20,000 is pressed in one small towns, 3000, non-irrigated lavatory, including other sanitary sewages,
Daily generation semisolid excrement is dirty and excrement slurry 300 stands.Using the device shown in Fig. 2, the built-in filtering cabin in thick straw filtering workshop is set
10,2, filtrate collection pond, each volume 300 stands;30 mixing filtrate fermentation plants, built-in 28 of each fermentation plant mixes
Close filtrate fermentation cabin, 7 fertilizer main fermentation storehouses, fermentation plant amounts to 35X30=105;Mixing media filtration cleaning shop 1
Individual, filtering cabin 5, each plant feed bin of total 120.Fecal suction truck collects excrement dirt, is tentatively filtered by thick straw filtering storehouse, and filtrate is received
Ji Chi collect filtrate, filtrate spray fermentation plant fermentation, unnecessary percolate by mix media filtration purification workshop purification process after
Do agricultural irrigation water to use.Processing center consumes straw 300 daily and stands, about 45 tons of straws, produces fertilizer (moisture <
20%) 90 100 tons, evaporation sewage 225 stands.
Claims (10)
1. a kind of imitative forest surface ecosystems process the dirty method simultaneously producing fertilizer of liquid excrement, and the method includes following step
Suddenly:
(A) by solid contents<The liquid excrement dirt of 5 mass % is transported to the thick straw media filtration storehouse using thick straw filtrate
In, filtered using the thick straw filtrate in thick straw media filtration storehouse, filtrate is collected in the first sewage collecting pool, wherein
The particle diameter of thick straw is 1-5cm, and the thickness of straw filtering layer is 10-150cm (preferably 30-100cm, more preferably 40-60cm);
(B) in the first sewage collecting pool add fermentation with biological bacteria (such as sewage EM compound biological bacterium, effective viable bacteria >=
5.0×109Cfu), then spray (for example utilizing sludge pump) is on the first mixing filtrate in the first mixing media filtration storehouse, sharp
With mixing media filtration, filtrate collects in the second sewage collecting pool, wherein said first mixing filtrate include organic materials with
Inorganic material, described organic materials can be selected for dry branches and fallen leaves, straw or wood flour, preferably straw, described organic materials particle diameter<1cm
(such as particle size range 0.01-0.99cm);Described inorganic material select clay, bentonite, flyash, preferably bentonite, described
Inorganic material particle diameter 80 300 mesh, preferably 200 mesh;Described inorganic material volume accounts for the 5%--20% of total volume of material, preferably
10%;Described first mixing filtrate thickness is 100-300cm, preferably 150cm-250cm;
(C) sewage collecting step (B) sprays on the thin straw filtrate in the second mixing media filtration storehouse, using the second mixing
Media filtration, filtrate is collected in the 3rd sewage collecting pool, and wherein said second mixing filtrate mixes filtrate group with described first
Split-phase is same;
(D) by the 3rd sewage collecting pool collect sewage transport to ooze soon in sand filter purify, the sterilized (example of sewage after purification
As disinfection by ultraviolet light) as Treated sewage reusing;
(E) by the mixing filtrate in thick straw media filtration storehouse, the first mixing media filtration storehouse and the second mixing media filtration storehouse
Mix with the solid-state feces on thick straw filtrate, send into the hot fermentation that fertilizer main fermentation storehouse carries out 50-80 DEG C, after fermentation
(for example in greenhouse or hot house, ambient temperature 20-40 DEG C) is piled up in pack, ferment in second time, obtains fertilizer.
2. method according to claim 1, wherein, adds 1kg/m for the first time to the first sewage collecting pool3Sewage, often later
It adds 0.1kg/m3Sewage EM compound biological bacterium, effective viable bacteria >=5.0 × 109cfu;
Or, wherein, using sewage pump respectively to thick straw media filtration storehouse, the first mixing media filtration storehouse and the second mixing filter
Dirty or sewage the flow of material filtering cabin coating liquid excrement is 2-20 cube m/h, more preferably 5-10 cube m/h;
Or, wherein, thick straw media filtration storehouse is often filtered 12 hours and is changed 1/2nd materials, the first mixing media filtration
Every 12 hours in storehouse and the second mixing media filtration storehouse change 1/5th materials;
Or, wherein, the time of described ferment in second time is 30-50 days, intermittent aeration.
3. method according to claim 1 and 2, wherein, described hot fermentation be solid-state feces with filter after filtrate by body
Amass and compare 1:0.3-10, preferably 1:0.5-5, more preferably 1:1-4, such as 1:1 mix and blend, is warmed up to 50-60 DEG C for 1-2 days, for example
About 55 DEG C, air blast cooling when reaching more than 70 DEG C, maintenance 5-10 days, e.g., from about 7 days.The preferred 30-80% of humidity in fermentation cabin, more
Preferably 50%-60%, ph value is between 6.5-8.5, preferably 7-8.
4. a kind of imitative forest surface ecosystems process the dirty device simultaneously producing fertilizer of liquid excrement, and this device includes:
Thick straw media filtration storehouse, the particle diameter of the thick straw of thick straw media filtration storehouse filling is 1-5cm, the thickness of straw filtering layer
Spend for 10-150cm (preferably 30-100cm, more preferably 40-60cm),
The first sewage collecting pool connecting with thick straw media filtration storehouse bottom filtrate (liquid,
Mix media filtration storehouse by pipeline is connected with the first sewage collecting pool first,
The second sewage collecting pool connecting with the first mixing media filtration storehouse bottom filtrate (liquid,
Mix media filtration storehouse by pipeline is connected with the second sewage collecting pool second,
First mixing media filtration storehouse and the mixing filtrate of the second mixing media filtration storehouse filling, described first mixing filtrate includes
Organic materials and inorganic material, described organic materials can be selected for dry branches and fallen leaves, straw or wood flour, preferably straw, described Organic substance
Material particle diameter<1cm (such as particle size range 0.01-0.99cm);Described inorganic material selects clay, bentonite, flyash, preferably swollen
Profit soil, described inorganic material particle diameter 80 300 mesh, preferably 200 mesh;Described inorganic material volume accounts for the 5%-- of total volume of material
20%, preferably 10%;Described first mixing filtrate thickness is 100-300cm, preferably 150cm-250cm;
Described second mixing filtrate is identical with the described first mixing filtrate component;
The 3rd sewage collecting pool connecting with the second mixing media filtration storehouse bottom filtrate (liquid,
Sand filter is oozed soon with the 3rd sewage collecting pool is connected by pipeline,
The clear water reserviors being connected with the lower part outlet oozing sand filter soon,
For by the solid-state feces on thick straw filtrate with thick straw filtrate, the fertilizer main fermentation that mixes filtrate co-fermentation
Storehouse.
5. device according to claim 4, it further includes for carrying out to material after the fermentation of fertilizer main fermentation storehouse
The greenhouse of ferment in second time or hot house,
Or, wherein, the structure in thick straw media filtration storehouse includes a warehouse, positioned at the straw filtrate charging port on warehouse top
The dirty charging aperture with excrement, and optionally it is provided with overfall, positioned at upper strata V-arrangement filter plate and lower floor's V-arrangement filter plate of warehouse bottom, positioned at upper strata
Filter material layer between V-arrangement filter plate and lower floor's V-arrangement filter plate, warehouse bottom is the Lower Hold of closing, and is provided with filtrate (liquid, in addition in storehouse
Body bottom is provided with spiral discharging machine;
Or, wherein, fertilizer main fermentation storehouse, the first mixing media filtration storehouse, the second mixing media filtration chamber structure are identical, respectively
From including a warehouse, warehouse top is provided with deodorization cover, is optionally provided with shower below deodorization cover, is thing below shower
The bed of material, the material bed lower Lower Hold being V-arrangement filter plate, below V-arrangement filter plate being closing, it is additionally provided with blast pipe below V-arrangement filter plate, be used for
Into warehouse, air blast cooling, is provided with spiral discharging machine in the bottom of V-arrangement filter plate, material bed lower section, is provided with straw on warehouse top
Stalk charging aperture, is provided with filtrate (liquid in the Lower Hold of closing.
6. a kind of imitative forest surface ecosystems process the method that semisolid excrement dirty and sticky excrement slurry produces fertilizer simultaneously, the party
Method comprises the following steps:
(A) by 5 mass %≤solid contents<The sticky excrement slurry of 10 mass % and 10 mass %≤solids content≤30 mass %
Semisolid excrement dirt be transported to using in the thick straw media filtration storehouse of thick straw filtrate, using in thick straw media filtration storehouse
Thick straw filtrate is filtered, and the particle diameter of wherein thick straw is 1-5cm, and the thickness of straw filtering layer is 10-150cm (preferably 30-
100cm, more preferably 40-60cm);
(B) (such as fertilizer specific complex beneficial bacteria powder, viable bacteria is total introducing biofermentation bacterium for the filtrate that step (A) obtains
Number >=1.0 × 109Cfu/g) to the filter material layer spray in mixing filtrate fermentation cabin, filtrate fermentation in mixing filtrate fermentation cabin produces
Biological heat energy evaporation and concentration sewage, this sewage is after leachate collection pool collection also to filter material layer spray in mixing filtrate fermentation cabin
Drench,
Described first mixing filtrate includes organic materials and inorganic material, described organic materials can be selected for dry branches and fallen leaves, straw or
Wood flour, preferably straw, described organic materials particle diameter<1cm (such as particle size range 0.01-0.99cm);Described inorganic material is selected
Clay, bentonite, flyash, preferably bentonite, described inorganic material particle diameter 80 300 mesh, preferably 200 mesh;Described inorganic matters
Material volume accounts for the 5%--20% of total volume of material, and preferably 10%;Described first mixing filtrate thickness is 100-300cm, preferably
150cm-250cm;
(C) by the filtrate in thick straw filtering storehouse, mixing filtrate fermentation cabin, the solid-state feces mixing on thick straw, enter organic
Fertile main fermentation storehouse, carries out 50-80 DEG C of hot fermentation, packs and pile up (for example in greenhouse or plastics at ambient temperature after fermentation
In booth, ambient temperature 20-40 DEG C), ferment in second time, obtain fertilizer.
7. method according to claim 6, wherein, in step (B), the mixing filtrate of absorption effluent in fermentation cabin,
Under high humidity more than 80%, maintain 50-60 DEG C, preferably from about 55 DEG C, hot fermentation 25 30 days, every cubic metre of filter daily
Material fermentation 20 30 kilograms of sewage of evaporation;
Or, wherein, described hot fermentation be solid-state feces with filter after mix filtrate by volume 1:0.3-10, preferably 1:
0.5-8, more preferably 1:3-5, such as 1:4 mix and blends, are warmed up to 50-60 DEG C for 1-2 days, e.g., from about 55 DEG C, reach more than 70 DEG C
When air blast cooling, maintain 5-10 days, e.g., from about 7 days.The preferred 30-80% of humidity, more preferably 50%-60% in fermentation cabin, ph value
Between 6.5-8.5, preferably 7-8;
Or, wherein, the filtrate fermentation in described filtrate fermentation cabin is to be warmed up within 12 days more than 55 DEG C, air blast when more than 70 DEG C
Cooling;
Or, wherein, disposably add 3kg fertilizer specific complex beneficial bacteria powder to filter sewage collecting pit, total viable count >=
1.0 × 109cfu/g, adds 0.1kg later daily;
Or, the time of wherein said ferment in second time is 30-50 days, intermittent aeration.
8. a kind of imitative forest surface ecosystems process the device that semisolid excrement dirty and sticky excrement slurry produces fertilizer simultaneously, this dress
Put including:
Thick straw media filtration storehouse, the particle diameter of the thick straw of thick straw media filtration storehouse filling is 1-5cm, the thickness of straw filtering layer
Spend for 10-150cm (preferably 30-100cm, more preferably 40-60cm),
The filtrate collecting pit connecting with thick straw media filtration storehouse bottom filtrate (liquid,
The one or more mixing filtrate fermentation cabin being connected with filtrate collecting pit by pipeline,
The leachate collection pool connecting with one or more mixing filtrate fermentation cabin bottoms filtrate (liquid, leachate collection pool is provided with
For percolate in leachate collection pool being sprayed the filtrate in one or more mixed fermentation storehouses,
The filtrate of filling in filtrate fermentation cabin, described mixing filtrate includes organic materials and inorganic material, and described organic materials can
From dry branches and fallen leaves, straw or wood flour, preferably straw, described organic materials particle diameter<1cm (such as particle size range 0.01-
0.99cm);Described inorganic material selects clay, bentonite, flyash, preferably bentonite, described inorganic material particle diameter 80 300
Mesh, preferably 200 mesh;Described inorganic material volume accounts for the 5%--20% of total volume of material, and preferably 10%;Described mixing filter material layer
Thick is 100-300cm, preferably 150cm-250cm;
For by the solid-state feces on thick straw filtrate and thick straw filtrate, the fertilizer main fermentation storehouse mixing filtrate fermentation.
9. device according to claim 8, it further includes for carrying out secondary to material after the fermentation of main fermentation storehouse
The greenhouse of ferment or hot house;
Or, wherein, the structure in thick straw media filtration storehouse includes a warehouse, positioned at the straw filtrate charging port on warehouse top
And overfall, positioned at upper strata V-arrangement filter plate and lower floor's V-arrangement filter plate of warehouse bottom, positioned at upper strata V-arrangement filter plate and lower floor's V-arrangement filter plate
Between filter material layer, warehouse bottom is the Lower Hold of closing, and is provided with filtrate (liquid, is in addition provided with spiral discharging in warehouse bottom
Machine;
Or, wherein, main fermentation storehouse, mixing filtrate fermentation chamber structure are identical, and including a warehouse, warehouse top is provided with deodorization
Cover, is optionally provided with shower below deodorization cover, is material bed below shower, and material bed is down V-arrangement filter plate, V-arrangement filter plate
Lower section is the Lower Hold of closing, is additionally provided with blast pipe, for lowering the temperature to air blast in warehouse, at the bottom of V-arrangement filter plate below V-arrangement filter plate
Portion, material bed lower section are provided with spiral discharging machine, are provided with straw charging aperture on warehouse top, are provided with filtrate in the Lower Hold of closing and go out
Mouthful.
10. the device according to claim 4-5 or 8-9, whole device is in greenhouse or hot house.
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107129039A (en) * | 2017-07-11 | 2017-09-05 | 河南省图天新能源科技有限公司 | Stalk as filtering layer livestock and poultry sewage water treatment method and device |
CN108358264A (en) * | 2018-04-25 | 2018-08-03 | 冯占余 | Biological heat energy coupled low temperature heat circulation evaporation process sewage recycles heat energy apparatus |
CN111203027A (en) * | 2020-01-13 | 2020-05-29 | 许洁 | Environment-friendly organic fertilizer sewage filtering device |
CN112723927A (en) * | 2021-01-15 | 2021-04-30 | 东北农业大学 | Device for making fertilizer from rural sewage and straw and using method thereof |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN203938611U (en) * | 2014-06-04 | 2014-11-12 | 牧原食品股份有限公司 | The efficient processing and utilizing system of a kind of pig farm excrement material |
CN104774043A (en) * | 2015-04-02 | 2015-07-15 | 昆山市畜牧兽医站 | Method for filtering and recycling cow dung dry-wet separating liquid by straws in large-scale dairy farm |
CN105036836A (en) * | 2015-06-12 | 2015-11-11 | 许道军 | Farm liquid manure treatment system and method |
CN204897915U (en) * | 2015-08-10 | 2015-12-23 | 段国昌 | Novel automatic methane system in high -efficient multipotency source |
CN105217898A (en) * | 2015-11-12 | 2016-01-06 | 山东省农业科学院农业资源与环境研究所 | A kind of Waste Water Treatment being applicable to middle-size and small-size plant |
CN105753263A (en) * | 2016-04-27 | 2016-07-13 | 常州大学 | Large breeding farm waste treatment device and method |
-
2016
- 2016-11-16 CN CN201611027417.2A patent/CN106431580A/en active Pending
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN203938611U (en) * | 2014-06-04 | 2014-11-12 | 牧原食品股份有限公司 | The efficient processing and utilizing system of a kind of pig farm excrement material |
CN104774043A (en) * | 2015-04-02 | 2015-07-15 | 昆山市畜牧兽医站 | Method for filtering and recycling cow dung dry-wet separating liquid by straws in large-scale dairy farm |
CN105036836A (en) * | 2015-06-12 | 2015-11-11 | 许道军 | Farm liquid manure treatment system and method |
CN204897915U (en) * | 2015-08-10 | 2015-12-23 | 段国昌 | Novel automatic methane system in high -efficient multipotency source |
CN105217898A (en) * | 2015-11-12 | 2016-01-06 | 山东省农业科学院农业资源与环境研究所 | A kind of Waste Water Treatment being applicable to middle-size and small-size plant |
CN105753263A (en) * | 2016-04-27 | 2016-07-13 | 常州大学 | Large breeding farm waste treatment device and method |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107129039A (en) * | 2017-07-11 | 2017-09-05 | 河南省图天新能源科技有限公司 | Stalk as filtering layer livestock and poultry sewage water treatment method and device |
CN108358264A (en) * | 2018-04-25 | 2018-08-03 | 冯占余 | Biological heat energy coupled low temperature heat circulation evaporation process sewage recycles heat energy apparatus |
CN111203027A (en) * | 2020-01-13 | 2020-05-29 | 许洁 | Environment-friendly organic fertilizer sewage filtering device |
CN112723927A (en) * | 2021-01-15 | 2021-04-30 | 东北农业大学 | Device for making fertilizer from rural sewage and straw and using method thereof |
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