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-Relations between maximum depth, maximum effective length, and proportion of unstratified profiles during May–Aug. (a) Maximum depth versus maximum effective length (n = 231). The reference line was found by Gorham and Boyce (1989) to separate north-temperate natural lakes with and without stable stratification. (b) Mean mixed depth vs. maximum effective length (n = 229). (c) Mean thermocline depth vs. maximum depth (n = 229).  

-Relations between maximum depth, maximum effective length, and proportion of unstratified profiles during May–Aug. (a) Maximum depth versus maximum effective length (n = 231). The reference line was found by Gorham and Boyce (1989) to separate north-temperate natural lakes with and without stable stratification. (b) Mean mixed depth vs. maximum effective length (n = 229). (c) Mean thermocline depth vs. maximum depth (n = 229).  

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Vertical profiles of water temperature (n = 7193) and dissolved oxygen (n = 6516) were collected from 235 Missouri reservoirs during 1989–2007; most data were collected during May–August and provide a regional summary of summer conditions. Collectively, surface water temperature ranged from a mean of ∼22 C in May to ∼28 C in July, and individual su...

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... summer. In the shallowest basins (<3 m), however, strat- ification was rare or ephemeral; 13 (including 7 oxbows) had homothermal profiles in >75% of the collections. Mor- phology varied among reservoirs, and a combination of maximum depth and maximum effective length (MEL) ex- plained 52% of variation in the frequency of homothermal conditions (Fig. 2a). These, and other standard dimensions (surface area, maximum length, maximum effective width), are strongly intercorrelated, and alternate combinations ex- plained similar variation in mixing frequency. Interestingly, while most Missouri reservoirs stably stratify, the analysis by Gorham and Boyce (1989) shows that natural lakes with ...
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... maximum length, maximum effective width), are strongly intercorrelated, and alternate combinations ex- plained similar variation in mixing frequency. Interestingly, while most Missouri reservoirs stably stratify, the analysis by Gorham and Boyce (1989) shows that natural lakes with similar depth and length would not stratify (reference line in Fig. 2a). ...
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... mixed depths and thermocline depths (Table 1) were strongly correlated with reservoir dimensions, and the fit was improved by limiting data to reservoirs that were stratified in >75% of profiles (stably stratified dataset). Variation in mixed depth was ex- plained by both MEL (57% in the full dataset, and 68% in the stably stratified dataset; Fig. 2b) and by maximum depth (Z max , >72% of variation in both datasets; Fig. ...
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... with reservoir dimensions, and the fit was improved by limiting data to reservoirs that were stratified in >75% of profiles (stably stratified dataset). Variation in mixed depth was ex- plained by both MEL (57% in the full dataset, and 68% in the stably stratified dataset; Fig. 2b) and by maximum depth (Z max , >72% of variation in both datasets; Fig. ...
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... natural lakes that are shallow relative to their sur- face area and with similar dimensions to Missouri reservoirs would not stratify ( Fig. 2a; Gorham and Boyce 1989). An explanation for this difference is that Missouri reservoirs are impounded in the valleys of erosional topography, and many are located in public lands with forested riparian zones; both features potentially reduce wind exposure and favor strati- fication of shallow water bodies (Demers and Kalff 1993, France ...

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... Studies have shown that thermal stratification is a common characteristic of deep-water lakes and reservoirs, significantly affecting the vertical distribution of dissolved oxygen concentration and plankton populations (Jones et al. 2011, Zhang et al. 2015, Niu et al. 2016, Qiu et al. 2016, Novais et al. 2019. The formation of thermal stratification can deteriorate water quality and accelerate the consumption of dissolved oxygen in the bottom water (Lu & Li 2014). ...
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... Epilimnetic temperature and dissolved oxygen were determined for each pro le by taking the mean of these parameters above the mixing depth. The depth where anoxia began, or anoxia depth, was considered to be the rst depth where dissolved oxygen concentrations were ≤ 1 mg L − 1 (Jones et al. 2011). Annual means of mixing depth, anoxia depth, epilimnetic temperature, and epilimnetic dissolved oxygen were used for statistical analyses. ...
... Water Temperature and Water Levels Warm water temperatures could limit zebra mussels from reaching high densities in Missouri reservoirs. Between May and August, surface water temperatures in most Missouri reservoirs are greater than 25°C, while mean surface water temperatures in a quarter of reservoirs is ≥ 30°C (Jones et al. 2011). Zebra mussel ltration rates begin to decline above 22°C; above 25°C, zebra mussel growth rates decline (Thorp et al. 1998 . ...
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... Studies have shown that, in the thermal stratification period, the penetration of dissolved oxygen and nutrients in the water will be blocked by the thermocline, resulting in the oxycline and bottom hypoxia phenomena, and, at the same time, nutrients will also form a stratification phenomenon [38,39]. In this study, the number of species showed a gradually decreasing trend from the I-VI layers (Figure 4), which was related to the existence of the thermocline. ...
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... As for the process of production and mitigation of N 2 O in wastewater treatment plant, the mechanism of N 2 O production have been investigated (Chen et al. , 2021Ni and Yuan 2015), however, when it referred to stratified reservoirs, thermal and dissolved oxygen (DO) stratification may have great effects on N 2 O production (Deemer et al., 2011;Jones et al., 2011). Research on thermal and DO stratification has examined the spatiotemporal variation mechanism in N 2 O production Liu et al., 2017), N 2 O dynamics in water layers (Beaulieu et al. 2014(Beaulieu et al. , 2015, the impact of reservoir management on N 2 O production (Bao et al., 2015;Yu et al., 2018). ...
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... Most reservoirs stably stratify by mid May, but few are sufficiently deep to have hypolimnia with near-uniform temperatures (Jones et al. 2011a). showing mean long-term total phosphorus concentrations (mg/L) for each reservoir. ...
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Jones JR, Thorpe AP, Obrecht DV. 2020. Limnological characteristics of Missouri reservoirs: synthesis of a long-term assessment. Lake Reserv Manage. XX:XX–XX. Missouri reservoirs reflect their edaphic location in the midcontinent ecotone between historic prairies and forests. Most are small (median surface area of 28 ha) but provide essential services in a region with few natural lakes. Long-term summer monitoring data (1978–2016) show that they span the full trophic state range, with oligotrophic reservoirs in deep, forested valleys and eutrophic–hypereutrophic impoundments in agricultural regions. In regression analysis, row crop (a surrogate for agricultural nutrient loss) along with depth and flushing rate accounted for some two-thirds of variation among reservoir nutrients. Hydrology is a strong influence; total phosphorus (TP) effectively doubles between flushing rates of 0.25/yr and 2/yr when holding land cover and depth constant. Temporal variation characterizes these impoundments; many show >3-fold range in mean summer trophic state metrics, which is influenced by the volume and timing of annual inflow. This variation may mask gradual nutrient-driven changes in trophic state; based on simulation, doubling chlorophyll (Chl) in a given lake over 20 yr could be undetectable with routine summer monitoring. Some two-thirds of cross-system variation in mean Chl was explained by TP, and inorganic solids further reduced variation (negative coefficient). On average, Chl:TP ratios increased from 0.28 to 0.48 during summer, coincident with a decline in inorganic solids. Inorganic particulates largely determine Secchi transparency and can result in light limitation of phytoplankton. Small reservoirs cover nearly double the area of major impoundments worldwide and are known for an intensity of ecological processes, making this information relevant beyond the region.
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... Anthropogenic nutrient loads have increased phytoplankton growth and the subsequent decomposition of the associated organic material has increased hypolimnetic hypoxia in lakes since the 1850s (Jenny et al. 2016). Cold water fish require access to cool water refugia, and these areas are rendered uninhabitable by hypoxia (Coutant 1985;Müller and Stadelmann 2004;Plumb and Blanchfield 2009;Jones et al. 2011;Arend et al. 2011). Warm-water fish generally tolerate hypoxia but hypoxia, coupled with a warm epilimnion, can cause fish species that require cooler temperatures to experience a 'thermal-dissolved oxygen squeeze' (after Coutant 1985) requiring them to select between suboptimal temperatures or oxygen (Arend et al. 2011). ...
... Specifically, managers should have tools to determine how a reduction in nutrient loads and associated changes in observed phytoplankton abundance would improve dissolved oxygen concentrations. Relationships between nutrient concentrations and chlorophyll (Chl) are readily available (Jones and Bachmann 1976) but empirical relationships between Chl and dissolved oxygen concentrations are rarely reported (Jones et al. 2011). ...
... This estimate of DO m necessarily includes some measurements in the metalimnion, which may increase our estimates of DO m relative to studies that can focus only on the hypolimnion. However, many lakes in the MO and NLA datasets were too shallow to maintain a hypolimnion with small vertical temperature gradients (Jones et al. 2011), and therefore, an approach for consistently defining the hypolimnion for all lakes was not available (Quinlan et al. 2005), and we opted to include all depths below the thermocline in our calculation of DO m . The depth of the lake below the thermocline was also computed as the difference between the maximum depth recorded for each lake and the mean depth of the upper boundary of the metalimnion as defined above. ...
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