CN102303991A - Plant cultivation mixed medium and preparation method thereof - Google Patents

Plant cultivation mixed medium and preparation method thereof Download PDF

Info

Publication number
CN102303991A
CN102303991A CN201110122453A CN201110122453A CN102303991A CN 102303991 A CN102303991 A CN 102303991A CN 201110122453 A CN201110122453 A CN 201110122453A CN 201110122453 A CN201110122453 A CN 201110122453A CN 102303991 A CN102303991 A CN 102303991A
Authority
CN
China
Prior art keywords
matrix
agriculture
organic waste
waste material
forestry organic
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.)
Granted
Application number
CN201110122453A
Other languages
Chinese (zh)
Other versions
CN102303991B (en
Inventor
孙向阳
田赟
曹吉鑫
张璐
龚小强
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.)
Beijing Forestry University
Original Assignee
Beijing Forestry 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 Beijing Forestry University filed Critical Beijing Forestry University
Priority to CN2011101224538A priority Critical patent/CN102303991B/en
Publication of CN102303991A publication Critical patent/CN102303991A/en
Application granted granted Critical
Publication of CN102303991B publication Critical patent/CN102303991B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Landscapes

  • Fertilizers (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention discloses a plant cultivation mixed medium and a preparation method thereof. The cultivation medium comprises peat, an agriculture and forest waste compost fermentation medium and an agriculture and forest waste high-temperature pyrolysis medium, wherein the ratio of the volume of the peat to the total volume of the agriculture and forest waste compost fermentation medium and the agriculture and forest waste high-temperature pyrolysis medium in the medium is (10-40):(60-90); and the volume ratio of the agriculture and forest waste compost fermentation medium to the agriculture and forest waste high-temperature pyrolysis medium is 1:(0.4-3.5). The mixed cultivation medium prepared by the invention has balance nutrition, high nutrient content and stable physical properties. The cultivation medium prepared by the invention is reasonable in nutritional structure, facilitates the absorption of the nutrients by foliage plants, meets the growth needs of foliage plants and improves the survival rate and ornament effects of the foliage plants.

Description

One plant cultivating mixed-matrix and preparation method thereof
Technical field
The present invention relates to a kind of nutraceutical matrix of plant cultivation, particularly a kind of nutraceutical matrix of foliage plants soilless culture.
Background technology
Matrix is the basis of soilless substyate culture, and substrate culture is the maximum a kind of facility cultivation mode of popularizing area in the soilless culture.It is that root system with plant is fixed in the matrix of organic or inorganic, through the method for drip irrigation or trickle irrigation, supplies with plant nutrition.At present, peat is as China's soilless culture substrate raw material commonly used, is widely used in the aspects such as industrial seedling rearing, roof greening, soil improvement of flower culture, vegetables and nursery stock.
Peat is called the peat composed of rotten mosses, peat soil or mud coal again, and the coal that degree of coalification is minimum is the plant residue stores different decomposition degree, soft, and its content organic and humic acid is very high.It is aseptic, nontoxic, pollution-free that peat has, and the water-permeable and air permeable performance is good, and quality is light, the water holding fertilizer-preserving ability is strong, help microbial activities, strengthens biological property, and nutritious advantage promptly can be used as cultivation matrix, can be used as good soil mediator agent again.
Though peat is a kind of raw material of good cultivation matrix, its stock number is limited, is a kind of non-renewable in a short time natural resources, and overexploitation can damage the wetland environment; And, use peat to have physical instability merely as cultivation matrix, therefore easy shortcoming such as subside presses for the substitute of exploitation peat growing medium, adopts other raw materials to come all or part of alternative peat to carry out plant growing.
For example publication number is the full nutraceutical matrix that the application for a patent for invention of CN1702061A discloses a kind of botanical seedling culturing and cultivation.It is that the peat of 50-70%, the perlite that weight ratio is 20-25%, vermiculite and active substance, the nutritive substance that weight ratio is 10-15% mix that this nutraceutical matrix adopts weight ratio.Peat is through high-temperature sterilization, and active substance is to be merged by multiple microorganism and plant-growth regulator to be polymerized in this matrix.But the size of the cultivation matrix of this disclosure of the Invention differs, and after watering, the fine particle in the matrix has been absorbed in the bigger noncapilarry porosity, and matrix shrinks and sedimentation, causes the noncapilarry porosity of matrix to diminish, thereby has reduced the gas-water ratio of matrix; Crude fiber content in this full nutraceutical matrix is low in addition, and the addition of the material that need have additional nutrients has improved production cost.
And for example the patent No. is that 200910076676.8 patent of invention discloses a kind of flower culture matrix and preparation method thereof; This flower culture matrix comprises major ingredient and additive; Wherein major ingredient comprises peat, perlite and vermiculite; Additive comprises that water supply in media amendment, pH regulator agent and nutrition start agent, and the particle diameter of peat, perlite and vermiculite is greater than 3mm.This flower culture matrix physical properties is stable; The water supply in media amendment can reduce stromal surface tension force; Improve the wetting capacity and the homogeneity of stromal surface; Change the appearance stability of peat; Prevent that moisture scatters and disappears fast; Improve in actual the use infiltration rate rate under the moisture, significantly improved the water-absorbent of peat growing medium, delay the efflorescence of peat.But perlite and vermiculite also are natural products, have non-renewable, frangible in the use, the improved effect of peat growing medium is not had a persistence, and perlite itself is alkalescence, make the pH value rising of matrix own to be unfavorable for plant-growth.
At present China's relevant industries to cultivation matrix year total demand about 1,000 ten thousand m 3About, market demand is very big, and also in cumulative year after year, but peat has been on the verge of exhaustion as a kind of Nonrenewable resources, and the alternative base starting material of seeking peat is extremely urgent, and the agricultural organic waste is exactly one type of ideal equivalent material.
Agriculture and forestry organic waste material is the byproduct that produces in agricultural and the production of forestry and the course of processing; Enormous amount; Have renewable, the regeneration period short, biodegradable, advantages of environment protection; Be important biomass resource, mainly contain bark, shell, limb, stalk, bagasse, rice husk, mushroom slag, corn cob etc.
In the today of advocating thriftiness resource and Sustainable development energetically; China also is in the starting stage to the research that agriculture and forestry organic waste material utilizes again; The traditional agriculture and forestry organic waste material processing mode of China mainly is landfill or burning; Though removed most of agriculture and forestry organic waste material; But these modes have been brought the environmental pollution and the wasting of resources; Excessively remove agriculture and forestry organic waste material also can cause the serious meta-acid of soil or partially alkali, organic matter and nutrient content reduce, be prone to harden, many-sided problem such as air permeability difference; The circulation of destruction soil ecology descends soil fertility year by year.
Based on environment protection with for market provides the consideration of localization matrix of super quality and competitive price, utilize agriculture and forestry organic waste material to produce variation, innoxious substrate products, realize that the reusable edible of natural resources becomes the focus of Recent study.China is peat resource-starved country, and maldistribution of the resources, and peat mainly concentrates on northeast, and being transported to region of Southeast will increase cost.Therefore; Investigators turn one's attention on numerous agriculture and forestry organic waste materials, with these organic waste development soilless culture substrates, the handling problem that has not only solved organic waste; Also, improved the level of agriculture and forestry organic waste material resource reutilization for soilless culture provides good matrix.
Modern study shows; With the agriculture and forestry organic waste material compost treatment; Not only can reduce the area of landfill yard and the breeding place of pathogenic bacteria; Also have and increase soil fertility; Improve the soil physics structure, water moisture self restraint reduces functions such as city dust from flying, the soil erosion and rainwash; And can also the beautifying city view, reduce the urban green space maintenance cost and also drive recycling economy development; On the other hand, utilize again, also can make it revert to soil or replace peat to serve as fertilizer or soilless culture substrate plays important effect in flower culture through garden waste.
In addition, through the pyrolytic processing mode agriculture and forestry organic waste material is utilized also gradually by people's cognition again.So-called pyrolysis processing is to adopt dry distillation; After agriculture and forestry organic waste material is pulverized or granulation handles; The agriculture and forestry organic waste material particle of handling well is placed in the charring furnace, obtains the process of the pyrolysis product of similar peat through oven dry material moisture, pyrolysis processing and desalting treatment etc.The materials such as mushroom that itself have through the agriculture and forestry organic waste material behind the high temperature pyrolysis are inactivation under hot conditions all; Has certain vermins-proof effect; In addition; Product after the pyrolysis have slow discharge nutritive element, hygro-expansivity better, characteristics such as dimensional stabilizing; Be used with peat and composting substrate, can effectively improve the ratio of matrix ventilating slit and water holding hole, improve the slump resistance of matrix; Make matrix environment more help the growth of plant, increase its appreciation effect.
Summary of the invention
The object of the present invention is to provide plant cultivation matrix and preparation method thereof, matrix of the present invention is cheap, and the peat consumption reduces, and also for the reasonable utilization of agriculture and forestry organic waste material aspect plant soil-less culturing scientific basis is provided simultaneously.The present invention had both made full use of the agricultural organic waste; Saved the consumption of peat again; And the cultivation matrix chemical property of preparation is stable; The soda acid appropriateness; Permeability is good; Physical and chemical index all reaches the requirement of soilless culture substrate, can good and stable matrix environment be provided for plant-growth, especially is suitable for the cultivation of foliage plants.
For realizing the object of the invention, one aspect of the present invention provides a plant cultivating mixed-matrix, comprises matrix peat, agriculture and forestry organic waste material composting substrate, agriculture and forestry organic waste material high temperature pyrolysis matrix and sterilant.
Wherein, the volume of said matrix peat is 10-40: 60-90 with the ratio of the cumulative volume of agriculture and forestry organic waste material composting substrate and agriculture and forestry organic waste material pyrolysis matrix, and wherein, the ratio of the volume of agriculture and forestry organic waste material composting substrate and agriculture and forestry organic waste material pyrolysis matrix is 1: 0.4-3.5.
Particularly, the consumption of said sterilant is every 1m 3Matrix peat, agriculture and forestry organic waste material composting substrate and agriculture and forestry organic waste material pyrolysis matrix in add sterilant 0.1-2.0kg, be preferably 0.2-1.6kg.
Wherein, one or more during described sterilant selection derosal, sterilant selection derosal, F-1991, dimetachlone, anilazine, fast Poly or enemy's power are taken off.
Wherein, described agriculture and forestry organic waste material composting substrate is prepared from according to following steps: after agriculture and forestry organic waste material, fermenting agent and fermenting additive are mixed, carry out fermentative processing, wherein, said fermenting additive is that bamboo vinegar liquid is or/and wood vinegar.
Particularly, the weight part proportioning of said agriculture and forestry organic waste material and fermenting agent is 100: 0.1-1 is preferably 100: 0.3-0.6.
Wherein, living bacteria count in the described fermenting agent >=200,000,000/g, the pH value is 5.5-8.5, effectively viable bacteria contains actinomycetes, thermophile bacteria, whiterot fungi, vinelandii, phosphate solubilizing bacteria, potassium solubilizing bacteria, cellulose-decomposing bacterium etc.
Particularly, the consumption of fermenting additive is to add the said fermenting additive of 8-50ml in every 100kg agriculture and forestry organic waste material.
Wherein, the pH value of said bamboo vinegar liquid is 2-32, and density is 0.9-1.5g/ml, and organic acid content is 7-11%; Content of phenolic compounds is 6-8%; The pH value of said wood vinegar is 2.5-3.5, and density is 0.8-2.0g/ml, and organic acid content is 7-13%, and content of phenolic compounds is 8-12%.
Bamboo vinegar liquid, wood vinegar are hydrophilic solution; Stronger absorption, penetrating power are arranged; It can be used as plant promoting agent, growth stimulant, fertilizer-keeping agent, soil improvement agent, soil disinfectant etc., and nontoxic, harmless, noresidue, is a kind of ideal green solvent.
Wherein, said fermentative processing comprises following step in sequence:
1) C/N that regulates agriculture and forestry organic waste material is than being 20-35;
2) add fermenting agent and water, mix, make the water ratio of waste reach 60-70%;
3) waste is piled the fermentation heap body; The fermentative processing of banking up; Wherein, The temperature and the water ratio of monitoring heap body in the fermentative processing process of banking up; Every 3-7 days to fermentation heap body sprinkling fermenting additive once; The consumption of each fermenting additive that sprays is that every 100kg waste sprays 1-2.5ml, and when the water ratio of fermentation heap body less than 50% the time, spray water to water ratio and reach 60-70% to piling body.
Particularly, the ratio of the C/N described in the step 1) is preferably 25-30; The weight part proportioning of fermenting agent step 2) and agriculture and forestry organic waste material is 0.1-1: 100, be preferably 0.3-0.6: 100.
Especially, living bacteria count in the described fermenting agent >=200,000,000/g, the pH value is 5.5-8.5, effectively viable bacteria contains actinomycetes, thermophile bacteria, whiterot fungi, vinelandii, phosphate solubilizing bacteria, potassium solubilizing bacteria, cellulose-decomposing bacterium etc.
Particularly, the number of times of sprinkling fermenting additive is 8-20 time in the step 3).
Especially, the sprinkling total amount of fermenting additive is that every 100kg waste sprays 8-50ml.
Particularly, bank up described in the step 3) and carry out turning according to following mode in the fermentative processing:
A) when heap temperature is higher than 55 ℃, carry out turning and handle, the control heap temperature is lower than 75 ℃;
B) be reduced to gradually when being lower than 55 ℃ when heap temperature, carried out turning and handle in every 6-12 days;
C) after heap temperature is reduced to 20-35 ℃, continue again to stack 7-21 days, wherein, carried out turning and handle in every 6-12 days.
Wherein, also comprise in fermenting additive, adding entry, spray after processing the additive diluent.
Particularly, the ratio of starter and the volume of water is 1 in the additive diluent: 800-2000.
Wherein, Said agriculture and forestry organic waste material pyrolysis matrix is prepared from according to following steps: the agriculture and forestry organic waste material of water ratio≤10% is carried out the high temperature pyrolysis processing; Collecting solid product promptly gets; Wherein, The temperature of pyrolysis processing is 160-220 ℃; Treatment time 10-20min, control oxygen volumn concentration≤10% in the said high temperature pyrolysis treating processes.
Particularly, the water ratio of the agriculture and forestry organic waste material of high temperature pyrolysis processing is preferably 5-10%; The pyrolysis processing time is preferably 10-15min; The oxygen volumn concentration is preferably 2-10% in the pyrolysis processing process.
Particularly, also comprise the solid product after the pyrolysis processing is immersed in the water, carry out desalination place 20-120min.
Wherein, the solid product after the pyrolysis processing is 1 with the ratio of the volume of water: 2-3.5.
Particularly, to be dried to water ratio be 15-20% to the solid product after the desalting treatment.
The present invention provides a kind of above-mentioned plant to plant the preparation method of mixed cultivation matrix on the other hand, and raw material matrix peat, agriculture and forestry organic waste material composting substrate, agriculture and forestry organic waste material pyrolysis matrix and sterilant are mixed.
Wherein, the volume of said matrix peat is 10-40: 60-90 with the ratio of the cumulative volume of agriculture and forestry organic waste material composting substrate and agriculture and forestry organic waste material pyrolysis matrix, and wherein, the ratio of the volume of agriculture and forestry organic waste material composting substrate and agriculture and forestry organic waste material pyrolysis matrix is 1: 0.4-3.5.
Particularly, the consumption of said sterilant is every 1m 3Matrix peat, agriculture and forestry organic waste material composting substrate and agriculture and forestry organic waste material pyrolysis matrix in add sterilant 0.1-2.0kg, be preferably 0.2-1.6kg.
Foliage plants cultivation mixed-matrix of the present invention has the following advantages:
1, the agricultural organic waste is handled the matrix that makes through bank up fermentative processing and high temperature pyrolysis and be used to prepare the cultivation matrix of foliage plants; The present situation of the application that the utilising efficiency of having broken the agricultural organic wastes is lower, can not get other any high added values; Overcome the waste treatment difficulty; Cause On Situation of Environmental Disruption; Increased the value added of agriculture and forestry organic waste material; Utilize resources synthetically is beneficial to environment protection.
2, cultivation mixed-matrix of the present invention has solved plant growing process mesostroma and has been overly dependent upon peat, a high difficult problem, the exhausted day by day predicament of peat resource of matrix production cost; The substitution rate of peat is high among the present invention; Reach 60-90%; Saved the peat resource; Fully effectively utilized agriculture and forestry organic waste material, agriculture and forestry organic waste material is grown fat is treasured.
3, the present invention prepares fermentation and banks up in the process of matrix; The nitrogen element of fermenting additive in can the set agriculture and forestry organic waste material; The stink that can not only suppress to bank up and produce in the fermenting process; Can also effectively promote the activity of organism of fermentation; Accelerate organic decomposition in the compost; The C/N of the mixed-matrix of feasible preparation improves compost fermentation efficient than high.
4, cultivation mixed-matrix physicochemical property of the present invention are stable, potential of hydrogen moderate (pH6.36~7.02), and specific conductivity (EC value) is 0.68-1.12mS/cm, unit dry weight is 0.16-0.28g/cm 3, total porosity is 74.32-84.30%, and the ventilation space reaches 19.04-26.53%, and the cultivation mixed-matrix of preparation is loose, and permeability is good, and venting capability is good, and the physical and chemical performance index meets the requirement of gardening plant suitable growth, is suitable for cultivation of plants.
5, the maximum retention ability of the cultivation mixed-matrix of the present invention's preparation reaches 1.92-3.61g/g; The water holding hole reaches 53.94-59.79%; The water-retaining capacity that soilless culture substrate of the present invention is described is strong; All but sticking is equivalent to the about 1.92-3.61 of the own wt water yield doubly; Can be plant competent moisture condition is provided; And can reduce the number of times that waters, water saving, streamlining management measure.
6, nitrogen content is 1.46-2.16% in the mixed-matrix of the present invention's preparation; Phosphorus content is 0.14-0.96%; Potassium content is 0.94-1.28%; Content of humic acid is 21.04-28.63%; Organic content is 63.83-88.52%, and C/N is 21.62-26.17, and trophic structure is reasonable; Be convenient to plant absorbing, satisfy the plant-growth needs.
7, the blended solid matrix of the present invention's preparation has promoter action to plant-growth, and the plant hat width of cloth is big, and plant is high, and plant biomass accumulation value is high, and the cultivation mixed-matrix of the present invention's preparation meets or exceeds the quality of peat growing medium.
8, preparing method's technology of the present invention is simple, easy to operate, and the product yield is high, controllable product quality, the physical and chemical index of the soilless culture substrate of preparation near in addition have be better than peat growing medium, satisfy the requirement of soilless culture substrate.
Embodiment
Below in conjunction with specific embodiment, further set forth the present invention., these embodiment are not used in restriction scope of the present invention but only limiting to the present invention is described.
The peat that uses in the embodiment of the invention is the Pin Shi peat available from company of Denmark Pin Shi Top (group).
Embodiment 1
1, the agriculture and forestry organic waste material fermented manure is handled
1) adopt pulverizer (Beijing many meanings Dragon Lord machinery limited liability company) garden waste limb (limbs of prunings such as willow, Chinese scholartree, willow) to be ground into the particle of particle diameter≤1cm; Make the waste particle; Measure waste particulate organic carbon content and nitrogen content simultaneously, it is as shown in table 1 to measure the result.
Adopt Kjeldahl determination to measure waste particulate nitrogen content;
Adopting potassium bichromate titrimetric method---outer heating method is measured the organic carbon content in the cultivation mixed-matrix, and concrete measuring method is following: after in exsiccant hard test tube, adding air-dry cultivation mixed-matrix, add K 2Cr 2O 7Standardized solution and dense H 2SO 4, then test tube is made liquid boiling 5min in vitro under 170-180 ℃, pour out in vitro tolerantly then, carry out titration with the ferrous sulfate standardized solution, the consumption according to ferrous sulfate calculates organic carbon content.
2) in the waste particle, add urea, regulating waste particulate C/N ratio is 25, makes the fermented manure particle, wherein, adds urea 2.476kg in every 100kg waste particle (dry weight).
Except using urea to regulate the waste particle C/N ratio, can also use feces of livestock and poultry (like cow dung, chicken manure, horsehit etc.) to increase the nitrogen content of waste.
3) in fermented abandoned composition granule, add fermenting agent organic waste zymophyte bent (Beijing Jingpuyuan Bio-engineering Co., Ltd.) and water, and mix, make waste particulate water ratio reach 65%; Wherein, The consumption of fermenting agent is to be added with the bent 1kg of organic waste zymophyte in every 100kg (dry weight) waste particle; Wherein, Living bacteria count >=200,000,000 in the organic waste zymophyte song/g; The pH value is 5.5, and effectively viable bacteria contains actinomycetes, thermophile bacteria, whiterot fungi, vinelandii, phosphate solubilizing bacteria, potassium solubilizing bacteria, cellulose-decomposing bacterium etc.
Use fermenting agent mainly to comprise tens bacterial classifications (like actinomycetes, thermophile bacteria, whiterot fungi, vinelandii, phosphate solubilizing bacteria, potassium solubilizing bacteria, cellulose-decomposing bacterium etc.) of four big floras such as bacterium, fungi, actinomycetes, yeast in the embodiment of the invention, have heat-resisting, phosphorus decomposing, potassium decomposing, fixed nitrogen and decomposition of cellulose function.
4) it is indoor with the water ratio that has added fermenting agent to be that 65% fermentation wastes particle is stacked in, the long 2m of heap body base portion, wide 1.5m, high 1m, and processings of banking up of fermenting, and monitor temperature and the water ratio of piling body;
5) when heap temperature reaches 55 ℃; The heap body is carried out turning to be handled; Strict control heap temperature≤75 ℃; Carrying out along with fermentation; Heap temperature reduces gradually, when heap temperature is lower than 55 ℃, carries out turning and handles in per 6 days; After heap temperature is reduced to room temperature (25 ℃); Continued again to bank up 14 days, and carried out turning in per 6 days and handle, make the agriculture and forestry organic waste material composting substrate; Wherein, In treating processes is banked up in fermentation,, the heap body begins to calculate when beginning to ferment, and per 6 days are to heap body sprinkling fermenting additive diluent (bamboo vinegar liquid diluent) once; Spray altogether 12 times; The consumption of each bamboo vinegar liquid diluent that sprays is the bamboo leachate diluent 2L that sprays preparation in 100kg (dry weight) the waste particle, and wherein, bamboo vinegar liquid is 1: 1000 with the ratio of the volume of water in the bamboo vinegar liquid diluent; The pH value of bamboo vinegar liquid is 2.5, and density is 0.9g/ml; Organic acid content is 10%, and content of phenolic compounds is 6%, and promptly in process was banked up in fermentation, every 100kg (dry weight) waste particle sprayed 24L bamboo vinegar liquid diluent altogether, that is to say, every 100kg (dry weight) waste particle sprays the 24ml bamboo vinegar liquid altogether; Simultaneously, when the water ratio of fermentation heap body less than 50% the time, spraying water to water ratio to the heap body reaches 65%.
2, agriculture and forestry organic waste material pyrolysis processing
1) adopt pulverizer (Beijing many meanings Dragon Lord machinery limited liability company) that garden waste limb (limbs of prunings such as willow, Chinese scholartree, willow) is ground into the waste particle that particle diameter is 1-2cm.
2) add the garden waste particle after opening carbonizer (Beijing many meanings Dragon Lords machinery limited liability companys, SL-II type) heat temperature raising to 100 ℃, under 100 ℃, dry to the particle water ratio be 10%;
3) continue to be heated to 220 ℃, under 220 ℃, the oxygen volumn concentration in the control carbonizer is 10%, under the described conditions pyrolysis processing 10min.
4) stop heating, the waste particle after the taking-up pyrolysis processing is soaked in the water, carries out desalting treatment, and wherein soak time is 90min, and water and particulate volume ratio are 2: 1.
5) waste particle natural air drying to the particle water ratio under room temperature (25 ℃) with desalting treatment is 20%, obtains agriculture and forestry organic waste material pyrolysis matrix.
3, the preparation of cultivation mixed-matrix
1) gets the raw materials ready according to following volume proportion
Sterilant is except derosal among the present invention, and other sterilant such as F-1991, dimetachlone, anilazine, fast Poly, enemy's power are taken off etc. and all to be applicable to the present invention.
2) above-mentioned raw materials is joined in the fermenter (Beijing Jingpuyuan Bio-engineering Co., Ltd.), add water, the water content of the mixture that makes reaches 60%, mixes, leave standstill 2 days after, being dried to water ratio is 15%, promptly gets.
The performance index of the cultivation mixed-matrix of preparation detect according to following method:
Unit dry weight, maximum retention ability, total porosity, ventilating slit, water holding hole adopt core cutter method to measure, and concrete measuring method is following:
It is 200cm that the air-dry cultivation mixed-matrix of getting present embodiment preparation is filled it up with volume 31 cutting ring, wherein the weight of cutting ring is W 0, the gross weight of cultivation mixed-matrix and cutting ring is W 1, then cutting ring and cultivation mixed-matrix are immersed in the water, to weigh behind the immersion 24h, weight is W 2, (W again weighs after the moisture in the cutting ring freely drains 3), calculate by following formula:
Unit dry weight (g/cm 3)=(w 1-w 0)/200
Maximum retention ability (g/g)=(w 3-w 1)/(w 1-w 0)
Total porosity (%)=(w 2-w 1)/200 * 100%
Ventilating slit (%)=(w 2-w 3)/200 * 100%
Water holding hole (%)=total porosity-ventilating slit
Adopt pH meter and electrical conductivity meter to measure base starting material pH value; The EC value; Concrete measuring method is following: will cultivate mixed-matrix and hydromining use solid-to-liquid ratio is the mixed of 1: 10 (W/V), and centrifuging behind the vibration 30min uses pH meter, electrical conductivity meter to measure pH value and EC value in the filtrating.
Adopt potassium bichromate titrimetric method to measure the total humic acid in the base starting material; Concrete measuring method is following: cook extraction agent with the trisodium phosphate basic solution; The humic acid of the base starting material that lixiviate goes out; Can be in strongly acidic solution by potassium dichromate oxidation; According to the consumption of potassium bichromate, calculate the content of humic acid.
Nitrogen adopts Kjeldahl determination to measure; Phosphorus H 2SO 4-H 2O 2Method disappears and boils, and molybdenum antimony resistance colorimetric method is measured; Potassium adopts H 2SO 4-H 2O 2Method disappears and boils, and flare photometer is measured.
Adopting potassium bichromate titrimetric method---outer heating method is measured the organic carbon content in the cultivation mixed-matrix, and concrete measuring method is following: after in exsiccant hard test tube, adding air-dry cultivation mixed-matrix, add K 2Cr 2O 7Standardized solution and dense H 2SO 4, then test tube is made liquid boiling 5min in vitro under 170~180 ℃, pour out in vitro tolerantly then, carry out titration with the ferrous sulfate standardized solution, the consumption according to ferrous sulfate calculates organic content.
The performance index detected result of cultivation mixed-matrix is like table 2, shown in 3.
Embodiment 2
1, the agriculture and forestry organic waste material fermented manure is handled
1) adopt pulverizer that the agriculture and forestry organic waste material corn cob meal is broken into the particle that length is 0.5-1.5cm, make the waste particle, measure waste particulate organic carbon content and nitrogen content simultaneously, it is as shown in table 1 to measure the result.
2) in corn cob granule, add urea, the C/N ratio of regulating corn cob granule is 27, makes the fermented manure particle, wherein, adds urea 0.813kg in every 100kg waste particle (dry weight).
3) in fermented abandoned composition granule, add fermenting agent organic waste zymophyte bent (Beijing Jingpuyuan Bio-engineering Co., Ltd.) and water, and mix, make waste particulate water ratio reach 60%; Wherein, The consumption of fermenting agent is to be added with the bent 0.5kg of organic waste zymophyte in every 100kg (dry weight) waste particle; Wherein, Living bacteria count >=200,000,000 in the organic waste zymophyte song/g; The pH value is 8.5, and effectively viable bacteria contains actinomycetes, thermophile bacteria, whiterot fungi, vinelandii, phosphate solubilizing bacteria, potassium solubilizing bacteria, cellulose-decomposing bacterium etc.
4) it is indoor with the water ratio that has added fermenting agent to be that 60% fermentation wastes particle is stacked in, the long 2m of heap body base portion, wide 1.5m, high 1m, and processings of banking up of fermenting, and monitor temperature and the water ratio of piling body.
5) when heap temperature reaches 55 ℃; The heap body is carried out turning to be handled; Strict control heap temperature≤75 ℃; Carrying out along with fermentation; Heap temperature reduces gradually; When heap temperature is lower than 55 ℃; Carrying out turning in per 12 days handles; After heap temperature is reduced to room temperature (20 ℃); Continued again to bank up 21 days; And carrying out turning in per 12 days handles; Make the agriculture and forestry organic waste material composting substrate; Wherein, In treating processes is banked up in fermentation;, the heap body begins to calculate when beginning to ferment; To heap body sprinkling fermenting additive diluent (bamboo vinegar liquid diluent) once sprayed altogether 20 times in per 3 days, the consumption of each bamboo vinegar liquid diluent that sprays is the bamboo leachate diluent 2L that sprays preparation in 100kg (dry weight) the waste particle; Wherein, Bamboo vinegar liquid is 1: 800 with the ratio of the volume of water in the bamboo vinegar liquid diluent, and the pH value of bamboo vinegar liquid is 2, and density is 1.5g/ml; Organic acid content is 11%; Content of phenolic compounds is 8%, and promptly in process was banked up in fermentation, every 100kg (dry weight) waste particle sprayed 40L bamboo vinegar liquid diluent altogether; That is to say that every 100kg (dry weight) waste particle sprays the 50ml bamboo vinegar liquid altogether; Simultaneously, when the water ratio of fermentation heap body less than 50% the time, spraying water to water ratio to the heap body reaches 60%.
2, agriculture and forestry organic waste material pyrolysis processing
1) adopt pulverizer that corn cob meal is broken into the waste particle that particle diameter is 0.5-1.5cm.
2) add the agriculture and forestry organic waste material particle after opening carbonizer heat temperature raising to 80 ℃, under 80 ℃, dry to particle water ratio 5%.
3) continue to be heated to 180 ℃, under 180 ℃, the oxygen volumn concentration in the control carbonizer is 5%, under the described conditions pyrolysis processing 10min.
4) stop heating, the waste particle after the taking-up pyrolysis processing is soaked in the water, carries out desalting treatment, and wherein soak time is 90min, and water and particulate volume ratio are 2: 1.
5) waste particle natural air drying to the particle water ratio under room temperature (25 ℃) with desalting treatment is 20%, obtains agriculture and forestry organic waste material pyrolysis matrix.
3, the preparation of cultivation mixed-matrix
1) gets the raw materials ready according to following weight proportion
Figure BDA0000060778090000111
2) above-mentioned raw materials is joined in the fermenter, add water, the water content of the mixture that makes reaches 50%, mixes, leave standstill 2 days after, being dried to water ratio is 10%, promptly gets.
Measure the performance index of the cultivation mixed-matrix of preparation, detected result is like table 2, shown in 3.
Embodiment 3
1, the agriculture and forestry organic waste material fermented manure is handled
1) be raw material with the agricultural wastes rice husk, measure the organic carbon content and the nitrogen content of agricultural wastes rice husk, it is as shown in table 1 to measure the result.
2) in waste rice husk particle, add urea, regulating waste particulate C/N ratio is 30, makes the fermented manure particle, wherein, adds urea 1.473kg in every 100kg waste particle (dry weight).
3) in fermented abandoned composition granule, add fermenting agent organic waste zymophyte bent (Beijing Jingpuyuan Bio-engineering Co., Ltd.) and spray water and mix, make waste particulate water ratio reach 70%; Wherein, The consumption of fermenting agent is to be added with the bent 0.1kg of organic waste zymophyte in every 100kg waste particle (dry weight); Wherein, Living bacteria count >=200,000,000 in the organic waste zymophyte song/g; The pH value is 7.5, and effectively viable bacteria contains actinomycetes, thermophile bacteria, whiterot fungi, vinelandii, phosphate solubilizing bacteria, potassium solubilizing bacteria, cellulose-decomposing bacterium etc.
4) it is indoor with the water ratio that has added fermenting agent to be that 70% fermentation wastes particle is stacked in, the long 2m of heap body base portion, wide 1.5m, high 1m, and processings of banking up of fermenting, and monitor temperature and the water ratio of piling body.
5) when heap temperature reaches 60 ℃; The heap body is carried out turning to be handled; Strict control heap temperature≤75 ℃; When heap temperature is lower than 55 ℃; Carrying out turning in per 9 days handles; After heap temperature reaches room temperature (35 ℃); Continued again to bank up 7 days, and carried out making the agriculture and forestry organic waste material composting substrate when turning is handled in 7 days, wherein; In treating processes is banked up in fermentation; When the heap body begins to ferment, begin to calculate, to heap body sprinkling fermenting additive diluent (wood vinegar diluent) once sprayed altogether 10 times in per 5 days; The consumption of each wood vinegar diluent that sprays is the pyroligneous liquor diluent 2L that sprays preparation in 100kg (dry weight) the waste particle; Wherein wood vinegar is 1: 1500 with the ratio of the volume of water, and the pH value of wood vinegar is 3.2, and density is 1.0g/ml; Organic acid content is 7%, and content of phenolic compounds is 7%.Promptly in process was banked up in fermentation, every 100kg (dry weight) waste particle sprayed 20L wood vinegar diluent altogether, that is to say, every 100kg (dry weight) waste particle sprays the 13.3ml wood vinegar altogether; Simultaneously, when the water ratio of fermentation heap body less than 50% the time, spraying water to water ratio to the heap body reaches 70%.
2, agriculture and forestry organic waste material pyrolysis processing
1) add agriculture and forestry organic waste material rice husk particle after opening carbonizer heat temperature raising to 80 ℃, dry to water ratio be 10%.
2) continue to be heated to 200 ℃, under 200 ℃, the oxygen volumn concentration in the control carbonizer is 2%, under the described conditions pyrolysis processing 10min.
3) stop heating, the waste particle after the taking-up pyrolysis processing is soaked in the water, carries out desalting treatment, and wherein soak time is 120min, and water and particulate volume ratio are 3.5: 1.
4) waste particle natural air drying to the particle water ratio under room temperature (25 ℃) with desalting treatment is 20%, obtains agriculture and forestry organic waste material pyrolysis matrix.
3, the preparation of cultivation mixed-matrix
1) gets the raw materials ready according to following weight proportion
Figure BDA0000060778090000121
2) above-mentioned raw materials is joined in the fermenter (Beijing Jingpuyuan Bio-engineering Co., Ltd.), add water, the water content of the mixture that makes reaches 70%, mixes, leave standstill 2 days after, being dried to water ratio is 20%, promptly gets.
Measure the performance index of the cultivation mixed-matrix of preparation, detected result is like table 2, shown in 3.
Embodiment 4
1, the agriculture and forestry organic waste material fermented manure is handled
1) adopt pulverizer that agricultural wastes straw (wheat straw, straw etc.) is ground into the particle of particle diameter≤1cm, make the waste particle, measure waste particulate organic carbon content and nitrogen content simultaneously, it is as shown in table 1 to measure the result.
2) in the waste particle, add urea, regulating waste particulate C/N ratio is 20, makes the fermented manure particle, wherein, adds urea 0.604kg in every 100kg waste particle (dry weight).
3) in fermented abandoned composition granule, add fermenting agent organic waste zymophyte bent (Beijing Jingpuyuan Bio-engineering Co., Ltd.) and water, and mix, make waste particulate water ratio reach 65%; Wherein, The consumption of fermenting agent is to be added with the bent 1kg of organic waste zymophyte in every 100kg (dry weight) waste particle; Wherein, Living bacteria count >=200,000,000 in the organic waste zymophyte song/g; The pH value is 6.5, and effectively viable bacteria contains actinomycetes, thermophile bacteria, whiterot fungi, vinelandii, phosphate solubilizing bacteria, potassium solubilizing bacteria, cellulose-decomposing bacterium etc.
4) it is indoor with the water ratio that has added fermenting agent to be that 65% fermentation wastes particle is stacked in, the long 2m of heap body base portion, wide 1.5m, high 1m, and processings of banking up of fermenting, and monitor temperature and the water ratio of piling body.
5) when heap temperature reaches 55 ℃; The heap body is carried out turning to be handled; Strict control heap temperature≤75 ℃; Carrying out along with fermentation; Heap temperature reduces gradually, when heap temperature is lower than 55 ℃, carries out turning and handles in per 6 days; After heap temperature is reduced to room temperature (25 ℃); Continued again to bank up 14 days, and carried out turning in per 9 days and handle, make the agriculture and forestry organic waste material composting substrate; Wherein, In treating processes is banked up in fermentation,, the heap body begins to calculate when beginning to ferment, and per 7 days are to heap body sprinkling fermenting additive diluent (bamboo vinegar liquid diluent) once; Spray altogether 8 times; The consumption of each bamboo vinegar liquid diluent that sprays is the bamboo leachate diluent 2L that sprays preparation in 100kg (dry weight) the waste particle, and wherein, bamboo vinegar liquid is 1: 2000 with the ratio of the volume of water in the bamboo vinegar liquid diluent; The pH value of bamboo vinegar liquid is 2.6, and density is 1.2g/ml; Organic acid content is 9%, and content of phenolic compounds is 7%.Promptly in process was banked up in fermentation, every 100kg (dry weight) waste particle sprayed 16L bamboo vinegar liquid diluent altogether, that is to say, every 100kg (dry weight) waste particle sprays the 8ml bamboo vinegar liquid altogether; Simultaneously, when the water ratio of fermentation heap body less than 50% the time, spraying water to water ratio to the heap body reaches 65%.
2, agriculture and forestry organic waste material pyrolysis processing
1) adopting pulverizer is that 15% agriculture and forestry organic waste material stalk (wheat straw, straw etc.) is pulverized with water ratio, uses tablets press (Beijing many meanings Dragon Lords machinery limited liability companys) to process the waste particle that particle diameter is 1-2cm then.
2) open carbonizer, add the agriculture and forestry organic waste material particle behind the heat temperature raising to 90 ℃, under 90 ℃, dry to particle water ratio 8%;
3) continue to be heated to 180 ℃, under 180 ℃, the oxygen volumn concentration in the control carbonizer is 7%, under the described conditions pyrolysis processing 10min.
4) the waste particle of pyrolysis processing obtains agriculture and forestry organic waste material high temperature pyrolysis matrix in room temperature (25 ℃).
3, the preparation of cultivation mixed-matrix
1) gets the raw materials ready according to following weight proportion
Figure BDA0000060778090000141
2) above-mentioned raw materials is joined in the fermenter (Beijing Jingpuyuan Bio-engineering Co., Ltd.), add water, the water content of the mixture that makes reaches 60%, mixes, leave standstill 2 days after, being dried to water ratio is 15%, promptly gets.
Measure the performance index of the cultivation mixed-matrix of preparation, detected result is like table 2, shown in 3.
Embodiment 5
1, the agriculture and forestry organic waste material fermented manure is handled
1) employing pulverizer (Beijing many meanings Dragon Lords machinery limited liability companys) is considered the garden waste grass to be worth doing be ground into particle diameter≤0.5cm particle, makes the waste particle, measures waste particulate organic carbon content and nitrogen content simultaneously, and it is as shown in table 1 to measure the result.
2) in the waste particle, add urea, regulating waste particulate C/N ratio is 35, makes the fermented manure particle, wherein, adds urea 0.667kg in every 100kg waste particle (dry weight).
3) in fermented abandoned composition granule, add fermenting agent organic waste zymophyte bent (Beijing Jingpuyuan Bio-engineering Co., Ltd.) and water, and mix, make waste particulate water ratio reach 60%; Wherein, The consumption of fermenting agent is to be added with the bent 0.6kg of organic waste zymophyte in every 100kg (dry weight) waste particle; Wherein, Living bacteria count >=200,000,000 in the organic waste zymophyte song/g; The pH value is 5.5, and effectively viable bacteria contains actinomycetes, thermophile bacteria, whiterot fungi, vinelandii, phosphate solubilizing bacteria, potassium solubilizing bacteria, cellulose-decomposing bacterium etc.
4) it is indoor with the water ratio that has added fermenting agent to be that 60% fermentation wastes particle is stacked in, the long 2m of heap body base portion, wide 1.5m, high 1m, and processings of banking up of fermenting, and monitor temperature and the water ratio of piling body.
5) when heap temperature reaches 55 ℃; The heap body is carried out turning to be handled; Strict control heap temperature≤75 ℃; Carrying out along with fermentation; Heap temperature reduces gradually, when heap temperature is lower than 55 ℃, carries out turning and handles in per 6 days; After heap temperature is reduced to room temperature (25 ℃); Continued again to bank up 7 days, and carried out turning in per 7 days and handle, make the agriculture and forestry organic waste material composting substrate; Wherein, In treating processes is banked up in fermentation,, the heap body begins to calculate when beginning to ferment, and per 4 days are to heap body sprinkling fermenting additive diluent (wood vinegar diluent) once; Spray altogether 14 times; The consumption of each wood vinegar diluent that sprays is the pyroligneous liquor diluent 2L that sprays preparation in 100kg (dry weight) the waste particle, and wherein, wood vinegar is 3: 4000 with the ratio of the volume of water in the wood vinegar diluent; The pH value of wood vinegar is 3, and density is 1.3g/ml; Organic acid content is 9%, and content of phenolic compounds is 10%.Promptly in process was banked up in fermentation, every 100kg (dry weight) waste particle sprayed 28L wood vinegar diluent altogether, that is to say, every 100kg (dry weight) waste particle sprays the 21ml wood vinegar altogether; Simultaneously, when the water ratio of fermentation heap body less than 50% the time, spraying water to water ratio to the heap body reaches 60%.
2, agriculture and forestry organic waste material pyrolysis processing
1) adopting pulverizer is that 20% garden waste grass bits are pulverized with water ratio, uses tablets press to process the waste particle of particle diameter as 0.5-1.5cm then.
2) add the agriculture and forestry organic waste material particle after opening carbonizer (Beijing many meanings Dragon Lords machinery limited liability companys, SL-II type) heat temperature raising to 80 ℃, under 80 ℃, dry to particle water ratio 10%;
3) continue to be heated to 160 ℃, under 160 ℃, the oxygen volumn concentration in the control carbonizer is 5%, under the described conditions pyrolysis processing 15min.
4) the waste particle with pyrolysis processing obtains agriculture and forestry organic waste material high temperature pyrolysis matrix in room temperature (25 ℃).
3, the preparation of cultivation mixed-matrix
1) gets the raw materials ready according to following weight proportion
Figure BDA0000060778090000151
2) above-mentioned raw materials is joined in the fermenter (Beijing Jingpuyuan Bio-engineering Co., Ltd.), add water, the water content of the mixture that makes reaches 60%, mixes, leave standstill 2 days after, being dried to water ratio is 15%, promptly gets.
Measure the performance index of the cultivation mixed-matrix of preparation, detected result is like table 2, shown in 3.
Embodiment 6
1, the agriculture and forestry organic waste material fermented manure is handled
1) adopt pulverizer agricultural wastes mushroom slag (mushroom, straw mushroom, mushroom, auricularia auriculajudae, white fungus, hedgehog hydnum, dictyophora phalloidea, Trichotoma matsutake, dried mushroom, russule, bolete etc.) to be ground into the particle of particle diameter≤1cm; Make the waste particle; Measure waste particulate organic carbon content and nitrogen content simultaneously, it is as shown in table 1 to measure the result.
Table 1 agriculture and forestry organic waste material particulate characteristic
Organic carbon (%) TN(%)
Embodiment 1 47.61 0.79
Embodiment 2 36.87 1.0
Embodiment 3 34.3 0.48
Embodiment 4 39.61 0.86
Embodiment 5 42.5 4.4
Embodiment 6 38.7 0.54
2) in the waste particle, add urea, regulating waste particulate C/N ratio is 25, makes the fermented manure particle, wherein, adds urea 3.100kg in every 100kg waste particle (dry weight).
3) in fermented abandoned composition granule, add fermenting agent organic waste zymophyte bent (Beijing Jingpuyuan Bio-engineering Co., Ltd.) and water, and mix, make waste particulate water ratio reach 70%; Wherein, The consumption of fermenting agent is to be added with the bent 0.3kg of organic waste zymophyte in every 100kg (dry weight) waste particle; Wherein, Living bacteria count >=200,000,000 in the organic waste zymophyte song/g; The pH value is 5.5-8.5, and effectively viable bacteria contains actinomycetes, thermophile bacteria, whiterot fungi, vinelandii, phosphate solubilizing bacteria, potassium solubilizing bacteria, cellulose-decomposing bacterium etc.
4) it is indoor with the water ratio that has added fermenting agent to be that 70% fermentation wastes particle is stacked in, the long 2m of heap body base portion, wide 1.5m, high 1m, and processings of banking up of fermenting, and monitor temperature and the water ratio of piling body.
5) when heap temperature reaches 55 ℃; The heap body is carried out turning to be handled; Strict control heap temperature≤75 ℃; Carrying out along with fermentation; Heap temperature reduces gradually, when heap temperature is lower than 55 ℃, carries out turning and handles in per 6 days; After heap temperature is reduced to room temperature (25 ℃); Continued again to bank up 14 days, and carried out turning in per 6 days and handle, make the agriculture and forestry organic waste material composting substrate; Wherein, In treating processes is banked up in fermentation,, the heap body begins to calculate when beginning to ferment, and per 3 days are to heap body sprinkling fermenting additive diluent (bamboo vinegar liquid diluent) once; Spray altogether 16 times; The consumption of each bamboo vinegar liquid diluent that sprays is the bamboo leachate diluent 2L that sprays preparation in 100kg (dry weight) the waste particle, and wherein, bamboo vinegar liquid is 1: 1000 with the ratio of the volume of water in the bamboo vinegar liquid diluent; The pH value of bamboo vinegar liquid is 2.5, and density is 1g/ml; Organic acid content is 9%, and content of phenolic compounds is 8%.Promptly in process was banked up in fermentation, every 100kg (dry weight) waste particle sprayed 32L bamboo vinegar liquid diluent altogether, that is to say, every 100kg (dry weight) waste particle sprays the 32ml bamboo vinegar liquid altogether; Simultaneously, when the water ratio of fermentation heap body less than 50% the time, spraying water to water ratio to the heap body reaches 70%.
2, agriculture and forestry organic waste material pyrolysis processing
1) adopting pulverizer is that 20% agricultural wastes mushroom slag (mushroom, straw mushroom, mushroom, auricularia auriculajudae, white fungus, hedgehog hydnum, dictyophora phalloidea, Trichotoma matsutake, dried mushroom, russule, bolete etc.) is pulverized with water ratio, uses tablets press to process the waste particle of particle diameter as 1-2cm then.
2) add the agriculture and forestry organic waste material particle after opening carbonizer (Beijing many meanings Dragon Lords machinery limited liability companys, SL-II type) heat temperature raising to 100 ℃, under 100 ℃, dry to particle water ratio 5%.
3) continue to be heated to 190 ℃, under 190 ℃, the oxygen volumn concentration in the control carbonizer is 5%, under the described conditions pyrolysis processing 10min.
4) stop heating, the waste particle after the taking-up pyrolysis processing is soaked in the water, carries out desalting treatment, and wherein soak time is 20min, and water and particulate volume ratio are 3: 1.
5) waste particle natural air drying to the particle water ratio under room temperature (25 ℃) with desalting treatment is 20%, obtains agriculture and forestry organic waste material high temperature pyrolysis matrix.
3, the preparation of cultivation mixed-matrix
1) gets the raw materials ready according to following weight proportion
Figure BDA0000060778090000171
2) above-mentioned raw materials is joined in the fermenter (Beijing Jingpuyuan Bio-engineering Co., Ltd.), add water, the water content of the mixture that makes reaches 60%, mixes, leave standstill 2 days after, being dried to water ratio is 15%, promptly gets.
Measure the performance index of the cultivation mixed-matrix of preparation, detected result is like table 2, shown in 3.
Reference examples
With Denmark Pin Shi (Pindstrup) peat is reference examples.The unit dry weight of reference examples matrix, maximum retention ability, total porosity, ventilating slit, water holding hole, pH value, EC value, total content of humic acid, TN, TP, TK and organic content are measured as described in example 1 above method and are carried out.Detected result is like table 2, shown in 3.
The basic physical behavior of table 2 cultivation matrix
Detected result in the table 1 shows:
1, the unit dry weight of the cultivation mixed-matrix of the present invention's preparation is 0.16-0.28g/cm 3, meet the cultivation matrix unit weight (0.1~0.8g/cm of plant-growth 3) requirement, suitable with the unit weight of reference examples peat growing medium, show that cultivation matrix of the present invention is loose, permeability is good, and fixing plant performance is good;
2, the total porosity of the cultivation matrix of the present invention's preparation is 74.32-84.30%, and the ventilation space reaches air permeability and the good water-retaining property that 19.04-26.53.% shows soilless culture substrate of the present invention; The maximum retention ability of matrix of the present invention reaches 1.92-3.61g/g; The water holding hole reaches 53.94-59.79%; The water-retaining capacity that soilless culture substrate of the present invention is described is strong; All but sticking is equivalent to the about 1.92-3.61 of the own wt water yield doubly; Can be plant competent moisture condition is provided; And can reduce the number of times that waters, water saving, streamlining management measure;
3, performance index such as the air permeability of the cultivation mixed-matrix of the present invention's preparation, water-retentivity, unit weight all meet the requirement of plant growth medium; And the peat growing medium that its physicochemical property all approach even are better than contrasting satisfies the requirement of soilless culture solid substrate.
4, the present invention preparation cultivation mixed-matrix unit weight less, the loose hole of matrix is many; Air permeability is good; Be beneficial to the growth of arrowroot and the conversion of matrix nutrient, can satisfy the demand of Calathea orbifolia growth, promote the accumulation of its biomass during growing water, gas, nutrient etc.
The basic chemical property of table 3 cultivation matrix
Embodiment 1 Embodiment 2 Embodiment 3 Embodiment 4 Embodiment 5 Embodiment 6 Reference examples
pH 6.98 6.79 6.53 6.79 6.36 7.02 6.42
EC(mS/cm) 0.68 0.74 0.94 0.92 1.09 1.12 0.38
TN 1.76 1.46 1.97 2.15 2.16 1.88 1.05
TP 0.14 0.84 0.96 0.82 0.28 0.76 0.09
TK 1.00 1.09 1.28 0.94 1.04 1.20 0.02
Organic % 79.42 63.83 83.26 80.12 88.52 74.83 90.06
Total humic acid % 28.63 22.23 26.57 27.38 27.63 21.04 21.72
C/N 26.17 23.73 24.51 21.62 23.77 23.09 49.75
The detected result of table 3 shows:
1, the potential of hydrogen of the cultivation mixed-matrix of the present invention's preparation is weak acid to neutral, and pH is 6.36-7.02; The EC value is 0.68-1.12mS/cm; Illustrate that mixed cultivation solid substrate of the present invention can provide stable matrix growing environment for plant; Can not cause toxic action, can not cause detrimentally affect yet, not influence the balance of nutritive medium the nutritive medium that puts on plant to plant.
2, in the soilless culture substrate of the present invention; Total nitrogen content is 1.46-2.16%; Content of tatal phosphorus is 0.14-0.96%, and full potassium content is 0.94-1.28%, and content of humic acid is 21.04-28.63%; Organic content is 63.83-88.52%; C/N is 21.62-26.17, shows that the trophic structure of cultivating mixed-matrix is reasonable, is convenient to plant absorbing; For the growth of plant provides the sufficient nutrient element, satisfy the plant-growth needs.
3, the cultivation matrix quality of the present invention preparation has reached the quality of import peat growing medium, can import substitutes, practiced thrift expense greatly.
The pot experiment of Test Example 1 Calathea orbifolia
In Beijing Daxing flowers company Calathea orbifolia cultivation greenhouse, adopt the Pin Shi peat growing medium of cultivation mixed-matrix and the reference examples of embodiment of the invention 1-6 preparation to carry out the pot experiment of Calathea orbifolia respectively.Full-automatic temperature-controlling, ventilation facility can guarantee at duration of test in the greenhouse, for supplying the examination material a metastable suitable growth environment are provided.
Choose the about 15cm of plant height; The leaf growth stalwartness is consistent, root system is complete, Calathea orbifolia (the Calathca rotundifola cv.Fasciata.) seedling of no disease and pest; Place in the plastic flowerpot of 180mm * 160mm; Carry out pot experiment; Each cultivation matrix is a processing; 60 repetitions are carried out in each processing, and promptly each cultivation matrix is cultivated 60 strain arrowroots, and potted plant adopts completely random to put.Except that cultivation matrix, other envrionment conditions and cultivation management measure all are consistent.Behind the last basin about 180 days; Arrowroot all reaches the most productive period of nourishing and growing; Each is handled picked at random 10 strains; Observing root grabs native ability and plant is taken out clean; Measure growth indexes; Measure and total fresh weight of record plant, plant height, always be preced with the width of cloth, root fresh weight, leaf fresh weight, send out a branch number (leaf is long>10cm), heavy, the oven dry Ye Chong of oven dry root etc.; Measure the result respectively shown in table 4-6; Wherein testing data adopts Microsoft Office Excel 2007 and SPSS16.0 data processing software, carries out variance analysis and multiple comparisons.
1, matrix is to the influence of arrowroot aerial growth situation
Table 4 different substrates handles the Calathea orbifolia plant height, always be preced with the width of cloth and send out the influence of branch number
Plant height average (cm) Total hat width of cloth average (cm 2) Send out a branch number (average (individual) of leaf diameter>10cm)
Embodiment 1 47.03 bc ?3650.10 a 26 ab
Embodiment 2 45.73 bc ?3026.31 b 22 b
Embodiment 3 52.43 a ?3809.91 a 27 a
Embodiment 4 49.97 ab ?3654.60 a 26 ab
Embodiment 5 43.63 c ?3007.05 b 23 ab
Embodiment 6 46.03 bc ?3082.57 b 24 ab
Reference examples 45.67 bc ?2695.23 b 24 ab
2, matrix is to the influence of arrowroot biomass
Table 5 different substrates is handled the variation to the Calathea orbifolia biomass
Figure BDA0000060778090000201
Table 6 different substrates is handled the variation to the Calathea orbifolia biomass
Figure BDA0000060778090000202
Figure BDA0000060778090000211
Test-results shows:
1) adopt the arrowroot shoot and leaf growth of cultivation mixed-matrix plantation of the present invention sturdy, color and luster is dark green, and exterior quality is good.
2) utilize the cultivation matrix of the inventive method preparation to cultivate Calathea orbifolia; Matrix is remarkable to the promoter action of plant strain growth; The plant strain growth later stage; The hat width of cloth is big; Plant is high; The plant biomass accumulation is high; Underground part dry-matter accumulation amount reaches the 38.433-53.900g/ strain; Over-ground part dry-matter accumulation amount reaches the 36.167-58.767g/ strain; The accumulation of biomass is higher than the peat growing medium of import; The cultivation matrix of the inventive method preparation has reached the peat growing medium quality, therefore can substitute peat growing medium, has lowered the expense of cultivation matrix greatly.
The test of planting of Test Example 2 new pteris ferns
The Pin Shi peat growing medium of the cultivation mixed-matrix of employing embodiment of the invention 1-6 preparation and reference examples carries out the pot experiment of new pteris fern in Daxing, Beijing flowers company cultivating Asplenium nidus greenhouse.Full-automatic temperature-controlling, ventilation facility can guarantee at duration of test in the greenhouse, for supplying the examination material a metastable suitable growth environment are provided.
Choose the about 15cm of plant height; The leaf growth stalwartness is consistent, root system is complete, new pteris fern (the Asplenium antiquum Aspleniumnidu) seedling of no disease and pest; Place in the plastic flowerpot of 180mm * 160mm; Carry out pot experiment; Each cultivation matrix is a processing; 60 repetitions are carried out in each processing, and promptly each cultivation matrix is cultivated 60 strain new pteris ferns, and potted plant adopts completely random to put.Except that cultivation matrix, other envrionment conditions and cultivation management measure all are consistent.Behind the last basin about 180 days; New pteris fern all reaches the most productive period of nourishing and growing; Each is handled picked at random 10 strains; Plant is taken out clean; The mensuration growth indexes is measured and total fresh weight, plant height, root fresh weight, leaf fresh weight, foliation number, the oven dry root of record plant are heavy, dry Ye Chong etc., measures the result respectively shown in table 7-9; Wherein testing data adopts Microsoft Office Excel 2007 and SPSS16.0 data processing software, carries out variance analysis and multiple comparisons.
1, matrix is to the influence of arrowroot aerial growth situation
Table 8 different substrates is handled the influence to a new pteris fern plant height and a branch number
Plant height average (cm) Foliation number average value (individual)
Embodiment 1 69.33 ab 59 b
Embodiment 2 69.33 ab 56 c
Embodiment 3 72.08 a 62 a
Embodiment 4 72.74 a 59 b
Embodiment 5 68.80 ab 55 c
Embodiment 6 65.53 b 55 c
Reference examples 54.69 c 53 d
2, matrix is to the influence of new pteris fern biomass
Table 9 different substrates is handled the variation to the new pteris fern biomass
Table 10 different substrates is handled the variation to the new pteris fern biomass
Figure BDA0000060778090000222
Test-results shows:
1) adopt the new pteris fern shoot and leaf growth of cultivation mixed-matrix plantation of the present invention sturdy, color and luster is dark green, and exterior quality is good.
2) utilize the cultivation matrix of the inventive method preparation to cultivate new pteris fern; Matrix is remarkable to the promoter action of plant strain growth; The plant strain growth later stage; The hat width of cloth is big; Plant is high; The plant biomass accumulation is high; Over-ground part dry-matter accumulation amount reaches the 44.000-47.580g/ strain; Underground part dry-matter accumulation amount reaches the 47.843-52.123g/ strain; The accumulation of biomass is higher than the peat growing medium of import; The cultivation matrix of the inventive method preparation has reached the peat growing medium quality, therefore can substitute peat growing medium, has lowered the expense of cultivation matrix greatly.

Claims (10)

1. a plant cultivating mixed-matrix comprises matrix peat, agriculture and forestry organic waste material composting substrate, agriculture and forestry organic waste material pyrolysis matrix and sterilant.
2. cultivation mixed-matrix as claimed in claim 1; The volume that it is characterized in that said matrix peat is 10-40: 60-90 with the ratio of the cumulative volume of agriculture and forestry organic waste material composting substrate and agriculture and forestry organic waste material pyrolysis matrix; Wherein, the ratio of the volume of agriculture and forestry organic waste material composting substrate and agriculture and forestry organic waste material pyrolysis matrix is 1: 0.4-3.5.
3. cultivation mixed-matrix as claimed in claim 1 or 2, the consumption that it is characterized in that said sterilant is every 1m 3Matrix peat, agriculture and forestry organic waste material composting substrate and agriculture and forestry organic waste material high temperature pyrolysis matrix in add sterilant 0.1-2kg.
4. one of cultivation mixed-matrix as claimed in claim 1 or 2; It is characterized in that said agriculture and forestry organic waste material composting substrate is prepared from according to following steps: after agriculture and forestry organic waste material, fermenting agent and fermenting additive are mixed; Carry out fermentative processing; Wherein, said fermenting additive is that bamboo vinegar liquid is or/and wood vinegar.
5. cultivation mixed-matrix as claimed in claim 4, the consumption that it is characterized in that fermenting additive are that the adding volume is the said fermenting additive of 8-50ml in every 100kg agriculture and forestry organic waste material.
6. cultivation mixed-matrix as claimed in claim 4, the weight part proportioning that it is characterized in that said agriculture and forestry organic waste material and fermenting agent is 100: 0.1-1.
7. cultivation mixed-matrix as claimed in claim 4 is characterized in that said fermentative processing comprises following step in sequence:
1) with after the agriculture and forestry organic waste material pulverizing, regulates its C/N than being 20-35;
2) add fermenting agent and water, mix, make the water ratio of waste reach 60-70%;
3) waste is piled the fermentation heap body; The fermentative processing of banking up; Wherein, The temperature and the water ratio of monitoring heap body in the fermentative processing process of banking up; Every 3-7 days to fermentation heap body sprinkling fermenting additive once; The consumption of each fermenting additive that sprays is that every 100kg waste sprays 1-2.5ml, and when the water ratio of fermentation heap body less than 50% the time, spray water to water ratio and reach 60-70% to piling body.
8. cultivation mixed-matrix as claimed in claim 7, carry out turning according to following mode in the fermentative processing that it is characterized in that banking up described in the step 3):
A) when heap temperature is higher than 55 ℃, carry out turning and handle, the control heap temperature is lower than 75 ℃;
B) be reduced to gradually when being lower than 55 ℃ when heap temperature, carried out turning and handle in every 6-12 days;
C) after heap temperature is reduced to 20-35 ℃, continue again to stack 7-21 days, wherein, carried out turning and handle in every 6-12 days.
9. cultivation mixed-matrix as claimed in claim 1 or 2; It is characterized in that said agriculture and forestry organic waste material pyrolysis matrix is prepared from according to following steps: the agriculture and forestry organic waste material of water ratio≤10% is carried out the high temperature pyrolysis processing; Collecting solid product promptly gets; Wherein, The temperature of pyrolysis processing is 160-220 ℃; Treatment time 10-20min, control oxygen volumn concentration≤10% in the said high temperature pyrolysis treating processes.
10. the preparation method of plant growing mixed-matrix according to claim 1 is characterized in that raw material matrix peat, agriculture and forestry organic waste material composting substrate, agriculture and forestry organic waste material pyrolysis matrix and sterilant are mixed.
CN2011101224538A 2011-05-12 2011-05-12 Plant cultivation mixed medium and preparation method thereof Expired - Fee Related CN102303991B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2011101224538A CN102303991B (en) 2011-05-12 2011-05-12 Plant cultivation mixed medium and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2011101224538A CN102303991B (en) 2011-05-12 2011-05-12 Plant cultivation mixed medium and preparation method thereof

Publications (2)

Publication Number Publication Date
CN102303991A true CN102303991A (en) 2012-01-04
CN102303991B CN102303991B (en) 2013-01-23

Family

ID=45377935

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2011101224538A Expired - Fee Related CN102303991B (en) 2011-05-12 2011-05-12 Plant cultivation mixed medium and preparation method thereof

Country Status (1)

Country Link
CN (1) CN102303991B (en)

Cited By (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102627481A (en) * 2012-04-09 2012-08-08 北京林业大学 Preparation method of plant cultivation substrate and cultivation substrate prepared by such method
CN103340096A (en) * 2013-07-05 2013-10-09 北京林业大学 Ecological cushion
CN103430818A (en) * 2013-08-09 2013-12-11 盐城工学院 Biomass charcoal seedling culturing material with high germination percentage and preparation method and application thereof
CN103588568A (en) * 2013-11-10 2014-02-19 湖州艺萌城市农业发展有限公司 Melon and fruit substrate soil for micro agriculture
CN103733965A (en) * 2014-01-15 2014-04-23 东北师范大学 Production method of composite diatomite soilless culture substrate for ginseng
CN103936517A (en) * 2014-04-25 2014-07-23 董大鹏 Special greening matrix for saline-alkali soil and preparation method thereof
CN104072321A (en) * 2014-07-11 2014-10-01 河北民族师范学院 Soil conditioner and preparation method thereof
CN105638416A (en) * 2016-02-01 2016-06-08 攀枝花丽新园艺技术有限公司 New pteris fern spore seedling growing method
CN106106073A (en) * 2016-06-22 2016-11-16 吉林省林业科学研究院 A kind of method utilizing discarded Auricularia fungus matrix manufacturing Breeding of Fraxinus mandshurica substrate
CN106187431A (en) * 2016-06-30 2016-12-07 全椒县大墅镇刘邦家庭农场 A kind of purple taro sowing seed dressing
CN106556550A (en) * 2016-11-09 2017-04-05 北京林业大学 The method for promoting Larix principis-rupprechtii Decomposition of leaf litter
CN111066621A (en) * 2019-11-19 2020-04-28 龙川县顺利农业生态旅游投资有限公司 Asplenium nidus culture medium and preparation method thereof
CN114621041A (en) * 2022-03-24 2022-06-14 金华生物质产业科技研究院 Method for preparing plant growth promoting agent by using kitchen waste and agricultural and forestry waste in synergy mode
CN114731928A (en) * 2022-04-08 2022-07-12 丽水市瑞芝食用菌科技有限公司 Process and equipment for manufacturing culture medium by using agricultural, forestry and animal husbandry wastes
CN114847126A (en) * 2021-05-26 2022-08-05 北京城市排水集团有限责任公司 Catharanthus roseus culture medium and preparation method and application thereof

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101548639A (en) * 2009-01-15 2009-10-07 孙向阳 Flower cultivation medium and preparing method thereof
CN101715721A (en) * 2010-02-01 2010-06-02 北京林业大学 Method for preparing soil-less culture substrate with agriculture and forestry organic waste material and soil-less culture substrate

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101548639A (en) * 2009-01-15 2009-10-07 孙向阳 Flower cultivation medium and preparing method thereof
CN101715721A (en) * 2010-02-01 2010-06-02 北京林业大学 Method for preparing soil-less culture substrate with agriculture and forestry organic waste material and soil-less culture substrate

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
田赟等: "农林废弃物环保型基质再利用研究进展与展望", 《土壤通报》 *

Cited By (18)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102627481A (en) * 2012-04-09 2012-08-08 北京林业大学 Preparation method of plant cultivation substrate and cultivation substrate prepared by such method
CN103340096B (en) * 2013-07-05 2014-11-26 北京林业大学 Ecological cushion
CN103340096A (en) * 2013-07-05 2013-10-09 北京林业大学 Ecological cushion
CN103430818A (en) * 2013-08-09 2013-12-11 盐城工学院 Biomass charcoal seedling culturing material with high germination percentage and preparation method and application thereof
CN103588568A (en) * 2013-11-10 2014-02-19 湖州艺萌城市农业发展有限公司 Melon and fruit substrate soil for micro agriculture
CN103733965A (en) * 2014-01-15 2014-04-23 东北师范大学 Production method of composite diatomite soilless culture substrate for ginseng
CN103936517B (en) * 2014-04-25 2016-01-20 董大鹏 A kind of saline land greening dedicated substrate and preparation method thereof
CN103936517A (en) * 2014-04-25 2014-07-23 董大鹏 Special greening matrix for saline-alkali soil and preparation method thereof
CN104072321A (en) * 2014-07-11 2014-10-01 河北民族师范学院 Soil conditioner and preparation method thereof
CN104072321B (en) * 2014-07-11 2016-08-17 河北民族师范学院 A kind of soil conditioner and preparation method thereof
CN105638416A (en) * 2016-02-01 2016-06-08 攀枝花丽新园艺技术有限公司 New pteris fern spore seedling growing method
CN106106073A (en) * 2016-06-22 2016-11-16 吉林省林业科学研究院 A kind of method utilizing discarded Auricularia fungus matrix manufacturing Breeding of Fraxinus mandshurica substrate
CN106187431A (en) * 2016-06-30 2016-12-07 全椒县大墅镇刘邦家庭农场 A kind of purple taro sowing seed dressing
CN106556550A (en) * 2016-11-09 2017-04-05 北京林业大学 The method for promoting Larix principis-rupprechtii Decomposition of leaf litter
CN111066621A (en) * 2019-11-19 2020-04-28 龙川县顺利农业生态旅游投资有限公司 Asplenium nidus culture medium and preparation method thereof
CN114847126A (en) * 2021-05-26 2022-08-05 北京城市排水集团有限责任公司 Catharanthus roseus culture medium and preparation method and application thereof
CN114621041A (en) * 2022-03-24 2022-06-14 金华生物质产业科技研究院 Method for preparing plant growth promoting agent by using kitchen waste and agricultural and forestry waste in synergy mode
CN114731928A (en) * 2022-04-08 2022-07-12 丽水市瑞芝食用菌科技有限公司 Process and equipment for manufacturing culture medium by using agricultural, forestry and animal husbandry wastes

Also Published As

Publication number Publication date
CN102303991B (en) 2013-01-23

Similar Documents

Publication Publication Date Title
CN102295488B (en) Mixed plant culture medium and preparation method thereof
CN102303991B (en) Plant cultivation mixed medium and preparation method thereof
CN102617239B (en) Compound type plant cultivation matrix and preparation method thereof
CN102627481B (en) Preparation method of plant cultivation substrate and cultivation substrate prepared by such method
CN101697705B (en) Soilless culture organic matrix used for tomato seedling raising and preparation method thereof
CN103848701B (en) A kind of preparation method of soilless plant cultivation matrix and the matrix prepared by the method
CN103621353B (en) A kind of seedling medium and preparation method thereof
CN104387136A (en) Method for producing organic fertilizer from municipal dry branch/fallen leaf waste and application thereof
CN102633544B (en) Method for taking farmyard manure as raw material to produce tobacco biofertilizer
CN102939892B (en) Method for preparing organic seedling-raising lightweight medium by taking pinus kesiya barks as raw materials
CN104261983A (en) Method for preparing culture substrate
CN102976839A (en) Scindapsus aureus cultivation medium and preparation method thereof
CN106673878A (en) Seedling raising nutritive bowl and preparation method thereof
CN105272421A (en) Agricultural culturing medium, producing method thereof and application thereof
CN103435410A (en) Fully-nutritional biochar used as flower culture medium, and preparation method thereof
CN104860738A (en) Biomass charcoal-based seedling growing matrix and preparation method thereof
CN102503654A (en) Seedling raising substrate for mechanically-transplanting rice
CN101697704A (en) Soilless cultivation organic substrate used for seedling raising of capsicums and preparation method thereof
CN106187338A (en) A kind of soilless plant cultivation substrate and preparation method thereof
CN105503333A (en) Seedling raising medium special for organic rice
CN109197512A (en) A kind of organic culture substrate and preparation method thereof
CN107188674A (en) A kind of medium for culturing solanaceous fruit vegetable seedlings and preparation method thereof
CN106083354A (en) Plant cultivation media conditioner, this conditioner is utilized to prepare the method for compound cultivation matrix and the cultivation matrix of preparation
CN105638399A (en) Functional soilless culture substrate taking mushroom dregs and biogas dregs as raw materials
CN111972254A (en) Method for producing seedling raising substrate by using vegetable straw compost

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20130123

Termination date: 20150512

EXPY Termination of patent right or utility model