微生物-生物促生剂协同修复河道底泥——促生剂投量对修复效果的影响

采用5个110L的模拟河道反应器,在投加菌剂的基础上（底泥稳定后向底泥和水中分别注射浓度为0.09%和0.03%的菌剂）,生物促生剂投量分别设计为0.08,0.09,0.10和0.11g/L,单独投加菌剂组作为空白实验.通过为期四十余天的实验研究微生物与促生剂协同作用时的修复效果.结果表明,促生剂投量为0.10g/L时,上覆水COD去除率69%高于其余各组;各协同修复组上覆水中NO₃^--N基本无积累,且促生剂投量为0.11g/L时NO₃^--N去除率最高,可达96%;40d内各组底泥TOC,TN含量变化不显著,延长反应时间至84d,各协同修复组底泥TOC,TN去除率均有明显提升.各协同修复组脲酶活性均波动下降,蛋白酶活性在15d左右时达到峰值,增幅可达106%~237%.通过高通量测序技术发现,43d时Desulfuromonas,Pseudomonas,Treponema_2,Blvii28_wastewater-sludge_group等主要功能菌群的相对丰度与空白实验组相比均增加,且促生剂投量为0.10g/L可使微生物群落向更适宜降解去除氮素及有机质的方向演替,有效改善底泥环境.协同修复对底泥,上覆水水质及微生物群落有良好改善效果,且促生剂投量为0.1g/L时整体修复情况更为理想.     

安徽铜陵铜尾矿硫形态及硫同位素分布特征

分析讨论了安徽铜陵水木冲S和SP剖面尾矿砂的理化指标、硫形态变化和硫酸根硫同位素组成与分布特征.结果显示：S和SP剖面整体呈酸性,pH值为2.59~6.12和3.50~6.27,由下而上有明显的降低趋势;Eh随剖面由下至上明显升高,范围为66~457和-37~307mV;酸可挥发性硫（AVS）含量为0~62.36和0~3.44mg/g,黄铁矿硫（CRS）含量为0.70~32.30mg/g和0.17~5.39mg/g;AVS与CRS的变化趋势基本一致,随剖面自下而上减少,且AVS先于CRS被氧化.2个剖面元素硫（ES）含量为0~8.83和0~3.62mg/g,随深度变化无明显规律.硫酸根硫（SO₄^2--S）含量为8.44~66.34和8.48~29.87mg/g,自下而上呈降低趋势,且分别在剖面的氢氧化物薄膜层（11.5~16.5cm和18~54cm）出现高值区.2个剖面总硫（TS）含量为9.18~109.69和12.38~37.72mg/g,表层由于淋滤含量较低,底层变化则不大.位于斜坡上的SP剖面TS及各形态硫含量均低于S剖面,表明淋滤对硫含量影响更明显.硫酸根硫同位素δ³⁴S为-3.32‰~13.43‰和-3.08‰~1.80‰,S-9硫酸根δ³⁴S为13.43‰,指示其来自于伴生硬石膏,其余层位δ³⁴S偏负且变幅较小,指示其硫酸根主要来源于硫化物的氧化.     

EK∕PRB修复砷污染土壤影响因素及机理

为明确EK/PRB（电动联合渗透反应格栅）修复As污染土壤过程中各因素的影响机理、提高As的去除效率,以As污染高岭土为研究对象,考察PRB加入、PRB位置、pH调控及腐殖酸强化影响下,EK/PRB系统中电流密度、土壤pH分布和土壤中As残余量、电渗透系数及电渗流的变化规律;探讨EK/PRB修复后土壤中As形态的迁移转化规律.结果表明:①单独EK修复对土壤中As的去除效率较低,加入PRB后去除率为由42%增至57%,并且EK/PRB修复可以将土壤中的As由不容易去除的可还原态转变成较容易去除的酸溶态.②采用盐酸调节阴极pH,可以将土壤中As的去除率由57%增至63%,但同时能耗也明显升高,由5.22 kW·h/g升至39.38 kW·h/g.③添加腐殖酸会促进土壤中As的迁移、提高As的去除效率,但也会增加土壤中难处理的可氧化态和残渣态As的占比.研究显示,EK/PRB除As过程中以PRB的去除作用为主,阴极pH调控及腐殖酸强化均可以提高土壤中As的去除率.      

重庆市煤矸山周边农产品镉健康风险评价及土壤环境基准值推导

以重庆市煤矸山周边农用地土壤和农产品（玉米和水稻）为研究对象,测定土壤和农产品（玉米和水稻）中Cd含量,评估摄入农产品（玉米和水稻）对人体的潜在健康风险,并基于物种敏感性分布法（SSD）推导土壤环境基准值.结果表明,重庆煤矸山周边旱地土壤Cd含量超风险筛选值的点位占55.8%,水田土壤Cd含量超风险筛选值的点位占31.6%,土壤Cd以较高生态危害和高生态危害为主,分别占47.4%和36.8%.玉米Cd含量超标点位占4.4%,水稻Cd含量均未超标.健康风险评价表明因食用玉米和水稻摄入Cd的非致癌健康风险可忽略,食用玉米摄入Cd存在可耐受致癌健康风险,食用水稻摄入Cd存在不可耐受致癌健康风险,且玉米和水稻Cd含量敏感度最高.SSD推导出煤矸山周边旱地土壤在pH≤5.5、5.57.5时Cd的环境基准值分别为0.491、0.382、0.376和0.588 mg ·kg^-1,水田土壤Cd的环境基准值为0.807 mg ·kg^-1.水田土壤和旱地土壤pH≤7.5时,现行土壤标准（GB 15618-2018）相对偏严;旱地土壤pH>7.5时,现行土壤标准（GB 15618-2018）相对偏宽松.应加强煤矸山周边土壤Cd污染防治和农产品安全利用研究,并对土壤Cd环境基准值进行适当调整.     

Germination,Growth, and Nodulation of Sesbania rostrata Grown in Pb/Zn Mine Tailings

Sesbania rostrata in pure and amended Pb/Zn tailings. About 90% of seeds of S. rostrata germinated in pure Pb/Zn tailings, which contained high concentrations of Pb, Zn, Cu, and Cd. Although seedling growth suffered from the adverse environment of Pb/Zn tailings, they became established on tailings stands, in the greenhouse, as well as on the actual tailings dam, and completed their life cycle in 4 months. Dry matter production and nitrogen accumulation was 3200 kg/ha and 69.4 kg/ha, respectively in the actual tailings dam. Applying inorganic fertilizer to Pb/Zn tailings led to no obvious improvement in growth and nodulation of S. rostrata, while tailings amended by river sediment or domestic refuse rich in organic matter improved the growth and nodulation of the species. Azorhizobium caulinodans survived and formed N-fixing stem and root nodules in S. rostrata grown in pure Pb/Zn tailings with a nodule biomass exceeding 300 mg fresh matter per plant.     

ENVIRONMENTAL IMPACT ASSESSMENT OF TAILINGS DISPERSAL FROM A URANIUM MINE USING TOXICITY TESTING PROTOCOLS1

ABSTRACT: Toxicity testing is a means of establishing the environmental risk of a uranium tailings release. It is valuable in designing tailings containment structures because it assists in setting acceptable levels of risk for the design. This paper presents details of toxicity tests of the tailings from Ranger Uranium Mine, Northern Territory, Australia. The results suggest that the non-radiological toxicity of the tailings is low. The environmental risk of a tailings release is more likely to be related to the physical impacts of the tailings, including infilling of billabongs and changes in the sedimentology of riparian ecosystems rather than their biogeochemical impact. Two major results were: (1) water from treatment with washed tailing fines were not toxic to Hydra viridissima, and (2) mixtures of washed tailings fines and natural floodplain sediment (overlying water or elutriates) were not toxic to Hydra viridissima or Moinodaphnia macleayi.     

矿山清洁生产示范研究

矿山清洁生产具有双重性。矿山生命周期决定了矿山清洁生产体系的特殊性。矿山清洁生产体系是由培训体系、生命周期清洁生产体系和监合与审核体系构成的一个系统，生命周期清洁生产体系包括从资源勘探-规划设计-开发-闭矿-后续土地利用与监测的各个阶段。与其他行业相比，矿山清洁生产难度大且明显滞后，开展矿山清洁生产示范研究势在必行。     

基于模糊聚类关联分析法的煤与瓦斯突出程度分析

运用模糊聚类分析方法对煤与瓦斯突出的样本集合进行分类,建立了不同突出程度的模糊模式.用关联分析确定待分析样本与模式的关联程度,以此预测预报样本的煤与瓦斯突出危险程度.实例分析表明,与模糊聚类分类后、将模式与待预报样本组成新样本集合进行聚类分析并以此分类结果进行预报的方法相比,这种预报方法不仅可靠程度高,而且能定量描述待报样本与模式的亲和程度.     

加大加强通风量对防止煤矿瓦斯爆炸的副作用

分析产生瓦斯爆炸的基本条件,指出在绝对瓦斯涌出量为5～75m3/min或更大的轻度瓦斯突出的异常情况下,风筒送入的风与突出的瓦斯混合,会在较长巷道内形成大量的瓦斯浓度处于爆炸上限与下限之间的可爆混气.风量越大,形成的可爆混气体积越大,如400m3/min的风量在2 min内就可形成≥842 m3的可爆混气.遇火源可发生强烈的爆炸甚至爆轰,造成较大的伤亡甚至整个矿井内大部分人员死亡.这表明,加大加强的风量对防止煤矿瓦斯爆炸起副(反)作用.这种副作用已在试验巷道用天然气爆炸试验中得到证明.目前煤炭界采取的各种措施不能有效地消除加大加强风量引起的副(反)作用.提出了2种消除副作用的措施,即瓦斯传感器断电与复电方法和抽吸方法,并经试验证明是有效的.     

In-situ electrochemical measurements of total concentration and speciation of heavy metals in acid mine drainage (AMD): assessment of the use of anodic stripping voltammetry

We assessed the use of anodic stripping voltammetry (ASV) for in-situ determinations of both total concentration and speciation of dissolved heavy metals (Cd, Cu, Pb and Zn) in acid mine drainage (AMD). In the Kwangyang Au–Ag mine area of South Korea, different sites with varying water chemistry within an AMD were studied with a field portable anodic stripping voltammeter. Anodic stripping voltammetry after wet oxidation (acidification) was very sensitive enough to determine total concentration of dissolved Cd because Cd was dominantly present as ‘labile’ species, whilst the technique was not so effective for determining total Cu especially in the downstream sites from the retention pond, due to its complexation with organic matter. For dissolved Pb, the concentrations determined by ASV after wet oxidation generally agreed with those by ICP-AES. In the downstream samples (pH>5), however, ASV data after wet oxidation were lower than ICP-AES data because a significant fraction of dissolved Pb was present in those samples as ‘inert’ species associated with colloidal iron oxide particles. The determination of total dissolved Zn by ASV after wet oxidation appeared to be unsatisfactory for the samples with high Cu content, possibly due to the interference by the formation of Zn–Cu intermetallic compounds on the mercury coated electrode. In AMD samples with high dissolved iron, use of ultraviolet irradiation was not effective for determining total concentrations because humate destruction by UV irradiation possibly resulted in the removal of a part of dissolved heavy metals from waters through the precipitation of iron hydroxides.