Article

Bacterioplankton and Phytoplankton Populations in a Rapidly‐Flushed Eutrophic Reservoir

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Abstract

Densities of bacterioplankton and phytoplankton were studied in relation to water retention time, temperature, nutrient concentrations, and other variables in a eutrophic montane reservoir (Bluestone Lake, West Virginia, U.S.A.). Weak temperature stratification occurred occasionally during the summer, but the reservoir did not become anaerobic. Water retention times were short (3.9 to 9.7 days between June and December), and differences in flushing rate within that range were important in regulating phytoplankton populations. Green algae and planktonic diatoms were dominant in summer during periods when water residence times were shorter. The occurrence of blue-green algal blooms in fall was related to increased water residence times. Retention time was highly correlated with the percent composition of phytoplankton represented by Anabaena spp. and Microcystis sp. (r=0.898, p<0.001). Advective effects limited phytoplankton biomass when retention time was shortest, but were not as important when retention times were longer. Peaks in bacterial densities often coincided with decreases in viable algal cell densities, so bacterioplankton were less directly related to retention time.

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... Conversely, from May to August, the water column mixes. Cyanobacterial blooms generally occur when the retention time is longer, whereas diatoms and Chlorophyta have shorter retention times (Perry et al., 1990). ...
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... d -1 is exceeded. However, Perry et al. (1990) reported that standing crops were limited by rates of cell export only at extremely high flushing rates (>0.25 d -1 ), and that the effects were not pronounced at 0.1-0.17 d -1 flushing rates. ...
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... Besides this, higher flow rates and shorter water residence time tend to favour faster-growing diatom taxa (e.g. Perry et al., 1990). ...
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... In fact, the hydrologic conditions in 1997, reflected by the lower water retention time and increased hydraulic loading, may have selected against organisms with longer generation times (Basu and Pick, 1996) but may have favoured plankters with shorter generation times (phytoplankton, rotifers). However, water residence time in TDNP (131.4 days) exceeded the critical period needed for maturation of plankton communities (Perry et al., 1990;Basu and Pick, 1996), although water velocity can be high enough, particularly in spring, to dilute crustaceans in TDNP. Assuming that crustacean rinsing is negligible on a whole year basis, we suggest that dispersing mosquito fish populations, which occurred in 1997 (Alvarez-Cobelas, personal observation), effectively controlled crustacean biomass by predation (Meffe and Snelson, 1989;Rojo et al., 2000). ...
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... Similarly to other data reported (STRASKRABOVA, 1979, PERRY at al. 1990) the spatial and seasonal changes of the bacteria abundance are better expressed than the vertical gradient during the time of summer stratifi cation. Furthermore the seasonal changes (differences between spring and summer abundances) of bacterioplankton biomass were better expressed than the algal ones. ...
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Some trophic characteristics as chlorophyll-a, Secchi-disk transparency, turbidity, phytoplankton and bacterioplabkton abundances were investigated during spring and summer of 2005 in three reservoirs in northeastern Bulgaria, suggested by the experts of the Ministry of Environment and Waters (MEW) as po-tential reference sites. Different characteristics show differences in the assessment of the reservoir trophic status as only Tsonevo seems to be appropriate to reference site on the basis of the most of characteristics studied. Secchi-disk transparency seems to be inappropriate for assessment of the ecological status of the studied water bodies without considering its different components especially at the time of spring high waters. It is necessary to separate clearly different zones (water bodies) of reservoirs, which strongly depend on the morphometry, seasons, retention time and development of their shoreline. Phytoplankton (both abundance and composition) seems to be a good indicator for the differentiation of reservoir zones. Bacterial contribution to some of investigated variables (e.g. turbidity) and bacteria-algae relationships were also studied. Indication for top-down control of mixotrophic algae on bacteria was obtained under conditions of P-limitation.
... In this regard, Abdel-Tawwab (2003) and Abdel-Tawwab and El-Marakby (2004) reported that Nile tilapia has the capability to select Cyanobacteria as a food item, in addition to Bacillariophyceae, Chlorophyceae, and Euglenophyceae. On the other hand, Perry et al. (1990) found that green algae and diatoms were dominant in summer, while blue green algae were dominant in autumn. ...
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... Several studies have shown that algal communities during pre-disturbance periods with short residence time are generally dominated by diatoms. Cyanobacterial communities often dominate in post-distrurbance periods with variations in flushing rates (Stockner and Benson, 1967; Peterson and Stevenson, 1989; Perry et al., 1990). Additionally, changes in phytoplankton diversity can be dependent on the availability of growth limiting resources. ...
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... A residence time of -3 days may be critical. The shortest onset of growth was found after 3-4 days (Perry et al., 1990; Basu and Pick, 1996). This threshold is in agreement with the generation times of rotifers (Walz, 1987). ...
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Primary production in Marion Lake is inversely related to the rate at which water enters the lake when light intensity is corrected to a standard level. Increased flushing rates reduce the phytoplankton standing crop thereby lowering the total primary productivity in the lake. Thus seasonal variations in rainfall in southwestern British Columbia exert an appreciable influence on the annual productivity pattern of the lake’s phytoplankton. Lake water artificially enclosed within small areas of the lake produced algal blooms while phytoplankton standing crop in the rest of the lake remained low. Nannoplankton appear to have a selective advantage over larger, more slowly reproducing forms in Marion Lake. The production: biomass ratio for lake phytoplankton was used as an indication of the general type of limiting factor affecting the instantaneous rate of productivity in the lake.
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Water renewal may influence reservoir zooplankton communities through the mechanisms of dilution, transport (selective removal or addition), or through localized modifications of limnological conditions (e.g., light penetration, food quality, temperature) which then provide the setting for alteration of zooplankton community structure. An inverse relationship between reproduction in cladoceran zooplankton and water renewal time was found for six reservoirs sampled during summer 1980. This relationship suggests a strategic response in resource allocation by cladoaerans to dilution effects associated with water renewal. However, analysis of variation in cladoceran demography at different sites within each of the reservoirs and over a four-month period at a single site in one reservoir demonstrated that repoductive variation could be explained by spatial or temporal variation in limnological conditions and independently of transport or dilution processes associated with water renewal.
Article
The zooplankton of the Blue Nile overcomes the adverse conditions of the flood by entering into a state of diapause. Resting stages were found in the river bottom, flowing water and rain pools. They were blown to different localities by wind and can withstand long periods of desiccation. Some species of zooplankton go into diapause more than once a year, notably during their seasonal peaks of abundance. Release from diapause occurred in the temperature range 20–30°C and was facilitated by longer photoperiods and decreased concentrations of suspended silt. Various species of zooplankton were induced in facultative diapause when stored in complete darkness.
Article
We examined the abundance and heterotrophic uptake of bacteria attached to particulate matter suspended in five coastal ponds and two marshes near Woods Hole, Mass. Although the number of particle-bound bacteria was low (<10%), these bacteria incorporated a large proportion (>40%) of [ ¹⁴ C]glucose and [ ¹⁴ C]glutamate in selected aquatic systems. The uptake per cell was significantly higher for epibacteria than for unattached bacteria in all systems. Two groups of the aquatic environments sampled were statistically different in the contribution made by particle-bound bacteria to total bacterial abundance and to total assimilation of [ ¹⁴ C]glucose and [ ¹⁴ C]glutamate. Particle-bound bacteria were more important in those waters with a high particle concentration and not flushed regularly by tides than in waters with a low particle concentration and flushed regularly.
Article
During 1981 the seasonal growth and community composition of phytoplankton were investigated at six sampling stations in Eau Galle reservoir, a shallow eutrophic basin located in central Wisconsin, U.S.A. Eau Galle was strongly dominated by diatoms (spring and fall), and co-dominated by cyanophytes and dinoflagellates (summer). Three species (Stephanodiscus hantzschii Grun., Aphanizomenon flos- aquae (L.) Ralfs, and Ceratium hirundinella (O.F.M.) Schrank) collectively contributed about 50% of total annual phytoplankton biomass. Phytoplankton response was quite similar at open water sampling stations, but differed at a station in the littoral zone and at another located near the mouth of the primary inflowing river. Depressed epilimnetic silica concentrations occurred during spring and fall periods of diatom growth. The development of nitrogen-fixing cyanophyte populations during the summer reflected reduced dissolved inorganic nitrogen availability. Midsummer mixing events reduced water column stability. Shifts in the phytoplankton species composition of Eau Galle appeared to occur in response to major changes in water column stability.
Article
1. This review considers the periodic cycles of species dominance in a wide selection of temperate lakes. By ascribing individual species to assemblages, a high incidence of similarity among periodic cycles is demonstrated. Reference to lakes at high and low latitudes, as well as to rivers, shows conformity to parts of the same broad patterns. 2. The role of population dynamics in shaping community structure is emphasized. Two types of change are recognized: autogenic, undirectional subsequences (successions), regulated by specific responses to critically changing resource-ratio gradients; and allogenic changes, regulated by variability in the physical environment. 3. Analysis of the responses of representative species to allogenic change permits further grouping of the assemblages. These groupings coincide with clear morphological distinctions among the same phytoplankton species according to their unit sizes and surface area/volume ratios. 4. It is argued that these properties condition the physiological responses of algae to seasonal variations in temperature, mixing and exposure to the underwater light field. The responses are compounded by relative resistances to loss processes (sinking, grazing), by short-term photosynthetic adaptation and vertical migratory behaviour. 5. Graphical summaries are presented that relate the morphologically-, physiologically- and behaviourally-mediated responses to a hierarchy of physical, chemical and biotic environmental variables. Phytoplankton periodicity is the outcome of these interactions.
Article
1. The diel vertical distribution and abundance of zooplankton in the Red River arm of Lake Texoma, Oklahoma‐Texas, U.S.A., were examined between 25 January and 26 June 1982. 2. During periods of low river inflow, zooplankton vertical patchiness was related to wind stress. Zooplankton did not maintain distinct vertical patches under strong mixing. 3. In mid May heavy rainfall in the drainage basin increased discharge from the Red River and reduced water retention time in the reservoir. The Red River water mass entered the lake as a turbid, surface overflow plume. During this period of flooding most zooplankton populations declined and the distributions of remaining individuals deepened. Greatest population losses occurred between 0 and 7m, depths where most zooplankton had been concentrated prior to the flood. 4. A model of population dynamics based on depth specific rates of water exchange between the lake and the Red River, estimated from conductivity changes through time, accounted for the general pattern of change in zooplankton abundance and vertical dispersion.
Article
Zooplankton community structure was examined at five stations in Normandy Reservoir, Tennessee, on six dates from 11 July to 15 September 1980. Four physical and chemical parameters at three depths at each station were used to discriminate statistically among areas of the reservoir over time; a similar analysis based on nine taxonomic and ecological categories of zooplankton was also completed. Each of the two multi-variate analyses provided a matrix of similarities among station-times (n = 30) in the reservoir. The two similarity matrices were compared by the Mantel test and were found to be not significantly concordant, suggesting that physical-chemical variation among areas in the reservoir during the summer months was not precisely reflected by zooplankton community structure. The lack of congruence between physically- and chemically-determined reservoir structure and structure implied by zooplankton taxa or functional groups was also observed in the results of a random-effects-model ANOVA of physical and chemical parameters and zooplankton densities. ANOVA of zooplankton densities revealed that spatial variation was generally greater than temporal variation, although most of the spatial variation was ephemeral (station-time interaction) rather than fixed (station effects). An ANOVA of physical and chemical variables revealed considerable fixed spatial variation over the same time scale.
Article
Various methods for the estimation of populations of algae and other small freshwater organisms are described. A method of counting is described in detail. It is basically that of Utermhl and uses an inverted microscope.If the organisms are randomly distributed, a single count is sufficient to obtain an estimate of their abundance and confidence limits for this estimate, even if pipetting, dilution or concentration are involved.The errors in the actual counting and in converting colony counts to cell numbers are considered and found to be small relative to the random sampling error.Data are also given for a variant of Utermhl''s method using a normal microscope and for a method of using a haemocytometer for the larger plankton algae.
Article
Dilution water, low in macronutrients, was added to Moses Lake on three occasions in 1977 and once in 1978 during the spring-summer period. The addition resulted in reducing the annual average inflow concentration of phosphorus from about 130–140 μg l−1 to 100 μg l−1. The water exchange rate in Parker Horn, which is 8% of the lake volume, increased from about 1% day−1 normally to 7 and 11% day−1 for the May–September period in 1977 and 1978, respectively. Lake water was displaced at a predictable rate in the whole lake as well as the areas proximal to the input, as verified by specific conductance.Improvements in lake quality, compared to values from 1969–70, were rather good with greater reductions in algal biomass occurring than might have been expected to result from the less impressive reductions in total P content. Chlorophyll a decreased by about 60–80% and total P decreased by about 50–60%, depending on the area of the lake. However, Chl a averaged only 15 μg l−1 during May–September 1978, while total P was rather high at 70–80 μg l−1. The fraction of the phytoplankton composed by blue-green algae decreased from 96% in 1970 to 68% in 1977–78. The cause for the effect on biomass and species composition is unknown, but may be related to dilution of blue-green excretory products.A dilution water input of about 6 m3 s−1 continuously during April–September would require 20% less total water and should provide adequate control of eutrophication in at least 30% of the lake volume proximal to the input and Parker Horn. That would provide an exchange rate of 5% day−1 for Parker Horn and should achieve lake water residuals by midsummer of ⩽50%. Two additional inputs to the lake are also proposed as two more phases in the restoration project.
Article
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Article
The seasonal succession of the phytoplankton of a small reservoir (Guelph Lake, Ontario) in the spring-summer of 1982 was compared to that in 1981. Mixing of the deeper waters occurred several times throughout the summer in 1982 but not in 1981. The water at 10 m became anoxic for only 2 weeks in late July in 1982. In contrast, in 1981, the water at 10 m became anoxic at the beginning of July and remained so until mid-September. The phytoplankton dynamics observed in 1982 did not follow the typical progression from spring diatoms to summer species adapted to survive under stratified conditions, as in 1981. Diatoms were present throughout the summer in higher amounts in 1982 than in 1981. The most obvious difference in the two summers was the much greater abundance of Aphanizomenon flow-aquae in 1982. Other blue-green algae including Microcystis aeruginosa, Gomphosphasria lacustris , and Lyngbya birgei appeared earlier on in 1982, but did not immediately increase in abundance as in 1981. In 1982, rates of phytoplankton community change were low in May and June and increases were observed in mid-July, early August, late August and late September. In contrast, in 1981, the rate of community change increased in late May, mid-June, early July and late July and remained low throughout August and September.
1969: Some effrcts of lake renewd on pliyt,oplankton productivity and species coin-position.--limnol
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DICKMAN, M.. 1969: Some effrcts of lake renewd on pliyt,oplankton productivity and species coin-position.--limnol. Ocemogr. 14: 660-666.
Ameriran Water U'orks A4ssociat,ion. ;tnd WiLtvr Pollution Control Federation). lYXf : Stondard Methods for t h c Esa.minat,ion of Wat.er and Wastewater. 15t.h Sea-sonal growth and community composition of phyt
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References AI'HA et trl. (Amrrican Public He;tlt,h Assoriat,ion, Ameriran Water U'orks A4ssociat,ion. ;tnd WiLtvr Pollution Control Federation). lYXf : Stondard Methods for t h c Esa.minat,ion of Wat.er and Wastewater. 15t.h. ed.--Aniericm Public Henlth Association, Wtmhingt'on, D.C. 1134 pp. BARKO, J. W., D.,T. BATES, C. J. FILBIN, S. M. HENNINCTON and D. C. MCPARLAND, 1984: Sea-sonal growth and community composition of phyt,oplankton in a eutrophic Wisconsin inipoiuid-nicnt,.-J. Freshx-atcr Erol. 2: 519-533.
The phospliorus-cliloropliyll rclationship in 1akrs
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DILLON, P. J., nnd P. H. RIGLEK, 1974: The phospliorus-cliloropliyll rclationship in 1akrs.---Liniriol. Oceanogr. 19: 767-773.
Water Resources Data West Virginia, Water Year 1985
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Portion) OECD Eutrophication Project: Nutrient Loading-Lake Response Relationships and Trophic State Indices
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SAS User's Guide.-Cary, North Carolina
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SAS User's Guide.-Cary North Carolina
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Studies on redox potential of marine sediments
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Geological Survey and West Virginia Geological and Economic Survey Morgantown W
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Plankton in a rapidly flushed impoundment: spatial distribution, population dynamics and community structure
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