发光细菌法评价排污口污水中总有机污染物毒性

利用发光细菌发光原理,建立以明亮发光杆菌(photobacterium phosphoreum)T3变种作为毒性测试物种检测环境中总有机污染物毒性的方法,并用该方法评价环渤海排污口总有机物毒性分布状况。测试结果显示,建立的相关方程及相关性显著性检验P0.01,HgCl2 EC50值基本在0.10±0.02 mg/L范围内波动,指标符合方法规定要求,即发光菌监测排污口中总有机污染物毒性测试结果是准确可信的。用发光细菌法评价环渤海20个排污口,其中剧毒占10%,高毒占25%,重毒占5%,中毒占10%,低毒占50%。发光细菌法能客观、快速、准确地反映废水中总有机污染物毒性状况,该方法在水质监测总有机物毒性中有着广泛的应用前景。     

基于荧光素酶发光体系测试饮用水中农药的综合毒性

利用农药对荧光素酶催化的发光反应具有非常显著的抑制作用,对甲拌磷、乐果、毒死蜱、百草枯等4种农药分别进行单一毒性和等比混合法联合毒性测试,建立了一种快速检测饮用水中农药综合毒性的生物学方法。试验结果表明,单一农药乐果、甲拌磷、百草枯和毒死蜱的EC50值分别为7.56 mg/L、12.7 mg/L、19.0 mg/L和65.3 mg/L,毒性强弱顺序为乐果甲拌磷百草枯毒死蜱,相关系数≥0.995;将4种农药以等比方式配制成两两混合液后,当质量浓度为20.0 mg/L~100 mg/L时,除百草枯与毒死蜱表现为毒性协同外,其他两两混合农药的毒性以拮抗作用为主。     

化工园区污水特征分析及生物毒性研究

对天津市某化工园区9个主要污染企业及总排放口的废水进行监测分析,测定了12项水质常规指标和8项重金属指标,采用主成分分析法和生物毒性测试对化工区废水的水质进行了综合评价。结果表明,水质指标中大部分常规项目(如COD、氨氮和重金属含量)在多数企业污水中都符合排放标准,总氮、总磷污染较重,其中磷的污染最严重,最高超标23.83倍;影响污水性质的第一主成分为氯化物、电导率、全盐量和Cr,第二主成分为溶解氧、悬浮物、氨氮、总氮、总磷和As;废水具有一定的生物毒性,且不同化工企业之间毒性差异较大。水质化学测定的结果和生物毒性程度有一定相关性,但也存在差异,应该结合两者综合评价水质污染特征。     

非离子氨对NO-2-N作用于草鱼种毒性的影响

在(25±1)℃水温条件下,通过急性毒性实验,探讨非离子氨对NO-2-N作用于草鱼种毒性的影响.结果表明,在不加非离子氨时,N0-2N对草鱼种48 hrLC50和96 hrLC50值分别为6.76、5.99mg/L,而当非离子氨达0.8 mg/L,其值分别为3.54、2.41 mg/L.这说明非离子氨增强了NO-2-N对草鱼种的致死效应.     

水质生物毒性预警系统建设及在海宁市饮用水源保护中的应用

介绍了基于微生物燃料电池原理的水质生物毒性预警系统,说明了其在海宁市饮用水源保护中的应用。该水质生物毒性预警系统具有可感知毒性物质及有机物质污染、响应迅速、灵敏度高、维护管理容易、管理费用低等特点。     

对苯二酚对海洋底栖双壳类毛蚶和紫贻贝毒性效应研究

通过对中国近岸常见底栖双壳类毛蚶（Scapharca subcrenata）、紫贻贝（Mytilus edulis）急性和慢性毒性试验，运用Log-logistic模型及Weibull毒性效应阈值模型计算对苯二酚对2种受试生物的半致死效应浓度（LC₅₀）、非检测效应浓度（NDEC)及无观测效应浓度（NOEC）；分析慢性毒性试验对受试生物体质量、体长及消化腺超氧化物歧化酶（SOD）活性的影响。结果显示，对苯二酚对毛蚶、紫贻贝的LC₅₀分别为34.10和66.50 mg/L，NDEC分别为0.36和0.50 mg/L，NOEC分别为0.40和0.60 mg/L。慢性试验周期内受试生物体质量、体长的组内与组间差异不显著（P>0.1）；SOD酶活性仅在个别时间段对照组和处理组间存在显著差异（P<0.05）。     

春节烟花爆竹燃放期间苏州市区PM2.5组分特征分析

为了解春节期间烟花爆竹燃放对苏州市空气质量的影响,在苏州市南门监测点利用在线监测仪器(包括颗粒物分析仪、在线离子色谱、OC/EC分析仪和重金属分析仪)对环境空气中的PM2.5浓度水平、颗粒物水溶性离子、有机碳(OC)、元素碳(EC)和重金属浓度进行连续观测。通过比较烟花爆竹燃放时段和正常时段的PM2.5浓度水平和化学组成,分析并探讨烟花爆竹燃放对PM2.5浓度水平及其组分特征的影响。研究结果表明,大量烟花爆竹的集中燃放造成了PM2.5短时严重污染,最高质量浓度达到了571μg/m3,但随烟花爆竹燃放的减少,PM2.5浓度迅速降低。在烟花爆竹燃放高峰时段,SO42-、Cl-、K+、Mg2+和OC出现了明显的浓度峰值,SO42-质量浓度达到了93.2μg/m3,Cl-质量浓度达到了42.3μg/m3,K+质量浓度达到了115.6μg/m3,OC质量浓度达到了53.8μg/m3。另外,重金属浓度也出现了明显的峰值,Fe质量浓度达到了2.426μg/m3,Cu质量浓度达到了0.727μg/m3,Zn质量浓度达到了1.159μg/m3,Ba质量浓度达到了5.168μg/m3,Pb质量浓度达到了1.245μg/m3。烟花爆竹的燃放造成苏州市区环境空气中有毒有害物质的短期急剧上升,有必要限制烟花爆竹的燃放。     

土壤环境中锑的生物毒性评价方法比较

锑的生物毒性测试可以间接反映锑及其化合物对生物与生态系统的影响。在简要介绍锑在土壤环境中赋存特征的基础上,综述了不同类型生物对土壤及其浸提液中锑的毒性响应,比较了不同的生物毒性测试方法在土壤环境中锑污染识别的可行性及适应性,并提出了考虑土壤性质及老化时间对锑生物毒性评价的影响,以及使用不同营养等级指示生物(微生物、动物和植物)评价等建议。     

应用斑马鱼和凡纳对虾诊断污染场地污水的生物毒性

应用斑马鱼(Brachydanio rerio)和凡纳对虾(Penaeus vannamei)对某废弃有机污染场地中有毒有机废弃物堆积产生的污水(1号塘污水)和场地及周边地表径流积水(2号塘污水)的生物毒性进行了试验.结果表明,1号塘污水对斑马鱼和凡纳对虾96 hLC50分别为46.2%和59.6%, 2号塘污水的毒性试验中两种试验生物的死亡率皆为0.化学检测表明,1号塘污水中的主要污染物为苯酚类和酞酸脂类物质,而2号塘污水中均未检出有机污染物.化学检测结果与毒性试验结果具有较好的相关性.     

西宁市城区冬季PM2.5和PM10中有机碳、元素碳污染特征

2014年11月—2015年1月对西宁市冬季开展PM_(2.5)和PM_(10)的连续监测。利用DRI 2001A型热光碳分析仪(美国)对有机碳和元素碳进行分析,结果表明:西宁市冬季PM_(2.5)和PM_(10)中碳气溶胶所占比例分别为33.13%±6.83%、24.21%±6.27%,说明碳气溶胶主要集中在PM_(2.5)中;OC/EC值均大于2,说明西宁市大气中存在二次污染;SOC占PM_(2.5)和PM_(10)的质量浓度比例分别为46.50%和57.40%,PM_(2.5)中SOC浓度占PM_(10)中SOC浓度的61.88%,说明SOC主要存在于PM_(2.5)中,且SOC形成的二次污染和直接排放的一次污染都是西宁市碳气溶胶的主要来源;与其他城市比较发现,西宁市冬季PM_(2.5)中的碳气溶胶含量普遍高于其他城市,PM_(10)中OC质量浓度相对其他城市较高,EC质量浓度偏低;OC和EC的相关性不显著,说明来源不统一;进一步对OC和EC各组分质量浓度进行分析知,西宁市冬季碳气溶胶主要来源于机动车汽油排放、燃煤和生物质燃烧。     

Acute aquatic toxicity of western juniper (Juniperus occidentalis) foliage and Port Orford cedar (Chamaecyparis lawsoniana) heartwood oils

Recently, interest has developed for using essential oils from Western juniper (Juniperus occidentalis) foliage and Port Orford cedar (Chamaecyparis lawsoniana) heartwood in commercial products such as pest repellents and cosmetics. In order to gauge the relative toxicological risk that these oils pose to freshwater and marine organisms, the acute aquatic toxicity of these oils was evaluated using OPPTS guidelines to the cladoceran Daphnia magna, the rainbow trout Oncorhynchus mykiss and the green alga Selenastrum capricornutum. For western juniper foliage oil, no toxicity was exhibited toward D. magna or O. mykiss, even at 5.0 mg/L (the highest concentration tested and limit of solubility). For toxicity to S. capricornutum using algal cell density, the 72 and 96 h EC₅₀ value was 1.7 mg/L and the no observable effect concentration (NOEC) was 0.63 mg/L. For Port Orford cedar heartwood oil, no toxicity was exhibited toward O. mykiss or S. capricornutum, even at 5.0 mg/L (the highest concentration tested and limit of solubility). The 48-h D. magna EC₅₀ value was 1.9 mg/L; the NOEC values for algal cell density were 1.25 mg/L (72 h) and 0.63 mg/L (96 h). In summary, this study shows that western juniper foliage and Port Orford cedar heartwood oils demonstrate little to no risk to aquatic organisms.     

A new <Emphasis Type="Italic">P. putida</Emphasis> instrumental toxicity bioassay

Here, we present a new toxicity bioassay (CO₂-TOX), able to detect toxic or inhibitory compounds in water samples, based on the quantification of Pseudomonas putida KT2440 CO₂ production. The metabolically produced CO₂ was measured continuously and directly in the liquid assay media, with a potentiometric gas electrode. The optimization studies were performed using as a model toxicant 3,5-DCP (3,5-dichlorophenol); later, heavy metals (Pb²⁺, Cu²⁺, or Zn²⁺) and a metalloid (As⁵⁺) were assayed. The response to toxics was evident after 15 min of incubation and at relatively low concentrations (e.g., 1.1 mg/L of 3,5-DCP), showing that the CO₂-TOX bioassay is fast and sensitive. The EC₅₀ values obtained were 4.93, 0.12, 6.05, 32.17, and 37.81 mg/L for 3,5-DCP, Cu²⁺, Zn²⁺, As⁵⁺, and Pb²⁺, respectively, at neutral pH. Additionally, the effect of the pH of the sample and the use of lyophilized bacteria were also analyzed showing that the bioassay can be implemented in different conditions. Moreover, highly turbid samples and samples with very low oxygen levels were measured successfully with the new instrumental bioassay described here. Finally, simulated samples containing 3,5-DCP or a heavy metal mixture were tested using the proposed bioassay and a standard ISO bioassay, showing that our test is more sensible to the phenol but less sensible to the metal mixtures. Therefore, we propose CO₂-TOX as a rapid, sensitive, low-cost, and robust instrumental bioassay that could perform as an industrial wastewater-process monitor among other applications.     

不同亲疏水性质纳米氧化铝存在下铜对斜生栅藻毒性效应的研究

纳米氧化铝是应用非常广泛的一类人工纳米材料。当它被释放到水环境中后,会与环境中原有的重金属发生相互作用并对其毒性产生影响。文章研究了不同亲疏水性质的纳米氧化铝存在下铜对斜生栅藻的毒性效应,测定了藻细胞的生长抑制、金属积累及超氧化物歧化酶、谷胱甘肽、丙二醛等生化指标的变化。结果表明,纳米氧化铝显著降低了铜离子对藻细胞的生长抑制,藻细胞内铜的积累量及氧化损伤降低。但不同亲疏水性质的纳米氧化铝之间并不存在显著差别。这可能是由于纳米氧化铝对水中的铜离子发生了吸附,间接降低了藻液中的不稳态铜的浓度,从而减轻了铜对藻细胞的毒害。而纳米氧化铝的不同亲疏水性质对吸附水中铜离子的能力没有显著的影响。     

Utility of nematode Acrobeloides nanus for assessing subacute toxicity of heavy metals

Nematodes offer perspectives for ecotoxicological research as their characters and most of toxicity assessment focused on Caenorhabditis elegans. In order to enrich the limited numbers of nematode species used for toxicity test, this study assessed the subacute effects of copper and zinc to the life history characters of nematode Acrobeloides nanus. Compared with control, the 72-h effective concentration (EC)₅₀, EC₂₀, and EC₁₀ for reproduction in A. nanus were 1.35, 0.49, and 0.20 mg/L, respectively, for Cu and 829.46, 330.29, and 163.90 mg/L, respectively, for Zn. The EC₁₀ for growth at 72 h and 96 h of the 2nd generation in A. nanus were 1.13 and 0.97 mg/L, respectively, for Cu, and 353.46 and 284.20 mg/L, respectively, for Zn. During the exposure, the effect of copper–zinc on reproduction was less than additive, and the copper–zinc effect on growth changed from a synergistic to antagonistic.     

3种大环内酯类抗生素对海洋发光菌的毒性作用

以海洋发光菌为受试生物，研究了红霉素、罗红霉素、乙酰螺旋霉素3种抗生素的单一和联合毒性作用。基于常见的3种联合作用评价方法，对混合体系的联合毒性作用进行了评价研究。结果表明，3种抗生素对发光菌单独作用的半最大效应浓度(EC₅₀)分别为:0.725 9×10^-3，1.207 8×10^-3和0.633×10^-3mol/L；二元联合体系对发光菌的毒性强弱为：红霉素+乙酰螺旋霉素>罗红霉素+红霉素>罗红霉素+乙酰螺旋霉素。3种抗生素联合体系作用类型的不同与每种抗生素不同取代基对微生物生理生化过程的影响有关。在选择的联合研究体系中，以毒性单位法获得参数的数值较大，灵敏度较高。研究大环内酯类抗生素对发光菌的毒性作用可为环境风险评价提供基础数据。     

Sensitivity of isolated eggs of pond snails: a new method for toxicity assays and risk assessment

The concentration of heavy metals in the environment is normally low. We here address whether using the development of isolated pond snail Radix auricularia eggs would provide a more sensitive endpoint and whether the gelatinous matrix of the egg mass surrounding the eggs indeed protects the snail embryos. In the present study, artificial removal of the gelatinous matrix of egg masses greatly increased the sensitivity of developing eggs to a heavy metal (cadmium). The sensitivity of isolated eggs to cadmium was determined using several convenient endpoints, including mortality, hatching rate, and heart rate, with an acute toxicity test and a subchronic test. In the acute toxicity test, a 96-h LC₅₀ value of 58.26 μg/L cadmium was determined. In the subchronic toxicity test, sublethal effects in terms of a significant reduction in hatching rate could be found in the 25-μg/L treatment, and a significant decrease of heart rate was observed in both treatments (5 and 25 μg/L). The high sensitivity of isolated eggs indicates that such tests can be efficient for toxicity assays and risk assessment, although one needs to keep in mind that the ecologically relevant measure of toxicity will be how eggs are affected when they are still inside the egg mass.     

Cement for stabilisation of industrial residues containing heavy metals

A method aimed at decreasing the toxicity of heavy metals [namely, Zn(II) and Cr(III)] in real polluted residues by immobilisation has been developed. The residues were processed either with two cement-type stabilisers or lime. The cement-type stabilisers were Portland cement and Depocrete SM/2 at the self-generated pH (ca. 11) which afforded physical as well as chemical potential for the immobilisation of heavy metals. The other stabiliser, lime, reduced organic compounds, thus favouring the decrease of the chemical oxygen demand (COD) and endowing the residue with better mechanical properties for transport. After leaching the stabilised residues using the standard leaching test [Order 13/10/89, Boletín Oficial del Estado (BOE) 270 10/11/89], three ways for establishing the toxicity of the treated residues were used, namely: (1) the ecotoxicity test using Photobacterium phosphoreum (DIN 38 412); (2) determination of the concentration of heavy metals by atomic absorption spectrometry (AAS); (3) determination of the COD or oxygen required for complete chemical oxidation of a water sample. Portland cement (20%) blended with Depocrete SM/2 (3%) acted as an effective stabiliser for residues containing heavy metals as it increased the ecotoxicity index (EC50) by more than five times. Thus the heavy metal concentration in the leaching liquid was lowered to less than 0.1 mg l-1. The addition of 5% of lime afforded a residue easily transportable from the place of treatment to the landfill. The precision of the method was studied in terms of both repeatability and reproducibility. The values found with respect to EC50 and expressed as the relative standard deviation (RSD) were 1.6% and 5.1%, respectively.     

Toxicity assessment for petroleum-contaminated soil using terrestrial invertebrates and plant bioassays

The assessment of soil quality after a chemical or oil spill and/or remediation effort may be measured by evaluating the toxicity of soil organisms. To enhance our understanding of the soil quality resulting from laboratory and oil field spill remediation, we assessed toxicity levels by using earthworms and springtails testing and plant growth experiments. Total petroleum hydrocarbons (TPH)-contaminated soil samples were collected from an oilfield in Sfax, Tunisia. Two types of bioassays were performed. The first assessed the toxicity of spiked crude oil (API gravity 32) in Organization for Economic Co-operation and Development artificial soil. The second evaluated the habitat function through the avoidance responses of earthworms and springtails and the ability of Avena sativa to grow in TPH-contaminated soils diluted with farmland soil. The EC₅₀ of petroleum-contaminated soil for earthworms was 644 mg of TPH/kg of soil at 14 days, with 67 % of the earthworms dying after 14 days when the TPH content reached 1,000 mg/kg. The average germination rate, calculated 8 days after sowing, varied between 64 and 74 % in low contaminated soils and less than 50 % in highly contaminated soils.     

Toxicity of propargylic alcohols on green alga--Pseudokirchneriella subcapitata

The present study evaluates the toxicity of 34 propargylic alcohols, including primary, primary homo-, secondary, and tertiary alcohols, based on their effects on phytoplankton. A closed-system algal toxicity test was applied because the closed-system technique presents more realistic concentration-response relationships for the above compounds than the conventional batch tests. The green alga, Pseudokirchneriella subcapitata, was the test organism and final yield and growth rate were chosen as the test endpoints. Among all the propargylic alcohols tested, 1-pentyn-3-ol is the most toxic compound with its EC50 equal to 0.50 mg L(-1), which can be classified as a "R50" compound (very toxic to aquatic organisms, EC50/LC50 < 1 mg L(-1)), following the current practice for classification of chemicals in the European Union (EU). There are several other compounds including 2-decyn-1-ol, 3-decyn-1-ol, 1-hexyn-3-ol, 3-butyn-2-ol, and 3-hexyne-2,5-diol, which deserve more attention for their possible adverse impact on the aquatic environment, because these alcohols can be classified as "R51" compounds (toxic to aquatic organisms, EC50/LC50 between 1 and 10 mg L(-1)). Compared to the base-line toxicity relationship (narcosis QSAR) derived previously, tertiary propargylic alcohols can be identified as nonpolar narcotic chemicals, while secondary alcohols and primary alcohols with low molecular weight generally exhibit obvious excess toxicity in relation to the base-line toxicity. Finally, quantitative structure-activity relationships were established for deriving a preliminary estimation of the toxicity of other propargylic alcohols.