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    河北张宣矿区干排铁尾矿植生基质分级评价

    Graded assessment of dry-stacked iron tailings as revegetation substrates in the Zhangxuan mining area of Hebei province

    • 摘要: 【目的】明确张宣矿区干排铁尾矿的植生限制及分级依据,为半干旱矿区基质改良提供区域参照。【方法】比较10个林草参照样地与裸露尾矿KA、自然定居尾矿KB的表层理化性质,结合绿化种植土壤和污染风险标准,区分区域分布、一般配置目标和强化配置目标。【结果】形成4类19项指标框架,其中12项开展理化比较、7项设置风险对照。参照容重均值为1.073 g/cm3,KA和KB分别高78.9%和51.0%;水稳性团聚体参照均值为41.9%,两尾矿报告值均为0;有机质参照均值为2.67%,尾矿分别为0.2%和0.3%。按4项共同量化要求,两尾矿均有3项不满足;按8项强化配置要求,分别有6项和5项不满足。自然定居尾矿盖度为10%,其低有机质和供氮、供磷不足仍突出。毛管孔隙度、团聚体和全氮保留区域分布信息,区域统计区间与标准配置值分别列示。【结论】一般配置目标用于识别基本改良任务,强化配置目标用于细化养分配置;区域分布补充说明结构与肥力差异,分级应用须结合风险检测和现场植生表现。

       

      Abstract: Objective Establishing vegetation on dry-discharged iron tailings requires a substrate with suitable physical and chemical properties. In the semiarid Zhangxuan mining area, the relation between regional soil conditions and engineering requirements needs to be clarified before grading values can guide substrate improvement. This study aimed to identify the main limitations of tailings and develop a graded assessment that distinguishes observed regional conditions from general and enhanced substrate targets.Methods Surface samples from ten forest, shrubland and grassland reference plots were compared with bare tailings (KA) and naturally colonized tailings (KB). Twelve physicochemical indicators were examined within a framework containing nineteen indicators in four categories. Regional summaries were combined with greening soil requirements and soil contamination screening values. Four common quantitative requirements were used for the general target, and eight were used for the enhanced target. Seven potentially harmful elements were included as risk comparison items but were not measured. Reference distributions were treated as descriptive information rather than plant response thresholds. Structural summaries included ranges, means and quartiles, with leave-one-plot-out calculations used to examine sensitivity to reference composition. Non-capillary porosity was estimated using an assumed particle density of 2.65 g/cm3. Particle-size composition was summarized for nine reference plots after one inconsistent record was excluded; the other indicators for that plot were retained. Results Reference bulk density averaged 1.073 g/cm3, whereas the values in KA and KB were 1.92 and 1.62 g/cm3, respectively, representing increases of 78.9% and 51.0%. Water-stable aggregates larger than 0.25 mm averaged 41.9% in the reference plots, while both tailings samples had reported values of zero. Mean reference organic matter was 2.67%, compared with 0.2% in KA and 0.3% in KB. Reference total nitrogen averaged 1 390 mg/kg, compared with 120 and 200 mg/kg in the two tailings samples. Cation exchange capacity was 4.0 cmol(+)/kg in KA and 12.5 cmol(+)/kg in KB, compared with a reference mean of 21.08 cmol(+)/kg. Both tailings samples failed three of the four common requirements, but the failed items differed: KA had excessive bulk density, low estimated non-capillary porosity and low organic matter, whereas KB had excessive bulk density, low organic matter and a pH above the general greening range. Under the eight enhanced requirements, KA failed six and KB failed five. Vegetation cover in KB was 10%, while organic matter and available nitrogen and phosphorus remained low. The observed presence of vegetation therefore coexisted with substantial substrate limitations. Regional distributions provided additional information for indicators without sufficiently supported grading boundaries, including capillary porosity, water-stable aggregates and total nitrogen. Conclusions The general target identifies basic substrate improvement tasks, while the enhanced target specifies additional nutrient and exchange-capacity requirements. Regional observations help interpret structural and fertility differences. Application of the grading framework requires separate risk testing and evaluation of vegetation performance under field conditions; the framework supports substrate design and staged management in the study area.

       

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