CN103739403A - Compound substrate for cultivating lawns and preparation method thereof - Google Patents

Compound substrate for cultivating lawns and preparation method thereof Download PDF

Info

Publication number
CN103739403A
CN103739403A CN201410028912.XA CN201410028912A CN103739403A CN 103739403 A CN103739403 A CN 103739403A CN 201410028912 A CN201410028912 A CN 201410028912A CN 103739403 A CN103739403 A CN 103739403A
Authority
CN
China
Prior art keywords
mineralized waste
composite interstitial
soil
hogwash
interstitial substance
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
Application number
CN201410028912.XA
Other languages
Chinese (zh)
Inventor
李广科
武凤娇
师帅
孙宇欣
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Shanxi University
Original Assignee
Shanxi University
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Shanxi University filed Critical Shanxi University
Priority to CN201410028912.XA priority Critical patent/CN103739403A/en
Publication of CN103739403A publication Critical patent/CN103739403A/en
Pending legal-status Critical Current

Links

Images

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Cultivation Of Plants (AREA)

Abstract

The invention discloses a compound substrate for cultivating lawns and a preparation method thereof. The substrate is prepared by taking mineralized refuse as a main component, sufficiently curing the mineralized refuse and hogwash refuse and then mixing a mixture with greened soil, coal ash or desulfurized gypsum; the prepared compound substrate can be used for replacing common greened soil to produce the lawns. According to the compound substrate, on one hand, a recycling way of four wastes including the mineralized refuse, hogwash, the coal ash and the desulfurized gypsum is expanded; on the other hand, the production cost can be saved so as to be good for solving the problems of damages to the soil, soil salinization and the like in the production of conventional lawns in China.

Description

A kind of composite interstitial substance of cultivating lawn and preparation method thereof
Technical field
The present invention relates to the matrix of culturing plants, specifically belong to a kind of composite interstitial substance of cultivating lawn and preparation method thereof.
Background technology
Mineralized waste be domestic refuse in refuse landfill after landfill is for many years stable, a kind of soil-like grain material of formation.In mineralized waste, contain the required nutritive substance of a large amount of plant-growths and trace element, the cultivation of using it for lawn is feasible, but due to physical structure, the physico-chemical property of former mineralized waste and other pollution substances that contain, the grow generation restraining effect of meeting to plant, therefore, directly utilize former mineralized waste production lawn not reach desirable effect, the quality that must produce through improvement guarantee lawn.
Flyash is the waste residue that coal-fired station produces under hot conditions, wherein contain nutritive element and the trace elements such as the required Mg of a large amount of plant-growths, P, K, flyash adds in mineralized waste as mineralized waste modifying agent, can promote the growth of plant, increase the biomass of plant, also can change the physico-chemical property of mineralized waste, improve the fertility of mineralized waste simultaneously.
Desulfurated plaster is the by product that the flue gas that produces after coal combustion obtains after desulfurization is processed, wherein contain abundant plant essential mineral element S, Ca, Si etc., desulfurated plaster and organic mixing modifying agent can improve the physical structure of mineralized waste, total porosity, the increase hollow billet space that can reduce mineralized waste capacity, increase mineralized waste, reduce non-hollow billet space.The chemical ion that can improve mineralized waste simultaneously forms, and reduces the total salt quantity of mineralized waste.
Summary of the invention
The object of the present invention is to provide a kind of composite interstitial substance of cultivating lawn and preparation method thereof, this composite interstitial substance can replace afforesting autochthonal product lawn not only can, by mineralized waste resource utilization, can also save the land resources of China.
A kind of composite interstitial substance of cultivating lawn provided by the invention, is to take mineralized waste as main body, adopts multiple modifying agent that mineralized waste is improved and formed, and its components in mass portion is counted meter: mineralized waste 100, hogwash 10-30, afforests native 10-30.
Described greening soil replaces with flyash or desulfurated plaster.
A kind of composite interstitial substance of cultivating lawn provided by the invention, components in mass portion is counted meter: mineralized waste 100, hogwash 10-30, flyash 10-15, afforests native 10-15.
Described flyash replaces with desulfurated plaster.
A kind of preparation method who cultivates the composite interstitial substance on lawn provided by the invention, step comprises: after first mineralized waste and hogwash evenly being mixed and become thoroughly decomposed by said components proportioning, then mix with remaining component.
Above-described becoming thoroughly decomposed is that pretreated former mineralized waste and hogwash are banked up about 30 days 25 ℃ of left and right.
Prepare after matrix, before turf plant, to the matrix infiltration of will repeatedly spraying water, guarantee that the moisture in matrix is sufficient.The lawn maintenance in its later stage carries out according to ordinary method with irrigation.
Compared with prior art, advantage of the present invention:
The present invention utilizes mineralized waste, hogwash, flyash, the multiple waste of desulfurated plaster as the matrix of cultivating lawn, find an approach that rationally utilizes multiple waste, utilize turf quality that the present invention produces to be better than the lawn of the autochthonal product of common greening, so the present invention can replace greening soil completely and cultivate lawn.Mineralized waste after improvement comes production lawn can greatly solve a large amount of farmlands soil destruction problem that lawn production brings as Nutrition Soil, can realize the circulation sustainable use of refuse landfill simultaneously, to saving China's land resources, has great significance.
Accompanying drawing explanation
Fig. 1-1 is the rye grass plant height and former mineralized waste (AH), the common figure that contrasts that afforests soil (GS) contrast that embodiment 1 composite interstitial substance is cultivated.
Fig. 1-2 be the rye grass cultivated of embodiment 1 composite interstitial substance on the ground fresh weight contrast with former mineralized waste (AH), common greening soil (GS) contrast figure.
Fig. 1-3 be the rye grass cultivated of embodiment 1 composite interstitial substance on the ground dry weight contrast with former mineralized waste (AH), common greening soil (GS) contrast figure.
Fig. 1-4 are the underground fresh weight of rye grass and former mineralized waste (AH), the common figure that contrasts that afforests soil (GS) contrast that embodiment 1 composite interstitial substance is cultivated.
Fig. 1-5 are the underground dry weight of rye grass and former mineralized waste (AH), the common figure that contrasts that afforests soil (GS) contrast that embodiment 1 composite interstitial substance is cultivated.
Fig. 2-1 is the rye grass plant height and former mineralized waste (AH), the common figure that contrasts that afforests soil (GS) contrast that embodiment 2 composite interstitial substances are cultivated.
Fig. 2-2 be the rye grass cultivated of embodiment 2 composite interstitial substances on the ground fresh weight contrast with former mineralized waste (AH), common greening soil (GS) contrast figure.
Fig. 2-3 be the rye grass cultivated of embodiment 2 composite interstitial substances on the ground dry weight contrast with former mineralized waste (AH), common greening soil (GS) contrast figure.
Fig. 2-4 are the underground fresh weight of rye grass and former mineralized waste (AH), the common figure that contrasts that afforests soil (GS) contrast that embodiment 2 composite interstitial substances are cultivated.
Fig. 2-5 are the underground dry weight of rye grass and former mineralized waste (AH), the common figure that contrasts that afforests soil (GS) contrast that embodiment 2 composite interstitial substances are cultivated.
Embodiment
The native composite interstitial substance of embodiment 1(mineralized waste-hogwash-flyash-afforest)
By 4kg particle diameter, it is the plastic tub that mineralized waste below 900 μ m and 0.8kg hogwash rubbish are put into diameter 34cm, high 11cm, add 2L water, fully stir, mix, then tight with plastics film covering, at 25 ℃, fully become thoroughly decomposed fermentation after about 30 days, add again stir after 0.6kg greening soil and 0.6kg flyash standby, form final composite interstitial substance, with A, represent, with this composite interstitial substance, cultivate turfgrasses in North China kind rye grass.With former mineralising Rubbish medium (AH) in contrast, common greening soil matrix matter (GS) is as reference.Concrete growth data is if Fig. 1-1 is to Fig. 1-5.As can be seen from the figure:
The growth vigor of the rye grass that mineralized waste-hogwash-flyash-afforest native composite interstitial substance (A) is cultivated clearly always, the plant height of rye grass, ground fresh weight, ground dry weight, underground fresh weight, underground dry weight are all apparently higher than control group (AH), substantially close to common greening local soil type (GS).
Embodiment 2(mineralized waste-hogwash-desulfurated plaster composite interstitial substance)
By 4kg particle diameter, it is the plastic tub that mineralized waste below 900 μ m and 0.8kg hogwash rubbish are put into diameter 34cm, high 11cm, add 2L water, fully stir, mix, then with plastics film, cover tight, at 25 ℃, fully become thoroughly decomposed fermentation after about 30 days, add again to stir after 1.2kg desulfurated plaster standbyly, form final composite interstitial substance, with B, represent, with this composite interstitial substance, cultivate turfgrasses in North China kind rye grass, growing way is substantially close to common greening soil.With former mineralising Rubbish medium (AH) in contrast, common greening soil matrix matter (GS) is as benchmark.Concrete growth data is as Fig. 2-1 to Fig. 2-5: as can be seen from the figure:
In the growth indexes of the rye grass that mineralized waste-hogwash-desulfurated plaster composite interstitial substance (B) is cultivated, the plant height of rye grass, ground fresh weight, ground dry weight, underground fresh weight, underground dry weight are all apparently higher than control group (AH), substantially close to common greening local soil type (GS).
The native composite interstitial substance of embodiment 3(mineralized waste-hogwash-afforest)
By 4kg particle diameter, it is the plastic tub that mineralized waste below 900 μ m and 0.8kg hogwash rubbish are put into diameter 34cm, high 11cm, add 2L water, fully stir, mix, then tight with plastics film covering, at 25 ℃, fully become thoroughly decomposed fermentation after about 30 days, add again stir after 1.2kg greening soil standby, form final composite interstitial substance, with this composite interstitial substance, cultivate turfgrasses in North China kind rye grass, growing way is substantially close to common greening soil.Concrete growth data figure omits, and its result approaches embodiment 1, embodiment 2 substantially.
Embodiment 4(mineralized waste-hogwash-flyash composite interstitial substance)
By 4kg particle diameter, it is the plastic tub that mineralized waste below 900 μ m and 0.8kg hogwash rubbish are put into diameter 34cm, high 11cm, add 2L water, fully stir, mix, then tight with plastics film covering, at 25 ℃, fully become thoroughly decomposed fermentation after about 30 days, add again stir after 1.2kg flyash standby, form final composite interstitial substance, with this composite interstitial substance, cultivate turfgrasses in North China kind rye grass, growing way is substantially close to common greening soil.Concrete growth data figure omits, and its result approaches embodiment 1, embodiment 2 substantially.
The native composite interstitial substance of embodiment 5(mineralized waste-hogwash-desulfurated plaster-afforest)
By 4kg particle diameter, it is the plastic tub that mineralized waste below 900 μ m and 0.8kg hogwash rubbish are put into diameter 34cm, high 11cm, add 2L water, fully stir, mix, then tight with plastics film covering, at 25 ℃, fully become thoroughly decomposed fermentation after about 30 days, add again stir after 0.6kg desulfurated plaster and 0.6kg greening soil standby, form final composite interstitial substance, with this composite interstitial substance, cultivate turfgrasses in North China kind rye grass, growing way is substantially close to common greening soil.Concrete growth data figure omits, and its result approaches embodiment 1, embodiment 2 substantially.

Claims (5)

1. a composite interstitial substance of cultivating lawn, is characterized in that, components in mass portion is counted meter: mineralized waste 100, hogwash 10-30, afforests native 10-30.
2. a kind of composite interstitial substance of cultivating lawn as claimed in claim 1, is characterized in that, described greening soil replaces with flyash or desulfurated plaster.
3. a composite interstitial substance of cultivating lawn, is characterized in that: components in mass portion is counted meter: mineralized waste 100, and hogwash 10-30, flyash 10-15, afforests native 10-15.
4. a kind of composite interstitial substance of cultivating lawn as claimed in claim 3, is characterized in that, described flyash replaces with desulfurated plaster.
5. a kind of preparation method who cultivates the composite interstitial substance on lawn as described in claim 1,2,3 or 4, it is characterized in that, step comprises: after first mineralized waste and hogwash evenly being mixed and become thoroughly decomposed by component proportion described in claim 1,2,3 or 4, then mix with remaining component.
CN201410028912.XA 2014-01-22 2014-01-22 Compound substrate for cultivating lawns and preparation method thereof Pending CN103739403A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410028912.XA CN103739403A (en) 2014-01-22 2014-01-22 Compound substrate for cultivating lawns and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410028912.XA CN103739403A (en) 2014-01-22 2014-01-22 Compound substrate for cultivating lawns and preparation method thereof

Publications (1)

Publication Number Publication Date
CN103739403A true CN103739403A (en) 2014-04-23

Family

ID=50496495

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410028912.XA Pending CN103739403A (en) 2014-01-22 2014-01-22 Compound substrate for cultivating lawns and preparation method thereof

Country Status (1)

Country Link
CN (1) CN103739403A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110142275A (en) * 2019-06-11 2019-08-20 成都市兴蓉再生能源有限公司 A method of it is covered using the aging rubbish of depth mineralising is compound for landfill yard
CN111084072A (en) * 2020-01-03 2020-05-01 镇江润祥园林科技发展有限公司 Formula of soilless lawn production substrate utilizing swill dried substance
CN111084088A (en) * 2020-01-03 2020-05-01 镇江润祥园林科技发展有限公司 Method for producing soilless lawn by utilizing swill drying material

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1896248A (en) * 2006-06-19 2007-01-17 同济大学 Production of hydrogen for combining mineralize refuse, swill waste and sludge
CN102180727A (en) * 2011-01-17 2011-09-14 重庆交通大学 Surface layer composite soil for ecological remediation of refuse landfill
CN102260115A (en) * 2011-05-18 2011-11-30 重庆大学 Preparation method of ecotype carpet turf substrate
CN102577854A (en) * 2012-03-07 2012-07-18 浙江师范大学 Method for application study of mineralized rubbish as lawn soil
CN102939893A (en) * 2012-12-06 2013-02-27 甘肃省敦煌种业股份有限公司玉门市种子公司 Artificial lawn cultivation medium
CN103086786A (en) * 2011-11-04 2013-05-08 天津市北方园林生态科学技术研究所 Preparation method of artificial soil for roof greening
CN103304302A (en) * 2012-03-08 2013-09-18 天津市北方园林生态科学技术研究所 Nutrient substrate used for vertical greening, three-dimensional greening and roof greening
CN103373880A (en) * 2012-04-23 2013-10-30 天津市北方园林生态科学技术研究所 Configuration method for artificial substrate for vegetables in protected area
CN103461084A (en) * 2013-09-12 2013-12-25 北京林业大学 Afforesting matrix for improving stone-pit waste muck and preparation method and application of afforesting matrix
CN103461082A (en) * 2013-09-03 2013-12-25 北京林业大学 Cyclamen cultivation medium prepared from refuse humus soil and preparation method of cyclamen cultivation medium

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1896248A (en) * 2006-06-19 2007-01-17 同济大学 Production of hydrogen for combining mineralize refuse, swill waste and sludge
CN102180727A (en) * 2011-01-17 2011-09-14 重庆交通大学 Surface layer composite soil for ecological remediation of refuse landfill
CN102260115A (en) * 2011-05-18 2011-11-30 重庆大学 Preparation method of ecotype carpet turf substrate
CN103086786A (en) * 2011-11-04 2013-05-08 天津市北方园林生态科学技术研究所 Preparation method of artificial soil for roof greening
CN102577854A (en) * 2012-03-07 2012-07-18 浙江师范大学 Method for application study of mineralized rubbish as lawn soil
CN103304302A (en) * 2012-03-08 2013-09-18 天津市北方园林生态科学技术研究所 Nutrient substrate used for vertical greening, three-dimensional greening and roof greening
CN103373880A (en) * 2012-04-23 2013-10-30 天津市北方园林生态科学技术研究所 Configuration method for artificial substrate for vegetables in protected area
CN102939893A (en) * 2012-12-06 2013-02-27 甘肃省敦煌种业股份有限公司玉门市种子公司 Artificial lawn cultivation medium
CN103461082A (en) * 2013-09-03 2013-12-25 北京林业大学 Cyclamen cultivation medium prepared from refuse humus soil and preparation method of cyclamen cultivation medium
CN103461084A (en) * 2013-09-12 2013-12-25 北京林业大学 Afforesting matrix for improving stone-pit waste muck and preparation method and application of afforesting matrix

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
刘小芳: "矿化垃圾作为草坪土的应用研究", 《中国优秀硕士学位论文全文数据库 工程科技I辑》 *
刘小芳等: "矿化垃圾用作草坪土的改良初探", 《第六届全国环境化学大会暨环境科学仪器与分析仪器展览会摘要集》 *
黄俊龙等: "矿化垃圾的改良及其在草坪生产中的应用研究", 《安全与环境学报》 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110142275A (en) * 2019-06-11 2019-08-20 成都市兴蓉再生能源有限公司 A method of it is covered using the aging rubbish of depth mineralising is compound for landfill yard
CN110142275B (en) * 2019-06-11 2021-07-23 成都市兴蓉再生能源有限公司 Method for covering landfill by using deep mineralized and aged refuse
CN111084072A (en) * 2020-01-03 2020-05-01 镇江润祥园林科技发展有限公司 Formula of soilless lawn production substrate utilizing swill dried substance
CN111084088A (en) * 2020-01-03 2020-05-01 镇江润祥园林科技发展有限公司 Method for producing soilless lawn by utilizing swill drying material

Similar Documents

Publication Publication Date Title
CN102875227B (en) Lightweight ecological nutrient soil for roof greening and method for preparing lightweight ecological nutrient soil
CN102219614B (en) Biological improving fertilizer special for saline-alkali soil and preparation method thereof
CN108977203A (en) A kind of red mud soil renovation agent and its method of administration
CN102898196B (en) Organic fertilizer using chicken manure and mushroom dreg as raw materials and preparation technology
CN102220137B (en) Soil modifier, and preparation method and use method thereof
CN103922826B (en) Rice seedling raising ground substance method of cultivation
CN102524008A (en) Organic medium special for raising rice by mechanical seedling transplantation and production method for organic medium
CN103553794A (en) Excretion fermented seedling compound fertilizer and preparation method thereof
CN105646103A (en) Silkworm excrement and shell ecologic acidic soil conditioner and preparation method thereof
CN105777326A (en) Method for producing rice seedling cultivation matrix through earthworm conversion of cow dung
CN105112060A (en) Soil amendment and preparation method therefor
CN105967769A (en) Zymolytic humic acid for agriculture and production method thereof
CN103435381B (en) Resource utilization method of ageratina adenophora
CN112893430A (en) Method for soil remediation by using coal-based solid waste remediation material
CN103739403A (en) Compound substrate for cultivating lawns and preparation method thereof
CN104892249A (en) High-efficiency organic fertilizer for vegetables in greenhouses and preparation method of high-efficiency organic fertilizer
CN104311177A (en) Method of preparing bio-organic fertilizer by utilizing papermaking sludge and tradtional Chinese medicine residues
CN104909899A (en) Production technology of special organic fertilizer for peanut
CN104529628A (en) Organic bone meal fertilizer and preparation method thereof
CN106888605A (en) A kind of tea garden soil improvement method
CN105693333A (en) Light media for vertical greening, preparation method and light compound media for vertical greening
CN104629770A (en) Saline-alkali soil conditioner based on flue gas desulfurization gypsum
CN111742816A (en) Solid waste reconstruction planting soil
CN103204715A (en) Method for producing an amino acid bio-organic fertilizer in a fermenting way by adopting solidified livestock and poultry manure and product thereof
CN103910571B (en) Matrix method of cultivation educated by vegetable seedling dish

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20140423