[go: up one dir, main page]

CN102180715A - Straw compost after-ripening accelerator and use method thereof - Google Patents

Straw compost after-ripening accelerator and use method thereof Download PDF

Info

Publication number
CN102180715A
CN102180715A CN2011100248408A CN201110024840A CN102180715A CN 102180715 A CN102180715 A CN 102180715A CN 2011100248408 A CN2011100248408 A CN 2011100248408A CN 201110024840 A CN201110024840 A CN 201110024840A CN 102180715 A CN102180715 A CN 102180715A
Authority
CN
China
Prior art keywords
compost
straw
ripening
composting
treatment
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
CN2011100248408A
Other languages
Chinese (zh)
Other versions
CN102180715B (en
Inventor
彭智平
黄继川
杨少海
于俊红
李文英
杨林香
林志军
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.)
Institute of Agricultural Resources and Environment of Guangdong Academy of Agricultural Sciences
Original Assignee
GUANGDONG AAS SOIL AND FERTILIZER RESEARCH INSTITUTE
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 GUANGDONG AAS SOIL AND FERTILIZER RESEARCH INSTITUTE filed Critical GUANGDONG AAS SOIL AND FERTILIZER RESEARCH INSTITUTE
Priority to CN2011100248408A priority Critical patent/CN102180715B/en
Publication of CN102180715A publication Critical patent/CN102180715A/en
Application granted granted Critical
Publication of CN102180715B publication Critical patent/CN102180715B/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)

Abstract

本发明涉及秸秆堆肥处理技术领域,具体是提供一种秸秆堆肥后熟促进剂及其使用方法。本发明的组成为:10-20kg的造纸污泥、0~10kg的纤维素酶、5~10kg的甜菜碱及2~5kg的精氨酸。使用方法是:在常规堆肥高温转为低温阶段加入乌洛托品调整剂,并加入后熟促进剂和表面活性剂,常温堆制10-15天。采用本发明,秸秆纤维素分解率可达50%以上,堆制产物在作物上使用的增产效果显著,并具有改良土壤,提高农产品品质的效果。The invention relates to the technical field of straw composting treatment, and in particular provides a straw composting post-ripening accelerator and a use method thereof. The composition of the invention is: 10-20kg of papermaking sludge, 0-10kg of cellulase, 5-10kg of betaine and 2-5kg of arginine. The method of use is: add urotropine regulator, post-ripening accelerator and surfactant at the stage of normal composting from high temperature to low temperature, and compost at normal temperature for 10-15 days. By adopting the invention, the straw cellulose decomposition rate can reach more than 50%, and the use of the composting products on crops has a significant effect of increasing production, and has the effects of improving soil and improving the quality of agricultural products.

Description

一种秸秆堆肥后熟促进剂及其使用方法A kind of straw compost post-ripening accelerator and its application method

技术领域technical field

本发明涉及秸秆堆肥处理技术领域,具体是提供一种秸秆堆肥后熟促进剂及其使用方法。The invention relates to the technical field of straw composting treatment, and in particular provides a straw composting post-ripening accelerator and a use method thereof.

背景技术Background technique

我国是粮食生产大国,也是秸秆生产大国。加强农作物秸秆综合利用,是我国新阶段农业和农村经济发展的一项重大课题。但农民往往采用焚烧的方式处理,秸秆乱丢乱弃的现象十分严重,造成严重的资源浪费并加剧了对环境的污染,已成为我国农业和农村环境建设中亟待解决的共性问题。加强秸秆的发酵腐熟和利用技术研究,是秸秆资源有效利用和适应农业可持续发展需要的较佳途径,既有利于资源的合理利用,又可广辟肥源,提高土壤生产力,减少污染。my country is a big country of grain production and also a big country of straw production. Strengthening the comprehensive utilization of crop stalks is a major issue in my country's new stage of agricultural and rural economic development. However, farmers often use incineration to deal with it, and the phenomenon of straw littering is very serious, causing serious waste of resources and exacerbating environmental pollution. Strengthening the research on straw fermentation and utilization technology is a better way to effectively utilize straw resources and meet the needs of sustainable agricultural development.

由于秸秆中纤维素、半纤维素和木质素在堆肥过程中降解速度缓慢,采用传统的堆肥方法耗时长,成本高,又不利于氮素养分的保存,已成为堆肥技术中的主要难题。接种纤维分解菌,并选择合适的条件成为秸秆堆肥的重要技术,由于堆肥过程中物料温度会呈现低温-高温-低温的变化,纤维分解菌在高温条件下难以成活,现有专利和文献报道往往在堆肥初期接种纤维分解菌在低温阶段有一定的效果,但进入高温阶段纤维素的分解就大受影响。因此,秸秆堆肥往往需要较长的时间,同时,腐熟程度不高,大田使用效果大受影响。Due to the slow degradation rate of cellulose, hemicellulose and lignin in the composting process, the traditional composting method is time-consuming, high cost, and not conducive to the preservation of nitrogen nutrients, which has become a major problem in composting technology. Inoculation of cellulolytic bacteria and selection of suitable conditions have become an important technology for straw composting. Since the temperature of the material during the composting process will change from low temperature to high temperature to low temperature, it is difficult for cellulolytic bacteria to survive under high temperature conditions. Existing patents and literature reports often The inoculation of cellulolytic bacteria in the initial stage of composting has a certain effect in the low temperature stage, but the decomposition of cellulose will be greatly affected in the high temperature stage. Therefore, straw composting often takes a long time, and at the same time, the degree of decomposition is not high, and the effect of field use is greatly affected.

发明内容Contents of the invention

本发明是针对以上不足,提供一种秸秆堆肥后熟促进剂及其使用方法,其解决了采用常规的堆肥方法时纤维素分解率低,堆肥产物难以达到分解纤维素的问题。The present invention aims at the above deficiencies, and provides a post-ripening accelerator for straw composting and its use method, which solves the problem that the cellulose decomposition rate is low and the compost product is difficult to decompose cellulose when the conventional composting method is adopted.

本发明所采用的技术方案如下:The technical scheme adopted in the present invention is as follows:

一种秸秆堆肥后熟促进剂,其组分包含有:造纸污泥10-50kg,纤维素酶0~10kg;甜菜碱5~10kg;精氨酸0~10kg。A post-ripening accelerator for straw composting, the components of which include: 10-50 kg of papermaking sludge, 0-10 kg of cellulase, 5-10 kg of betaine, and 0-10 kg of arginine.

组分按照重量比为:造纸污泥10-20kg;纤维素酶2~6kg;甜菜碱6~8kg;精氨酸2~5kg。According to the weight ratio, the components are: 10-20kg of papermaking sludge; 2-6kg of cellulase; 6-8kg of betaine; and 2-5kg of arginine.

一种秸秆堆肥后熟促进剂的使用方法,其方法步骤包括:A method for using a post-ripening accelerator for straw composting, the method steps comprising:

A、在每立方堆肥中加入乌洛托品5-20kg,翻堆混匀,放置4-5天;A. Add 5-20kg of urotropine to each cubic compost, turn the compost and mix well, and place it for 4-5 days;

B、加入造纸污泥10-50kg,纤维素酶0~10kg;甜菜碱5~10kg;精氨酸0~10kg;表面活性剂5-10kg,放置10-15天后物料腐熟。B. Add 10-50kg of papermaking sludge, 0-10kg of cellulase, 5-10kg of betaine, 0-10kg of arginine, and 5-10kg of surfactant, and the material will be decomposed after 10-15 days.

步骤B需要在满足步骤A的堆肥堆体温度低于45℃的前提下进行。Step B needs to be carried out under the premise that the temperature of the compost heap satisfying step A is lower than 45°C.

步骤B采用翻堆混匀或分层添加的方法。Step B adopts the method of turning over and mixing or adding in layers.

步骤B中加入的造纸污泥为10-20kg,纤维素酶为2~6kg,甜菜碱为6~8kg,精氨酸为2~5kg。The amount of papermaking sludge added in step B is 10-20 kg, the amount of cellulase is 2-6 kg, the amount of betaine is 6-8 kg, and the amount of arginine is 2-5 kg.

表面活性剂为卵磷脂、羟乙基纤维素、环糊精、海藻酸中的一种或两种。The surfactant is one or two of lecithin, hydroxyethyl cellulose, cyclodextrin and alginic acid.

与已有技术相比,本发明具有如下技术优势:Compared with the prior art, the present invention has the following technical advantages:

1、本发明的一种秸秆堆肥后熟促进剂,所含物质无毒无害,对作物有调节生长的作用;1. A post-ripening accelerator for straw composting of the present invention, the contained substance is non-toxic and harmless, and has the effect of regulating the growth of crops;

2、与常规堆肥比较,本发明涉及的配方在堆肥高温转为低温时使用,主要目的在于促进秸秆中纤维素物质的分解,从而促进堆料的腐熟。2. Compared with conventional composting, the formula involved in the present invention is used when the high temperature of composting turns to low temperature, the main purpose is to promote the decomposition of cellulose in the straw, thereby promoting the composting of the compost.

使用本发明一种秸秆堆肥后熟促进剂,秸秆纤维素分解率可达50%以上,堆制产物在作物上使用的增产效果显著,且本发明的秸秆堆肥后熟促进剂还具有改良土壤,提高农产品品质的效果。Using the post-ripening accelerator for straw composting of the present invention, the decomposition rate of straw cellulose can reach more than 50%, and the effect of increasing the yield of the composting product on crops is remarkable, and the post-ripening accelerator for straw composting of the present invention also has the function of improving soil, The effect of improving the quality of agricultural products.

具体实施方式Detailed ways

下面结合具体实施例对本发明的一种秸秆堆肥后熟促进剂及其使用方法作进一步的描述。The following is a further description of a straw compost post-ripening accelerator and its application method according to the present invention in conjunction with specific examples.

实施例1:Example 1:

采用牛粪、花生麸和玉米秸秆为堆肥材料,室外条垛堆肥。具体步骤和工艺条件如下:Cow dung, peanut bran and corn stalks are used as compost materials, and composted in strips outdoors. Concrete steps and process conditions are as follows:

将玉米秸秆风干粉碎至5厘米以下备用。将含水量为80%的牛粪320kg和含水量11%的风干粉碎玉米秸秆140kg以及含水量8%的花生麸40kg充分混合,堆肥物料含水量为55%;将堆肥物料堆成80厘米左右高度,塑料膜覆盖,5天翻堆1次。The corn stalks are air-dried and crushed to less than 5 cm for later use. Fully mix 320kg of cow dung with a moisture content of 80%, 140kg of air-dried crushed corn stalks with a moisture content of 11%, and 40kg of peanut bran with a moisture content of 8%. , covered with plastic film, turned once every 5 days.

待堆体温度下降至45℃以下时,将堆肥分成两等份。其中一份按照10kg/立方堆料用量加入乌洛托品,翻堆混匀,作用4天;之后按照20kg/立方米添加堆肥后熟促进剂(按造纸污泥10kg,纤维素酶3kg,甜菜碱6kg,精氨酸3kg配制),5kg/立方米添加表面活性剂,充分混匀后塑料膜覆盖。另一份加入等量的含水量50%的泥土作为对照,充分混匀用塑料膜覆盖。When the temperature of the heap drops below 45°C, divide the compost into two equal parts. One of them adds urotropine according to the amount of 10kg/cubic stockpile, turns and mixes the pile, and acts for 4 days; then adds a compost post-ripening accelerator according to 20kg/m3 (according to 10kg of papermaking sludge, 3kg of cellulase, sugar beet Alkali 6kg, arginine 3kg preparation), 5kg/cubic meter add surfactant, fully mix and cover with plastic film. The other part added the same amount of soil with a water content of 50% as a control, mixed well and covered with a plastic film.

堆肥后熟条件控制一致,经过15天,物料腐熟。测定结果见表1。After composting, the post-ripening conditions are controlled uniformly, and after 15 days, the materials are decomposed. The measurement results are shown in Table 1.

堆肥肥效试验①:采用芥菜作试验材料进行盆栽试验。试验共设4个处理,每盆装土12kg,施肥的3个处理在等养分条件下施肥,处理1:单施秸秆堆肥(100g堆肥/盆,养分含量为N 21.72g/kg,P2O5 24.27/kg,K2O 27.83g/kg)、处理2:单施化肥(46%尿素4.72g,12%过磷酸钙20.25g,60%氯化钾4.63g)、处理3:二者配施(50g堆肥+46%尿素2.36g,12%过磷酸钙10.13g,60%氯化钾2.32g)以及无肥对照(CK),在芥菜的收获期测定产量,可溶性糖和可溶性蛋白质以及VC含量。结果见表2。Compost fertilizer effect test ①: Use mustard as the test material to conduct a pot test. There were 4 treatments in the test, with 12 kg of soil in each pot. The 3 treatments of fertilization were fertilized under equal nutrient conditions. Treatment 1: single application of straw compost (100g compost/pot, nutrient content of N 21.72g/kg, P2O5 24.27/ kg, K2O 27.83g/kg), treatment 2: single application of chemical fertilizers (4.72g of 46% urea, 20.25g of 12% superphosphate, 4.63g of 60% potassium chloride), treatment 3: combined application of both (50g compost + 46% urea 2.36g, 12% superphosphate 10.13g, 60% potassium chloride 2.32g) and no fertilizer control (CK), the yield, soluble sugar and soluble protein and VC content were measured during the harvest period of mustard. The results are shown in Table 2.

堆肥肥效试验②:采用玉米作试验材料进行田间试验。试验共设4个处理,处理1为无肥对照(ck),处理2为单施化肥处理,处理3为市面有机肥+化肥处理,处理4为堆肥+化肥处理。其中处理2、处理3和处理4所用化肥量相等,处理3所用市面有机肥和处理4所用堆肥重量相等。在生菜收获期测定产量,可溶性糖和可溶固形物以及VC含量。结果见表3。Compost fertilizer efficiency test ②: use corn as the test material to conduct a field test. There are 4 treatments in the experiment, treatment 1 is no fertilizer control (ck), treatment 2 is single chemical fertilizer treatment, treatment 3 is market organic fertilizer + chemical fertilizer treatment, and treatment 4 is compost + chemical fertilizer treatment. Among them, the amount of chemical fertilizer used in treatment 2, treatment 3 and treatment 4 was equal, and the weight of compost used in treatment 3 and treatment 4 was equal. Yield, soluble sugar and soluble solids, and VC content were measured at the lettuce harvest stage. The results are shown in Table 3.

表1Table 1

Figure BDA0000044919390000031
Figure BDA0000044919390000031

结果表明:使用本发明的堆肥后熟促进剂能够使堆肥后熟期纤维素酶活性提高20.53个单位,纤维素降解率提高9.86个百分点,失重率提高8.41个百分点,堆肥浸出液发芽势提高7.49个百分点。The result shows: use post-ripening accelerator of compost of the present invention can make the cellulase activity of post-ripening stage of composting improve 20.53 units, the cellulose degradation rate improves 9.86 percentage points, the weight loss rate improves 8.41 percentage points, and the germination potential of compost leaching liquid improves 7.49 units percentage point.

表2Table 2

Figure BDA0000044919390000032
Figure BDA0000044919390000032

Figure BDA0000044919390000041
Figure BDA0000044919390000041

表3table 3

实施例2:Example 2:

采用猪粪、花生麸和玉米秸秆为堆肥材料,室外条垛堆肥。具体步骤和工艺条件如下:Use pig manure, peanut bran and corn stalks as compost materials, and compost in strips outdoors. Concrete steps and process conditions are as follows:

(1)将玉米秸秆风干粉碎至5厘米以下备用。将含水量为76%的猪粪350kg和含水量11%的风干粉碎玉米秸秆130kg以及含水量8%的花生麸30kg充分混合,此时堆肥物料含水量为56.5%;将堆肥物料堆成80厘米左右高度,塑料膜覆盖,5天翻堆1次。(1) Air-dry and crush the corn stalks to less than 5 cm for later use. Fully mix 350kg of pig manure with a moisture content of 76%, 130kg of air-dried crushed corn stalks with a moisture content of 11%, and 30kg of peanut bran with a moisture content of 8%. At this time, the moisture content of the compost material is 56.5%. Left and right heights, covered with plastic film, turned once every 5 days.

(2)待堆体温度下降至45℃以下时,将堆肥分成两等份。其中一份按照10kg/立方堆料用量加入乌洛托品,翻堆混匀,作用4天;之后按照20kg/立方添加堆肥后熟促进剂(按造纸污泥40份,纤维素酶10份,甜菜碱10份,精氨酸10 份配制),5kg/立方添加表面活性剂,充分混匀后塑料膜覆盖。另一份加入等量的含水量50%的泥土作为对照,混匀用塑料膜覆盖。(2) When the temperature of the heap body drops below 45°C, divide the compost into two equal parts. One of them adds urotropine according to the amount of 10kg/cubic stockpile, turns over and mixes, and acts for 4 days; then adds compost post-ripening accelerator according to 20kg/cubic (by 40 parts of papermaking sludge, 10 parts of cellulase, 10 parts of betaine, 10 parts of arginine (preparation), 5kg/cubic addition of surfactant, fully mixed and covered with plastic film. The same amount of soil with a water content of 50% was added to another part as a control, mixed evenly and covered with a plastic film.

(3)堆肥后熟条件控制一致,经过15天,物料腐熟。结果见表4。(3) The post-ripening conditions of composting are controlled uniformly, and the materials are decomposed after 15 days. The results are shown in Table 4.

(4)堆肥肥效试验①:采用生菜作试验材料进行盆栽试验。试验共设4个处理,每盆装土12kg,施肥的3个处理在等养分条件下施肥。处理1:单施秸秆堆肥(100g堆肥/盆,养分含量为N 21.72g/kg,P2O5 24.27/kg,K2O 27.83g/kg)、处理2:单施化肥(46%尿素4.72g,12%过磷酸钙20.25g,60%氯化钾4.63g)和处理3:二者配施(50g堆肥+46%尿素2.36g,12%过磷酸钙10.13g,60%氯化钾2.32g)以及无肥对照(CK),在生菜的收获期测定产量,可溶性糖和可溶性蛋白质以及VC含量。结果见表5。(4) Compost fertilizer effect test ①: Use lettuce as the test material to conduct a pot test. There were 4 treatments in the test, each pot was filled with 12kg of soil, and 3 treatments were fertilized under equal nutrient conditions. Treatment 1: single application of straw compost (100g compost/pot, nutrient content of N 21.72g/kg, P2O5 24.27/kg, K2O 27.83g/kg), treatment 2: single application of chemical fertilizer (46% urea 4.72g, 12% over Calcium phosphate 20.25g, 60% potassium chloride 4.63g) and treatment 3: the combination of both (50g compost+46% urea 2.36g, 12% superphosphate 10.13g, 60% potassium chloride 2.32g) and no fertilizer For the control (CK), yield, soluble sugar and soluble protein, and VC content were measured at the harvest stage of lettuce. The results are shown in Table 5.

(5)堆肥肥效试验②:采用生菜作试验材料进行大田试验。试验共设4个处理,处理1为无肥对照(ck),处理2为单施化肥处理,处理3为市面有机肥+化肥处理,处理4为堆肥+化肥处理。其中处理2、处理3和处理4所用化肥量相等,处理3所用市面有机肥和处理4所用堆肥重量相等。在生菜收获期测定产量,可溶性糖和可溶性蛋白质以及VC含量。结果见表6。(5) Compost fertilizer effect test ②: Lettuce was used as the test material for field test. There are 4 treatments in the experiment, treatment 1 is no fertilizer control (ck), treatment 2 is single chemical fertilizer treatment, treatment 3 is market organic fertilizer + chemical fertilizer treatment, and treatment 4 is compost + chemical fertilizer treatment. Among them, the amount of chemical fertilizer used in treatment 2, treatment 3 and treatment 4 was equal, and the weight of compost used in treatment 3 and treatment 4 was equal. Yield, soluble sugar and soluble protein, and VC content were determined at the lettuce harvest stage. The results are shown in Table 6.

表4Table 4

结果表明:使用本发明的堆肥后熟促进剂能够使堆肥后熟期纤维素酶活性提高12.8个单位,纤维素降解率提高10.27个百分点,失重率提高7.19个百分点,堆肥浸出液发芽势提高6.55个百分点。The result shows: use post-ripening accelerator of compost of the present invention can make cellulase activity improve 12.8 units in compost post-ripening stage, cellulose degradation rate improves 10.27 percentage points, weight loss rate improves 7.19 percentage points, compost leaching solution germination potential improves 6.55 units percentage point.

表5table 5

Figure BDA0000044919390000061
Figure BDA0000044919390000061

表6Table 6

Figure BDA0000044919390000062
Figure BDA0000044919390000062

上述的实施例中,用纤维素降解率(%)来表示采用各实施例后降低堆肥物料中所含纤维素的效果,用纤维素酶活性(微摩尔葡萄糖/分钟克鲜重)来表示纤维素转化的能力,纤维素降解率和纤维素酶活性越高,则表明分解纤维素的功能越强,并采用增产率(%)、可溶糖含量(%鲜重)、可溶性蛋白(mg/g)和维生素C含量(mg/100g)表示施用实施例中涉及的堆肥产物对于产量和品质的效应。In the above-mentioned examples, the cellulose degradation rate (%) is used to represent the effect of reducing the cellulose contained in the compost material after adopting each embodiment, and the cellulase activity (micromole glucose/min gram fresh weight) is used to represent the fiber The higher the cellulose degradation rate and cellulase activity, the stronger the function of decomposing cellulose, and the yield (%), soluble sugar content (% fresh weight), soluble protein (mg/ g) and vitamin C content (mg/100g) represent the effect of applying the compost products involved in the examples on yield and quality.

以上所述的实施例,只是本发明较优选的具体实施方式的一种,本领域的技术人员在本发明技术方案范围内进行的通常变化和替换都应包含在本发明的保护范围内。The embodiments described above are only one of the more preferred specific implementations of the present invention, and the usual changes and replacements performed by those skilled in the art within the scope of the technical solutions of the present invention should be included in the protection scope of the present invention.

Claims (6)

1. a straw compost after-ripening promotor is characterized in that its component is made of following composition: paper mill sludge 10-50kg, cellulase 0~10kg; Trimethyl-glycine 5~10kg; Arginine 0~10kg.
2. a kind of straw compost after-ripening promotor according to claim 1 is characterized in that its component is made of following composition: paper mill sludge 10-20kg; Cellulase 2~6kg; Trimethyl-glycine 6~8kg; Arginase 12~5kg.
3. the using method of a straw compost after-ripening promotor is characterized in that, its method steps comprises:
A, add urotropine 5-20kg in every cube of compost, the turning mixing is placed and is made its compost temperature be lower than 45 ℃;
B, adding paper mill sludge 10-50kg, cellulase 0~10kg; Trimethyl-glycine 5~10kg; Arginine 0~10kg; Tensio-active agent 5-10kg is placed to material and becomes thoroughly decomposed.
4. according to the using method of claim 3 or 4 described a kind of straw compost after-ripening promotor, it is characterized in that wherein step B adopts the method that turning mixing or layering are added.
5. according to the using method of claim 3 or 4 described a kind of straw compost after-ripening promotor, it is characterized in that wherein the paper mill sludge that adds among the step B is 10-20kg, cellulase is 2~6kg, and trimethyl-glycine is 6~8kg, and arginine is 2~5kg.
6. according to the using method of claim 3 or 4 described a kind of straw compost after-ripening promotor, it is characterized in that wherein tensio-active agent is one or both in Yelkin TTS, Natvosol, cyclodextrin, the Lalgine.
CN2011100248408A 2011-01-24 2011-01-24 A kind of straw compost post-ripening accelerator and its application method Expired - Fee Related CN102180715B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2011100248408A CN102180715B (en) 2011-01-24 2011-01-24 A kind of straw compost post-ripening accelerator and its application method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2011100248408A CN102180715B (en) 2011-01-24 2011-01-24 A kind of straw compost post-ripening accelerator and its application method

Publications (2)

Publication Number Publication Date
CN102180715A true CN102180715A (en) 2011-09-14
CN102180715B CN102180715B (en) 2013-05-15

Family

ID=44567032

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2011100248408A Expired - Fee Related CN102180715B (en) 2011-01-24 2011-01-24 A kind of straw compost post-ripening accelerator and its application method

Country Status (1)

Country Link
CN (1) CN102180715B (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104478505A (en) * 2014-12-23 2015-04-01 常熟市添源环保科技有限公司 Method for producing organic fertilizer through combination of pond sludge, algae and straw
CN105837270A (en) * 2016-03-29 2016-08-10 四川大学 Method for preparing organic fertilizer from crop straws

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6241795B1 (en) * 1999-04-16 2001-06-05 Miller Chemical And Fertilizer Corporation Soluble fertilizer formulation
CN1471409A (en) * 2000-08-22 2004-01-28 ��ɫũҵ��Դ��˾ Concept for slurry separation and biogas production
US20050197252A1 (en) * 2004-03-04 2005-09-08 Yamashita Thomas T. Methods for treating a plant exposed to a phytotoxicant
CN101892182A (en) * 2010-06-07 2010-11-24 中国农业大学 A strain of Bacillus licheniformis and its application in promoting cellulose degradation

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6241795B1 (en) * 1999-04-16 2001-06-05 Miller Chemical And Fertilizer Corporation Soluble fertilizer formulation
CN1471409A (en) * 2000-08-22 2004-01-28 ��ɫũҵ��Դ��˾ Concept for slurry separation and biogas production
US20050197252A1 (en) * 2004-03-04 2005-09-08 Yamashita Thomas T. Methods for treating a plant exposed to a phytotoxicant
CN101892182A (en) * 2010-06-07 2010-11-24 中国农业大学 A strain of Bacillus licheniformis and its application in promoting cellulose degradation

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104478505A (en) * 2014-12-23 2015-04-01 常熟市添源环保科技有限公司 Method for producing organic fertilizer through combination of pond sludge, algae and straw
CN105837270A (en) * 2016-03-29 2016-08-10 四川大学 Method for preparing organic fertilizer from crop straws

Also Published As

Publication number Publication date
CN102180715B (en) 2013-05-15

Similar Documents

Publication Publication Date Title
CN101439997B (en) Preparation of seaweed organic fertilizer
CN101306962B (en) Kitchen waste composting method using mushroom bran as conditioner
CN103113144B (en) Organic fertilizer for tobacco and preparation method thereof
CN102220137B (en) Soil modifier, and preparation method and use method thereof
CN103725631B (en) A straw decomposing agent
CN103288554B (en) Organic microbial fertilizer for lettuces and preparation method thereof
CN107759323A (en) A kind of Queensland nut composite fertilizer and preparation method thereof
CN104557199A (en) Method for producing amino-acid biological liquid fertilizer by utilizing fish wastes
CN106916021A (en) A kind of double source humic acid biological fertilizer and preparation method and application
CN104774114A (en) Production method for selenium-rich organic fertilizer
CN103274852A (en) Algae synergistic ammonium phosphate fertilizer and preparation method thereof
CN105254353A (en) Maize straw high-temperature decomposition agent and preparing method thereof
CN104255420A (en) Melon disease prevention and growth promotion seedling cultivation matrix and preparation method thereof
CN105152707A (en) Fermentation raw materials of vegetable seedling substrate and rapid cultivating technology of vegetable seedling substrate
CN106810407A (en) A kind of ecological organic fertilier and preparation method thereof
CN102942417A (en) Plant growth promoting rhinoacteria (PGPR) bio-organic fertilizers and production method thereof
CN108101685A (en) A kind of bio-organic fertilizer and preparation method thereof
CN105566002A (en) Preparation method of ferment mineral substance drought-resisting and water-retaining selenium-rich fertilizer
CN105801283A (en) Environment-friendly organic biomass fertilizer special for oil peonies
CN104276898A (en) Organic fertilizer and preparation method thereof
CN105948997A (en) Biomass organic fertilizer capable of increasing PH of acid soil
CN103145503B (en) Spruce culture medium prepared from cassava stalk
CN105777427A (en) Organic fertilizer doped with gasified slag and preparation method thereof
CN102180715B (en) A kind of straw compost post-ripening accelerator and its application method
CN108083950A (en) A kind of complex fertilizer and preparation method thereof

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
C56 Change in the name or address of the patentee
CP01 Change in the name or title of a patent holder

Address after: 510640 Guangdong city of Guangzhou province Tianhe District five road, SFI.

Patentee after: INSTITUTE OF AGRICULTURAL RESOURCES AND ENVIRONMENT, GUANGDONG ACADEMY OF AGRICULTURAL SCIENCES

Address before: 510640 Guangdong city of Guangzhou province Tianhe District five road, SFI.

Patentee before: Guangdong AAS Soil and Fertilizer Research Institute

CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20130515

CF01 Termination of patent right due to non-payment of annual fee