鄱阳湖丰水期着生藻类群落空间分布特征

着生藻类一般生长位置相对稳定,其群落分布主要受环境因素的影响,同时,着生藻类还是重要的水环境指示生物.本研究对鄱阳湖丰水期5个典型湖区(主航道、西部湿地、南矶湿地、撮箕湖和东南湖汊)着生藻类的群落结构特征进行调查,包括生物量、优势种及生物多样性,分析影响着生藻类群落区域分布的环境因子,以期为鄱阳湖水环境保护和水资源合理利用提供基础资料.结果表明:鄱阳湖着生藻类群落以硅藻、绿藻和蓝藻为主;鄱阳湖着生藻类总生物量有着明显的区域差异:主航道区域的生物量相对最高,平均为419 mg/m^2;其次是东南湖汊,平均为322 mg/m^2;南矶湿地和西部湿地分别为172和52 mg/m^2;而撮箕湖的总生物量相对最低,为9 mg/m^2.主航道的着生藻类优势种群为绿藻和硅藻,西部湿地、南矶湿地、撮箕湖和东南湖汊4个区域的优势种群为硅藻.冗余分析结果显示鄱阳湖丰水期着生藻类群落分布与总磷、电导率、pH值、总氮、硝态氮和悬浮物等理化因子关系较为密切.鄱阳湖主航道与长江连通,水体流速高;西部湿地、南矶湿地、撮箕湖和东南湖汊为季节性连通湖泊,丰水季节与主湖区水体连为一体,枯水季节独立蓄水.5个湖区的区域差异是导致其着生藻类群落结构差异的重要原因之一.着生藻类的多样性指数分析表明鄱阳湖水体处于中度污染状态.     

风场对鄱阳湖丰水期表层蓝藻密度的影响

目前,在风场对蓝藻的影响研究方面,国内针对太湖、滇池、巢湖等浅水湖泊的研究较多,针对鄱阳湖的研究则多集中于蓝藻群落特征及其与营养盐之间的关系。近年来,作为长江流域重要的通江湖泊,处于轻度富营养化状态的鄱阳湖水体蓝藻水华在局部库湾和部分水域出现,风场如何影响鄱阳湖表层蓝藻密度是一个值得探讨的问题。2019-2021年,在鄱阳湖布设13~49个采样点,于平水期、丰水期和枯水期现场采集各个点位表层水样、藻类、风场和流场数据,分析风场对鄱阳湖丰水期表层蓝藻密度的影响。结果表明,2019-2021年鄱阳湖丰水期风速与表层蓝藻密度呈显著正相关性,风场对水体的充分混合及驱动水体形成的风生流是促进蓝藻生长的原因之一。在流速较高(>0.05 m/s)的区域,无论风速高于还是低于临界风速(3~4 m/s),鄱阳湖表层蓝藻密度的空间分布受流场的影响更大;在流速较低(<0.05 m/s)的区域,风速在临界风速以下时,鄱阳湖表层蓝藻密度的空间分布受风场影响更大。2019-2021年鄱阳湖丰水期蓝藻密度超过水华暴发的阈值,但在高风速高流速的共同作用下未能发生大范围的蓝藻水华,仅能在风速适宜(<3~4 m/s)、流速较低(<0.05 m/s)的内湾、尾闾区等区域发生小面积的蓝藻水华。鄱阳湖丰水期水体处于长江顶托的低流速且微风条件下时,发生大面积蓝藻水华的概率可能会明显上升。     

2010-2017年太湖总磷浓度变化趋势分析及成因探讨

近年来,太湖流域各省市政府加大治理力度,流域水体水质取得明显好转,氨氮浓度和总氮浓度呈大幅度下降趋势,然而太湖水体总磷浓度呈上升趋势.为探讨太湖总磷浓度升高的原因,采用太湖流域管理局2010年以来的水质水量实测数据、遥感监测数据等,分别从太湖入湖河流污染负荷量、水生植被和蓝藻与总磷浓度的关系3个方面进行相关性分析.结果表明,入湖河流总磷浓度高于太湖水体总磷浓度,且磷不易出湖,逐年总磷净入湖量持续累积与太湖总磷浓度有明显的正相关性,入湖污染负荷量大是太湖总磷浓度居高不下的根本原因;水生植被可吸收湖泊沉积物中的营养盐,并抑制底泥再悬浮从而降低内源性营养盐的释放,东太湖水生植被的大量减少,一方面减少了沉水植物对磷元素的吸收,另一方面增加了风浪对底泥的扰动再悬浮,造成磷元素释放,是造成湖水总磷浓度升高的重要因素;近年来太湖蓝藻密度呈上升趋势,受其影响,总磷浓度也有上升,蓝藻水华加快湖体磷循环,藻类密度增加也是太湖总磷浓度升高的影响因素之一.     

巢湖西湖心底泥蓝藻对水体蓝藻生物量的贡献

2018年10月-2019年10月对巢湖西湖心水体浮游藻类群落结构以及水体和底泥蓝藻生物量进行了月度调查.结果表明:巢湖西湖心浮游藻类的主要优势种属为微囊藻属、席藻属、十字藻、卵形隐藻和鱼腥藻属.蓝藻优势种属在5-10月为微囊藻属,11-12月为鱼腥藻属,1-4月为席藻属.巢湖水体和底泥蓝藻生物量峰值分别出现在9月和2月,水体蓝藻的衰亡下沉会导致底泥蓝藻生物量的上升.巢湖蓝藻主要分布在水体,底泥蓝藻生物量相对较低,单位面积水柱与底泥蓝藻生物量6月的比值大于100,在11-3月相对较低,最低值小于2.底泥蓝藻主要分布在底泥表层0～2 cm.通过安装原位捕获器,监测了蓝藻在西巢湖湖心水柱和底泥中的垂直迁移过程和通量.结果表明:11月和2月蓝藻有明显从水柱向底泥迁移的过程;底泥蓝藻全年向水体的静态迁移量都很低,而动态迁移在11月和6月出现两个峰值,主要受底泥蓝藻生物量和再悬浮的影响.本研究结果表明削减巢湖西湖心底泥种源的最佳时期为10月至来年2月,但是由于底泥蓝藻生物量远远小于水柱蓝藻生物量,底泥蓝藻向水体复苏迁移的通量也较低,即使削减了底泥种源,也不能有效降低水体蓝藻生物量.     

江西柘林湖富营养化现状与藻类时空分布特征

江西柘林湖是首批入围国家良好湖泊保护专项的示范湖泊.为揭示柘林湖富营养化现状与藻类时空演替特征,于2012年8月至2013年7月对全湖及主要入湖支流进行了周年采样分析,结果表明:柘林湖主要营养盐在地表水Ⅲ类以内,处于中营养状态.全湖藻类演替以蓝藻-硅藻交替为主,夏季以鱼腥藻和微囊藻为优势种,冬季直链藻、小环藻和针杆藻占优.藻类空间分布呈现西部高于东部、上游高于下游的特征,西部部分湖区夏季甚至出现了鱼腥藻水华.柘林湖3个大型饮用水源地中东渡水源地夏季也同样面临蓝藻水华问题,但蓝藻毒素未超标.在重点监测的4条柘林湖主要入湖支流中,3条支流的藻类夏、冬季细胞丰度均在1×107cells/L以下,但烟港水的藻细胞丰度夏、冬季分别接近和超过该界限,应加以警惕并采取适当措施.枯水期水位变化、水体分层、较低的水体透明度和较长的滞留时间是影响柘林湖局部湖区蓝藻水华形成的关键因素.     

丰水期鄱阳湖超微型浮游植物空间分布特征及其影响因子

2014年夏季对鄱阳湖进行采样调查,以探究超微型浮游植物在鄱阳湖中的空间分布特征及其与环境因子的关系.结果表明,丰水期鄱阳湖超微型浮游植物细胞丰度较高,平均值为1.04×108cells/L,超微蓝藻是超微型浮游植物的优势种群,尤其在北部通江湖区,占总超微藻丰度的比例超过80%.超微藻对总浮游植物净初级生产力和生物量(以叶绿素a浓度表示)贡献率的均值分别为44%和46%.鄱阳湖超微藻在空间分布上存在差异,超微藻丰度和叶绿素a浓度在南部湖区最高,其次是北部湖区,在东部和中部湖区相对较低.北部湖区超微藻对总浮游植物净初级生产力和生物量的贡献率全湖最高,分别能达到60%和50%.相关性分析表明,营养盐对超微型浮游植物生长的作用表现不明显,超微藻对总浮游植物净初级生产力的贡献率与水体透明度呈极显著负相关,水体p H值对超微真核藻丰度有显著影响.     

太湖蓝藻水华的预防、预测和预警的理论与实践

综述了蓝藻水华预防、预测预警的重要意义及其理论与技术体系.基于作者所提出的将蓝藻水华形成分为休眠、复苏、生长和上浮聚集形成水华的"四阶段理论",以及太湖蓝藻越冬、春季复苏和水华形成的时空规律,提出了太湖蓝藻水华的预防理念.综述了国内外蓝藻水华形成与预测研究进展,阐述了蓝藻水华形成关键过程的主导生态因子及其阈值:确定了水华蓝藻越冬的空间分布与生命特征,利用室内模拟实验和野外原位观测与捕捉,得到了蓝藻春季复苏的室内和野外温度阈值分别为14℃和9℃,发现了蓝藻复苏量与有效生理积温呈正相关的基本规律;初步揭示了水华蓝藻生长竞争优势形成的生物学与生态学机理以及光利用策略,利用细胞分裂频率法测定了夏季太湖水华蓝藻的原位生长速率为0.2-0.4;确定了在不同水文气象条件下,水华蓝藻在水体中垂直分布和在不同湖区之间输移的基本格局,发现藻类在水体中各层间百分含量的变异系数随着风浪的增大而减小,进一步证明了蓝藻水华形成是在适当水文气象要素驱动下,已经成为优势种群的水华蓝藻在湖体中空间位置的改变而引起的.建立了太湖蓝藻水华预测模型和工作流程,在2007年和2008年在太湖实施了未来3d的蓝藻水华预测预警,预测分析了2008年全年太湖蓝藻水华情势.对预测结果的回顾性评估与分析表明,目前已有的理论研究结果和预测工作流程可以对太湖蓝藻水华发生概率、发生地点和强度进行预测,预测准确率达到60%-80%.此外,还提出了未来蓝藻水华预测的研究方向.     

2012-2018年巢湖水质变化趋势分析和蓝藻防控建议

巢湖自1990s中期至2012年间水质明显改善,但是近年来水质改善效果变缓,2018年蓝藻水华面积显著增加,为有效评估巢湖水体环境的变化,通过对20122018年巢湖17个点位的逐月调查数据分析阐述了近年来巢湖水质和藻情的变化特征,并在流域空间尺度上分析了巢湖流域水污染治理的进展和不足,为后续治理方向的调整和确定提供支撑.20122018年湖区调查数据显示:巢湖湖体总磷和总氮浓度显著升高,铵态氮浓度显著下降,水华蓝藻总量显著升高.在空间上,各污染指标水平呈现由西向东呈逐渐降低的趋势,但是各指标在不同湖区随时间的变化趋势差异明显,西部湖区的总磷、总氮和水华蓝藻指标近年来略有下降或持平,中部和东部湖区则显著升高,所以巢湖湖体总氮和总磷浓度的升高主要源于中、东部湖区的升高,这也是这两个湖区水华蓝藻变动的主要驱动因素.主要入湖河口数据显示:西部4条主要入湖污染河流(南淝河、十五里河、塘西河和派河)水质明显改善,但仍处于较高污染水平,中东部入湖河流(兆河、双桥河和柘皋河)总磷浓度明显升高,是中东部湖区水体营养盐升高的主要原因.中东部河流入湖污染的增加加剧了该区域湖体的富营养化水平,尤其是总磷浓度明显提升,导致中东部湖区夏季水华蓝藻的优势种从鱼腥藻种类演替为微囊藻种类.夏季微囊藻的大量繁殖,使得2018年巢湖中东部湖区部分月份水华面积异常增高.因此,巢湖流域的治理应该在持续强化流域西部合肥市污染治理的同时,增加对流域中部和东部治理的关注和投入.     

鄱阳湖河湖转换期间鱼腥藻(Anabaena)的变化

鄱阳湖作为我国长江目前仅存的两个通江湖泊之一,年内水位变幅巨大.通过在鄱阳湖2013年河湖转换期间(5—11月)对鄱阳湖主航道都昌段进行每月3~4次的高频监测,以考察鄱阳湖水体中鱼腥藻(Anabaena)的动态变化,分析鄱阳湖中鱼腥藻生长并占优势的影响因素.结果表明,蓝藻为鄱阳湖浮游植物的次级优势种,8月蓝藻生物量平均占浮游植物生物量的57%,蓝藻取代硅藻成为暂时的优势种.夏、秋季水华蓝藻以固氮鱼腥藻为主,主要与夏、秋季水温较高以及适宜的营养盐条件等有关.研究期间鄱阳湖水体氮磷比平均在15左右,鱼腥藻能够产生有固氮能力的异形胞,并在水华蓝藻中成为优势种,也反映了鄱阳湖某些湖区存在氮相对缺乏的阶段.     

太湖越冬蓝藻空间分布的初步研究

为确定2007-2008年冬季蓝藻在太湖各个湖区的分布及其变化规律,在冬季逐月对太湖主要湖区14个位点采集底泥和水样,应用荧光分析法测定样品中藻蓝素含量,以确定冬季太湖各个湖区的藻蓝素分布状况,比较冬季太湖各个湖区水体和底泥中蓝藻的分布差异.实验结果说明与夏季情况不同,相对于西南太湖水域,2007-2008年冬季北太湖水体和底泥中的蓝藻含量均较低,而西南湖区部分区域12月仍出现了蓝藻的聚集,底泥表面的藻蓝素含量也较高,说明调查期间,冬季越冬蓝藻主要分布于西太湖和南太湖.     

The nutrient forms, cycling and exchange flux in the sediment and overlying water system in lakes from the middle and lower reaches of Yangtze River

This paper is a review of research works concerning the nutrient transportation, transformation and exchange between water, sediment and biota in the lakes from the middle and lower reaches of the Yangtze River conducted in the context of project entitled "The Processes and Mechanism of Lake Eutrophication in Middle and Lower Reaches of Yangtze River". All the lakes from this area are shallow lakes. According to the typical lake site research, the lakes from the middle and lower reaches of Yangtze River have a higher baseline of nutrition in the history. Normally the trophic status of these lakes can be categorized into medium-trophic or eutrophic. Human activities have been enhanced during the last decades, which speed up the lake eutrophic process. Lake eutrophication control needs to reduce not only the external nutrient inputs from watershed but also the internal loading from the sediments. Investigations revealed that the lake sediments in this area are considerablly high in nutrition in which at most about 30% of phosphorus exists in the form of bio-available in the sediment. The surface sediment will exert great effects on the nutrient exchange between water-sediment interface via adsorption and release of nutrient. The nutrient release from the sediment in these shallow lakes is mainly in two ways, i.e. in the undisturbed condition the nutrient is released through diffusion created by the nutrient gradient from sediment to overlying water; whereas in disturbed condition, the nutrient release is determined by the hydrodynamic forcing intensity and the sediment resuspension. Metallic elements such as the iron, manganese and aluminium and the aerobic-anaerobic ambience will affect the release of nutrients. The disturbed release will increase the total nutrients in the water column significantly in the short period. At the beginning of sediment resuspension, the dissolved nutrient concentration will increase. This increase will be damped if the ferric oxide and aluminium are rich in sediment because of the adsorption and flocculation. This means that the lakes have capability of eliminating the nutrient loadings. Investigations for the lakes from middle and down stream of Yangtze River have suggested that most lakes have the self-cleaning capability. Dredging the control of the internal loading, therefore, is only applicable to the small lakes or undisturbed bays which normally are situated nearby the city or town and rich in organic materials in the sediment. In addition, the strong reduction condition and weak aeration of these lakes and bays make these small lakes and bays release much more bio-available nutrient and without much self-eliminating capability. Moreover, eutrophication induced algal bloom in these lakes will change the pH of water, which further induces the increase in the nutrient release. In turn, the increase in nutrient release promotes the growth of phytoplankton and results in severe algal bloom. For the heavily polluted water, research suggests that the biomass of bacteria and alkaline phosphatase activity will be higher corresponding to the higher concentration of nutrients, which accelerates the nutrient recycling between water, sediment and biota. Quick recycling of nutrient, in turn, promotes the production and biomass growth of microorganism and leads to more severe eutrophication. Further research work should focus on the nutrient transformation mechanism and the effects of microbial loop on the eutrophication.     

The nutrient forms,cycling and exchange flux in the sediment and overlying water system in lakes from the middle and lower reaches of Yangtze River

This paper is a review of research works concerning the nutrient transportation, transformation and exchange between water, sediment and biota in the lakes from the middle and lower reaches of the Yangtze River conducted in the context of project entitled “The Processes and Mechanism of Lake Eutrophication in Middle and Lower Reaches of Yangtze River”. All the lakes from this area are shallow lakes. According to the typical lake site research, the lakes from the middle and lower reaches of Yangtze River have a higher baseline of nutrition in the history. Normally the trophic status of these lakes can be categorized into medium-trophic or eutrophic Human activities have been enhanced during the last decades, which speed up the lake eutrophic process. Lake eutrophication control needs to reduce not only the external nutrient inputs from watershed but also the internal loading from the sediments. Investigations revealed that the lake sediments in this area are considerablly high in nutrition in which at most about 30% of phosphorus exists in the form of bio-available in the sediment. The surface sediment will exert great effects on the nutrient exchange between water-sediment interface via adsorption and release of nutrient. The nutrient release from the sediment in these shallow lakes is mainly in two ways, i.e. in the undisturbed condition the nutrient is released through diffusion created by the nutrient gradient from sediment to overlying water; whereas in disturbed condition, the nutrient release is determined by the hydrodynamic forcing intensity and the sediment resuspension. Metallic elements such as the iron, manganese and aluminium and the aerobic-anaerobic ambience will affect the release of nutrients. The disturbed release will increase the total nutrients in the water column significantly in the short period. At the beginning of sediment resuspension, the dissolved nutrient concentration will increase. This increase will be damped if the ferric oxide and aluminium are rich in sediment because of the adsorption and flocculation. This means that the lakes have capability of eliminating the nutrient loadings. Investigations for the lakes from middle and down stream of Yangtze River have suggested that most lakes have the self-cleaning capability. Dredging the control of the internal loading, therefore, is only applicable to the small lakes or undisturbed bays which normally are situated nearby the city or town and rich in organic materials in the sediment. In addition, the strong reduction condition and weak aeration of these lakes and bays make these small lakes and bays release much more bio-available nutrient and without much self-eliminating capability. Moreover, eutrophication induced algal bloom in these lakes will change the pH of water, which further induces the increase in the nutrient release. In turn, the increase in nutrient release promotes the growth of phytoplankton and results in severe algal bloom. For the heavily polluted water, research suggests that the biomass of bacteria and alkaline phosphatase activity will be higher corresponding to the higher concentration of nutrients, which accelerates the nutrient recycling between water, sediment and biota. Quick recycling of nutrient, in turn, promotes the production and biomass growth of microorganism and leads to more severe eutrophication. Further research work should focus on the nutrient transformation mechanism and the effects of microbial loop on the eutrophication.

     

Characterization of total suspended solid dynamics in a large shallow lake using long‐term daily satellite images

Large, shallow‐water lakes located on floodplains play an important role in creating highly productive ecosystems and are prone to high concentrations of suspended solids due to sediment resuspension. In this study, the aim was to determine the dominant processes governing the total suspended solid (TSS) concentration at the water surface in Tonle Sap Lake, Cambodia, which is a large, shallow‐water lake. Satellite remotely sensed daily reflectance data from 2003 to 2017 were used. Seasonal changes in TSS concentration indicated that bottom sediment resuspension during dry seasons was mostly caused by wind and the TSS concentration was closely correlated with the water depth of the lake. The TSS concentration during flood periods was controlled by both wind and inflow currents from the Tonle Sap River. Additionally, we confirmed that surface/subsurface flow with a low TSS concentration from forests on the floodplain lowered the TSS concentration year round, except during August and September. This fact implied that the floodplain forest area decrease may increase the lake TSS concentration. An analysis of the long‐term changes in TSS indicated that a decrease in the water level during flood periods resulted in the high TSS concentrations observed during the subsequent dry periods. Therefore, climate change and water resource development, which are likely to cause water level reductions in the Mekong River during flood periods, may increase the TSS concentration in Tonle Sap Lake, particularly during the dry season.     

近70年来太湖水体磷浓度变化特征及未来控制策略

分析湖泊中磷浓度的变化特征,揭示其变化的驱动机制,是有效实施湖泊水体磷浓度控制的前提.本文整理分析了太湖70年来(1949 2020年)水体磷浓度监测历史资料,对比了太湖不同湖区、不同时间尺度水体磷浓度的差异性及波动性,发现影响太湖磷浓度变化的原因既有人为的因素,也有自然的因素.无论是污染较轻的1950年,还是污染负荷相对较重的近30年,太湖水体磷浓度一直存在较大时空差异性.暴雨引发入湖河流携带磷污染的扩散、风浪扰动引起的内源释放及蓝藻水华期间藻类生物量的大幅时空变化,都加剧了太湖水体磷浓度的不稳定性.近20年的太湖水污染治理对磷浓度的时空分布影响明显,1998年的太湖水污染治理"零点行动",2007年以来的水利调度等系列水污染治理工程,以及2017年以来的藻情变化等,都对太湖水体磷浓度的时空格局产生了影响.然而,高强度治理投入下太湖水体磷浓度依然偏高,其原因与流域建设用地比例增加、人口增加、耕地种植结构变化等外源负荷因素发生变化有关,也与湖体沉水植被退化、出入流结构发生变化、气候变化引发的蓝藻水华扩张等内源强度及水体表观磷浓度决定因素的生态环境变化有关.近70年来太湖水体磷浓度的变化过程对类似大型浅水湖泊的磷控制策略具有启示意义:大型浅水湖泊存在磷浓度较大波动的自然属性,在水环境保护目标考核中应充分考虑其不确定性,制定切实可行的控制目标;在控制策略上应将外源负荷控制放在首位,在流域污水处理厂深度除磷及流域土地利用调整等方面采取措施,实现入湖磷负荷的大幅削减,同时实施湖体生态修复与食物链调控措施,才能逐步实现湖泊水体磷浓度的控制目标.     

亚热带城市湖泊与河流CO2气体通量特征及其影响因素

湖泊、河流等内陆水体是连接陆地生态系统和海洋的“长程碳环路”的重要节点,也是温室气体二氧化碳(CO₂)排放源,在调节陆地、海洋间的碳迁移转换中发挥着重要作用。相对于自然水体,城市水体因面积小、水深浅且受监测方法限制,水-气界面碳通量经常被忽略。为探讨我国亚热带城市水体温室气体排放特征,本研究以湖南省长沙市典型城市水体,包括洋湖、西湖、松雅湖、月湖4个湖泊和湘江长沙段为研究对象,分别于2022年4和10月采用光化学反馈-腔增强吸收光谱法(OF-CEAS)和扩散模型法对水-气界面CO₂通量进行对比测定。结果表明,长沙城市湖泊与河流春季为CO₂排放源,秋季为吸收汇,河流水-气界面CO₂通量呈显著季节差异。河湖之间CO₂通量在春季表现为显著差异,秋季差异不显著。CO₂通量与水体溶解氧、水体总氮浓度等呈显著正相关。2种方法的CO₂通量对比测定在湖泊上显著相关,但对河流而言相关性不显著。研究揭示的城市湖泊与河流CO₂气体的排放特征有利于深入探究城市水体碳的迁移转化,可对全面了解全球气候变化过程和河湖湿地温室气体减排和调控提供科学支撑。     

用生态修复调控浮游植物种群局部控制富营养化——以贵州红枫湖水质生态修复工程为例

利用物理生态工程在水深10 m左右,水位变幅7 m左右的贵阳红枫湖/水库(正常水位时57.2 km2)右二湾富营养水体进行局部(围隔水体面积1.33 hm2)生态修复.对工程前后和内外水体浮游植物的群落结构、丰度、生物量等进行比较,结果表明,当植物浮岛覆盖率超过1/5～1/3时(可视为阈值),物理生态工程可以调控浮游植物种群结构和丰度,浮游植物优势种群由生态修复前的微囊藻属、角甲藻属及同期外环境的蓝藻门蓝纤维藻属转变为硅藻门的直链藻属.工程内与工程外比较,种属数减少了29.4%,特别是减少了蓝藻中可能释放藻毒素的微囊藻、鱼腥藻等属,蓝藻丰度和生物量分别减少了55.5%和57.9%;而硅藻的种属数则增多120.0%,且其丰度和生物量分别增加了56.4%和60.3%.从藻类总体统计资料看,工程内与工程外比较,藻类丰度减少53.6%,生物量减少39.1%,透明度提高了数十厘米以上,稳定在120～220 cm.当工程区外浮游植物优势种群是蓝藻,暴发蓝藻水华,且可释放藻毒素的种属有多次检出时,工程区内仍然以硅藻为优势种,未曾检测出可释放藻毒素的种属,从而在红枫湖局部水体实现了水质改善和富营养化控制.在目前高污染负荷下恢复浅水湖泊沉水植被时,本项目发展的可全年镶嵌式种植包括香根草、杞柳等高杆植物在内的多种水面植物的浮岛可作为防浪削浪、遏制蓝藻、改善水质、提高透明度的先锋性措施,以保障局部水面植被覆盖面积超过上述阈值,成为保护沉水植物生长、遏制暴发蓝藻水华的可操作途径.     

城市湖泊春季绿藻水华特征及其影响因素——以宁波月湖为例

城市湖泊富营养化问题日趋严峻,以往对水华的研究多集中于大型自然淡水湖库,而对小型城市浅水湖泊的水华动态相对较少.以宁波月湖为研究对象,探讨水华暴发期间浮游植物变化特征及与影响因子之间的关系,以期判别影响城市湖泊水华的主控因子.月湖水华期间营养盐水平处于中富营养至极端富营养之间,此次共检出浮游植物8门61属,藻种组成以绿藻门（51.79%）和硅藻门（21.43%）为主,各点位浮游植物生长主要受水温、光照驱动,经历了隐藻门→硅藻门→绿藻门→蓝藻门的演替.水华种为雷氏衣藻（Chlamydomonas reinhardtii）,总藻密度最高达到1.55×10⁸ cells/L,水华暴发后各点位衣藻属比例升高（最高达到81.10%）,群落结构呈现单一化特征.通过Pearson相关性分析和RDA分析发现衣藻属生长与水温、pH、总磷浓度均呈显著正相关,春季气温回升、天气持续晴好,城市浅水湖泊高营养盐负荷、水体流动性差等特点为带鞭毛的衣藻属提供了适宜的生存条件,在环境条件均适宜的情况下拥有最大生长潜力的衣藻属在营养盐、光照等竞争中生长速率明显优于其他藻种,从而发生绿藻水华.