[go: up one dir, main page]

CN106116946B - Biological organic fertilizer for repairing soil heavy metal and preparation method thereof - Google Patents

Biological organic fertilizer for repairing soil heavy metal and preparation method thereof Download PDF

Info

Publication number
CN106116946B
CN106116946B CN201610458389.3A CN201610458389A CN106116946B CN 106116946 B CN106116946 B CN 106116946B CN 201610458389 A CN201610458389 A CN 201610458389A CN 106116946 B CN106116946 B CN 106116946B
Authority
CN
China
Prior art keywords
organic fertilizer
percent
soil
straw
biological 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.)
Active
Application number
CN201610458389.3A
Other languages
Chinese (zh)
Other versions
CN106116946A (en
Inventor
关统伟
李智强
王鹏昊
杨洋
邓奥宇
姚虞
赵顺先
李越
向慧平
范文斌
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.)
Chengdu Huahong Biotechnology Co ltd
Original Assignee
Chengdu Huahong Biotechnology Co ltd
Xihua 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 Chengdu Huahong Biotechnology Co ltd, Xihua University filed Critical Chengdu Huahong Biotechnology Co ltd
Priority to CN201610458389.3A priority Critical patent/CN106116946B/en
Publication of CN106116946A publication Critical patent/CN106116946A/en
Application granted granted Critical
Publication of CN106116946B publication Critical patent/CN106116946B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
    • C05G3/00Mixtures of one or more fertilisers with additives not having a specially fertilising activity
    • C05G3/80Soil conditioners
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05CNITROGENOUS FERTILISERS
    • C05C9/00Fertilisers containing urea or urea compounds
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F17/00Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
    • C05F17/50Treatments combining two or more different biological or biochemical treatments, e.g. anaerobic and aerobic treatment or vermicomposting and aerobic treatment
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
    • C05G3/00Mixtures of one or more fertilisers with additives not having a specially fertilising activity
    • 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

  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Organic Chemistry (AREA)
  • Molecular Biology (AREA)
  • Pest Control & Pesticides (AREA)
  • Health & Medical Sciences (AREA)
  • Soil Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Biochemistry (AREA)
  • Biotechnology (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Microbiology (AREA)
  • Fertilizers (AREA)

Abstract

The invention discloses a biological organic fertilizer for repairing soil heavy metal, which is prepared by preparing animal wastes, straws, kitchen waste and specially treated microorganism mixed flora into the biological organic fertilizer, and can reduce the content of soil high-valence heavy metal ions by more than 8 percent; the heavy metal enrichment of crops is reduced by more than 10 percent; particularly, the reduction of Cr reaches more than 70 percent; the yield of crops is increased by more than 5 percent, and the method has various effects of water retention, fertilizer retention, soil structure improvement and the like, and is a novel bioremediation method with low cost, high efficiency, simplicity, convenience and environmental friendliness.

Description

一种修复土壤重金属的生物有机肥料及其制备方法A kind of bio-organic fertilizer for repairing heavy metals in soil and preparation method thereof

技术领域technical field

本产品涉及农业肥料技术领域,特别是涉及一种修复土壤重金属的生物有机肥料。The product relates to the technical field of agricultural fertilizers, in particular to a bio-organic fertilizer for repairing heavy metals in soil.

背景技术Background technique

目前,由于人类对重金属的开采、冶炼、加工及商业制造活动日益增多,造成不少重金属如铅、汞、镉、钴等进入大气、水、土壤中,引起严重的环境污染,土壤的重金属污染更是个日益严重的环境问题,已经引起中央政府的高度关注,在《2016年中央对地方税收返还和支付预算表》中,用于土壤污染专性治理的预算经费高达90.89亿元。土壤重金属污染物主要来源于污水灌溉、工业废渣、城市垃圾、工业废弃物堆放及大气沉降。污水中占较大比例的工业废水的成分比较复杂,且都不同程度的含有生物难以降解的多种重金属,是土壤重金属污染物的主要来源。目前,全世界平均每年排放Hg约1.5万吨,Cu约340万吨,Pb约500万吨,Mn约1500万吨,Ni约100万吨。据我国农业部调查,在约140万公顷的污水灌区中,遭受重金属污染的土地面积占污水灌区面积的64.8%,其中轻度污染的占46.7%,中度污染的占9.7%,严重污染的占8.4%。At present, due to the increasing number of heavy metal mining, smelting, processing and commercial manufacturing activities by humans, many heavy metals such as lead, mercury, cadmium, cobalt, etc. enter the atmosphere, water, and soil, causing serious environmental pollution. Heavy metal pollution of soil It is an increasingly serious environmental problem, which has attracted the attention of the central government. In the "2016 Central Government's Budget for Tax Return and Payment to Local Governments", the budget for soil pollution control is as high as 9.089 billion yuan. Heavy metal pollutants in soil mainly come from sewage irrigation, industrial waste residue, municipal waste, industrial waste stacking and atmospheric deposition. The industrial wastewater, which accounts for a large proportion of the sewage, is relatively complex in composition, and contains various heavy metals that are difficult to biodegrade to varying degrees, and is the main source of heavy metal pollutants in soil. At present, the world's average annual emission of Hg is about 15,000 tons, Cu is about 3.4 million tons, Pb is about 5 million tons, Mn is about 15 million tons, and Ni is about 1 million tons. According to the survey of the Ministry of Agriculture of my country, in the sewage irrigation area of about 1.4 million hectares, the land area polluted by heavy metals accounts for 64.8% of the sewage irrigation area, of which 46.7% are lightly polluted, 9.7% are moderately polluted, and 9.7% are severely polluted. 8.4%.

国内外用来降解或消除土壤重金属污染的方法基本上可以分为物理法、化学修复技术、生物修复技术等3大类。物理/化学修复技术主要基于土壤理化性质和重金属的不同特性,通过物理化学手段来分离或固定土壤中的重金属达到清洁土壤和降低污染物环境风险和健康风险的技术手段。物理化学修复技术包括换土、客土、深耕翻土等法,土壤淋洗法,热解吸法、玻璃化技术、电动修复等。物理化学技术实施方便灵活,周期较短,适用于多种重金属的处理,在重金属污染土壤工程的修复中得到广泛应用,但该技术实施的工程量较大,成本较高,一定程度上限值其推广应用。因此,迫切需要发展一种低成本、高效、简便、环境友好的新型生物修复方法。At home and abroad, the methods used to degrade or eliminate heavy metal pollution in soil can be basically divided into three categories: physical methods, chemical remediation techniques, and bioremediation techniques. Physical/chemical remediation technology is mainly based on the physical and chemical properties of soil and the different characteristics of heavy metals, and uses physical and chemical means to separate or fix heavy metals in soil to clean soil and reduce environmental and health risks of pollutants. Physical and chemical restoration techniques include soil replacement, foreign soil, deep ploughing, soil leaching, thermal desorption, vitrification, and electric restoration. The physical and chemical technology is convenient and flexible to implement and has a short cycle. It is suitable for the treatment of various heavy metals and has been widely used in the remediation of heavy metal-contaminated soil engineering. its promotion and application. Therefore, there is an urgent need to develop a novel bioremediation method that is low-cost, efficient, simple, and environmentally friendly.

发明内容SUMMARY OF THE INVENTION

为解决上述技术问题,本发明提供一种高效、简便、环境友好的修复土壤重金属的生物有机肥料。In order to solve the above technical problems, the present invention provides an efficient, simple and environmentally friendly bio-organic fertilizer for repairing heavy metals in soil.

近些年来,由于农业机械化程度的提高,从而使农业机械取代了牲畜。从而使秸秆用作饲料的量大大减少。每年农作物成熟的时候,农民收割作物以后手中剩下的大量秸秆便只能焚烧处理。秸秆露天焚烧污染大气、浪费资源,严重到甚至已影响和干扰了经济的正常秩序,形成新的安全隐患。将秸秆处理制成生物有机肥,不仅避免了焚烧带来的环境污染和资源浪费,而且能够通过一系列生物化学反应将秸秆分解成较稳定的腐殖质,补充氮、磷、钾等作物必需的营养元素,从而改善土壤结构。同时餐厨垃圾也是导致城市污染的重要原因之一。为此,在本发明中还有效利用了餐厨垃圾丰富的营养,经发酵和生物转化为生物有机肥料,从而变废为宝,降低城市污染。In recent years, due to the increase in the degree of agricultural mechanization, agricultural machinery has replaced livestock. Thus, the amount of straw used as feed is greatly reduced. When the crops are mature every year, the large amount of straw left by farmers after harvesting the crops can only be burned. The open burning of straw pollutes the atmosphere, wastes resources, and even affects and interferes with the normal order of the economy, creating new security risks. The processing of straw into bio-organic fertilizer not only avoids environmental pollution and resource waste caused by incineration, but also decomposes the straw into relatively stable humus through a series of biochemical reactions, supplementing the nutrients necessary for crops such as nitrogen, phosphorus and potassium. elements, thereby improving soil structure. At the same time, kitchen waste is also one of the important causes of urban pollution. Therefore, in the present invention, the rich nutrition of kitchen waste is also effectively utilized, and it is fermented and biologically transformed into a biological organic fertilizer, thereby turning waste into treasure and reducing urban pollution.

根据文献报道,胶质芽孢杆菌(Bacillus mucilaginosus)对重金属铬是一种有效的微生物吸附剂(高玉振,2015);酿酒酵母(Saccharomyces cerevisiae)菌株不仅是具有实用潜力的生物吸附剂,也是研究重金属生物吸附机理的良好材料(陈灿,2006);黑曲霉(Aspergillus niger)能够很好的抗重金属并具有很好的富集重金属的能力(樊霆,2012)。According to literature reports, Bacillus mucilaginosus is an effective microbial adsorbent for heavy metal chromium (Gao Yuzhen, 2015). Good materials for biosorption mechanism (Chen Can, 2006); Aspergillus niger can resist heavy metals and has a good ability to enrich heavy metals (Fan Ting, 2012).

为此,本发明利用胶质芽孢杆菌、酿酒酵母和黑曲霉,结合畜禽粪、农田秸秆和餐厨垃圾,混合堆置制备能够脱重金属的生物有机肥,将有效降低土壤中重金属离子的毒性;同时,结合有机肥对土壤进行修复,改善土壤结构,促进植物对营养元素的吸收,达到健壮植株、增强坑逆性、提高作物产量、降低环境污染和保障人们生活健康的目的。To this end, the present invention utilizes Bacillus colloid, Saccharomyces cerevisiae and Aspergillus niger, combined with livestock and poultry manure, farmland straw and kitchen waste, and mixed stacking to prepare a bio-organic fertilizer capable of removing heavy metals, which will effectively reduce the toxicity of heavy metal ions in the soil. At the same time, combined with organic fertilizer to repair the soil, improve the soil structure, promote the absorption of nutrient elements by plants, and achieve the purpose of strengthening plants, enhancing pit stress, increasing crop yield, reducing environmental pollution and ensuring people's health.

一种修复土壤重金属的生物有机肥料,包括以下重量百分比的成分:A bio-organic fertilizer for repairing heavy metals in soil, comprising the following components by weight:

Figure BDA0001025772870000031
Figure BDA0001025772870000031

优选的,所述的秸秆-粪便肥料包括以下主要成分:Preferably, the straw-manure fertilizer includes the following main components:

Figure BDA0001025772870000032
Figure BDA0001025772870000032

优选的,所述的畜禽粪便为鸡粪和牛粪等量混合而成。Preferably, the livestock manure is prepared by mixing chicken manure and cow manure in equal amounts.

一种修复土壤重金属的生物有机肥料的制备方法,包括以下步骤:A preparation method of a bio-organic fertilizer for repairing heavy metals in soil, comprising the following steps:

(1)微生物菌剂的制备(1) Preparation of microbial inoculants

A、酿酒酵母菌剂的制备方法:取酿酒酵母菌种,加入30℃水中恒温搅拌直至完全溶解,所得到的液体加至液体培养基中,培养4-6d后检测菌体密度达到1.5-3.1×109cfu/mL,即得酿酒酵母菌剂;A. The preparation method of Saccharomyces cerevisiae agent: take Saccharomyces cerevisiae strain, add it into 30 ℃ water and stir at constant temperature until it is completely dissolved, the obtained liquid is added to the liquid medium, and after culturing for 4-6 days, the density of the bacteria is detected to reach 1.5-3.1 ×10 9 cfu/mL to obtain Saccharomyces cerevisiae;

B、胶质芽孢杆菌菌剂的制备方法:取胶质芽孢杆菌菌种,加入水中恒温搅拌至完全溶解;所得到的液体加至液体培养基中,150rpm,30-35℃下恒温震荡培养4-6d,使得菌体密度达到6.2-8.3×109cfu/mL即得胶质芽孢杆菌菌剂;B, the preparation method of the Bacillus colloid bacteria agent: get the Bacillus colloid bacteria strain, add it into the water and stir at a constant temperature until it is completely dissolved; the obtained liquid is added to the liquid medium, 150rpm, 30-35 ℃ under constant temperature shaking culture 4 -6d, so that the cell density reaches 6.2-8.3×10 9 cfu/mL to obtain Bacillus colloid bacteria agent;

C、黑曲霉菌剂的制备方法:取黑曲霉菌种,加入水中恒温搅拌直至完全溶解,把所得到的液体加入到无机盐溶液中,将无机盐溶液与配料混合,进行搅拌接种,25-30℃下恒温发酵4-6d后即得黑曲霉菌剂;C, the preparation method of Aspergillus niger: get Aspergillus niger species, add water at constant temperature and stir until completely dissolved, add the obtained liquid to the inorganic salt solution, mix the inorganic salt solution with the ingredients, stir and inoculate, 25- The Aspergillus niger agent is obtained after constant temperature fermentation at 30℃ for 4-6d;

(2)秸秆-粪便堆肥腐熟(2) The straw-manure compost is fully decomposed

取秸秆粉碎为直径小于2mm的碎末,加入餐厨垃圾混匀,再加入腐熟剂和畜禽粪便,保持水分在60%-70%,控制堆肥高度为1.5米,控制温度为25-35℃条件下堆积腐熟23-26d;之后堆积腐熟升温,使得温度达到60-70℃,维持2-3d,制得腐熟的秸秆-粪便堆肥;Take the straw and pulverize it into pieces with a diameter of less than 2mm, add kitchen waste and mix well, then add decomposing agent and livestock and poultry manure, keep the moisture at 60%-70%, control the compost height to 1.5 meters, and control the temperature to 25-35 ℃ Under the condition of 23-26d accumulation and decomposing; then the accumulation and decomposing heat up, so that the temperature reaches 60-70 ℃, and maintains for 2-3d, to obtain decomposed straw-feces compost;

(3)生物有机肥的制备(3) Preparation of bio-organic fertilizer

将上述制得的秸秆-粪便肥料进行摊晾,使其温度降至30-35℃后,均匀混入胶质芽孢杆菌菌剂,并添加尿素、硫酸镁、以及活性炭与硼砂,充分混合发酵2-3d;发酵完成后加入酿酒酵母菌剂和黑曲霉菌剂混合均匀后控制温度25℃再次发酵2-3d;将发酵后的混合物进行干燥、计量装袋,即得生物有机肥料。The straw-fecal fertilizer prepared above is spread out, and after its temperature is lowered to 30-35 ° C, the Bacillus colloid bacteria is evenly mixed, and urea, magnesium sulfate, and activated carbon and borax are added, and fully mixed and fermented for 2- 3d; after the fermentation is completed, add Saccharomyces cerevisiae agent and Aspergillus niger agent to mix evenly, control the temperature to 25°C and ferment again for 2-3d; dry the fermented mixture, measure and bag it to obtain bio-organic fertilizer.

优选的,所述的酿酒酵母菌剂液体培养基的组成为:20g蛋白胨、10g酵母抽提物、2g葡萄糖,适量双蒸水溶解,再加入15ml 0.2%腺嘌呤溶液,定容到1L;120℃高压灭菌15min。Preferably, the liquid culture medium for Saccharomyces cerevisiae is composed of: 20g peptone, 10g yeast extract, 2g glucose, dissolved in an appropriate amount of double-distilled water, and then add 15ml of 0.2% adenine solution, and set the volume to 1L; 120 Autoclave at ℃ for 15 min.

优选的,所述的胶质芽孢杆菌菌剂的液体培养基的组成为:蔗糖10g、酵母浸膏0.3g、硫酸铵0.5g、碳酸钙0.5g、七水硫酸镁0.5g、磷酸氢二钾1g,调整pH值7.0-7.5并定容到1L。Preferably, the composition of the liquid culture medium of the Bacillus colloid bacteria agent is: 10 g of sucrose, 0.3 g of yeast extract, 0.5 g of ammonium sulfate, 0.5 g of calcium carbonate, 0.5 g of magnesium sulfate heptahydrate, and dipotassium hydrogen phosphate 1g, adjust the pH to 7.0-7.5 and make up to 1L.

优选的,所述的无机盐溶液的成分为:NaCl 1份,CaCl2 0.5份,KCl 0.5份,K2HPO40.5份,NaHCO3 0.25份,MgSO4 1份,FeSO4·7H2O0.025份,蒸馏水2000份;所述的配料混合为:麸皮2000份,豆饼粉2000份,花生秸秆粉1000份。Preferably, the components of the inorganic salt solution are: 1 part of NaCl, 0.5 part of CaCl 2 , 0.5 part of KCl, 0.5 part of K 2 HPO 4 , 0.25 part of NaHCO 3 , 1 part of MgSO 4 , FeSO 4 7H 2 O0. 025 parts, 2,000 parts of distilled water; the ingredients are mixed as follows: 2,000 parts of bran, 2,000 parts of bean cake flour, and 1,000 parts of peanut straw powder.

与现有技术相比本发明的有益效果为:本发明制备的生物有机肥料有机质≥60%,有效活菌数≥0.5亿/g,粪大肠菌群数≤30个/g。与普通化肥相比(100kg/亩),可降低土壤高价重金属离子含量8%以上;减少作物对重金属富集10%以上;特别是对于Cr的还原达到70%以上;使作物增产5%以上,并且具有保水、保肥和改良土壤结构等多种功效。Compared with the prior art, the present invention has the following beneficial effects: the organic matter of the bio-organic fertilizer prepared by the present invention is greater than or equal to 60%, the number of effective viable bacteria is greater than or equal to 050 million/g, and the number of fecal coliforms is less than or equal to 30/g. Compared with ordinary chemical fertilizers (100kg/mu), it can reduce the content of high-value heavy metal ions in soil by more than 8%; reduce the accumulation of heavy metals in crops by more than 10%; especially for the reduction of Cr to more than 70%; increase crop yield by more than 5%, And it has many functions such as water retention, fertilizer retention and soil structure improvement.

具体实施方式Detailed ways

下面结合实施例,对本发明的具体实施方式作进一步详细描述。以下实施例用于说明本发明,但不用来限制本发明的范围。The specific embodiments of the present invention will be further described in detail below with reference to the examples. The following examples are intended to illustrate the present invention, but not to limit the scope of the present invention.

一种修复土壤重金属的生物有机肥料的制备方法,包括以下步骤:A preparation method of a bio-organic fertilizer for repairing heavy metals in soil, comprising the following steps:

(1)微生物菌剂制备(1) Preparation of microbial inoculum

酿酒酵母菌剂的制备方法:取酿酒酵母菌种20份,加入30℃五倍质量的水恒温搅拌0.5h直至完全溶解,所得到的液体加至1L体积的液体培养基中,培养5d后检测菌体密度达到2.2×109cfu/mL。The preparation method of Saccharomyces cerevisiae inoculum: take 20 strains of Saccharomyces cerevisiae, add 5 times the mass of water at 30°C and stir at constant temperature for 0.5h until completely dissolved, the obtained liquid is added to a liquid medium of 1L volume, and tested after culturing for 5 days The cell density reached 2.2×10 9 cfu/mL.

液体培养基的组成部分为:20g蛋白胨、10g酵母抽提物、2g葡萄糖,适量双蒸水溶解,再加入15ml 0.2%腺嘌呤溶液,定容到1L;120℃高压灭菌15min。The components of the liquid medium are: 20g peptone, 10g yeast extract, 2g glucose, dissolved in an appropriate amount of double-distilled water, and then add 15ml of 0.2% adenine solution to make the volume to 1L; autoclave at 120°C for 15min.

胶质芽孢杆菌菌剂的制备方法:取胶质芽孢杆菌菌种20份,加入35℃五倍质量的水恒温搅拌0.5h直至完全溶解;所得到的液体加至1L体积的液体培养基中,150rpm,32℃下恒温震荡培养6d,使得菌体密度达到7.8×109cfu/mL。The preparation method of Bacillus colloids inoculum: take 20 copies of Bacillus colloids strains, add five times the mass of water at 35°C and stir at constant temperature for 0.5h until completely dissolved; the obtained liquid is added to a 1L volume of liquid medium, 150rpm, constant temperature shaking culture at 32°C for 6 days, so that the cell density reaches 7.8×10 9 cfu/mL.

液体培养基的组成为:蔗糖10g、酵母浸膏0.3g、硫酸铵0.5g、碳酸钙0.5g、七水硫酸镁0.5g、磷酸氢二钾1g,调整pH值7.0-7.5并定容到1L。The composition of the liquid medium is: 10g of sucrose, 0.3g of yeast extract, 0.5g of ammonium sulfate, 0.5g of calcium carbonate, 0.5g of magnesium sulfate heptahydrate, 1g of dipotassium hydrogen phosphate, adjust the pH value to 7.0-7.5 and set the volume to 1L .

黑曲霉菌剂的制备方法:取黑曲霉菌种20份,加入30℃五倍质量的水恒温搅拌0.5h直至完全溶解,把所得到的液体加入到无机盐溶液中,将无机盐溶液(NaCl 1g,CaCl20.5g,KCl 0.5g,K2HPO4 0.5g,NaHCO3 0.25g,MgSO4 1g,FeSO4·7H2O 25mg,蒸馏水2L)与5kg配料混合(麸皮:豆饼粉:花生秸秆粉=2:2:1)进行搅拌接种。28℃下恒温发酵5d后即得黑曲霉菌剂。The preparation method of the Aspergillus niger agent: take 20 parts of Aspergillus niger species, add five times the mass of water at 30°C and stir at constant temperature for 0.5h until completely dissolved, add the obtained liquid to the inorganic salt solution, mix the inorganic salt solution (NaCl 1g, CaCl 2 0.5g, KCl 0.5g, K 2 HPO 4 0.5g, NaHCO 3 0.25g, MgSO 4 1g, FeSO 4 7H 2 O 25mg, distilled water 2L) mixed with 5kg of ingredients (bran: bean cake flour: peanut Straw powder = 2:2:1) for stirring and inoculation. The Aspergillus niger agent was obtained after 5 days of constant temperature fermentation at 28°C.

(2)秸秆-粪便堆肥腐熟(2) The straw-manure compost is fully decomposed

取秸秆粉碎为直径小于2mm的碎末,加入餐厨垃圾混匀,再加入腐熟剂和畜禽粪便,保持水分在60%-70%,控制堆肥高度为1.5米,控制温度为30℃条件下堆积腐熟25d;之后堆积腐熟升温,使得温度达到60-70℃,维持2d,制得腐熟的秸秆-粪便堆肥;Take the straw and smash it into pieces with a diameter of less than 2mm, add kitchen waste and mix well, then add decomposing agent and livestock and poultry manure, keep the moisture at 60%-70%, control the compost height to 1.5 meters, and control the temperature to 30 ℃. The piles are decomposed for 25 days; then the piles are decomposed and heated up, so that the temperature reaches 60-70 °C and maintained for 2 days to obtain decomposed straw-feces compost;

(3)生物有机肥的制备(3) Preparation of bio-organic fertilizer

将上述制得的秸秆-粪便肥料进行摊晾,使其温度降至30℃后,均匀混入胶质芽孢杆菌菌剂,并添加尿素、硫酸镁、以及0.5%的活性炭与0.1%的硼砂,充分混合发酵2d;发酵完成后加入1%的酿酒酵母菌剂和1%的黑曲霉菌剂混合均匀后控制温度25℃再次发酵3d;将发酵后的混合物进行干燥、计量装袋,即得生物有机肥料。The straw-fecal fertilizer prepared above was spread out to make the temperature drop to 30°C, and then evenly mixed with Bacillus colloid bacteria agent, and urea, magnesium sulfate, 0.5% activated carbon and 0.1% borax were added to fully Mix and ferment for 2 days; add 1% of Saccharomyces cerevisiae agent and 1% of Aspergillus niger after the fermentation is completed and mix evenly, control the temperature to 25°C and ferment again for 3 days; dry the fermented mixture, measure and bag it to obtain bio-organic fertilizer.

所述的修复土壤重金属的生物有机肥料,包括以下重量百分比的成分:The bio-organic fertilizer for repairing heavy metals in soil includes the following components by weight:

Figure BDA0001025772870000061
Figure BDA0001025772870000061

所述的秸秆-粪便肥料包括以下主要成分:The straw-manure fertilizer includes the following main components:

Figure BDA0001025772870000062
Figure BDA0001025772870000062

所述的畜禽粪便为鸡粪和牛粪等量混合而成。The livestock and poultry manure is prepared by mixing chicken manure and cow manure in equal amounts.

所述的50%秸秆包括20%玉米秸秆,20%水稻秸秆,10%小麦秸秆。The 50% straw includes 20% corn straw, 20% rice straw and 10% wheat straw.

各实施例中生物有机肥料的各重量百分比的成分请见下表:The composition of each weight percentage of the bio-organic fertilizer in each embodiment is shown in the following table:

Figure BDA0001025772870000063
Figure BDA0001025772870000063

Figure BDA0001025772870000071
Figure BDA0001025772870000071

各实施例中秸秆-粪便肥料的各重量百分比的成分请见下表:The composition of each weight percentage of straw-fecal fertilizer in each embodiment is shown in the following table:

实施例1Example 1 实施例2Example 2 实施例3Example 3 实施例4Example 4 实施例5Example 5 实施例6Example 6 实施例7Example 7 秸秆straw 5050 4040 4545 5555 6060 6565 4545 腐熟剂decomposer 11 0.80.8 0.90.9 1.51.5 1.21.2 1.51.5 11 餐厨垃圾kitchen waste 55 33 55 88 77 66 55 畜禽粪便livestock manure 余量margin 余量margin 余量margin 余量margin 余量margin 余量margin 余量margin

对本发明制备的生物有机肥料进行测试得到如下数据:The bio-organic fertilizer prepared by the present invention is tested to obtain the following data:

Figure BDA0001025772870000072
Figure BDA0001025772870000072

将本发明的肥料应用于水稻种植,测试一年后重金属处理效果并与普通的复合肥(N:P2O5:K2O=2:1:3)进行对比,得到如下数据:The fertilizer of the present invention is applied to rice planting, and the heavy metal treatment effect after one year is tested and compared with ordinary compound fertilizer (N:P 2 O 5 :K 2 O=2:1:3), and the following data are obtained:

施肥量:100kg/亩,可降低土壤高价重金属离子含量8.5-10%;减少作物对重金属富集12-15%;对于Cr的还原达到75-80%;使作物增产6-8%。Fertilization rate: 100kg/mu, which can reduce the content of high-value heavy metal ions in soil by 8.5-10%; reduce the accumulation of heavy metals in crops by 12-15%; reduce Cr to 75-80%; increase crop yield by 6-8%.

以下为对比实施例,对本发明中的肥料中的菌群进行具体分析。The following is a comparative example, which specifically analyzes the flora in the fertilizer of the present invention.

对比实施例1Comparative Example 1

将实施例1中的胶质芽孢杆菌菌剂去除,测试一年后重金属处理效果并与普通的复合肥(N:P2O5:K2O=2:1:3)进行对比,得到如下数据:The Bacillus colloid bacteria in Example 1 was removed, and the effect of heavy metal treatment after one year was tested and compared with ordinary compound fertilizers (N:P 2 O 5 :K 2 O=2:1:3), and the following results were obtained. data:

施肥量:100kg/亩,可降低土壤高价重金属离子含量2-3%;减少作物对重金属富集3-5%;对于Cr的还原达到25-30%;使作物增产4-5%。Fertilization rate: 100kg/mu, which can reduce the content of high-value heavy metal ions in the soil by 2-3%; reduce the accumulation of heavy metals in crops by 3-5%; reduce Cr by 25-30%; increase crop yield by 4-5%.

对比实施例2Comparative Example 2

将实施例1中的酿酒酵母菌剂去除,测试一年后重金属处理效果并与普通的复合肥(N:P2O5:K2O=2:1:3)进行对比,得到如下数据:Saccharomyces cerevisiae in Example 1 was removed, and the heavy metal treatment effect after one year was tested and compared with the common compound fertilizer (N:P 2 O 5 :K 2 O=2:1:3) to obtain the following data:

施肥量:100kg/亩,可降低土壤高价重金属离子含量2-3%;减少作物对重金属富集2-3%;对于Cr的还原达到55-60%;使作物增产5-6%。Fertilization rate: 100kg/mu, which can reduce the content of high-value heavy metal ions in the soil by 2-3%; reduce the accumulation of heavy metals in crops by 2-3%; reduce Cr to 55-60%; increase crop yield by 5-6%.

对比实施例3Comparative Example 3

将实施例1中的黑曲霉菌剂去除,测试一年后重金属处理效果并与普通的复合肥(N:P2O5:K2O=2:1:3)进行对比,得到如下数据:The Aspergillus niger agent in Example 1 was removed, and the heavy metal treatment effect after one year was tested and compared with the common compound fertilizer (N:P 2 O 5 :K 2 O=2:1:3) to obtain the following data:

施肥量:100kg/亩,可降低土壤高价重金属离子含量3-4%;减少作物对重金属富集6-8%;对于Cr的还原达到45-50%;使作物增产3-5%。Fertilization rate: 100kg/mu, which can reduce the content of high-value heavy metal ions in soil by 3-4%; reduce the accumulation of heavy metals in crops by 6-8%; reduce Cr to 45-50%; increase crop yield by 3-5%.

对比实施例4Comparative Example 4

将实施例1中的黑曲霉菌剂和酿酒酵母菌剂去除,测试一年后重金属处理效果并与普通的复合肥(N:P2O5:K2O=2:1:3)进行对比,得到如下数据:The Aspergillus niger and Saccharomyces cerevisiae in Example 1 were removed, and the effect of heavy metal treatment after one year was tested and compared with ordinary compound fertilizer (N:P 2 O 5 :K 2 O=2:1:3) , get the following data:

施肥量:100kg/亩,可降低土壤高价重金属离子含量1-2%;减少作物对重金属富集2-3%;对于Cr的还原达到20-30%;使作物增产3-5%。Fertilization rate: 100kg/mu, which can reduce the content of high-value heavy metal ions in soil by 1-2%; reduce the accumulation of heavy metals by crops by 2-3%; reduce Cr by 20-30%; increase crop yield by 3-5%.

由对比实施例1-4的测试数据可以知道,将三种微生物共同使用比单独使用一种微生物或两种微生物共同使用的土壤重金属修复效果好很多。From the test data of Comparative Examples 1-4, it can be known that the combined use of three microorganisms is much better than the soil heavy metal remediation effect of using one microorganism or two microorganisms together.

以上所述仅是本发明的优选实施方式,应当指出,对于本技术领域的普通技术人员来说,在不脱离本发明技术原理的前提下,还可以做出若干改进和变型,这些改进和变型也应视为本发明的保护范围。The above are only the preferred embodiments of the present invention. It should be pointed out that for those skilled in the art, without departing from the technical principles of the present invention, several improvements and modifications can also be made. These improvements and modifications It should also be regarded as the protection scope of the present invention.

Claims (4)

1. The biological organic fertilizer for repairing soil heavy metals is characterized by comprising the following components in percentage by weight:
1-3% of Bacillus mucilaginosus fungicide
0.2 to 0.7 percent of urea
Magnesium sulfate 0.05-0.2%
0.3 to 0.8 percent of active carbon
0.08 to 0.15 percent of borax
Saccharomyces cerevisiae 0.5-1.5%
0.7 to 2 percent of Aspergillus niger microbial inoculum
The balance of straw-manure fertilizer;
the straw-excrement fertilizer comprises the following main components:
40 to 65 percent of straw
0.8 to 1.5 percent of decomposition agent
3 to 8 percent of kitchen waste
The rest of the livestock and poultry manure;
the preparation method of the biological organic fertilizer for repairing the heavy metals in the soil comprises the following steps:
(1) preparation of microbial agent
A. The preparation method of the saccharomyces cerevisiae agent comprises the following steps: adding Saccharomyces cerevisiae strain into 30 deg.C water, stirring at constant temperature until completely dissolved, adding the obtained liquid into liquid culture medium, culturing for 4-6d, and detecting thallus density to 1.5-3.1 × 109cfu/mL to obtain a saccharomyces cerevisiae agent;
B. the preparation method of the bacillus mucilaginosus agent comprises the following steps: taking bacillus mucilaginosus strain, adding into water, and stirring at constant temperature until the bacillus mucilaginosus strain is completely dissolved; adding the obtained liquid into liquid culture medium, shake culturing at 150rpm and 30-35 deg.C for 4-6 days to make thallus density reach 6.2-8.3 × 109cfu/mL to obtain the bacillus mucilaginosus agent;
C. the preparation method of the aspergillus niger agent comprises the following steps: adding 20 parts of aspergillus niger strains into water with the mass of 5 times of the aspergillus niger strains, stirring at constant temperature until the aspergillus niger strains are completely dissolved, adding the obtained liquid into an inorganic salt solution, mixing the inorganic salt solution with ingredients, stirring and inoculating, and fermenting at constant temperature of 25-30 ℃ for 4-6 days to obtain an aspergillus niger agent; the inorganic salt solution comprises the following components: 1 part of NaCl, CaCl20.5 part, KCl 0.5 part, K2HPO40.5 part of NaHCO30.25 part of MgSO 241 part of FeSO4·7H20.025 parts of O and 2000 parts of distilled water; the mixture of the ingredients is as follows: 2000 parts of bran, 2000 parts of bean cake powder and 1000 parts of peanut straw powder;
(2) straw-excrement compost becomes thoroughly decomposed
Crushing straws into powder with the diameter less than 2mm, adding kitchen waste, uniformly mixing, adding a decomposition agent and livestock and poultry manure, keeping the water content at 60-70%, controlling the compost height to be 1.5 m, and stacking for decomposition for 23-26d at the temperature of 25-35 ℃; then stacking, decomposing and heating to make the temperature reach 60-70 ℃, and maintaining for 2-3d to prepare decomposed straw-excrement compost;
(3) preparation of biological organic fertilizer
Spreading and drying the prepared straw-excrement fertilizer, cooling the temperature to 30-35 ℃, uniformly mixing with a bacillus mucilaginosus microbial inoculum, adding urea, magnesium sulfate, active carbon and borax, and fully mixing and fermenting for 2-3 d; after fermentation, adding a saccharomyces cerevisiae microbial inoculum and an aspergillus niger microbial inoculum, uniformly mixing, and controlling the temperature to be 25 ℃ for secondary fermentation for 2-3 d; and drying, metering and bagging the fermented mixture to obtain the biological organic fertilizer.
2. The biological organic fertilizer for remediating heavy metals in soil as claimed in claim 1, wherein the livestock manure is a mixture of chicken manure and cow manure in equal amount.
3. The biological organic fertilizer for remediating soil heavy metals as claimed in claim 1, wherein the saccharomyces cerevisiae liquid culture medium comprises the following components: 20g of peptone, 10g of yeast extract, 2g of glucose and a proper amount of double distilled water are dissolved, 15ml of 0.2% adenine solution is added, and the volume is fixed to 1L; autoclaving at 120 deg.C for 15 min.
4. The biological organic fertilizer for remediating heavy metals in soil as claimed in claim 1, wherein the liquid culture medium of the bacillus mucilaginosus microbial inoculum comprises the following components: 10g of sucrose, 0.3g of yeast extract, 0.5g of ammonium sulfate, 0.5g of calcium carbonate, 0.5g of magnesium sulfate heptahydrate and 1g of dipotassium phosphate, adjusting the pH value to 7.0-7.5 and fixing the volume to 1L.
CN201610458389.3A 2016-06-22 2016-06-22 Biological organic fertilizer for repairing soil heavy metal and preparation method thereof Active CN106116946B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610458389.3A CN106116946B (en) 2016-06-22 2016-06-22 Biological organic fertilizer for repairing soil heavy metal and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610458389.3A CN106116946B (en) 2016-06-22 2016-06-22 Biological organic fertilizer for repairing soil heavy metal and preparation method thereof

Publications (2)

Publication Number Publication Date
CN106116946A CN106116946A (en) 2016-11-16
CN106116946B true CN106116946B (en) 2020-10-27

Family

ID=57267957

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610458389.3A Active CN106116946B (en) 2016-06-22 2016-06-22 Biological organic fertilizer for repairing soil heavy metal and preparation method thereof

Country Status (1)

Country Link
CN (1) CN106116946B (en)

Families Citing this family (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106591378A (en) * 2016-12-26 2017-04-26 北京大学深圳研究生院 Method for carrying out anaerobic digestion by using heavy metal ions-rich biomass waste materials
CN107056492A (en) * 2017-05-31 2017-08-18 安徽永志环能科技有限公司 Suitable for the leavening agent for poultry excrement and its application method of cold district
CN107827645A (en) * 2017-11-15 2018-03-23 李永锋 A kind of bio-feritlizer of reduction Cd pollutions
CN107739280A (en) * 2017-11-15 2018-02-27 李永锋 A kind of bio-feritlizer of reduction Cr pollutions
CN107827382A (en) * 2017-11-16 2018-03-23 广东弘朝科技有限公司 A kind of hexavalent chrome reduction agent and preparation method thereof
CN108076948A (en) * 2017-12-20 2018-05-29 中国计量大学 A kind of method that sodium acid carbonate is applied in the soil of highly acid tea place and reduces plumbi content of tea
CN108043873A (en) * 2017-12-25 2018-05-18 谢涛 A kind of heavy metal-polluted soil biological fixation agent and its application process
CN109912345A (en) * 2019-04-02 2019-06-21 北京国达恒泰科贸有限责任公司 Solid organic castoff is the function organic compound fertilizer and preparation method of substrate and application
CN109988020A (en) * 2019-04-15 2019-07-09 深圳绿欣农业环保科技有限公司 Aquaculture and planting industry cyclic utilization of waste method
CN110937952A (en) * 2019-10-28 2020-03-31 安徽省通源环境节能股份有限公司 Preparation method of ecological restoration matrix for heavy metal contaminated soil
CN113511926A (en) * 2021-04-28 2021-10-19 新至农业生态科技有限公司 Method for comprehensively utilizing livestock and poultry manure resources and returning to field
CN117185873A (en) * 2023-09-20 2023-12-08 中国科学院沈阳应用生态研究所 Fertilizer for improving soil productivity and preparation method thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1054362C (en) * 1996-04-29 2000-07-12 刘文治 Method for producing organic and inorganic mixed microbe fertilizer
CN103495602A (en) * 2013-09-30 2014-01-08 河南金谷实业发展有限公司 Method for restoring hexavalent chromium-polluted soil by utilizing microbial fermentation
CN104761410A (en) * 2014-01-06 2015-07-08 英卓科技有限公司 Preparation method of humic acid-containing fertilizer and soil conditioner composition
CN104788263A (en) * 2015-04-16 2015-07-22 王龙潮 Composite soil conditioner

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1054362C (en) * 1996-04-29 2000-07-12 刘文治 Method for producing organic and inorganic mixed microbe fertilizer
CN103495602A (en) * 2013-09-30 2014-01-08 河南金谷实业发展有限公司 Method for restoring hexavalent chromium-polluted soil by utilizing microbial fermentation
CN104761410A (en) * 2014-01-06 2015-07-08 英卓科技有限公司 Preparation method of humic acid-containing fertilizer and soil conditioner composition
CN104788263A (en) * 2015-04-16 2015-07-22 王龙潮 Composite soil conditioner

Also Published As

Publication number Publication date
CN106116946A (en) 2016-11-16

Similar Documents

Publication Publication Date Title
CN106116946B (en) Biological organic fertilizer for repairing soil heavy metal and preparation method thereof
CN111011159B (en) A kind of preparation method of ecological improvement substrate based on coal gangue and sludge
CN103694010B (en) A kind of Ultrahigh-temperaturaerobic aerobic fermentation method for sludge and application thereof
CN101054552A (en) Microorganism composite bacterium agent and preparation method and application thereof
CN106914484B (en) Ecological restoration method for rural solid waste polluted soil
CN105482827A (en) Soil conditioner with function of heavy metal-polluted soil restoration
CN104449744A (en) Microbial soil remediation agent and preparation method thereof
CN104072321B (en) A kind of soil conditioner and preparation method thereof
CN105695354A (en) Process and application for treating municipal sewage sludge by means of ultrahigh-temperature aerobic composting fermentation
CN103920706B (en) A kind of immobilization mix bacterium agent repairs the method for heavy metals soil
CN117049910B (en) Method for producing bio-organic fertilizer by treating municipal sludge with microbial agent
CN108456105A (en) A kind of pine charcoal base microbe soil conditioner and preparation method thereof
CN106734184A (en) A kind of in-situ remediation method of heavy-metal contaminated soil
CN102634465B (en) Acinetobacter with authigenic nitrogen fixation capacity and application thereof
CN114988926A (en) Organic compound fertilizer produced by eighty percent of sludge with water content and manufacturing method thereof
CN108440035B (en) Composting method for reducing emission of nitrous oxide and ammonia gas
CN113773987A (en) A kind of biological bacterial agent for improving the efficiency of aerobic fermentation of organic waste and preparation method thereof
CN105505843B (en) A photosynthetic bacterial strain, liquid fertilizer containing the strain, preparation method and application
CN108707032A (en) The biological organic fertilizer and preparation method thereof that microbial degradation house refuse obtains
CN106212094A (en) A kind of salt-soda soil is special reclaims improvement substrate and preparation method thereof
CN103724135B (en) A kind of High-protein biological organic fertilizer and preparation method thereof
CN105566010A (en) Soil amendment
CN105237280A (en) Microorganism in-problem soil ecological restoration preparation, preparation method and application thereof
CN107337506A (en) Anaerobic fermentation compound additive and promotion biogas residue, the method for biogas slurry fertilizer anaerobic fermentation
CN105820976A (en) Sludge compost thermophilic microbial agent and application

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20210426

Address after: 611830 no.615, Yanhua Road, Sichuan Dujiangyan Economic Development Zone, Dujiangyan City, Chengdu City, Sichuan Province

Patentee after: CHENGDU HUAHONG BIOTECHNOLOGY Co.,Ltd.

Address before: 610039 No. 999, golden week Road, Chengdu, Sichuan, Jinniu District

Patentee before: XIHUA University

Patentee before: CHENGDU HUAHONG BIOTECHNOLOGY Co.,Ltd.