煤矸石中潜在有害微量元素淋溶析出研究

在煤矸石淋溶实验的基础上，研究了有害微量元素从煤矸石中淋溶析出的浓度与其在煤矸石中的含量和赋存状态的关系。结果表明，溶出浓度受淋溶时间，淋溶液温度，酸碱度的影响。淋溶液温度越高，淋溶时间越长，则有害微量元素从煤矸石中析出的浓度越高；不同的有害微量元素受淋溶液pH值大小影响程度也不相同。     

Major and trace elements in plants and soils in Horton Plains National Park,Sri Lanka: an approach to explain forest die back

Forest die back has been observed from 1980s in the montane moist forest of Horton Plains in the Central Sri Lanka for which the aetiology appears to be uncertain. The concentration levels of Na, K, Ca, Mg, Fe, Mn, Cu, Ni, Zn and Pb in canopy leaves, bark and roots, which were collected from dying and healthy plants of three different endemic species, Calophyllum walkeri, Syzygium rotundifolium and Cinnamomum ovalifolium, from three different die back sites were studied. Soils underlying the plants were also analyzed for their extractable trace metals and total contents of major oxides. Analysis of dead and healthy plants does not show any remarkable differences in the concentrations of studied trace elements. The results show that there is a low status of pollution based on the concentrations of chemical elements of environmental concern. Extractable and total trace element analysis indicates a low content of Ca in soils due to high soil acidity that probably leads to Mg and Al toxicity to certain plants. Relatively high Al levels in the soil would affect the root system and hamper the uptake and transport of essential cations to the plant. It therefore seems that the forest declining appears to be a natural phenomenon, which occurs due to the imbalance of macro and micronutrients in the natural forest due to excessive weathering and the continuous leaching of essential elements.     

湖南典型地区大气降水与下渗水元素地球化学特征及其影响因素研究

对比了湖南典型地区大气降水与下渗水中阴离子含量、Cd等重金属元素含量特征,并研究了Cd等重金属元素下渗的影响因素。研究表明,郴州市和株洲市大气降水中SO42-含量均比桂东—汝城地区和岳阳市高,郴州市和株洲市大气受到较为严重的污染。郴州市和株洲市大气降水及土壤中Cd等重金属元素含量均明显高于桂东—汝城地区和岳阳市,但下渗水中Cd等重金属元素含量差异不大。用元素浓度下渗比(下渗水中重金属元素含量/大气降水中重金属元素含量)来表征水循环过程中土壤重金属元素的累积性,结果显示郴州市和株洲市降水对土壤Cd等重金属元素累积的贡献大于桂东—汝城地区和岳阳市。综合对比表明郴州市和株洲市表层土壤Cd等重金属元素累积明显。影响Cd等重金属元素下渗的因素非常复杂,其中土壤有机碳和pH是控制As、Cd和Pb下渗的主要因素。     

石灰岩山地淡竹林“岩石-土壤-植物”的元素分布与迁移积聚特征

本研究以石灰岩山地淡竹林为研究对象,测定了岩石、土壤和4种淡竹群落植物[优势种淡竹(Phyllostachys glauca),伴生种枸骨(Ilex cornuta)、油茶(Camellia oleifera)和胡颓子(Elaeagnus pungens）]的N、P、K、Ca、Mg、Fe、Al、Mn和Na等9种元素含量,对元素迁移积聚特征进行了分析,结果表明:（1）淡竹林石灰岩Ca含量高（363.09 g· kg-1）;土壤Ca含量下降至2.68 g·kg-1,Fe、Al含量升高（48.12 g·kg-1、84.00 g·kg-1）;与土壤相比,植物N、P和Ca含量上升,其他元素含量则降低;（2）从岩石到土壤,Ca为纯迁移,迁移积累系数仅为0.01;Fe和Al明显富集,迁移积累系数分别高达9.98和14.10;从土壤到植物,N、Ca、P为富集,Fe、Al生物吸收系数很低,仅为1.41和2.08;（3）除K外,群落优势种淡竹的元素含量和生物吸收系数均小于伴生种。研究发现,强淋溶作用下淡竹林石灰岩发育为酸性红石灰土,其生长的植物均非喜钙植物;“岩石—土壤—植物”元素迁聚特征因土壤发育过程和植物种间特征而异,红石灰土Ca积累少;淡竹对土壤元素需求少可能是其在石灰岩生境占据竞争优势的生理基础。      

煤中微量元素在土壤环境中的迁移

煤或煤矸石中的微量元素在水等条件作用下发生变化,并从其中析出随水体进入土壤环境中,在土壤环境中发生迁移和富集,其迁移的能力受土壤环境的制约,本文通过对煤的淋溶实验,分析了煤中微量元素在土壤环境迁移的能力,根据对煤矸石堆周转土壤中微量元素的平面上和垂向上的含量变化,研究了微量元素在土壤环境中富集能力及煤中微量元素对土壤环境的影响,为正确评价煤中微量元素在土壤中的环境效应提供依据。     

Release of arsenic and other trace elements from poultry litter: Insights from a field experiment on the Delmarva Peninsula,Delaware

A poultry litter application was conducted to examine field scale release and transport of trace elements from poultry litter into the subsurface. Field monitoring before and after litter application demonstrated increases in major ion, nutrient, and trace element concentrations in soil water after application, but concentrations of trace elements were all below regulatory standards. Using laboratory stepwise extractions of litter, calculated leaching rates of trace elements are fastest for As, followed by Cu and Zn. Comparison of the projected (from laboratory extractions) to actual (measured in the field) trace element concentrations in litter show that laboratory-derived rates generally over-predict leaching, but the long-term projections of Cu and Zn concentrations remaining in litter are within 20% of the field measurement. Arsenic leaching from litter was under-predicted by the laboratory leaching model by over 100%, suggesting that other processes (perhaps biological) occurring in the field allowed for additional As to be leached/removed. Mass balance coupled with conservative tracer calculations reveal that the vadose sediment was the main sink for the trace elements, with lesser uptake of Cu and Zn (not As) by orchard grass. Overall, results of this study showed that the fate and transport of trace elements from poultry litter are controlled by their leaching rate from litter, adsorption, uptake in vegetation and dilution. An additional process affecting As is biotransformation.     

高强度模拟酸雨量对珠三角地区潮土中重金属元素释放的影响

采用平均离子强度下30年雨量的模拟酸雨淋滤珠江三角洲潮土,电感耦合等离子体质谱法测定重金属元素,研究潮土0~90 cm处各节土壤柱中重金属镉、钴、铜、锌、铅、砷、钛、钒、铬、锰等元素的释放情况。研究表明,在高强度模拟酸雨淋滤下,潮土中重金属元素的释放情况存在较大差异。长期的酸雨淋滤,土壤中的镉、钴、铜、锌和铅在不同深度均有不同程度的淋失;砷、钛、钒、铬、锰等元素不会造成大量的淋失。利用这种差异可以评估重金属元素对环境的潜在影响,为农田生态系统的预警预测提供依据。     

Effect of simulated acid rain on soil acidification and rare earth elements leaching loss in soils of rare earth mining area in southern Jiangxi Province of China

Acid rain has long been a great concern because of environmental and ecological problems; however, the effect of acid rain on soil acidification, loss of rare earth elements (REEs) via the leaching process, and transformation are rarely reported in rare earth mining areas. Through a simulated acid rain leaching experience, the effect of acid rain was studied on soil acidification and REEs leaching loss. The results showed that the tested soil had certain buffering capacity against nearly neutral rainwater. However, simulated acid rain of low and very low pH (pH ≤ 3.5) had a greater impact on soil acidification. After eluviating by simulated acid rain of pH 3.5 for 36 h, the pH of tailings, garden soil, paddy soil, and alluvial soil decreased by 20.41, 32.03, 13.60, 16.88, and 15.83 %, respectively, from the original values. For simulated acid rain of pH 2.5, it was 31.89, 44.76, 31.26, 29.87, and 29.15 %, respectively. After simulated acid rain eluviations of low and very low pH (pH ≤ 3.5), the order of the leaching rate of REEs in the tested soil was as follows: garden soil > tailings > paddy soil > alluvial soil. For nearly neutral rainwater (pH 4.5 simulated acid rain and pH 5.6 deionized water), the order was tailings > garden soil > paddy soil > alluvial soil. For simulated acid rain of the same pH, the leaching amounts of REEs in tailings and garden soil were higher than those in paddy soil and alluvial soil. After leaching by low and very low pH-simulated acid rain (pH ≤ 3.5), the peak value of the leaching amount of REEs in all tested soil appeared at 2 h, and then gradually reduced and reached a stable leaching state 20 h after leaching. On leaching by simulated acid rain of pH 2.5, the maximum REEs contents of leachate in tailings, garden soil, paddy soil, and alluvial soil were 156.35, 145.82, 99.88, and 85.97 mg/L, respectively. For pH 3.5 of simulated acid rain, it was 130.49, 110.49, 80.57, and 62.73 mg/L, respectively. On leaching by simulated acid rain of pH 4.5, the maximum contents of REEs in the leachate were 53.46 and 29.82 mg/L, respectively, which were observed after leaching for 6 h in tailings and garden soil that became stable 12 h after leaching. The contents of leached REEs in paddy soil and alluvial soil were always in a lower and stable state. After eluviations with deionized water of pH 5.6, the contents of leached REEs in other soils were lower, except for the slight fluctuations in tailings. The maximum content in the leachate of REEs was in the water-soluble and exchangeable fraction. When bound to carbonate fractions, REEs were not detected in the leachate. REEs bound to iron-manganese (Fe–Mn) oxides fraction and to organic matter fraction in the leachate possibly came from the tested soil or from the REEs transformation during the migration process. The content of residual fraction REEs in the leachate was very low.     

白云鄂博矿区土壤和植物中稀土元素的分布特征

白云鄂博矿区是稀土的主要产出地,在矿山开采和选炼等过程中,稀土元素通过迁移、富集等作用进入植物体,研究稀土元素的分布特征和迁移规律,可为白云鄂博矿体闭坑后的生物修复提供数据支持。本文设置了7个土壤采样点,采集铁花、沙蒿、沙打旺、沙朋、青蒿、小叶杨、猪毛菜七种植物,用电感耦合等离子体质谱法测定土壤和植物的根、茎、叶及整株的稀土含量,研究稀土元素在土壤和植物中的分布特征和迁移规律。统计分析结果表明:随着采样区与主矿区的距离增加,土壤样品中的稀土含量逐渐减少;在七种植物中,铁花的稀土含量最高,青蒿最低;对不同植物的整株稀土含量和各部位(根、茎、叶)稀土含量进行多元线性回归分析,叶(或花)的稀土含量在整珠植物中的占比最大。此外在不同季节,植物中的稀土含量基本保持不变,含量较高的稀土元素为Ce(0.0035%～0.020%)、La(0.0012%～0.011%)、Nd(0.0010%～0.0094%)和Pr(0.00036%～0.0046%),其中Ce最高。本研究提出:根据土壤样品中的稀土含量逐渐减少的特征,矿区周围土壤的稀土来源可能是矿石在采、选过程中的扩散造成的;根据植物富集稀土的能力,在矿山闭坑后,可种植富集稀土能力强的植物——铁花,进行矿山生物修复。     

化学元素淋溶性质的定量表示

化学元素淋溶性质的研究对于土壤学和风成沉积地球化学的研究具有重要的意义,然而目前的研究还局限在定性描述的水平,同时很多表示的方法和代用参数存在误区。文章主要分析了元素发生化学淋溶的微观过程,通过对兰州市周边地区土壤浸泡、离心分液和离子色谱分析的验证实验,认为大气降水淋岀液中元素的数量与大气降水的量成对数关系,并且给出了确切的函数关系。另外我们得到利用淋溶系数η或λ定量表示元素淋溶性质的方法,该方法可以应用于土壤肥力保持能力的评估和风成沉积地球化学的研究。     

长白山区暗棕壤成土作用地球化学特征

以代表性暗棕壤垂直剖面土壤地球化学数据为依据,研究了长白山区特定的森林景观条件下成土过程中元素的分异与富集特征。研究结果表明,在岩石风化过程中主要以CaO、Na2O、Sr淋溶为主,有机酸淋溶过程中SiO2、Al2O3、K2O部分被淋溶,部分游离铁下渗到土体中下部氧化成铁锰胶膜;微量元素在风化过程中被次生黏土矿物吸附,不同程度地富集,在腐殖质积累过程中Cd、Zn、Pb、Mo、Hg、Co、Mn、Cr等亲生物元素进一步富集于表层土壤,Ce、Ni、Sb、Ti、V、Y、Zr在表生环境中地球化学性质稳定,残留富集于土壤表层。母质层继承和保留了基岩元素地球化学分布的基本特征。     

黑龙江省讷河市土壤某些微量元素地球化学特征

根据东北黑土地1：250000土地质量地球化学调查数据，对黑龙江省讷河市土壤中微量元素B、Cu、Mo、Fe、Mn、Zn元素全量和有效态含量分布特征进行了分析研究.结果显示：①土壤表层Mn元素含量丰富，Fe、Mo元素含量较丰富，B、Cu、Zn元素含量较缺乏；②土壤表层微量元素Cu、Fe、Mn、Zn有效态含量丰富，B有效态含量中等，Mo有效态含量缺乏；③黑土剖面中微量元素淋溶淀积程度明显，表现为以淋溶层较低，表层和淀积层较高，而草甸土淋溶淀积不明显.依据土壤中微量元素全量和有效态含量分布特点，应选择施用微量元素肥料，促进农业可持续发展.     

黑龙江省讷河市土壤某些微量元素地球化学特征

根据东北黑土地1：250000土地质量地球化学调查数据,对黑龙江省讷河市土壤中微量元素B、Cu、Mo、Fe、Mn、Zn元素全量和有效态含量分布特征进行了分析研究.结果显示：①土壤表层Mn元素含量丰富,Fe、Mo元素含量较丰富,B、Cu、Zn元素含量较缺乏;②土壤表层微量元素Cu、Fe、Mn、Zn有效态含量丰富,B有效态含量中等,Mo有效态含量缺乏;③黑土剖面中微量元素淋溶淀积程度明显,表现为以淋溶层较低,表层和淀积层较高,而草甸土淋溶淀积不明显.依据土壤中微量元素全量和有效态含量分布特点,应选择施用微量元素肥料,促进农业可持续发展.     

Physicochemical numerical simulation of extraction of critical elements from polluted objects

Physicochemical numerical simulation of the “water-rock” system open to atmospheric gases was carried out to study leaching of rock-forming and critical (As, Mo, W) elements from the tailing dump and polluted soil of the industrial site of metallurgical plant. It was shown that (a) results of simulation of polluted soil leaching are of an order of magnitude similar to those shown by laboratory experiments [2], (2) with growth of rock-water mass ratio (decrease of water exchange), the intensity of pollutant leaching from polluted soil decreases: 0.067–0.00009 mg As/kg water from 1 kg soil, 16.5?0.84 mg Mo/kg water from 1 kg soil, 79–0.037 mg W/kg water from 1 kg soil; (c) ecological hazard of element leaching from tailing dump by rain waters decreases with time.     

土壤-灰岩岩溶系统中水文地球化学动力学过程模拟及其意义

在实验室模拟了土壤－灰夺岩溶系统,对降水 滤下元素地球化学动态进行了系统监测。结果表明,岩溶作用使土壤中易移动性组分淋溶,Ｃａ＾２＋、ＨＣＯ３＾－的淋出动态表现为开始的快速下降和随之的平衡两个淋出阶段,淋出量与土壤中水溶性Ｃａ、可氧化有机质的含量有关。土壤对ＨＣＯ３＾－的淋出与排释有促进作用。这种动力学特征对解释岩溶沉积古记录和岩溶作用的大气ＣＯ２汇效应具有重要意义。     

模拟酸雨及施磷对水稻土中铅的淋溶特性影响

采用pH=3.0、pH=4.5与对照pH=5.6的3种模拟酸雨淋溶土柱的方法,研究酸雨及含磷酸雨淋溶下合肥市郊水稻土中铅的释放特征与规律。结果表明:经过相当于1 980 mm降水量的淋溶后,铅释放量总体上表现为随着酸雨强度增加累积淋溶量也增加的现象。酸雨作用下,施磷量越多土壤中铅的淋失总量越大。在酸雨及施磷条件下,大兴地区黄褐土中Pb较义城地区水稻土中易于淋失。     

包气带中原油的迁移和降解研究

在石油的开采和集输过程中,常常有大量的原油抛洒和泄漏,这对土壤和植物地造成严重污染,本文通过大量野外和室内的原油渗透试验,含油地层的淋滤试验和石油的生物降解试验,来研究石油污染物在包气带中迁移,转化和降解规律,从而地下水石油污染的潜在性作出科学的评价。     

溶解性有机质对冻融作用下污染土壤中重金属Pb的溶出释放规律

采用室内模拟实验方法研究了溶解性有机质（DOM）对冻融作用下污染土壤中重金属Pb的溶出规律。结果表明：冻融作用明显改变了土壤基本理化性质和重金属Pb的化学形态;与未冻融土壤相比,DOM明显促进了冻融土壤中Pb的溶出释放。DOM对污染土壤中Pb的溶出释放作用与土壤类型、土壤污染时间和污染程度有关：DOM对棕壤中Pb的溶出释放作用大于对黑土中Pb的溶出释放作用;而且随着土壤Pb污染时间越长和污染程度越重,DOM对土壤中Pb的溶出释放作用越大。DOM对土壤中Pb的溶出释放还与DOM质量浓度、性质和组成密切相关：DOM质量浓度的增加提高了污染土壤中Pb的溶出释放;DOM的低pH和小分子量亲水性组分利于土壤中Pb的溶出释放。     

不同岩溶生态系统中元素的地球化学迁移特征比较——以广西弄拉和弄岗自然保护区为例

研究了广西弄拉和弄岗自然保护区两种不同岩溶生态系统的元素地球化学循环特点,结果表明,弄拉、弄岗的成土过程都表现为Si和Fe相对累积,而其它化学元素则表现为相对淋失。弄岗与弄拉相比,其元素的淋失程度更为强烈,但在植物中两者表现出比较相似的元素地球化学特点。弄岗泉水p H比弄拉的低,水的溶蚀能力增大,水中可溶物增多,元素循环也比弄拉的快。      

Investigation of heavy metal uptake by three types of ornamental plants as affected by application of organic and chemical fertilizers in contaminated soils

Accumulation of heavy metals in soil media is considered as a serious environmental problem, which is hazardous to human and animal health. There have been several methods for the removal of these toxic metals. One of the commonly used methods is the use of plants, especially ornamental plants to remove heavy metals from soils. In this regard, the study has been conducted on the soils contaminated with Mn, Pb, Ni, and Cd using factorial experiment in a completely randomized design with two factors including three types of soil (soil A for the highest level of contamination, B for the lowest level of pollution, and C for the non-contaminated soil) with different contamination levels as well as three types of ornamental plants, gladiolus, daffodils, and narcissus with four replications. In another part of the study, soil A and gladiolus were used in a completely randomized design with three replications, and also three types of fertilizers, such as municipal solid waste compost, triple superphosphate and diammonium phosphate, were added to this soil. In addition, the availability of heavy metal was studied in gladiolus as influenced by the application of organic and chemical fertilizers. The results showed that heavy metal pollution caused reduction in the dry weight of gladiolus and tulips compared to the control sample, while there was no significant effect of pollution on the dry weight of narcissus. The uptake of Mn, Pb, Ni, and Cd by all three plants has been increased with enhancing the pollution levels of heavy metals. The highest concentration of Pb in the shoots of plants was observed in soil A with an average amount of 61.16 (mg kg^?1), which revealed a substantial difference relative to the treatment of soil B and C. The most and least amount of Ni in the plants shoots were related to soil A and soil C with an average of 2.35 and 0.89 mg kg^?1, respectively. The uptake of Pb by shoots of all three plants was nearly similar to each other, while more Pb was absorbed by the bulbs of gladiolus compared to the bulbs of other plants. Increment in the pollution levels led to the decrement in enrichment factor (EF); however, there was no effect of pollution levels on EF of Mn and Pb. Moreover, there was no effect of increasing pollution levels on translocation factor of these elements. In gladiolus, after application of organic and chemical fertilizers, it was observed that the concentration of heavy metals was far more in the bulbs compared to the shoots. In conclusion, the cultivation of these ornamental plants is highly recommended due to not only their decorative aspect but also their ability for bioremediation as well as being economical.