CN115500238B - Method for improving phosphogypsum storage yard soil by using waste straw - Google Patents

Method for improving phosphogypsum storage yard soil by using waste straw Download PDF

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CN115500238B
CN115500238B CN202211123797.5A CN202211123797A CN115500238B CN 115500238 B CN115500238 B CN 115500238B CN 202211123797 A CN202211123797 A CN 202211123797A CN 115500238 B CN115500238 B CN 115500238B
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soil
phosphogypsum
matrix
culture
cellulose
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CN115500238A (en
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肖春桥
金泳彤
池汝安
李毅中
许鸿娟
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Hubei Three Gorges Laboratory
Wuhan Institute of Technology
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Hubei Three Gorges Laboratory
Wuhan Institute of Technology
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    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G24/00Growth substrates; Culture media; Apparatus or methods therefor
    • A01G24/10Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material
    • A01G24/12Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material containing soil minerals
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G24/00Growth substrates; Culture media; Apparatus or methods therefor
    • A01G24/10Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G24/00Growth substrates; Culture media; Apparatus or methods therefor
    • A01G24/20Growth substrates; Culture media; Apparatus or methods therefor based on or containing natural organic material
    • A01G24/22Growth substrates; Culture media; Apparatus or methods therefor based on or containing natural organic material containing plant material
    • 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

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  • Life Sciences & Earth Sciences (AREA)
  • Environmental Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • Soil Sciences (AREA)
  • Soil Conditioners And Soil-Stabilizing Materials (AREA)

Abstract

The invention relates to a method for improving phosphogypsum storage yard soil by utilizing waste straws, which specifically comprises the following steps: s1: mixing phosphogypsum powder and alkaline soil according to a certain mass ratio to obtain pretreated phosphogypsum; s2: mixing the pretreated phosphogypsum with straw powder, and spraying a composite bacterial liquid to obtain a primary soil-like matrix; s3: introducing pioneer plants into the primary soil-like matrix to obtain a medium-grade soil-like matrix; s4: and introducing common plants into the medium soil-like matrix to obtain the high soil-like matrix. The invention has the beneficial effects that phosphogypsum storage yard can be subjected to soil formation, and meanwhile, the agricultural waste straw is efficiently utilized, so that the problem of piling up a large amount of phosphogypsum and the agricultural waste straw is solved, and the invention has great practical significance for environmental ecological protection and resource recycling integration and has the advantages of simple process, high treatment efficiency, green ecology and low cost.

Description

一种利用废弃秸秆对磷石膏堆场土壤化改良的方法A method of using waste straw to improve the soil of phosphogypsum stockyards

技术领域Technical field

本发明涉及资源整合利用和生态修复的技术领域,具体涉及一种利用废弃秸秆对磷石膏堆场土壤化改良的方法。The present invention relates to the technical field of resource integrated utilization and ecological restoration, and specifically relates to a method for utilizing waste straw to improve the soil of a phosphogypsum stockpile.

背景技术Background technique

磷石膏是湿法磷酸生产过程中硫酸分解磷矿得到的副产物,此外含有磷、氟等有害杂质。我国大量的磷石膏仍以堆存为主,这些磷石膏的堆存不仅占用了大量土地,其长时间堆存会导致磷石膏中含有的可溶磷、氟等进入土壤、地表水、地下水,会造成严重的环境问题。同时,磷石膏不同于一般的土壤和常规金属尾矿,具有很大的离散性,垂直渗透系数要大于水平渗透系数,导致堆场容易出现溶洞、溶沟,进而导致安全问题。针对磷石膏堆场可溶磷、可溶氟的释放带来的环境问题,在环保监管日益严格、能源结构转型的背景下,实现磷石膏的无害化处置和土壤化改良以及生态化利用对磷化工产业链的健康发展至关重要。Phosphogypsum is a by-product obtained by decomposing phosphate rock with sulfuric acid during the production of wet phosphoric acid. It also contains harmful impurities such as phosphorus and fluorine. A large amount of phosphogypsum in my country is still mainly stored in stockpiles. The stockpiles of these phosphogypsum not only occupy a large amount of land, but their long-term stockpiling will cause the soluble phosphorus and fluorine contained in the phosphogypsum to enter the soil, surface water, and groundwater. Will cause serious environmental problems. At the same time, phosphogypsum is different from ordinary soil and conventional metal tailings in that it is highly discrete. The vertical permeability coefficient is greater than the horizontal permeability coefficient, causing caves and ditches to easily appear in the stockyard, which in turn leads to safety problems. In view of the environmental problems caused by the release of soluble phosphorus and soluble fluorine in phosphogypsum stockyards, in the context of increasingly strict environmental protection supervision and the transformation of the energy structure, the harmless disposal, soil improvement and ecological utilization of phosphogypsum are necessary. The healthy development of the phosphorus chemical industry chain is crucial.

针对磷石膏的无害化处理目前研究报道仍主要集中利用及改良传统方法进行磷石膏处理,传统方法具有效益单一、工艺复杂、能耗较高和二次污染等缺点。目前未见以磷石膏与农业秸秆联合高效生物质降解菌实现磷石膏土壤化的研究。Current research reports on the harmless treatment of phosphogypsum still mainly focus on the use and improvement of traditional methods for phosphogypsum treatment. Traditional methods have shortcomings such as single benefit, complex process, high energy consumption and secondary pollution. At present, there is no research on using phosphogypsum and agricultural straw combined with efficient biomass-degrading bacteria to achieve soilification of phosphogypsum.

发明内容Contents of the invention

本发明所要解决的技术问题是提供一种利用废弃秸秆对磷石膏堆场土壤化改良的方法,旨在解决现有技术中的问题。The technical problem to be solved by the present invention is to provide a method for improving the soil of a phosphogypsum stockpile using waste straw, aiming to solve the problems in the existing technology.

本发明解决上述技术问题的技术方案如下:The technical solutions of the present invention to solve the above technical problems are as follows:

一种利用废弃秸秆对磷石膏堆场土壤化改良的方法,具体包括以下步骤:A method of using waste straw to improve the soil of a phosphogypsum stockpile, specifically including the following steps:

S1:将磷石膏粉末和碱性土壤按照一定质量比混合,获得预处理磷石膏;S1: Mix phosphogypsum powder and alkaline soil according to a certain mass ratio to obtain pretreated phosphogypsum;

S2:将上述预处理磷石膏与秸秆粉混合,并喷淋复合菌液,获得初级类土基质;S2: Mix the above pretreated phosphogypsum and straw powder, and spray the compound bacterial solution to obtain a primary soil-like matrix;

S3:将上述初级类土基质中引入先锋植物,获得中级类土基质;S3: Introduce pioneer plants into the above-mentioned primary soil-like matrix to obtain an intermediate soil-like matrix;

S4:在上述中级类土基质中引入普通植物,获得高级类土基质。S4: Introduce ordinary plants into the above-mentioned intermediate soil-like matrix to obtain an advanced soil-like matrix.

本发明的有益效果是:本发明能够将磷石膏堆场进行土壤化,同时高效利用了农业废弃秸秆,解决了大量磷石膏和农业废弃秸秆堆存的问题,对于环境生态保护和资源循环利用综合化具有很大的现实意义,具有工艺简单、处理效率高、绿色生态以及成本低廉的优点。The beneficial effects of the present invention are: the present invention can soilize the phosphogypsum storage yard, and at the same time efficiently utilize agricultural waste straw, solve the problem of storing a large amount of phosphogypsum and agricultural waste straw, and comprehensively improve environmental and ecological protection and resource recycling. Chemicalization has great practical significance and has the advantages of simple process, high processing efficiency, green ecology and low cost.

在上述技术方案的基础上,本发明还可以做如下改进。On the basis of the above technical solution, the present invention can also make the following improvements.

进一步,所述S1之前还包括S0,复合菌液的制备,具体包括以下步骤:Further, the step S1 also includes S0, the preparation of the composite bacterial solution, which specifically includes the following steps:

S01:将分离纯化的不同菌株分别在液体培养基中富集培养,得到不同纤维素降解菌的富集培养液;S01: Enrich and culture the isolated and purified strains in liquid culture media to obtain enriched culture solutions of different cellulose-degrading bacteria;

S02:将上述不同的富集培养液分别进行代次驯化培养,得到不同纤维素降解菌的驯化培养液,并将上述不同驯化培养液按照一定体积比混合后获得复合菌液。S02: The above-mentioned different enriched culture liquids are domesticated and cultured for generations to obtain domesticated culture liquids of different cellulose-degrading bacteria, and the above-mentioned different domesticated culture liquids are mixed according to a certain volume ratio to obtain a composite bacterial liquid.

采用上述进一步方案的有益效果是该方法工艺简单,能够快速的获得复合菌液。The beneficial effect of adopting the above-mentioned further scheme is that the method is simple in process and can quickly obtain the compound bacterial liquid.

进一步,所述S01具体包括以下步骤:Further, the S01 specifically includes the following steps:

S011:采集腐生植物以及周围土壤样品,将其与无菌水按质量比(1-2):1 装入容器中,混合沉淀后,获得上清液;S011: Collect saprophytic plants and surrounding soil samples, put them into a container with sterile water at a mass ratio of (1-2):1, mix and settle, and obtain the supernatant;

S012:将上述上清液与富集培养基按照体积比(0.1-0.4):1装入容器中,将容器置于25-35℃恒温摇床在160-200转/分钟的转速下振荡培养,得到富集菌液;S012: Put the above supernatant and enriched culture medium into a container according to the volume ratio (0.1-0.4):1, place the container in a constant temperature shaker at 25-35°C, and shake and culture at a speed of 160-200 rpm. , to obtain enriched bacterial liquid;

S013:将富集菌液与解纤维素培养基按照体积比2:(5-10)混合均匀后,于26-32℃恒温摇床在160-200转/分钟的转速下培养3-7天,得到纤维素复合菌菌液;S013: Mix the enriched bacterial liquid and cellulolytic medium evenly according to the volume ratio of 2: (5-10), then culture it in a constant temperature shaker at 26-32°C at a speed of 160-200 rpm for 3-7 days. , obtain the cellulose composite bacteria liquid;

S014:将纤维素复合菌液接种到解纤维素培养基中,于26-32℃倒置培养3-5天后,得到纤维素降解菌的菌落,并选择单一的、形态不同的菌落利用平板画线分离培养的方式于26-32℃纯化培养3-5天,获得纯化后的解纤维素菌菌株;S014: Inoculate the cellulose complex bacterial solution into the cellulolytic medium, and incubate it upside down at 26-32°C for 3-5 days to obtain colonies of cellulose-degrading bacteria, and select single colonies with different shapes to draw lines on the plate. Purify and culture at 26-32°C for 3-5 days through isolation and culture to obtain the purified cellulolytic bacteria strain;

S015:将纯化的纤维素降解菌菌株接种至解纤维素培养基中,于28-30℃倒置培养3-5天,筛选出具有透明圈的纤维素降解菌株;S015: Inoculate the purified cellulose-degrading bacterial strain into the cellulolytic medium, culture it upside down at 28-30°C for 3-5 days, and screen out the cellulose-degrading strain with a transparent circle;

S016:将筛选出的纤维素降解菌株接种于液体产酶培养基中,置于 26-32℃恒温摇床在160-200转/分钟的转速下振荡培养5-7天后,比较培养液中总纤维素酶活高低并获得高效纤维素降解菌;S016: Inoculate the selected cellulose-degrading strain into the liquid enzyme-producing medium, place it in a constant-temperature shaker at 26-32°C, and culture it with shaking at a speed of 160-200 rpm for 5-7 days. The cellulase activity is high and low and efficient cellulose-degrading bacteria are obtained;

S017:分离筛选出虫拟蜡菌、链霉菌、枯草芽孢杆菌、里氏木霉、毛壳菌和解淀粉芽孢杆菌的菌株,并将扩大培养培养基所筛选的以上菌株置于 26-32℃恒温摇床在180-220转/分钟的转速下培养5-7天,获得扩大培养后的不同富集培养液。S017: Isolate and screen out strains of Cereus, Streptomyces, Bacillus subtilis, Trichoderma reesei, Chaetomium and Bacillus amyloliquefaciens, and place the above selected strains in the expanded culture medium at a constant temperature of 26-32°C The shaker was incubated at a rotation speed of 180-220 rpm for 5-7 days to obtain different enriched culture fluids after expanded culture.

采用上述进一步方案的有益效果是该方法工艺简单,能够快速获得不同的富集培养液,方便快捷。The beneficial effects of adopting the above-mentioned further scheme are that the method is simple in process, can quickly obtain different enriched culture fluids, and is convenient and fast.

进一步,所述S02具体包括以下步骤:Further, the S02 specifically includes the following steps:

S021:将不同纤维素降解菌的富集培养液接种至含秸秆粉与磷石膏的驯化培养基中,于26-32℃下传代驯化培养4-7次,直至各菌液中纤维素降解菌的总浓度为107-109/mL,获得不同纤维素降解菌菌液;S021: Inoculate the enriched culture solution of different cellulose-degrading bacteria into the acclimation medium containing straw powder and phosphogypsum, and subculture it at 26-32°C for 4-7 times until the cellulose-degrading bacteria in each bacterial solution The total concentration is 10 7 -10 9 /mL, and different cellulose-degrading bacteria liquids are obtained;

S022:将不同的纤维素降解菌菌液分别进行扩大培养,并按照一定的体积比混合制成复合菌液。S022: Expand culture different cellulose-degrading bacteria liquids separately, and mix them according to a certain volume ratio to make a composite bacterial liquid.

采用上述进一步方案的有益效果是该方法工艺简单,能够利用富集培养液获得不同的纤维素降解菌菌液,然后利用不同的纤维素降解菌菌液进行扩大培养,并获得复合菌液。The beneficial effect of adopting the above-mentioned further scheme is that the method has a simple process and can use enriched culture liquid to obtain different cellulose-degrading bacterial liquids, and then use different cellulose-degrading bacterial liquids to expand the culture and obtain a composite bacterial liquid.

进一步,所述S1中,磷石膏:碱性土壤按照质量比1:(2-4)混合。Further, in the S1, phosphogypsum and alkaline soil are mixed according to a mass ratio of 1: (2-4).

采用上述进一步方案的有益效果是该比例适宜,以便更好的利用磷石膏和碱性土壤,以废治废,节能环保。The beneficial effect of adopting the above further scheme is that the ratio is suitable to better utilize phosphogypsum and alkaline soil, treat waste with waste, save energy and protect the environment.

进一步,所述S2具体包括以下步骤:Further, the S2 specifically includes the following steps:

S21:将预处理磷石膏与废弃秸秆粉按质量比1:(1-3)装入搅拌器中,在40-60转/分钟的转速下混合2-10小时,得到有机磷石膏;S21: Put the pretreated phosphogypsum and waste straw powder into a mixer according to the mass ratio of 1: (1-3), and mix at a speed of 40-60 rpm for 2-10 hours to obtain organophosphogypsum;

S22:将复合菌液以7-15L/(h.m2)的喷淋速度间歇式喷淋于有机磷石膏中,每间隔1-2h喷淋1h,经过15-60天的生长、定植后,获得初级类土基质。S22: Spray the compound bacterial solution into the organophosphogypsum intermittently at a spray speed of 7-15L/(hm 2 ), spray for 1 hour every 1-2 hours, and after 15-60 days of growth and colonization, obtain Primary soil-like matrix.

采用上述进一步方案的有益效果是该方法工艺简单,利用复合菌液中的菌种分解初级土壤中的成分,以获得初级类土基质。The beneficial effect of adopting the above-mentioned further scheme is that the method is simple in process and uses the bacteria in the compound bacterial solution to decompose the components in the primary soil to obtain a primary soil-like matrix.

进一步,所述S3具体包括以下步骤:Further, the S3 specifically includes the following steps:

将先锋植物种植在所述S2中的初级类土基质中,经1-5轮定植生长后获得中级类土基质。Pioneer plants are planted in the primary soil-like matrix in S2, and after 1-5 rounds of colonization and growth, an intermediate soil-like matrix is obtained.

采用上述进一步方案的有益效果是选择合理,上述先锋植物具有生命力顽强、生长速度快、环境抗性强、根系发达等特点,可以通过其根系生理活动综合提高磷石膏生态功能。The beneficial effect of adopting the above-mentioned further scheme is that the selection is reasonable. The above-mentioned pioneer plants have the characteristics of tenacious vitality, fast growth rate, strong environmental resistance, and developed root systems. They can comprehensively improve the ecological functions of phosphogypsum through their root physiological activities.

进一步,所述S3中,先锋植物包括植凤尾蕨和黑麦草中的一种或多种。Further, in S3, the pioneer plant includes one or more of fern and ryegrass.

采用上述进一步方案的有益效果是选择合理,品种常见,取材方便。The beneficial effects of adopting the above further scheme are reasonable selection, common varieties and convenient material collection.

进一步,所述S4具体包括以下步骤:将普通植物种植在所述S3中的中级类土基质中,经1-5轮定植生长后获得高级类土基质。Further, the S4 specifically includes the following steps: planting ordinary plants in the intermediate soil-like matrix in the S3, and obtaining a high-grade soil-like matrix after 1-5 rounds of planting and growth.

采用上述进一步方案的有益效果是工艺简单,设计合理,进一步提高类土基质的营养。The beneficial effects of adopting the above-mentioned further scheme are simple process, reasonable design, and further improving the nutrition of the soil-like matrix.

进一步,所述S4中,普通植物包括小花碱茅、草地早熟禾、紫苜蓿和百脉根中的一种或多种。Further, in the S4, the common plants include one or more of Alpinia parvum, Poa annua, alfalfa and Lotus japonicus.

采用上述进一步方案的有益效果是上述普通植物能够促进植物生长及发挥生理功能,促进团聚体形成及矿质养分的提升。The beneficial effect of adopting the above further solution is that the above-mentioned common plants can promote plant growth and exert physiological functions, promote the formation of aggregates and increase mineral nutrients.

附图说明Description of the drawings

图1为本发明的工艺流程图。Figure 1 is a process flow diagram of the present invention.

具体实施方式Detailed ways

需要说明的是,在不冲突的情况下,本发明中的实施例及实施例中的特征可以相互组合。It should be noted that, as long as there is no conflict, the embodiments and features in the embodiments of the present invention can be combined with each other.

在本发明的描述中,需要理解的是,术语“中心”、“纵向”、“横向”、“上”、“下”、“前”、“后”、“左”、“右”、“竖直”、“水平”、“顶”、“底”、“内”、“外”等指示的方位或位置关系为基于附图所示的方位或位置关系,仅是为了便于描述本发明和简化描述,而不是指示或暗示所指的装置或元件必须具有特定的方位、以特定的方位构造和操作,因此不能理解为对本发明的限制。此外,术语“第一”、“第二”等仅用于描述目的,而不能理解为指示或暗示相对重要性或者隐含指明所指示的技术特征的数量。由此,限定有“第一”、“第二”等的特征可以明示或者隐含地包括一个或者更多个该特征。在本发明的描述中,除非另有说明,“多个”的含义是两个或两个以上。In the description of the present invention, it should be understood that the terms "center", "longitudinal", "lateral", "upper", "lower", "front", "rear", "left", "right", " The orientations or positional relationships indicated by "vertical", "horizontal", "top", "bottom", "inner", "outer", etc. are based on the orientations or positional relationships shown in the drawings, and are only for the convenience of describing the present invention and The simplified description is not intended to indicate or imply that the device or element referred to must have a specific orientation, be constructed and operate in a specific orientation, and therefore should not be construed as a limitation of the present invention. Furthermore, the terms “first”, “second”, etc. are used for descriptive purposes only and cannot be understood as indicating or implying relative importance or implicitly indicating the quantity of indicated technical features. Thus, features defined by "first," "second," etc. may explicitly or implicitly include one or more of such features. In the description of the present invention, unless otherwise specified, "plurality" means two or more.

在本发明的描述中,需要说明的是,除非另有明确的规定和限定,术语“安装”、“相连”、“连接”应做广义理解,例如,可以是固定连接,也可以是可拆卸连接,或一体地连接;可以是机械连接,也可以是电连接;可以是直接相连,也可以通过中间媒介间接相连,可以是两个元件内部的连通。对于本领域的普通技术人员而言,可以通过具体情况理解上述术语在本发明中的具体含义。In the description of the present invention, it should be noted that, unless otherwise clearly stated and limited, the terms "installation", "connection" and "connection" should be understood in a broad sense. For example, it can be a fixed connection or a detachable connection. Connection, or integral connection; it can be a mechanical connection or an electrical connection; it can be a direct connection or an indirect connection through an intermediate medium; it can be an internal connection between two components. For those of ordinary skill in the art, the specific meanings of the above terms in the present invention can be understood through specific situations.

下面将参考附图并结合实施例来详细说明本发明。The present invention will be described in detail below with reference to the accompanying drawings and embodiments.

实施例1Example 1

如图1所示,本实施例提供一种利用废弃秸秆对磷石膏堆场土壤化改良的方法,具体包括以下步骤:As shown in Figure 1, this embodiment provides a method for using waste straw to improve the soil of a phosphogypsum stockpile, which specifically includes the following steps:

S1:将磷石膏粉末和碱性土壤按照一定质量比混合,获得预处理磷石膏;S1: Mix phosphogypsum powder and alkaline soil according to a certain mass ratio to obtain pretreated phosphogypsum;

S2:将上述预处理磷石膏与秸秆粉混合,并喷淋复合菌液,获得初级类土基质;S2: Mix the above pretreated phosphogypsum and straw powder, and spray the compound bacterial solution to obtain a primary soil-like matrix;

S3:将上述初级类土基质中引入先锋植物,获得中级类土基质;S3: Introduce pioneer plants into the above-mentioned primary soil-like matrix to obtain an intermediate soil-like matrix;

S4:在上述中级类土基质中引入普通植物,获得高级类土基质。S4: Introduce ordinary plants into the above-mentioned intermediate soil-like matrix to obtain an advanced soil-like matrix.

本实施例能够将磷石膏堆场进行土壤化,同时高效利用了农业废弃秸秆,解决了大量磷石膏和农业废弃秸秆堆存的问题,对于环境生态保护和资源循环利用综合化具有很大的现实意义,具有工艺简单、处理效率高、绿色生态以及成本低廉的优点。This embodiment can soilize the phosphogypsum storage yard, and at the same time efficiently utilize agricultural waste straw, solving the problem of storing a large amount of phosphogypsum and agricultural waste straw, and has great practicality for environmental and ecological protection and comprehensive resource recycling. It has the advantages of simple process, high processing efficiency, green ecology and low cost.

实施例2Example 2

在实施例1的基础上,本实施例中,所述S1之前还包括S0,复合菌液的制备,具体包括以下步骤:On the basis of Example 1, in this example, S1 is preceded by S0, and the preparation of the composite bacterial solution specifically includes the following steps:

S01:将分离纯化的不同菌株分别在液体培养基中富集培养,得到不同纤维素降解菌的富集培养液;S01: Enrich and culture the isolated and purified strains in liquid culture media to obtain enriched culture solutions of different cellulose-degrading bacteria;

S02:将上述不同的富集培养液分别进行代次驯化培养,得到不同纤维素降解菌的驯化培养液,并将上述不同驯化培养液按照一定体积比混合后获得复合菌液。S02: The above-mentioned different enriched culture liquids are domesticated and cultured for generations to obtain domesticated culture liquids of different cellulose-degrading bacteria, and the above-mentioned different domesticated culture liquids are mixed according to a certain volume ratio to obtain a composite bacterial liquid.

该方法工艺简单,能够快速的获得复合菌液。This method has a simple process and can quickly obtain a compound bacterial solution.

实施例3Example 3

在实施例2的基础上,本实施例中,所述S01具体包括以下步骤:Based on Embodiment 2, in this embodiment, the S01 specifically includes the following steps:

S011:采集腐生植物以及周围土壤样品,将其与无菌水按质量比(1-2):1 装入容器中,混合沉淀后,获得上清液;S011: Collect saprophytic plants and surrounding soil samples, put them into a container with sterile water at a mass ratio of (1-2):1, mix and settle, and obtain the supernatant;

S012:将上述上清液与富集培养基按照体积比(0.1-0.4):1装入容器中,将容器置于25-35℃恒温摇床在160-200转/分钟的转速下振荡培养,得到富集菌液;S012: Put the above supernatant and enriched culture medium into a container according to the volume ratio (0.1-0.4):1, place the container in a constant temperature shaker at 25-35°C, and shake and culture at a speed of 160-200 rpm. , to obtain enriched bacterial liquid;

S013:将富集菌液与解纤维素培养基按照体积比2:(5-10)混合均匀后,于26-32℃恒温摇床在160-200转/分钟的转速下培养3-7天,得到纤维素复合菌菌液;S013: Mix the enriched bacterial liquid and cellulolytic medium evenly according to the volume ratio of 2: (5-10), then culture it in a constant temperature shaker at 26-32°C at a speed of 160-200 rpm for 3-7 days. , obtain the cellulose composite bacteria liquid;

S014:将纤维素复合菌液接种到解纤维素培养基中,于26-32℃倒置培养3-5天后,得到纤维素降解菌的菌落,并选择单一的、形态不同的菌落利用平板画线分离培养的方式于26-32℃纯化培养3-5天,获得纯化后的解纤维素菌菌株;S014: Inoculate the cellulose complex bacterial solution into the cellulolytic medium, and incubate it upside down at 26-32°C for 3-5 days to obtain colonies of cellulose-degrading bacteria, and select single colonies with different shapes to draw lines on the plate. Purify and culture at 26-32°C for 3-5 days through isolation and culture to obtain the purified cellulolytic bacteria strain;

S015:将纯化的纤维素降解菌菌株接种至解纤维素培养基中,于28-30℃倒置培养3-5天,筛选出具有透明圈的纤维素降解菌株;S015: Inoculate the purified cellulose-degrading bacterial strain into the cellulolytic medium, culture it upside down at 28-30°C for 3-5 days, and screen out the cellulose-degrading strain with a transparent circle;

S016:将筛选出的纤维素降解菌株接种于液体产酶培养基中,置于 26-32℃恒温摇床在160-200转/分钟的转速下振荡培养5-7天后,比较培养液中总纤维素酶活高低并获得高效纤维素降解菌;S016: Inoculate the selected cellulose-degrading strain into the liquid enzyme-producing medium, place it in a constant-temperature shaker at 26-32°C, and culture it with shaking at a speed of 160-200 rpm for 5-7 days. The cellulase activity is high and low and efficient cellulose-degrading bacteria are obtained;

S017:分离筛选出虫拟蜡菌、链霉菌、枯草芽孢杆菌、里氏木霉、毛壳菌和解淀粉芽孢杆菌的菌株,并将扩大培养培养基所筛选的以上菌株置于 26-32℃恒温摇床在180-220转/分钟的转速下培养5-7天,获得扩大培养后的不同富集培养液。S017: Isolate and screen out strains of Cereus, Streptomyces, Bacillus subtilis, Trichoderma reesei, Chaetomium and Bacillus amyloliquefaciens, and place the above selected strains in the expanded culture medium at a constant temperature of 26-32°C The shaker was incubated at a rotation speed of 180-220 rpm for 5-7 days to obtain different enriched culture fluids after expanded culture.

该方法工艺简单,能够快速获得不同的富集培养液,方便快捷。This method has a simple process, can quickly obtain different enriched culture fluids, and is convenient and fast.

优选地,本实施例中,将高效纤维素降解菌进行16S rDNA鉴定和NCBI 比对(分子鉴定),经比对后确定分离筛选的菌株为:虫拟蜡菌、链霉菌、枯草芽孢杆菌、里氏木霉、毛壳菌、解淀粉芽孢杆菌。Preferably, in this embodiment, the highly efficient cellulose-degrading bacteria are subjected to 16S rDNA identification and NCBI comparison (molecular identification). After comparison, it is determined that the strains isolated and screened are: Pseudomonas cereus, Streptomyces, Bacillus subtilis, Trichoderma reesei, Chaetomium amyloliquefaciens, Bacillus amyloliquefaciens.

优选地,本实施例中,上述富集培养基的成分为:2g/L K2HPO4、1.4g/L (NH4)2SO4、0.3g/L Mg SO4·7H2O、0.3g/L Ca Cl2、5mg/L FeSO4·7H2O、1.6 mg/L MnSO4、1.7mg/LZnSO4及2mg/L CoCl2,溶剂为无菌水。Preferably, in this embodiment, the components of the enrichment medium are: 2g/LK 2 HPO 4 , 1.4g/L (NH 4 ) 2 SO 4 , 0.3g/L MgSO 4 ·7H 2 O, 0.3g /L Ca Cl 2 , 5mg/L FeSO 4 ·7H 2 O, 1.6 mg/L MnSO 4 , 1.7mg/LZnSO 4 and 2mg/L CoCl 2. The solvent is sterile water.

优选地,本实施例中,上述解纤维素培养基的成分为:10g/L羧甲基纤维素钠、2g/LK2HPO4、0.5g/L MgSO4、0.25g/L刚果红、16g/L琼脂及3g/L 明胶,溶剂为无菌水。Preferably, in this embodiment, the components of the above-mentioned cellulolytic medium are: 10g/L sodium carboxymethylcellulose, 2g/LK 2 HPO 4 , 0.5g/L MgSO 4 , 0.25g/L Congo red, 16g /L agar and 3g/L gelatin, the solvent is sterile water.

优选地,本实施例中,上述所述液体产酶培养基的成分为:5-10g/L羧甲基纤维素钠、1-2g/L NH4Cl、0.5-1g/L MgSO4·7H2O、1-2g/L KH2PO4及1-2g/L 酵母浸粉,溶剂为无菌水。Preferably, in this embodiment, the components of the above-mentioned liquid enzyme-producing culture medium are: 5-10g/L sodium carboxymethylcellulose, 1-2g/L NH 4 Cl, 0.5-1g/L MgSO 4 ·7H 2 O, 1-2g/L KH 2 PO 4 and 1-2g/L yeast extract powder, the solvent is sterile water.

优选地,本实施例中,上述所述扩大培养培养基的成分为:胰蛋白胨 10g/L、酵母提取物5g/L及氯化钠10g/L,溶剂为无菌水。Preferably, in this embodiment, the components of the above-mentioned expanded culture medium are: tryptone 10g/L, yeast extract 5g/L and sodium chloride 10g/L, and the solvent is sterile water.

实施例4Example 4

在实施例2至实施例3任一项的基础上,本实施例中,所述S02具体包括以下步骤:Based on any one of Embodiment 2 to Embodiment 3, in this embodiment, the S02 specifically includes the following steps:

S021:将不同纤维素降解菌的富集培养液接种至含秸秆粉与磷石膏的驯化培养基中,于26-32℃下传代驯化培养4-7次,直至各菌液中纤维素降解菌的总浓度为107-109个/mL,获得不同纤维素降解菌菌液;S021: Inoculate the enriched culture solution of different cellulose-degrading bacteria into the acclimation medium containing straw powder and phosphogypsum, and subculture it at 26-32°C for 4-7 times until the cellulose-degrading bacteria in each bacterial solution The total concentration is 10 7 -10 9 /mL, and different cellulose-degrading bacteria liquids are obtained;

S022:将不同的纤维素降解菌菌液分别进行扩大培养,并按照一定的体积比混合制成复合菌液。S022: Expand culture different cellulose-degrading bacteria liquids separately, and mix them according to a certain volume ratio to make a composite bacterial liquid.

该方法工艺简单,能够利用富集培养液获得不同的纤维素降解菌菌液,然后利用不同的纤维素降解菌菌液进行扩大培养,并获得复合菌液。This method has a simple process and can use enriched culture liquid to obtain different cellulose-degrading bacterial liquids, and then use different cellulose-degrading bacterial liquids to expand the culture and obtain a composite bacterial liquid.

优选地,本实施例中,上述驯化液体培养基的成分为:1.0g/L KH2PO4、 0.3g/LMgSO4、0.1g/L NaCl、2.5g/L NaNO3、0.1/L CaCl2·6H2O、0.01g/L FeCl3、 20g/L秸秆粉及10g/L磷石膏粉,溶剂为无菌水。Preferably, in this embodiment, the components of the above-mentioned acclimation liquid culture medium are: 1.0g/L KH 2 PO 4 , 0.3g/LMgSO 4 , 0.1g/L NaCl, 2.5g/L NaNO 3 , 0.1/L CaCl 2 ·6H 2 O, 0.01g/L FeCl 3 , 20g/L straw powder and 10g/L phosphogypsum powder, the solvent is sterile water.

优选地,本实施例中,上述S022中虫拟蜡菌、链霉菌、枯草芽孢杆菌、里氏木霉、毛壳菌和解淀粉芽孢杆菌的菌株按照1:(1-3):(2-4):(1-3):(1-3):(2-4) 的体积比制成复合菌液。Preferably, in this embodiment, the above-mentioned strains of Cereus, Streptomyces, Bacillus subtilis, Trichoderma reesei, Chaetomium and Bacillus amyloliquefaciens in S022 are according to 1: (1-3): (2-4 ):(1-3):(1-3):(2-4) to prepare a compound bacterial solution.

实施例5Example 5

在上述各实施例的基础上,本实施例中,所述S1中,磷石膏与碱性土壤按照质量比1:(2-4)混合。On the basis of the above embodiments, in this embodiment, in S1, phosphogypsum and alkaline soil are mixed according to a mass ratio of 1: (2-4).

该比例适宜,以便更好的利用磷石膏和碱性土壤,以废治废,节能环保。The ratio is appropriate to better utilize phosphogypsum and alkaline soil, treat waste with waste, save energy and protect the environment.

实施例6Example 6

在上述各实施例的基础上,本实施例中,所述S2具体包括以下步骤:Based on the above embodiments, in this embodiment, the S2 specifically includes the following steps:

S21:将预处理磷石膏与废弃秸秆粉按质量比1:(1-3)装入搅拌器中,在40-60转/分钟的转速下混合2-10小时,得到有机磷石膏;S21: Put the pretreated phosphogypsum and waste straw powder into a mixer according to the mass ratio of 1: (1-3), and mix at a speed of 40-60 rpm for 2-10 hours to obtain organophosphogypsum;

S22:将复合菌液以7-15L/(h.m2)的喷淋速度间歇式喷淋于有机磷石膏中,每间隔1-2h喷淋1h,经过15-60天的生长、定植后,获得初级类土基质。S22: Spray the compound bacterial solution into the organophosphogypsum intermittently at a spray speed of 7-15L/(hm 2 ), spray for 1 hour every 1-2 hours, and after 15-60 days of growth and colonization, obtain Primary soil-like matrix.

该方法工艺简单,利用复合菌液中的菌种分解有机磷石膏中的成分,以获得初级类土基质。This method has a simple process and uses bacteria in the compound bacterial solution to decompose the components in organophosphogypsum to obtain a primary soil-like matrix.

实施例7Example 7

在上述各实施例的基础上,本实施例中,所述S3具体包括以下步骤:Based on the above embodiments, in this embodiment, the S3 specifically includes the following steps:

将先锋植物种植在所述S2中的初级类土基质中,经1-5轮定植生长后获得中级类土基质。Pioneer plants are planted in the primary soil-like matrix in S2, and after 1-5 rounds of colonization and growth, an intermediate soil-like matrix is obtained.

该方案选择合理,上述先锋植物具有生命力顽强、生长速度快、环境抗性强、根系发达等特点,可以通过其根系生理活动综合提高磷石膏生态功能。The choice of this plan is reasonable. The above-mentioned pioneer plants have the characteristics of tenacious vitality, fast growth rate, strong environmental resistance, and developed root systems. They can comprehensively improve the ecological functions of phosphogypsum through their root physiological activities.

实施例8Example 8

在实施例7的基础上,本实施例中,所述S3中,先锋植物包括植凤尾蕨和黑麦草中的一种或多种。On the basis of Example 7, in this example, in S3, the pioneer plant includes one or more of ferns and ryegrass.

该方案选择合理,品种常见,取材方便。The program is reasonably selected, with common varieties and easy access to materials.

实施例9Example 9

在上述各实施例的基础上,本实施例中,所述S4具体包括以下步骤:Based on the above embodiments, in this embodiment, the S4 specifically includes the following steps:

将普通植物种植在所述S3中的中级类土基质中,经1-5轮定植生长后获得高级类土基质。Ordinary plants are planted in the intermediate soil-like matrix in S3, and after 1-5 rounds of planting and growth, a high-grade soil-like matrix is obtained.

该方案工艺简单,设计合理,进一步提高类土基质的营养。This solution has simple technology and reasonable design, which can further improve the nutrition of soil-like substrate.

实施例10Example 10

在实施例9的基础上,本实施例中,所述S4中,普通植物包括小花碱茅、草地早熟禾、紫苜蓿和百脉根中的一种或多种。On the basis of Embodiment 9, in this embodiment, in S4, common plants include one or more of Alpinia parvum, Poa annua, alfalfa, and Lotus japonicus.

上述普通植物能够促进植物生长及发挥生理功能,促进团聚体形成及矿质养分的提升。The above-mentioned common plants can promote plant growth and physiological functions, promote the formation of aggregates and increase mineral nutrients.

将上述先锋植物和普通植物等具体化后的实施方式如下:The embodiments of the above-mentioned pioneer plants and common plants are as follows:

实施例11Example 11

一种利用废弃秸秆对磷石膏堆场土壤化改良的方法,包括如下步骤:A method of using waste straw to improve the soil of a phosphogypsum stockpile, including the following steps:

1)采集腐生植物以及周围土壤样品,将其与无菌水按质量比1:1的比例装入容器中,混合沉淀后,得到上清液;1) Collect saprophytic plants and surrounding soil samples, put them into a container with sterile water at a mass ratio of 1:1, mix and settle, and obtain the supernatant;

将上清液与富集培养基按照体积比0.2:1装入容器中,将容器置于30℃恒温摇床在160转/分钟的转速下振荡培养,得到富集菌液;Put the supernatant and enriched culture medium into a container at a volume ratio of 0.2:1, place the container on a 30°C constant-temperature shaker and perform shaking culture at 160 rpm to obtain enriched bacterial liquid;

将富集菌液与解纤维素培养基按照2:5的体积比混合均匀后,置于28℃恒温摇床在180转/分钟的转速下培养3天,得到纤维素复合菌菌液;Mix the enriched bacterial liquid and cellulolytic culture medium at a volume ratio of 2:5, then place them in a constant temperature shaker at 28°C and culture them at a rotation speed of 180 rpm for 3 days to obtain a cellulose compound bacterial liquid;

将培养后所得到的复合菌液接种到解纤维素培养基中,于28℃倒置培养 3天后,得到纤维素降解菌的菌落,并选择单一的、形态不同的菌落并利用平板画线分离培养的方式于30℃纯化培养3天,以此得到纯化后的解纤维素菌菌株;Inoculate the composite bacterial solution obtained after culture into the cellulose-degrading medium, and incubate it upside down at 28°C for 3 days to obtain colonies of cellulose-degrading bacteria. Select single colonies with different shapes and separate them by drawing lines on a plate. Purify and culture at 30°C for 3 days to obtain the purified cellulolytic bacteria strain;

将纯化的纤维素降解菌菌株接种至解纤维素培养基中,于30℃倒置培养 3天,筛选出具有透明圈的纤维素降解菌株;Inoculate the purified cellulose-degrading bacterial strain into the cellulolytic medium, culture it upside down at 30°C for 3 days, and screen out the cellulose-degrading strain with a transparent circle;

将筛选出的纤维素降解菌株接种于液体产酶培养基中,置于28℃恒温摇床在180转/分钟的转速下振荡培养5天后,比较培养液中总纤维素酶活高低,选择该项指标最高的菌株确定为高效纤维素降解菌;The selected cellulose-degrading strain was inoculated into a liquid enzyme-producing medium, placed in a constant-temperature shaker at 28°C and cultured at a rotation speed of 180 rpm for 5 days. After comparing the total cellulase activity in the culture medium, select this strain. The strain with the highest index was identified as an efficient cellulose-degrading bacterium;

将高效纤维素降解菌进行16S rDNA鉴定,确定分离筛选的菌株为:虫拟蜡菌、链霉菌、枯草芽孢杆菌、里氏木霉、毛壳菌、解淀粉芽孢杆菌。The high-efficiency cellulose-degrading bacteria were identified by 16S rDNA, and the strains isolated and screened were determined to be: Pseudomonas cereus, Streptomyces, Bacillus subtilis, Trichoderma reesei, Chaetomium, and Bacillus amyloliquefaciens.

将高效纤维素降解菌进行扩大培养,于28℃条件下,180转/分钟的转速下恒温摇床培养5天,得到扩大培养后的菌液。The high-efficiency cellulose-degrading bacteria are expanded and cultured in a constant-temperature shaker at 28°C and 180 rpm for 5 days to obtain the expanded cultured bacterial liquid.

2)将不同的纤维素降解菌菌液接种至含秸秆粉与磷石膏的驯化培养基中于28℃下传代驯化培养4次,直至各菌液中纤维素降解菌的总浓度为107个/mL;2) Inoculate different cellulose-degrading bacteria liquids into an acclimation medium containing straw powder and phosphogypsum, and subculture it at 28°C for 4 times until the total concentration of cellulose-degrading bacteria in each bacterial liquid is 10 7 /mL;

将所选择经驯化后的虫拟蜡菌、链霉菌、枯草芽孢杆菌、里氏木霉、毛壳菌、解淀粉芽孢杆菌的菌落进行扩大培养,并按照1:2:4:3:2:4的体积比制成复合菌液。Expand the selected colonies of the domesticated Celeroides, Streptomyces, Bacillus subtilis, Trichoderma reesei, Chaetomium, and Bacillus amyloliquefaciens, and follow 1:2:4:3:2: The volume ratio of 4 is used to prepare a compound bacterial liquid.

3)将磷石膏与碱性土壤按质量比1:3混合均匀,其得到预处理磷石膏。3) Mix phosphogypsum and alkaline soil evenly at a mass ratio of 1:3 to obtain pretreated phosphogypsum.

4)将预处理磷石膏与废弃秸秆粉按质量比1:3装入搅拌器中,在45 转/分钟的转速下混合6小时,得到有机磷石膏;4) Put the pretreated phosphogypsum and waste straw powder into a mixer at a mass ratio of 1:3, and mix at a speed of 45 rpm for 6 hours to obtain organophosphogypsum;

将所筛选驯化后的高效解纤维素降解菌按照体积比1:2:4:3:2:4混合制成复合菌液后喷淋于有机磷石膏中;Mix the selected and domesticated high-efficiency cellulose-degrading bacteria according to the volume ratio of 1:2:4:3:2:4 to prepare a composite bacterial solution and then spray it into the organophosphogypsum;

复合菌液喷淋速度为7L/(h.m2),喷淋方式为间歇式,每间隔1h喷淋1h;复合菌液中的微生物经过60天的生长、定植后,得到初级类土基质。The spray speed of the compound bacterial solution is 7L/(hm 2 ), and the spraying method is intermittent, spraying for 1 hour every 1 hour. After 60 days of growth and colonization, the microorganisms in the compound bacterial solution obtain a primary soil-like matrix.

5)在初级类土基质中,种植先锋植物凤尾蕨,并提供其相应的生长环境与营养素。将得到的初级类土基质在室温条件下稳定5天,使内部理化条件达到一定平衡。种植直接在初级类土基质中进行种植,同时也计算种子发芽率。分为5组每组的土壤量为10kg,每组凤尾蕨撒播种子数量为9、11、 13、14、15粒,7天后统计发芽率。经过植物生长两个周期时间的定植后,得到中级类土基质。5) Plant the pioneer plant Pteris fern in the primary soil-like matrix and provide its corresponding growth environment and nutrients. The obtained primary soil-like matrix was stabilized at room temperature for 5 days to allow the internal physical and chemical conditions to reach a certain balance. Plantings were carried out directly in primary soil-like substrates, and seed germination rates were also calculated. Divide into 5 groups. The amount of soil in each group is 10kg. The number of seeds sown in each group is 9, 11, 13, 14 and 15. The germination rate is calculated after 7 days. After two cycles of plant growth and colonization, an intermediate soil-like matrix is obtained.

6)在中级类土基质中,种植小花碱茅、草地早熟禾、紫苜蓿、百脉根等植物。撒播10粒种子+3粒百脉根种子,每三天施放复合肥一次,7天后计算种子发芽率。经植物生长三个周期时间的定植后,得到高级类土基质。6) In the intermediate soil-like matrix, plant Alpinia parviflora, Bluegrass, alfalfa, Lotus japonicus and other plants. Sow 10 seeds + 3 Lotus japonicus seeds, apply compound fertilizer once every three days, and calculate the seed germination rate after 7 days. After three cycles of plant growth and colonization, a high-grade soil-like matrix is obtained.

表1为本实施例改良后的土壤理化指标Table 1 shows the physical and chemical indicators of the improved soil in this example.

根据表1中的数据可知,初级类土基质、中级类土基质和高级类土基质中的营养成分明显提升,且初级类土基质、中级类土基质和高级类土基质中土壤的营养成分依次得以提升。According to the data in Table 1, it can be seen that the nutrients in the primary soil-like matrix, intermediate soil-like matrix and advanced soil-like matrix are significantly improved, and the nutritional components of the soil in the primary soil-like matrix, intermediate soil-like matrix and advanced soil-like matrix are in order be promoted.

实施例12Example 12

一种利用废弃秸秆对磷石膏堆场土壤化改良的方法,包括如下步骤:A method of using waste straw to improve the soil of a phosphogypsum stockpile, including the following steps:

1)采集腐生植物以及周围土壤样品,将其与无菌水按重量比2:1的比例装入容器中,混合沉淀后,得到上清液;1) Collect saprophytic plants and surrounding soil samples, put them into a container with sterile water at a weight ratio of 2:1, mix and settle, and obtain the supernatant;

将上清液与富集培养基按照体积比0.4:1装入容器中,将容器置于30℃恒温摇床在200转/分钟的转速下振荡培养,得到富集菌液;Put the supernatant and enriched culture medium into a container at a volume ratio of 0.4:1, place the container in a 30°C constant-temperature shaker and perform shaking culture at 200 rpm to obtain enriched bacterial liquid;

将富集菌液与解纤维素培养基按照2:7的体积比混合均匀后,置于28℃恒温摇床在160转/分钟的转速下培养5天,得到纤维素复合菌菌液;After the enriched bacterial liquid and cellulolytic medium are evenly mixed according to a volume ratio of 2:7, they are placed in a constant temperature shaker at 28°C and cultured at a rotation speed of 160 rpm for 5 days to obtain a cellulose compound bacterial liquid;

将培养后所得到的复合菌液接种到解纤维素培养基中,于30℃倒置培养 3天后,得到纤维素降解菌的菌落,并选择单一的、形态不同的菌落并利用平板画线分离培养的方式于28℃纯化培养4天,以此得到纯化后的解纤维素菌菌株;Inoculate the composite bacterial solution obtained after culture into the cellulolytic medium, and incubate it upside down at 30°C for 3 days to obtain colonies of cellulose-degrading bacteria. Select single colonies with different shapes and separate them by drawing lines on a plate. Purify and culture at 28°C for 4 days to obtain the purified cellulolytic bacteria strain;

将纯化的纤维素降解菌菌株接种至解纤维素培养基中,于30℃倒置培养 3天,筛选出具有透明圈的纤维素降解菌株;Inoculate the purified cellulose-degrading bacterial strain into the cellulolytic medium, culture it upside down at 30°C for 3 days, and screen out the cellulose-degrading strain with a transparent circle;

将筛选出的纤维素降解菌株接种于液体产酶培养基中,置于30℃恒温摇床在200转/分钟的转速下振荡培养7天后,比较培养液中总纤维素酶活高低,选择该项指标最高的菌株确定为高效纤维素降解菌;The selected cellulose-degrading strains were inoculated into a liquid enzyme-producing culture medium, placed in a 30°C constant-temperature shaker at a rotation speed of 200 rpm, and cultured for 7 days. After comparing the total cellulase activity in the culture medium, select this strain. The strain with the highest index was identified as an efficient cellulose-degrading bacterium;

将高效纤维素降解菌进行16S rDNA鉴定,确定分离筛选的菌株为:虫拟蜡菌、链霉菌、枯草芽孢杆菌、里氏木霉、毛壳菌、解淀粉芽孢杆菌;The high-efficiency cellulose-degrading bacteria were identified by 16S rDNA, and the strains isolated and screened were determined to be: Pseudomonas cereus, Streptomyces, Bacillus subtilis, Trichoderma reesei, Chaetomium, and Bacillus amyloliquefaciens;

将高效纤维素降解菌进行扩大培养,置于30℃恒温摇床在200转/分钟的转速下培养5天,得到扩大培养后的菌液。The high-efficiency cellulose-degrading bacteria are expanded and cultured, placed in a 30°C constant-temperature shaker at a rotation speed of 200 rpm for 5 days, and the expanded cultured bacterial liquid is obtained.

2)将不同的纤维素降解菌菌液接种至含秸秆粉与磷石膏的驯化培养基中于28℃下传代驯化培养6次,直至各菌液中纤维素降解菌的总浓度为107个/mL;2) Inoculate different cellulose-degrading bacteria liquids into the acclimation medium containing straw powder and phosphogypsum, and subculture it at 28°C for 6 times until the total concentration of cellulose-degrading bacteria in each bacterial liquid is 10 7 /mL;

将所选择经驯化后的虫拟蜡菌、链霉菌、枯草芽孢杆菌、里氏木霉、毛壳菌、解淀粉芽孢杆菌的菌落进行扩大培养,按体积比1:2:4:3:2:4制成复合菌液。Expand the selected colonies of the domesticated Celeroides, Streptomyces, Bacillus subtilis, Trichoderma reesei, Chaetomium, and Bacillus amyloliquefaciens at a volume ratio of 1:2:4:3:2 :4 Make compound bacterial liquid.

3)将磷石膏与碱性土壤按质量比1:2充分混匀,其得到预处理磷石膏。3) Fully mix phosphogypsum and alkaline soil at a mass ratio of 1:2 to obtain pretreated phosphogypsum.

4)将预处理磷石膏与废弃秸秆粉按质量比1:3装入搅拌器中,在45 转/分钟的转速下混合4小时,得到有机磷石膏;4) Put the pretreated phosphogypsum and waste straw powder into a mixer at a mass ratio of 1:3, and mix at a speed of 45 rpm for 4 hours to obtain organophosphogypsum;

将所筛选驯化后的高效解纤维素降解菌按体积比1:2:4:3:2:4混合制成复合菌液后喷淋于有机磷石膏中;Mix the selected and domesticated high-efficiency cellulose-degrading bacteria in a volume ratio of 1:2:4:3:2:4 to prepare a composite bacterial solution and then spray it into the organophosphogypsum;

复合菌液喷淋速度为15L/(h.m2),喷淋方式为间歇式,每间隔2h喷淋 1h。复合菌液中的微生物经过30天的生长、定植后,得到初级类土基质。The spray speed of the compound bacterial solution is 15L/(h.m2), and the spray method is intermittent, spraying for 1 hour every 2 hours. After 30 days of growth and colonization of the microorganisms in the compound bacterial solution, a primary soil-like matrix is obtained.

5)在初级类土基质中,种植先锋植物黑麦草,并提供其相应的生长环境与营养素。将得到的初级类土基质在室温条件下稳定5天,使内部理化条件达到一定平衡。5) Plant the pioneer plant ryegrass in the primary soil-like matrix and provide its corresponding growth environment and nutrients. The obtained primary soil-like matrix was stabilized at room temperature for 5 days to allow the internal physical and chemical conditions to reach a certain balance.

直接在初级类土基质中进行种植,同时也计算种子发芽率。分为5组每组的土壤量为7kg、9kg、10kg、12kg、15kg,每组黑麦草撒播种子数量为9、 11、13、14、15粒,7天后统计发芽率经过植物生长三个周期时间的定植后,得到中级类土基质。Plant directly in a primary soil-like substrate and the seed germination rate is also calculated. Divided into 5 groups, the amount of soil in each group is 7kg, 9kg, 10kg, 12kg, and 15kg. The number of ryegrass seeds sown in each group is 9, 11, 13, 14, and 15. After 7 days, the germination rate is calculated after three cycles of plant growth. After time of colonization, an intermediate soil-like matrix is obtained.

6)在中级类土基质中,种植小花碱茅、草地早熟禾、紫苜蓿、百脉根等植物。撒播13粒种子+3粒百脉根种子,每三天施放复合肥一次,7天后计算种子发芽率。植物生长3个周期时间的定植后,得到高级类土基质。6) In the intermediate soil-like matrix, plant Alpinia parviflora, Bluegrass, alfalfa, Lotus japonicus and other plants. Sow 13 seeds + 3 Lotus japonicus seeds, apply compound fertilizer once every three days, and calculate the seed germination rate after 7 days. After three cycles of plant growth and colonization, a high-grade soil-like matrix is obtained.

表2为本实施例改良后的土壤理化指标Table 2 shows the physical and chemical indicators of the improved soil in this example.

项目project 磷石膏组Phosphogypsum group 初级类土基质Primary soil-like matrix 中级类土基质Intermediate soil-like matrix 高级类土基质Advanced soil-like matrix pH值pH value 1.41.4 4.474.47 5.125.12 7.577.57 土壤总孔隙度(%)Total soil porosity (%) // 34%34% 44%44% 57%57% 氮(%)nitrogen(%) // 0.07%0.07% 0.22%0.22% 0.30%0.30% 全磷(g/kg)Total phosphorus (g/kg) // 0.470.47 0.590.59 0.790.79 全钾(g/kg)Total potassium (g/kg) // 1111 1414 21twenty one 腐殖酸humic acid // 0.64%0.64% 0.17%0.17% 2.01%2.01%

根据表2中的数据可知,初级类土基质、中级类土基质和高级类土基质中的营养成分明显提升,且初级类土基质、中级类土基质和高级类土基质中土壤的营养成分依次得以提升。According to the data in Table 2, it can be seen that the nutrients in the primary soil-like matrix, intermediate soil-like matrix and advanced soil-like matrix are significantly improved, and the nutritional components of the soil in the primary soil-like matrix, intermediate soil-like matrix and advanced soil-like matrix are in order be promoted.

实施例13Example 13

一种利用废弃秸秆对磷石膏堆场土壤化改良的方法,包括如下步骤:A method of using waste straw to improve the soil of a phosphogypsum stockpile, including the following steps:

1)采集腐生植物以及周围土壤样品,将其与无菌水按重量比2:1的比例装入容器中,混合沉淀后,得到上清液;1) Collect saprophytic plants and surrounding soil samples, put them into a container with sterile water at a weight ratio of 2:1, mix and settle, and obtain the supernatant;

将上清液与富集培养基按照体积比0.3:1装入容器中,将容器置于30℃恒温摇床在200转/分钟的转速下振荡培养,得到富集菌液;Put the supernatant and enriched culture medium into a container at a volume ratio of 0.3:1, place the container on a 30°C constant-temperature shaker and perform shaking culture at 200 rpm to obtain enriched bacterial liquid;

将富集菌液与解纤维素培养基按照2:10的体积比混合均匀后,置于26℃恒温摇床在200转/分钟的转速下培养5天,得到纤维素复合菌菌液;After the enriched bacterial liquid and cellulolytic medium are evenly mixed according to a volume ratio of 2:10, they are placed in a constant temperature shaker at 26°C and cultured at a rotation speed of 200 rpm for 5 days to obtain a cellulose compound bacterial liquid;

将培养后所得到的复合菌液接种到解纤维素培养基中,于32℃倒置培养 3天后,得到纤维素降解菌的菌落,并选择单一的、形态不同的菌落并利用平板画线分离培养的方式于32℃纯化培养3天,以此得到纯化后的解纤维素菌菌株;Inoculate the composite bacterial solution obtained after culture into the cellulolytic medium and incubate it upside down at 32°C for 3 days to obtain colonies of cellulose-degrading bacteria. Select single colonies with different shapes and separate them by drawing lines on a plate. Purify and culture at 32°C for 3 days to obtain the purified cellulolytic bacteria strain;

将纯化的纤维素降解菌菌株接种至解纤维素培养基中,于30℃倒置培养 3天,筛选出具有透明圈的纤维素降解菌株;Inoculate the purified cellulose-degrading bacterial strain into the cellulolytic medium, culture it upside down at 30°C for 3 days, and screen out the cellulose-degrading strain with a transparent circle;

将筛选出的纤维素降解菌株接种于液体产酶培养基中,置于30℃恒温摇床在180转/分钟的转速下振荡培养7天后,比较培养液中总纤维素酶活高低,选择该项指标最高的菌株确定为高效纤维素降解菌;The selected cellulose-degrading strain was inoculated into a liquid enzyme-producing culture medium, placed in a 30°C constant-temperature shaker at a rotation speed of 180 rpm, and cultured for 7 days. After comparing the total cellulase activity in the culture medium, select this strain. The strain with the highest index was identified as an efficient cellulose-degrading bacterium;

将高效纤维素降解菌进行16S rDNA鉴定,确定分离筛选的菌株为:虫拟蜡菌、链霉菌、枯草芽孢杆菌、里氏木霉、毛壳菌、解淀粉芽孢杆菌;The high-efficiency cellulose-degrading bacteria were identified by 16S rDNA, and the strains isolated and screened were determined to be: Pseudomonas cereus, Streptomyces, Bacillus subtilis, Trichoderma reesei, Chaetomium, and Bacillus amyloliquefaciens;

将高效纤维素降解菌进行扩大培养,置于30℃恒温摇床在180转/分钟的转速下培养5天,得到扩大培养后的菌液。The high-efficiency cellulose-degrading bacteria are expanded and cultured, placed in a 30°C constant-temperature shaker at a rotation speed of 180 rpm for 5 days, and the expanded cultured bacterial liquid is obtained.

2)将不同的纤维素降解菌菌液接种至含秸秆粉与磷石膏的驯化培养基中于28℃下传代驯化培养6次,直至各菌液中纤维素降解菌的总浓度为107个/mL;2) Inoculate different cellulose-degrading bacteria liquids into the acclimation medium containing straw powder and phosphogypsum, and subculture it at 28°C for 6 times until the total concentration of cellulose-degrading bacteria in each bacterial liquid is 10 7 /mL;

将所选择经驯化后的虫拟蜡菌、链霉菌、枯草芽孢杆菌、里氏木霉、毛壳菌、解淀粉芽孢杆菌的菌落进行扩大培养,按体积比1:3:4:3:1:4制成复合菌液。Expand the selected colonies of domesticated Celeroides, Streptomyces, Bacillus subtilis, Trichoderma reesei, Chaetomium and Bacillus amyloliquefaciens at a volume ratio of 1:3:4:3:1 :4 Make compound bacterial liquid.

3)将磷石膏与碱性土壤按质量比1:3充分混匀,其得到预处理磷石膏。3) Fully mix phosphogypsum and alkaline soil at a mass ratio of 1:3 to obtain pretreated phosphogypsum.

4)将预处理磷石膏与废弃秸秆粉按质量比1:3装入搅拌器中,在45 转/分钟的转速下混合8小时,得到有机磷石膏;4) Put the pretreated phosphogypsum and waste straw powder into a mixer at a mass ratio of 1:3, and mix at a speed of 45 rpm for 8 hours to obtain organophosphogypsum;

将所筛选驯化后的高效解纤维素降解菌按体积比1:3:3:3:2:4混合制成复合菌液后喷淋于预处理磷石膏中;Mix the selected and domesticated high-efficiency cellulose-degrading bacteria in a volume ratio of 1:3:3:3:2:4 to prepare a composite bacterial solution and then spray it into the pretreated phosphogypsum;

复合菌液喷淋速度为10L/(h.m2),喷淋方式为间歇式,每间隔2h喷淋 1h。复合菌液中的微生物经过45天的生长、定植后,得到初级类土基质。The spray speed of the compound bacterial solution is 10L/(h.m2), and the spray method is intermittent, spraying for 1 hour every 2 hours. After 45 days of growth and colonization, the microorganisms in the compound bacterial solution obtain a primary soil-like matrix.

5)在初级类土基质中,种植先锋植物黑麦草,并提供其相应的生长环境与营养素。将得到的初级类土基质在室温条件下稳定5天,使内部理化条件达到一定平衡。5) Plant the pioneer plant ryegrass in the primary soil-like matrix and provide its corresponding growth environment and nutrients. The obtained primary soil-like matrix was stabilized at room temperature for 5 days to allow the internal physical and chemical conditions to reach a certain balance.

直接在初级类土基质中进行种植,同时也计算种子发芽率。分为5组每组的土壤量为7kg、9kg、10kg、12kg、15kg,每组黑麦草撒播种子数量为9、 11、13、14、15粒,7天后统计发芽率经过植物生长三个周期时间的定植后,得到中级类土基质。Plant directly in a primary soil-like substrate and the seed germination rate is also calculated. Divided into 5 groups, the amount of soil in each group is 7kg, 9kg, 10kg, 12kg, and 15kg. The number of ryegrass seeds sown in each group is 9, 11, 13, 14, and 15. After 7 days, the germination rate is calculated after three cycles of plant growth. After time of colonization, an intermediate soil-like matrix is obtained.

6)在中级类土基质中,种植小花碱茅、草地早熟禾、紫苜蓿、百脉根等植物。撒播13粒种子+3粒百脉根种子,每三天施放复合肥一次,7天后计算种子发芽率。植物生长3个周期时间的定植后,得到高级类土基质。6) In the intermediate soil-like matrix, plant Alpinia parviflora, Bluegrass, alfalfa, Lotus japonicus and other plants. Sow 13 seeds + 3 Lotus japonicus seeds, apply compound fertilizer once every three days, and calculate the seed germination rate after 7 days. After three cycles of plant growth and colonization, a high-grade soil-like matrix is obtained.

表3为本实施例改良后的土壤理化指标Table 3 shows the physical and chemical indicators of the improved soil in this example.

项目project 磷石膏组Phosphogypsum group 初级类土基质Primary soil-like matrix 中级类土基质Intermediate soil-like matrix 高级类土基质Advanced soil-like matrix pH值pH value 1.41.4 4.534.53 5.465.46 7.887.88 土壤总孔隙度(%)Total soil porosity (%) // 36%36% 43%43% 56%56% 氮(%)nitrogen(%) // 0.09%0.09% 0.23%0.23% 0.32%0.32% 全磷(g/kg)Total phosphorus (g/kg) // 0.430.43 0.550.55 0.770.77 全钾(g/kg)Total potassium (g/kg) // 1313 1616 24twenty four 腐殖酸humic acid // 0.64%0.64% 0.21%0.21% 2.07%2.07%

根据表3中的数据可知,初级类土基质、中级类土基质和高级类土基质中的营养成分明显提升,且初级类土基质、中级类土基质和高级类土基质中土壤的营养成分依次得以提升。According to the data in Table 3, it can be seen that the nutrients in the primary soil-like matrix, intermediate soil-like matrix and advanced soil-like matrix are significantly improved, and the nutritional components of the soil in the primary soil-like matrix, intermediate soil-like matrix and advanced soil-like matrix are in order be promoted.

本发明结合农业废弃秸秆将磷石膏堆场转变为类土基质,既可以解决磷石膏和农业废弃秸秆堆存的难题,而且还可以改善土壤问题。The invention combines agricultural waste straw to convert the phosphogypsum stockpile into a soil-like matrix, which can not only solve the problem of storing phosphogypsum and agricultural waste straw, but also improve soil problems.

本发明的有益效果是:The beneficial effects of the present invention are:

1、磷石膏来自磷石膏堆场,采用本发明方法可以解决大量磷石膏的堆存难题,且本发明充分利用了废弃生物质,也能够解决农业废弃物秸秆的大量堆存难题;1. Phosphogypsum comes from the phosphogypsum storage yard. The method of the present invention can solve the problem of storing a large amount of phosphogypsum. Moreover, the present invention makes full use of waste biomass and can also solve the problem of storing a large amount of agricultural waste straw;

2、将磷石膏联合废弃生物质进行土壤化改良不仅解决了污染问题,实现了更好地废弃污染资源综合化,具备很高的应用价值符合国家保护环境、生态的理念;2. Combining phosphogypsum with waste biomass for soil improvement not only solves the pollution problem, but also achieves better integration of waste polluted resources. It has high application value and is in line with the national concept of protecting the environment and ecology;

3、本发明具有工艺简单、处理效率高、绿色生态以及成本低廉等特点。3. The present invention has the characteristics of simple process, high processing efficiency, green ecology and low cost.

本发明所使用的农业利用废弃秸秆经解纤维素菌分解后,不仅可以为微生物提供可利用的营养物质等,因其结构的特点,微生物生长后,也较为容易在秸秆中定植。本发明所使用的磷石膏不仅可以对土壤环境进行改良,在微生物与其作用的途中,还可以增大磷元素的可吸收量,增强了土壤的肥力、以及提供了植物所需的营养素,磷石膏又可改善土壤的理化环境,以此将磷石膏进行土壤化改良。The agricultural waste straw used in the present invention, after being decomposed by cellulolytic bacteria, can not only provide available nutrients for microorganisms, etc., but due to its structural characteristics, it is also easier for microorganisms to colonize in the straw after growth. The phosphogypsum used in the present invention can not only improve the soil environment, but also increase the absorbable amount of phosphorus during the interaction between microorganisms and microorganisms, enhance soil fertility, and provide nutrients needed by plants. Phosphogypsum It can also improve the physical and chemical environment of the soil, thereby improving the soil with phosphogypsum.

对于本领域技术人员而言,显然本发明不限于上述示范性实施例的细节,而且在不背离本发明的精神或基本特征的情况下,能够以其他的具体形式实现本发明。因此,无论从哪一点来看,均应将实施例看作是示范性的,而且是非限制性的,本发明的范围由所附权利要求而不是上述说明限定,因此旨在将落在权利要求的等同要件的含义和范围内的所有变化囊括在本发明内。不应将权利要求中的任何附图标记视为限制所涉及的权利要求。It is obvious to those skilled in the art that the present invention is not limited to the details of the above-described exemplary embodiments, and that the present invention can be implemented in other specific forms without departing from the spirit or essential characteristics of the present invention. Therefore, the embodiments should be regarded as illustrative and non-restrictive from any point of view, and the scope of the present invention is defined by the appended claims rather than the above description, and it is therefore intended that all claims falling within the claims All changes within the meaning and scope of equivalent elements are included in the present invention. Any reference signs in the claims shall not be construed as limiting the claim in question.

此外,应当理解,虽然本说明书按照实施方式加以描述,但并非每个实施方式仅包含一个独立的技术方案,说明书的这种叙述方式仅仅是为清楚起见,本领域技术人员应当将说明书作为一个整体,各实施例中的技术方案也可以经适当组合,形成本领域技术人员可以理解的其他实施方式。In addition, it should be understood that although this specification is described in terms of implementations, not each implementation only contains an independent technical solution. This description of the specification is only for the sake of clarity, and those skilled in the art should take the specification as a whole. , the technical solutions in each embodiment can also be appropriately combined to form other implementations that can be understood by those skilled in the art.

以上所述仅为本发明的较佳实施例,并不用以限制本发明,凡在本发明的精神和原则之内,所作的任何修改、等同替换、改进等,均应包含在本发明的保护范围之内。The above are only preferred embodiments of the present invention and are not intended to limit the present invention. Any modifications, equivalent substitutions, improvements, etc. made within the spirit and principles of the present invention shall be included in the protection of the present invention. within the range.

Claims (8)

1. The method for improving the phosphogypsum storage yard soil by utilizing the waste straws is characterized by comprising the following steps of:
s1: mixing phosphogypsum powder and alkaline soil according to a certain mass ratio to obtain pretreated phosphogypsum, wherein the preparation method comprises the following steps:
s01: the different separated and purified strains are respectively enriched and cultured in a liquid culture medium to obtain enriched culture solutions of different cellulose degrading bacteria, and the enriched culture solutions are specifically as follows:
s011: collecting saprophyte and surrounding soil samples, filling the saprophyte and the surrounding soil samples into a container according to a mass ratio (1-2) of 1 with sterile water, mixing and precipitating to obtain supernatant;
s012: filling the supernatant and the enrichment medium into a container according to the volume ratio (0.1-0.4): 1, and placing the container into a constant temperature shaking table at 25-35 ℃ for shaking culture at the rotating speed of 160-200 rpm to obtain an enrichment bacterial liquid;
s013: uniformly mixing the enriched bacterial liquid and a cellulolytic culture medium according to the volume ratio of (5-10), and culturing for 3-7 days at a constant temperature shaking table of 26-32 ℃ and a rotating speed of 160-200 rpm to obtain a cellulose composite bacterial liquid;
s014: inoculating the cellulose composite bacterial liquid into a cellulolytic culture medium, inversely culturing for 3-5 days at 26-32 ℃ to obtain bacterial colonies of cellulose degrading bacteria, selecting single bacterial colonies with different forms, purifying and culturing for 3-5 days at 26-32 ℃ by using a plate drawing line separation culture mode to obtain purified cellulolytic bacterial strains;
s015: inoculating the purified cellulose degrading strain into a cellulose degrading culture medium, and reversely culturing for 3-5 days at 28-30 ℃ to screen the cellulose degrading strain with transparent rings;
s016: inoculating the screened cellulose degradation strain into a liquid enzyme production culture medium, placing the liquid enzyme production culture medium in a constant temperature shaking table at 26-32 ℃ for shaking culture at a rotating speed of 160-200 rpm for 5-7 days, and comparing the total cellulase activity in the culture solution to obtain high-efficiency cellulose degradation bacteria;
s017: separating and screening strains of cermets, streptomyces, bacillus subtilis, trichoderma reesei, chaetomium and bacillus amyloliquefaciens, and placing the strains screened by the expansion culture medium into a constant temperature shaking table at 26-32 ℃ for culturing for 5-7 days at a rotating speed of 180-220 rpm to obtain different enrichment culture solutions after expansion culture;
s02: respectively carrying out generation domestication culture on the different enrichment culture solutions to obtain domestication culture solutions of different cellulose degrading bacteria, and mixing the different domestication culture solutions according to a certain volume ratio to obtain a composite bacterial solution
S2: mixing the pretreated phosphogypsum with straw powder, and spraying a composite bacterial liquid to obtain a primary soil-like matrix;
s3: introducing pioneer plants into the primary soil-like matrix to obtain a medium-grade soil-like matrix;
s4: and introducing common plants into the medium soil-like matrix to obtain the high soil-like matrix.
2. The method for improving phosphogypsum yard soil by using waste straw as claimed in claim 1, wherein the step S02 specifically comprises the following steps:
s021: inoculating the enriched culture solution of different cellulose degrading bacteria into domestication culture medium containing straw powder and phosphogypsum, and subculturing at 26-32deg.C for 4-7 times until fiber in each bacterial solutionThe total concentration of the vitamin degrading bacteria is 10 7 -10 9 Obtaining different cellulose degrading bacteria liquid by the method per mL;
s022: and (3) respectively carrying out expansion culture on different cellulose degrading bacterial solutions, and mixing the bacterial solutions according to a certain volume ratio to prepare the composite bacterial solution.
3. The method for improving phosphogypsum yard soil by using waste straws according to any one of claims 1-2, which is characterized in that: in the step S1, phosphogypsum and alkaline soil are mixed according to the mass ratio of 1 (2-4).
4. The method for improving the phosphogypsum yard soil by utilizing waste straws according to any one of claims 1-2, wherein the step S2 specifically comprises the following steps:
s21: the preparation method comprises the following steps of (1) pre-treating phosphogypsum and waste straw powder according to a mass ratio of 1: (1-3) placing the mixture into a stirrer, and mixing the mixture for 2-10 hours at a rotating speed of 40-60 revolutions per minute to obtain the organic phosphogypsum;
s22: the compound bacterial liquid is treated by 7-15L/(h.m) 2 ) The spraying speed of the water-based composite material is intermittently sprayed in the organic phosphogypsum for 1h at intervals of 1-2h, and the primary soil-like matrix is obtained after 15-60 days of growth and field planting.
5. The method for improving the phosphogypsum yard soil by utilizing waste straws according to any one of claims 1-2, wherein the step S3 specifically comprises the following steps:
and (2) planting pioneer plants in the primary soil-like matrix in the step (S2), and obtaining the intermediate soil-like matrix after 1-5 rounds of field planting growth.
6. The method for improving phosphogypsum yard soil by using waste straws as set forth in claim 5, which is characterized in that: in the step S3, the pioneer plant comprises one or more of pteris multifida and ryegrass.
7. The method for improving the phosphogypsum yard soil by utilizing waste straws according to any one of claims 1-2, wherein the step S4 specifically comprises the following steps: and (3) planting the common plants in the medium-class soil matrix in the step (S3), and obtaining the high-class soil matrix after 1-5 rounds of field planting growth.
8. The method for improving phosphogypsum yard soil by using waste straw as set forth in claim 7, which is characterized in that: in the step S4, the common plants comprise one or more of the group consisting of fescue, bluegrass, alfalfa and centella asiatica.
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