土壤重金属污染对蚯蚓的急性毒性效应研究

测定了草甸棕壤条件下 ,Cu、Zn、Pb、Cd单一 /复合污染对蚯蚓的急性致死及亚致死效应 .结果表明 ,Cu、Pb浓度与蚯蚓死亡率显著相关 (α=0 .0 5 ,RCu=0 .86 ,RPb=0 .87) ,Cu浓度与生长抑制率显著相关 (α=0 .0 5 ,RCu=0 .84) ,其他供试重金属浓度与蚯蚓死亡率和生长抑制率相关性不显著 .蚯蚓个体对重金属毒性的耐受程度差别较大 .其毒性阈值 (引起个体蚯蚓死亡浓度 )分别为 :Cu 30 0mg·kg-1,Zn 130 0mg·kg-1,Pb 170 0mg·kg-1,Cd 30 0mg·kg-1.LC50 分别为 :Cu 40 0～ 45 0mg·kg-1,Zn15 0 0～ 190 0mg·kg-1,Pb2 35 0～ 2 40 0mg·kg-1,Cd 90 0mg·kg-1.在Cu、Zn、Pb、Cd单一污染引起 >10 %蚯蚓死亡的浓度下 ,复合污染导致 10 0 %蚯蚓死亡 ,表明复合污染极强的协同效应 .     

铅、镉和锌3种重金属离子对水螅的联合毒性研究

以水螅为实验生物,采用相加指数法,研究了铅、镉和锌3种重金属离子复合污染物的联合毒性.结果表明:铅和锌共存时的联合毒性为拮抗作用,而镉和锌,镉和铅共存时主要表现为毒性剧增的协同作用.铅、镉和锌三者共存时的联合毒性较为复杂,三者浓度比1∶1∶1时表现为协同作用,而毒性比1∶1∶1时表现为拮抗作用.     

铅、镉、铬单一和复合污染对青菜种子萌发的生物学效应

重金属污染是当今世界上倍受重视的一类公害。重金属以汞毒性最大 ,镉次之 ,铅、铬、砷也有相当毒性 ,有人称之为“五毒”。冶炼和采矿是向环境中释放重金属的最重要的污染源。此外 ,不少工业部门也通过三废向环境中排放重金属。农作物受到重金属污染后 ,不仅严重影响其产量和质量 ,更为严重的是重金属经食物链进入人体 ,在人体内富集 ,危害人类健康。近几年 ,国外利用陆生植物进行毒性试验已有所增加 ,其中包括植物种子发芽毒性试验[1] 。植物种子发芽毒性试验较其它毒性试验方法有两大优点 :一是方法简单 ,持续时间短 ;二是这种方法对毒物…     

东南景天对锌、镉复合污染的反应及其对锌、镉的吸收和积累特性

东南景天(Sedum alfredii Hance)已被鉴定为一种中国原生的新的锌超积累植物。 本文主要研究了锌(Zn)、镉(Cd)复合处理水平对东南景天的生长及其对锌、镉的吸收积累特性的影响。 结果表明,在Zn/Cd复合水平为500/100 祄ol/L时,植物生长最佳。Zn/Cd在东南景天叶片、茎部和根系中含量随着Zn/Cd处理水平的提高而增高。在Zn/Cd 复合水平为50/400 祄ol/L时茎叶中Cd含量达最高,其中叶片Cd含量达12.1 g/kg;在Zn/Cd 复合水平为1 000/50 祄ol/L时茎叶中Zn含量达最高, 其中茎中Zn含量达 23.2 g/kg。 植株各部位Cd含量的分布为:叶片>茎>>根系,而Zn在体内的分布为: 茎>叶片>>根系。 Zn、Cd在地上部和根部的积累量也随着处理水平的提高而增加,分别在Zn/Cd复合水平为250/400和500/100 祄ol/L下达高峰值。 东南景天地上部积累最高Zn和Cd的量分别达11和5 g/plant, 其比根系的积累量分别大10和25余倍。 Zn、Cd对东南景天的生长、吸收积累的相互作用依赖于Zn/Cd复合水平和植物部位。 在适宜Zn/Cd 处理水平范围内,Zn和Cd的吸收和积累具有相互促进作用。 高Zn或高Cd处理均抑制了植物对Zn和Cd的吸收和积累。 本研究结果表明,东南景天不仅具有忍耐高Zn/Cd复合污染,而且具有超量积累Zn和Cd的特异能力。 它为进一步研究植物Zn、Cd     

高铜、高锌猪粪对蚯蚓的急性毒性效应研究

测定了高Cu、高Zn猪粪条件下Cu、Zn单一与复合污染对蚯蚓的急性致死及亚致死效应.结果表明,Cu、Zn浓度与蚯蚓死亡率显著正相关(a=0.05,r_Cu=0.99,r_Zn=0.99),与体重增长率显著负相关(a=0.05,r_Cu=-0.99,r_Zn=-0.96).蚯蚓个体对Cu、Zn的耐受程度不同,其毒性阈值(引起蚯蚓个体死亡浓度)分别为:Cu250mg·kg^-1、Zn400mg·kg^-1.LD₅₀分别为:Cu646.68mg·kg^-1、Zn947.38mg·kg^-1.复合污染情况下,Cu浓度为250、500mg·kg^-1时,Cu、Zn复合污染表现为协同效应;Cu浓度为750mg·kg^-1时,Cu、Zn复合污染表现为拮抗效应,可见,猪粪中Cu、Zn复合污染的毒性效应与各组浓度组合密切相关.     

东南景天对锌、镉复合污染的反应及其对锌、镉的吸收和积累特性

Sedum alfredii Hance has been identified as a new Zn-hyperaccumulator native to China. In this study, responses and metal accumulation of S. alfredii were examined under Zn/Cd complex polluted conditions. The results showed that optimal growth of S. alfredii in terms of the maximum dry matter yield was observed at Zn/Cd complex level of 500/100 祄ol/L. Plant cadmium (Cd) or zinc (Zn) concentrations increased with increasing Cd or Zn supply. During the 20 d treatment, the highest Cd concentration in the leaves reached 12.1 g/kg at Zn /Cd level of 50/400 祄ol/L and that of Zn in the stems was 23.2 g/kg at Zn/Cd level of 1 000/50 祄ol/L. The distribution of Cd in different plant parts decreased in the order: leaf ＞ stem≥ root, whereas that of Zn was: stem ＞ leaf ≥ root. The accumulation of Cd and Zn in the shoots and roots of S. afredii increased with the increasing of Zn/Cd supply levels, peaked at Zn/Cd levels of 250/400 and 500/100 祄ol/L, respectively. The highest Cd and Zn uptake by the shoots was approximately 5 and 11 mg/plant, and was over 20 and 10 times higher than those in the roots, respectively. Zn supply at levels ≤ 500 祄ol/L increased plant Cd concentrations, whereas high Zn supply decreased root Cd but did not affect leaf Cd concentrations in S. alfredii. Low Cd supply increased Zn concentration in the leaves, but Cd supply higher than 50 祄ol/L considerably reduced root Zn concentrations, especially at low Zn level. These results indicate that S. alfredii can tolerate high Zn/Cd complex levels and has an extraordinary ability to hyperaccumulate not only Zn but also Cd. It could provide a new valuable plant material for understanding the mechanisms responsible for co-hyperaccumulation of Zn and Cd as well as for phytoremediation of the Cd/Zn complex polluted soils.     

多菌灵和敌百虫单一与复合污染对蚯蚓的毒性效应研究

采用滤纸接触法研究了赤峰市周边地区普遍使用的农药多菌灵和敌百虫单一与复合污染对蚯蚓毒性效应.单一试验结果表明蚯蚓在这两种农药作用下表现出不同的中毒症状和死亡情况,敌百虫的毒性大于多菌灵的毒性,48 h时多菌灵和敌百虫的LC50分别为1.2795 g·L-1和0.0511 g·L-1;复合试验结果表明,多菌灵与敌百虫混合后毒性减弱,即二者复合作用表现为拮抗作用.     

蜈蚣草耐铅、铜、锌毒性和修复能力的研究

重金属复合污染是主要土壤污染类型之一。为了探明蜈蚣草修复土壤重金属复合污染的能力,土培试验研究了分别添加不同浓度铅、铜、锌条件下蜈蚣草生物量变化,结果表明,不同浓度铅和较低浓度锌处理下蜈蚣草生物量呈显著性地增加,土壤Pb、Zn添加浓度分别为1750mg／kg和1350mg／kg,蜈蚣草生物量最大。说明蜈蚣草有极强的耐Pb、Zn毒性能力,能在较高有效态Pb或Zn污染土壤上正常生长。蜈蚣草具有一定的耐Cu毒性能力,在Cu耐性方面,蜈蚣草可能存在生态型的差异。以上结果说明,利用蜈蚣草修复萃取Pb—As,Zn—As,Cu-As等复合污染土壤上As有重要的意义。     

镉、汞复合污染对土壤脲酶和酸性磷酸酶活性的影响

通过土壤培养试验, 研究了重金属镉（Cd）、汞（Hg）复合污染对小粉土和黄红壤脲酶和酸性磷酸酶活性的影响.结果表明：整个培养过程中,Cd、Hg单一及复合污染都对两种土壤中脲酶和酸性磷酸酶的活性具有明显抑制作用,且随重金属浓度增强而增强（浓度≤1 mg·kg^-1Cd除外）.与单一Cd或Hg污染相比,同剂量Cd和Hg复合污染时两种酶活性的净变化量均大于0,表明Cd和Hg复合污染在两种土壤中对土壤脲酶和酸性磷酸酶活性的抑制作用均表现为一定的协同作用.所有处理黄红壤脲酶和酸性磷酸酶活性均高于小粉土,这可能与黄红壤有机质和粘粒含量相对较高有关.     

汞、镉复合污染对金鱼藻的影响及其抗性机制的探讨

研究了金鱼藻在不同浓度 Hg2 +、Cd2 +以及 Hg2 +、Cd2 +共同胁迫下叶绿素含量、叶绿素 a/b值、可溶性蛋白含量、SOD活性和游离脯氨酸含量等的变化。结果表明 :低浓度 Cd2 + (≤ 2 mg.L- 1)对上述指标有激应性反应 ,低浓度 Hg2 + (≤ 0 .5mg.L- 1)对叶绿素含量、叶绿素 a/b值、可溶性蛋白含量、SOD活性也有激应性反应 ;可以认为这是植物的一种保护性机制。但随着 H2 +、Cd2 +处理浓度增大 ,上述生理指标呈下降趋势 ,表明植物细胞遭受伤害。Hg2 + 、Cd2 + 共同胁迫下上述生理指标下降幅度明显增大 ,表现为协同作用。     

Individual and combined toxicity of three heavy metals,Cu, Cd and Cr for the marine copepod Tisbe holothuriae

The acute toxicity of Cu, Cd and Cr to the marine copepod Tisbe holothuriae, Humes, was estimated by static bioassays and the LC _inf50 ^su48h (in mg/l) was calculated. Copper proved to be the most toxic (LC _inf50 ^su48h = 0,08 ± 0,01 mg/l) and chromium the least toxic (LC _inf50 ^su48h = 8,14 ± 0,05 mg/l), while cadmium showed an intermediate toxicity (LC _inf50 ^su48h = 0,97 ± 0,04 mg/l).In mixtures of the two metals an obvious synergism of the effects was observed in all cases. In all three combinations with two metals (Cu + Cd, Cu + Cr, and Cd + Cr) the mortality was higher than that expected on a purely additive basis. The mixture of the three metals presented a higher toxicity than that of the individual metals acting separately, but lower than that of all two metals mixture.     

Effects of heavy metals Cd2+, Pb2+ and Zn2+ on DNA damage of loach Misgurnus anguillicaudatus

The effects of heavy metals Cd2+, Pb2+ and Zn2+ at 0.05, 0.5 and 5.0 mg/L level and their interactions at 0.5 mg/L level on DNA damage in hepatopancreas of loach Misgurnus anguillicaudatus for 1-35 days exposure were examined by single cell gel electrophoresis (SCGE). For each test group, 20 loaches with similar body size (5.17-7.99g; 11.79-13.21 cm) were selected and kept in aquaria with dechlori-nated water at (22±1)℃ and fed a commercial diet every 48 h. According to the percentage of damaged DNA with tail and its TL/D (tail length to diameter of nucleus) value, the relationship between DNA damage degree and heavy metal dose and exposure time was determined. Results showed that the percentage of damaged DNA and the TL/D value were increased with the prolonged exposure time. The highest percentage (84.85%) of damaged DNA was shown in 5.0 mg/L Zn2+ group after 28 days exposure and the biggest TL/D value (2.50) in all treated groups after 35 days exposure. During the first treated week, the damnification of DNA was mainly recognized as the first level, after that time, the third damaged level was mostly observed and the percentage of damaged DNA was beyond 80%. The joint toxic effects among Cd2+, Pb2+ or Zn2+ revealed much complexity, but it generally displayed that the presence of Cd2+ could enhance the genotoxicity of Pb2+ or Zn2+. In conclusion, the results suggested that there was a significant time-and dose-depended relationship between the heavy metal and DNA damage in hepatopancreas of loach, and SCGE could represent a useful means to evaluate the genotoxicity of environmental contamination on aquatic organisms.     

Accumulation of Ag, Cd, Co, Cu, Hg, Ni and Pb in Pavlova viridis Tseng (Haptophyceae)

The flagellate alga Pavlova viridis Tseng was investigated in the laboratory for accumulation of the heavy metals, silver, cadmium, cobalt, copper, mercury, nickel and lead. The cultures were grown in an artificial seawater medium mixed with the individual metals at different concentrations. Based on data from the controls, the baseline metal concentrations in P. viridis were shown to be in an order of Cu > Pb > Co > Cd > Ni > Ag > Hg. In the experimental groups, the seven metals displayed different isotherm equilibrium patterns and the metal uptake capacity of the alga was Ni > Pb > Co > Hg > Cu > Cd > Ag at equilibrium. When assessed using the bioconcentration factors, metal accumulation by P. viridis was demonstrated to be the most efficient at a concentration of 0.001 mg L-1 for Ag, Cd and Co, and at 0.01 mg L-1 for Cu, Hg, Ni and Pb. This study suggests that P. viridis can be a source of mineral supplements in mariculture. The alga is not, however, recognized as an effective agent for removing heavy metals from wastewater. This revised version was published online in June 2006 with corrections to the Cover Date.     

镉和十二烷基硫酸钠对克氏原螯虾的单一和联合毒性

采用静水生物测试法,研究了十二烷基硫酸钠(SDS)和Cd2+对克氏原螯虾的单一和联合毒性效应。结果表明,SDS对克氏原螯虾24、48、72和96h的半致死浓度(LC50)分别为1365.60、1171.72、1128.43和1120.43mg·L-1,安全浓度(SC)为258.79mg·L-1;Cd2+对克氏原螯虾24、48、72和96h的LC50分别为1197.09、142.06、90.85和82.64mg·L-1,SC值为0.6mg·L-1。SDS和Cd2+对克氏原螯虾的毒性分别为低毒和高毒,毒性大小为Cd2+>SDS。联合毒性试验表明,二者毒性比为1∶1,暴露时间为24、48、72和96h时,相加指数(AI)分别为0.335、0.017、0.030和0.032,联合作用结果均为毒性增强的协同作用。     

青霉菌Penicillium janthinellum 菌株 GXCR的高抗重金属盐及其对Cu2+和 Zn2+离子吸收的特性

从广西某矿区污泥中分离了一株高抗Cu2 的真菌,编号为GXCR,根据形态和5.8SrRNA基因的内转录间隔子区的DNA序列同源性将其鉴定为Penicilliumjanthinellum。GXCR能够耐200mmolL–1的Cu2 ,在5mmolL–1Mn2 存在下,可在含800mmolL–1Cu2 的PDA上生长。在PDA培养基上,限制GXCR生长的其它金属盐的最小浓度(mmolL–1)依次为:Zn2 ,>1200;Al3 ,>500;Na ,>250;Mn2 ,>200;Cd2 ,50;Cr3 ,>60;Cr6 ,>3;Ni2 ,20;Pb2 ,50。对Cu2 、Cr6 、Pb2 和Zn2 ,的抗性是pH依赖性的,在pH3~7,随着pH的升高,其抗性急剧下降。在含3种金属盐混合物的PDL(未添加琼脂的PDA)中的GXCR生长的正交实验结果表明:金属盐之间存在显著的毒性协同效应;毒性协同效应强度不仅与盐的种类也与组成盐之间的浓度相关;GXCR有较高的抗3种金属盐混合物的能力。原子吸收测定结果表明:在含20mmolL–1Cu2 去离子水溶液中,未经NaOH预处理的自然菌体的Cu2 吸收量为38.1mgg-1干菌体,经200mmolL–1NaOH预处理的菌体的吸收量为76.9mgg-1干菌体;在含1200mmolL–1Zn2 的PDL(未加琼脂的PDA)中,接种分生孢子并连续培养7d后,菌体的Zn2 吸收量为258.3mgg-1干菌体。     

Tolerance and hyperaccumulation of a mixture of heavy metals (Cu,Pb, Hg,and Zn) by four aquatic macrophytes

In the present investigation, four macrophytes, namely Typha latifolia (L.), Lemna minor (L.), Eichhornia crassipes (Mart.) Solms-Laubach, and Myriophyllum aquaticum (Vell.) Verdc, were evaluated for their heavy metal (Cu, Pb, Hg, and Zn) hyperaccumulation potential under laboratory conditions. Tolerance analyses were performed for 7 days of exposure at five different treatments of the metals mixture (Cu⁺², Hg⁺², Pb⁺², and Zn⁺²). The production of chlorophyll and carotenoids was determined at the end of each treatment. L. minor revealed to be sensitive, because it did not survive in all the tested concentrations after 72 hours of exposure. E. crassipes and M. aquaticum displayed the highest tolerance to the metals mixture. For the most tolerant species of aquatic macrophytes, The removal kinetics of E. crassipes and M. aquaticum was carried out, using the following mixture of metals: Cu (0.5 mg/L) and Hg, Pb, and Zn 0.25 mg/L. The obtained results revealed that E. crassipes can remove 99.80% of Cu, 97.88% of Pb, 99.53% of Hg, and 94.37% of Zn. M. aquaticum withdraws 95.2% of Cu, 94.28% of Pb, 99.19% of Hg, and 91.91% of Zn. The obtained results suggest that these two species of macrophytes could be used for the phytoremediation of this mixture of heavy metals from the polluted water bodies.     

Plant Cd2+ and Zn2+ status effects on root and shoot heavy metal accumulation in Thlaspi caerulescens

* In this study we address the impact of changes in plant heavy metal, (i.e. zinc (Zn) and cadmium (Cd)) status on metal accumulation in the Zn/Cd hyperaccumulator, Thlaspi caerulescens. * Thlaspi caerulescens plants were grown hydroponically on both high and low Zn and Cd regimes and whole-shoot and -root metal accumulation, and root (109)Cd(2+) influx were determined. * High-Zn-grown (500 microm Zn) plants were found to be more Cd-tolerant than plants grown in standard Zn conditions (1 microm Zn). Furthermore, shoot Cd accumulation was significantly greater in the high-Zn-grown plants. A positive correlation was also found between shoot Zn accumulation and increased plant Cd status. Radiotracer (109)Cd root flux experiments demonstrated that high-Zn-grown plants maintained significantly higher root Cd(2+) influx than plants grown on 1 microm Zn. It was also found that both nickel (Ni) and copper (Cu) shoot accumulation were stimulated by high plant Zn status, while manganese (Mn) accumulation was not affected. * A speculative model is presented to explain these findings, suggesting that xylem loading may be one of the key sites responsible for the hyperaccumulation of Zn and Cd accumulation in Thlaspi caerulescens.     

Stability of Ca2+-, Cd2+-, Cu2+-[illite-humic] complexes and pH influence

Decomposition of fresh plant residues in soil is expected to produce humic fractions varying in molecular size. It was hypothesized that metal adsorption by soil, to some degree, will depend on humic acid content and molecular size. The latter is expected to vary in number and type of functional groups. In this study, illite-humic complexes were used to evaluate Ca²⁺, Cd²⁺, and Cu²⁺ adsorption and how this adsorption was affected by humic acids, differing in molecular size, under various pH values. Potentiometric titration using ion-selective electrodes with a stop-and-go procedure was employed to evaluate metal-[illite-humic] complex formation. The results showed that illite-humic complexes exhibited at least two types of metal-ion adsorption sites (low and high affinity) and molecular size of humic fractions had a large potential influence on total metal adsorption but a relatively smaller influence on metal-complex stability. Relative strength of metal-ion-[illite-humic] complexes followed the order of Cu²⁺>Cd²⁺>Ca²⁺ and were affected by pH, especially for low metal-ion affinity sites. Magnitude of metal-[illite-humic] stability constants, depending on molecular size of humic fraction and pH, varied on a log-scale from 3.52 to 4.21 for Ca²⁺, 4.38 to 5.18 for Cd²⁺and from 5.23 to 5.83 for Cu²⁺. There was an approximate 5-fold difference in these stability constants between the three different sizes of humic fractions. The larger the humic fraction, the lower the metal-[illite-humic] stability constant. This revised version was published online in June 2006 with corrections to the Cover Date. This revised version was published online in June 2006 with corrections to the Cover Date. This revised version was published online in June 2006 with corrections to the Cover Date.     

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。