CN113519372A - Preparation method of composite green repairing backfill material - Google Patents
Preparation method of composite green repairing backfill material Download PDFInfo
- Publication number
- CN113519372A CN113519372A CN202110944711.4A CN202110944711A CN113519372A CN 113519372 A CN113519372 A CN 113519372A CN 202110944711 A CN202110944711 A CN 202110944711A CN 113519372 A CN113519372 A CN 113519372A
- Authority
- CN
- China
- Prior art keywords
- parts
- solid waste
- backfill material
- restoration
- seeds
- 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
- 239000000463 material Substances 0.000 title claims abstract description 42
- 238000002360 preparation method Methods 0.000 title claims abstract description 7
- 239000002131 composite material Substances 0.000 title claims description 5
- 239000010902 straw Substances 0.000 claims abstract description 49
- 240000004784 Cymbopogon citratus Species 0.000 claims abstract description 38
- 235000017897 Cymbopogon citratus Nutrition 0.000 claims abstract description 38
- 239000002689 soil Substances 0.000 claims abstract description 36
- 239000002910 solid waste Substances 0.000 claims abstract description 31
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 claims abstract description 30
- 239000000920 calcium hydroxide Substances 0.000 claims abstract description 30
- 229910001861 calcium hydroxide Inorganic materials 0.000 claims abstract description 30
- 235000011116 calcium hydroxide Nutrition 0.000 claims abstract description 30
- 238000002156 mixing Methods 0.000 claims abstract description 25
- 239000002245 particle Substances 0.000 claims abstract description 24
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 22
- 239000003245 coal Substances 0.000 claims abstract description 20
- 239000000203 mixture Substances 0.000 claims abstract description 13
- 239000003818 cinder Substances 0.000 claims abstract description 12
- 241000234642 Festuca Species 0.000 claims abstract description 10
- 239000003463 adsorbent Substances 0.000 claims abstract description 7
- 239000002994 raw material Substances 0.000 claims abstract description 7
- 238000003825 pressing Methods 0.000 claims abstract description 4
- 238000002791 soaking Methods 0.000 claims abstract description 4
- 238000007873 sieving Methods 0.000 claims abstract description 3
- 238000000034 method Methods 0.000 claims description 19
- 239000002699 waste material Substances 0.000 claims description 19
- 239000004567 concrete Substances 0.000 claims description 16
- 238000005507 spraying Methods 0.000 claims description 15
- 239000002985 plastic film Substances 0.000 claims description 10
- 229920006255 plastic film Polymers 0.000 claims description 10
- 238000010276 construction Methods 0.000 claims description 9
- YYRMJZQKEFZXMX-UHFFFAOYSA-L calcium bis(dihydrogenphosphate) Chemical class [Ca+2].OP(O)([O-])=O.OP(O)([O-])=O YYRMJZQKEFZXMX-UHFFFAOYSA-L 0.000 claims description 8
- 229920002472 Starch Polymers 0.000 claims description 7
- 239000011449 brick Substances 0.000 claims description 7
- 235000019698 starch Nutrition 0.000 claims description 7
- 239000008107 starch Substances 0.000 claims description 7
- 239000011381 foam concrete Substances 0.000 claims description 6
- 239000002253 acid Substances 0.000 claims description 4
- 229920001495 poly(sodium acrylate) polymer Polymers 0.000 claims description 4
- NNMHYFLPFNGQFZ-UHFFFAOYSA-M sodium polyacrylate Chemical compound [Na+].[O-]C(=O)C=C NNMHYFLPFNGQFZ-UHFFFAOYSA-M 0.000 claims description 4
- 238000004519 manufacturing process Methods 0.000 claims description 3
- 239000003125 aqueous solvent Substances 0.000 claims description 2
- 241000894007 species Species 0.000 claims 2
- WWILHZQYNPQALT-UHFFFAOYSA-N 2-methyl-2-morpholin-4-ylpropanal Chemical compound O=CC(C)(C)N1CCOCC1 WWILHZQYNPQALT-UHFFFAOYSA-N 0.000 claims 1
- 230000001965 increasing effect Effects 0.000 description 28
- 239000005416 organic matter Substances 0.000 description 14
- 239000003513 alkali Substances 0.000 description 11
- 241001464837 Viridiplantae Species 0.000 description 10
- 239000000243 solution Substances 0.000 description 10
- 230000004083 survival effect Effects 0.000 description 10
- 241000218642 Abies Species 0.000 description 7
- 235000008331 Pinus X rigitaeda Nutrition 0.000 description 7
- 235000011613 Pinus brutia Nutrition 0.000 description 7
- 241000018646 Pinus brutia Species 0.000 description 7
- 241000124033 Salix Species 0.000 description 7
- 244000025254 Cannabis sativa Species 0.000 description 6
- 235000016709 nutrition Nutrition 0.000 description 6
- 230000035764 nutrition Effects 0.000 description 6
- 238000003860 storage Methods 0.000 description 6
- 206010016654 Fibrosis Diseases 0.000 description 5
- 230000004761 fibrosis Effects 0.000 description 5
- 230000000052 comparative effect Effects 0.000 description 4
- 230000018109 developmental process Effects 0.000 description 4
- 241000196324 Embryophyta Species 0.000 description 3
- BIGPRXCJEDHCLP-UHFFFAOYSA-N ammonium bisulfate Chemical compound [NH4+].OS([O-])(=O)=O BIGPRXCJEDHCLP-UHFFFAOYSA-N 0.000 description 3
- 230000009286 beneficial effect Effects 0.000 description 3
- 244000166675 Cymbopogon nardus Species 0.000 description 2
- 239000003929 acidic solution Substances 0.000 description 2
- 230000008595 infiltration Effects 0.000 description 2
- 238000001764 infiltration Methods 0.000 description 2
- 238000005065 mining Methods 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 235000019691 monocalcium phosphate Nutrition 0.000 description 2
- 235000015097 nutrients Nutrition 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 230000008439 repair process Effects 0.000 description 2
- 238000004062 sedimentation Methods 0.000 description 2
- 239000002893 slag Substances 0.000 description 2
- 238000009331 sowing Methods 0.000 description 2
- 239000007921 spray Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 239000002585 base Substances 0.000 description 1
- 238000009395 breeding Methods 0.000 description 1
- 230000001488 breeding effect Effects 0.000 description 1
- 229960005069 calcium Drugs 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 229940062672 calcium dihydrogen phosphate Drugs 0.000 description 1
- 229910000389 calcium phosphate Inorganic materials 0.000 description 1
- 239000001506 calcium phosphate Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000002708 enhancing effect Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 230000007717 exclusion Effects 0.000 description 1
- 239000004744 fabric Substances 0.000 description 1
- 230000035558 fertility Effects 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 230000035784 germination Effects 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 235000010755 mineral Nutrition 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 229910000150 monocalcium phosphate Inorganic materials 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- 150000007524 organic acids Chemical class 0.000 description 1
- 230000002093 peripheral effect Effects 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 230000002035 prolonged effect Effects 0.000 description 1
- 230000001681 protective effect Effects 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 239000012047 saturated solution Substances 0.000 description 1
- 235000013619 trace mineral Nutrition 0.000 description 1
- 239000011573 trace mineral Substances 0.000 description 1
- 230000004584 weight gain Effects 0.000 description 1
- 235000019786 weight gain Nutrition 0.000 description 1
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
- A01G24/10—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
- A01C—PLANTING; SOWING; FERTILISING
- A01C1/00—Apparatus, or methods of use thereof, for testing or treating seed, roots, or the like, prior to sowing or planting
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01C—PLANTING; SOWING; FERTILISING
- A01C1/00—Apparatus, or methods of use thereof, for testing or treating seed, roots, or the like, prior to sowing or planting
- A01C1/06—Coating or dressing seed
-
- 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
- A01G20/00—Cultivation of turf, lawn or the like; Apparatus or methods therefor
-
- 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
- A01G24/17—Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material containing slag
-
- 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
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Environmental Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Inorganic Chemistry (AREA)
- Soil Sciences (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
The invention discloses a preparation method of a re-greening restoration backfill material, which comprises the following steps: obtaining raw materials, wherein the raw materials comprise, by weight, 100 parts of extra soil, 10-15 parts of coal cinder, 0.5-2 parts of dry cymbopogon citratus seeds, 10-20 parts of building solid waste, 20-30 parts of straws and 2-4 parts of slaked lime; pretreating and crushing building solid waste: crushing the building solid waste by a crusher, and sieving to obtain building solid waste particles with qualified sizes; premixing straws and slaked lime: adjusting the humidity of the straws, fully mixing the straws with slaked lime, and pressing and slaking the mixture under proper pressure; and (3) treating the seeds of the common fescue: soaking the dry citionella seeds in the water solution mixed with a proper amount of the adsorbent at room temperature until the citionella seeds are properly weighted; mixing the soil, coal cinder, dry Cymbopogon citratus seed, solid waste of building, straw and slaked lime. The scheme is convenient and simple to operate, and provides a preparation scheme of the high-efficiency green-recovering backfill material, so that the high-quality backfill material can be obtained more efficiently.
Description
Technical Field
The invention relates to an ecological restoration technology for a side slope of a mine pit, in particular to a preparation method of a re-greening restoration backfill material.
Background
The development and utilization of mineral resources such as coal and the like promote economic and social development and bring a series of ecological environment disasters. The method is characterized in that mine pits and the like left after the mining are finished can greatly influence the surface ecology and safety, the soil in a dumping field formed by stacking a large amount of stripped objects generated in the mining process is barren, in addition, the heavy truck rolls the soil in the dumping process to seriously compact the surface of the soil, so that the root pricking of plants is difficult, a large amount of surface runoff is formed under the rainfall condition, sedimentation cracks are generated due to the non-uniform sedimentation of the dumping field, the runoff is gathered and drilled into the cracks after rainfall, the infiltration is concentrated, the infiltration is exposed from the lower side slopes, and the collapse, the landslide and the slope debris flow are induced, and even the whole tatter is sunk. These all have a great influence on the production and life of the peripheral area.
For surface or underground leaving caused by production operation such as a mine pit, a landfill restoration scheme is generally adopted to restore the surface or underground leaving. In the traditional backfill materials, materials such as slag, concrete, industrial solid waste, building solid waste and the like are utilized in large quantity, and the recycling of waste resources is realized, but when the materials are soaked in underground water for a long time, alkaline substances are easily separated out to generate alkali return, so that the nutrition and planting capability of the backfill materials are influenced, and the greening work of a backfill area is further influenced. In addition, because the backfill material is relatively loose, water and soil loss is easy to generate, so that a protective net is usually covered on the ground in the conventional scheme, the construction time is prolonged, and the operation cost is increased. The information disclosed in this background section is only for enhancement of understanding of the general background of the invention and should not be taken as an acknowledgement or any form of suggestion that this information forms the prior art already known to a person skilled in the art.
Disclosure of Invention
The invention aims to provide a preparation method of a re-greening restoration backfill material, which obtains a re-greening restoration material for purposefully designing pits and the like by selecting and processing raw materials, effectively improves the recycling of waste resources, and is beneficial to improving the ecological restoration of backfill soil while enhancing the water and soil fixing capacity by adopting special auxiliary restoration plants.
In order to achieve the above object, an embodiment of the present invention provides a method for preparing a composite green repair backfill material, including: obtaining raw materials, wherein the raw materials comprise, by weight, 100 parts of soil, 10-15 parts of coal cinder, 0.5-2 parts of dry cymbopogon citratus seeds, 10-20 parts of building solid waste, 20-30 parts of straws and 2-4 parts of slaked lime; pretreating and crushing building solid waste: crushing the building solid waste by a crusher, and sieving to obtain building solid waste particles with qualified sizes; premixing straws and slaked lime: adjusting the humidity of the straws, fully mixing the straws with slaked lime, and pressing and slaking the mixture under proper pressure; and (3) treating the seeds of the common fescue: soaking the dry citionella seeds in the water solution mixed with a proper amount of the adsorbent at room temperature until the citionella seeds are properly weighted; mixing the soil, coal cinder, dry Cymbopogon citratus seed, solid waste of building, straw and slaked lime.
In one or more embodiments of the present invention, the construction waste comprises waste bricks or waste concrete precast blocks or foamed concrete blocks.
In one or more embodiments of the invention, the crushing of the solid waste of the building is to crush waste bricks or waste concrete precast blocks to a particle size of 1-2 cm or foam concrete blocks to a particle size of 0.5-1 cm by using a jaw crusher or a roller crusher.
In one or more embodiments of the invention, the construction solid waste is also subjected to spray treatment by using an acidic solution at room temperature, and the spray amount of the construction solid waste per cubic meter is 10-20 Kg.
In one or more embodiments of the invention, the acidic solution is a saturated solution of monocalcium phosphate or a 1M solution of ammonium bisulfate. The solution with weak acidity is selected, so that the short-term acid impact with overlarge acid concentration can be effectively avoided, the influence on the growth of the plants in the cymbopogon citratus or the restoration area is caused, and the environment friendliness is good while the acid-base property of the soil is balanced for a long time.
In one or more embodiments of the invention, the mixed straw and hydrated lime is pressed and hydrated to stack the mixed straw and hydrated lime to a height of 3-4m and cover a plastic film, and 200-400kg/m is applied by briquetting2Stacking for 6-8h under the pressure of (3).
In one or more embodiments of the invention, the moisture content of the straw is 10-20 v/v%.
In one or more embodiments of the invention, the citronella species is treated by soaking the citronella species to a weight gain of 10-20%.
In one or more embodiments of the invention, the adsorbent is gelatinized starch or sodium polyacrylate. Preferably, the adsorbent is present in the aqueous solvent in an amount of 0.1 to 0.3 wt.%.
Compared with the prior art, the method has the advantages that the operation is convenient, the operation convenience is good, the environment friendliness is good, the greening restoration backfill material obtained by the method fully utilizes industrial solid wastes as the backfill material, the waste resources are recycled, meanwhile, the solid wastes are utilized to provide trace elements for a backfill material area, all the micropore structures of the solid wastes are fully utilized, a proper amount of water storage and microorganism breeding space is provided underground, the fixation of fabric root systems in the restoration area and the development and growth of the root systems are facilitated, and the growth and development of the root systems are promoted. Of course, the water storage structures are also beneficial to increasing the storage of alkali educts in the solid waste and the neutralization reaction of the alkali educts with the stored calcium dihydrogen phosphate, playing a role in slow release and consumption, fixing elements such as phosphorus, calcium and the like, and simultaneously being beneficial to the storage of organic acid and nutrient elements generated by the decay of organic matters in a long term, thereby achieving the purposes of environmental alkali return and fertilizer storage. Meanwhile, the characteristics of the lemongrass are fully utilized, the soil fertility restoration of a restoration area is effectively enhanced while the normal green-recovering planting operation is not influenced, the absorption and storage of nutrient substances by solid waste micropores in backfill materials are accelerated, and the restoration efficiency and speed are effectively enhanced.
Detailed Description
The following detailed description of specific embodiments of the invention is provided, but it should be understood that the scope of the invention is not limited to the specific embodiments.
Throughout the specification and claims, unless explicitly stated otherwise, the word "comprise", or variations such as "comprises" or "comprising", will be understood to imply the inclusion of a stated element or component but not the exclusion of any other element or component.
Example 1
The re-greening restoration backfill material comprises, by weight, 100 parts of foreign soil, 10 parts of coal cinder and 0.5 part of dry cymbopogon citratus seeds, 10 parts of broken blocks particles with the particle size of 1-2 cm obtained by crushing waste bricks through a jaw crusher, 20 parts of straws and 2 parts of hydrated lime which are mixed in advance are added for fully mixing, after mixing, a mixture of straws (measured by compacted volume) with the water content of 10 v/v% and the hydrated lime is piled up to the height of 3m and covered with a plastic film, and then concrete is pressed into 200kg/m blocks2Is stored for 8 hours under the pressure of the straw, so as to realize the preliminary fibrosis and curing of the straw. Spraying saturated calcium dihydrogen phosphate solution at room temperature before mixing, wherein the spraying amount is 10kg/m3. The common fescue seeds are soaked in normal-temperature water added with 0.1 wt.% of gelatinized starch before being mixed until the weight of the grass seeds is increased by 10%.
In the implementation of the embodiment, the method is applied to open-air coal pits in certain places in Shanxi, the backfill material is 30cm thick, trees such as pine trees, fir trees and willow trees are planted on the ground after the restoration in spring, and the growth state of the citionella canadensis is monitored. The survival rate of green plants in one year is about 98%, the survival rate of green plants in two years is about 97%, the growth situation is good, the nutrition is not poor, the growth state is normal, and from 2 years to 5 years, compared with the growth situation of forest trees in the same area, the growth situation of the forest trees is increased by 5-10% by calculating the chest circumference of the forest trees at a distance of 1m from the ground every year.
Meanwhile, the growth state of the lemongrass in a pit repairing area is good, the coverage rate of the lemongrass on the ground surface reaches more than 70% in 3 months in the first year, the complete coverage is realized in 4-7 months in the current year, the organic matter content in the soil is increased by 0.8-1% in the current year after the lemongrass is completely rotted, and the organic matter content is gradually increased to 1.1-1.8%, 2.2-2.5%, 2.7-3.2% and 3.5-4% in the following 2-5 years. And the pH value of the soil is monitored within 5 years of restoration, and the pH value of a restoration area is found to be stable without obvious alkali return.
Example 2
The re-greening restoration backfill material comprises, by weight, 100 parts of foreign soil, 12 parts of coal cinder and 2 parts of dry cymbopogon citratus seeds, 15 parts of broken block particles with the particle size of 1-2 cm and obtained by crushing waste concrete precast blocks through a roller crusher, 22 parts of straws and 3 parts of hydrated lime which are mixed in advance are added for fully mixing, a mixture of the straws (measured by compacted volume) with the water content of 15 v/v% and the hydrated lime is stacked for 4m high and covered with a plastic film, and concrete briquettes are used for covering 400kg/m2Is stored for 7.5 hours under the pressure of the straw, so as to realize the preliminary fiberization and curing of the straw. Spraying saturated calcium dihydrogen phosphate solution at room temperature before mixing, wherein the spraying amount is 20kg/m3. The common fescue seeds are soaked in normal-temperature water added with 0.15 wt.% of gelatinized starch before being mixed until the weight of the grass seeds is increased by 20%.
In the implementation of the embodiment, the method is applied to open-air coal pits in certain places in Shanxi, the backfill material is 30cm thick, trees such as pine trees, fir trees and willow trees are planted on the ground after the restoration in spring, and the growth state of the citionella canadensis is monitored. The survival rate of green plants in one year is about 98%, the survival rate of green plants in two years is about 97%, the growth situation is good, the nutrition is not poor, the growth state is normal, and from 2 years to 5 years, compared with the growth situation of forest trees in the same area, the growth situation of the forest trees is increased by 5-10% by calculating the chest circumference of the forest trees at a distance of 1m from the ground every year.
Meanwhile, the growth state of the lemongrass in a pit repairing area is good, the coverage rate of the lemongrass on the ground surface reaches more than 70% in 3 months in the first year, the complete coverage is realized in 4-7 months in the current year, the organic matter content in the soil is increased by 0.7-1% in the current year after the lemongrass is completely rotted, and the organic matter content is gradually increased to 1.1-1.5%, 2.2-2.4%, 2.6-3.0% and 3.2-3.6% in the following 2-5 years. And the pH value of the soil is monitored within 5 years of restoration, and the pH value of a restoration area is found to be stable without obvious alkali return.
Example 3
The re-greening restoration backfill material comprises, by weight, 100 parts of foreign soil, 13 parts of coal cinder and 1.3 parts of dry cymbopogon citratus seeds, 20 parts of broken particles with the particle size of 1-2 cm, which are obtained by crushing waste concrete precast blocks by a jaw crusher, 28 parts of straws and 4 parts of hydrated lime which are mixed in advance, the mixture of the straws with the water content of 18 v/v% (measured by compacted volume) and the hydrated lime is piled up to the height of 3.4m and covered with a plastic film, and then concrete briquettes are used for covering the plastic film at the height of 300kg/m2Is stored for 6.5 hours under the pressure of the straw, so as to realize the preliminary fiberization and curing of the straw. Spraying saturated calcium dihydrogen phosphate solution at room temperature before mixing, wherein the spraying amount is 12kg/m3. Before mixing, the common fescue seeds are soaked in normal-temperature water added with 0.23 wt.% of sodium polyacrylate until the weight of the grass seeds is increased by 15%.
In the implementation of the embodiment, the method is applied to open-air coal pits in certain places in Shanxi, the backfill material is 30cm thick, trees such as pine trees, fir trees and willow trees are planted on the ground after the restoration in spring, and the growth state of the citionella canadensis is monitored. The survival rate of green plants in one year is about 98%, the survival rate of green plants in two years is about 97%, the growth situation is good, the nutrition is not poor, the growth state is normal, and from 2 years to 5 years, compared with the growth situation of forest trees in the same area, the growth situation of the forest trees is increased by 5-10% by calculating the chest circumference of the forest trees at a distance of 1m from the ground every year.
Meanwhile, the growth state of the lemongrass in a pit repairing area is good, the coverage rate of the lemongrass on the ground surface reaches more than 70% in 3 months in the first year, the complete coverage is realized in 4-7 months in the current year, the organic matter content in the soil is increased by 0.6-0.9% in the current year after the lemongrass is completely rotted, and the organic matter content is gradually increased to 1.1-1.6%, 2.1-2.3%, 2.7-3.1% and 3.4-3.8% in the following 2-5 years. And the pH value of the soil is monitored within 5 years of restoration, and the pH value of a restoration area is found to be stable without obvious alkali return.
Example 4
The green-recovery repair backfill material comprises, by weight, 100 parts of foreign soil and coal14 parts of slag, 1.8 parts of dry cymbopogon citratus seeds, 10 parts of broken particles with the particle size of 1-2 cm obtained by crushing waste concrete precast blocks by a roller crusher, 5 parts of broken particles with the particle size of 0.5-1 cm obtained by crushing foam concrete blocks, 23 parts of straws and 2.4 parts of hydrated lime which are mixed in advance are added for full mixing, after mixing, a mixture of straws (measured by compacted volume) with the water content of 13 v/v% and the hydrated lime is piled up to the height of 3.5m and covered with a plastic film, and then concrete briquettes are used for 250kg/m2Is stored for 7 hours under the pressure of the straw, so as to realize the preliminary fibrosis and curing of the straw. The construction solid waste is treated by 1M ammonium bisulfate solution spraying at room temperature before mixing, the spraying amount is 14kg/M3. The common fescue seeds are soaked in normal-temperature water added with 0.13 wt.% of gelatinized starch before being mixed until the weight of the grass seeds is increased by 18%.
In the implementation of the embodiment, the method is applied to open-air coal pits in certain places in Shanxi, the backfill material is 30cm thick, trees such as pine trees, fir trees and willow trees are planted on the ground after the restoration in spring, and the growth state of the citionella canadensis is monitored. The survival rate of green plants in one year is about 98%, the survival rate of green plants in two years is about 97%, the growth situation is good, the nutrition is not poor, the growth state is normal, and from 2 years to 5 years, compared with the growth situation of forest trees in the same area, the growth situation of the forest trees is increased by 7-12% by calculating the chest circumference of the forest trees at a distance of 1m from the ground every year.
Meanwhile, the growth state of the lemongrass in a pit repairing area is good, the coverage rate of the lemongrass on the ground surface reaches more than 70% in 3 months in the first year, the complete coverage is realized in 4-7 months in the current year, the organic matter content in the soil is increased by 0.9-1% in the current year after the lemongrass is completely rotted, and the organic matter content is gradually increased to 1.3-2.0%, 2.4-2.6%, 2.8-3.5% and 3.7-4.3% in the following 2-5 years. And the pH value of the soil is monitored within 5 years of restoration, and the pH value of a restoration area is found to be stable without obvious alkali return.
Example 5
The re-greening restoration backfill material comprises, by weight, 100 parts of foreign soil, 15 parts of coal cinder, 0.8 part of dry cymbopogon citratus seeds, 15 parts of broken blocks of 1-2 cm in particle size obtained by crushing waste bricks through a roller crusher, and foamed concrete blocks3 parts of the obtained broken particles with the particle size of 0.5-1 cm are added with 30 parts of straws and 3.6 parts of hydrated lime which are mixed in advance and fully mixed, after mixing, the mixture of the straws (measured by compacted volume) with the water content of 20 v/v% and the hydrated lime is piled up for 3.2m and covered with a plastic film, and then the mixture is pressed into blocks with the concrete of 350kg/m2Is stored for 6 hours under the pressure of the straw, so as to realize the preliminary fibrosis and curing of the straw. The construction solid waste is treated by 1M ammonium bisulfate solution spraying at room temperature before mixing, the spraying amount is 16kg/M3. Before mixing, the seeds of the common fescue are soaked in normal-temperature water added with 0.3 wt.% of sodium polyacrylate until the weight of the seeds is increased by 16%.
In the implementation of the embodiment, the method is applied to open-air coal pits in certain places in Shanxi, the backfill material is 30cm thick, trees such as pine trees, fir trees and willow trees are planted on the ground after the restoration in spring, and the growth state of the citionella canadensis is monitored. The survival rate of green plants in one year is about 98%, the survival rate of green plants in two years is about 97%, the growth situation is good, the nutrition is not poor, the growth state is normal, and from 2 years to 5 years, compared with the growth situation of forest trees in the same area, the growth situation of the forest trees is calculated by the chest circumference of the forest trees which are 1m away from the ground every year, the growth situation is increased by 8-13%.
Meanwhile, the growth state of the lemongrass in a pit repairing area is good, the coverage rate of the lemongrass on the ground surface reaches over 75% in 3 months in the first year, the complete coverage is realized in 4-7 months in the current year, the organic matter content in the soil is increased by 0.8-1.2% in the current year after the lemongrass is completely rotted, and the organic matter content is gradually increased to 1.5-1.8%, 2.3-2.7%, 2.8-3.4% and 3.7-4.2% in the following 2-5 years. And the pH value of the soil is monitored within 5 years of restoration, and the pH value of a restoration area is found to be stable without obvious alkali return.
Comparative example 1
The re-greening restoration backfill material of the comparative example comprises, by weight, 100 parts of foreign soil, 10 parts of coal cinder and 0.5 part of dry cymbopogon citratus seeds, 10 parts of broken particles with the particle size of 1-2 cm obtained by crushing waste concrete precast blocks by a jaw crusher, 20 parts of straws and 2 parts of hydrated lime which are mixed in advance are added for full mixing, a mixture of straws (measured by compacted volume) with the water content of 10 v/v% and the hydrated lime is piled up to 3m high and covered with a plastic film,then pressing the mixture into blocks of 200kg/m by using concrete2Is stored for 8 hours under the pressure of the straw, so as to realize the preliminary fibrosis and curing of the straw. Spraying saturated calcium dihydrogen phosphate solution at room temperature before mixing, wherein the spraying amount is 10kg/m3. Before mixing, the common fescue seeds are soaked in normal-temperature water added with 0.1 wt.% of gelatinized starch until the weight of the grass seeds is increased by 40%.
When the scheme is implemented, the application is carried out in an open-air coal mine pit in a place in Shanxi, the thickness of the backfill material is 30cm, after the restoration, the growth state of trees such as pine trees, fir trees, willow trees and the like planted on the ground is restored in spring, and meanwhile, the growth state of the lemongrass is monitored.
Meanwhile, the growth state of the lemongrass in a pit repairing area is good, the coverage rate of the lemongrass on the ground surface reaches 40-50% in 3 months in the first year, a large part of non-germination vacancy exists in a sowing area, partial seeds are found to mildew after soil turning, the organic matter content in the soil is increased by 0.1-0.2% in the current year after the lemongrass is completely rotten, and the organic matter content is gradually increased to 0.2-0.3%, 0.4-0.6%, 0.7-0.9% and 1-1.2% in the later 2-5 years. And the pH value of the soil is monitored within 5 years of restoration, and the pH value of a restoration area is found to be stable without obvious alkali return.
Comparative example 2
The re-greening restoration backfill material of the comparative example comprises, by weight, 100 parts of foreign soil, 10 parts of coal cinder and 0.5 part of dry cymbopogon citratus seeds, 10 parts of broken blocks particles with the particle size of 1-2 cm obtained by crushing waste bricks through a roller crusher, 20 parts of straws and 2 parts of hydrated lime which are mixed in advance are added for full mixing, the mixture of the straws with the water content of 10 v/v% (measured by compacted volume) and the hydrated lime is piled up to the height of 3m and covered with a plastic film, and then the mixture is pressed into 200kg/m by a concrete block2Is stored for 8 hours under the pressure of the straw, so as to realize the preliminary fibrosis and curing of the straw. Spraying saturated calcium dihydrogen phosphate solution at room temperature before mixing, wherein the spraying amount is 10kg/m3. The common fescue seeds are soaked in normal-temperature water added with 0.1 wt.% of gelatinized starch before being mixed until the weight of the grass seeds is increased by 5%.
When the scheme is implemented, the application is carried out in an open-air coal mine pit in a place in Shanxi, the thickness of the backfill material is 30cm, after the restoration, the growth state of trees such as pine trees, fir trees, willow trees and the like planted on the ground is restored in spring, and meanwhile, the growth state of the lemongrass is monitored.
Meanwhile, the growth state of the lemongrass in a pit repairing area is good, the coverage rate of the lemongrass on the ground surface reaches 40-50% in 3 months in the first year, a large part of non-germinated vacant area exists in a sowing area, the organic matter content in the soil is increased by 0.1-0.3% in the current year after the lemongrass are completely rotted, and the organic matter content is gradually increased to 0.4-0.5%, 0.5-0.7%, 0.8-1% and 1.1-1.3% in the following 2-5 years. And the pH value of the soil is monitored within 5 years of restoration, and the pH value of a restoration area is found to be stable without obvious alkali return.
The foregoing descriptions of specific exemplary embodiments of the present invention have been presented for purposes of illustration and description. It is not intended to limit the invention to the precise form disclosed, and obviously many modifications and variations are possible in light of the above teaching. The exemplary embodiments were chosen and described in order to explain certain principles of the invention and its practical application to enable one skilled in the art to make and use various exemplary embodiments of the invention and various alternatives and modifications as are suited to the particular use contemplated. It is intended that the scope of the invention be defined by the claims and their equivalents.
Claims (10)
1. A preparation method of a complex green restoration backfill material comprises the following steps:
obtaining raw materials, wherein the raw materials comprise, by weight, 100 parts of soil, 10-15 parts of coal cinder, 0.5-2 parts of dry cymbopogon citratus seeds, 10-20 parts of building solid waste, 20-30 parts of straws and 2-4 parts of slaked lime;
pretreating and crushing building solid waste: crushing the building solid waste by a crusher, and sieving to obtain building solid waste particles with qualified sizes;
premixing straws and slaked lime: adjusting the humidity of the straws, fully mixing the straws with slaked lime, and pressing and slaking the mixture under proper pressure;
and (3) treating the seeds of the common fescue: soaking the dry citionella seeds in the water solution mixed with a proper amount of the adsorbent at room temperature until the citionella seeds are properly weighted;
mixing the soil, coal cinder, dry Cymbopogon citratus seed, solid waste of building, straw and slaked lime.
2. The method for preparing a re-greening restoration backfill material according to claim 1, wherein the construction solid waste comprises waste bricks or waste concrete precast blocks or foam concrete blocks.
3. The method for preparing the re-greening restoration backfill material according to claim 2, wherein the step of crushing the building solid waste is to crush waste bricks or waste concrete precast blocks to a particle size of 1-2 cm or to crush foam concrete blocks to a particle size of 0.5-1 cm by using a jaw crusher or a roller crusher.
4. A method for preparing a re-greening restoration backfill material according to any one of claims 1-3, characterized in that the construction solid waste is also sprayed with an acid solution at room temperature, and the spraying amount per cubic meter of construction solid waste is 10-20 Kg.
5. The method for preparing a composite green repairing backfill material according to the claim 4, characterized in that the acid solution is saturated calcium dihydrogen phosphate solution or 1M ammonium hydrogen sulfate solution.
6. The method for preparing a composite green restoration backfill material according to claim 1, wherein the straw and hydrated lime after mixing are pressed and hydrated to stack the mixed straw and hydrated lime to a height of 3-4m and cover a plastic film, and 200-400kg/m is applied by briquetting2Stacking for 6-8h under the pressure of (3).
7. The method for preparing a re-greening restoration backfill material according to claim 6, wherein the moisture content of the straw is 10-20 v/v%.
8. The method for preparing a re-greening restoration backfill material according to claim 1, characterized in that the citionella species is soaked to increase the weight by 10-20% during the citionella species treatment.
9. The method for preparing a greening restoration backfilling material according to claim 1, wherein the adsorbent is gelatinized starch or sodium polyacrylate.
10. The method of making a greenish restoration backfill material according to claim 9, wherein the adsorbent is present in the aqueous solvent in an amount of 0.1-0.3 wt.%.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202110944711.4A CN113519372A (en) | 2021-08-17 | 2021-08-17 | Preparation method of composite green repairing backfill material |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202110944711.4A CN113519372A (en) | 2021-08-17 | 2021-08-17 | Preparation method of composite green repairing backfill material |
Publications (1)
Publication Number | Publication Date |
---|---|
CN113519372A true CN113519372A (en) | 2021-10-22 |
Family
ID=78091749
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202110944711.4A Pending CN113519372A (en) | 2021-08-17 | 2021-08-17 | Preparation method of composite green repairing backfill material |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN113519372A (en) |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101960980A (en) * | 2010-02-24 | 2011-02-02 | 武汉市林业果树科学研究所 | Roof greening light host material made from industrial and agricultural wastes |
CN105908693A (en) * | 2016-04-27 | 2016-08-31 | 杭州中艺生态环境工程有限公司 | Planting blanket used for original soil improvement of muddy coastal saline-alkali land |
CN106132188A (en) * | 2014-03-28 | 2016-11-16 | 住友化学株式会社 | Rice coating material and coated rice seed |
CN108298893A (en) * | 2018-02-05 | 2018-07-20 | 湖州中煤地质工程有限公司 | A kind of Slope greening construction method and Slope greening matrix concrete |
CN110121968A (en) * | 2018-02-02 | 2019-08-16 | 中国科学院寒区旱区环境与工程研究所 | A kind of mining area stone pit ecological restoring method |
CN112715316A (en) * | 2020-12-25 | 2021-04-30 | 中煤浙江生态环境发展有限公司 | Re-greening restoration backfill planting material and application thereof |
-
2021
- 2021-08-17 CN CN202110944711.4A patent/CN113519372A/en active Pending
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101960980A (en) * | 2010-02-24 | 2011-02-02 | 武汉市林业果树科学研究所 | Roof greening light host material made from industrial and agricultural wastes |
CN106132188A (en) * | 2014-03-28 | 2016-11-16 | 住友化学株式会社 | Rice coating material and coated rice seed |
CN105908693A (en) * | 2016-04-27 | 2016-08-31 | 杭州中艺生态环境工程有限公司 | Planting blanket used for original soil improvement of muddy coastal saline-alkali land |
CN110121968A (en) * | 2018-02-02 | 2019-08-16 | 中国科学院寒区旱区环境与工程研究所 | A kind of mining area stone pit ecological restoring method |
CN108298893A (en) * | 2018-02-05 | 2018-07-20 | 湖州中煤地质工程有限公司 | A kind of Slope greening construction method and Slope greening matrix concrete |
CN112715316A (en) * | 2020-12-25 | 2021-04-30 | 中煤浙江生态环境发展有限公司 | Re-greening restoration backfill planting material and application thereof |
Non-Patent Citations (1)
Title |
---|
陈伟等: "矿山废弃地生态环境恢复治理进展", 《环境工程技术学报》 * |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
WO2022160922A1 (en) | Solid waste-based porous material, preparation method therefor and method for ecological restoration of coal gangue mountains | |
CN102775206A (en) | Method for preparing improved matrix capable of improving urban soil properties | |
CN110637698A (en) | Organic garden soil prepared from construction waste and municipal sludge | |
CN108901559B (en) | Vegetation restoration method for coal mining area | |
CN110090845B (en) | Method for converting red mud into soil by using pyrite cinder | |
CN101503327A (en) | Special improver for alkaline soil alkalinity reducing salt-restricting sunflower and method of processing the same | |
CN103787751B (en) | A kind of regeneration compound gardens soil utilizing building waste and industrial waste to prepare | |
CN113243279A (en) | Coal gangue hill matrix improvement method | |
CN112854261A (en) | Ecological restoration method suitable for concrete spraying side slope | |
CN110720273A (en) | Method for constructing artificial ecological engineering of copper sulfide biological heap leaching site side slope | |
CN107094390A (en) | A kind of new method for building sponge city | |
CN101429079A (en) | Production of alkalescent fertilizer with abandoned salty mud of alkali-chloride factory and producing method thereof | |
KR101576282B1 (en) | Fertilizer using waste ston powder and the manufacturing method thereof | |
CN111662720A (en) | Organic soil conditioner and preparation method thereof | |
CN113728893A (en) | High-cold-grass original ore area rock slope regreening matrix and preparation method thereof | |
CN113519372A (en) | Preparation method of composite green repairing backfill material | |
CN109133751B (en) | Ecological slope protection brick and preparation method thereof | |
CN113647308B (en) | Re-greening repair backfill material | |
CN111393215A (en) | Soil conditioner and preparation method and application thereof | |
KR102335450B1 (en) | Greening method using greening soil | |
CN105969373A (en) | Soil remediation agent for urban afforestation and greening | |
CN116076189A (en) | Method for promoting improvement of red mud soil formation and vegetation recovery by sintering process | |
JP2000204558A (en) | Greening base material and greening method for face of slope or the like | |
CN107602300A (en) | Salt-soda soil fertilizer based on coal-fired flue gas desulfurization gypsum and sludge and preparation method thereof | |
CN105481538B (en) | Environment-friendly treatment process for red mud |
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 |
Application publication date: 20211022 |
|
RJ01 | Rejection of invention patent application after publication |