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1.
武汉东湖大茨藻群落的研究 总被引:3,自引:0,他引:3
本文总结了1962—1964年和1972—1982年对东湖大茨藻群落的研究工作。研究的主要内容有:群落面积和生物量的逐年变化,物候相和种子发芽率,植物的光合作用和呼吸作用,以及植物群落对太阳能量的利用效率。最后提出了对大茨藻群落的改造问题。 相似文献
2.
大茨藻的碎屑形成过程 总被引:1,自引:0,他引:1
在实验室条件下,大茨藻(Najas major)死亡前后的形态变化可分为如下几个阶段:临界期或死亡前期;细胞核变色期;细胞质收缩期和胶体形成期。作者把细胞核变色期定为大茨藻的碎屑开始期。同时,还考察了天然条件下大茨藻死亡后形态的降解情况。 相似文献
3.
在实验室条件下,大茨藻(Najas major)死亡前后的形态变化可分为如下几个阶段:临界期或死亡前期;细胞核变色期;细胞质收缩期和胶体形成期。作者把细胞核变色期定为大茨藻的碎屑开始期。同时,还考察了天然条件下大茨藻死亡后形态的降解情况。
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4.
本文根据1992~1993年调查结果并结合前人研究资料,讨论了东湖水生植物群落30多年来的动态变化及其与富营养化和渔业养殖等因素的关系,提出了东湖水生植物群落的演替系列是从微齿眼子菜阶段→微齿眼子菜+大茨藻+金鱼藻+狐尾藻阶段→微齿眼子菜消失阶段→大茨藻阶段→大茨藻+狐尾藻+苦草阶段。同时,还从物种生理生态、补偿和再生能力、生活史及生殖对策、种间关系等方面探讨了水生植物群落演替的物种替代机制及其演替模式,为湖泊水生植被恢复、人工调控和优化提供理论依据。 相似文献
5.
武汉东湖水生植被春恢复途径探讨 总被引:2,自引:0,他引:2
1992-1993年对武汉东湖三个主要湖区水生植被的调查表明,该湖区共有水一植 物32种优势种为大茨藻、狐尾藻、苦草和菱。金鱼藻呈不断扩大的趋势。 相似文献
6.
白洋淀水生植被初步调查 总被引:14,自引:0,他引:14
通过野外实地调查对白洋淀水生植被的物种组成、群落类型、分布格局及物种生物量进行了初步研究.结果表明:白洋淀湿地共有水生植物39种,隶属于21科32属,其中挺水植物16种,沉水植物14种,浮叶根生植物6种,漂浮植物3种.与20世纪90年代初相比,水生植物共减少了9种,群落类型也由原来的16种变为现在的13种,大面积轮叶黑藻、大茨藻等优势群落消失,物种分布格局也发生了巨大变化.群落生物量较1980年大幅下降.人工养殖、污染物随意排放和水位的变化可能是造成白洋淀湿地退化、水生植被格局发生巨大变化的主要原因. 相似文献
7.
通过对草茨藻Najas graminea Del.,多倍体系列的分析,笔者认为首次发现的分布于云南的二倍体居群为偏性特有。该居群的迁移与今天草茨藻在亚洲的分布图式密切相关。该图式不表现多倍体随纬度或海拔增加而增多,也不明显与生态爱好相关。二倍体和六倍体居群核型比较以及其它证据指示草茨藻的多倍体起源可能是同源多倍化。在茨藻属中,草茨藻具最强的核型不对称性,最高的倍性和极减化的花部器官等特征,均可能指示它是该属中进化程度最高的类群。 相似文献
8.
在水生植物茨藻目中,茨藻科Najadaceae和角果藻科Zannichelliaceae植物由于其结构、尤其是花部结构的极度简化和趋同适应,系统关系仍不清楚。本文应用光学显微镜、扫描电镜和透射电镜对上述2科4属的10种代表植物的花粉形态进行了观察,系统描述了各属、种的花粉形态。结果表明角果藻科植物花粉均无萌发孔,外壁纹饰通常为拟网状至浅网状。花粉形态的研究结果支持将Vleisia作为角果藻属Zannichellia的近缘属处理的观点。茨藻科植物花粉外壁光滑、稍皱波状或为疣状,具颗粒状纹饰,萌发孔的有无在种间存在变异。花粉形态的研究结果表明角果藻科与眼子菜科Potamogetonaceae近缘,茨藻科可能与水蕹科Aponogetonaceae或水鳖科Hydrocharitaceae中具单沟花粉的类群有一定联系,而与角果藻科和眼子菜科则相去甚远。 相似文献
9.
两种茨藻属植物的染色体组型 总被引:2,自引:0,他引:2
游浚;孙祥钟;王徽勤 《武汉植物学研究》1990,8(4):387-389
笔者曾在1985年报道过分布于我国大陆的6种茨藻属(Najas L.)植物的染色体数目及核型分析结果。而高雄茨藻(N. browniana Rendle)和弯果茨藻(N. ancistrocarpa A. Br. ex Magnus)为笔者不久前(1987年)才发现它们在我国大陆上有分布。据载,仅弯果茨藻前人作过染色体计数工作。因此,作为对整个茨藻属细胞分 相似文献
10.
黄河三角洲湿地水生植物组成及生态位 总被引:9,自引:0,他引:9
通过大范围的野外调查和室内测定,运用Levins及Pianka公式,对近代黄河三角洲湿地水生植物的构成及主要物种的生态位进行了研究.结果表明:调查样方内共有水生植物34 种,隶属于16科26属;各调查区域间物种组成和群落类型具有一定的差异性.区域形成的年份越久,其物种数和群落类型就越丰富;挺水植物中以芦苇的生态位宽度最大,为0.905,藨草的最低,为0.127; 沉水植物中轮藻、穗花狐尾藻、川蔓藻及小茨藻的生态位宽度较大,分别为0.783、0.673、0.669和0.640,金鱼藻的最低,仅为0.100.龙须眼子菜、大茨藻和苦草间,马来眼子菜和菹草间生态位重叠值较大,说明这几种植物具有相似的环境适应能力.物种的生态位宽度与该物种的分布范围及耐盐区间的大小存在显著的相关性,由此可以断定土壤和水体盐度是导致黄河三角洲湿地水生植物生态位分化的关键因子. 相似文献
11.
本文是根据1962—1964年部分调查研究资料整理而成的。文中列出了83种水生维管束植物(以下简称水生植物)的名录,比较了全湖21个采集断面、3个植物带和17个植物群丛以及长江中下游6个浅水湖泊水生植物的生物量,分析了东湖两个断面(Ⅻ和ⅪⅡ)的生物量的周年变化和湖中不同水深区的生物量变化情况。全湖面积为28.5平方公里。8月是生物量的高峰期,平均每平方米的生物量为1,068.1克(湿重)或94.8克(风干重)或82克(烘干重)或322千卡(能量)。其中,以黄丝草所占的比例为最大,其次为大茨藻、聚草、黑藻和金鱼藻。全湖水生植物的年生产量为30,440吨(湿重)或2,337吨(烘干重)或9×109千卡(能量),连同浮游植物(16×109千卡)一起,则东湖全年的原初生产量为25×109千卡,其中水生植物约占总原初生产量的36%。本文最后讨论了水生植物在湖泊渔业上的合理利用问题,提出了草食性鱼种放养量的计算公式和合理利用水生植物资源的建议。
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12.
鸭儿湖污染治理研究 总被引:1,自引:0,他引:1
鸭儿湖污染是通过氧化塘系统控制的。氧化塘系统,由四个串联氧化塘组成,总面积为2800亩,塘深3米,当废水量为7万吨/天时停留时间为80天。并利用净化后的废水培育鱼种(鱼种塘),通过菌—藻—浮游动物—鱼的相互作用,以鱼种形式回收部分营养元素。以解决在氧化塘沿岸的东西排灌渠12.8公里两岸人民的灌溉水和饮用水的污染问题。从1976年底氧化塘初步建成,四年运转结果表明:COD、有机磷、对硝基酚、对硫磷、马拉硫磷、乐果和六六六处理效果分别为77.3、82.5、99.3、98.7、98.4、92.9和86.2%。每天实际废水负荷为8万吨。1977年以来水生态系逐渐得到恢复,至1979年鱼的畸型率下降到0.1%。鱼体内(背肌)六六六残留从15—30毫克/公斤下降到0.155毫克/公斤,农作物中六六六的残留1979年比氧化塘建立之前降低了2.7—9.4倍。
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13.
作者采用常规生化分析法测定草食性鱼类天然食料(七种水生高等植物)的生化成分和能值。在实验室特定条件下测定了草鱼和团头鲂的系列体重组对七种水生高等植物的最大摄食量和消化率。1.七种水生高等植物的生化成分的含量和能值的分析结果表明,菹草、黄丝草、聚草、苦草、小茨草、轮叶黑藻和紫背浮萍的水分百分含量范围为80.85—92.72%、蛋白质为1.69—4.96%、脂肪为0.35—1.09%、灰分为0.98—2.6%、纤维素为0.66—2.17%、无氮浸出物为2.3—9.95%。七种水生植物的蛋白质均含有常见十七种氨基酸,包括鱼体必需氨基酸九种和非必需氨基酸八种。其中菹草的氨基酸含量最高(36.63mg/g 湿重)、苦草最低(12.92mg/g 湿重);菹草的能值最高(3.36KJ/g 湿重)、小茨藻最低(1.28KJ/g 湿重)。2.草鱼、团头鲂对七种水生植物的最大摄食量(Y,g/24h)及消化率(Y,%)与鱼体重(X,g)相关显著,关系式为 Y=aX~b。从结果表明,随着鱼体重的增加,鱼对七种食料的相对摄食量下降(绝对摄食量上升),消化率提高。草鱼的最大摄食量一般比团头鲂高,而消化率一般比团头鲂低。
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14.
Seeds of the submerged vascular plants Najas marina, Najas minor and Najas flexilis are reported from submarine Holocene deposits from the southwestern part of the Baltic Sea, and we also report on a find of Najas minor from an Eemian deposit in Jutland, which is the first record of this species from the Eemian of Denmark. The common and widespread occurrence of especially the southern extralimital N. minor is indicative of higher than present summer temperatures during the period from 10300 to 8000cal.yearsBP. 相似文献
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16.
The limnology of an oligotrophic lake, Langvatn, situated in Trøndelag county in Central Norway, has been studied for five years (1974–1978). In two years, 1975 and 1976, the lake was fertilized with a general fertilizer to change feeding conditions for the zooplankton. Mean phytoplankton biomass in the epilimnion and primary production for the years (1974–1978) were 417, 618, 1370, 607 and 779 mg m−3 and 10.6, 22.2, 49.0, 26.8 and 17.7 g C m−2 yr−1 , respectively. Cladocerans were the dominant herbivore group in 1974 and 1975 and Rotifera in the next three years. The main difference in the interaction between phytoplankton and zooplankton occurred when cladoceran dominance gave way to rotifer dominance. Heavy phytoplankton grazing by cladocerans in 1974 and 1975 stabilized the biomass and maintained it at a low level, which also resulted in a relatively low primary production. The rotifer-dominated community during the years 1976–1978 did not possess the ability to maintain a stable level of algal biomass. Primary production was also relatively high during these years. 相似文献
17.
Marked changes in the relative numbers of roach Rutilus rulilus (L.), rudd Scardinius erylhroplhalmus (L.) and perch Perca fIuviatilis L. , in Slapton Ley, Devon, have been observed over the period 1967–1978. Historically, the lake had been dominated by rudd and perch; significant numbers of roach were not thought to be present until 1967. From then onwards the roach population exhibited a considerable expansion, apparently replacing the rudd, which had virtually disappeared by 1974. In 1975 extensive mortalities of roach were caused by the pseudophyllidean cestode Ligula intestinalis L. During 1976 and 1977 larger number of rudd, belonging to the 1975 and 1976 year classes, were present, suggesting that the roach mortalities might be giving the rudd a chance to recover. However, very few rudd were present during 1978, possibly because lower incidences of ligulosis during 1976–1978 had allowed the roach to recover from the main outbreak of the disease in 1975, and to replace the rudd for the second time. Evidence from trap catches indicated that the perch population had shown a consistent decline between 1970 and 1977. The major phase of this decrease occurred between 1971 and 1973, when the roach population was increasing the most rapidly. Comparisons were made with changes in fish populations in other localities. The major reason for the changes observed was thought to be a competitive relationship between the plankton feeding younger stages, with roach being the dominant species, although other factors may also have been involved. 相似文献
18.
Profundal chironomid populations during a fertilization experiment in Langvatn, Norway 总被引:1,自引:0,他引:1
Kaare Aagaard 《Ecography》1982,5(3):325-331
Populations of Heterotrissocladius subpilosus and Phaenopsectra (Sergentia) coracina were studied from 1974 to 1978 in Langvatn, South-Trøndelag, Norway. During 1975 and 1976 the lake was fertilized respectively by 1600 kg and 1000 kg fertilizer, (20% N, 4,8% P).
Fertilization had a positive effect on primary production and zooplankton. The effect on the two chironomid species, which both need more than one year for development, was ambiguous. However, there was a positive relationship between the density of H. subpilosus larvae and the primary production.
The number of P. (S.) coracina larvae steadily increased during the investigated period. Production estimates gave values in the range 0.6–1.5 g w.w. m−2 yr−1 for H. subpilosus and ca 2.3 g w.w. m−2 yr−1 for P. (S.) coracina . 相似文献
Fertilization had a positive effect on primary production and zooplankton. The effect on the two chironomid species, which both need more than one year for development, was ambiguous. However, there was a positive relationship between the density of H. subpilosus larvae and the primary production.
The number of P. (S.) coracina larvae steadily increased during the investigated period. Production estimates gave values in the range 0.6–1.5 g w.w. m
19.
江苏为全国多湖泊的省份之一,水生植被十分繁茂。影响湖泊水生植被生长、分布的环境因素是多方面的,湖水深度与透明度的影响最为明显。江苏湖泊水生植被的组成植物隶属30科,48属,共62种,可区分为挺水、浮叶、漂浮及沉水四类生活型植物。它们的分布有一定的规律,在沿湖岸浅水处,形成挺水植物带,向湖心方向随着湖水变深,而为浮叶植物带、沉水植物带。漂浮植物因流动性大,通常不形成独立的植物带。各植物带内分别形成相应的植物群落,在两个植物带叠接处则形成混交的群落。江苏湖泊水生植被共有16个主要群落类型。本文对湖泊水生植被的经济用途作了较详细的讨论。 相似文献
20.
Interactions between zooplankton and fish in a fertilized lake 总被引:16,自引:0,他引:16
Arnfinn Langeland 《Ecography》1982,5(3):273-310
The effects of fish predation on the zooplankton community in an oligotrophic lake, Langvatn, near Trondheim in Central Norway, were investigated during a six-year period (1973–1978), together with the added effects of changes produced by adding artificial fertilizer in 1975 and 1976. The improved nutrient conditions in 1975 resulted in a rapid increase in biomass and production of the largest herbivore zooplankton species and of the fish population. A change in the behaviour and food habits of the arctic char was recorded; they became more pelagic and fed mainly on zooplankton. An increased survival rate of 0-group and biomass of planktivorous fish in 1975 enhanced the degree of fish predation on the zooplankton during subsequent years (1976–1978). As a consequence of fish predation, the composition of the zooplankton changed, from a mainly large-sized to a mainly small-sized community, dominated by Bosmina longirostris and rotifers. Since fish predation is size-selective and visibility-dependent, it induced a decrease in mean size and in body length at onset of maturity of the cladoceran populations and probably also weakened their ability to produce resting eggs. 相似文献