重金属和油处理剂对水稻根系的影响

试验了Ｎｉ、Ｚｎ、Ｍｎ、Ｓｎ、Ｃｒ和Ｃｕ等６种重金属及油处理剂对水稻根系的影响，结果表明．水中含Ｎｉ０．００７ｍｇ／１、Ｃｕ０．００５ｍｇ／１时，能阻碍根系的伸长；含Ｚｎ０．５ｍｇ／１以上时。不利于根系的伸长；水中含Ｍｎ２０ｍｇ／１，Ｓｎ、Ｃｒ￣（６－）各５ｍｇ／１时，对根系有明显危害；水中含Ｃｒ￣（２＋）＋Ｃｒ￣（６＋）时，当１种离子浓度保持不变，根系的抑制程度随着另１种离子浓度的增加而增大。水中含油处理剂１０００ｍｇ／１时，能抑制水稻发根。     

海南省几种草本植物微量元素的组成

海南省位于我国热带地区,草本植物微量元素组成可反映热带区域生物地球化学特点。海南植物微量元素含量属正常范围值,仅个别植物Ｃｄ、Ｈｇ含量偏高。植物Ｚｎ、Ｃｕ、Ｍｏ含量大多在５ｍｇ／ｋｇ以上,Ｐｂ、Ｃｕ、Ｃｄ含量一般低于２ｍｇ／ｋｇ,Ｈｇ、Ａｓ、Ｎｉ通常不足１ｍｇ／ｋｇ。雀稗（Ｐａｓｐａｌｕｍｃｏｍｍｅｒｓｏｎｉ）、地胆草（Ｅｌｅｐｈａｎｔｏｐｕｓｓｃａｂｅｒ）等微量元素含量普遍较高。红裂稃草（Ｓｃｈｉｚａｃｈｙｒｉｕｍｓａｎｇｕｉｎｅｕｍ）、白茅（Ｉｍｐｅｒａｔａｃｙｌｉｎｄｒｉｃａ）等微量元素含量一般较低。植物微量元素组成与植物种类及其生境条件有关。生物吸收系数反映植物摄取元素的强度,Ｍｏ、Ｃｄ、Ｈｇ、Ｚｎ、Ｃｕ的生物吸收系数通常大于１．０,属强积聚元素,Ｐｂ、Ｃｒ、Ｎｉ、Ａｓ的生物吸收系数大多低于０．３,是弱摄取元素。     

重金属对蚯蚓的毒性毒理研究

通过室内模拟实验以及对株洲市重金属污染区农田土壤中采样，进行了重金属对蚯蚓的毒性毒理研究．毒性实验表明，各重金属元素４８ｈ的ＬＤ５０分别为：Ｃｄ１０００ｍｇ／ｋｇ，Ｐｂ８１２ｍｇ／ｋｇ，Ｃｕ６３３ｍｇ／ｋｇ，Ｈｇ３０４ｍｇ／ｋｇ，Ｚｎ５２８ｍｇ／ｋｇ，Ｃｒ４２８ｍｇ／ｋｇ．对蚯蚓毒理研究证明，重金属对蚯蚓酯酶同工酶有抑活作用，而重金属对蚯蚓过氧化物酶同工酶有激活作用．在光镜下观察，可见重金属污染可引起蚯蚓的体表溃疡及产生肿瘤，可使胃肠道粘膜层出血、背血管肿胀，同时可引起胃肠道粘膜上皮细胞产生萎缩或溃疡灶．蚯蚓特有的黄色细胞团污染程度不同而显示出消长规律．在电镜下可见到在重污染区的蚯蚓胃肠道粘膜上皮细胞中的ｒＥＲ肿胀、高尔基体膨大，线粒体嵴消失，甚至空泡化或解体．另可见细胞核膜间隙肿胀、断裂、核质外溢，胞质自溶．蚯蚓以上病变的大小是随土壤重金属污染区的污染级别而定；各病理变化指标均能定性地反映土壤重金属污染状况．     

污泥对区域生态环境的影响

对上海某乡因施用大量污泥而造成的污染状况作跟踪调查研究和质量评价。研究对象为土壤、水稻和蔬菜，被研究的污染元素为Ｃｄ、Ｚｎ、Ｃｕ、Ｐｈ、Ｎｉ、Ｃｒ、Ｈｇ和Ａｓ．结果表明，该乡土壤为复合污染，Ｃｄ、Ｚｎ、Ｃｕ是主要污染元素．污泥施用越多的地区，水稻、蔬菜受污染就越严重，尤以Ｃｄ污染最为突出，超过了允许卫生标准。确定了污染村、污染程度和污染面积。     

电镀废水中铜锌铬镍对农业环境的影响

电镀废水排入河涌会污染农业环境。以广东省南 海市平洲地区为例,农田灌溉水中Ｃｕ、Ｚｎ、Ｎｉ的含量超过允许限值１ ～１４ 倍,河涌底泥Ｃｕ、Ｚｎ、Ｃｒ、Ｎｉ超标１２ ～３７倍,土壤超标０．５ ～２．９倍,作物超标０．３ ～８ 倍。进入河涌的Ｃｕ、Ｚｎ、Ｃｒ、Ｎｉ能较快沉积于底泥中。进入土壤的Ｃｕ、Ｚｎ、Ｃｒ、Ｎｉ主要累积在耕作层中。作物对Ｃｕ、Ｚｎ 的吸收能力远远高于对Ｃｒ、Ｎｉ的吸收能力,作物吸收系数是Ｚｎ ＞ Ｃｕ ＞ Ｎｉ＞ Ｃｒ     

内蒙阿拉善地区植物与土壤元素背景值特征及其相互关系

内蒙阿拉善地区植物、土壤的元素背景特征及其相互关系的研究结果表明：５３种植物的９种元素（Ｚｎ、Ｃｕ、Ｎｉ、Ｐｂ、Ｃｄ、Ｃｏ、Ｃｒ、Ｖ、Ｍｎ）背景含量有很大差异．不同生活型植物背景值也各异，总的规律为：Ｍｎ＞Ｚｎ＞Ｖ＞Ｃｕ＞Ｎｉ＞Ｃｒ＞Ｐｂ＞Ｃｏ＞Ｃｄ；同种植物的元素含量在不同群落中有明显差别，但都在同一个数量级．土壤９种元素的背景含量均以Ｍｎ含量最高，其次为Ｚｎ和Ｖ，Ｃｄ的含量最低；不同上类各剖面各种元素的垂直分布规律为底层或表层的元素含量高于中间各层．土壤元素背景值都高于植物背景值，前者一般为后者的２～２０倍．植物对元素的吸收系数以Ｃｄ最大，Ｃｒ最小．土壤元素含量与有机质含量的相关性因土类不同而异：沙土的有机质含量最低，只有Ｚｎ含量与有机质相关性显著；而盐土的有机质含量最高，有Ｃｏ、Ｃｄ、Ｍｎ、Ｎｉ、Ｃｒ、Ｚｎ６种元素含量与之显著相关．     

含铬污液在土壤中迁移规律的研究

通过静态吸附和动态土柱淋溶实验，研究了含铬污液中Ｃｒ（Ⅲ）、Ｃｒ（Ⅵ）在土壤中的迁移规律。结果表明，土壤对Ｃｒ（Ⅲ）、Ｃｒ（Ⅵ）的等温吸附过程均符合Ｌａｎｇｍｕｉｒ方程，土壤对Ｃｒ（Ⅲ）、Ｃｒ（Ⅵ）的饱和吸附量分别为２．１７＊１０＾４ｍｇ／ｋｇ、１７５ｍｇ／ｋｇ；动态截留量分别为７．００＊１０＾３ｍｇ／ｋｇ、５６．７ｍｇ／ｋｇ。     

煤中痕量元素分布的多变量分析及实验研究

本文用多变量分析法研究了煤中痕量元素的分布，并用实验研究了有机溶剂提取前后青山烟煤中痕量元素的变化。多变量分析结果表明：Ａｓ，Ｃｒ，Ｃｏ，Ｎｉ，Ｃｕ，Ｃｄ，Ｖ，Ｐｂ等元素与Ｂｅ，Ｇｅ在煤中具有不同的分布特征，对青山烟煤的实验研究结果则表明：Ｃｒ，Ｃｏ，Ｎｉ，Ｃｕ，Ｃｄ，Ｐｂ等元素趋向于与煤中的矿物质相结合，而Ｂｅ，Ｇｅ两元素有较强的有机亲和性。实验研究结果与多变量分析结果相符。     

厌氧消化过程中Fe,Co,Ni对NH4^＋—N的拮抗作用

论文以血清瓶为间歇反应器，以醋酸钙为基质，研究了厌氧消化过程中甲烷菌所需要的微量金属营养元素Ｆｅ、Ｃｏ、ＮＩ（１．０ｍｇ／（Ｌ．ｄ），０．１ｍｇ／（Ｌ．ｄ），０．２ｍｇ／（Ｌ．ｄ）对毒性物质ＮＨ４＾＋－Ｎ的拮抗作用，研究结果表明，Ｆｅ、Ｃｏ、Ｎｉ对毒性物质ＮＨ４＾＋－Ｎ有明显的拮抗作用，而且ＮＨ４＾＋－Ｎ浓度越高，Ｆｅ、Ｃｏ、Ｎｉ对其毒性的拮抗作用越明显。     

电镀废水中铜锌铬镍对农业环境的影响

电镀废水排水河涌会污染农业环境,以广东省南,海市平洲地区为例,农田灌溉水中Ｃｕ,Ｚｎ,Ｎｉ的含量超过允许限值１－１４倍,河涌底泥Ｃｕ,Ｚｎ,Ｃｒ,Ｎｉ超标１２－３７倍,土壤超标０．５－２．９倍,作物超标０．３－８倍。进入河涌的Ｃｕ,Ｚｎ,Ｃｒ,Ｎｉ能较快沉积于底泥中。     

Bioavailability and health risk assessment of potentially toxic elements in Thriasio Plain,near Athens,Greece

Elevated concentrations of potentially toxic elements (PTEs) are usually found in areas of intense industrial activity. Thriasio Plain is a plain near Athens, Greece, where most of the heavy industry of the country has been situated for decades, but it also is a residential and horticultural area. We aimed at measuring the levels of PTEs in soils and indigenous plant species and assessing the health risk associated with direct soil ingestion. Samples of soils at roadsides and growing plants were collected from 31 sites of that area. Concentrations of Al, As, Cd, Co, Cr, Cu, Fe, Mn, Mo, Ni, Pb, V and Zn were measured in both soils (as pseudo-total) and aerial plant tissues. We found that As, Cd, Cr, Cu, Ni, Pb and Zn were higher than maximum regulatory limits. Element concentrations in plants were rather lower than expected, probably because indigenous plants have developed excluder behaviour over time. Copper and Zn soil-to-plant coefficients were highest among the other elements; for Cu this was unexpected, and probably associated with recent Cu-releasing industrial activity. Risk assessment analysis indicated that As was the element contributing more than 50 % of the health risk related to direct soil ingestion, followed by Cr, Pb, and, surprisingly, Mn. We concluded that in a multi-element contamination situation, elevated risk of PTEs (such as As, Cr and Pb) may reduce the tolerance limits of exposure to less-toxic elements (here, Mn).     

神木煤矿区土壤重金属污染特征研究

通过对神府煤田开采区3个煤矿区周围土壤Cu、Cd、Cr、Mn、Ni质量分数进行测定及分析,评价了煤田开采对周围土壤的污染程度。结果表明,长期的煤炭资源开发、运输等活动,已导致周围土壤受到重金属不同程度的累积性污染,土壤中Cd、Ni质量分数高于陕西省土壤背景值,且Cd污染程度较高,Ni污染程度较低,而Cu、Cr、Mn基本不受污染。3个煤矿表层土壤各重金属元素质量分数均表现出污染区大于对照区,但这种变化幅度存在一定差异;Cu、Cr、Mn 3种重金属元素虽没有超出背景值,但已表现出一定程度的累积;煤矿周围土壤重金属污染受到开采年限、土壤质地、风向等因素的影响。3个煤矿污染区土壤剖面样品中,5种重金属元素质量分数基本上随着土壤深度的增加呈现降低的趋势,且这种趋势具有波动性。     

西安城市路边土壤重金属含量与污染评价

选择西安市东西和南北方向各两条交通主干道,采集道路两侧的表层土壤样品,通过X-Ray荧光光谱仪测定其重金属的含量.结果表明:西安城市路边土壤中Co、Cr、Cu、Mn、Ni、Pb和Zn的平均含量均高于陕西土壤元素背景值和中国土壤元素背景值,其中,Cu、Pb和Zn的富集程度高,累积量大,As、Mn和Ni累积量相对较小.地累...     

秸秆生物炭修复电镀厂污染土壤的效果和作用机理初探

以某电镀厂污染场地重污染区域土壤为研究对象,利用秸秆生物炭对污染土壤进行稳定化试验,研究不同生物炭添加量(0、10、30、50、70和100 g.kg-1)条件下土壤中重金属全量和形态变化。结果表明,秸秆生物炭能够改变污染土壤中重金属的形态分布,对该污染土壤有明显的稳定化作用。其中对铬的作用效果最明显,随生物炭添加量的增加,残渣态铬含量明显上升,100 g.kg-1生物炭添加量处理残渣态铬含量较对照(1 098.75 mg.kg-1)增幅最大,增加59.51 mg.kg-1;对铜和镍的稳定化效果受添加量的影响,当生物炭添加量分别在70和30g.kg-1以上时,对铜和镍有一定稳定化作用;对该污染土壤中锌则无明显稳定化作用。当生物炭添加量为50 g.kg-1时,4种重金属残渣态总量较对照(1 745 mg.kg-1)明显增加,为1 805.95 mg.kg-1,添加量也较为合理。     

芜湖市三山区菜地土壤重金属污染特征分析

从芜湖市三山区蔬菜基地采集82个农田土壤样品,测试其中的As、Zn、Pb、Cr、Ni、Co、Mn和Fe 8种金属总量和生物有效态含量,对蔬菜基地农田土壤含量特征及来源进行了分析.结果表明:蔬菜基地土壤中8种元素的含量均高于其土壤背景值,其中As(30.01 mg/kg)含量是其土壤背景值的2.83倍.与我国《土壤环境质...     

Spatial distribution and ecological risk assessment of heavy metals in surface sediments from a typical plateau lake wetland, China

Surface sediment (0-15 cm) samples were collected from 31 different grid points throughout the Yilong Lake in April 2004. Samples were subjected to a total digestion technique and analyzed for As, Cd, Cr, Pb, Ni, Cu, and Zn in order to study spatial distribution characteristics based on Kriging method and assess their ecological risks posed by these heavy metals. Results showed that the mean concentrations of these heavy metals were lower than potential effect levels. Patches of higher heavy metal concentrations occurred in the inflow area of the Cheng River and northeast area nearby the road and railway. The higher concentrations of As and Cr also appeared in the east area (lake outlet), while the patches of lower concentrations were uniformly distributed at the southwest corner between Luosewan and Xiaoguoxi. The heavy metal loads such as As, Cd and Pb might come from the common sources due to industrial sewage and traffic pollution, while higher concentrations of Ni, Cr, and Zn in these sediments were dominated by parent rocks. However, Cu originated from both sources. Sediments with respect to As, Cd and Cu were grouped below the effect range low (ERL) at all sites, and with respect to Cr and Pb were grouped into the range from ERL to the effect range median (ERM) at more than 50% of sampling sites. The mean heavy metal toxic units in the Yilong Lake decreased following the order Pb > Cr > As > Ni > Zn > Cd > Cu, with higher contributions to the sum of toxic units of Pb, Cr and As.     

Alterations in some renal parameters of rats induced by aqueous soil extracts

Soil ingestion can be an important route of exposure to contaminants present in the environment. This study examined the effects of exposure to contaminants in aqueous soil extracts from an industrial urban settlement in renal biochemical parameters of treated rats. Male Wistar rats were gavaged with an aqueous soil extract, from the municipality of Rio Grande, Southern Brazil. After exposure, plasma and urine concentrations and plasma protein were assessed compared to rats treated with aqueous soil from relatively unpolluted site (control soil). There was increase in plasma creatinine and total protein in urine, and a decreased glomerular filtration rate in treated rats compared to control. It is possible that Cd, Cr, As, Cu, Pb, Zn, and Ni analyzed in the soil samples and unidentified components may have provoked the observed changes in renal biochemistry of the exposed rat. This may suggest that exposure to contaminated soils can cause damage to the viscera in mammals and it is of public health importance.     

探讨富集因子背景值的选择

为探讨富集因子(EF)背景值的选择,利用黑龙江省甘南县大气降尘重金属元素数据,分别选用黑龙江省A层土壤环境、平均大陆地壳、大陆上地壳为背景,计算Cr、Mn、Ni、Pb、As、Cu、Zn的EF值.研究表明,采用平均大陆地壳和大陆上地壳元素丰度作为背景值时,Pb、Zn、As等元素的EF均值大于2,元素富集一定程度上与人为输入作用有关;采用黑龙江省A层土壤作为背景,As元素EF均值小于2,元素在大气中的富集主要为自然输入;通过相关性分析,As与Cr、Mn、Ni、Cu同为自然源,结果与选用黑龙江省A层土壤为背景时判别结果较一致.本文认为,导致不同背景值取得的EF值差异较大的原因为自然条件下元素的富集和亏损,采用区域土壤元素背景值能够较为准确地判断大气降尘中元素的主要来源.     

Ecological and human health risks from metal(loid)s in peri-urban soil in Nanjing,China

In order to investigate the ecological and human health risks of metal(loid)s (Cu, Pb, Zn, Ni, Cd, Mn, Cr, and As) in peri-urban soils, 43 surface soil samples were collected from the peri-urban area around Nanjing, a megacity in China. The average contents were 1.19, 67.8, 37.6, 105, 167, 44.6, 722, and 50.8 mg kg^?1 for Cd, Cr, Ni, Pb, Zn, Cu, Mn, and As, respectively. A significant positive correlation was found between Cu, Pb, Zn, Cd, Mn, and As (p < 0.01), and Cr had a significant positive correlation with Ni (p < 0.01). Geoaccumulation indices indicate the presence of Cd and As contamination in all of the peri-urban soil samples. Potential ecological risk indices show that the metal(loid)s in the soil could result in higher ecological risks. Cd is the main contributor to the risk, followed by As. The levels of Cu, Pb, Zn, Cd, Mn, and As in stomach and intestinal phases show a positive linear correlation with their total contents. Mn, Zn, Ni, Cd, and Pb in stomach phase showed higher bioaccessibility, while in intestinal phase, Cu, Cr, and As had the higher bioaccessibility. The carcinogenic risk in children and adults posed by As, Pb, and Cr via ingestion was deemed acceptable. The non-carcinogenic risks posed by these metal(loid)s via ingestion to children are higher than to adults and mainly result from As.     

Contamination and vertical distribution of As,Cd, Cr,Cu, Pb,Tl, and Zn in paddy soil irrigated with untreated leachate from tailings retention ponds

The contamination and vertical distribution of As, Cd, Cr, Cu, Pb, Tl, and Zn in paddy soil irrigated with untreated leachate from the tailings retention pond were investigated. As, Cr, Cu, and Zn were slightly contaminated in the surface soil and hence their vertical distribution was not obvious. However, Cd and Pb were highly contaminated in the surface soil, while their concentrations decreased with depth, being negatively correlated with pH and positively with total organic matter. Tl was considerably contaminated in the surface soil and a V-shaped vertical distribution was observed where the concentration increased to a maximum at about 30 cm depth and decreased thereafter. The findings revealed that the regular irrigation with untreated leachate from the tailings retention ponds could cause considerable contamination of Cd, Pb, and Tl, and thus tailings should be stringently treated before disposal to minimize their potential environmental impacts on the surroundings.