Direct and indirect effects of pesticides on a benthic grazer during its life cycle

Background

Macroinvertebrates in aquatic ecosystems are repeatedly exposed to pesticides during their life cycle. Effects of consecutive exposure during different life stages and possible synergistic effects are not addressed in the standardized hazard assessment. The present study investigated two environmentally relevant exposure scenarios in batch (microcosm) and artificial indoor stream (mesocosm) experiments using the larvae of the mayfly Rhithrogena semicolorata (grazer) and natural aufwuchs. Grazers were analysed regarding growth, physiological condition, and drift behaviour, while the aufwuchs was analysed in terms of biomass using the particulate organic carbon as well as the chlorophyll a content. The aim was to reveal direct and indirect effects of an herbicide exposure during autumn on juvenile grazers and an insecticide exposure during spring on semi-juvenile grazers.

Results

Direct and indirect effects were found in both exposure scenarios at environmentally relevant concentrations. In the herbicide exposure scenario with terbutryn, clear direct effects on the aufwuchs community with a LOEC of 0.38 µg L^?1 were found. Effect levels of grazers due to indirect effects were equal, with the overnight drift being the most sensitive grazer endpoint. In the insecticide exposure scenario, clear lethal and sub lethal effects of lambda-cyhalothrin were evident. Derived LC₅₀ values for the artificial indoor stream and batch experiment were 2.42 µg g^?1 OC (69 days) and 1.2 µg g^?1 OC (28 days), respectively. Sub lethal effects in terms of increased drift as well-reduced growth and triglyceride levels were found at concentrations of 1.4 and 0.09 µg g^?1 OC (LOECs). These results were confirmed by the batch experiment, which revealed effect values in the similar range. Finally, a clear indirect effect of the insecticide on the aufwuchs was evident in the batch experiment with an LOEC at 0.9 µg g^?1 OC.

Conclusion

Toxicity Exposure Ratios calculated with the derived effect values indicate a risk for the investigated grazer by both pesticides. Moreover, observed indirect effects during the herbicide exposure seem to be able to affect the grazers during a second exposure with an insecticide, due to reduced physiological conditions. We suggest further research with time-shifted exposure scenarios to gain a better understanding of the complex interactions of pesticides with the life cycle and the food webs of macroinvertebrates.

     

Ultrastructural responses and oxidative stress induced by cypermethrin in the liver of Labeo rohita

The present study was conducted to establish the relationship between selected oxidative stress parameters and ultrastructural responses in liver tissue of Labeo rohita fingerlings exposed to cypermethrin. Fish were exposed to lethal (4.0 μg L^?1) and sublethal (0.4 μg L^?1) concentrations of cypermethrin for a period of 24, 48, 72 and 96 h for acute studies and 1, 5, 10 and 15 days for subacute studies, respectively. Results showed increased catalase (CAT) and protease activity, hydrogen peroxide (H₂O₂), malondialdehyde (MDA), protein carbonyls and free amino acid (FAA) levels at both concentrations. This suggests participation of free-radical-induced oxidative cell injury in mediating the hepatotoxicity of cypermethrin. In corroboration of this, ultrastructural lesions witnessed a reduction in the number of cell organelles, swollen, vacuolated and condensed mitochondria, dilated rough endoplasmic reticulum, and reduced numbers of smooth enodplasmic reticulum, peroxisomes and lysosomes at the lethal (4.0 μg L^?1) concentration. At the sublethal (0.4 μg L^?1) concentration, cytoplasmic vacuolation, condensed, vacuolated and swollen mitochondria, dilated rough endoplasmic reticulum and an absence of hepatocyte microvilli were prominent. Ultrastructural changes were exhibited as subcellular responses due to the imbalance in cellular oxidative status by means of oxidative damage.     

氯氰菊酯对海洋卡盾藻的毒性效应

为了解拟除虫菊酯农药对海洋生态系统以及海洋初级生产力的影响,研究了氯氰菊酯对重要赤潮藻类海洋卡盾藻(Chattonella marina)的生长及生化指标的影响.结果表明,低浓度(≤10μg·L-1)的氯氰菊酯对海洋卡盾藻生长具有明显的促进作用,而高于50μg·L-1则产生较明显的抑制效应,但暴露后期会出现一定的超补偿效应.藻细胞内叶绿素a(Chl.a)、可溶性糖和可溶性蛋白含量及超氧化物歧化酶(SOD)活性在暴露初期变化较剧烈,24h或48h后趋于平稳.随着培养(暴露)时间的延长,低浓度暴露组以上指标均呈现先促进后恢复趋势,而高浓度暴露组则呈现先抑制后恢复趋势,丙二醛(MDA)含量随培养(暴露)时间的延长呈先促进后恢复趋势且随氯氰菊酯浓度升高而明显升高.在实验设计浓度下,氯氰菊酯对SOD活性和MDA含量的最低作用剂量为10μg·L-1,而对其他生长和生化指标的最低抑制浓度为50μg·L-1,SOD和MDA可作为监测环境中氯氰菊酯污染的敏感指标.     

Determination of selected semi-volatile organic compounds in water using automated online solid-phase extraction with large-volume injection/gas chromatography/mass spectrometry

A rapid, sensitive, and cost-effective analytical method was developed for the analysis of selected semi-volatile organic compounds in water. The method used an automated online solid-phase extraction technique coupled with programmed-temperature vaporization large-volume injection gas chromatography/mass spectrometry. The water samples were extracted by using a fully automated mobile rack system based on x-y-z robotic techniques using syringes and disposable 96-well extraction plates. The method was validated for the analysis of 30 semivolatile analytes in drinking water, groundwater, and surface water. For a sample volume of 10 mL, the linear calibrations ranged from 0.01 or 0.05 to 2.5 ??g·L^?1, and the method detection limits were less than 0.1 ??g·L^?1. For the reagent water samples fortified at 1.0 ??g·L^?1 and 2.0 ??g·L^?1, the obtained mean absolute recoveries were 70%?C130% with relative standard deviations of less than 20% for most analytes. For the drinking water, groundwater, and surface water samples fortified at 1.0 ??g·L^?1, the obtained mean absolute recoveries were 50%?C130% with relative standard deviations of less than 20% for most analytes. The new method demonstrated three advantages: 1) no manipulation except the fortification of surrogate standards prior to extraction; 2) significant cost reduction associated with sample collection, shipping, storage, and preparation; and 3) reduced exposure to hazardous solvents and other chemicals. As a result, this new automated method can be used as an effective approach for screening and/or compliance monitoring of selected semi-volatile organic compounds in water.     

邻苯二甲酸丁基苄酯致神经细胞氧化损伤

为探究邻苯二甲酸丁基苄酯(butyl benzyl phthalate,BBP)对小鼠神经的毒性作用,进行了小鼠体外毒理学研究。首先用不同浓度的邻苯二甲酸丁基苄酯染毒神经模型细胞—N2a神经瘤细胞,通过噻唑蓝比色法(MTT),Hoechst 33258染色实验评价邻苯二甲酸丁基苄酯的细胞毒效应;通过对染毒细胞氧自由基(ROS)、丙二醛(MDA)、还原型谷胱甘肽(GSH)含量的检测来探究BBP对小鼠神经瘤细胞的氧化损伤效应。随着BBP浓度的不断增高,细胞的MTT值逐渐变小,当BBP的浓度达到10 g·L-1时,MTT实验结果与对照组出现显著性差异;Hoechst 33258染色结果显示:高浓度的BBP导致细胞核呈现出不规则状态,出现了凋亡小体;随着BBP染毒浓度的升高N2a细胞中的ROS水平和MDA含量逐渐上升,分别在0.16 g·L-1和10 g·L-1开始与对照组相比出现了显著性的差异(p0.05);而GSH系数呈现下降趋势,在0.32 g·L-1时开始出现显著性差异(p0.05)。实验结果表明高浓度的邻苯二甲酸丁基苄酯可以导致神经瘤细胞的凋亡,并产生氧化损伤效应。     

Alterations in serum electrolyte levels after dimethoate exposure and recovery in the freshwater air-breathing catfish,Heteropneustes fossilis (Bloch)

Dimethoate, a moderately toxic insecticide, has a wide range of agricultural and domestic applications. Like other organophosphates, dimethoate has anticholinesterase activity. Fish are non-target organisms, inadvertently exposed to pesticides and their metabolic products. The present study includes short-term (96 h) and long-term (36 d) effects of dimethoate exposure on some serum electrolytes Ca²⁺, Mg²⁺, and Pi in the freshwater air-breathing catfish Heteropneustes fossilis. The concentration of dimethoate for short-term exposure was 2.24 mg L^?1 (75% of 96 h LC₅₀) and for long-term exposure 0.75 mg L^?1 (25% of 96 h LC₅₀). The study includes the recovery pattern in serum electrolytes after placing the fish in pesticide-free water. Fish show hypocalcemia, hypermagnesemia, and hyperphosphatemia after short-term and long-term exposure to dimethoate. When placed in pesticide-free water, these electrolytes exhibit recovery towards normalization, indicating significant (p < 0.05) recovery.     

纳米二氧化硅对秀丽线虫的毒性作用研究

为探讨二氧化硅纳米颗粒(SiNP)的毒性作用.以微米SiO2和空白做对照,将尺寸为20和60 nm的SiNP分别以0.2,1.0和5.0 g·L-13个浓度对模式生物秀丽隐杆线虫进行染毒.通过第一代和第二代线虫体长、身体弯曲频率、头部摆动频率以及第一代线虫后代数目、世代时间等发育、运动和生殖的相关评价指标,对SiNP毒...     

Heavy metals in the polychaete Glycera longipinnis from the southwest of India

Metal concentrations in sediment and in whole tissue of the benthic polychaete Glycera longipinnis collected along the southwest coast of India were analysed. Relative seasonal accumulation of metals (Cu, Pb, Cr, Ni, Zn, Cd, Hg) was studied by categorising the habitat as less polluted or highly polluted based on metal contamination routed through industrial and urban sources. The metal content in tissues varied seasonally in the ranges, Cu: 2.21–27.08 μg·g^?1, Pb: 0.06–4.92 μg·g^?1, Cr: 1.73–29.20 μg·g^?1, Ni: 1.60–4.61 μg·g^?1, Zn: 14.72–82.30 μg·g^?1, Cd: 0.04–1.38 μg·g^?1and Hg: below decetable limits to 0.86 μg·g^?1. Concentration of heavy metals was found to be high in the whole body of G. longipinnis pooled from the polluted transects. The results of this study suggest that G. longipinnis may act as a useful biological indicator for heavy metal pollution along the southwest coast of India.     

Low uptakes of Cd,Cu, and Zn in Dugesia japonica,a freshwater planarian with higher tolerance to metals

Although a freshwater planarian is proposed as a potential model for studying toxicities of environmental pollutants, they are less sensitive to metal exposures, compared to other freshwater invertebrates. We hypothesised that the metal uptake is low in treated planarians, which may lead to their higher tolerance to metals. The acute toxicities of Cu and Zn to Dugesia japonica were determined. The 24- and 48-h median lethal concentrations were 4.50 and 3.46?mg?L^?1, respectively, for Cu, and 41.97 and 37.79?mg?L^?1, respectively, for Zn. Accordingly, combining with the data on Cd in our previous study, higher tolerance of planarians to metals was revealed. Also, tissue levels of Cd, Cu, and Zn in treated D. japonica were determined, and their dissolved uptake rate constants (k₁) were calculated. Results showed that bioaccumulations of these metals in D. japonica were, indeed, lower than that in other freshwater invertebrates having higher susceptibilities to these metals.     

重金属胁迫对日本对虾(Penaeus japonicas )胚胎发育的影响

以受精1 h以内的日本对虾受精卵为实验对象,采用静水试验方法,研究了Zn、Hg、Cu、Pb、As、Cd和Cr 7种重金属对日本对虾胚胎发育的影响。结果表明,在实验浓度范围内,7种重金属中Hg、Cu对日本对虾胚胎发育毒性最大,其次是Zn、As、Cd,Pb和Cr无明显影响。Hg、Cu、Cd、As、Zn对日本对虾胚胎LC₅₀值分别为：0.0177 mg·L^-1、0.1070 mg·L^-1、1.6057 mg·L^-1、3.3682 mg·L^-1、8.2644 mg·L^-1,致死效应最低可观测效用浓度（LOEC）分别为0.0037 mg·L^-1、0.0166 mg·L^-1、0.1302 mg·L^-1、1.1572 mg·L^-1、2.1522 mg·L^-1;抑制发育LOEC分别为0.0062 mg·L^-1、0.0176 mg·L^-1、0.4002 mg·L^-1、1.9497 mg·L^-1、0.0617 mg·L^-1。随着Hg、Cu浓度的升高,胚胎孵化率不断下降,无节幼体死亡率不断上升,在Hg 0.0256 mg·L^-1浓度组中,胚胎48 h死亡率达到100%。以上结果说明,Hg、Cu等重金属的存在会延缓日本对虾胚胎的发育速度,随着重金属浓度的增加,滞育现象愈加明显,在Cu 0.32 mg·L^-1浓度组中,未见无节幼体孵出。     

多杀菌素、阿维菌素乳油和高效氯氰菊酯3种农药对环境生物的安全性评价

防治同一类病虫害的农药种类很多,在保证药效的前提下,选择对施药环境中其他生物安全的农药是非常必要的。通过毒性试验,比较了25 g·L^-1多杀菌素悬浮剂、1.8%阿维菌素乳油和4.5%高效氯氰菊酯水乳剂对环境生物蜜蜂、家蚕、赤眼蜂、大型溞和斑马鱼的风险。结果表明,25 g·L^-1多杀菌素悬浮剂对蜜蜂为高毒,对家蚕为剧毒,对赤眼蜂为高风险,对斑马鱼和大型溞为低毒;1.8%阿维菌素乳油对蜜蜂为高毒,对家蚕为剧毒,对赤眼蜂为高风险,对斑马鱼和大型溞为剧毒;4.5%高效氯氰菊酯水乳剂对蜜蜂为高毒,对家蚕为剧毒,对赤眼蜂为高风险,对斑马鱼和大型溞为剧毒。3种农药对家蚕、蜜蜂、赤眼蜂均为高风险,但与阿维菌素和高效氯氰菊酯相比多杀菌素对水生生物更安全。     

21种杀菌剂对家蚕的急性毒性与风险评价

旨在为桑园及周围农田合理选择和使用农药提供科学依据,采用食下毒叶法测定了农业生产上常用的21种杀菌剂对家蚕的急性毒性,并进行了风险评价.急性毒性测定结果表明:20％苯醚甲环唑微乳剂、10％氟硅唑水乳剂、12.5％腈菌唑水乳剂、12.5％烯唑醇可湿性粉剂和70％嗯霉灵可湿性粉剂对家蚕的96 h-LC50值为46.5(41...     

全氟辛烷磺酸盐(PFOS)替代品对家蚕大造的生态毒性

以中国本地家蚕品种大造作为受试生物,实现实验室规模化饲料饲养和初步实验动物化;建立家蚕大造环境危害评价急性毒性测试方法;对4种PFOS替代品包括:50%的全氟丁基有机铵盐阳离子表面活性剂、用调聚法合成的织物三防整理剂(含固率23.7%)、用电解氟化法合成的C4和C6织物三防整理剂,进行了急性接触毒性、急性饲喂毒性及慢性饲喂毒性的安全风险评价。实验使用的4种PFOS替代品试验急性饲喂浓度均达到或超过2000mg·L-1,家蚕未出现明显死亡;在接触实验浓度达到10g·L-1时,家蚕未出现明显死亡,以上结果证明,4种PFOS替代品对大造蚕种的急性饲喂毒性和接触毒性均为低毒。较低浓度的表面活性剂会严重影响到大造蚕种的结茧率,当表面活性剂浓度为0.4g·kg-1时,蚕种不能结茧,其余3种化学品在浓度大于0.004g·kg-1,对大造蚕种的结茧率产生一定的影响作用,但抑制作用相对较为平缓。替代品均会降低家蚕茧层率,表面活性剂在浓度为0.04g·kg-1时,茧层率剧烈下降,其他3种替代品抑制作用相对平缓。织物三防整理剂、C4和C6织物三防整理剂几乎不会影响蚕卵孵化,但表面活性剂会造成家蚕孵化率降低,在0.04g·kg-1后孵化率为0。     

Decolorization of azo dyes by a salt-tolerant Staphylococcus cohnii strain isolated from textile wastewater

The salt-tolerant Staphylococcus cohnii strain, isolated from textile wastewater, has been found effective on decolorizing several kinds of azo dyes with different structures. The optimal conditions for azo dye acid red B (ARB) decolorization by S. cohnii were determined to be pH = 7.0 and 30°C. The decolorization efficiency increased with the increase of the salinity concentration, and around 90% of ARB (100 mg·L^?1) could be decolorized in 24 h when the salinity concentration was up to 50 g·L^?1. Moreover, the strain could still decolorize 19% of ARB in 24 h even when the NaCl concentration was increased to 150 g·L^?1. Meanwhile, the dependence of the specific decolorization rate by S. cohnii on the ARB concentration could be described with Michaelis-Menten kinetics (K _m = 585.7mg·L^?1, V _max = 109.8 mg·g cell^?1·h^?1). The addition of quinone redox mediator, named 2-hydroxy-1,4-naphthoquinone and anthraquinone-2,6-disulfonate, significantly accelerated the decolorization performance of S. cohnii. Furtherly, the activities of azoreductase (0.55 ??mol·mg protein^?1·min^?1) and Nicotineamide adenine dinucleotide-dichlorophenol indophenol (NADH-DCIP) reductase (8.9 ??mol·mg protein^?1·min^?1) have been observed in the crude cell extracts of S. cohnii. The decolorization products of ARB were analyzed by HPLC-MS, and the results indicated the reductive pathway was responsible for azo dye decolorization by S. cohnii.     

Metabolic responses of Azolla pinnata to cadmium stress: photosynthesis,antioxidative system and phytoremediation

This present study deals with the growth, photosynthesis, oxidative stress and phytoremediation character of Azolla pinnata L. exposed to different levels (0.05, 0.1, 0.5, 1.0, 1.5 and 2.0 mg·L^?1) of cadmium (Cd). Significant accumulation of Cd in Azolla fronds was noticed after 24 and 96 h of exposure and the accumulation rate was dose and time dependent. Growth of A. pinnata increased significantly after both exposure times with and without metal. At lower Cd doses (0.05 and 0.1 mg·L^?1), growth and photosynthesis of A. pinnata showed a marginal increase over the respective control, however, at higher Cd doses (0.5, 1.0, 1.5 and 2.0 mg·L^?1), a decreasing trend was noticed. At lower doses, Azolla fronds could counterbalance the negative effect of enhanced levels of superoxide radicals (SOR) and hydrogen peroxide (H₂O₂) through the greater activity of antioxidative enzymes. The decaresing trends in catalase and peroxidase activity at higher Cd doses suggest that Azolla fronds were not able to mitigate the negative effects of H₂O₂, hence an increase in malondialdehyde content was noticed. The study concludes that up to 0.1 ,mg·L^?1 Cd, A. pinnata can flourish and be used as biofertiliser and for phytoremedial purposes in Cd-contaminated fields; beyond this concentration poor growth may restrict its application.     

Formation of resistance in the Chironomus plumosus to four pesticides over 45 generations

A study was conducted on the Chironomus plumosus larvae to determine initiation of resistance to four pesticides – chlorfenvinphos, chlorpyrifos, chlorpyrifos-methyl, and malathion. First generational LC₅₀ values were well within the threshold value for chironomids based upon the literature. Subsequent LC₅₀ values were observed to increase, indicating a lessening of the toxicity of the pesticides to the chironomid. In the case of chlorfenvinphos, the 96 h LC₅₀ for generations 1–23 was 6 µg L^?1, in generations 3–7 was 8.57 µg L^?1 and 11.14 µg L^?1 for generations 8–9. Generations 10–12 had an LC₅₀ value of 22.58 µg L^?1 and generation 13 had an LC₅₀ value of 35.08 µg L^?1. Generation 14 had an LC₅₀ value of 47.58 µg L^?1. Generations 15–19 and 20–24 had 96 h LC₅₀ values of 60.68 µg L^?1, 72.58 µg L^?1, 85.08 µg L^?1, 97.58 µg L^?1 and 110.08 µg L^?1, respectively. Generations 25, 26 to 30, 31 to 38 and 39 to 45 had 96 h LC₅₀ values of 160.42 µg L^?1, 210.7 µg L^?1, 262.24 µg L^?1 and 274.36 µg L^?1, respectively. The variation between LC₅₀ values was found to be statistically significant. This was observed for most pesticides tested. Larval size and life cycle duration was observed to change from generation to generation with the body size decreasing markedly from 1 to 0.3 cm with life cycle increasing from 7 to 39 days.     

Assessment of toxicity of two nitroaromatic compounds in the freshwater fish Cyprinus carpio

This study was conducted to evaluate the toxicological response of p-nitrotoluene and p-nitroaniline to the key fish species, Cyprinus carpio. A freshwater fish bioassay based on the 96 h LC ₅₀ was used to estimate the single and joint toxicity of the two chemicals. The toxicity of p-nitrotoluene was greater than that of p-nitroaniline based on 96 h LC ₅₀ values of 40.74 mg·L^?1 and 48.99 mg·L^?1, respectively. Both compounds had moderate toxicity toward Cyprinus carpio, and this toxicity increased with the exposure duration and concentration. Binary mixtures of the compounds were more toxic than the individual compounds at 96 h, and they acted upon partial addition. When the exposure time was longer, the toxicity increased for mixtures of compounds with the same concentration or toxicity. The results of this study suggest that exposure to a combination of these chemicals would result in a higher environmental risk in aquatic systems than exposure to either compound alone. Further research is needed to investigate the combined effects and sublethal toxicity of p-nitrotoluene and p-nitroaniline, since they are both still used in China.     

Endosulfan reduces fertilization success and causes abnormal embryo development to zebrafish

Abstract

Reproductive and teratogenic effects of endosulfan were investigated by exposure of mature breeding zebrafish (Danio rerio) to environmentally relevant concentrations of 0.01–1.2?μg L^?1 and monitoring their spawning, fertilization success, and gonad histology. Fertilization success was negatively correlated to duration of exposure at endosulfan concentration of 1.2?μg L^?1. No apparent effect was observed on fish gonads after histological examination. Teratogenic effects were assayed by exposing newly spawned embryos to endosulfan at 1.0–200?μg L^?1 and determining coagulation, tail development, eye formation, and spontaneous movements 24?h after fertilization; pigmentation, heart rate, edema, and mortality after 48?h and hatch time, mortality, and spinal deformations after 144?h. At 50–100?μg L^?1, endosulfan caused impaired tail development and differentiation, and at 10–200?μg L^?1 spinal deformation and increased mortality, depending upon the timing of exposure.     

Effective degradation of tetracycline by mesoporous Bi<Subscript>2</Subscript>WO<Subscript>6</Subscript> under visible light irradiation

Bi₂WO₆ was synthesized with a hydrothermal method at different pHs and used for the degradation of tetracycline (TC) in water. The mesoporous Bi₂WO₆ prepared at pH 1 (BWO-1) displayed the highest adsorption and degradation capacity to TC due to its large surface area and more efficient capacity to separate photogenerated electrons and holes. 97% of TC at 20 mg·L^?1 was removed by BWO-1 at 0.5 g·L^?1 after 120 min irradiation under simulated solar light. Only 31% of the total organic carbon (TOC) was removed after 360 min irradiation although the TC removal reached 100%, suggesting that TC was mainly transformed to intermediate products rather than completely mineralized. The intermediates were identified by high-performance liquid chromatography-time of flight-mass spectrometry (HPLC-TOF-MS) and possible photodegradation pathways were proposed.     

Acute toxicity of 30 pharmaceutically active compounds to freshwater planarians,Dugesia japonica

Pharmaceutically active compounds are produced worldwide and consumed in large quantities, so these chemicals are frequently detected in limnic environments posing potential ecological risks. Thirty pharmaceutically active compounds were selected for examination of their acute toxicity for freshwater planarians (Dugesia japonica). Among the 30 compounds tested, diclofenac, mefenamic acid, naproxen, propranolol HCl, and diphenhydramine HCl had a 48-h nominal LC₅₀ below10 mg L^?1, and for 18 chemicals, it exceeded 100 mg L^?1. The 96-h nominal LC₅₀ was below 10 mg L^?1 for diclofenac, mefenamic acid, naproxen, propranolol HCl, diltiazem HCl, diphenhydramine HCl, hydroxyzine HCl, and triprolidine HCl, and for 15 chemicals, it exceeded 100 mg L^?1. Among different therapeutic groups, analgesics were most toxic to planarians, and antibiotics were least toxic. Antihistamines and beta blockers varied in their acute toxicity to planarians. At the current environmental levels, none of the tested pharmaceutically active compounds may have acutely harmful impacts on aquatic invertebrates. To answer the question whether chronic, long-term exposure to pharmaceutically active compounds may entail ecological risks for aquatic ecosystems, further investigations with different end points in multiple species tests are needed.