二苯甲酮类紫外防晒剂发光菌急性毒性及QSAR研究

二苯甲酮类化合物广泛用于防晒剂、塑料添加剂、香味剂等。随着紫外防晒产品的大量使用,其环境及健康风险越来越受到人们的关注。为揭示二苯甲酮类污染物的毒性特征,选择了14种二苯甲酮类化合物作为目标化合物,测试了它们对发光细菌的急性毒性效应。分别运用二维、三维定量构效相关技术和分子对接技术探讨了目标化合物的分子结构特征对毒性效应的影响。结果表明14种二苯甲酮类化合物对发光菌急性毒性的EC50值在17.67到243.82 mg·L-1范围内,其中2-羟基-4-甲氧基-5-磺酸基二苯甲酮的急性毒性最低,2,2',4,4'-四羟基二苯甲酮的毒性最高。羟基取代的二苯甲酮化合物的急性毒性随着分子中羟基数量的增加而升高;具有相同羟基数量的二苯甲酮类化合物,羟基位于苯环4-位时毒性最高,3-位时次之,2-位时毒性最低。QSAR结果表明,运用静电场、氢键受体场和氢键供体场能很好解释这类化合物的毒性特征,若在苯环4-位引入带正电荷的官能团、在苯环2-,4-位引入氢键受体,都将导致毒性升高。上述研究结果将为科学评价该类化合物的潜在生态风险提供基础数据。     

Acute toxicity of chlorpyrifos to embryo and larvae of banded gourami Trichogaster fasciata

This study elucidated the acute toxicity of chlorpyrifos on the early life stages of banded gourami (Trichogaster fasciata). To determine the acute effects of chlorpyrifos on their survival and development, we exposedthe embryos and two-day-old larvae to six concentrations (0, 0.01, 0.10, 1.0, 10 and 100 µg L^?1) of chlorpyrifos in plastic bowls. Log-logistic regression was used to calculate LC10 and LC50 values. Results showed that embryo mortality significantly increased with increasing chlorpyrifos concentrations. The 24-h LC10 and LC50 values (with 95% confidence limits) of chlorpyrifos for embryos were 0.89 (0.50–1.58) and 11.8 (9.12–15.4) µg L^?1, respectively. Hatching success decreased and mortality of larvae significantly increased with increasing concentrations of chlorpyrifos. The 24-h LC10 and LC50 values (with 95% confidence limits) of chlorpyrifos for larvae were 0.53 (0.27–1.06) and 21.7 (15.9–29.4) µg L^?1, respectively; the 48-h LC10 and LC50 for larvae were 0.04 (0.02–0.09) and 5.47 (3.77–7.94) µg L^?1, respectively. The results of this study suggest that 1 µg L^?1 of chlorpyrifos in the aquatic environment may adversely affect the development and the reproduction of banded gourami. Our study also suggests that banded gourami fish can serve as an ideal model species for evaluating developmental toxicity of environmental contaminants.     

污染水体中河蚬的生物毒性响应研究进展

河蚬作为广泛分布于世界各国的典型底栖生物,由于其活动性低、滤食性等特征被广泛用作指示生物研究多种水体污染物的生物有效性。但迄今为止,尚没有系统论述污染水体中河蚬生物毒性响应的研究进展。为此,本文从污染物种类、测试指标、试验参数等角度探讨了过去30多年间河蚬在氨、重金属、有机污染物生物富集及生物毒性效应等方面的研究过程及主要成果。以往研究主要以河蚬生物体内累积、形态学及行为学观察、生化指标、代谢组学、基因完整性等指标表征污染水体的生物毒性效应,并随着分子生物学的发展已逐步由多指标全面表征代替单一指标测试。此外,现有研究多偏重于重金属和持久性有机污染物,对氨、新型污染物及纳米材料的河蚬生物毒性效应探讨尚处于起步阶段。河蚬在自然水体污染状况评估、污染水体的生物修复、水体毒性预测等方面具有较高适用性,但河蚬在沉积物毒性鉴定评估(TIE,Toxicity Identification and Evaluation)中的应用研究依然较为缺乏,有待进一步开展。     

吡唑醚菌酯对不同阶段斑马鱼的毒性效应评价

为评价吡唑醚菌酯对鱼类不同生命阶段的毒性效应,以斑马鱼(Brachydanio rerio)为测试生物,测定了其对斑马鱼胚胎、仔鱼(孵化3 d和孵化12 d)和成鱼的急性毒性及对胚胎和仔鱼(孵化3 d)的发育毒性。结果表明,吡唑醚菌酯对斑马鱼胚胎、仔鱼(孵化3 d)、仔鱼(孵化12 d)和成鱼的96 h-LC50分别为0.0578(0.0540~0.0631)、0.0299(0.0282~0.0320)、0.0330(0.0310~0.0350)和0.0756(0.0692~0.0862)mg·L-1,其毒性大小依次为仔鱼(孵化3 d)仔鱼(孵化12 d)胚胎成鱼。与对照组相比,吡唑醚菌酯0.101 mg·L-1处理,可对斑马鱼胚胎24 h自主运动产生显著抑制作用;0.0609、0.0777和0.101 mg·L-1处理,可对斑马鱼胚胎48h心跳速率产生显著抑制作用;0.0609和0.0777 mg·L-1处理,可对斑马鱼胚胎96 h孵化仔鱼体长产生显著抑制作用。在供试浓度下吡唑醚菌酯暴露96 h后,均可对斑马鱼仔鱼(孵化3 d)体重和体长产生明显的抑制效应,对斑马鱼仔鱼(孵化3 d)心跳未产生明显影响。在高浓度下,吡唑醚菌酯可诱导斑马鱼胚胎产生畸形,主要包括心包水肿、卵黄囊水肿等;而对仔鱼(孵化3 d)未观察到明显的致畸效应。     

Distribution,Sources, and Possible Adverse Biological Effects of Trace Metals in Surface Sediments of a Tropical Estuary

Metal (Cu, Zn, Pb, Cd, Ni, Co, and Fe) contamination in sediments from a tropical estuary (Ébrié Lagoon, Ivory Coast) was assessed using pollution indices, multivariate analyses and sediment quality guidelines (SQGs). The results demonstrate that increased input of the studied metals occurred over the past 6 years compared to that from 20 years ago, due to rapid population growth, along with the increase of industrial and agricultural activities in the vicinity of the estuary. Ébrié Lagoon was also found to be one of the most contaminated tropical coastal estuaries. Very high average total organic carbon (TOC) content was found (1.9–3.70%) with significant spatial variation as a result of the influence of anthropogenic activities. This study also found that TOC plays an important role in the distribution of Cu, Zn, Co, and Cd in the Ébrié Lagoon sediments. Moderate to high sediment contamination was observed for Cd and Cu, moderate contamination was observed for Zn and Pb, while low contamination was observed for Ni, Co, and Fe. Cluster analysis (CA) and principal component analysis (PCA) investigation revealed that Cu, Zn, Cd, and Co result mainly from anthropogenic sources while Pb, Ni, and Fe may be of natural origin. The pollution-loading index (PLI) indicated that all of the sites close to wastewater discharges were highly polluted. The sediments are likely to be an occasional threat to aquatic organisms due to Cu, Zn, Pb, Cd, and Ni contents, based on the SQGs approach.     

电解锰渣无害化处理技术简

电解锰渣是湿法电解金属锰工艺产生的废渣，环境危害性大、治理难度大。为消除锰渣的污染性，实验研究了锰渣浸出液中污染物种类，并分别采用生石灰和氢氧化钠作处理剂，从成本、处理效果方面进行比较，确定处理剂以及最佳运行条件。得出结论：锰渣中主要污染物为锰和氨氮（分别超过相关标准453倍和26倍），选取生石灰做处理剂，处理后的锰渣，浸出液中锰离子和氨氮的减排量分别达到99%和97%以上，水溶性锰离子浓度低于5 mg/L、氨氮浓度低于25 mg/L，均达到《污水综合排放标准》（GB8978-1996）中的排放标准；反应时间30 h以上、避免雨淋、不通风、无日照为最佳反应条件。     

VENTILATORY RESPONSES OF BLUEGILL SUNFISH TO SUBLETHAL,FLUCTUATING EXPOSURES TO HEAVY METALS (Zn++ and Cu++)1

ABSTRACT Minicomputer interfaced, continuous, noncontact sensing of the ventilatory behavior of the bluegill (Lepomis macrochirus) was used to investigate the response to exposure to solutions of copper and zinc under various modes of application. The results of these studies indicate that fish respond to sublethal concentrations of these toxicants by increasing the average ventilatory rate as well as decreasing the amplitude of the ventilatory signal. Appropriate statistics for the analysis of these data are also described.     

Comprehensive Analysis of Radioactive and Chemical Contamination of Water Bodies in the Area of Radium-Industry Waste Storage

Genotoxicity and cytotoxicity of water samples from the creeks flowing through the area of radium mining waste storage into the Ukhta River and from this river were assessed using biological tests with Allium schoenoprasum L. Chemical analysis of the samples indicated that concentrations of parent heavy natural radionuclides, ²¹⁰Pb, and ²¹⁰Po do not exceed the allowable level. Of ten heavy metals, only Zn and Mn concentrations exceeded MACs. The results of biological tests provided evidence for the significantly increased genotoxicity of water samples. The mitotic index increased with an increase in the concentration of Zn ions and manifested an inverse dependence on the activity of ²³⁸U. The genotoxic effect linearly depended on Zn concentration. Possible mechanisms responsible for the induction of these biological effects are discussed.     

Regional differences in mercury levels in aquatic ecosystems: A discussion of possible causal factors with implications for the Tennessee river system and the Northern Hemisphere

Concern about mercury pollution from atmospheric deposition has risen markedly in the last decade because of high levels of mercury in freshwater fish from relatively pristine waters. Whereas high concentrations have been found principally in Canada, the northern United States, and Scandinavia, they have also recently been observed throughout much of Florida. Recent surveys of the Tennessee River system, however, have found no locations where fish levels exceed EPA guidelines for fish consumption. This paper evaluates a number of factors that may cause certain regions in the northern hemisphere to experience unacceptable fish mercury levels while other regions do not. Relevant regional differences include: (1) Waters of the Tennessee River system are generally nonacidic (pH>6) and well buffered, whereas 16%, 22%, and 40% of the lakes in upper Midwest, Northeast, and Florida, respectively, have acid-neutralizing capacities below 50 μeq/liter. Acidity correlates highly with fish mercury levels in a number of lake surveys, and experimental manipulations of acidity have significantly raised fish mercury levels. (2) The ratio of land area to water surface area in the Tennessee Valley averages about 30, whereas it is 15 in the upper Midwest and 6 in Florida. Low ratios allow mercury in precipitation to be directly deposited to aquatic bodies, without an opportunity for the mercury to be sequestered by terrestrial ecosystems. (3) Stream organic matter concentrations in Florida, the upper Midwest, and Sweden are 2–10 times those in the Tennessee Valley. Mercury binds strongly to organic matter, and organic matter transport in runoff is a major pathway by which mercury enters aquatic ecosystems.