CN108273833A - The layering on the spot of building solid waste utilizes and the application on reducing soil alkaline - Google Patents

The layering on the spot of building solid waste utilizes and the application on reducing soil alkaline Download PDF

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Publication number
CN108273833A
CN108273833A CN201810205918.8A CN201810205918A CN108273833A CN 108273833 A CN108273833 A CN 108273833A CN 201810205918 A CN201810205918 A CN 201810205918A CN 108273833 A CN108273833 A CN 108273833A
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solid waste
soil
waste
layer
green plants
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CN108273833B (en
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张浪
朱永官
罗启仕
郑思俊
韩继刚
李晓策
伍海兵
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Shanghai Academy of Landscape Architecture Science and Planning
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Shanghai Academy of Landscape Architecture Science and Planning
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • B09C1/10Reclamation of contaminated soil microbiologically, biologically or by using enzymes

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  • Engineering & Computer Science (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Soil Sciences (AREA)
  • Biomedical Technology (AREA)
  • General Health & Medical Sciences (AREA)
  • Microbiology (AREA)
  • Molecular Biology (AREA)
  • Mycology (AREA)
  • Biotechnology (AREA)
  • Health & Medical Sciences (AREA)
  • Cultivation Of Plants (AREA)
  • Processing Of Solid Wastes (AREA)
  • Soil Conditioners And Soil-Stabilizing Materials (AREA)

Abstract

The present invention provides a kind of utilization of layering on the spot of building solid waste, including thick solid waste, thin solid waste two types are crushed and are sieved to place building solid waste;Thick green plants waste and thin green plants waste two types are to including that plant residue, weeds, fallen leaves, branch crush;It is for use with the raw-soil to being formed after place original soil addition soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent;Utilize the place after digging original soil, from bottom to surface layer, thick solid waste layer, thin solid waste nitride layer, thick green plants waste layer, thin solid waste nitride layer, thin green plants waste layer are filled respectively and matches raw soil layer, and are finally overlying on planting soil layer, compaction treatment when placement in layers.Technical solution using the present invention reduces the cost of improvement engineering project place soil physical arrangement, and it is notable to recycle environmental protection effect;Solid waste nitride layer cut-out soil capillary pore avoids accumulation of salt in the surface soil alkali problem.

Description

The layering on the spot of building solid waste is using and on reduction soil alkaline Using
Technical field
The present invention relates to a kind of ecological utilization methods of the solid waste of building, and specifically the solid waste exists It reduces on soil alkaline, and obtains economic effect.
Background technology
The solid waste such as building are one of main sources of urban solid garbage, and engineering project place generally retains largely The solid waste such as building need to handle and clear, and for solid waste processing, generally there are three approach both at home and abroad at present:Directly It connects and clears strange land landfill, do building materials utilization as recycling after landform construction material and processing.Due to the solid wastes such as being built Species type is various, transports the factors such as inconvenient and Project Cost Control influences, and urban architecture waste is mainly filled out with strange land at present It buries based on mode, needs the processing cost and transportation cost that put into a large amount of solid refuse, bring unnecessary waste.Meanwhile Landfill is also to cause the waste of land resource and with the risk of secondary pollution for land resource city in short supply.Thus, Need it is a kind of effectively and reasonably and the technical methods of the solid waste such as easy on-site elimination engineering project place building is answered To the above problem, and pollution is not generated to place soil.Meanwhile the solid waste local use such as building is bound to cause Site Soil Earth nutrient it is barren, be unfavorable for the subsequent ecological use in place, such as build park green land, build ecology corridor.
Invention content
In view of the above-mentioned problems, the present invention provides a kind of side in situ for dissolving the solid waste such as building and improveing soil alkaline Method purpose of the present invention is to comprehensively utilize the solid waste such as consumption place different-grain diameter building, and applies green plants waste And its compost product and improve original position soil nutrient condition with the raw-soil, while reducing soil alkaline.This method have it is convenient and efficient, Less investment, and the characteristics of do not generate secondary pollution, meanwhile, having improves urban soil physical arrangement and nutrient condition and reduction A variety of effects such as soil alkaline have significant economic benefit and ecological benefits.
A method of the solid waste such as layering consumption building and reduction soil alkaline on the spot specifically include following step Suddenly:
(1)Place building solid waste is broken and sieves:
Place building solid waste is crushed and is sieved by thick solid waste, thin solid waste two types; Sort out the material for causing volume variable to cause foundation deformation (such as residual branch, foam) that can rot for a long time(General control is 10- 30cm);
The thick solid waste:Refer to the solid waste formed after building, terrace forcible entry after sorting, pulverization process, grain Solid waste of the diameter in 16cm-30cm;
The thin solid waste:Refer to the solid waste formed after building, terrace forcible entry after sorting, pulverization process, grain Diameter is in 16cm solid waste below.
(2)It is prepared by green plants waste:
By thick green plants waste and thin green plants waste two types to including plant residue, weeds, fallen leaves, branch It crushes;
The thick green plants waste, produced by referring in urban green space or suburb forest land in green plants nature or maintenance processes Shrub lop, intermediate cutting object, turf-mown object, weeds, fallen leaves, branch, the waste that the showy flowers of herbaceous plants is discarded in garden and flower bed, Grain size 20-40mm;
The thin green plants waste, produced by referring in urban green space or suburb forest land in green plants nature or maintenance processes Shrub lop, intermediate cutting object, turf-mown object, weeds, fallen leaves, branch, the waste that the showy flowers of herbaceous plants is discarded in garden and flower bed, Grain size is less than 13mm.
(3)It is prepared with the raw-soil:
Digging original soil, it is for use with the raw-soil to being formed after place original soil addition soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent; Described with the raw-soil refers to that human intervention is made and meets the soil of plant health fast-growth nutritional need.It is mainly characterized by root According to land occupation condition, science configuration is carried out to original soil, soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent, is had preferable Physical property and higher bioactivity and environment conditioning ability.
The physicochemical property with original soil in the raw-soil is pH>8、EC<0.3mS/cm, organic matter<12g/kg, quality are viscous Weight.The physicochemical property of soil moved in improve the original is pH>9、EC<0.15mS/cm, organic matter<10g/kg, heavy texture.
The described addition mass ratio with original soil in the raw-soil, soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent is 100:20-40:1-10:0.1-2.
The described addition mass ratio with original soil in the raw-soil, soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent is 100:28:6:1.
The organic-inorganic improved materials are by dry branches and fallen leaves waste, mushroom slag, acid-sludge, organic fertilizer, humic acid, poly- third Acrylamide, desulfurated plaster, sulphur 40-50 in mass ratio:10-15:16-25:10-15:1-5:1-8:3-7:5-10 is formed.
Further preferably the organic-inorganic improved materials further include ammonium polyphosphate, and the additive amount of ammonium polyphosphate occupies The 10%-15% of machine Inorganic Modified Material;The polyacrylamide can be replaced by acrylic acid or acrylic amide modified chitosan; The desulfurated plaster can be replaced ardealite.
The organic-inorganic improved materials are preferably further ammonium polyphosphate, ardealite, humic acid, acrylic acid or third The chitosan that acrylamide is modified, mass ratio 1-3:20-40:5-10:5-10, further preferred mass ratio are 2:33:8:8.
The microbial bacterial agent is the microbial inoculum for improveing soil, specifically includes phosphorus decomposing quasi-microorganism microbial inoculum(Bacillus megaterium), silicate microbial bacterial agent(Bacillus mucilaginosus), organic matter decomposing inoculant(Bacillus subtilis、Paenibacillus polymyxa、Bacillus pumilus)Or soil remediation microbial inoculum(Bacillus licheniformis、Pseudomonas putida)In it is one or more.
(4)Layering consumption construction method:
It is true according to the type of solid waste, the green plants wastes such as building etc. and total amount using the place after digging original soil Surely depth of field and lift height are dissolved, from bottom to surface layer, fill respectively thick solid waste layer, thin solid waste nitride layer, Thick green plants waste layer, thin solid waste nitride layer, thin green plants waste layer and match raw soil layer, and is finally overlying on plantation Soil layer(Meet the soil of afforestation planting requirement on same court), compaction treatment when placement in layers, you can it is solid to complete building The layering on the spot of body waste utilizes.
The step(4)In, from bottom to surface layer, thick solid waste layer, thin solid waste nitride layer, thick is filled respectively Green plants waste layer, thin solid waste nitride layer, thin green plants waste layer and the thickness with raw soil layer are followed successively by 25- 50cm、25-50cm、10-20cm、10-20cm、10-20cm、50cm。
The further preferably step(4)In, from bottom to surface layer, thick solid waste layer is filled respectively, is carefully consolidated Body waste layer, thick green plants waste layer, thin solid waste nitride layer, thin green plants waste layer and the thickness with raw soil layer Degree is followed successively by 40cm, 30cm, 15cm, 15cm, 15cm, 50cm.
Technical scheme of the present invention, which utilizes the layering on the spot of the building solid waste, is reducing soil alkaline On application.Salt affected soil refers to reach the soil of 0.1%-0.2%, skill using the present invention containing solubility salt and salt content Saline-alkali soil can reduce 15%-20% by soil salt content in 1 year after art scheme.
The advantages of the invention:
Technical scheme of the present invention forms different aperture item by using the solid waste layerwise construction such as building of different-grain diameter The multilayered structure of part is, it can be achieved that solid waste rationally utilizes on the spot, and does not destroy soil basic structure, in combination with using The greening waste and its composting production of different disposal degree and with the raw-soil to improve soil nutrient, soil depletion can be evaded and asked Topic.The infiltration rate of place soil can be greatly improved in above-mentioned multilayered structure, there is the leaching for accelerating urban soil saline and alkaline to reduce saline and alkaline The adjection of degree.
It is of the present invention with the raw-soil formula in, using the organic-inorganic improved materials by ammonium polyphosphate, ardealite, Humic acid, acrylic acid or acrylic amide modified Chitosan Polymer Materials and other raw materials compound, and improve the physics and chemistry in original soil Property.The ammonium polyphosphate energy slow release effect of N and P factor used, improves the nutrient structure of soil.On the one hand ardealite used carries For a certain amount of phosphorus nutrient, soil acidity or alkalinity is on the other hand adjusted, enhances buffering power of soil.Humic acid used can in water Metal ion clutch is conducive to nutrient and is transmitted to crop, and can improve soil texture, is conducive to the growth of crops.Institute It can be significantly increased soil water stability granule with acrylic acid or acrylic amide modified Chitosan Polymer Materials soil conditioner Content, soil anti-erodibility by water increase, and soil erosion is accordingly reduced.
And after dry branches and fallen leaves waste described herein, mushroom slag, acid-sludge are mixed with other raw materials, it is acted in faintly acid Under, it is suitble to microorganism growth respiration, increases the porosity, contribute to the decomposition of green plants solid waste, reaches consumption solution row Effect.
The method of the present invention is simple and efficient, and cost is less than, easy to spread, has the advantages that various aspects, such as directly utilizes on the spot The solid waste such as building reduce the wasting of resources and secondary pollution;Low cost improvement engineering project place soil physical arrangement, is followed Ring is notable using environmental protection effect;Soil capillary pore, which is cut off, by solid wastes nitride layer such as buildings avoids accumulation of salt in the surface soil alkali problem;With life Soil nutrient condition is apt in land reform, is conducive to the ecological use in later stage place;Processing for engineering project place solid waste Using and place soil improvement have it is high instruct application value, and there is considerable economic benefit.
Description of the drawings
Fig. 1 is that the layering on the spot of building solid waste of the present invention dissolves construction structure figure, wherein 1. is thick solid Body waste layer, 2. thin solid waste nitride layer, 3. thick green plants waste layers, 4. thin green plants wastes are mixed with the raw-soil Close layer, 5. planting soil layers.
Specific implementation mode and
Embodiment 1
(1)Place building solid waste is broken and sieves:
Place building solid waste is crushed and is sieved by thick solid waste, thin solid waste two types; Sort out the material for causing volume variable to cause foundation deformation (such as residual branch, foam) that can rot for a long time;
The thick solid waste:Refer to the solid waste formed after building, terrace forcible entry after sorting, pulverization process, grain Solid waste of the diameter in 20-30cm;
The thin solid waste:Refer to the solid waste formed after building, terrace forcible entry after sorting, pulverization process, grain Solid waste of the diameter in 10-16cm.
(2)It is prepared by green plants waste:
By thick green plants waste and thin green plants waste two types to including plant residue, weeds, fallen leaves, branch It crushes;
The thick green plants waste, produced by referring in urban green space or suburb forest land in green plants nature or maintenance processes Shrub lop, intermediate cutting object, turf-mown object, weeds, fallen leaves, branch, the waste that the showy flowers of herbaceous plants is discarded in garden and flower bed, Grain size 35-40mm;
The thin green plants waste, produced by referring in urban green space or suburb forest land in green plants nature or maintenance processes Shrub lop, intermediate cutting object, turf-mown object, weeds, fallen leaves, branch, the waste that the showy flowers of herbaceous plants is discarded in garden and flower bed, Grain size 5-8mm.
(3)It is prepared with the raw-soil:
Digging original soil, it is for use with the raw-soil to being formed after place original soil addition soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent; Described with the raw-soil refers to that human intervention is made and meets the soil of plant health fast-growth nutritional need.It is mainly characterized by root According to land occupation condition, science configuration is carried out to original soil, soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent, is had preferable Physical property and higher bioactivity and environment conditioning ability.
The described addition mass ratio with original soil in the raw-soil, soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent is 100:28:6:1.The physicochemical property with original soil in the raw-soil is pH>8、EC<0.3mS/cm, organic matter<12g/kg, quality Viscous weight.The physicochemical property of soil moved in improve the original is pH>9、EC<0.15mS/cm, organic matter<10g/kg, heavy texture.
The organic-inorganic improved materials are high by ammonium polyphosphate, ardealite, humic acid, acrylic amide modified chitosan Molecular material is 2 in mass ratio:33:8:8 compositions.
The microbial bacterial agent isBacillus megaterium
(4)Layering consumption construction method:
It is true according to the type of solid waste, the green plants wastes such as building etc. and total amount using the place after digging original soil Surely depth of field and lift height are dissolved, from bottom to surface layer, fill respectively thick solid waste layer, thin solid waste nitride layer, Thick green plants waste layer, thin solid waste nitride layer, thin green plants waste layer and match raw soil layer, and is finally overlying on plantation Soil layer(Meet the soil of afforestation planting requirement on same court), compaction treatment when placement in layers, you can it is solid to complete building The layering on the spot of body waste utilizes.
From bottom to surface layer, thick solid waste layer, thin solid waste nitride layer, thick green plants waste are filled respectively Layer, thin solid waste nitride layer, thin green plants waste and match raw-soil mixed layer(The batch mixing ratio of the two is 1:1)Thickness successively For 40cm, 30cm, 15cm, 15cm, 50cm.
Technical solution using the present invention can by reach containing solubility salt and salt content 0.15% salt affected soil, 6 In a month(March-September part)It will decrease to 0.141%.
Embodiment 2
(1)Place building solid waste is broken and sieves:
Place building solid waste is crushed and is sieved by thick solid waste, thin solid waste two types; Sort out the material for causing volume variable to cause foundation deformation (such as residual branch, foam) that can rot for a long time;
The thick solid waste:Refer to the solid waste formed after building, terrace forcible entry after sorting, pulverization process, grain Solid waste of the diameter in 16cm-20cm;
The thin solid waste:Refer to the solid waste formed after building, terrace forcible entry after sorting, pulverization process, grain Solid waste of the diameter in 10cm-16cm.
(2)It is prepared by green plants waste:
By thick green plants waste and thin green plants waste two types to including plant residue, weeds, fallen leaves, branch It crushes;
The thick green plants waste, produced by referring in urban green space or suburb forest land in green plants nature or maintenance processes Shrub lop, intermediate cutting object, turf-mown object, weeds, fallen leaves, branch, the waste that the showy flowers of herbaceous plants is discarded in garden and flower bed, Grain size 25-35mm;
The thin green plants waste, produced by referring in urban green space or suburb forest land in green plants nature or maintenance processes Shrub lop, intermediate cutting object, turf-mown object, weeds, fallen leaves, branch, the waste that the showy flowers of herbaceous plants is discarded in garden and flower bed, Grain size 10-13mm.
(3)It is prepared with the raw-soil:
Digging original soil, it is for use with the raw-soil to being formed after place original soil addition soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent; Described with the raw-soil refers to that human intervention is made and meets the soil of plant health fast-growth nutritional need.It is mainly characterized by root According to land occupation condition, science configuration is carried out to original soil, soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent, is had preferable Physical property and higher bioactivity and environment conditioning ability.
The described addition mass ratio with original soil in the raw-soil, soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent is 100:28:7.2:1.5.The physicochemical property with original soil in the raw-soil is pH>8、EC<0.3mS/cm, organic matter<12g/kg、 Heavy texture.The physicochemical property of soil moved in improve the original is pH>9、EC<0.15mS/cm, organic matter<10g/kg, heavy texture.
The organic-inorganic improved materials are by ammonium polyphosphate, ardealite, humic acid, acrylic acid modified chitosan high score Sub- material is 1.5 in mass ratio:28:6.5:6 compositions.
The microbial bacterial agent isPaenibacillus polymyxa。
(4)Layering consumption construction method:
It is true according to the type of solid waste, the green plants wastes such as building etc. and total amount using the place after digging original soil Surely depth of field and lift height are dissolved, from bottom to surface layer, fill respectively thick solid waste layer, thin solid waste nitride layer, Thick green plants waste layer, thin solid waste nitride layer, thin green plants waste layer and match raw soil layer, and is finally overlying on plantation Soil layer(Meet the soil of afforestation planting requirement on same court), compaction treatment when placement in layers, you can it is solid to complete building The layering on the spot of body waste utilizes.
From bottom to surface layer, thick solid waste layer, thin solid waste nitride layer, thick green plants waste are filled respectively Layer, thin solid waste nitride layer, thin green plants waste and match raw-soil mixed layer(The batch mixing ratio of the two is 1:1)Thickness successively For 30cm, 25cm, 20cm, 20cm, 50cm.
Technical scheme of the present invention, which utilizes the layering on the spot of the building solid waste, is reducing soil alkaline On application.
Technical solution using the present invention can by reach containing solubility salt and salt content 0.15% salt affected soil, In 10 months(January next year in March-)It will decrease to 0.133%.
Embodiment 3
(1)Place building solid waste is broken and sieves:
Place building solid waste is crushed and is sieved by thick solid waste, thin solid waste two types; Sort out the material for causing volume variable to cause foundation deformation (such as residual branch, foam) that can rot for a long time;
The thick solid waste:Refer to the solid waste formed after building, terrace forcible entry after sorting, pulverization process, grain Solid waste of the diameter in 25-30cm;
The thin solid waste:Refer to the solid waste formed after building, terrace forcible entry after sorting, pulverization process, grain Solid waste of the diameter in 8-12cm.
(2)It is prepared by green plants waste:
By thick green plants waste and thin green plants waste two types to including plant residue, weeds, fallen leaves, branch It crushes;
The thick green plants waste, produced by referring in urban green space or suburb forest land in green plants nature or maintenance processes Shrub lop, intermediate cutting object, turf-mown object, weeds, fallen leaves, branch, the waste that the showy flowers of herbaceous plants is discarded in garden and flower bed, Grain size 35-40mm;
The thin green plants waste, produced by referring in urban green space or suburb forest land in green plants nature or maintenance processes Shrub lop, intermediate cutting object, turf-mown object, weeds, fallen leaves, branch, the waste that the showy flowers of herbaceous plants is discarded in garden and flower bed, Grain size 5-8mm.
(3)It is prepared with the raw-soil:
Digging original soil, it is for use with the raw-soil to being formed after place original soil addition soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent; Described with the raw-soil refers to that human intervention is made and meets the soil of plant health fast-growth nutritional need.It is mainly characterized by root According to land occupation condition, science configuration is carried out to original soil, soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent, is had preferable Physical property and higher bioactivity and environment conditioning ability.
The described addition mass ratio with original soil in the raw-soil, soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent is 100:21:7:1.1.The physicochemical property with original soil in the raw-soil is pH>8、EC<0.3mS/cm, organic matter<12g/kg, matter Glue weight in ground.The physicochemical property of soil moved in improve the original is pH>9、EC<0.15mS/cm, organic matter<10g/kg, heavy texture.
The organic-inorganic improved materials are by dry branches and fallen leaves waste, mushroom slag, acid-sludge, organic fertilizer, humic acid, poly- third Acrylamide, desulfurated plaster, sulphur in mass ratio 43:12:20:14:3.5:2.7:3.5:6.8 composition.
The microbial bacterial agent isBacillus megaterium
(4)Layering consumption construction method:
It is true according to the type of solid waste, the green plants wastes such as building etc. and total amount using the place after digging original soil Surely depth of field and lift height are dissolved, from bottom to surface layer, fill respectively thick solid waste layer, thin solid waste nitride layer, Thick green plants waste layer, thin solid waste nitride layer, thin green plants waste layer and match raw soil layer, and is finally overlying on plantation Soil layer(Meet the soil of afforestation planting requirement on same court), compaction treatment when placement in layers, you can it is solid to complete building The layering on the spot of body waste utilizes.
From bottom to surface layer, thick solid waste layer, thin solid waste nitride layer, thick green plants waste are filled respectively Layer, thin solid waste nitride layer, thin green plants waste and match raw-soil mixed layer(The batch mixing ratio of the two is 1:1)Thickness successively For 44cm, 38cm, 19cm, 12cm, 50cm.
Technical solution using the present invention can by reach containing solubility salt and salt content 0.15% salt affected soil, In 12 months(March next year in March-)It will decrease to 0.12%.
Embodiment 4
(1)Place building solid waste is broken and sieves:
Place building solid waste is crushed and is sieved by thick solid waste, thin solid waste two types; Sort out the material for causing volume variable to cause foundation deformation (such as residual branch, foam) that can rot for a long time;
The thick solid waste:Refer to the solid waste formed after building, terrace forcible entry after sorting, pulverization process, grain Solid waste of the diameter in 16cm-20cm;
The thin solid waste:Refer to the solid waste formed after building, terrace forcible entry after sorting, pulverization process, grain Solid waste of the diameter in 10cm-16cm.
(2)It is prepared by green plants waste:
By thick green plants waste and thin green plants waste two types to including plant residue, weeds, fallen leaves, branch It crushes;
The thick green plants waste, produced by referring in urban green space or suburb forest land in green plants nature or maintenance processes Shrub lop, intermediate cutting object, turf-mown object, weeds, fallen leaves, branch, the waste that the showy flowers of herbaceous plants is discarded in garden and flower bed, Grain size 25-35mm;
The thin green plants waste, produced by referring in urban green space or suburb forest land in green plants nature or maintenance processes Shrub lop, intermediate cutting object, turf-mown object, weeds, fallen leaves, branch, the waste that the showy flowers of herbaceous plants is discarded in garden and flower bed, Grain size 10-13mm.
(3)It is prepared with the raw-soil:
Digging original soil, it is for use with the raw-soil to being formed after place original soil addition soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent; Described with the raw-soil refers to that human intervention is made and meets the soil of plant health fast-growth nutritional need.It is mainly characterized by root According to land occupation condition, science configuration is carried out to original soil, soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent, is had preferable Physical property and higher bioactivity and environment conditioning ability.
The described addition mass ratio with original soil in the raw-soil, soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent is 100:30:5:1.5.The physicochemical property with original soil in the raw-soil is pH>8、EC<0.3mS/cm, organic matter<12g/kg, matter Glue weight in ground.The physicochemical property of soil moved in improve the original is pH>9、EC<0.15mS/cm, organic matter<10g/kg, heavy texture.
The organic-inorganic improved materials are by dry branches and fallen leaves waste, mushroom slag, acid-sludge, organic fertilizer, humic acid, propylene The modified chitosan replacement of acid, ardealite, sulphur, ammonium polyphosphate are 42 in mass ratio:13:22:13:3.5:2.5:5.5:8.5: 15.4 compositions.
The microbial bacterial agent isBacillus subtilis。
(4)Layering consumption construction method:
It is true according to the type of solid waste, the green plants wastes such as building etc. and total amount using the place after digging original soil Surely depth of field and lift height are dissolved, from bottom to surface layer, fill respectively thick solid waste layer, thin solid waste nitride layer, Thick green plants waste layer, thin solid waste nitride layer, thin green plants waste layer and match raw soil layer, and is finally overlying on plantation Soil layer(Meet the soil of afforestation planting requirement on same court), compaction treatment when placement in layers, you can it is solid to complete building The layering on the spot of body waste utilizes.
From bottom to surface layer, thick solid waste layer, thin solid waste nitride layer, thick green plants waste are filled respectively Layer, thin solid waste nitride layer, thin green plants waste and match raw-soil mixed layer(The batch mixing ratio of the two is 1:1)Thickness successively For 38cm, 25cm, 16cm, 14cm, 50cm.
Technical scheme of the present invention, which utilizes the layering on the spot of the building solid waste, is reducing soil alkaline On application.
Technical solution using the present invention can by reach containing solubility salt and salt content 0.15% salt affected soil, In 12 months(March next year in March-)It will decrease to 0.12%.

Claims (10)

1. the layering on the spot of building solid waste utilizes, which is characterized in that
(1)Place building solid waste is broken and sieves:
Place building solid waste is crushed and is sieved by thick solid waste, thin solid waste two types;
(2)It is prepared by green plants waste:
By thick green plants waste and thin green plants waste two types to including plant residue, weeds, fallen leaves, branch It crushes and sieves;
(3)It is prepared with the raw-soil:
Digging original soil, it is for use with the raw-soil to being formed after place original soil addition soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent;
(4)Layering consumption construction method:
Using the place after digging original soil, from bottom to surface layer, fill respectively thick solid waste layer, thin solid waste nitride layer, Thick green plants waste layer, thin solid waste nitride layer, thin green plants waste layer and match raw soil layer, and is finally overlying on plantation Soil layer, compaction treatment when placement in layers, you can the layering on the spot for completing building solid waste utilizes.
2. the layering on the spot of building solid waste described in claim 1 utilizes, which is characterized in that
The thick solid waste:Refer to the solid waste formed after building, terrace forcible entry after sorting, pulverization process, grain Solid waste of the diameter in 16cm-30cm;
The thin solid waste:Refer to the solid waste formed after building, terrace forcible entry after sorting, pulverization process, grain Diameter is in 16cm solid waste below.
3. the layering on the spot of building solid waste described in claim 1 utilizes, which is characterized in that
The thick green plants waste, produced by referring in urban green space or suburb forest land in green plants nature or maintenance processes Shrub lop, intermediate cutting object, turf-mown object, weeds, fallen leaves, branch, the waste that the showy flowers of herbaceous plants is discarded in garden and flower bed, Grain size 20-40mm;
The thin green plants waste, produced by referring in urban green space or suburb forest land in green plants nature or maintenance processes Shrub lop, intermediate cutting object, turf-mown object, weeds, fallen leaves, branch, the waste that the showy flowers of herbaceous plants is discarded in garden and flower bed, Grain size is less than 13mm.
4. the layering on the spot of building solid waste described in claim 1 utilizes, which is characterized in that described matches in the raw-soil Original soil, soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent addition mass ratio be 100:20-40:1-10:0.1-2.
5. the layering on the spot of building solid waste described in claim 1 utilizes, which is characterized in that described matches in the raw-soil Original soil, soil moved in improve the original, organic-inorganic improved materials and microbial bacterial agent addition mass ratio be 100:28:6:1.
6. the layering on the spot of the building solid waste described in claim 4 or 5 utilizes, which is characterized in that described is organic Inorganic Modified Material is by dry branches and fallen leaves waste, mushroom slag, acid-sludge, organic fertilizer, humic acid, polyacrylamide, desulfurated plaster, sulphur Sulphur 40-50 in mass ratio:10-15:16-25:10-15:1-5:1-8:3-7:5-10 is formed.
7. the layering on the spot of the building solid waste described in claim 6 utilizes, which is characterized in that the organic-inorganic Improved materials further include ammonium polyphosphate, and the additive amount of ammonium polyphosphate occupies the 10%-15% of machine Inorganic Modified Material;Described poly- third Acrylamide can be replaced by acrylic acid or acrylic amide modified chitosan;The desulfurated plaster can be replaced ardealite.
8. the layering on the spot of building solid waste described in claim 1 utilizes, which is characterized in that the step(4) In, from bottom to surface layer, thick solid waste layer is filled respectively, thin solid waste nitride layer, thick green plants waste layer, is carefully consolidated Body waste layer, thin green plants waste layer and the thickness with raw soil layer be followed successively by 25-50cm, 25-50cm, 10-20cm, 10-20cm、10-20cm、50cm。
9. the layering on the spot of building solid waste described in claim 1 utilizes, which is characterized in that the step(4) In, from bottom to surface layer, thick solid waste layer is filled respectively, thin solid waste nitride layer, thick green plants waste layer, is carefully consolidated Body waste layer, thin green plants waste layer and the thickness with raw soil layer be followed successively by 40cm, 30cm, 15cm, 15cm, 15cm, 50cm。
10. the layering on the spot of claim 1-9 any one of them building solid waste utilizes on reducing soil alkaline Application.
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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109095875A (en) * 2018-10-15 2018-12-28 葛洲坝当阳水泥有限公司 The method for manufacturing compressive resistance roadbed material with building waste
CN112292957A (en) * 2020-10-30 2021-02-02 中国科学院地理科学与资源研究所 Method for repairing ammonia nitrogen and sulfate radical pollution of ionic storage yard
CN114190130A (en) * 2021-12-15 2022-03-18 中国科学院武汉岩土力学研究所 Artificial soil for treating saline-alkali soil and use method thereof
CN115777487A (en) * 2022-11-29 2023-03-14 上海市园林科学规划研究院 Prepared soil prepared by using solid waste as raw material and application thereof

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20020067953A1 (en) * 2000-09-05 2002-06-06 Ankeny Mark D. Design, monitoring and control of soil carburetors for degradation of volatile compounds
JP3896444B2 (en) * 2001-03-01 2007-03-22 Dowaエコシステム株式会社 Detoxification method for contaminated soil
CN104719055A (en) * 2015-03-24 2015-06-24 沈阳市园林科学研究院 Layering covering method for garden greenbelt organic mulches
CN104763017A (en) * 2015-04-20 2015-07-08 江苏山水环境建设集团股份有限公司 Ground permeating rainwater recovery system utilizing building waste materials and construction method of ground permeating rainwater recovery system
CN105110717A (en) * 2015-07-20 2015-12-02 上海宝田新型建材有限公司 Foundation reinforcement material, preparation method and application thereof
CN106613138A (en) * 2016-11-16 2017-05-10 西施生态科技股份有限公司 Ecological restoration method of solid waste yards
CN206251590U (en) * 2016-12-07 2017-06-16 无锡市鸣腾园林工程股份有限公司 Ecology of alkali saline land comprehensive improvement system
CN107371432A (en) * 2017-08-30 2017-11-24 中国冶集团有限公司 A kind of method using charcoal soil and construction waste soil comprehensive improvement beach sandy soil

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20020067953A1 (en) * 2000-09-05 2002-06-06 Ankeny Mark D. Design, monitoring and control of soil carburetors for degradation of volatile compounds
JP3896444B2 (en) * 2001-03-01 2007-03-22 Dowaエコシステム株式会社 Detoxification method for contaminated soil
CN104719055A (en) * 2015-03-24 2015-06-24 沈阳市园林科学研究院 Layering covering method for garden greenbelt organic mulches
CN104763017A (en) * 2015-04-20 2015-07-08 江苏山水环境建设集团股份有限公司 Ground permeating rainwater recovery system utilizing building waste materials and construction method of ground permeating rainwater recovery system
CN105110717A (en) * 2015-07-20 2015-12-02 上海宝田新型建材有限公司 Foundation reinforcement material, preparation method and application thereof
CN106613138A (en) * 2016-11-16 2017-05-10 西施生态科技股份有限公司 Ecological restoration method of solid waste yards
CN206251590U (en) * 2016-12-07 2017-06-16 无锡市鸣腾园林工程股份有限公司 Ecology of alkali saline land comprehensive improvement system
CN107371432A (en) * 2017-08-30 2017-11-24 中国冶集团有限公司 A kind of method using charcoal soil and construction waste soil comprehensive improvement beach sandy soil

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
张浪等: "关于园林绿化快速成景配生土的思考", 《土壤通报》 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109095875A (en) * 2018-10-15 2018-12-28 葛洲坝当阳水泥有限公司 The method for manufacturing compressive resistance roadbed material with building waste
CN112292957A (en) * 2020-10-30 2021-02-02 中国科学院地理科学与资源研究所 Method for repairing ammonia nitrogen and sulfate radical pollution of ionic storage yard
CN114190130A (en) * 2021-12-15 2022-03-18 中国科学院武汉岩土力学研究所 Artificial soil for treating saline-alkali soil and use method thereof
CN115777487A (en) * 2022-11-29 2023-03-14 上海市园林科学规划研究院 Prepared soil prepared by using solid waste as raw material and application thereof

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