CN111869540A - Method for manufacturing available medium by utilizing waste aerated concrete blocks - Google Patents
Method for manufacturing available medium by utilizing waste aerated concrete blocks Download PDFInfo
- Publication number
- CN111869540A CN111869540A CN202010558772.2A CN202010558772A CN111869540A CN 111869540 A CN111869540 A CN 111869540A CN 202010558772 A CN202010558772 A CN 202010558772A CN 111869540 A CN111869540 A CN 111869540A
- Authority
- CN
- China
- Prior art keywords
- product
- aerated concrete
- concrete blocks
- fermentation
- proportion
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 238000000034 method Methods 0.000 title claims abstract description 76
- 239000002699 waste material Substances 0.000 title claims abstract description 44
- 238000004519 manufacturing process Methods 0.000 title claims description 13
- 239000002245 particle Substances 0.000 claims abstract description 29
- 230000008569 process Effects 0.000 claims abstract description 25
- 239000003337 fertilizer Substances 0.000 claims abstract description 17
- 239000000843 powder Substances 0.000 claims abstract description 11
- 239000000463 material Substances 0.000 claims description 77
- 239000000047 product Substances 0.000 claims description 76
- 238000000855 fermentation Methods 0.000 claims description 62
- 230000004151 fermentation Effects 0.000 claims description 62
- 241000196324 Embryophyta Species 0.000 claims description 47
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 39
- 238000003756 stirring Methods 0.000 claims description 33
- 239000000203 mixture Substances 0.000 claims description 23
- 238000004332 deodorization Methods 0.000 claims description 21
- 238000002156 mixing Methods 0.000 claims description 14
- 239000010802 sludge Substances 0.000 claims description 12
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 10
- 239000003513 alkali Substances 0.000 claims description 9
- 244000025254 Cannabis sativa Species 0.000 claims description 7
- 150000003839 salts Chemical class 0.000 claims description 7
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 6
- 229910052799 carbon Inorganic materials 0.000 claims description 6
- 239000007789 gas Substances 0.000 claims description 6
- 229910052757 nitrogen Inorganic materials 0.000 claims description 5
- 235000013619 trace mineral Nutrition 0.000 claims description 5
- 239000011573 trace mineral Substances 0.000 claims description 5
- 230000003203 everyday effect Effects 0.000 claims description 4
- 230000007935 neutral effect Effects 0.000 claims description 4
- 244000144977 poultry Species 0.000 claims description 4
- 238000002791 soaking Methods 0.000 claims description 4
- 230000032683 aging Effects 0.000 claims description 3
- 230000000249 desinfective effect Effects 0.000 claims description 3
- 239000008234 soft water Substances 0.000 claims description 3
- 230000001954 sterilising effect Effects 0.000 claims description 3
- 239000013589 supplement Substances 0.000 claims description 3
- 238000010276 construction Methods 0.000 abstract description 15
- 230000008929 regeneration Effects 0.000 abstract description 3
- 238000011069 regeneration method Methods 0.000 abstract description 3
- 239000002609 medium Substances 0.000 description 26
- 239000002689 soil Substances 0.000 description 9
- 230000000694 effects Effects 0.000 description 5
- 239000010908 plant waste Substances 0.000 description 5
- 239000008399 tap water Substances 0.000 description 4
- 235000020679 tap water Nutrition 0.000 description 4
- 239000011449 brick Substances 0.000 description 3
- 230000002354 daily effect Effects 0.000 description 3
- 238000005034 decoration Methods 0.000 description 3
- 238000010413 gardening Methods 0.000 description 3
- 239000003895 organic fertilizer Substances 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 235000013311 vegetables Nutrition 0.000 description 3
- 238000005406 washing Methods 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 2
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 2
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 2
- 239000012752 auxiliary agent Substances 0.000 description 2
- 238000009264 composting Methods 0.000 description 2
- 230000001877 deodorizing effect Effects 0.000 description 2
- 238000007599 discharging Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 230000005484 gravity Effects 0.000 description 2
- 239000003864 humus Substances 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- 238000012423 maintenance Methods 0.000 description 2
- 239000011159 matrix material Substances 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 235000010755 mineral Nutrition 0.000 description 2
- 235000015097 nutrients Nutrition 0.000 description 2
- 239000011368 organic material Substances 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 230000035699 permeability Effects 0.000 description 2
- 229910052698 phosphorus Inorganic materials 0.000 description 2
- 239000011574 phosphorus Substances 0.000 description 2
- 229910052700 potassium Inorganic materials 0.000 description 2
- 239000011591 potassium Substances 0.000 description 2
- 239000003516 soil conditioner Substances 0.000 description 2
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 description 1
- 229910000013 Ammonium bicarbonate Inorganic materials 0.000 description 1
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 1
- 229920002522 Wood fibre Polymers 0.000 description 1
- CKUAXEQHGKSLHN-UHFFFAOYSA-N [C].[N] Chemical compound [C].[N] CKUAXEQHGKSLHN-UHFFFAOYSA-N 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 235000012538 ammonium bicarbonate Nutrition 0.000 description 1
- 239000001099 ammonium carbonate Substances 0.000 description 1
- 238000004500 asepsis Methods 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 238000009435 building construction Methods 0.000 description 1
- 239000004202 carbamide Substances 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 239000002781 deodorant agent Substances 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 230000018109 developmental process Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000011049 filling Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000000796 flavoring agent Substances 0.000 description 1
- 230000002431 foraging effect Effects 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 239000004615 ingredient Substances 0.000 description 1
- 238000011068 loading method Methods 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 239000003607 modifier Substances 0.000 description 1
- 239000000618 nitrogen fertilizer Substances 0.000 description 1
- 235000016709 nutrition Nutrition 0.000 description 1
- 230000035764 nutrition Effects 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 238000013138 pruning Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 238000012216 screening Methods 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 239000012258 stirred mixture Substances 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
- 230000007306 turnover Effects 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
- 239000002025 wood fiber Substances 0.000 description 1
Images
Classifications
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
- A01G24/20—Growth substrates; Culture media; Apparatus or methods therefor based on or containing natural organic material
- A01G24/22—Growth substrates; Culture media; Apparatus or methods therefor based on or containing natural organic material containing plant material
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
- A01G24/10—Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
- A01G24/20—Growth substrates; Culture media; Apparatus or methods therefor based on or containing natural organic material
Abstract
The invention relates to the field of garbage regeneration, in particular to a method for preparing an available medium by utilizing waste aerated concrete blocks, which is characterized in that 5-10 mm aerated concrete block particles are added in a powder fertilizer process and fermented, so that the aerated concrete blocks in construction garbage are utilized.
Description
Technical Field
The invention relates to the field of garbage regeneration, in particular to a method for manufacturing an available medium by utilizing waste aerated concrete blocks.
Background
Tap water tail mud: the tail mud generated by water filtration in urban waterworks every day is characterized in that mineral substances in the mud are carried away by water, and the mud is free of nutrition and pollution; the method is characterized in that the method comprises the following steps of (1) a 500 ten thousand population grade city, wherein the daily production of tail mud is more than 200 tons, and the annual production is 6-7 ten thousand tons, and the general treatment mode is that the tail mud is sent to an urban landfill site to be buried, but the landfill site library is limited, and part of the tail mud is transported to a main city and a city with conditions outside the city to be professionally treated, so that the operation cost is very high; for the tail sludge of the water plant, the environmental protection department has the possibility of limiting the transfer as the sludge of the sewage plant, which causes the problems of comprehensive treatment and reuse. Meanwhile, due to comprehensive reasons of water source land protection, dredging and the like, the tail mud has extremely low organic matter content, poor water permeability, large specific gravity, easy hardening, no comprehensive treatment and basic no reutilization.
Aerated concrete blocks in construction waste: the concrete aerated block is used as a light filling material in the building industry, has a great amount of application in building construction, and simultaneously generates a great amount of building decoration garbage due to home decoration. The method includes the steps that 50 million tons of waiting treatment amount of construction and decoration garbage is expected in 2020 Suzhou city, wherein 3 million tons of aerated concrete blocks are used, and the recycled brick making is mainly used at present, but the strength is not high, and the recycling application range is narrow; the aerated concrete blocks in the construction waste are light expansion materials, the brick making strength is not high, the application range is narrow, and the development of the comprehensive utilization technology of the renewable resources in the construction waste is not effectively developed and is a blank at present.
At the present stage, a related technology treatment system for treating the tail mud of the water works is immature, and the independent treatment basically has no use value, so that the method has the advantages of extremely low organic matter content, poor water permeability, high specific gravity, easy hardening and incapability of directly returning to the field for use; secondly, the structure strength is not high, and the brick cannot be made; thirdly, limited public resources are wasted again, whether they are filled or incinerated. The prior art mainly focuses on the disposal and utilization of sludge in lakes and rivers of cities, and does not have a relevant and reasonable technical application mode for tail mud. Meanwhile, the sludge and the tail sludge are different in essential composition, the composition of the sludge is complex, and the sludge generally contains more harmful substances and cannot be directly used due to a lot of uncertainty according to the condition of a place of origin. And the water taking place of the water works is a water source protection place, and the quality of the mud is safe.
How to utilize aerated concrete blocks in construction waste and tail mud of a tap water plant is a problem to be solved at present.
Disclosure of Invention
The invention aims to solve the problem of how to utilize aerated concrete blocks in construction waste, and provides a method for preparing a usable medium by using waste aerated concrete blocks, wherein 5-10 mm aerated concrete block particles are added in a powder fertilizer process and fermented, so that the aerated concrete blocks in the construction waste are utilized.
In order to solve the technical problems, the invention provides a method for manufacturing available media by utilizing waste aerated concrete blocks,
the method comprises the following steps: forming a first product by performing a crushing treatment process on a plant material;
step two: carrying out a mixing treatment process on the first product, the tail mud of the water works and the strains to form a second product;
step three: forming the second product into a usable medium by a powder fertilizer process;
the powder fertilizer process comprises the following steps:
crushing the aerated concrete blocks, wherein the size of crushed particles is 5-10 mm;
carrying out alkali and salt treatment on the crushed aerated concrete blocks;
adjusting the pH value of the crushed aerated concrete block subjected to alkali and salt treatment to be neutral to form aerated concrete block particles;
mixing and stirring the first product, the second product and the first auxiliary material to uniformly mix the first product, the second product and the first auxiliary material, and crushing the large hardened material; the first auxiliary materials comprise aerated concrete block particles, slow release fertilizer particles, trace elements (mainly nitrogen, phosphorus and potassium) and grass carbon, wherein the proportion of the second product is 75-85%, the proportion of the first product is a stirring filament material, the proportion of the first product is 8-12%, the proportion of the grass carbon is 8-12%, and the proportion of the aerated concrete block particles is 2-5%;
fermentation takes place and a usable medium is formed.
Preferably, the second product accounts for 80%, the first product accounts for 9%, the grass carbon accounts for 8%, and the aerated concrete block particles account for 3%.
The invention provides a method for preparing an available medium by utilizing waste aerated concrete blocks, which comprises the following steps of:
soaking in soft water with EC value of 0.1-0.5 for at least 3 times (each time for 7-10 days).
The invention provides a method for manufacturing an available medium by utilizing waste aerated concrete blocks, which comprises the following steps:
sorting and classifying the plant materials;
sterilizing and disinfecting the sorted and classified plant materials;
crushing the sterilized plant materials to less than 1 cm;
the crushed plant material is processed into a first product.
The invention provides a method for manufacturing an available medium by utilizing waste aerated concrete blocks, which comprises the following steps:
mixing and stirring the tail mud of the water works, the first product and the strain to ensure that the water content is between 50 and 65 percent;
then carrying out high-temperature oxygen-consuming fermentation;
and (5) after the fermentation is basically decomposed, aging or performing secondary fermentation to form a second product.
The invention provides a method for preparing an available medium by utilizing waste aerated concrete blocks, which comprises the following steps of mixing and stirring tail mud of a waterworks, a first product and a strain, and integrating the moisture of the tail mud of the waterworks to 50-65 percent:
preparing materials: the tail mud of the water works is proportioned by using a double-shaft feeding screw, namely, the tail mud of the water works is added into a double-shaft stirring and stirring machine in proportion, and the purpose of adjusting the adding amount of the tail mud of the water works is achieved by controlling the rotating speed of double-shaft feeding;
the first product is proportioned by using a double-shaft feeding screw, namely, the first product is added into a double-shaft stirring and splicing machine in proportion, and the purpose of adjusting the adding amount of the first product is achieved by controlling the rotating speed of double-shaft feeding;
the strain is proportioned by using a strain feeding screw, namely, the strain is added into a single-shaft screw feeder in proportion, and the purpose of adjusting the adding amount of the strain is achieved through the rotating speed of the screw feeder;
stirring: and (3) feeding the tail mud, the first product and the strain which are added in proportion into a continuous stirrer to be stirred to form a mixture.
The invention provides a method for preparing an available medium by utilizing waste aerated concrete blocks, which comprises the following steps:
uniformly distributing the mixture into a fermentation tank through a belt conveyor for high-temperature fermentation;
and after the temperature of the mixture entering the fermentation tank rises to 50-60 ℃, starting the turner to fully turn and throw the mixture for 1-2 times every day.
The invention provides a method for preparing an available medium by utilizing waste aerated concrete blocks, which further comprises the following steps: deodorization treatment in the fermentation process.
The invention provides a method for preparing an available medium by utilizing waste aerated concrete blocks, and the deodorization treatment method in the fermentation process comprises biological deodorization and foul gas collection deodorization.
The invention provides a method for preparing an available medium by utilizing waste aerated concrete blocks, and a second auxiliary material is also added in the step two to supplement a nitrogen source.
The invention provides a method for manufacturing an available medium by utilizing waste aerated concrete blocks, and poultry excrement particles are also added in the step two.
The method has the beneficial effects that the method for preparing the available medium by utilizing the waste aerated concrete blocks is provided, and the aerated concrete blocks in the construction waste are utilized by adding 5-10 mm aerated concrete block particles in a powder fertilizer process and fermenting; the plant material subjected to the crushing treatment process is mixed with the tail mud of the water works and the strains to form a usable medium, so that the tail mud of the water works is utilized, and the double utilization of the tail mud and aerated concrete blocks in the construction waste is realized;
the method for jointly treating various urban garbage to regenerate usable products comprises the steps of sorting, crushing, fiberizing and composting and fermenting the three urban garbage including water plant tail mud, aerated concrete blocks in construction garbage and plant wastes to generate the usable products. The utilization of the plant wastes is subdivided, and the plant wastes of all specifications can be effectively utilized. The tail mud and the plant material are fermented together and mutually complemented, and the plant material brings humus, a plurality of trace elements required by plant production, integrates the moisture of the tail mud and improves the soil structure of the tail mud; the tail mud brings a better fermentation platform for plant materials, expands a resource platform brought by plant humus, and can produce more soil improvement products. The over-alkaline treated aerated concrete block particles are added as auxiliary materials to retain water, ventilate and fertilizer and increase soil activity. The method really integrates three types of municipal wastes such as aerated concrete block particles in the tail mud of a water plant, construction wastes and the like by taking the treatment and application of plant wastes as a center. Through sorting, crushing, fiberizing treatment, composting fermentation treatment and harmless treatment, waste is changed into valuable, resource regeneration is carried out, and the final purpose is scientifically and effectively recycled.
Drawings
The invention is further illustrated with reference to the following figures and examples.
FIG. 1 is a flow diagram of a hybrid treatment process provided by the present invention.
FIG. 2 is a flow chart of the powder fertilizer process provided by the invention
Fig. 3 is a flow chart of the process for crushing the plant material provided by the invention.
Detailed Description
The present invention will now be described in further detail with reference to the accompanying drawings. These drawings are simplified schematic views illustrating only the basic structure of the present invention in a schematic manner, and thus show only the constitution related to the present invention.
Plant materials discarded by urban plants and plant materials in daily life such as vegetable farms: the main sources are urban public greenbelts, residential greenbelts, scenic spot greenbelts, municipal greening land, vegetable fields and the like. The plant wastes generated in the plant maintenance and pruning process comprise branches, twigs, grass, fallen leaves, flowers, plants and the like. Along with the ecological construction of the country, the greening area of urban plants is continuously increased, and the quantity of plant greening wastes is also increased. The greening waste increased year by year at present has caused huge pressure on greening maintenance management, and on the premise of scarce land resources, the traditional treatment mode (backfilling and burning) not only causes waste of resources, but also causes potential safety hazards such as fire and the like.
Referring to fig. 1 and 2, a method for producing a usable medium from tail mud of a waterworks,
the method comprises the following steps: the method comprises the steps of forming a first product by crushing plant materials, wherein the plant materials comprise waste plant materials in urban gardens, plant materials in daily life such as vegetable fields and the like, and the first product is a crushed plant material or/and a shred stirring material;
step two: mixing the first product, the tail mud of the water works and the strains to form a second product, wherein the second product can be a business modifier;
step three: forming a usable medium by the second product through a powder fertilizer process, wherein the usable medium is nutrient soil or plant medium soil;
referring to fig. 2, the powder fertilizer process includes:
the aerated concrete blocks are crushed, the size of the crushed particles is 5mm-10mm, and the supporting capacity is improved while the water retention and ventilation effects are achieved;
carrying out alkali and salt treatment on the crushed aerated concrete blocks;
adjusting the pH value of the crushed aerated concrete block subjected to alkali and salt treatment to be neutral to form aerated concrete block particles;
mixing and stirring the first product, the second product and the first auxiliary material to uniformly mix the first product, the second product and the first auxiliary material, and crushing the large hardened material; the first auxiliary materials comprise aerated concrete block particles, slow release fertilizer particles and trace elements (mainly nitrogen, phosphorus and potassium); fermenting to form a usable medium, wherein the first product is a stirred filament material accounting for 10 percent, the second product accounts for 80 percent, grass carbon accounts for 5 to 8 percent, and aerated concrete block particles account for 2 to 5 percent.
The method for treating the broken aerated concrete blocks by alkali and salt treatment comprises the following steps:
the PH value of the broken aerated concrete block is adjusted to be neutral by soaking the aerated concrete block in soft water with the EC value of 0.1-0.5 for not less than 3 times, and the soaking time is 7-10 days each time.
Referring to fig. 3, the crushing process includes the following steps:
sorting and classifying the plant materials;
sterilizing and disinfecting the sorted and classified plant materials;
crushing the sterilized plant materials to less than 1 cm;
the crushed plant material is processed into a first product. The asepsis of the materials is ensured, and the materials are crushed to be less than 1cm, so that the full fermentation is ensured.
According to product subdivision: the plant material can be broken into sawdust material aiming at soil conditioner and organic fertilizer;
crushing the mixture into granules with different interfaces, and aiming at nutrient soil and matrix soil produced by the gardening pot culture;
the plant material stirring threads are in a wood fiber form and aim at medium soil produced by high-end gardening pot plants.
Referring to fig. 1, in one embodiment, the hybrid processing process includes the following steps:
mixing and stirring the tail mud of the water works, the first product and the strain to ensure that the water content is between 50 and 65 percent; the stirring before fermentation mainly aims at adding a certain proportion of broken plant materials and strains into the tail mud, changing the carbon-nitrogen ratio and the moisture of the materials, enabling the mixture to interact, and meeting the conditions of rapid temperature rise and fermentation;
distributing the mixed material into a fermentation tank through a belt conveyor or a forklift, and then carrying out high-temperature oxygen-consuming fermentation;
and (5) after the fermentation is basically decomposed, aging or performing secondary fermentation to form a second product.
The fermented second product has two uses: one is directly loading the vehicle and directly using the vehicle as a soil conditioner or planting soil.
The second is adding certain other raw materials, stirring, crushing and screening, and then using in bulk as matrix, medium and organic fertilizer in various proportions for gardening production.
Firstly, preparing fermented second products, plant materials with different particle sizes and auxiliary materials according to different product requirements, putting organic materials into a bin of a feeding belt conveyor by using a forklift or a belt conveyor when producing powdered fertilizer, then putting a first product and a first auxiliary material (the first auxiliary material comprises aerated concrete block particles, slow-release fertilizer particles, trace elements and the like) according to a proportion, uniformly feeding the organic materials by using a belt arranged below the bin, and performing secondary fermentation treatment according to the product requirements after uniformly mixing to finally form a usable medium.
Referring to fig. 1, the method for mixing and stirring the tail sludge of the waterworks, the first product and the strain to synthesize the water content of the tail sludge of the waterworks to 50-65% comprises the following steps:
preparing materials: the tail mud of the water works is proportioned by using a double-shaft feeding screw, namely, the tail mud of the water works is added into a double-shaft stirring and stirring machine in proportion, and the purpose of adjusting the adding amount of the tail mud of the water works is achieved by controlling the rotating speed of double-shaft feeding;
the first product is proportioned by using a double-shaft feeding screw, namely, the first product is added into a double-shaft stirring and splicing machine in proportion, and the purpose of adjusting the adding amount of the first product is achieved by controlling the rotating speed of double-shaft feeding;
the strain is proportioned by using a strain feeding screw, namely, the strain is added into a single-shaft screw feeder in proportion, and the purpose of adjusting the adding amount of the strain is achieved through the rotating speed of the screw feeder;
stirring: the tail mud of the waterworks, the first product and the strain which are added in proportion enter a continuous stirrer to be stirred to form a mixture, wherein the tail mud of the waterworks is 4.5 to 5.5 tons, the first product is 2.5 to 3.5 tons, and the strain is 0.5 to 1 kilogram.
Preferably, the amount of the tail mud of the waterworks is 5 tons, the amount of the first product is 2 tons, and the amount of the strain is 1 kg.
During stirring, the tail mud is mixed by using a double-shaft feeding screw, the tail mud is added into a double-shaft stirring and stirring machine in proportion, and the purpose of adjusting the adding amount of the tail mud is achieved by controlling the rotating speed of double-shaft feeding; the first product is also proportioned by using a double-shaft feeding screw, and is added into a double-shaft stirring and splicing machine in proportion, and the purpose of adjusting the adding amount of the first product is achieved by controlling the rotating speed of double-shaft feeding; the strain is proportioned by using a feeding screw in the strain, the strain is added into a single-shaft screw feeder in proportion, and the purpose of adjusting the adding amount of the strain is achieved through the rotating speed of the screw feeder. All the rotating speed regulation is carried out through a frequency converter, so that the adding amount of various materials is controlled. Adding the sludge, the first product and the strain in proportion, feeding the mixture into a continuous stirrer for stirring, feeding the mixture from one end of the stirrer, discharging the mixture from the other end of the stirrer while feeding, and conveying the stirred mixture out through a belt conveyor. Then evenly distributing the mixture into a fermentation tank through a forklift or a belt conveyor for high-temperature fermentation. And starting the turner to turn over the materials after the temperature of the materials entering the fermentation tank is raised to 50-60 ℃. The turning purpose is mainly three: firstly, the water evaporated at high temperature when the material is fermented is emitted. And secondly, timely supplying oxygen to the materials. Thirdly, the material is displaced and pushed from the feeding end to the discharging end of the fermentation tank. The material can be moved by 3-4 meters by improving the large span and turning over once. In order to improve the fermentation effect, shorten the fermentation period and reduce the fermentation cost, a sunlight shed is used in a fermentation workshop, and the temperature of the fermentation workshop can be increased by the sunlight shed.
In one embodiment, a method of high temperature oxygen-consuming fermentation comprises:
uniformly distributing the mixture into a fermentation tank through a belt conveyor for high-temperature fermentation;
and after the temperature of the mixture entering the fermentation tank rises to 50-60 ℃, starting a turner to fully turn and throw the mixture for 1-2 times every day, so that full fermentation is realized and decomposition is accelerated.
After the fermentation tank is fermented at high temperature for about 20-30 days, the materials are basically decomposed, and at the moment, the materials can be transferred out of the fermentation tank and piled into a warehouse for aging or secondary fermentation. If the conditions of the fermentation tank allow the suggested time for stacking the materials in the fermentation workshop to be as long as possible, the materials are fully decomposed, and the quality of the organic fertilizer is improved.
Wherein the method for high temperature oxygen-consuming fermentation further comprises: deodorization treatment in the fermentation process, and a deodorization treatment method in the fermentation process comprises biological deodorization and foul gas collection deodorization. The deodorization in the fermentation process mainly comprises two methods: firstly, biological deodorization in the fermentation process; secondly, foul gas is collected and deodorized.
The biological deodorization in the fermentation process mainly comprises the step of adding a certain deodorization auxiliary agent and biological bacteria in the ingredients and stirring before fermentation. Through the deodorizing bacteria, the generation of odor in the fermentation process can be effectively inhibited, and the fermentation environment is improved. In the later turning process, a relatively good fermentation environment can be basically obtained by spraying the water agent of the deodorizing auxiliary agent.
Secondly, foul gas is collected and deodorized. The addition of biological deodorants during the fermentation still produces a more or less low level of off-flavours. The peculiar smell generated in the fermentation process is mainly ammonia generated in the fermentation process, and the deodorization is carried out twice by adopting a method of sealing, dehumidifying, adding alkali washing and water washing in practice, so that a good deodorization effect is obtained. Better deodorization effect can be obtained after biological deodorization and foul gas collection, washing and deodorization, and no secondary pollution is generated to the surrounding environment.
And in the second step, a second auxiliary material is also added to supplement a nitrogen source, wherein the auxiliary material is a nitrogen fertilizer and comprises substances such as urea and ammonium bicarbonate, when the amount of the tail mud of the waterworks is 4.5-5.5 tons, the amount of the first product is 2.5-3.5 tons, the amount of the strain is 0.5-1 kg, and the amount of the second auxiliary material is 30-50 kg, preferably 40 kg.
In the second step, poultry excrement particles are also added to provide corresponding organic minerals; when the amount of tail mud from water works is 4.5-5.5 tons, the amount of the first product is 2.5-3.5 tons, the amount of the strain is 0.5-1 kg, and 1-2 tons of poultry excrement particles are added.
The invention provides a method for preparing an available medium by utilizing waste aerated concrete blocks, which is characterized in that 5-10 mm aerated concrete block particles are added in a powder fertilizer process and fermented, so that the aerated concrete blocks in construction waste are utilized; the plant material subjected to the crushing treatment process, the tail mud of the tap water plant and the strain are mixed to form a usable medium, so that the tail mud of the tap water plant is utilized, and the double utilization of the tail mud and aerated concrete blocks in construction waste is realized.
In light of the foregoing description of the preferred embodiment of the present invention, many modifications and variations will be apparent to those skilled in the art without departing from the spirit and scope of the invention. The technical scope of the present invention is not limited to the content of the specification, and must be determined according to the scope of the claims.
Claims (10)
1. A method for manufacturing an available medium by utilizing waste aerated concrete blocks is characterized in that,
the method comprises the following steps: forming a first product by performing a crushing treatment process on a plant material;
step two: carrying out a mixing treatment process on the first product, the tail mud of the water works and the strains to form a second product;
step three: forming the second product into a usable medium by a powder fertilizer process;
the powder fertilizer process comprises the following steps:
crushing the aerated concrete blocks, wherein the size of crushed particles is 5-10 mm;
carrying out alkali and salt treatment on the crushed aerated concrete blocks;
adjusting the pH value of the crushed aerated concrete block subjected to alkali and salt treatment to be neutral to form aerated concrete block particles;
mixing and stirring the first product, the second product and the first auxiliary material to uniformly mix the first product, the second product and the first auxiliary material, and crushing the large hardened material; the first auxiliary materials comprise aerated concrete block particles, slow release fertilizer particles, trace elements and grass carbon, wherein the proportion of the second product is 75-85%, the proportion of the first product is a stirring filament material, the proportion of the first product is 8-12%, the proportion of the grass carbon is 8-12%, and the proportion of the aerated concrete block particles is 2-5%;
fermentation takes place and a usable medium is formed.
2. The method for preparing the usable medium by using the waste aerated concrete blocks as claimed in claim 1, wherein the method for treating the crushed aerated concrete blocks by alkali and over-salt treatment comprises the following steps:
soaking in soft water with EC value of 0.1-0.5 for at least 3 times (each time for 7-10 days).
3. The method for preparing the usable medium by using the waste aerated concrete blocks as claimed in claim 1, wherein the crushing treatment process comprises the following steps:
sorting and classifying the plant materials;
sterilizing and disinfecting the sorted and classified plant materials;
crushing the sterilized plant materials to less than 1 cm;
the crushed plant material is processed into a first product.
4. The method for preparing the usable medium by using the waste aerated concrete blocks as claimed in claim 1, wherein the mixing treatment process comprises the following steps:
mixing and stirring the tail mud of the water works, the first product and the strain to ensure that the water content is between 50 and 65 percent;
then carrying out high-temperature oxygen-consuming fermentation;
and (5) after the fermentation is basically decomposed, aging or performing secondary fermentation to form a second product.
5. The method for preparing the utilizable medium by using the waste aerated concrete blocks as claimed in claim 4, wherein the method for mixing and stirring the waterworks tail sludge, the first product and the strain to integrate the water content of the waterworks tail sludge to 50-65% comprises the following steps:
preparing materials: the tail mud of the water works is proportioned by using a double-shaft feeding screw, namely, the tail mud of the water works is added into a double-shaft stirring and stirring machine in proportion, and the purpose of adjusting the adding amount of the tail mud of the water works is achieved by controlling the rotating speed of double-shaft feeding;
the first product is proportioned by using a double-shaft feeding screw, namely, the first product is added into a double-shaft stirring and splicing machine in proportion, and the purpose of adjusting the adding amount of the first product is achieved by controlling the rotating speed of double-shaft feeding;
the strain is proportioned by using a strain feeding screw, namely, the strain is added into a single-shaft screw feeder in proportion, and the purpose of adjusting the adding amount of the strain is achieved through the rotating speed of the screw feeder;
stirring: and (3) feeding the tail mud, the first product and the strain which are added in proportion into a continuous stirrer to be stirred to form a mixture.
6. The method for preparing the utilizable medium by using the waste aerated concrete blocks as claimed in claim 5, wherein the method for high-temperature oxygen-consuming fermentation comprises the following steps:
uniformly distributing the mixture into a fermentation tank through a belt conveyor for high-temperature fermentation;
and after the temperature of the mixture entering the fermentation tank rises to 50-60 ℃, starting the turner to fully turn and throw the mixture for 1-2 times every day.
7. The method for making a utilizable medium from waste aerated concrete blocks according to claim 6, wherein the method for high temperature oxygen-consuming fermentation further comprises: deodorization treatment in the fermentation process.
8. The method for preparing the usable medium by using the waste aerated concrete blocks as claimed in claim 7, wherein the deodorization treatment method of the fermentation process comprises biological deodorization and foul gas collection deodorization.
9. The method for preparing the utilizable medium by utilizing the waste aerated concrete blocks as claimed in claim 1, wherein a second auxiliary material is further added in the second step to supplement a nitrogen source.
10. The method for preparing the utilizable medium by using the waste aerated concrete blocks as claimed in claim 1, wherein poultry excrement particles are further added in the second step.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202010558772.2A CN111869540A (en) | 2020-06-18 | 2020-06-18 | Method for manufacturing available medium by utilizing waste aerated concrete blocks |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202010558772.2A CN111869540A (en) | 2020-06-18 | 2020-06-18 | Method for manufacturing available medium by utilizing waste aerated concrete blocks |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN111869540A true CN111869540A (en) | 2020-11-03 |
Family
ID=73156859
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202010558772.2A Pending CN111869540A (en) | 2020-06-18 | 2020-06-18 | Method for manufacturing available medium by utilizing waste aerated concrete blocks |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN111869540A (en) |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105693432A (en) * | 2016-03-25 | 2016-06-22 | 深圳市净土生活园科技有限公司 | Biological planting substrate and preparation method thereof |
| CN105900728A (en) * | 2016-05-13 | 2016-08-31 | 浙江建设职业技术学院 | Nutrient soil and method for succulent plant cultivation |
| CN106905077A (en) * | 2017-03-22 | 2017-06-30 | 海南瑞泽新材料研究院有限公司 | A kind of after-treatment building waste waste prepares the method for planting soil and the planting soil of acquisition |
| CN109006363A (en) * | 2018-09-30 | 2018-12-18 | 岭南生态文旅股份有限公司 | A kind of composite interstitial substance and preparation method thereof based on building waste and garden waste |
| CN110372456A (en) * | 2019-08-26 | 2019-10-25 | 郭平 | A kind of sludge afforestation fertilizer special for organic soil and preparation method thereof |
-
2020
- 2020-06-18 CN CN202010558772.2A patent/CN111869540A/en active Pending
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105693432A (en) * | 2016-03-25 | 2016-06-22 | 深圳市净土生活园科技有限公司 | Biological planting substrate and preparation method thereof |
| CN105900728A (en) * | 2016-05-13 | 2016-08-31 | 浙江建设职业技术学院 | Nutrient soil and method for succulent plant cultivation |
| CN106905077A (en) * | 2017-03-22 | 2017-06-30 | 海南瑞泽新材料研究院有限公司 | A kind of after-treatment building waste waste prepares the method for planting soil and the planting soil of acquisition |
| CN109006363A (en) * | 2018-09-30 | 2018-12-18 | 岭南生态文旅股份有限公司 | A kind of composite interstitial substance and preparation method thereof based on building waste and garden waste |
| CN110372456A (en) * | 2019-08-26 | 2019-10-25 | 郭平 | A kind of sludge afforestation fertilizer special for organic soil and preparation method thereof |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN101486613B (en) | Method for preparing organic fertilizer by mixed fermentation of water hyacinth and dewatered sludge | |
| CN101289336B (en) | Integral treatment method for city household refuse | |
| CN104370582B (en) | A kind of organic waste odorless aerobic compost method | |
| CN101913747B (en) | Method for producing methane by combination fermentation of paper mill sludge and food waste | |
| CN202988933U (en) | Sludge treatment land resource utilization system | |
| CN101618934B (en) | Sludge dry powder and preparation method thereof | |
| CN101597532B (en) | Sludge fuel and preparation method thereof | |
| CN106892690A (en) | Sewage treatment plant's domestic sludge compost method of disposal | |
| CN102441555B (en) | Comprehensive utilization and disposal method of urban domestic garbage | |
| CN102408177A (en) | Biological complex enzyme for sludge recycling and use method thereof | |
| CN204224405U (en) | A kind of city sewage sludge reclamation treatment system | |
| CN106031925A (en) | Processing technology for harmlessly reducing city garbage and converting city garbage into resources | |
| CN108636992B (en) | Garden waste aerobic fermentation energy recycling process | |
| CN108947728A (en) | A kind of preparation method of municipal sludge rare earth organic fertilizer | |
| CN1137870C (en) | Process for preparing compound organic fertilizer from municipal sludge | |
| EP0970933A2 (en) | Slow release matrix bound fertilisers | |
| CN105565914A (en) | Method for preparing organic fertilizer based on EM (Effective Microorganisms) probiotics and domestic garbage | |
| CN111869540A (en) | Method for manufacturing available medium by utilizing waste aerated concrete blocks | |
| CN111875421A (en) | Method for preparing available medium by using tail mud of water works | |
| CN107602300A (en) | Salt-soda soil fertilizer based on coal-fired flue gas desulfurization gypsum and sludge and preparation method thereof | |
| CN112893401A (en) | Perishable garbage and greening garbage co-processing method | |
| KR100348637B1 (en) | Witout Discharging Treatment System and Paddy Rice Fertilizer by The Composting Method of Livestock Sewage. | |
| CN112961009A (en) | Papermaking sludge nutrient soil and preparation method thereof | |
| CN112898056A (en) | Advanced technology for resource utilization of municipal domestic sludge | |
| CN106316480A (en) | Method for preparing soil organic fertilizer by mixing salty mud and sludge |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| RJ01 | Rejection of invention patent application after publication | ||
| RJ01 | Rejection of invention patent application after publication |
Application publication date: 20201103 |