CN102399111A - Greening matrix and phytoremediation technology method of pulverized coal gangue - Google Patents
Greening matrix and phytoremediation technology method of pulverized coal gangue Download PDFInfo
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Abstract
本发明涉及固体废弃物污染环境的植物修复技术,具体地说是公开了一种煤矸石粉碎物绿化基质和植物绿化煤矸石山的生态恢复技术,主要是利用煤矸石粉碎物和土壤的混合物作为绿化基质,其中煤矸石与南方营养土花土的体积比为:1∶2~2∶1(即煤矸石体积占1/3~1/2);种植重金属非累积植物烟草和Cd累积植物龙葵,从而实现煤矸石山绿化和生态恢复的目的。这种利用煤矸石固体废弃物基质的植物修复技术的使用,可有效地改善煤矿区的空气质量和生态环境。The present invention relates to the phytoremediation technology of the environment polluted by solid waste, and specifically discloses an ecological restoration technology for the greening matrix of crushed coal gangue and the greening of coal gangue hills by plants, mainly using the mixture of crushed coal gangue and soil as the Greening substrate, in which the volume ratio of coal gangue to southern nutrient soil and flower soil is: 1:2~2:1 (that is, the volume of coal gangue accounts for 1/3~1/2); plant heavy metal non-accumulating plant tobacco and Cd accumulating plant dragon Sunflower, so as to achieve the purpose of greening and ecological restoration of coal gangue hills. The use of this phytoremediation technology using coal gangue solid waste matrix can effectively improve the air quality and ecological environment in coal mining areas.
Description
技术领域: Technical field:
本发明涉及一种煤矿区煤矸石山生态恢复基质和植物修复技术,具体是指煤矸石山的植被绿化技术。The invention relates to a coal gangue hill ecological restoration matrix and plant restoration technology in a coal mining area, in particular to the vegetation greening technology of the coal gangue hill.
背景技术: Background technique:
煤炭是我国重要的能源物质之一,2007年全国的原煤产量达25.5亿吨。煤矸石是煤炭开采和加工过程中的固体废弃物,其产量占原煤的10%~30%。由于受资源性质、经济条件、技术设备以及市场变化的影响,目前我国煤矸石的利用率还不到30%。虽有一部分煤矸石可被再利用为建材、燃料,但工业综合利用率仍不到5%。所以,大部分煤矸石均采取地面定点堆放方式处置。随着社会对能源需求量的增加,煤炭资源的开采和加工量随之提高,煤矸石的不断排放堆积,形成大小不一的矸石山数千座,成为最大的工业固体废弃物源。Coal is one of the important energy sources in my country. In 2007, the national raw coal output reached 2.55 billion tons. Coal gangue is solid waste in the process of coal mining and processing, and its output accounts for 10% to 30% of raw coal. Due to the impact of resource properties, economic conditions, technical equipment and market changes, the utilization rate of coal gangue in my country is less than 30%. Although some coal gangue can be reused as building materials and fuels, the comprehensive industrial utilization rate is still less than 5%. Therefore, most of the coal gangue are disposed of in the way of fixed-point stacking on the ground. With the increase of society's demand for energy, the amount of mining and processing of coal resources has also increased, and the continuous discharge and accumulation of coal gangue has formed thousands of gangue hills of different sizes, becoming the largest source of industrial solid waste.
煤矸石主要有掘井巷时排出的煤矸石、选煤排出的煤矸石和露天采煤产生的剥离煤矸石,矿物成分较为复杂,通常为石英、云母、黏土(伊利石和高岭石)、硫铁矿(FeS2)以及钙、镁和铁的碳酸盐,主要化学元素为硅、铝、铁、钙、钛、硫、钾、镁和钠的氧化物,还有Cr、Cd,、Co、Cu,、Mn、Pb和Zn等重金属。煤矸石山的露天堆放极易发生自燃,自燃的物质主要是煤粉和可燃物硫,硫主要以硫铁矿形式存在。硫铁矿是在缺氧还原条件下生成的晶体结构,赋存于煤层及煤系地层之中,开采后暴露于空气中,由于其燃点低、耗氧量小、氧化放热量大,通过自然风化雨淋作用和微生物的催化作用,在适宜的水和空气条件下率先发生氧化反应,并释放热量,热积累使矸石山内部的温度逐渐升高引发自燃,进而导致爆炸和滑坡碎屑流等灾害,造成重大人员伤亡和财产损失!矸石山自燃释放大量的有刺激性气体气体,如CO、SO2、H2S和NO2,引起煤矿区人类呼吸道、癌症等疾病增加。同时,硫化物气体进而导致酸雨产生,形成的可溶性硫酸盐使周围环境的水质和土壤严重酸化。特别是硫铁矿在氧化过程中,其中的Fe2+被氧化成Fe3+,在水中水解形成Fe(OH)3,向水中释放更多的H+,降低了煤矸石风化物环境的pH值,加速了硫杆菌对硫和铁的氧化过程,SO4 2-累积淋溶形成酸性废水。此外,煤矸石除含黄铁矿外,还有部分硫化矿物,如白铁矿、磁黄铁矿、方铅矿、闪锌矿、黄铜矿、辉钼矿和针镍矿等,也是酸性废水的一个重要来源,相应的重金属如Mn、Pb、Cu、Zn和Mo等则被淋溶出来。降水则导致酸性废水和淋溶的重金属向山下和周边土壤、河流迁移,致使矸石山和周边土壤严重酸化和活性重金属的累积,矸石山变成了光秃秃的黑山!土壤植被破坏,矿区生态环境恶化。因此,矸石山的绿化治理是煤矿区生态环境改善的关键。Coal gangue mainly includes coal gangue discharged from well digging, coal gangue discharged from coal preparation and stripped coal gangue produced by open-pit coal mining. The mineral composition is relatively complex, usually quartz, mica, clay (illite and kaolinite), sulfur Iron ore (FeS2) and carbonates of calcium, magnesium and iron, the main chemical elements are oxides of silicon, aluminum, iron, calcium, titanium, sulfur, potassium, magnesium and sodium, as well as Cr, Cd, Co, Heavy metals such as Cu, Mn, Pb and Zn. The open-air stacking of coal gangue is very prone to spontaneous combustion, and the spontaneous combustion is mainly coal powder and combustible sulfur, and the sulfur mainly exists in the form of pyrite. Pyrite is a crystal structure formed under the condition of anoxic reduction. It occurs in coal seams and coal-measure strata. After mining, it is exposed to the air. The weathering rain effect and the catalysis of microorganisms take the lead in oxidation reaction under suitable water and air conditions, and release heat. The heat accumulation gradually increases the temperature inside the gangue hill, triggering spontaneous combustion, which in turn leads to explosions and landslide debris flows, etc. Disaster, causing heavy casualties and property damage! Spontaneous combustion of gangue dumps releases a large amount of irritating gases, such as CO, SO 2 , H 2 S and NO 2 , causing an increase in human respiratory and cancer diseases in coal mining areas. At the same time, sulfide gas leads to acid rain, and the soluble sulfate formed seriously acidifies the water quality and soil in the surrounding environment. Especially during the oxidation process of pyrite, the Fe 2+ in it is oxidized to Fe 3+ , which is hydrolyzed in water to form Fe(OH) 3 , which releases more H + into the water and lowers the pH of coal gangue weathered environment value, accelerated the oxidation process of sulfur and iron by Thiobacillus, and SO 4 2- accumulated and leached to form acidic wastewater. In addition, in addition to pyrite, coal gangue also contains some sulfide minerals, such as marcasite, pyrrhotite, galena, sphalerite, chalcopyrite, molybdenite and goethite, etc., which are also acidic. An important source of wastewater, the corresponding heavy metals such as Mn, Pb, Cu, Zn and Mo are leached out. Precipitation causes acid waste water and leached heavy metals to migrate to the downhill and surrounding soil and rivers, resulting in severe acidification and accumulation of active heavy metals in the gangue dump and surrounding soil, turning the gangue dump into a bare black mountain! The soil vegetation is destroyed, and the ecological environment of the mining area deteriorates. Therefore, the greening treatment of gangue hills is the key to the improvement of the ecological environment in coal mining areas.
矿区土地复垦和矸石山绿化是在国际上备受关注的研究领域,矸石山植被重建是矿区生态恢复的最佳策略。为了从源头控制矸石山黄铁矿氧化、防止酸性废水的产生、重金属的淋溶、表层风化物颗粒扬尘以及提高表层风化物的土壤肥力,多年来,国内外尝试了多种治理技术。如无覆土造林技术;黄土、污泥或堆肥覆盖技术阻止氧气和水向活性硫化物的渗透;投加氧化亚铁硫杆菌杀菌剂抑制黄铁矿生物氧化;煤矸石表面包膜钝化处理技术抑制黄铁矿氧化;投加粉煤灰和碱性物质(如NaOH、石灰石、生石灰、NaCO3)提高淋滤液pH,促进重金属沉淀、抑制黄铁矿的氧化和重金属的淋溶。由于污泥、粉煤灰和石灰石等有二次污染的风险,杀菌剂效果低、持续时间短,目前,矸石山依然是采用整型机械碾压后覆盖黄土的技术,然后,通过种草植树,人工构建植物生态系统,改善矸石山及其周围地区的生态环境。目前,我国的土地复垦率只有10%左右,原因之一是缺乏有效的固体废弃物处理技术和生态恢复技术。利用煤矸石作为绿化基质,种植生物量大的耐重金属的植物,既可以变废为宝,又可以扩大矿区绿化面积,使矿区的植被生态环境逐渐得以恢复,这一技术的应用对于矿区生态环境的改善和可持续发展具有重要意义。Land reclamation in mining areas and greening of gangue hills are research fields that have attracted much attention internationally, and vegetation reconstruction of waste rock hills is the best strategy for ecological restoration in mining areas. In order to control the oxidation of gangue pyrite from the source, prevent the generation of acid wastewater, the leaching of heavy metals, the dusting of surface weathered particles, and improve the soil fertility of surface weathered materials, various treatment technologies have been tried at home and abroad for many years. Such as no-covering soil afforestation technology; loess, sludge or compost covering technology to prevent the penetration of oxygen and water to active sulfide; adding Thiobacillus ferrooxidans fungicide to inhibit pyrite biooxidation; coal gangue surface coating passivation treatment technology Inhibit the oxidation of pyrite; add fly ash and alkaline substances (such as NaOH, limestone, quicklime, NaCO3) to increase the pH of the leachate, promote the precipitation of heavy metals, and inhibit the oxidation of pyrite and the leaching of heavy metals. Due to the risk of secondary pollution from sludge, fly ash and limestone, etc., the effect of fungicides is low and the duration is short. At present, gangue hills are still covered with loess after being rolled by plastic machinery, and then planted with grass and trees. , artificially build a plant ecosystem, and improve the ecological environment of the gangue dump and its surrounding areas. At present, the land reclamation rate in my country is only about 10%. One of the reasons is the lack of effective solid waste treatment technology and ecological restoration technology. Using coal gangue as a greening substrate and planting heavy metal-resistant plants with large biomass can not only turn waste into treasure, but also expand the greening area of the mining area, so that the vegetation ecological environment of the mining area can be gradually restored. The application of this technology is very important for the ecological environment of the mining area. The improvement and sustainable development are of great significance.
煤矸石粉碎物绿化基质和植物复垦技术方法,确定了复垦环境中适于植被生长的最佳煤矸石粉碎物与土壤基质混合比例范围,为降低矿山复垦的覆土量和复垦成本提供了有效方法。本方法探索出的适合生物量大的重金属非累积植物烟草(Nicotiana tabacu)和Cd累积植物龙葵(Solanum nigrum)生长的煤矸石粉碎物基质绿化技术,为煤矸石山复垦和绿化提供科学依据和技术支持。The greening matrix of crushed coal gangue and the technical method of plant reclamation have determined the optimum mixing ratio range of crushed coal gangue and soil matrix suitable for vegetation growth in the reclamation environment, providing a basis for reducing the amount of soil covering and reclamation costs for mine reclamation effective method. This method explores the greening technology of crushed coal gangue matrix suitable for the growth of heavy metal non-accumulating plant tobacco (Nicotiana tabacu) and Cd accumulating plant Solanum nigrum, which provides a scientific basis for reclamation and greening of coal gangue hills and technical support.
发明内容: Invention content:
本发明的目的在于提供一种煤矸石粉碎物绿化基质和植物复垦技术方法。该煤矸石粉碎物绿化基质的应用,不仅能为植物提供部分营养元素,而且防止土壤板结,提高烟草和龙葵植物的生物量;两种植物在煤矸石绿化基质中的生长和绿化技术为煤矸石山的复垦绿化提供了一条新路子。The object of the present invention is to provide a kind of coal gangue pulverized material greening substrate and plant reclamation technology method. The application of the coal gangue greening matrix can not only provide some nutrients for plants, but also prevent soil compaction and increase the biomass of tobacco and black nightshade plants; the growth and greening technology of the two plants in the coal gangue greening matrix are coal The reclamation and greening of gangue dumps provides a new way.
为了实现上述目的,本发明采用的技术方案是:In order to achieve the above object, the technical scheme adopted in the present invention is:
一种煤矸石粉碎物绿化基质,主要是利用煤矸石粉碎物作为基质,土壤选自长春花土厂生产的南方营养土(理化指标:粒度3.0-6.5mm,pH 4.5-5.5,有机质50%,氮300-600mg/kg,磷150-300mg/kg,钾300-500mg/kg,含水量45-55%),用于绿植、花卉、盆栽、种子、植物和园艺用品等。在煤矸石和土壤配制的煤矸石粉碎物基质中,煤矸石∶土壤=1∶2~2∶1,即煤矸石占煤矸石粉碎物基质的体积比为1/3~1/2,土壤占煤矸石粉碎物基质的体积比为1/3~1/2。A kind of greening matrix of crushed coal gangue mainly uses the crushed coal gangue as a substrate, and the soil is selected from the southern nutrient soil produced by Changchun Flower Soil Factory (physical and chemical indicators: particle size 3.0-6.5mm, pH 4.5-5.5,
植物复垦技术方法,主要是在该基质中种植重金属非累积植物烟草和重金属Cd累积植物龙葵。The technical method of plant reclamation is mainly to plant the heavy metal non-accumulating plant tobacco and the heavy metal Cd accumulating plant Solanum nigrum in the matrix.
附图说明: Description of drawings:
图1:烟草在不同煤矸石基质中的生长(图例中0、1/3、1/2、2/3和1分别表示煤矸石占煤矸石粉碎物基质的体积比);Figure 1: Growth of tobacco in different gangue matrices (0, 1/3, 1/2, 2/3 and 1 in the legend represent the volume ratios of gangue to gangue pulverized matrices respectively);
图2:烟草在不同煤矸石基质中的生物量和株高Figure 2: Tobacco biomass and plant height in different gangue matrices
图3:龙葵在不同煤矸石基质中的生长(图例中0、2/3和1分别表示煤矸石占煤矸石粉碎物基质的体积比);Figure 3: Growth of Solanum nigrum in different gangue substrates (0, 2/3 and 1 in the legend represent the volume ratio of gangue to the crushed gangue substrate respectively);
图4:在不同煤矸石基质中的生物量和株高;Figure 4: Biomass and plant height in different gangue matrices;
具体实施方式 Detailed ways
实例1烟草盆栽实验Example 1 Tobacco Pot Experiment
煤矸石样品采自安徽淮南矸石山,土壤选自南方营养土。煤矸石粉碎物绿化基质主要是利用煤矸石作为基质,煤矸石粉碎后过2mm筛,煤矸石样品与土壤混合即为煤矸石粉碎物绿化基质。煤矸石粉碎物与土壤按照0∶1、1∶2、1∶1、2∶1和1∶0等不同比例混合,使煤矸石占绿化基质的体积比分别达:0、1/3、1/2、2/3和1,装入15cm×13cm塑料盆中,浇水后进行播种。2009年5月27日播种烟草NC89,30天时间苗,每盆留2颗健壮幼苗;烟草生长3月时,从盆中取出两颗烟草植株,测定不同配比煤矸石基质中烟草的株高和生物量。实验地点设在中国矿业大学(北京)温室,在烟草生长期间根据盆缺水情况,不定期浇水。The coal gangue samples were collected from gangue hills in Huainan, Anhui, and the soil was selected from southern nutrient soil. The greening matrix of pulverized coal gangue mainly uses gangue as the matrix. After the crushed coal gangue passes through a 2mm sieve, the mixed gangue sample and soil are the greening matrix of pulverized coal gangue. The pulverized coal gangue and soil are mixed according to different ratios of 0:1, 1:2, 1:1, 2:1 and 1:0, so that the volume ratio of coal gangue to the greening matrix reaches: 0, 1/3, 1 /2, 2/3 and 1, put into 15cm×13cm plastic pots, and sow after watering. Tobacco NC89 was sown on May 27, 2009, seedlings were planted within 30 days, and 2 healthy seedlings were left in each pot; when the tobacco grew for 3 months, two tobacco plants were taken out of the pot, and the plant height of tobacco in different proportions of coal gangue matrix was measured and biomass. The experiment site was set in the greenhouse of China University of Mining and Technology (Beijing), and watering was performed irregularly during the tobacco growth period according to the water shortage in the basin.
实验结果如下:The experimental results are as follows:
烟草是植物领域研究的模式植物,易于组织培养和基因转化,不耐重金属。自09年5月27日播种至09年8月26日收获,生长约90天(图1)。播种23天时,全矸石基质中的幼苗烟草较小,而其他煤矸石粉碎物绿化基质中烟草幼苗比较一致,表明烟草可以利用煤矸石基质中的部分营养物质。62天时,从左至右随着煤矸石含量的不断提高,烟草株高的变化表现为先升高后降低的趋势。其中1/2~2/3矸石基质的烟草长势最好,株高大于全土壤的烟草,全矸石基质中幼苗叶片发黄、生长弱小。表明1/3~2/3的煤矸石绿化基质可改善土壤结构促进烟草幼苗前期的生长,而全矸石基质环境营养物质贫瘠不能满足烟草生长的需要。烟草生长90天时(图2),全煤矸石基质中烟草的生物量和株高很小,显著低于1/3~2/3的煤矸石绿化基质和全土壤;1/3~2/3的煤矸石绿化基质中烟草的生物量和株高分别达到全土壤中的烟草生物量和株高的75%和50%,但其下部叶片发黄干死,这可能是由于烟草生长后期需要大量的营养物质,而煤矸石基质养分缺乏所致。所以,如果要完成烟草整个生育期的生长,在生长后期必需施加一定的肥料。表明1/3~2/3的煤矸石绿化基质能促进烟草幼苗的前期生长,烟草可以用于煤矸石山的绿化治理。Tobacco is a model plant for plant research, easy for tissue culture and gene transformation, and not resistant to heavy metals. From sowing on May 27, 2009 to harvesting on August 26, 2009, it grew for about 90 days (Fig. 1). At 23 days after sowing, the tobacco seedlings in the whole gangue matrix were smaller, while the tobacco seedlings in the greening matrix of other crushed coal gangue were more consistent, indicating that tobacco could use part of the nutrients in the gangue matrix. At 62 days, from left to right, with the continuous increase of coal gangue content, the change of tobacco plant height showed a trend of first increasing and then decreasing. Among them, 1/2-2/3 of the gangue substrate grows best, and the plant height is higher than that of the whole soil. The leaves of the seedlings in the whole gangue substrate are yellow and weak. It indicated that 1/3~2/3 of the gangue greening substrate can improve the soil structure and promote the growth of tobacco seedlings in the early stage, while the whole gangue substrate is poor in nutrients and cannot meet the needs of tobacco growth. When the tobacco was grown for 90 days (Figure 2), the biomass and plant height of the tobacco in the whole gangue substrate were very small, significantly lower than 1/3-2/3 of the gangue greening substrate and the whole soil; 1/3-2/3 The biomass and plant height of tobacco in the gangue greening matrix reached 75% and 50% of the tobacco biomass and plant height in the whole soil respectively, but the lower leaves turned yellow and dried, which may be due to the need for a large amount of tobacco in the later stage of growth Nutrients, but due to the lack of nutrients in the gangue matrix. Therefore, if the growth of the entire growth period of tobacco is to be completed, certain fertilizers must be applied in the late growth period. It shows that 1/3~2/3 of coal gangue greening substrate can promote the early growth of tobacco seedlings, and tobacco can be used for greening treatment of coal gangue hills.
实例2龙葵盆栽实验Example 2 Solanum nigrum pot experiment
煤矸石样品采自安徽的矸石山,土壤选自南方营养土。煤矸石粉碎物绿化基质主要是利用煤矸石作为基质,煤矸石样品过2mm筛,与土壤混合即为煤矸石粉碎物绿化基质。煤矸石粉碎物与土壤按照0∶1、2∶1和1∶0等不同比例混合,使煤矸石占绿化基质的体积比分别达:0、2/3和1;装盆浇水后,于2009年6月3日播种龙葵,每盆播撒10粒种子,上覆一层薄土。在其生长期间根据盆缺水情况,不定期浇水。生长3月时,测定不同配比煤矸石基质中龙葵的株高和生物量。Coal gangue samples were collected from gangue hills in Anhui, and the soil was selected from southern nutrient soil. The greening matrix of pulverized coal gangue mainly uses coal gangue as the matrix, and the coal gangue sample is passed through a 2mm sieve and mixed with soil to form the greening matrix of pulverized coal gangue. The pulverized coal gangue and the soil are mixed according to different ratios of 0:1, 2:1 and 1:0, so that the volume ratio of coal gangue to the greening matrix reaches: 0, 2/3 and 1 respectively; Sow nightshade on June 3, 2009, sow 10 seeds per pot, and cover with a thin layer of soil. During its growth period, according to the lack of water in the pot, water it irregularly. When growing for 3 months, the plant height and biomass of Solanum nigrum in different proportions of coal gangue matrix were measured.
实验结果如下:The experimental results are as follows:
烟草是重金属敏感植物,从实例1得知1/3~2/3的煤矸石基质适用于烟草幼苗前期的生长。龙葵是重金属Cd累积植物,对Cd污染土壤的植物修复具有很大的应用潜力。煤矸石中含有微量的重金属,为了研究其对2/3煤矸石的修复能力,分析龙葵在0、2/3和1煤矸石基质中的生长和生物量。龙葵在不同的煤矸石基质中长势差异明显(图3),如生长40天时,龙葵在全矸石基质中的叶片始终发黄、弱小,而全土壤和2/3矸石基质中的龙葵叶片均保持绿色,且2/3矸石基质中的龙葵株高和生物量最大,明显高于全土壤和全矸石基质的植株。生长约3月时,不同基质中的龙葵均开花结果(图3),其中2/3矸石基质中龙葵的株高明显高于全土壤和全矸石基质中的植株(图4),但其侧枝分支和花果明显少于全土壤基质中的植株;全土壤基质中的龙葵枝繁叶茂,果实累累;全矸石基质中的龙葵植株矮小,分支和花果甚少,但毕竟能利用煤矸石中营养物质完成其整个生育期的生长,说明龙葵对煤矸石的修复能力高于烟草。生物量(图4)分析表明2/3矸石基质中龙葵的鲜重可达全土壤的66%,说明2/3的煤矸石基质可促进龙葵的前期生长。在开花结果期由于煤矸石养分的缺乏不能满足生长需要,所以2/3的煤矸石基质中龙葵分支少,与烟草盆栽试验结论一致。因此,在2/3煤矸石植被恢复过程中,适时添加肥料可以促进复垦植物的长期生长和开花结果。Tobacco is a heavy metal-sensitive plant. From Example 1, it is known that 1/3-2/3 of the gangue substrate is suitable for the growth of tobacco seedlings in the early stage. Solanum nigrum is a heavy metal Cd accumulating plant and has great application potential for phytoremediation of Cd-contaminated soil. Coal gangue contains trace amounts of heavy metals. In order to study its ability to repair 2/3 gangue, the growth and biomass of nightshade in 0, 2/3 and 1 gangue substrates were analyzed. The growth of nightshade in different gangue substrates is significantly different (Figure 3). For example, after 40 days of growth, the leaves of nightshade in the whole gangue substrate are always yellow and weak, while the leaves of nightshade in the whole soil and 2/3 gangue substrate The leaves remained green, and the plant height and biomass of Solanum nigrum in 2/3 gangue substrate were the largest, which were significantly higher than those in the whole soil and gangue substrate. When growing for about 3 months, the nightshade in different substrates all bloomed and bear fruit (Fig. 3), and the plant height of Solanum nigrum in 2/3 gangue substrate was significantly higher than that in the whole soil and the whole gangue substrate (Fig. 4), but Its side branches and flowers and fruits are obviously less than those in the whole soil matrix; the nightshade in the whole soil matrix is luxuriant in branches and leaves, and the fruits are numerous; the plants in the whole gangue matrix are short, with few branches, flowers and fruits, but after all It can use the nutrients in coal gangue to complete its growth throughout the growth period, which shows that nightshade has a higher repairing ability to coal gangue than tobacco. Biomass (Fig. 4) analysis shows that the fresh weight of Solanum nigrum in 2/3 gangue matrix can reach 66% of the whole soil, indicating that 2/3 of gangue matrix can promote the early growth of Solanum nigrum. During the flowering and fruiting period, because the lack of coal gangue nutrients can not meet the growth needs, 2/3 of the gangue matrix has fewer branches of nightshade, which is consistent with the conclusion of the tobacco pot experiment. Therefore, in the process of 2/3 coal gangue vegetation restoration, timely addition of fertilizers can promote the long-term growth and flowering of reclaimed plants.
本发明的新颖性在于:1.本方法中涉及复垦基质种类少,降低施工复杂程度,同时,避免了其他修复基质,如污泥、粉煤灰和石灰石等造成二次污染的风险;2.本方法可以节约复垦的覆土用量,,降低施工成本和难度;3.探索出的适于植物生长的最佳煤矸石粉碎物和土壤基质配比,为矿区复垦土壤植被绿化、提供了技术支持。The novelty of the present invention lies in: 1. In this method, there are few types of reclamation substrates, which reduces the complexity of construction, and at the same time, avoids the risk of secondary pollution caused by other restoration substrates, such as sludge, fly ash and limestone; 2. .This method can save the amount of covering soil for reclamation, and reduce the construction cost and difficulty; 3. The optimum ratio of crushed coal gangue and soil matrix suitable for plant growth has been explored, which provides a greening and greening of soil vegetation in mining areas. Technical Support.
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