CN105874957A - Garden planting method of waste soil - Google Patents
Garden planting method of waste soil Download PDFInfo
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- CN105874957A CN105874957A CN201610217653.4A CN201610217653A CN105874957A CN 105874957 A CN105874957 A CN 105874957A CN 201610217653 A CN201610217653 A CN 201610217653A CN 105874957 A CN105874957 A CN 105874957A
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- Prior art keywords
- waste soil
- soil
- medicament layer
- waste
- planting method
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- 239000002689 soil Substances 0.000 title claims abstract description 96
- 239000002699 waste material Substances 0.000 title claims abstract description 60
- 238000000034 method Methods 0.000 title claims abstract description 23
- 238000007514 turning Methods 0.000 claims abstract description 13
- 239000012535 impurity Substances 0.000 claims abstract description 7
- 239000002245 particle Substances 0.000 claims abstract description 7
- 238000012216 screening Methods 0.000 claims abstract description 4
- 239000003814 drug Substances 0.000 claims description 42
- 235000015097 nutrients Nutrition 0.000 claims description 9
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 claims description 6
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 6
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 claims description 6
- 239000001110 calcium chloride Substances 0.000 claims description 6
- 229910001628 calcium chloride Inorganic materials 0.000 claims description 6
- 239000003337 fertilizer Substances 0.000 claims description 6
- 239000003415 peat Substances 0.000 claims description 6
- 239000000155 melt Substances 0.000 claims description 5
- 239000003795 chemical substances by application Substances 0.000 claims description 4
- 239000003480 eluent Substances 0.000 claims description 4
- 239000007800 oxidant agent Substances 0.000 claims description 4
- 230000001590 oxidative effect Effects 0.000 claims description 4
- 238000005406 washing Methods 0.000 claims description 4
- POAOYUHQDCAZBD-UHFFFAOYSA-N 2-butoxyethanol Chemical compound CCCCOCCO POAOYUHQDCAZBD-UHFFFAOYSA-N 0.000 claims description 3
- XNRDLSNSMTUXBV-UHFFFAOYSA-N 2-fluoroethyl 4-methylbenzenesulfonate Chemical compound CC1=CC=C(S(=O)(=O)OCCF)C=C1 XNRDLSNSMTUXBV-UHFFFAOYSA-N 0.000 claims description 3
- ABICJYZKIYUWEE-UHFFFAOYSA-N 5-nitro-1,3-diazinane-2,4,6-trione Chemical compound [O-][N+](=O)C1C(=O)NC(=O)NC1=O ABICJYZKIYUWEE-UHFFFAOYSA-N 0.000 claims description 3
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims description 3
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 claims description 3
- 239000002253 acid Substances 0.000 claims description 3
- 235000013877 carbamide Nutrition 0.000 claims description 3
- 239000004202 carbamide Substances 0.000 claims description 3
- 239000004927 clay Substances 0.000 claims description 3
- 239000003599 detergent Substances 0.000 claims description 3
- OTYBMLCTZGSZBG-UHFFFAOYSA-L potassium sulfate Chemical compound [K+].[K+].[O-]S([O-])(=O)=O OTYBMLCTZGSZBG-UHFFFAOYSA-L 0.000 claims description 3
- 229910052939 potassium sulfate Inorganic materials 0.000 claims description 3
- 235000011151 potassium sulphates Nutrition 0.000 claims description 3
- 239000000843 powder Substances 0.000 claims description 3
- 238000012545 processing Methods 0.000 claims description 3
- 238000010298 pulverizing process Methods 0.000 claims description 3
- 229910052708 sodium Inorganic materials 0.000 claims description 3
- 239000011734 sodium Substances 0.000 claims description 3
- ZNCPFRVNHGOPAG-UHFFFAOYSA-L sodium oxalate Chemical compound [Na+].[Na+].[O-]C(=O)C([O-])=O ZNCPFRVNHGOPAG-UHFFFAOYSA-L 0.000 claims description 3
- BDHFUVZGWQCTTF-UHFFFAOYSA-M sulfonate Chemical compound [O-]S(=O)=O BDHFUVZGWQCTTF-UHFFFAOYSA-M 0.000 claims description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 3
- NWONKYPBYAMBJT-UHFFFAOYSA-L zinc sulfate Chemical compound [Zn+2].[O-]S([O-])(=O)=O NWONKYPBYAMBJT-UHFFFAOYSA-L 0.000 claims description 3
- 229960001763 zinc sulfate Drugs 0.000 claims description 3
- 229910000368 zinc sulfate Inorganic materials 0.000 claims description 3
- 229920002134 Carboxymethyl cellulose Polymers 0.000 claims description 2
- 239000001768 carboxy methyl cellulose Substances 0.000 claims description 2
- 235000010948 carboxy methyl cellulose Nutrition 0.000 claims description 2
- 239000008112 carboxymethyl-cellulose Substances 0.000 claims description 2
- 239000000126 substance Substances 0.000 abstract description 11
- 238000007605 air drying Methods 0.000 abstract 1
- 238000002386 leaching Methods 0.000 abstract 1
- 235000016709 nutrition Nutrition 0.000 abstract 1
- 238000005516 engineering process Methods 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000010521 absorption reaction Methods 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 125000002057 carboxymethyl group Chemical group [H]OC(=O)C([H])([H])[*] 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000000835 fiber Substances 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 210000004243 sweat Anatomy 0.000 description 1
- 239000008207 working material Substances 0.000 description 1
Classifications
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01B—SOIL WORKING IN AGRICULTURE OR FORESTRY; PARTS, DETAILS, OR ACCESSORIES OF AGRICULTURAL MACHINES OR IMPLEMENTS, IN GENERAL
- A01B79/00—Methods for working soil
- A01B79/02—Methods for working soil combined with other agricultural processing, e.g. fertilising, planting
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/02—Extraction using liquids, e.g. washing, leaching, flotation
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05C—NITROGENOUS FERTILISERS
- C05C9/00—Fertilisers containing urea or urea compounds
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
- C05D1/00—Fertilisers containing potassium
- C05D1/02—Manufacture from potassium chloride or sulfate or double or mixed salts thereof
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
- C05D3/00—Calcareous fertilisers
- C05D3/02—Calcareous fertilisers from limestone, calcium carbonate, calcium hydrate, slaked lime, calcium oxide, waste calcium products
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05G—MIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
- C05G3/00—Mixtures of one or more fertilisers with additives not having a specially fertilising activity
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Soil Sciences (AREA)
- Inorganic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Environmental Sciences (AREA)
- Mechanical Engineering (AREA)
- Environmental & Geological Engineering (AREA)
- Pest Control & Pesticides (AREA)
- Soil Conditioners And Soil-Stabilizing Materials (AREA)
- Fertilizers (AREA)
Abstract
The invention discloses a garden planting method of waste soil. The garden planting method comprises the following steps: A, crushing and screening waste soil to remove impurity particles in the waste soil; B, leaching the waste soil processed in the step A; C, air-drying the waste soil processed in the step B; D, placing the waste soil processed in the step C into a pit, wherein the depth of the pit is 4 to 5 m, paving and spreading a first chemical layer at a position which is 0.5 to 0.8 m away from the bottom of the pit, paving and spreading a second chemical layer on the top surface of the waste soil, paving and spreading a third chemical layer between the first chemical layer and the second chemical layer, wherein a distance from the third chemical layer to the first chemical layer and the second chemical layer is at least 0.5 m, standing for 72 to 80 h, turning the waste soil in the pit, and continuously standing for 48 h after the turning; and turning for 2 to 3 times to obtain nutritional soil. The garden planting method can overcome the weaknesses of the prior art and improve the improvement efficiency of the soil texture.
Description
Technical field
The present invention relates to Chinese garden planting field, a kind of Chinese garden planting method of waste soil.
Background technology
At present, the nutrient soil used by Chinese garden planting is by planting on sedendary soil, and current substantial amounts of discarded matter
Soil is different due to the kind of engineering waste soil, and the method when carrying out renewable resource utilization is completely different.Engineering
Refuse soil can not use directly as the soil of Chinese garden planting, needs by just can become after special process can
The earth working material used.Chinese invention patent application CN 103460845 A discloses a kind waste soil
Chinese garden planting method, it is achieved that the conversion of waste soil re-uses.But, this method is for soil property
Improvement needs a longer time cycle, and between the 3-5 used in the early stage, soil property is the most poor.
Summary of the invention
The technical problem to be solved in the present invention is to provide a kind of Chinese garden planting method of waste soil, it is possible to solve
The deficiencies in the prior art, improve the efficiency of the improvement of soil property.
For solving above-mentioned technical problem, the technical solution used in the present invention is as follows.
A kind of Chinese garden planting method of waste soil, comprises the steps:
A, carry out waste soil pulverizing, screening, remove impurity particle therein；
B, then the waste soil crossed through processing of step A is carried out drip washing；
C, then the waste soil processed through step B is carried out dry in the sun and air-dry；
D, putting in melt pit by the waste soil processed through step C, the melt pit degree of depth is 4～5m,
Away from position spreading first medicament layer at the melt pit end 0.5～0.8m, hole, at end face spreading second medicine of waste soil
Oxidant layer, spreading the 3rd medicament layer between the first medicament layer and the second medicament layer, the 3rd medicament layer and the first medicine
Spacing between oxidant layer and the second medicament layer is at least 0.5m, stands and keeps 72h～80h,
First medicament layer include the fertilizer of 45wt%～50wt%, the sawdust of 20wt%～25wt%, 5wt%～
The carbamide of 7wt%, the calcium chloride of 2wt%～3wt%, surplus is peat soil；It is total that first medicament layer accounts for waste soil
The 1.3%～1.5% of weight；
Second medicament layer include the fermented stalk of 20wt%～30wt%, the fertilizer of 10wt%～15wt%,
The water-retaining agent of 10wt%～20wt%, the potassium sulfate of 5wt%～7wt%, surplus is peat soil；Second medicament layer accounts for
The 0.5%～0.7% of waste soil gross weight；
3rd medicament layer include the Calx of 15wt%～20wt%, the soil sterilants of 3wt%～5wt%,
The carboxymethyl cellulose of 15wt%～25wt%, the zinc sulfate of 5wt%～10wt%, the wine that becomes thoroughly decomposed of 2wt%～4wt%
Grain, surplus is clay powder；3rd medicament layer accounts for 1.5wt%～2.5wt% of waste soil gross weight；
Then the waste soil in melt pit is carried out turning, continue after turning to stand 48h；Through 2～3 times
Turning, obtains nutrient soil.
As preferably, in step A, the diameter impurity particle more than 5mm is filtered.
As preferably, in step B, eluent includes,
The Disodium oxalate. of 7.5wt%, the hydrochloric acid of 3.7wt%, the calcium chloride of 11.5wt%, the ethylenediamine diethyl of 2wt%
Acid, the butyl glycol ether of 3.5wt%, the 5-Nitrobarbituric Acid of 0.75wt%, the detergent alkylate of 1.7wt%
Sodium sulfonate, the Fluoroethyl P-tosylate of 2.3wt%, surplus is water.
As preferably, in step C, after waste soil dry in the sun air-dries, the humidity of waste soil is 15%～20%.
As preferably, in step D, the temperature of waste soil is maintained at 35 DEG C～45 DEG C, waste soil
Humidity is maintained at 40%～50%.
Use having the beneficial effects that of being brought of technique scheme: the present invention by soil is carried out drip washing,
The harmful elements such as heavy metal in soil can be removed.Meanwhile, the eluent used can improve soil
Granule is for the absorption maintenance effect of nutrient substance, the richness of the nutrient substance during beneficially soil stores sth. in a cellar
Collection.The preliminary process that stores sth. in a cellar of soil uses the mode of layer-by-layer distribution, can improve the efficiency of soil nutrient,
Then carry out regular turning, it is achieved the homogenizing of soil nutrient, and utilize the interior nutrient substance generated of soil to soil
The sweat produced in earth is catalyzed, thus accelerates the improved speed of soil.
Detailed description of the invention
A kind of Chinese garden planting method of waste soil, comprises the steps:
A, carry out waste soil pulverizing, screening, remove impurity particle therein；
B, then the waste soil crossed through processing of step A is carried out drip washing；
C, then the waste soil processed through step B is carried out dry in the sun and air-dry；
D, putting in melt pit by the waste soil processed through step C, the melt pit degree of depth is 4m, away from ground
Position spreading first medicament layer of hole, hole end 0.6m, at end face spreading second medicament layer of waste soil,
Spreading the 3rd medicament layer between first medicament layer and the second medicament layer, the 3rd medicament layer and the first medicament layer and
Spacing between two medicament layers is at least 0.5m, stands and keeps 72h,
First medicament layer includes the fertilizer of 46wt%, the sawdust of 21wt%, the carbamide of 7wt%, 2.5wt%
Calcium chloride, surplus is peat soil；First medicament layer accounts for the 1.5% of waste soil gross weight；
Second medicament layer includes the fermented stalk of 27wt%, the fertilizer of 13wt%, the water-retaining agent of 18wt%, 5wt%
Potassium sulfate, surplus is peat soil；Second medicament layer accounts for the 0.6% of waste soil gross weight；
3rd medicament layer includes the carboxymethyl fibre of the Calx of 19wt%, the soil sterilants of 4wt%, 21wt%
Dimension element, the distiller grains that become thoroughly decomposed of the zinc sulfate of 8wt%, 2wt%, surplus is clay powder；3rd medicament layer accounts for discarded matter
The 2.1wt% of soil gross weight；
Then the waste soil in melt pit is carried out turning, continue after turning to stand 48h；Through 3 turnings,
Obtain nutrient soil.
In step A, the diameter impurity particle more than 5mm is filtered.
In step B, eluent includes,
The Disodium oxalate. of 7.5wt%, the hydrochloric acid of 3.7wt%, the calcium chloride of 11.5wt%, the ethylenediamine diethyl of 2wt%
Acid, the butyl glycol ether of 3.5wt%, the 5-Nitrobarbituric Acid of 0.75wt%, the detergent alkylate of 1.7wt%
Sodium sulfonate, the Fluoroethyl P-tosylate of 2.3wt%, surplus is water.
In step C, after waste soil dry in the sun air-dries, the humidity of waste soil is 15%～20%.
In step D, the temperature of waste soil is maintained at 40 DEG C～43 DEG C, and the humidity of waste soil is maintained at
40%～50%.
The processing method using the patented method quoted in background technology and the present invention to provide contrasts, soil sample
Sample detection result is as follows:
As seen from the above table, the battalion of soil after agent, soil treatment method provided by the present invention can significantly improve process
Support content.
The above is only the preferred embodiment of the present invention, it is noted that common for the art
For technical staff, under the premise without departing from the principles of the invention, it is also possible to make some improvements and modifications,
These improvements and modifications also should be regarded as protection scope of the present invention.
Claims (5)
1. the Chinese garden planting method of a waste soil, it is characterised in that comprise the steps:
A, carry out waste soil pulverizing, screening, remove impurity particle therein；
B, then the waste soil crossed through processing of step A is carried out drip washing；
C, then the waste soil processed through step B is carried out dry in the sun and air-dry；
D, putting in melt pit by the waste soil processed through step C, the melt pit degree of depth is 4～5m,
Away from position spreading first medicament layer at the melt pit end 0.5～0.8m, hole, at end face spreading second medicine of waste soil
Oxidant layer, spreading the 3rd medicament layer between the first medicament layer and the second medicament layer, the 3rd medicament layer and the first medicine
Spacing between oxidant layer and the second medicament layer is at least 0.5m, stands and keeps 72h～80h,
First medicament layer include the fertilizer of 45wt%～50wt%, the sawdust of 20wt%～25wt%, 5wt%～
The carbamide of 7wt%, the calcium chloride of 2wt%～3wt%, surplus is peat soil；It is total that first medicament layer accounts for waste soil
The 1.3%～1.5% of weight；
Second medicament layer include the fermented stalk of 20wt%～30wt%, the fertilizer of 10wt%～15wt%,
The water-retaining agent of 10wt%～20wt%, the potassium sulfate of 5wt%～7wt%, surplus is peat soil；Second medicament layer accounts for
The 0.5%～0.7% of waste soil gross weight；
3rd medicament layer include the Calx of 15wt%～20wt%, the soil sterilants of 3wt%～5wt%,
The carboxymethyl cellulose of 15wt%～25wt%, the zinc sulfate of 5wt%～10wt%, the wine that becomes thoroughly decomposed of 2wt%～4wt%
Grain, surplus is clay powder；3rd medicament layer accounts for 1.5wt%～2.5wt% of waste soil gross weight；
Then the waste soil in melt pit is carried out turning, continue after turning to stand 48h；Through 2～3 times
Turning, obtains nutrient soil.
The Chinese garden planting method of waste soil the most according to claim 1, it is characterised in that: step
In A, the diameter impurity particle more than 5mm is filtered.
The Chinese garden planting method of waste soil the most according to claim 1, it is characterised in that: step
In B, eluent includes,
The Disodium oxalate. of 7.5wt%, the hydrochloric acid of 3.7wt%, the calcium chloride of 11.5wt%, the ethylenediamine diethyl of 2wt%
Acid, the butyl glycol ether of 3.5wt%, the 5-Nitrobarbituric Acid of 0.75wt%, the detergent alkylate of 1.7wt%
Sodium sulfonate, the Fluoroethyl P-tosylate of 2.3wt%, surplus is water.
The Chinese garden planting method of waste soil the most according to claim 1, it is characterised in that: step
In C, after waste soil dry in the sun air-dries, the humidity of waste soil is 15%～20%.
The Chinese garden planting method of waste soil the most according to claim 1, it is characterised in that: step
In D, the temperature of waste soil is maintained at 35 DEG C～45 DEG C, and the humidity of waste soil is maintained at 40%～50%.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201610217653.4A CN105874957B (en) | 2016-04-03 | 2016-04-03 | A kind of Chinese garden planting method of waste soil |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201610217653.4A CN105874957B (en) | 2016-04-03 | 2016-04-03 | A kind of Chinese garden planting method of waste soil |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN105874957A true CN105874957A (en) | 2016-08-24 |
| CN105874957B CN105874957B (en) | 2017-10-10 |
Family
ID=57012586
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201610217653.4A Expired - Fee Related CN105874957B (en) | 2016-04-03 | 2016-04-03 | A kind of Chinese garden planting method of waste soil |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN105874957B (en) |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106613606A (en) * | 2016-09-22 | 2017-05-10 | 河南农业职业学院 | Garden planting method of waste soil |
| CN107455045A (en) * | 2017-07-01 | 2017-12-12 | 温州市华宏市政园林工程建设有限公司 | A kind of Chinese garden planting device and method |
| CN107903101A (en) * | 2017-09-26 | 2018-04-13 | 无为县喜乐农场 | It is layered composting gourd, fruit and vegetable seedbed seedling nutritious soil base-material and preparation method thereof |
| CN108941174A (en) * | 2018-07-10 | 2018-12-07 | 常州大学 | A kind of solid waste dismantling contaminated soil remediation device |
| CN109894469A (en) * | 2019-04-10 | 2019-06-18 | 河南工学院 | Medicament and restorative procedure are repaired for the efficient stableization of heavy-metal contaminated soil |
| CN111226527A (en) * | 2019-12-26 | 2020-06-05 | 景古环境建设股份有限公司 | Garden planting method of waste soil |
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| CN103460845A (en) * | 2013-09-10 | 2013-12-25 | 天津市森泰园林绿化有限公司 | Garden planting method of waste silt |
| CN103787751A (en) * | 2014-01-17 | 2014-05-14 | 北京奥润开元环保科技研究院有限公司 | Regenerated compound landscape soil prepared by utilizing building rubbish and industrial waste |
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| CN105000991A (en) * | 2015-07-27 | 2015-10-28 | 蒋文兰 | Production method for construction waste carbonized nutritional soil |
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- 2016-04-03 CN CN201610217653.4A patent/CN105874957B/en not_active Expired - Fee Related
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| CN103449911A (en) * | 2013-08-25 | 2013-12-18 | 清远绿由环保科技有限公司 | Medium soil produced from active sludge building waste residue and production method of medium soil |
| CN103460845A (en) * | 2013-09-10 | 2013-12-25 | 天津市森泰园林绿化有限公司 | Garden planting method of waste silt |
| CN103787751A (en) * | 2014-01-17 | 2014-05-14 | 北京奥润开元环保科技研究院有限公司 | Regenerated compound landscape soil prepared by utilizing building rubbish and industrial waste |
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Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106613606A (en) * | 2016-09-22 | 2017-05-10 | 河南农业职业学院 | Garden planting method of waste soil |
| CN107455045A (en) * | 2017-07-01 | 2017-12-12 | 温州市华宏市政园林工程建设有限公司 | A kind of Chinese garden planting device and method |
| CN107903101A (en) * | 2017-09-26 | 2018-04-13 | 无为县喜乐农场 | It is layered composting gourd, fruit and vegetable seedbed seedling nutritious soil base-material and preparation method thereof |
| CN108941174A (en) * | 2018-07-10 | 2018-12-07 | 常州大学 | A kind of solid waste dismantling contaminated soil remediation device |
| CN109894469A (en) * | 2019-04-10 | 2019-06-18 | 河南工学院 | Medicament and restorative procedure are repaired for the efficient stableization of heavy-metal contaminated soil |
| CN109894469B (en) * | 2019-04-10 | 2021-10-22 | 河南工学院 | Efficient stabilization and restoration method for heavy metal contaminated soil |
| CN111226527A (en) * | 2019-12-26 | 2020-06-05 | 景古环境建设股份有限公司 | Garden planting method of waste soil |
Also Published As
| Publication number | Publication date |
|---|---|
| CN105874957B (en) | 2017-10-10 |
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