CN111018622B - Rapid improvement material and method for gangue yard medium habitat - Google Patents
Rapid improvement material and method for gangue yard medium habitat Download PDFInfo
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- C05—FERTILISERS; MANUFACTURE THEREOF
- C05B—PHOSPHATIC FERTILISERS
- C05B17/00—Other phosphatic fertilisers, e.g. soft rock phosphates, bone meal
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/08—Reclamation of contaminated soil chemically
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
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- B09C1/105—Reclamation of contaminated soil microbiologically, biologically or by using enzymes using fungi or plants
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- C09K17/02—Soil-conditioning materials or soil-stabilising materials containing inorganic compounds only
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
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Abstract
本发明公开了一种矸石堆场介质生境的快速改良材料,包括有钝化材料和植生改良材料;植生改良材料包含有:混合厌氧发酵物85%~90%、磷矿粉9%~10%和硫酸盐还原菌群1%~5%;所述植生改良材料用以下方法制备得到:A.混合厌氧发酵物制备A1:混合物制备:按重量百分比计将35%~55%的豆粕和45%~65%的构树凋落物混匀;A2:向A1步骤的混合物中接种豆豉微生物,豆豉微生物加入量为混合物总重量的0.2~1.5%,厌氧条件下进行发酵得到混合厌氧发酵物;B.向步骤A的混合厌氧发酵物中加入磷矿粉和硫酸盐还原菌群,混匀得到植生改良材料。本发明能改善矸石堆场的物理性状,能提高矸石堆场的氮素、磷素和速效钾等养分含量,提高煤矸石中的微生物量,从而促进矸石堆场的生态重建。
The invention discloses a material for rapidly improving the medium habitat of gangue storage yard, which includes passivation material and vegetation improvement material; the vegetation improvement material includes: 85%-90% of mixed anaerobic fermentation product, 9%-10% of phosphate rock powder % and 1% to 5% of sulfate-reducing bacteria; the plant improvement material is prepared by the following method: A. Mixed anaerobic fermentation product preparation A1: mixture preparation: 35% to 55% of soybean meal and 45%~65% of the mulberry litter is mixed; A2: inoculate fermented soya bean microorganism in the mixture of A1 step, fermented fermented soya bean microbial addition is 0.2~1.5% of the total weight of the mixture, ferment under anaerobic condition to obtain mixed anaerobic fermentation B. Add phosphate rock powder and sulfate-reducing bacteria to the mixed anaerobic fermentation product in step A, and mix well to obtain plant growth improvement materials. The invention can improve the physical properties of the gangue storage yard, increase the nutrient content of nitrogen, phosphorus and available potassium in the gangue storage yard, increase the microbial biomass in the gangue storage yard, and thus promote the ecological reconstruction of the gangue storage yard.
Description
技术领域technical field
本发明涉及一种快速改良材料及其方法,特别是一种矸石堆场介质生境的快速改良材料及其方法。The invention relates to a rapid improvement material and a method thereof, in particular to a rapid improvement material and a method for the medium habitat of gangue storage yards.
背景技术Background technique
富含硫、铁的各类矸石在露天堆放后易氧化产酸而严重污染周边环境和威胁人体健康,其中,煤矸石的数量更为庞大、分布更广、污染也最为突出。煤矸石是煤炭开采和洗选过程中产生的固体废弃物,目前我国堆积量近50亿t,规模较大的煤矸石山有1600多座,占用土地约1.5万hm2。在自然环境中经过空气氧化、雨水淋溶及产酸微生物等综合作用下,极易风化形成低pH值、高铁、锰及硫酸根含量并含多种有害重金属离子的酸性矿山废水(acidmine drainage,AMD),严重污染周边水体、土壤等环境,引起陆生和水生生态系统的退化。煤矸石的含硫尾矿的风化过程、污染释放及可能产生的环境生态风险,污染防治及生态修复等方面已引起广泛关注。All kinds of gangue rich in sulfur and iron are easy to oxidize and produce acid after being stacked in the open air, which seriously pollutes the surrounding environment and threatens human health. Among them, coal gangue has a larger quantity, a wider distribution, and the most serious pollution. Coal gangue is solid waste produced during coal mining and washing. At present, the accumulated amount in China is nearly 5 billion tons. There are more than 1,600 large-scale coal gangue hills, occupying about 15,000 hm 2 of land. Under the combined effects of air oxidation, rainwater leaching and acid-producing microorganisms in the natural environment, it is easily weathered to form acid mine drainage with low pH value, high iron, manganese and sulfate content, and contains a variety of harmful heavy metal ions. AMD), seriously pollute the surrounding water body, soil and other environments, causing the degradation of terrestrial and aquatic ecosystems. The weathering process of sulfur-containing tailings of coal gangue, pollution release and possible environmental and ecological risks, pollution prevention and ecological restoration have attracted widespread attention.
植物修复是矿区生态恢复的主要内容和目标,通过利用不同植物吸收、富集、固定、降解土壤和水体(包括地下水)中的污染物并减少或避免水土流失,同时通过植物的生长增加植被覆盖,从而达到生态恢复或生态改良。但由于煤矸石堆场具有强酸度、强氧化性、物理结构差、保水持水能力差、高有毒有害金属浓度、高硫酸盐以及低营养物质等原因,在煤矸石堆场上,植物着生极其困难。专利(申请号为“201911078464.3”)利用改性灰岩和改性硅石-过氧化钙钝化材料,能对高硫高铁矸石中污染物的释放能进行有效控制,并显著抑制硫氧化细菌的生物活性,快速降低矸石的产酸能力,综合实现矸石堆场污染释放的控制,从而有效保护矸石堆场周边的生态环境。而上述专利所用材料的养分含量低,虽然改善了矸石堆场的理化性质,但由于养分状况不佳,阻碍了矸石堆场生态修复的进展。因此,在进行矸石堆场植物修复之前对煤矸石进行基质改良尤为重要。Phytoremediation is the main content and goal of ecological restoration in mining areas. By using different plants to absorb, enrich, fix, and degrade pollutants in soil and water (including groundwater), reduce or avoid soil erosion, and increase vegetation coverage through plant growth , so as to achieve ecological restoration or ecological improvement. However, due to the strong acidity, strong oxidizing properties, poor physical structure, poor water and water retention capacity, high concentration of toxic and harmful metals, high sulfate and low nutrients in the coal gangue yard, plants grow in the gangue yard. extremely difficult. The patent (application number "201911078464.3") uses modified limestone and modified silica-calcium peroxide passivation materials to effectively control the release of pollutants in high-sulfur and high-iron gangue, and significantly inhibit the growth of sulfur-oxidizing bacteria Active, quickly reduce the acid production capacity of waste rock, comprehensively realize the control of pollution release of waste rock storage yard, so as to effectively protect the ecological environment around the gangue storage yard. The nutrient content of the materials used in the above-mentioned patents is low. Although the physical and chemical properties of the gangue yard have been improved, the progress of ecological restoration of the gangue yard has been hindered due to poor nutrient status. Therefore, it is particularly important to improve the matrix of coal gangue before phytoremediation of gangue yards.
发明内容Contents of the invention
本发明的目的在于,提供一种矸石堆场介质生境的快速改良材料及其方法。本发明在专利(申请号为“201911078464.3”)的基础上,添加了植生改良材料,能改善矸石堆场的物理性状,能提高矸石堆场的氮素、磷素和速效钾等养分含量,提高煤矸石中的微生物量,从而促进矸石堆场的生态重建,同时,对专利(申请号为“201911078464.3”)所提供的高硫高铁污染物释放原位控制的效果影响也不大。且本发明所用材料易获取、易加工,价格低廉,施工工艺简单,效果显著,可操作性强。The object of the present invention is to provide a material and a method for rapidly improving the medium habitat of gangue storage yards. On the basis of the patent (the application number is "201911078464.3"), the present invention adds vegetation improvement materials, which can improve the physical properties of the gangue yard, increase the nutrient content of the gangue yard, such as nitrogen, phosphorus, and available potassium, and increase the The microbial biomass in coal gangue can promote the ecological reconstruction of gangue yards, and at the same time, it has little impact on the effect of in-situ control of the release of high-sulfur and high-iron pollutants provided by the patent (application number "201911078464.3"). Moreover, the material used in the invention is easy to obtain, easy to process, low in price, simple in construction technology, remarkable in effect and strong in operability.
本发明的技术方案:一种矸石堆场介质生境的快速改良材料,包括有钝化材料和植生改良材料;植生改良材料按重量百分比计包含有:混合厌氧发酵物85%~90%、磷矿粉9%~10%和硫酸盐还原菌群1%~5%;所述植生改良材料用以下方法制备得到:The technical solution of the present invention: a rapid improvement material for the medium habitat of gangue storage yard, including passivation material and vegetation improvement material; the vegetation improvement material contains: 85% to 90% of mixed anaerobic fermentation product, phosphorus 9% to 10% of mineral powder and 1% to 5% of sulfate-reducing bacteria; the plant improvement material is prepared by the following method:
A.混合厌氧发酵物制备A. Preparation of mixed anaerobic fermentation
A1:混合物制备:按重量百分比计将35%~55%的豆粕和45%~65%的构树凋落物混匀;A1: mixture preparation: mix 35%~55% soybean meal and 45%~65% mulberry litter by weight percentage;
A2:向A1步骤的混合物中接种豆豉微生物,豆豉微生物加入量为混合物总重量的0.2~1.5%,厌氧条件下进行发酵得到混合厌氧发酵物;A2: Inoculate Douchi microorganisms into the mixture of step A1, the amount of Douchi microorganisms added is 0.2 to 1.5% of the total weight of the mixture, and ferment under anaerobic conditions to obtain a mixed anaerobic fermentation product;
B.向步骤A的混合厌氧发酵物中加入磷矿粉和硫酸盐还原菌群,混匀得到植生改良材料。B. Add phosphate rock powder and sulfate-reducing bacteria to the mixed anaerobic fermentation product in step A, and mix well to obtain a plant growth improvement material.
前述的矸石堆场介质生境的快速改良材料中,所述豆豉微生物按重量百分比计包含有45%~75%的细菌和25%~55%的真菌。In the above-mentioned materials for rapid improvement of the medium habitat of gangue yards, the fermented soya bean microorganisms contain 45% to 75% of bacteria and 25% to 55% of fungi by weight percentage.
前述的矸石堆场介质生境的快速改良材料中,所述细菌按重量百分比计包含有:蓝细菌50%~60%,厚壁菌30%~40%,放线菌和变形菌1%~10%;所述真菌按重量百分比计包含有:接合菌门横梗霉90%~100%和子囊菌0~10%。In the above-mentioned materials for rapid improvement of the medium habitat of gangue storage yard, the bacteria include 50% to 60% of cyanobacteria, 30% to 40% of Firmicutes, 1% to 10% of actinomycetes and proteobacteria by weight percentage. %; the said fungus contains by weight percentage: 90%-100% of Zygomycota Rhizobacillus and 0-10% of Ascomycota.
前述的矸石堆场介质生境的快速改良材料中,所述步骤A2中,向A1步骤的混合物中接种豆豉微生物,并调节其含水量为55%~65%,25~35℃厌氧条件下发酵10~15天即得所需混合厌氧发酵物。In the above-mentioned materials for rapid improvement of the medium habitat of gangue storage yards, in the step A2, fermented soy bean microorganisms are inoculated into the mixture in the step A1, and the water content is adjusted to 55% to 65%, and fermented under anaerobic conditions at 25 to 35°C The required mixed anaerobic fermentation product can be obtained in 10-15 days.
前述的矸石堆场介质生境的快速改良材料中,所述钝化材料包含有钝化材料A和钝化材料B,所述钝化材料通过以下方法得到:In the aforementioned quick improvement material of waste rock stockpile medium habitat, the passivation material includes passivation material A and passivation material B, and the passivation material is obtained by the following method:
钝化材料A:将灰岩粉碎后,添加NaOH对灰岩进行改性,使其pH达9~11;Passivation material A: After the limestone is crushed, NaOH is added to modify the limestone so that its pH reaches 9-11;
钝化材料B:向粉碎后的硅石中加入NaOH混匀进行改性,并加入适量水,使硅石-NaOH体系中的含水率为40%~50%,使其pH稳定至10~11,将稳定后的改性硅石烘干至含水率为15%~20%,再向烘干后的改性硅石中加入CaO2,CaO2的加入量为烘干后的改性硅石质量的5%~12%。Passivation material B: Add NaOH to the pulverized silica and mix it evenly for modification, and add an appropriate amount of water to make the water content in the silica-
前述的矸石堆场介质生境的快速改良材料中,所述钝化材料制备过程中,将灰岩和硅石分别粉碎至50目以下。In the above-mentioned materials for rapidly improving the medium habitat of gangue yards, during the preparation process of the passivation materials, limestone and silica are respectively crushed to below 50 mesh.
前述的矸石堆场介质生境的快速改良材料中,所述灰岩中CaCO3含量为82%~90%。In the above-mentioned materials for rapidly improving the medium habitat of waste rock dumps, the content of CaCO 3 in the limestone is 82% to 90%.
一种矸石堆场介质生境的快速改良方法,具体的改良方法包括以下步骤:A method for rapidly improving the medium habitat of gangue storage yards. The specific improvement method includes the following steps:
(1)将矸石翻松,加入钝化材料A混匀,反应至pH稳定到5~6;(1) Loosen the gangue, add passivation material A and mix well, and react until the pH is stable to 5-6;
(2)再向经钝化材料A反应后的矸石中加入钝化材料B,混匀;(2) Add passivation material B to the gangue after the reaction of passivation material A, and mix evenly;
(3)再向经钝化后的矸石中加入植生改良材料,混匀即可。(3) Add the plant growth improvement material to the passivated gangue and mix evenly.
前述的矸石堆场介质生境的快速改良方法中,所述钝化材料B的加入量为矸石干重的3%~12%。In the aforementioned rapid improvement method for the medium habitat of the waste rock stockpile, the addition amount of the passivation material B is 3% to 12% of the dry weight of the waste rock.
前述的矸石堆场介质生境的快速改良方法中,所述植生改良材料的加入量为矸石干重的3%~12%。In the aforementioned rapid improvement method for the medium habitat of the waste rock stockpile, the added amount of the vegetation improvement material is 3% to 12% of the dry weight of the waste rock.
本发明的有益效果:与现有技术相比,本发明提供了一种强酸高硫高铁矸石堆场介质生境的快速改良方法及其改良材料,该方法所用的材料为豆粕和构树凋落物混合厌氧发酵物、磷矿粉和硫酸盐还原菌群;在上述组分中,豆粕的主要成分为蛋白质,赖氨酸,色氨酸,蛋氨酸,且氮磷钾及有机质含量丰富。其中,氮磷钾等的加入可直接提高土壤养分,氨基酸可直接被作物直接吸收利用,有利于养分的吸收转化及积累,同时增强土壤酶活性,加速养分转化。构树凋落物中含有糖类、蛋白质等可溶性营养物质,促进微生物的生长与繁殖。豆粕和构树凋落物经过厌氧发酵后能固定氮素,释放磷素促进微生物对磷的吸收,磷素在一定程度上会产生亏损,但磷矿粉的添加则能弥补这点不足。豆豉中的细菌组成丰富、真菌数量大,其添加能显著提升矸石堆场的微生物数量及多样性,且硫酸盐还原菌群的添加能释放碱度,提高煤矸石中的pH值,将矸石中的SO4 2-转化为S2-,S2-与金属离子形成稳定的硫化物沉淀,从而降低矸石中污染物质的释放。上述各组分合理搭配能够充分发挥多种作用,最终有效促进矸石堆场生境的改良,并能协同钝化材料一起控制煤矸石中污染物质的释放。Beneficial effects of the present invention: Compared with the prior art, the present invention provides a method for rapidly improving the medium habitat of strong-acid, high-sulfur, high-iron gangue yards and its improved materials. The material used in the method is a mixture of soybean meal and mulberry litter Anaerobic fermentation product, phosphate rock powder and sulfate-reducing bacteria group; among the above components, the main components of soybean meal are protein, lysine, tryptophan, methionine, and are rich in nitrogen, phosphorus, potassium and organic matter. Among them, the addition of nitrogen, phosphorus and potassium can directly increase soil nutrients, and amino acids can be directly absorbed and utilized by crops, which is conducive to the absorption, transformation and accumulation of nutrients, while enhancing soil enzyme activity and accelerating nutrient conversion. The mulberry litter contains soluble nutrients such as sugar and protein, which promote the growth and reproduction of microorganisms. After anaerobic fermentation, soybean meal and mulberry litter can fix nitrogen and release phosphorus to promote the absorption of phosphorus by microorganisms. Phosphorus will be lost to a certain extent, but the addition of phosphate rock powder can make up for this deficiency. Douchi is rich in bacterial composition and large in number of fungi, and its addition can significantly increase the number and diversity of microorganisms in gangue yards, and the addition of sulfate-reducing bacteria can release alkalinity, increase the pH value of gangue, and reduce the amount of microorganisms in gangue. The SO 4 2- is converted into S 2- , and S 2- forms stable sulfide precipitation with metal ions, thereby reducing the release of pollutants in gangue. The reasonable combination of the above-mentioned components can give full play to various functions, and finally effectively promote the improvement of the habitat of gangue storage yards, and can cooperate with passivation materials to control the release of pollutants in coal gangue.
附图说明Description of drawings
附图1是高硫高铁矸石(煤矸石)淋滤液pH的曲线图Accompanying drawing 1 is the graph of high sulfur and high iron gangue (coal gangue) leachate pH
附图2是高硫高铁矸石(煤矸石)淋滤液Eh的曲线图Accompanying drawing 2 is the curve diagram of high sulfur and high iron gangue (coal gangue) leachate Eh
附图3是高硫高铁矸石(煤矸石)淋滤液Fe含量的曲线图Accompanying drawing 3 is the graph of Fe content of leachate of high sulfur and high iron gangue (coal gangue)
附图4是高硫高铁矸石(煤矸石)淋滤液Mn含量的曲线图Accompanying drawing 4 is the graph of Mn content of leachate of high sulfur and high iron gangue (coal gangue)
附图5是高硫高铁矸石(煤矸石)淋滤液Cd含量的曲线图Accompanying drawing 5 is the graph of high-sulfur high-iron gangue (coal gangue) leachate Cd content curve
附图6是高硫高铁矸石(煤矸石)淋滤液Cr含量的曲线图Accompanying drawing 6 is the graph of Cr content of leachate of high sulfur and high iron gangue (coal gangue)
附图7是高硫高铁矸石(煤矸石)淋滤液Zn含量的曲线图Accompanying drawing 7 is the graph of Zn content of leachate of high sulfur and high iron gangue (coal gangue)
附图8是高硫高铁矸石(煤矸石)淋滤液Cu含量的曲线图Accompanying
附图9是高硫高铁矸石(煤矸石)淋滤液SO4 2-含量的曲线图Accompanying drawing 9 is the graph of SO 4 2- content of high-sulfur and high-iron gangue (coal gangue) leachate
附表1是改良前后对高硫高铁矸石(煤矸石)主要金属离子和SO4 2-释放的汇总表Attached Table 1 is a summary table of the main metal ions and SO 4 2- released from high-sulfur and high-iron gangue (coal gangue) before and after improvement
附表2是改良前后对高硫高铁矸石(煤矸石)介质生境状况基本指标的影响。Attached Table 2 shows the impact on the basic indicators of high-sulfur and high-iron gangue (coal gangue) medium habitat conditions before and after improvement.
具体实施方式detailed description
下面结合附图和实施例对本发明作进一步的说明,但并不作为对本发明限制的依据。The present invention will be further described below in conjunction with the accompanying drawings and embodiments, but not as a basis for limiting the present invention.
本发明的实施例1:一种矸石堆场介质生境的快速改良材料,包括有钝化材料和植生改良材料;植生改良材料按重量百分比计包含有:混合厌氧发酵物86%、磷矿粉9%和硫酸盐还原菌群5%;所述植生改良材料用以下方法制备得到:
A.混合厌氧发酵物制备A. Preparation of mixed anaerobic fermentation
A1:混合物制备:按重量百分比计将35%的豆粕和65%的构树凋落物混匀;A1: mixture preparation: by weight percentage, 35% soybean meal and 65% mulberry litter are mixed;
A2:向A1步骤的混合物中接种豆豉微生物,豆豉微生物加入量为混合物总重量的1%,调节含水量为60%,厌氧条件下30℃发酵10天得到混合厌氧发酵物;A2: inoculate fermented soya bean microorganisms in the mixture of step A1, fermented soya bean microorganisms add-on amount is 1% of the total weight of mixture, adjust water content to be 60%, ferment under anaerobic condition 30 ℃ for 10 days to obtain mixed anaerobic fermented product;
B.向步骤A的混合厌氧发酵物中加入磷矿粉和硫酸盐还原菌群,混匀得到植生改良材料。B. Add phosphate rock powder and sulfate-reducing bacteria to the mixed anaerobic fermentation product in step A, and mix well to obtain a plant growth improvement material.
所述豆豉微生物按重量百分比计包含有60%的细菌和40%的真菌。The fermented soya bean microorganism contains 60% bacteria and 40% fungus by weight percentage.
所述细菌按重量百分比计包含有:蓝细菌55%,厚壁菌37%,放线菌和变形菌共计8%;所述真菌按重量百分比计包含有:接合菌门横梗霉95%和子囊菌5%。Described bacterium comprises by weight percentage: Cyanobacteria 55%, Firmicutes 37%, Actinomycetes and Proteobacteria total 8%; Described fungi comprises by weight percentage: Zygomycota Rhizoma 95% and
所述钝化材料包含有钝化材料A和钝化材料B,所述钝化材料通过以下方法得到:Described passivation material comprises passivation material A and passivation material B, and described passivation material obtains by following method:
(1)钝化材料A:选用CaCO3含量为82%~90%的灰岩,将其粉碎至小于50目,然后添加NaOH对灰岩进行改性,使其pH值达9~11即可。(1) Passivation material A: choose limestone with a CaCO3 content of 82% to 90%, crush it to less than 50 mesh, and then add NaOH to modify the limestone so that its pH value reaches 9 to 11. .
(2)钝化材料B:将硅石粉碎至小于50目,然后加入NaOH混匀进行改性,并加入适量水,使硅石-NaOH体系中的含水率为40%~50%,使其pH稳定至10~11,再将稳定后的改性硅石烘干至含水率为15%~20%,再向烘干后的硅石中加入CaO2混匀后密封保存。加入的CaO2的量为烘干至含水率为15%~20%的改性硅石质量的10%。(2) Passivation material B: crush the silica to less than 50 mesh, then add NaOH and mix it for modification, and add an appropriate amount of water to make the water content in the silica-
一种矸石堆场介质生境的快速改良方法,具体包含以下步骤:A method for rapidly improving the medium habitat of gangue storage yards, specifically comprising the following steps:
(1)所用煤矸石废渣采自高硫高铁煤矸石堆场,采集风化煤矸石带回实验室,平铺牛皮纸上室内自然风干,过2mm筛,充分混匀。(1) The waste coal gangue used was collected from the high-sulfur and high-iron coal gangue stockpile. The weathered coal gangue was collected and brought back to the laboratory.
(2)按煤矸石的重量,向煤矸石中加入5%的钝化材料A,反应1个月,待pH稳定到5~6;(2) Add 5% passivation material A to the gangue by the weight of the gangue, react for 1 month, and wait for the pH to stabilize to 5-6;
(3)按煤矸石的重量向(2)中加入5%的钝化材料B,稳定1个月,使煤矸石系统中pH稳定到6左右;(3) add 5% passivation material B in (2) by the weight of coal gangue, stabilize for 1 month, make the pH in the gangue system stabilize to about 6;
(4)按煤矸石的重量向(3)中加入10%的植生改良材料,混匀即可。(4) Add 10% plant growth improvement material into (3) according to the weight of coal gangue, and mix well.
本发明的实施例2:一种矸石堆场介质生境的快速改良材料,包括有钝化材料和植生改良材料;植生改良材料按重量百分比计包含有:混合厌氧发酵物85%、磷矿粉10%和硫酸盐还原菌群5%;所述植生改良材料用以下方法制备得到:
A.混合厌氧发酵物制备A. Preparation of mixed anaerobic fermentation
A1:混合物制备:按重量百分比计将40%的豆粕和60%的构树凋落物混匀;A1: mixture preparation: by weight percentage, 40% soybean meal and 60% mulberry litter are mixed;
A2:向A1步骤的混合物中接种豆豉微生物,豆豉微生物加入量为混合物总重量的0.2%,调节含水量为55%,厌氧条件下25℃发酵15天得到混合厌氧发酵物;A2: Inoculate fermented soya bean microorganisms into the mixture of step A1, fermented soya bean microorganisms are added in an amount of 0.2% of the total weight of the mixture, the water content is adjusted to 55%, and fermented at 25° C. for 15 days under anaerobic conditions to obtain a mixed anaerobic fermented product;
B.向步骤A的混合厌氧发酵物中加入磷矿粉和硫酸盐还原菌群,混匀得到植生改良材料。B. Add phosphate rock powder and sulfate-reducing bacteria to the mixed anaerobic fermentation product in step A, and mix well to obtain a plant growth improvement material.
所述豆豉微生物按重量百分比计包含有45%的细菌和55%的真菌。The fermented soya bean microorganism contains 45% bacteria and 55% fungus by weight percentage.
所述细菌按重量百分比计包含有:蓝细菌50%,厚壁菌40%,放线菌和变形菌共计10%;所述真菌按重量百分比计包含有:接合菌门横梗霉90%和子囊菌10%。The bacterium comprises by weight percentage: cyanobacteria 50%,
所述钝化材料包含有钝化材料A和钝化材料B,所述钝化材料通过以下方法得到:Described passivation material comprises passivation material A and passivation material B, and described passivation material obtains by following method:
(1)钝化材料A:选用CaCO3含量为82%~90%的灰岩,将其粉碎至小于50目,然后添加NaOH对灰岩进行改性,使其pH值达9~11即可。(1) Passivation material A: choose limestone with a CaCO3 content of 82% to 90%, crush it to less than 50 mesh, and then add NaOH to modify the limestone so that its pH value reaches 9 to 11. .
(2)钝化材料B:将硅石粉碎至小于50目,然后加入NaOH混匀进行改性,并加入适量水,使硅石-NaOH体系中的含水率为40%~50%,使其pH稳定至10~11,再将稳定后的改性硅石烘干至含水率为15%~20%,再向烘干后的硅石中加入CaO2混匀后密封保存。加入的CaO2的量为烘干至含水率为15%~20%的改性硅石质量的12%。(2) Passivation material B: crush the silica to less than 50 mesh, then add NaOH and mix it for modification, and add an appropriate amount of water to make the water content in the silica-
一种矸石堆场介质生境的快速改良方法,具体包含以下步骤:A method for rapidly improving the medium habitat of gangue storage yards, specifically comprising the following steps:
(1)所用煤矸石废渣采自高硫高铁煤矸石堆场,采集风化煤矸石带回实验室,平铺牛皮纸上室内自然风干,过2mm筛,充分混匀。(1) The waste coal gangue used was collected from the high-sulfur and high-iron coal gangue stockpile. The weathered coal gangue was collected and brought back to the laboratory.
(2)按煤矸石的重量,向煤矸石中加入10%的钝化材料A,反应1个月,待pH稳定到5~6;(2) According to the weight of coal gangue, add 10% passivation material A to coal gangue, react for 1 month, and wait for pH to stabilize to 5~6;
(3)按煤矸石的重量向(2)中加入12%的钝化材料B,稳定1个月,使煤矸石系统中pH稳定到6左右;(3) add 12% passivation material B in (2) by the weight of coal gangue, stabilize for 1 month, make the pH in the gangue system stabilize to about 6;
(4)按煤矸石的重量向(3)中加入10%的植生改良材料,混匀即可。(4) Add 10% plant growth improvement material into (3) according to the weight of coal gangue, and mix well.
本发明的实施例3:一种矸石堆场介质生境的快速改良材料,包括有钝化材料和植生改良材料;植生改良材料按重量百分比计包含有:混合厌氧发酵物90%、磷矿粉9%和硫酸盐还原菌群1%;所述植生改良材料用以下方法制备得到:
A.混合厌氧发酵物制备A. Preparation of mixed anaerobic fermentation
A1:混合物制备:按重量百分比计将40%的豆粕和60%的构树凋落物混匀;A1: mixture preparation: by weight percentage, 40% soybean meal and 60% mulberry litter are mixed;
A2:向A1步骤的混合物中接种豆豉微生物,豆豉微生物加入量为混合物总重量的1%,调节含水量为65%,厌氧条件下35℃发酵10天得到混合厌氧发酵物;A2: Inoculate fermented soya bean microorganisms into the mixture of step A1, fermented soya bean microorganisms are added in an amount of 1% of the total weight of the mixture, the water content is adjusted to 65%, and fermented at 35° C. for 10 days under anaerobic conditions to obtain a mixed anaerobic fermented product;
B.向步骤A的混合厌氧发酵物中加入磷矿粉和硫酸盐还原菌群,混匀得到植生改良材料。B. Add phosphate rock powder and sulfate-reducing bacteria to the mixed anaerobic fermentation product in step A, and mix well to obtain a plant growth improvement material.
所述豆豉微生物按重量百分比计包含有75%的细菌和25%的真菌。The fermented soya bean microorganism contains 75% bacteria and 25% fungus by weight percentage.
所述细菌按重量百分比计包含有:蓝细菌60%,厚壁菌35%,放线菌和变形菌共计5%;所述真菌按重量百分比计包含有:接合菌门横梗霉100%。The bacteria include by weight percentage: 60% of cyanobacteria, 35% of Firmicutes, 5% of actinomycetes and proteobacteria in total;
所述钝化材料包含有钝化材料A和钝化材料B,所述钝化材料通过以下方法得到:Described passivation material comprises passivation material A and passivation material B, and described passivation material obtains by following method:
(1)钝化材料A:选用CaCO3含量为82%~90%的灰岩,将其粉碎至小于50目,然后添加NaOH对灰岩进行改性,使其pH值达9~11即可。(1) Passivation material A: choose limestone with a CaCO3 content of 82% to 90%, crush it to less than 50 mesh, and then add NaOH to modify the limestone so that its pH value reaches 9 to 11. .
(2)钝化材料B:将硅石粉碎至小于50目,然后加入NaOH混匀进行改性,并加入适量水,使硅石-NaOH体系中的含水率为40%~50%,使其pH稳定至10~11,再将稳定后的改性硅石烘干至含水率为15%~20%,再向烘干后的硅石中加入CaO2混匀后密封保存。加入的CaO2的量为烘干至含水率为15%~20%的改性硅石质量的5%。(2) Passivation material B: crush the silica to less than 50 mesh, then add NaOH and mix it for modification, and add an appropriate amount of water to make the water content in the silica-
一种矸石堆场介质生境的快速改良方法,具体包含以下步骤:A method for rapidly improving the medium habitat of gangue storage yards, specifically comprising the following steps:
(1)所用煤矸石废渣采自高硫高铁煤矸石堆场,采集风化煤矸石带回实验室,平铺牛皮纸上室内自然风干,过2mm筛,充分混匀。(1) The waste coal gangue used was collected from the high-sulfur and high-iron coal gangue stockpile. The weathered coal gangue was collected and brought back to the laboratory.
(2)按煤矸石的重量,向煤矸石中加入2%的钝化材料A,反应1个月,待pH稳定到5~6;(2) According to the weight of coal gangue, add 2% passivation material A to coal gangue, react for 1 month, and wait for the pH to stabilize to 5~6;
(3)按煤矸石的重量向(2)中加入3%的钝化材料B,稳定1个月,使煤矸石系统中pH稳定到6左右;(3) add 3% passivation material B in (2) by the weight of gangue, stabilize for 1 month, make the pH in the gangue system stabilize to about 6;
(4)按煤矸石的重量向(3)中加入10%的植生改良材料,混匀即可。(4) Add 10% plant growth improvement material into (3) according to the weight of coal gangue, and mix well.
本发明的实施例4:一种矸石堆场介质生境的快速改良材料,包括有钝化材料和植生改良材料;植生改良材料按重量百分比计包含有:混合厌氧发酵物87%、磷矿粉9%和硫酸盐还原菌群4%;所述植生改良材料用以下方法制备得到:
A.混合厌氧发酵物制备A. Preparation of mixed anaerobic fermentation
A1:混合物制备:按重量百分比计将35%的豆粕和65%的构树凋落物混匀;A1: mixture preparation: by weight percentage, 35% soybean meal and 65% mulberry litter are mixed;
A2:向A1步骤的混合物中接种豆豉微生物,豆豉微生物加入量为混合物总重量的1%,调节含水量为60%,厌氧条件下25℃发酵15天得到混合厌氧发酵物;A2: inoculate fermented soya bean microorganisms in the mixture of step A1, fermented soya bean microorganisms add-on amount is 1% of mixture gross weight, adjust water content to be 60%, under anaerobic condition 25 ℃ ferment 15 days to obtain mixed anaerobic fermented product;
B.向步骤A的混合厌氧发酵物中加入磷矿粉和硫酸盐还原菌群,混匀得到植生改良材料。B. Add phosphate rock powder and sulfate-reducing bacteria to the mixed anaerobic fermentation product in step A, and mix well to obtain a plant growth improvement material.
所述豆豉微生物按重量百分比计包含有55%的细菌和45%的真菌。The fermented soya bean microorganism contains 55% bacteria and 45% fungus by weight percentage.
所述细菌按重量百分比计包含有:蓝细菌55%,厚壁菌40%,放线菌和变形菌共计5%;所述真菌按重量百分比计包含有:接合菌门横梗霉95%和子囊菌5%。Described bacterium comprises by weight percentage: Cyanobacteria 55%,
所述钝化材料包含有钝化材料A和钝化材料B,所述钝化材料通过以下方法得到:Described passivation material comprises passivation material A and passivation material B, and described passivation material obtains by following method:
(1)钝化材料A:选用CaCO3含量为82%~90%的灰岩,将其粉碎至小于50目,然后添加NaOH对灰岩进行改性,使其pH值达9~11即可。(1) Passivation material A: choose limestone with a CaCO3 content of 82% to 90%, crush it to less than 50 mesh, and then add NaOH to modify the limestone so that its pH value reaches 9 to 11. .
(2)钝化材料B:将硅石粉碎至小于50目,然后加入NaOH混匀进行改性,并加入适量水,使硅石-NaOH体系中的含水率为40%~50%,使其pH稳定至10~11,再将稳定后的改性硅石烘干至含水率为15%~20%,再向烘干后的硅石中加入CaO2混匀后密封保存。加入的CaO2的量为烘干至含水率为15%~20%的改性硅石质量的7%。(2) Passivation material B: crush the silica to less than 50 mesh, then add NaOH and mix it for modification, and add an appropriate amount of water to make the water content in the silica-
一种矸石堆场介质生境的快速改良方法,具体包含以下步骤:A method for rapidly improving the medium habitat of gangue storage yards, specifically comprising the following steps:
(1)所用煤矸石废渣采自高硫高铁煤矸石堆场,采集风化煤矸石带回实验室,平铺牛皮纸上室内自然风干,过2mm筛,充分混匀。(1) The waste coal gangue used was collected from the high-sulfur and high-iron coal gangue stockpile. The weathered coal gangue was collected and brought back to the laboratory.
(2)按煤矸石的重量,向煤矸石中加入7%的钝化材料A,反应1个月,待pH稳定到5~6;(2) Add 7% passivation material A to the gangue by the weight of the gangue, react for 1 month, and wait for the pH to stabilize to 5-6;
(3)按煤矸石的重量向(2)中加入7%的钝化材料B,稳定1个月,使煤矸石系统中pH稳定到6左右;(3) add 7% passivation material B in (2) by the weight of coal gangue, stabilize for 1 month, make the pH in the gangue system stabilize to about 6;
(4)按煤矸石的重量向(3)中加入5%的植生改良材料,混匀即可。(4) Add 5% plant growth improvement material into (3) according to the weight of coal gangue, and mix well.
本发明的实施例5:一种矸石堆场介质生境的快速改良材料,包括有钝化材料和植生改良材料;植生改良材料按重量百分比计包含有:混合厌氧发酵物88%、磷矿粉10%和硫酸盐还原菌群2%;所述植生改良材料用以下方法制备得到:
A.混合厌氧发酵物制备A. Preparation of mixed anaerobic fermentation
A1:混合物制备:按重量百分比计将55%的豆粕和45%的构树凋落物混匀;A1: mixture preparation: by weight percentage, 55% soybean meal and 45% mulberry litter are mixed;
A2:向A1步骤的混合物中接种豆豉微生物,豆豉微生物加入量为混合物总重量的1.5%,调节含水量为60%,厌氧条件下35℃发酵10天得到混合厌氧发酵物;A2: inoculate fermented soya bean microorganism in the mixture of A1 step, fermented soya bean microorganism add-on amount is 1.5% of mixture gross weight, adjust water content to be 60%, 35 ℃ of fermentations under anaerobic condition obtain mixed anaerobic fermentation product for 10 days;
B.向步骤A的混合厌氧发酵物中加入磷矿粉和硫酸盐还原菌群,混匀得到植生改良材料。B. Add phosphate rock powder and sulfate-reducing bacteria to the mixed anaerobic fermentation product in step A, and mix well to obtain a plant growth improvement material.
所述豆豉微生物按重量百分比计包含有65%的细菌和35%的真菌。The fermented soya bean microorganism contains 65% bacteria and 35% fungus by weight percentage.
所述细菌按重量百分比计包含有:蓝细菌58%,厚壁菌32%,放线菌和变形菌共计10%;所述真菌按重量百分比计包含有:接合菌门横梗霉93%和子囊菌7%。Described bacterium comprises by weight percentage: Cyanobacteria 58%, Firmicutes 32%, Actinomycetes and Proteobacteria total 10%; Described fungus comprises by weight percentage: Zygomycota Rhizoma 93% and
所述钝化材料包含有钝化材料A和钝化材料B,所述钝化材料通过以下方法得到:Described passivation material comprises passivation material A and passivation material B, and described passivation material obtains by following method:
(1)钝化材料A:选用CaCO3含量为82%~90%的灰岩,将其粉碎至小于50目,然后添加NaOH对灰岩进行改性,使其pH值达9~11即可。(1) Passivation material A: choose limestone with a CaCO3 content of 82% to 90%, crush it to less than 50 mesh, and then add NaOH to modify the limestone so that its pH value reaches 9 to 11. .
(2)钝化材料B:将硅石粉碎至小于50目,然后加入NaOH混匀进行改性,并加入适量水,使硅石-NaOH体系中的含水率为40%~50%,使其pH稳定至10~11,再将稳定后的改性硅石烘干至含水率为15%~20%,再向烘干后的硅石中加入CaO2混匀后密封保存。加入的CaO2的量为烘干至含水率为15%~20%的改性硅石质量的7%。(2) Passivation material B: crush the silica to less than 50 mesh, then add NaOH and mix it for modification, and add an appropriate amount of water to make the water content in the silica-
一种矸石堆场介质生境的快速改良方法,具体包含以下步骤:A method for rapidly improving the medium habitat of gangue storage yards, specifically comprising the following steps:
(1)所用煤矸石废渣采自高硫高铁煤矸石堆场,采集风化煤矸石带回实验室,平铺牛皮纸上室内自然风干,过2mm筛,充分混匀。(1) The waste coal gangue used was collected from the high-sulfur and high-iron coal gangue stockpile. The weathered coal gangue was collected and brought back to the laboratory.
(2)按煤矸石的重量,向煤矸石中加入5%的钝化材料A,反应1个月,待pH稳定到5~6;(2) Add 5% passivation material A to the gangue by the weight of the gangue, react for 1 month, and wait for the pH to stabilize to 5-6;
(3)按煤矸石的重量向(2)中加入5%的钝化材料B,稳定1个月,使煤矸石系统中pH稳定到6左右;(3) add 5% passivation material B in (2) by the weight of coal gangue, stabilize for 1 month, make the pH in the gangue system stabilize to about 6;
(4)按煤矸石的重量向(3)中加入5%的植生改良材料,混匀即可。(4) Add 5% plant growth improvement material into (3) according to the weight of coal gangue, and mix well.
为了论证该植生改良方法对矸石(煤矸石)中最主要金属离子和SO4 2-释放和生境改良的影响,我方进行了相关试验。分别取上述5个实施例钝化处理后的煤矸石进行试验。试验过程中为:In order to demonstrate the effect of this vegetation improvement method on the release of the most important metal ions and SO 4 2- in gangue (coal gangue) and the improvement of habitat, we have carried out relevant experiments. The coal gangue after the passivation treatment of the above five embodiments were respectively taken for testing. During the test:
(1)将加入了钝化材料的煤矸石和未加入钝化材料煤矸石分别填满长50cm,直径为110mm的淋滤柱中,取当地一年的降雨量,采用淋滤的方式分五次分别对加入了植生改良材料的煤矸石和未加入任何改良材料煤矸石进行淋滤,以未添加任何改良材料的煤矸石作为对照(CK)。(1) Fill the leaching column with a length of 50 cm and a diameter of 110 mm with coal gangue added with passivation material and coal gangue without passivation material, and take the annual rainfall in the local area, and divide it into five parts by leaching The coal gangue added with vegetation improvement materials and the coal gangue without any improved materials were leached respectively, and the coal gangue without any improved materials was used as the control (CK).
(2)每次淋滤试验结束后,分析煤矸石淋出液pH、Eh、Fe、Mn以及主要重金属和SO4 2-等指标的变化。(2) After each leaching test, analyze the changes of coal gangue leachate pH, Eh, Fe, Mn, main heavy metals and SO 4 2- and other indicators.
在上述试验中,没有加入任何改良材料和加入了植生改良材料的煤矸石试验均设置3次重复,以减小试验误差。In the above experiments, three repetitions were set for the coal gangue experiment without any improved material and with the addition of vegetation improved material to reduce the experimental error.
其中实施例1的试验数据如表1、表2和附图1-9所示。Wherein the test data of
表1改良前后对高硫高铁矸石(煤矸石)中最主要金属离子和SO4 2-释放的影响Table 1 Effects of the most important metal ions and SO 4 2- release in high-sulfur and high-iron gangue (coal gangue) before and after improvement
表2改良前后对高硫高铁矸石(煤矸石)介质基本理化指标的影响Table 2 Effects on basic physical and chemical indicators of high-sulfur and high-iron gangue (coal gangue) medium before and after improvement
如附图和表所示,结果表明,添加植生改良材料可降低了煤矸石中主要金属离子和SO4 2-的溶出,且降低了淋滤液的淋出量、Eh、Fe、Mn、Cu、Zn、Cd、Cr以及SO4 2-的含量,提高淋滤液的pH值,使其呈碱性或偏碱性,并提高煤矸石介质中的氮素、磷素和速效钾含量,提高细菌、真菌、放线菌的含量,提高煤矸石pH值,降低土壤容重。以上试验结果表明,采用本发明的植生改良材料和方法成功实现对煤矸石生境进行改良,改良效果显著,同时减少煤矸石中污染物质的释放。As shown in the accompanying drawings and tables, the results show that adding vegetation improvement materials can reduce the dissolution of main metal ions and SO 4 2- in coal gangue, and reduce the leaching amount of leachate, Eh, Fe, Mn, Cu, The content of Zn, Cd, Cr and SO 4 2- can increase the pH value of the leachate to make it alkaline or slightly alkaline, and increase the content of nitrogen, phosphorus and available potassium in the gangue medium, and increase the bacteria, Increase the content of fungi and actinomycetes, increase the pH value of coal gangue, and reduce soil bulk density. The above test results show that the improvement of the coal gangue habitat is successfully achieved by using the vegetation improvement material and method of the present invention, the improvement effect is remarkable, and at the same time, the release of pollutants in the coal gangue is reduced.
其它实施例的试验结果与实施1的试验结构相类似,结果表明,本发明所提供一种矸石堆场介质生境的快速改良材料及其方法,能够有效地实现对煤矸石生境进行改良,改良效果显著,同时减少煤矸石中污染物质的释放。The test results of other embodiments are similar to the test structure of
以上只是本发明的具体应用范例,本发明还有其他的实施方式,凡采用等同替换或等效变换形成的技术方案,均落在本发明所要求的保护范围之内。The above are only specific application examples of the present invention. The present invention also has other implementation modes. All technical solutions formed by equivalent replacement or equivalent transformation fall within the scope of protection required by the present invention.
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