乙酰甲胺磷对斜生栅藻的毒性及细菌降解研究

采用血球计数法测定斜生栅藻细胞数目,研究了乙酰甲胺磷对斜生栅藻的毒性作用,并通过藻类培养液中接种经过筛选得到的乙酰甲胺磷高效降解菌测定其对乙酰甲胺磷毒性的去除影响。研究结果表明,乙酰甲胺磷对斜生栅藻的抑制中浓度(EC50)大于159 mg/L,急性毒性为低毒。但进一步研究发现,在7 d后,EC50为174.68 mg/L,明显低于24 h的1 128.57 mg/L,存在亚慢性毒性。通过藻类培养液接种高效降解菌Y-6,乙酰甲胺磷对藻类的生长抑制程度减轻。     

斜生栅藻的无菌化培养及其在原油降解中的应用研究

选用组合抗生素结合溶菌酶/SDS预处理方法对斜生栅藻进行无菌化培养,对不同抗生素组合的除菌效果进行了比较。青霉素+庆大霉素对斜生栅藻和附生菌都有强烈的抑制性能,而青霉素+利福平和青霉素+四环素组合除菌不彻底。青霉素+卡那霉素组合能彻底除去附生菌并且对藻的抑制作用最小,可得到无菌斜生栅藻。将斜生栅藻与石油组分降解菌构建菌藻共生体系,未除菌藻的附生菌与石油组分菌之间不能很好地相互适应,使得原油降解效果反而降低。纯栅藻则对石油降解菌表现出非常良好的促进作用,利用除菌后的斜生栅藻与石油组分降解菌构建了一个高效降解原油的菌藻共生体系,充分肯定了微藻无菌化培养的积极意义。     

栅藻LX1和雨生红球藻的胞外产物产生特性及其对藻细胞生长的影响

基于微藻在资源化大规模培养过程中,其胞外产物对藻细胞生长影响的不确定性,对比研究了两株高含油脂藻种,栅藻LX1（Scenedesmus sp.LX1）和雨生红球藻（Haematococcus pluvislis）的生长特征、胞外产物的产生特性,以及胞外产物对藻细胞生长的影响。研究结果表明,在相同培养条件下,栅藻LX1与雨生红球藻的内禀生长速率基本相当,分别为0.16和0.17 d-1。两株藻在不同生长期的胞外产物（以DOC值表征）产生速率不同,其中栅藻LX1胞外产物的对数期产生速率（1.4 mg·L-1·d-1）﹥稳定期后期产生速率（0.56 mg·L-1·d-1）﹥稳定期产生速率（0.48 mg·L-1·d-1）;雨生红球藻胞外产物的稳定期后期产生速率（2.3 mg·L-1·d-1）﹥稳定期产生速率（0.88 mg·L-1·d-1）﹥对数期产生速率（0.66 mg·L-1·d-1）。栅藻LX1胞外产物对其整个生长过程都有明显抑制;雨生红球藻胞外产物则在稳定期后期才对其生长产生明显抑制作用。     

蓝藻水华优势藻高效防控铜制剂的筛选

在对比络合铜、有机铜和无机铜3类5种典型铜制剂对蓝藻水华优势藻--铜绿微囊藻(Microcystis aeruginosa)和2种非靶标藻种--普通小球藻(Chlorella vulgaris)和斜生栅藻(Scenedesmus obliquus)的96 h生长抑制效果的基础上,进一步开展了3类铜制剂抑制铜绿微囊藻生长的15 d延长效应研究.试验结果表明,质量分数为25%的络氨铜水剂、30%琥胶肥酸铜可湿性粉剂和20%乙酸铜可湿性粉剂对蓝藻水华优势种有较好的生长抑制效果,其对初始密度为2×105～4×105mL-1铜绿微囊藻的96 h半抑制浓度(以下均以有效成分的质量计)分别为0.03、0.06和0.05 mg·L-1,且初始藻密度对抑藻效果并无明显影响.试验质量浓度为0.25 mg·L-1的25%络氨铜水剂、0.30 mg·L-1的30%琥胶肥酸铜可湿性粉剂或0.20 mg·L-1的20%乙酸铜可湿性粉剂均能抑制铜绿微囊藻增长,且在0～15 d内都不会出现藻细胞再次复苏和增长.此外,由于铜制剂对铜绿微囊藻的96 h半抑制浓度远低于其对普通小球藻和斜生栅藻的96 h半抑制浓度,因此可在有效控制靶标藻种的同时不对非靶标藻种的生长造成严重威胁.络氨铜、琥胶肥酸铜、乙酸铜有望被开发成为高效、绿色的蓝藻水华控制剂.     

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。     

抗生素利福平对萼花臂尾轮虫生命表参数的影响

以萼花臂尾轮虫(Brachionus calyciflorus)为受试动物,研究了在不同斜生栅藻(Scenedesmus obliquus)密度(1.0×10⁶,2.0×10⁶,4.0×10⁶个/mL)下,不同浓度(2.0,4.0,6.0,8.0,10.0μg/mL)的利福平溶液对萼花臂尾轮虫实验种群增长参数的影响.结果表明,与空白对照组及助溶剂对照组相比,1.0×10⁶个/mL藻密度下,各浓度的利福平显著提高了轮虫的后代混交率;2.0×10⁶个/mL藻密度下,2.0,4.0,10.0μg/mL的利福平显著提高了轮虫的內禀增长率,各浓度的利福平均提高了轮虫的后代混交率;4.0×10⁶个/mL藻密度下,各浓度的利福平均显著提高了轮虫的內禀增长率和后代混交率.藻密度为1.0×10⁶个/mL时,利福平浓度与轮虫的生命期望、世代时间、平均寿命和后代混交率间具有显著的剂量-效应关系;藻密度为2.0×10⁶个/mL时,利福平浓度与轮虫的后代混交率间具有显著的剂量-效应关系;藻密度为4.0×10⁶个/mL时,利福平浓度与轮虫的世代时间、净生殖率、內禀增长率和后代混交率间有显著的剂量-效应关系.     

有机锡化合物的毒性效应及其影响因素

以斜生栅藻(Scenedesmus obliquus)和大型蚤(Daphniamagna)为受试生物,采用静水试验法评价了5种有机锡化合物的毒性效应,并初步探讨了化合物结构和性质对其毒性效应的影响.结果表明,有机锡化合物对两种水生生物均显示出较强的毒性,且具有相同的变化规律,即毒性效应均表现为三丁基锡＞四丁基锡＞二丁基锡＞一丁基锡,但由于种间差异及外部因素的影响,同一有机锡化合物对两种水生生物的毒性作用差异明显.同时,有机锡化合物自身的理化性质和分子结构也影响着它们对水生生物的毒性效应,只有当Sn原子与C原子相连时才表现出毒性,即有机锡对水生生物具有毒性.在同一取代系列的有机锡化合物中,取代烷基的数目越多,毒性越大,但是当取代烷基数增加到一定程度后,由于分子体积过大,毒性反而降低.     

Isolation,identification, and biological characteristics of a wild Chaga mushroom北大核心CSCD

In this study, a pure culture strain (numbered as F1501) was obtained using tissue separation and purification methods from the sclerotia of Chaga mushroom from Russia. Further researches included studies on classification, optimum growth conditions of mycelia, extracellular polysaccharides from fermentation broth and their antioxidant activity, and artificial acclimation. According to the identification of the internal transcribed spacer (ITS) region, it was confirmed that F1501 was a species of the genus Inonotus and family Hymenochaetaceae, which had 99% similarity with Inonotus obliquus. F1501 was further classified as I. obliquus based on the morphological characteristics of its mycelia and sclerotia. The optimal carbon source, nitrogen source, C/N ratio, growth factor, temperature, and pH value for the growth of the F1501 strain mycelia were maltose, beef extracts, 10/1, B2, 28 °C, and 8.0, respectively. Liquid fermentation of F1501 was performed using PD media and a 10% inoculation amount at 28 °C and 150 r/min for 7 d. The content of polysaccharides in the fermentation broth was 476.32 mg/L, with a total antioxidant activity of 0.19 mmol/L (Trolox) and hydroxyl free radical-scavenging activity of 72.7%. Artificial acclimation study revealed that the fruiting body-like structure was obtained using cottonseed hulls as the main substrate. In the present study, a new strain of I. obliquus and its biological characteristics were explored, which could provide a theoretical basis for the artificial acclimation and development of wild mushrooms. © 2018 Science Press. All rights reserved.     

滏阳河河流水体中重金属污染特征及其对青海弧菌和斜生栅藻的毒性效应

为调查滏阳河水系的重金属污染状况,研究河流重金属污染对水生生物的毒性,根据河流结构、水文条件、排污口分布并考虑空间分布的均匀性,选取66个采样位点,采集河水及对应的表层沉积物样品,分析了样品中的重金属含量。用斜生栅藻和青海弧菌Q67作为模式生物,根据滏阳河水重金属污染较严重的邯郸近郊2号采样点采集水样的重金属含量配制系列重金属浓度的模拟河水进行重金属污染河水的生态毒性测试。结果表明,在全部66个采样点中,29个采样点河水重金属含量超过国家地表水III类水体重金属含量标准,主要污染元素是Hg、Pb、Cr、Zn。几乎所有采样点河水Mn和Fe含量都大大高于国家集中式生活饮用水地表水源地补充项目规定的标准限值。根据2号采样点河水样品中的重金属含量配成的模拟河水对青海弧菌Q67的EC_(50)值为6.65%,为毒性极强的污染物。模拟河水样品对斜生栅藻的抑制作用较小,在实验的最高浓度下(1 000倍河水重金属含量)暴露4 d尚未引起半数藻细胞死亡。随河水重金属浓度上升,斜生栅藻超氧化物歧化酶(SOD)活性总体上呈现先升高后降低的趋势,丙二醛(MDA)含量变化则与此相反,反映河水重金属污染可引起藻细胞的氧化损伤。叶绿素a和b含量则随暴露浓度的提高逐渐降低。在重金属浓度达到2号采样点河水的10%时,斜生栅藻叶绿素a含量已有显著降低,MDA含量显著升高,海河流域重金属污染对生态系统的影响应予以重视。河水发光菌Q67的生长抑制率、斜生栅藻的叶绿素a和MDA含量可以作为评估河流重金属污染生态危害的指标。     

Attached cultivation of Scenedesmus sp. LX1 on selected solids and the effect of surface properties on attachment

Attachment of Scenedesmus sp. LX1 was tested on certain materials. A criterion for selection of materials was used to choose seven materials. The amount of S. sp. LX1 attached on polyurethane foam was 51.74 mg/L. Materials’ surface influenced the attachment of microalgae. Hydrophilic and hydrophobic properties also affected the attachment of S. sp. LX1. Attached cultivation systems in the literature do not present a methodology to screen materials for microalgal growth. Hence, a method is needed to find suitable materials for attached cultivation that may enhance attachment of microalgae. In this paper, we have tested seven materials culturing Scenedesmus sp. LX1 (S. sp. LX1) to evaluate the attachment of microalgae on the material surface, its growth in suspension phase and the properties of the materials. Two materials showed attachment of S. sp. LX1, polyurethane foam and loofah sponge, and allowed microalgae to grow both in the surface of the material and suspended phase. Polyurethane foam proved to be a good material for attachment of S. sp. LX1 and the amount of attached microalgae obtained was 51.73 mg/L when adding 100 pieces/L. SEM images showed that the surface and the pore size of the materials affected the attachment of the microalgae, increasing its attachment in scaffold-like materials. Furthermore, the hydrophilic and hydrophobic properties of the materials also affected the attachment of microalgae. This research can be used as a methodology to search for the assessment of a material suitable for attachment of microalgae.