香根草和百喜草对铅锌尾矿重金属的抗性与吸收差异研究

铅锌尾矿是一类重金属含量极高,对植物生长产生毒害的生境.盆栽实验的结果显示,香根草和百喜草在纯尾矿或由尾矿和垃圾组成的混合基质上都能生长,但植物的长势随基质中重金属含量的增加而减弱,其中香根草的生物量所受的影响比百喜草的更大,即百喜草有比香根草更强的重金属抗性.2种植物体内的重金属含量高低均为Zn＞Pb＞Cu,但二者对它们的富集能力大小分别是,香根草为Zn＞Cu＞Pb,百喜草则为Cu＞Zn＞Pb.香根草和百喜草的根系对3种重金属都有较强的滞留效应,滞留率均在50%以上;其中香根草对重金属的滞留率又明显高于百喜草;而且,同一植物对不同的重金属的滞留率也明显不同,香根草对Pb的滞留率最高,而百喜草对Cu的滞留率显著高过对Zn和Pb.由于香根草的生物量明显大于百喜草,结果香根草对Pb、Zn的吸收量比百喜草高.当用25%的垃圾改良金属尾矿时,百喜草对重金属的吸收量即达最大;而香根草则在尾矿和垃圾各占50%的基质中吸收最多的重金属;因此,添加一定量的垃圾(25%～50%左右)用于尾矿改良时,不仅能使尾矿得到更快的植被恢复与更高的植物修复效果,而且能使垃圾资源得到充分合理的利用.总之,当开展对金属尾矿的植被恢复时,可选择种植抗性强、覆盖快的百喜草,但如果要对尾矿中的重金属进行生物净化,则应选择种植生物量大的香根草,种植香根草还可较好地防止重金属的二次污染或生物富集.     

香根草和鹅观草对Cu、Pb、Zn及其复合重金属的耐性研究

采用根伸长实验研究了香根草和鹅观草对重金属的耐性随着溶度的升高,耐性指数下降,当香根草和鹅观草受Cu2+、Pb2+、Zn2+单一污染时,三元素的危害作用依次为Cu2+>Pb2+>Zn2+;在Cu、Pb、Zn混合溶液中,其两种植物耐性指数的大小及变化与单一元素Cu溶液最为相似,Cu在溶液中起到主导因子作用;香根草与鹅观草相比,不论是受Cu、Pb、Zn单一污染还是三者的复合污染,香根草比鹅观草都具有较强抵制重金属的胁迫能力,其耐性指数大都大于0 5。因此香根草具有对重金属较强的耐性,在重金属污染土壤的植物修复及尾矿废弃地的植被重建中,可优先作为选择的材料。     

铜陵铜尾矿凤丹种植基地重金属污染初探

通过对安徽铜陵凤凰山铜尾矿凤丹种植基地土壤和凤丹中重金属污染状况进行采样分析.结果表明,在尾矿空白地和凤丹种植地土壤中Cu、Cd、Pb、Zn元素含量、存在形态差异明显,说明凤丹对尾矿土壤的修复效果明显; 尾矿土壤中的Cu、Cd元素总量分别是国家土壤环境质量二级标准的4.36～14.43倍和3.67～3.86倍,凤丹种植地重金属元素的CPI指数达到5.607,表明尾矿土壤中重金属元素污染仍相当严重.研究发现,4种元素在凤丹各部位含量明显不同: 叶和根心为Cu＞Zn＞Pb＞Cd,茎和根皮为Zn＞Cu＞Pb＞Cd,根皮中Zn含量最高;土壤中重金属元素各形态的变化与凤丹体内相应元素总量无显著相关; 丹皮内Cu、Cd、Pb元素含量与丹龄之间相关系数分别为0.842、0.993、0.992,Cu、Cd元素在凤丹体内含量约是出口药用植物绿色行业限量指标的1.43～2.53倍和1.17～3.17倍,可见缩短栽种时间可有效减少重金属元素对丹皮药效的影响.     

添加污泥对尾矿砂理化性质及香樟生理特性的影响

以香樟作为指示植物,选取黄岩、临海和路桥地区污水处理厂污泥,将污泥与尾矿砂按(污泥质量比例为0%对照、25%、50%和75%)配比进行栽培试验。测定添加污泥对尾矿砂理化性质以及香樟生理特性的影响。结果表明:随着污泥比例的增加,混合基质中的有机质、全氮、全磷明显增加,pH值明显降低,离子交换量明显减少,Cu和Cd总量明显增加,而Pb总量明显减少,Zn总量没有明显变化,Cu、Cd和Zn的DTPA提取量明显增加,而Pb的DTPA提取量明显减少。黄岩和临海污泥在25%和50%比例时,香樟叶和茎的生物量和叶绿素含量明显增加,而根的生物量没有明显变化,在75%比例时,生物量和叶绿素含量均明显减少;而添加路桥污泥使香樟叶、茎和根的生物量和叶绿素含量明显减少。丙二醛含量则与生物量和叶绿素含量呈现相反的变化特征。黄岩和临海污泥在25%和50%比例时,根和叶的Cu、Cd、Pb和Zn含量明显减少,在75%比例时,Cu、Cd和Zn含量则明显增加;而添加路桥污泥使叶和根的Cu、Cd和Zn含量明显增加,Pb含量明显减少。研究表明添加污泥提高了尾矿砂的养分含量,同时改变了其重金属组成,对污泥重金属含量和有机质组成的监控可以准确地预测污泥改良后尾矿砂对植物毒性的变化。     

凡口铅锌尾矿影响植物定居的主要因素分析

通过温室栽培和野外调查 ,分析了凡口铅锌尾矿影响植物定居的主要因素 .结果表明 ,铅锌尾矿的Pb、Zn、Cu和Cd的总量分别达 3430 0、3650 0、2 1 5和 82 .6mg·kg- 1 ;有效态的Pb、Zn、Cu和Cd分别为 1 .5、1 963、0 .71和 8.0 3mg·kg- 1 .在栽培试验中 ,重金属毒性严重抑制格拉姆柱花草 (Stylosanthesguianensis)根系的活力 ,使得植物无法利用无机养分 ,并可导致明显的白化症状 ,从而严重影响格拉姆柱花草的生长 ,无论在野外或在室内实验条件下 ,有效态Zn和Cd都与植物的生长呈显著负相关 ,重金属毒性 ,尤其是有效态Zn和Cd的毒性是凡口铅锌尾矿影响植物定居的限制因子 .极端贫瘠是影响植物定居的另一重要因素     

粤东铅锌尾矿三种优势植物对重金属的吸收和富集特性研究

为探讨铅锌矿废弃地优势植物在重金属污染土壤植物修复中的应用潜力,利用野外采样分析法,从粤东梅县丙村铅锌尾矿区采集其三种优势植物类芦、黄荆、盐肤木的根、茎、叶和土壤样品,测定和分析Pb、Zn、Cu、Cd四种重金属含量.结果表明:该矿区土壤污染严重,Pb、Zn、Cd含量远超土壤环境质量的三级标准,Cu超出二级标准;根际土壤和非根际土壤重金属含量均为Pb＞Zn＞Cu＞Cd,但根际土壤的重金属含量显著低于非根际土壤;这三种植物对Pb、Zn、Cu的转移系数大于1.0,对Cu的富集系数最高,Pb最小,但对四种重金属的富集系数均小于1.0,均未达到超富集植物临界含量标准.三种植物为该矿区的优势植物,说明它们对土壤的重金属污染有很强的耐性,虽然并非典型的超富集植物,但对污染土壤仍有较好的修复效果.     

污染条件下VAM玉米元素积累和分布与根际重金属形态变化的关系

为了了解重金属Cu、Zn、Pb、Cd在土壤－根际－植物系统中的行为,揭示VAM植物减弱土壤中过量重金属对植物生理毒的抗性机理,采用原子吸收光谱测定Cu、Zn、Pb、Cd在污灌土壤中生长的VA菌根玉米和无菌根玉米中的积累和分布,并用连接形态分析技术分析了菌根际中Cu、Zn、Pb、Cd的形态分布和变化趋势,结果表明,Cu、Zn、Pb、Cd在菌根玉米中的积累量比非攻根中积累量分别减少10％、18％和29％,Cd积累量没有改变,生长7周后,菌根玉米是非菌根玉米生物量的1．5倍,与对照土壤相比,根际中除Cu交换态显著增加外,Zn、Pb、Cd各形态相对改变量显著大于非菌根,且菌根根际上中Cu、Zn、Pb有机结合态增加量显著大于非根际土,说明菌根际金属向稳定状态转移的程度显著大于非菌根际,同时,讨论了根际金属形态对金属有效性的影响,及其与菌根植物金属抗性机理的关系。     

Pb污染对马蔺生长、体内重金属元素积累以及叶绿体超微结构的影响

通过土壤单因子Pb胁迫盆栽试验和铅锌尾矿污染土壤掺比试验研究了不同土培条件下Pb对马蔺（Iris lactea var chinensis）生长、体内重金属元素积累以及叶绿体超微结构的影响。结果表明：2种不同土壤Pb胁迫下马蔺株高、根长、叶数以及地上、地下部生物量均随Pb浓度的增加呈先增后降的趋势,其中,土壤单Pb胁迫下,低于500 mg?kg-1Pb胁迫（T1—T3）均增加了马蔺的株高和根长,仅800mg?kg-1高Pb浓度处理时马蔺生物量才出现轻微下降（P＞0.05）;与单一土壤Pb胁迫相比,铅锌尾矿污染土壤掺比试验中铅锌尾矿含量低于一定浓度下对马蔺株高、根长生长同样也具有促进效应,只有100%尾矿污染土壤处理下马蔺地上部和根系生物量下降显著（P＜0.05）。马蔺地上部和根系Pb含量均随土壤中Pb浓度和尾矿含量的增加而增加,800mg?kg-1土壤单Pb胁迫下为340.6、1700.02 mg?kg-1,100%尾矿污染土壤处理下为126.9、1725 mg?kg-1。Pb单独胁迫下马蔺地上部Zn含量随Pb含量的增加逐渐下降, Zn和Pb的吸收表现出一定的拮抗效应;而不同掺比污染土壤胁迫下马蔺地上部和根系Zn积累同Pb一样,均随土壤中Pb、Zn浓度的增加而增加,Zn和Pb的吸收表现为一种协同效应。而2种不同土壤Pb胁迫下马蔺对Cu、Cd的吸收均相对较少。本研究中,800mg?kg-1Pb胁迫处理和50%尾砂土壤胁迫处理下马蔺叶片叶绿体双层被膜及内部基粒和类囊体结构与对照相比变化不大。综上表明,马蔺对重金属Pb有较强的耐受性,具备修复Pb污染土壤的潜在能力。     

种植香根草对铜尾矿废弃地基质化学和生物学性质的影响

通过实地调查取样和室内分析,研究铜陵水木冲铜尾矿废弃地不同时期种植香根草(Vetiveria zizanioides L.)群落(近期种植香根草群落(V.zizanioides communities were established in the recent stage,JX),中期种植香根草群落(V.zizanioides communities were established in the middle stage,ZX)和早期种植香根草群落(V.zizanioides communities were established in the early stage,OX))对尾矿基质化学性质、微生物量和土壤酶活性的影响,探讨人工植被恢复对铜尾矿废弃地基质系统的修复作用。结果表明:香根草的定植能延缓铜尾矿的酸化过程,且随着香根草定植时间的延长,0—5 cm和5—20 cm层尾矿基质中总氮和速效磷含量提高(其中,0—5 cm层总氮积累更加显著),OX下0—5 cm表层基质总氮和速效磷的平均值分别是JX下的4.64倍和22.44倍。基质微生物量C、N含量和脱氢酶、过氧化氢酶、脲酶活性也随香根草种植时间的延长而有不同程度的升高,且基质化学性质对微生物量和酶活性有影响,其中基质微生物量C、N含量、脱氢酶和过氧化氢酶活性均与电导率呈显著或极显著负相关性;而基质微生物量N和4种酶活性均与总氮含量呈显著或极显著正相关性,表明总氮含量是影响基质微生物量N和酶活性的主要因子;基质微生物量N、脱氢酶和过氧化氢酶活性还与速效磷含量呈极显著正相关性。基质中Cu、Pb含量对脱氢酶、过氧化氢酶活性和微生物量均有显著抑制作用,而Zn对基质微生物活性有一定的激活作用。生长在尾矿废弃地上的香根草不仅显著地改善了铜尾矿废弃地的基质化学性质,且有利于基质微生物量和酶活性的增加,是一种良好的矿业废弃地生态修复物种。     

EDTA对铅锌尾矿改良土壤上玉米生长及铅锌累积特征的影响

针对铅锌尾矿废弃地的复垦,选用玉米在5种不同尾矿砂与土壤比例的改良基质上进行盆栽试验研究.盆栽培养基质以尾矿与土壤按0⒏100、25∶75、50∶50、75∶25、100∶0比例混合而成,分别标记为:TA00、TA25、TA50、TA75、TA100.研究结果表明:抑制玉米生长的主要因素是尾矿基质极端贫瘠,Pb、Zn含量过高.添加EDTA前,玉米在所有处理中都能正常生长,植株没有出现明显的毒害症状.添加EDTA后玉米生物量显著下降,并且在改良基质中尾矿所占比例越高,下降幅度越大.EDTA可以显著提高玉米对Pb、Zn的富集能力,其中对Pb的富集能力大于Zn.基质比例为50∶50时,添加EDTA后玉米对Pb、Zn的迁移量虽然比基质100∶0低,但是玉米的生物量、株高和根系各指标都比基质100∶0下降幅度小.因此,尾矿和土壤比例为50∶50的基质改良方式比较合理,可用于铅锌尾矿废弃地的复垦.     

Effects of Compost on Colonization of Roots of Plants Grown in Metalliferous Mine Tailings, as Examined by Fluorescence In Situ Hybridization

The relationship between compost amendment, plant biomass produced, and bacterial root colonization as measured by fluorescence in situ hybridization was examined following plant growth in mine tailings. Mine tailings can remain devoid of vegetation for decades after deposition due to a combination of factors that include heavy metal toxicity, low pH, poor substrate structure and water-holding capacity, and a severely impacted heterotrophic microbial community. Research has shown that plant establishment, a desired remedial objective to reduce eolian and water erosion of such tailings, is enhanced by organic matter amendment and is correlated with significant increases in rhizosphere populations of neutrophilic heterotrophic bacteria. Results show that for the acidic metalliferous tailings tested in this study, compost amendment was associated with significantly increased bacterial colonization of roots and increased production of plant biomass. In contrast, for a Vinton control soil, increased compost had no effect on root colonization and resulted only in increased plant biomass at high levels of compost amendment. These data suggest that the positive association between compost amendment and root colonization is important in the stressed mine tailings environment where root colonization may enhance both microbial and plant survival and growth.     

Utilization of spent mushroom compost for the revegetation of lead-zinc tailings: effects on physico-chemical properties of tailings and growth of Lolium perenne

In an attempt to promote sustainable vegetation cover on metalliferous tailings, a randomized factorial greenhouse trial of six-month duration was established to determine the effect of spent mushroom compost (SMC) amendment on the physical and chemical properties of the predominantly lead/zinc tailings. The tailings originated from the surface (20-30cm) of the partially-vegetated 76ha tailings management facility (TMF), where more than nine million tonnes of pyritic metalliferous material were deposited in an unlined land impoundment. SMC was incorporated at application rates of 0, 50, 100, 200 and 400tonha(-1), with each treatment replicated 10 times and Lolium perenne sown at a rate of 200kgha(-1). The addition of SMC was beneficent as a growing medium through improvement of the structural status of the tailings and ultimately through the provision of plant nutrients and reduction in metal concentrations. However, this improvement in the structural and chemical status of the tailings is not adequate in maintaining a sustainable vegetation cover and therefore other remedial options such as introducing a capillary break on the surface of the tailings facility are necessary.     

Identification of sulfate-reducing bacteria in methylmercury-contaminated mine tailings by analysis of SSU rRNA genes

Sulfate-reducing bacteria (SRB) are often used in bioremediation of acid mine drainage because microbial sulfate reduction increases pH and produces sulfide that binds with metals. Mercury methylation has also been linked with sulfate reduction. Previous geochemical analysis indicated the occurrence of sulfate reduction in mine tailings, but no molecular characterization of the mine tailings-associated microbial community has determined which SRB are present. This study characterizes the bacterial communities of two geochemically contrasting, high-methylmercury mine tailing environments, with emphasis on SRB, by analyzing small subunit (SSU) rRNA genes present in the tailings sediments and in enrichment cultures inoculated with tailings. Novel Deltaproteobacteria and Firmicutes -related sequences were detected in both the pH-neutral gold mine tailings and the acidic high-sulfide base-metal tailings. At the subphylum level, the SRB communities differed between sites, suggesting that the community structure was dependent on local geochemistry. Clones obtained from the gold tailings and enrichment cultures were more similar to previously cultured isolates whereas clones from acidic tailings were more closely related to uncultured lineages identified from other acidic sediments worldwide. This study provides new insights into the novelty and diversity of bacteria colonizing mine tailings, and identifies specific organisms that warrant further investigation with regard to their roles in mercury methylation and sulfur cycling in these environments.     

Mineralogy and geochemistry of tailings from a gold mine in northeastern Thailand

Mineralogical and geochemical characteristics of tailings from a gold mine in northeastern Thailand were investigated in relation to acid mine drainage (AMD) and the release potentials of toxic elements. The tailings can be divided into upper tailings and lower tailings. The upper tailings usually contain pyrrhotite, pyrite ± chalcopyrite, calcite, quartz, andradite and diopside. The lower tailings mainly contain goethite, quartz, chlorite, muscovite, calcite and hematite ± pyrrhotite. These assemblages clearly relate to the original types of gold deposit prior to mining and mineral processing. The upper tailings are defined as potential acid forming (PAF), whereas the lower tailings are classified as non-acid forming (NAF). Regarding heavy metals, apart from high Mn level, the other heavy metals appear to have low concentrations in the upper tailings. On the other hand, the lower tailings contain high contents of As, Cu and Pb, which appear to be higher than the National Total Threshold Limit Concentrations. Goethite, the main mineral assemblage in the lower tailings, reveals characteristic of arsenic adsorbent. As a result, the tailing pond is recommended to be covered to prevent the oxidizing processes of the upper tailings; otherwise, AMD generation may take place soon after the mine closure. Land reclamation and monitoring plans must be planned very well and carried out with great care since arsenic contamination has been reported in steam water close to the tailing dam.     

Significance of microbial communities and interactions in safeguarding reactive mine tailings by ecological engineering

Pyritic mine tailings (mineral waste generated by metal mining) pose significant risk to the environment as point sources of acidic, metal-rich effluents (acid mine drainage [AMD]). While the accelerated oxidative dissolution of pyrite and other sulfide minerals in tailings by acidophilic chemolithotrophic prokaryotes has been widely reported, other acidophiles (heterotrophic bacteria that catalyze the dissimilatory reduction of iron and sulfur) can reverse the reactions involved in AMD genesis, and these have been implicated in the "natural attenuation" of mine waters. We have investigated whether by manipulating microbial communities in tailings (inoculating with iron- and sulfur-reducing acidophilic bacteria and phototrophic acidophilic microalgae) it is possible to mitigate the impact of the acid-generating and metal-mobilizing chemolithotrophic prokaryotes that are indigenous to tailing deposits. Sixty tailings mesocosms were set up, using five different microbial inoculation variants, and analyzed at regular intervals for changes in physicochemical and microbiological parameters for up to 1 year. Differences between treatment protocols were most apparent between tailings that had been inoculated with acidophilic algae in addition to aerobic and anaerobic heterotrophic bacteria and those that had been inoculated with only pyrite-oxidizing chemolithotrophs; these differences included higher pH values, lower redox potentials, and smaller concentrations of soluble copper and zinc. The results suggest that empirical ecological engineering of tailing lagoons to promote the growth and activities of iron- and sulfate-reducing bacteria could minimize their risk of AMD production and that the heterotrophic populations could be sustained by facilitating the growth of microalgae to provide continuous inputs of organic carbon.     

Arsenic contamination of soils and sediments from tailings in the vicinity of Myungbong Au mine,Korea

Abstract

Geochemical characteristics of As contamination in the Myungbong gold mine area in Korea were investigated, and the mine tailings were found to contain high concentrations of As (2,500–6,420 mg/kg). The mine tailings are an obvious candidate for the source of contamination in the study area. From the sequential, and oxalate, extraction analyses the majority of the As in the tailings was found to be associated with Fe oxides produced when sulfide minerals are oxidised. Mineralogical examinations showed the formation of poorly crystalline Fe oxides on a rim of pyrite, onto which the As was retained. The sediments of two ponds affected by the tailings also contained significant levels of As. High concentrations of dissolved As were also found in pond and stream waters. It has been suggested that the mobility of the As was increased by the reductive dissolution of Fe oxides under reducing conditions in the pond. Agricultural fields, located beneath the tailing dumps, have been contaminated by the continuous use of contaminated stream water and groundwater for irrigation.     

Local Adaptation of Metallicolous and Non‐Metallicolous Anthyllis vulneraria Populations: Their Utilization in Soil Restoration

Restoration of metalliferous mine soils requires using plant species tolerant to high metal concentrations and adapted to nutrient‐poor soil. Legumes can increase plant productivity through N₂‐fixation, but they are often scarce in metalliferous sites. We examined survival, growth, and tolerance of four populations of a legume, Anthyllis vulneraria, from two metalliferous (MET) Zn‐Pb mine sites, Avinières (AV) ([Zn‐EDTA] = 26,000 mg/kg) and Eylie (EY) ([Zn‐EDTA] = 4,632 mg/kg), and two non‐metalliferous (NMET) sites located in the south of France with the aim to select the most appropriate populations for restoration of mined soils. In a common garden experiment, plants from each population were reciprocally grown in soil from the provenance of each population. The two NMET populations exhibited high mortality and low growth rates in soil from the mined sites. The AV MET exhibited a high growth rate in metalliferous soils, but showed high mortality in non‐metalliferous soils. The growth of the EY MET was very low in the AV‐contaminated soil, but was the highest of all populations in moderately and non‐metalliferous soils. Plants from the AV MET population showed a high growth and survival in metalliferous soil and would be appropriate in the restoration of metal‐contaminated sites (>30,000 mg Zn kg^?1). The EY MET population would be adapted to the restoration of moderate metal‐contaminated soils (<30,000 mg Zn kg^?1). Taking into account the broad distribution of A. vulneraria, these two populations could be suitable for the restoration of derelict mine sites in mediterranean and temperate regions of Europe and North America.     

Soil Seed Bank as an Input of Seed Source in Revegetation of Lead / Zinc Mine Tailings

The goal of the present study was to assess a soil seed bank as an input seed source for revegetating lead/zinc (Pb/Zn) mine tailings. The seed bank source was abandoned farmland, whose top 10‐cm layer of topsoil contained 6,850 ± 377 seeds/m² from 41 species. The seeds in the soil were principally distributed in the upper 0–2 cm, which held 75.8% of total seeds and 92.7% of species composition. The top 2‐cm layer of topsoil may be sufficient to serve the purpose of providing a seed source for revegetation on derelict lands, including mined lands. Four different thicknesses of topsoil (1, 2, 4, and 8 cm, redistributed from the total 0–10‐cm layer from the farmland) were field‐tested on the Pb/Zn mine tailings. There was no significant difference in seedling density among the 4 thickness treatments. Many seeds in the treatments with more than 1‐cm of topsoil were unable to emerge from the deeper layer. Seedlings in plots with topsoil of 1‐, 2‐ and 4‐cm failed to establish within 1 year due to the extremely high acidity (pH 2.39 to 2.76). A shallow layer of topsoil cannot neutralize the sulfuric acid generated from oxidation of pyrites in the tailings. For establishment of seedlings on metalliferous lands, an insulating layer such as subsoil, building rubble, or domestic refuse is necessary before covering with valuable topsoil. The woody legume Leucaena leucocephala grown on the tailings with a topsoil cover of 8‐cm was the most dominant species. Lead was accumulated in root, branch, stem bark, and xylem, which accounted for more than 80% of the total metal concentration in the plant. This portion of Pb will reside in the plant for a long period, while the smaller portion of Pb in the leaf (about 15%) could be returned to the environment as litter during growth. Woody plants may have an advantage in metal‐phyto‐remediation over herbaceous plants.     

华南铅锌尾矿生态恢复的理论与实践

介绍了近年来有关华南地区5个铅锌尾矿生态恢复研究领域的主要研究成果。内容包括：铅锌尾矿的理化性质和影响植物定居的限制因子;尾矿酸化的预测与控制;尾矿的基质改良;尾矿自然定居植物的生态对策;重金属耐性植物的筛选与耐性机理;豆科植物在废弃地植被恢复中的作用;尾矿湿地系统的重建及其废水处理效率;土壤种子库在尾矿生态恢复中的作用;尾矿植被恢复的野外中试研究等。同时,也讨论了尾矿废弃地生态恢复的未来研究方向。