应用环境微生物治理淡水湖泊微囊藻毒素污染的研究进展

近年来,随着水体富营养化程度的加剧,蓝藻水华现象时有发生,蓝藻及其释放的藻毒素对生态环境和人类健康构成严重威胁。在各种藻毒素中,以微囊藻毒素(Microcystins,MCs)毒性最强,对人类危害也最大,微囊藻毒素的化学性质相对稳定且难以通过常规水处理方法消除,因此如何有效去除环境中的MCs是国内外普遍关注的难题。研究发现自然界中的微生物能够有效降解和消除MCs污染,由此产生的环保技术极具应用价值。本文主要概述了微囊藻毒素的产生机理、化学结构以及毒性危害,总结了微囊藻毒素的自然分解过程以及微生物群落对微囊藻毒素的响应机制,重点分析了微生物群落在微囊藻毒素污染控制技术中的潜在应用,并对应用微生物技术治理微囊藻毒素污染的技术瓶颈提出了建议,以期加速微囊藻毒素微生物降解技术的完善和应用。     

样品制备过程对测定水中溶解态微囊藻毒素的影响

系统比较了5种不同材质滤膜对于制备溶解态微囊藻毒素的影响,发现了影响藻毒素测定样品前处理的关键操作步骤。结果表明,醋酸纤维滤膜（CA filter）最多可吸附样品中79%的藻毒素,导致测得的MCs浓度严重偏低。玻璃纤维（GF/C）滤膜和聚醚砜（PES）材质滤器对制备溶解态微囊藻毒素过程影响很小。另外,发现离心法无法完全去除野外水华样品中藻细胞,反而可能导致藻细胞破裂,释放藻毒素,影响水中溶解态微囊藻毒素的测定。研究结果将对发展水体中溶解态藻毒素测定标准方法提供依据。       

样品制备过程对测定水中溶解态微囊藻毒素的影响简

系统比较了5种不同材质滤膜对于制备溶解态微囊藻毒素的影响,发现了影响藻毒素测定样品前处理的关键操作步骤。结果表明,醋酸纤维滤膜(CA filter)最多可吸附样品中79%的藻毒素,导致测得的MCs浓度严重偏低。玻璃纤维(GF/C)滤膜和聚醚砜(PES)材质滤器对制备溶解态微囊藻毒素过程影响很小。另外,发现离心法无法完全去除野外水华样品中藻细胞,反而可能导致藻细胞破裂,释放藻毒素,影响水中溶解态微囊藻毒素的测定。研究结果将对发展水体中溶解态藻毒素测定标准方法提供依据。     

微囊藻毒素对水环境的影响研究进展

微囊藻毒素是富营养化淡水水体中最常见的藻类毒素,是湖泊蓝藻产生的一类肽类毒素,它的产生受到藻类的遗传和环境因素的共同影响。由于其毒性大,分布广,结构稳定,从而成为水环境中的潜在危害物质。有关微囊藻毒素性质、毒理毒性、在环境中的迁移、转化以及控制预防已成为关注热点。在总结国内外研究的基础上,综述了微囊藻毒素的性质、产生机理以及其与水环境、水生生物(水生植物、鱼类、无脊椎动物)间的相互作用,讨论了微囊藻毒素对水生生物的影响以及水生生物对微囊藻毒素的降解作用,为水体中微囊藻毒素的防治提供科学的依据。     

微囊藻毒素-LR的离体鳃灌流研究

随着水体富营养化进程的加剧, 有毒蓝藻的频繁暴发已成为一个世界性的难题。自1878年Francis1报道了世界上首例由于接触有毒蓝藻而引发的牲畜中毒事件以来, 已经有许多关于鱼类、爬行动物、鸟类和哺乳动物接触蓝藻而中毒甚至死亡的案例25。在为数众多的藻毒素中, 微囊藻毒素(Microcystins, MCs)因具有很强的肝毒性6, 7和促癌作用8, 而被认为是最具危害的种类之一。       

鲢鱼可溶性谷胱甘肽S-转移酶(sGST)基因cDNA全序列与5′调控区的克隆与分析

淡水鱼类可溶性谷胱甘肽S-转移酶(sGST)在微囊藻毒素去毒代谢过程中具有独特的关键作用,因而也称为微囊藻毒素去毒酶.从淡水食毒藻鱼类鲢鱼(Hypophthalmichthysmolitrix)肝脏通过简并引物克隆微囊藻毒素去毒酶基因cDNA核心序列,应用5′RACE和3′RACE技术分别扩增该序列的5′末端和3′末端序列,最后通过序列拼接获得鲢鱼肝脏微囊藻毒素去毒酶基因cDNA全序列.序列分析结果表明,鲢鱼肝脏微囊藻毒素去毒酶基因cDNA全长920bp,其中5′-UTR长74bp,3′-UTR长174bp,编码区长672bp,编码223个氨基酸.应用基因组步行法,在鲢鱼克隆得到淡水鱼类微囊藻毒素去毒酶基因5′侧翼区878bp序列.与哺乳动物及海水鱼sGST基因不同,鲢鱼微囊藻毒素去毒酶基因的5′侧翼区,发现存在多个脂多糖反应元件(LPSRE),表明来源于毒藻的脂多糖可能对鲢鱼微囊藻毒素去毒酶基因表达有潜在调控作用.     

水生态系统中微囊藻毒素的分布及其生态毒理效应研究进展

有毒蓝藻产生的蓝藻毒素对淡水生态系统构成了严重的全球性环境威胁,其中微囊藻毒素(MCs)是所有蓝藻毒素中分布最广、危害最大的一类肝毒素。MCs已对水生态系统的结构、功能和稳定性造成了不良影响,并对人类健康构成威胁。本文综述了当前MCs在水体、沉积物和水生动物体内的分布,以及MCs的生物毒性机制,在此基础上,总结了MCs对水生动物、水生植物及陆生植物的生态毒理效应,及其引发的人类健康风险,并关注了MCs的生物防治方法。最后,针对当前MCs相关研究领域中存在的不足提出展望,旨在为淡水水体中MCs的风险评估与治理管控提供参考。     

水环境中微囊藻毒素的生物降解

微囊藻毒素在水环境中的生物降解是决定其环境归趋和影响其毒性的重要因素。本文综述了水细菌、鱼类、水生植物、水生无脊椎动物、浮游动物等水生生物对微囊藻毒素生物降解方面的研究进展。目前报道的微囊藻毒素降解菌有鞘氨醇单胞菌、铜绿假单胞菌和青枯菌。鞘氨醇单胞菌和铜绿假单胞菌分别以微囊藻毒素酶和碱性蛋白酶降解毒素,青枯菌降解机理未明;而鱼类、水生植物、水生无脊椎动物、浮游动物等水生生物主要通过谷胱甘肽S-转移酶催化形成低毒性的微囊藻毒素-谷胱甘肽结合物进行转化。本文还对水环境微囊藻毒素的生物修复方式进行了初步的探讨。     

鲢鱼可溶性谷胱甘肽S-转移酶(sGST)基因cDNA全序列与5′调控区的克隆与分析

淡水鱼类可溶性谷胱甘肽S-转移酶(sGST)在微囊藻毒素去毒代谢过程中具有独特 的关键作用,因而也称为微囊藻毒素去毒酶. 从淡水食毒藻鱼类鲢鱼(Hypophthalmichthys molitrix)肝脏通过简并引物克隆微囊藻毒素去毒酶基因cDNA核心序列,应用5′RACE和3′RACE技术分别扩增该序列的5′末端和3′末端序列,最后通过序列拼接获得鲢鱼肝脏微囊藻毒素去毒酶基因cDNA全序列. 序列分析结果表明,鲢鱼肝脏微囊藻毒素去毒酶基因cDNA全长920 bp,其中5′-UTR长74 bp,3′-UTR长174 bp,编码区长672 bp,编码223个氨基酸. 应用基因组步行法,在鲢鱼克隆得到淡水鱼类微囊藻毒素去毒酶基因5′侧翼区878 bp序列. 与哺乳动物及海水鱼sGST基因不同,鲢鱼微囊藻毒素去毒酶基因的5′侧翼区,发现存在多个脂多糖反应元件(LPSRE),表明来源于毒藻的脂多糖可能对鲢鱼微囊藻毒素去毒酶基因表达有潜在调控作用.     

一株囊藻毒素降解辅助菌的发现

太湖、滇池等水体爆发的蓝藻水华,对水体生态环境及人们生活带来了严重的影响,引起了各级政府的高度重视。目前每年从太湖中打捞的水华数以亿吨计,但由于其毒性较大,无法利用,同时大规模发生蓝藻的水体底泥藻毒素含量也在不断提高。微囊藻毒素(Microcystins,MCs)是由淡水藻如微囊藻属、鱼腥藻属、     

水华蓝藻对鱼类的营养毒理学效应

水体富营养化导致蓝藻水华的发生已成为全球关注的水环境问题,很多鱼类处于水生态系统食物链的最高级,蓝藻水华的主要次级代谢产物-微囊藻毒素可通过鱼类的摄食活动或生物富集作用在鱼体组织中累积,并通过食物链危及人类健康。近年来,微囊藻毒素对鱼类的毒性效应引起众多科学家的关注。在天然水体中不少鱼类可以主动摄食蓝藻,所以,水华蓝藻对鱼类来说既具有营养物作用、也具有潜在的毒性作用。鉴于目前机械收获的水华蓝藻生物量资源化利用问题以及水产饲料业亟需大力开发鱼粉替代蛋白源的需要,从营养学和毒理学这两个角度来研究水华蓝藻对鱼类的营养作用和毒性效应具有较高的理论和现实意义。主要概述了蓝藻粉、蓝藻细胞对鱼类的营养学和毒理学效应,以期拓展水华蓝藻对鱼类毒性效应的研究视野,同时也为水华蓝藻的资源化利用提供新的思路。     

Effects of microcystins on human polymorphonuclear leukocytes

Microcystins (MCs) are cyclic heptapeptides produced by cyanobacteria present in water contaminated reservoirs. Reported toxic effects for microcystins are liver injury and tumour promotion. In this study, we evaluated the effects of two MCs, MC-LR and [Asp(3)]-MC-LR, on human neutrophil (PMN). We observed that even at concentrations lower than that recommended by World Health Organization for chronic exposure (0.1 nM), MCs affect human PMN. Both MCs have chemotactic activity, induce the production of reactive oxygen species, and increase phagocytosis of Candida albicans. MC-LR also increased C. albicans killing. The effect of MCs on PMN provides support for a damage process mediated by PMN and oxidative stress, and may explain liver injury and tumour promotion associated to long-term MCs exposures.     

微囊藻毒素对陆生植物的污染途径及累积研究进展

微囊藻毒素(Microcystins,MCs)是全世界范围内普遍存在、且随着水体污染的加剧而在自然环境中大量积聚的蓝藻毒素之一,对多种生物有着严重的毒性作用.MCs在生物体内富集并通过食物链传递,对人类健康造成威胁.近些年,MCs对陆生植物的毒害作用及累积研究尤为引人关注,取得了一批重要的研究成果.MC-LR(L为亮氨酸)和MC-RR(R为精氨酸)是淡水水体中普遍存在且危害较大的两种MCs异构体.针对这两种毒素,重点介绍其对陆生植物的污染途径、毒性作用及其在作物体内的累积量,对今后的研究进行了展望.     

Distribution and tissue retention of cesium-134 and cobalt-6o in the nile catfish clarias lazera (cuv. & val.)

The Nile catfish, Clarias lazera was found to concentrate radioactive cesium-134 and cobalt-6o from the aquatic environment. For cesium-134 the rate of uptake increased by increase of exposure time, while for cobalt-6o maximum uptake occurred after one day of exposure. The corresponding concentration factors at maximum uptake levels were 0.37 and 0.36 for cesium and cobalt respectively.The internal distribution of these radionuclides in the different tissues and organs of the fish due to uptake from the aquatic environment followed the decreasing order:For ¹³⁴Cs: muscle, bone, gills, stomach, kidneys, intestine and liver.For ⁶⁰Co: bone, muscle, gills, intestine, kidneys, stomach and liver.The internal distribution due to ingestion of these radionuclides followed nearly the same order as was found in case of uptake from the aquatic environment.     

Accumulation of the precious metals platinum, palladium and rhodium from automobile catalytic converters in Paratenuisentis ambiguus as compared with its fish host, Anguilla anguilla

The platinum group metals (PGM) Pt, Pd and Rh are emitted into the environment mainly by catalytic exhaust gas converters of cars. As PGM accumulate in sediments of aquatic ecosystems, the study was focused on the uptake of the noble metals by European eels, Anguilla anguilla infected with the acanthocephalan Paratenuisentis ambiguus. Eels were exposed to ground catalytic converter material for six weeks. After exposure Pt and Pd were detected in the liver and kidney of the eels and in the parasites. Palladium was also found in fish muscle and intestine. No Rh uptake by the eel tissues and the parasites occurred. Paratenuisentis ambiguus contained the highest levels of both metals with 40 times higher Pt concentrations and four times higher Pd concentrations than the liver of its host. Due to its accumulation capacity for PGM, P. ambiguus can be applied as a sensitive accumulation indicator in field studies to assess the degree of environmental PGM contamination in aquatic ecosystems.     

Chronic effects of copper exposure versus endocrine toxicity: two sides of the same toxicological process?

Chronic sub-lethal exposure to copper (Cu) causes a series of cellular and physiological changes in fish that enable the animal to survive. Copper is also an endocrine disrupting metal in the aquatic environment, and has a number of normal neuro-endocrine roles in vertebrates. This paper explores whether the chronic effects of Cu exposure can be explained by the effects of Cu on neuro-endocrine functions in fish. Chronic Cu exposure involves complex physiological adjustments in many body systems, including increased oxygen consumption, reduced mean swimming speed, up-regulation of ionic regulation, decreasing lymphocyte levels and increasing neutrophils, altered immunity, modulation of Cu-dependent and independent enzyme activities, and proliferation of epithelial cells in gills or intestine. These responses can occur with exposure via the food or the water and can be rationalised into three major categories: (1) up-regulation of enzymes/metabolism (2) altered haematopoietic responses and (3) altered cellularity (cell type, turnover or size) in tissues. Some of these responses can be explained by stimulation of general stress responses, including the adrenergic response and stimulated cortisol release via the hypothalamic-pituitary-interrenal axis. This can occur despite evidence of vacuolation and foci of necrosis in the brain, and increased macrophage activity, in the kidney of fish exposed to dietary Cu. In addition to generic stress responses, Cu regulates specific neuro-endocrine functions, including the loss of circadian rhythm during dietary Cu exposure that involves the failure to respond to circulating melatonin and a loss of circulating serotonin. We conclude that the chronic physiological effects of Cu and apparent endocrine disrupting effects of Cu are two sides of the same toxicological process.     

Mercury toxicity in livers of northern pike (Esox lucius) from Isle Royale, USA

Many laboratory studies have documented that mercury can be toxic to fish, but it is largely unknown if mercury is toxic to fish in their natural environments. The objective of our study was to investigate the toxic effects of mercury on northern pike (Esox lucius) at Isle Royale, Michigan. In 124 northern pike from eight inland lakes, concentrations of total mercury in skin-on fillets ranged from 0.069 to 0.622 microg/g wet mass (wet wt). Concentrations of total mercury in livers increased exponentially compared with concentrations in fillets, to a maximum of 3.1 microg/g wet wt. Methylmercury constituted a majority of the mercury in livers with total mercury concentrations <0.5 microg/g wet wt, but declined to 28-51% of the mercury in livers with total mercury concentrations >0.5 microg/g wet wt. Liver color (absorbance at 400 nm) varied among northern pike and was positively related to liver total mercury concentration. The pigment causing variation in liver color was identified as lipofuscin, which results from lipid peroxidation of membranous organelles. An analysis of covariance revealed lipofuscin accumulation was primarily associated with mercury exposure, and this association obscured any normal accumulation from aging. We also documented decreased lipid reserves in livers and poor condition factors of northern pike with high liver total mercury concentrations. Our results suggest (i) northern pike at Isle Royale are experiencing toxicity at concentrations of total mercury common for northern pike and other piscivorous fish elsewhere in North America and (ii) liver color may be useful for indicating mercury exposure and effects in northern pike at Isle Royale and possibly other aquatic ecosystems and other fish species.     

Hypoxia and the antipredator behaviours of fishes

Hypoxia is a phenomenon occurring in marine coastal areas with increasing frequency. While hypoxia has been documented to affect fish activity and metabolism, recent evidence shows that hypoxia can also have a detrimental effect on various antipredator behaviours. Here, we review such evidence with a focus on the effect of hypoxia on fish escape responses, its modulation by aquatic surface respiration (ASR) and schooling behaviour. The main effect of hypoxia on escape behaviour was found in responsiveness and directionality. Locomotor performance in escapes was expected to be relatively independent of hypoxia, since escape responses are fuelled anaerobically. However, hypoxia decreased locomotor performance in some species (Mugilidae) although only in the absence of ASR in severe hypoxia. ASR allows fish to show higher escape performance than fish staying in the water column where hypoxia occurs. This situation provides a trade-off whereby fish may perform ASR in order to avoid the detrimental effects of hypoxia, although they would be subjected to higher exposure to aerial predation. As a result of this trade-off, fishes appear to minimize surfacing behaviour in the presence of aerial predators and to surface near shelters, where possible. For many fish species, schooling can be an effective antipredator behaviour. Severe hypoxia may lead to the disruption of the school unit. At moderate levels, hypoxia can increase school volume and can change the shuffling behaviour of individuals. By altering school structure and dynamics, hypoxia may affect the well functioning of schooling in terms of synchronization and execution of antipredator manoeuvres. School structure and volume appear to be the results of numerous trade-offs, where school shape may be dictated by the presence of predators, the need for energy saving via hydrodynamic advantages and oxygen level. The effects of hypoxia on aquatic organisms can be taxon specific. While hypoxia may not necessarily increase the vulnerability of fish subject to predation by other fish (since feeding in fish also decreases in hypoxia), predators from other taxa such as birds, jellyfish or aquatic mammals may take advantage of the detrimental effects of hypoxia on fish escape ability. Therefore, the effect of hypoxia on fish antipredator behaviours may have major consequences for the composition of aquatic communities.     

水环境中工程纳米颗粒物的生态毒理学机理及理想模式生物的筛选

随着纳米技术产业的高速发展,大量工程纳米颗粒物(Engineering nano-particles,ENPs)被排放到自然水环境中,因此对其进行生态毒性及环境风险的研究尤为迫切。综述了ENPs在水环境中的毒理学机理及理想模式生物筛选的研究进展。目前的研究表明ENPs的毒性作用机制主要包括两方面:一是影响细胞信号通路,二是氧化应激造成基因表达的变化。此外,光催化活性、细胞表面附着、溶解特性、表面特征、赋存形态、溶剂效应及与其他环境污染物的协同作用也是可能的毒性作用机理。模式生物的筛选与确定在纳米生态毒理学研究中极为重要。鱼类作为水环境中普遍存在的脊椎动物,群落庞大,其具有行为端点敏感性高、且在生物毒性实验中存在明显的量效关系等特征,被认为是研究ENPs生态毒理学最适合的水生模式生物。研究表明针对在ENPs影响下的未成年鱼类的行为特征研究比传统的胚胎发育及致死率研究更为有效。无脊椎动物和浮游植物同样在各种水环境中普遍存在,对环境污染物极为敏感,且对有害物质具有显著的富集放大效应,因此作为模式生物也具有一定的优势。