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# Seasonality modulates wind-driven mixing pathways in a large lake

## Abstract

Turbulent mixing controls the vertical transfer of heat, gases and nutrients in stratified water bodies, shaping their response to environmental forcing. Nevertheless, due to technical limitations, the redistribution of wind-derived energy fuelling turbulence within stratified lakes has only been mapped over short (sub-annual) timescales. Here we present a year-round observational record of energy fluxes in the large Lake Geneva. Contrary to the standing view, we show that the benthic layers are the main locus for turbulent mixing only during winter. Instead, most turbulent mixing occurs in the water-column interior during the stratified summer season, when the co-occurrence of thermal stability and lighter winds weakens near-sediment currents. Since stratified conditions are becoming more prevalent –possibly reducing turbulent fluxes in deep benthic environments–, these results contribute to the ongoing efforts to anticipate the effects of climate change on freshwater quality and ecosystem services in large lakes.

## Introduction

Lake thermal regimes are being seriously altered worldwide due to ongoing climatic change1,2, with implications for the health of these ecosystems3,4. By controlling the vertical exchange of heat, greenhouse gases, oxygen, and nutrients5,6,7, turbulent mixing in stratified lakes regulates the strength of deep stratification8 and the thermal and ecological response to external forcing9,10,11. A comprehensive characterisation of the processes conducive to mixing in lakes is imperative to refine predictions of the fate of lake ecosystems under changing environmental conditions. Although mixing in the stratified interior of lakes relies almost exclusively on wind stress as an energy source12, energy pathways towards mixing are often tortuous, mediated by non-linear interactions13,14 and dependent on several morphological and environmental factors15,16,17. This complexity stems from the fact that, in the bulk of stratified interior waters, wind-driven turbulence occurs only indirectly via excitation of internal hydrodynamic motions (basin-scale seiches, internal waves, gyres, etc.18). Internal motions decay at the lake boundaries by friction with the bottom19,20 or degeneration through interaction with slopes21,22, or within the water-column due to shear instabilities23,24,25, all generating turbulent dissipation and diapycnal mixing but with distinct ecosystemic consequences26,27.

The detailed empirical quantification of energy dissipation and mixing pathways is hampered by the technical and operational challenges of measuring turbulent fluxes in the field over long periods. The standing knowledge builds upon a few integrative field studies aiming at resolving all relevant components of the turbulent kinetic energy (TKE) budget28,29,30,31, interspersed with a larger number of process-oriented campaigns targeting one or a few specific processes25,32,33,34,35. Integrative studies have historically represented major breakthroughs and facilitated the parameterisation of internal lake mixing in one-dimensional computational models36,37,38, which have been instrumental for predicting the long-term response of lakes to climatic changes39,40,41. Despite their relevance, integrative budgets have so far had limited temporal coverage. Therefore, little is known about the influence of seasonal variability of stratification and wind on the energy pathways and the intensity of turbulent fluxes.

We used a newly developed 100 m2 floating research infrastructure (LéXPLORE42) to carry out an integrative year-round TKE budget in the deep, large, oligomictic Lake Geneva (Switzerland-France, surface area 582 km2, mean and maximum depths 154 and 309 m, respectively, Supplementary Fig. 1). We quantified the temporal variability of the rates of energy input, dissipation and mixing, in the water-column and bottom boundary layer (BBL), between April 2019 and April 2020. The dataset43 includes continuous records of meteorological variables, full water-column moored measurements of temperature and current velocity (with acoustic Doppler current profilers, ADCP, moored near the surface), and near-bed temperature, current velocities, and turbulence (measured with a high-resolution current profiler). The continuous observations were interspersed with 447 regular (approximately weekly) microstructure turbulence profiles. This unique dataset is used here to unravel the mixing pathways across seasons depending on varying stratification and wind conditions. Our findings substantiate that energy pathways are modulated by seasonal stratification, with the benthic boundary layers being highly turbulent in winter but isolated from wind-driven mixing during the stratified season.

## Results

### Seasonal stratification

The sampling covered a typical annual cycle of stratification and destratification conditions44 (Fig. 1). During the spring period (April–July 2019, green bar) the net surface heat flux warmed the lake (Fig. 1a). Water-column temperatures (Fig. 1b) and the Schmidt stability (Sc, Fig. 1a), representing the strength of density stratification, increased over this period, as a broad seasonal thermocline formed, extending from the base of a shallow surface mixed layer (<10 m) to ~30 m depth (Fig. 1b). During summer (July – October 2019, yellow shading), heating progressively declined, water temperatures and Sc were maximal by early August and decreased thereafter. During autumn (October 2019–January 2020, brown bar), cooling was maximal, water temperatures dropped and the surface mixed layer deepened steadily from <10 m to ~70 m at the end of the period, eroding the main seasonal thermocline. Following this trend, Sc decreased, reaching minimum values at the onset of the winter period (January–April 2020, blue bar). During the first month of this period, the cooling rate progressively reduced. By mid-February, the lake experienced the minimum water-column temperature (7–8 C) and the deepest mixed layer (90 m). Thereafter, warming was re-established and a weak shallow stratification formed.

### Wind energy input

The supply of mechanical energy by wind, quantified as the downward flux of wind mechanical energy (P10) at 10 m above the lake surface, showed marked seasonal variations. Over the annual cycle, P10 averaged to 172 ± 243 mW m−2 (±standard deviation; Fig. 2a, Table 1), corresponding to a mean wind speed of W10 = 2.9 ± 2.5 m s−1, and was minimal in summer (respectively, 89 ± 228 mW m−2 and 2.6 ± 2.0 m s−1), and maximal in winter (resp., 261 ± 670 mW m−2 and 3.2 ± 2.9 m s−1) (Figs 1c, 2b,c). The actual transfer of wind energy into internal lake motions was quantified with the rate of wind work on surface currents (RW) determined from the correlation of wind stress and current velocity corresponding to the surface expression of deep-water motions (see Methods). The mean annual RW was 0.61 mW m−2, corresponding to an overall energy transfer efficiency of γW = RW/P10 = 0.36%. An alternative estimate of γW = 0.43 ± 0.05%, corresponding to 0.72 mW m−2, was computed with a linear regression of RW against P10 (Fig. 3). For low P10 500 mW m−2, negative RW values (i.e. wind working against lake currents) were as likely as positive, while positive RW were only clearly dominant for strong winds (Fig. 3). This suggests an important role of inertia in modulating the energy uptake by the lake, since only strong and persistent winds seem able to displace lake waters along the wind direction45. Local effects, contingent to the alignment of the wind and currents at the sampling location, explain the large scatter observed in this figure. Taking this variability into account, we assume γW = 0.36 − 0.43% as a plausible range of the fraction of mechanical energy that is injected into the lake’s internal motions. This small fraction is counterbalanced by the bulk of the downward wind energy flux (P10) being dissipated in the atmosphere and lake surface boundary layers and temporally stored in the surface wave field, which dissipates mostly in near-shore areas12.

### Internal motions

Despite the large seasonal variations in the wind energy flux, which was three times larger in winter than in summer, the seasonally-averaged, depth-integrated kinetic energy (KE) stored in internal motions measured with ADCP’s varied weakly around a mean value of 87 J m−2 (Fig. 1d, Table 1). Indeed, contrary to the energy input, mean KE was even slightly smaller in winter (79 J m−2) and autumn (81 J m−2), compared to spring (98 J m−2) and summer (91 J m−2). Stormy wind events in spring (e.g. May 2019) and winter (e.g. February 2020) produced short-lived events of high KE that were rapidly damped, not affecting the mean KE significantly. The available potential energy (PE) contained in baroclinic internal motions, quantified using temperature measurements recorded with two moored systems (Supplementary Fig. 2), was slightly larger than KE (the average PE:KE ratio was ≈1.26). With this ratio, we estimated that ~196 J m−2 of available mechanical energy (ME = KE + PE) were stored on average as internal motions (Fig. 2a).

Concerning the spatio-temporal structure of internal motions, the measured currents were mostly zonal, following the coastline orientation at the sampling location (Supplementary Fig. 1). Although the temporal variability of current velocities was concentrated around periods of 2–8 days year-round, both near the surface (4 m) and bottom (100 m), the overall intensity of near-bed velocities exhibited a strong seasonal modulation with lower values between June and October (Supplementary Fig. 3). This modulation was caused by a shift in the vertical structure of currents (Fig. 1e), from a two-layer structure with a node at the center of the thermocline (~15 m) during summer to vertically homogeneous profiles in winter (Fig. 1e). The summer current structure is consistent with the first baroclinic mode (M1), which dominated KE during this season, while the barotropic mode M0 dominated KE in winter (84%) and autumn (62%) (Fig. 1d). Summer observations are compatible with coastal-trapped internal Kelvin waves46,47. These co-existed with a net depth-integrated westward transport during spring and summer (Supplementary Fig. 1), explained by the contribution of the barotropic mode, which represented 33% and 56% of KE, respectively. This suggests the presence of a basin-wide cyclonic gyre as a response of dominant northeasterly winds48. During autumn and winter periods, the net depth-integrated transport was more erratic, due to stronger and more variable wind forcing (Supplementary Fig. 1).

### Water-column interior dissipation

The fate of the injected wind mechanical energy was assessed by quantifying the rates of energy dissipation and mixing in the water-column and the BBL. The TKE dissipation rates (ε) in the water-column determined from microstructure profiles were in the range of $${\varepsilon }_{{{{{{{{\rm{int}}}}}}}}}\approx {{{{{{{\mathcal{O}}}}}}}}(1{0}^{-10}-1{0}^{-8})$$ W kg−1 (mean: 4.4 [4.2 − 4.7] × 10−9 W kg−1 [99% confidence interval], median: 7.0 × 10−10 W kg−1). In spring, summer and autumn, the average ε profile decreased with depth across the thermocline from ~10−8 W kg−1 in subsurface layers to ~10−10 W kg−1 at ~70 m depth (Supplementary Fig. 4). In winter, ε profiles were almost homogeneous, with some enhancement in the upper and lower-most layers. The depth-integrated TKE dissipation in the water-column interior (between the surface and bottom boundary layers) was between $${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{int}}}}}}}}}=0.04-0.72$$ mW m−2 (5 and 95% percentiles) for individual profiles and averaged to 0.27 ± 0.24 mW m−2 (± SD) during the sampling period, with little seasonal variations (Supplementary Fig. 5, Table 1).

The microstructure profiles were collected on 51 individual days along the annual cycle and may not be representative of the system under all conditions. We attempted to overcome this limitation by deriving a scaling relationship between $${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{int}}}}}}}}}$$ and KE at the time of profiling using a type-II log-log linear regression49. This correlation suggested a significant dependence of dissipation on KE, $${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{int}}}}}}}}}\propto {{{{{{{{\rm{KE}}}}}}}}}^{0.64\pm 0.04}$$ (Fig. 4a). This empirical relation provided hourly $${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{int}}}}}}}}}$$ estimates based on ADCP-derived KE (Supplementary Fig. 5b), which averaged at 0.27 ± 0.22 mW m−2 over the annual cycle, very close to the microstructure observations (Table 1). Coherently with KE, measured and extrapolated $${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{int}}}}}}}}}^{{{{{{{{\rm{ADCP}}}}}}}}}$$ seasonal-mean estimates showed minor variability, mostly within <15% of the annual mean (Fig. 2a–d, Table 1).

### Bottom boundary layer dissipation

In the BBL, at 1 m above lake bed (mab), TKE dissipation rates obtained from the Aquadopp measurements varied within the range $${\varepsilon }_{1{{{{{{{\rm{mab}}}}}}}}}\approx {{{{{{{\mathcal{O}}}}}}}}(1{0}^{-10}-1{0}^{-6})$$ W kg−1, with higher values during the most energetic episodes in February 2020, when near-bed velocities reached ~10 cm s−1 (Supplementary Fig. 6). The average ε1mab during the Aquadopp deployment period (August 2019–August 2020, mean: 2.2 [1.4 − 3.6] × 10−8 W kg−1, median: 4.1 × 10−9 W kg−1) was about one order of magnitude larger than εint. The TKE dissipation rate integrated over the Ekman BBL and averaged during the deployment time overlapping with the study period (August 2019–April 2020) was $${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{BBL}}}}}}}}}=0.16\pm 3.38$$ mW m−2. The large standard deviation reflects the strong dissipation events occurring in winter (Supplementary Fig. 5c). As a consequence, seasonally averaged $${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{BBL}}}}}}}}}$$ increased by almost one order of magnitude from a minimum in summer (0.05 mW m−2) to a maximum in winter (0.42 mW m−2) (Table 1).

Since near-bed observations were not available in spring 2019, an indirect estimate was computed from near-bed velocities measured with the surface-moored ADCP (see Methods). The derived mean annual BBL dissipation was $${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{BBL}}}}}}}}}^{{{{{{{{\rm{ADCP}}}}}}}}}=0.20\pm 0.77$$ mW m−2, with strong seasonal variations, being minimal in summer (0.03 mW m−2), maximal in winter (0.38 mW m−2), and intermediate in spring and autumn (~0.17 mW m−2) (Fig. 2a-d). These estimates were in agreement with the Aquadopp measurements within roughly a factor of 2 (Table 1), which is coherent with the error of ~40% estimated for the drag coefficient used in this calculation (CD = 0.0032 ± 0.0013). In addition to turbulent dissipation, KE in the BBL is also lost by laminar friction within the thin viscous sublayer28,50. This term averaged to $${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{BBL}}}}}}}}}^{{{{{{{{\rm{lam}}}}}}}}}=0.11\pm 0.38$$ mW m−2 (Fig. 2d).

### Mixing

The fraction of TKE spent in vertical mixing, that is, in producing a net downward buoyancy flux (or an upward mass flux) across the stable stratification, was evaluated using the flux Richardson number, Rf = b/(ε + b), where b = KTN2 is the turbulent buoyancy flux, KT is the turbulent diffusivity51, and N is the buoyancy frequency (a measure of density stratification). Mean Rf, computed from microstructure profiles in the water-column (Fig. 4b) and near-bed measurements (Fig. 5, Supplementary Fig. 7), were Rf  ≈ 0.14 and ~0.12, respectively, both close to the canonical value of Rf = 0.16 − 0.2052,53, suggesting a relatively tight coupling between b and ε (insets in Figs. 4b, 5b). The relatively high value of Rf in the BBL is at odds with previous studies suggesting that Rf can be much lower in this layer, where strong turbulence normally operates in a weakly stratified environment27,54,55. The near-bed measurements showed that, despite episodes of strong dissipation, the BBL was moderately and persistently stratified (mean N2 = 0.91 × 10−5 s−2, Fig. 5a). These findings endorse the idea that secondary circulations continuously resupply buoyancy to sloping regions19,56,57,58, maintaining stratification and allowing mixing to continue. Taking these results into account, we assumed a time-constant mixing efficiency (Γ = Rf/(1 − Rf) ≈0.17, and 0.13 in the water-column interior and BBL, respectively) and estimated the time-averaged, depth-integrated buoyancy fluxes as $${{{{{{{\mathcal{B}}}}}}}}={{\Gamma }}{{{{{{{\mathcal{E}}}}}}}}$$. Annually, water-column and bottom turbulence produced a buoyancy flux of $${{{{{{{{\mathcal{B}}}}}}}}}_{{{{{{{{\rm{int}}}}}}}}}=0.046\pm 0.037$$ mW m−2 and $${{{{{{{{\mathcal{B}}}}}}}}}_{{{{{{{{\rm{BBL}}}}}}}}}=0.026\pm 0.100$$ mW m−2, respectively.

## Discussion

In summary, the correlation between wind and near-surface water velocities indicates that annually γW = 0.36−0.43% of the downward wind energy flux (P10 ≈ 172 mW m−2) feeds the internal motions of Lake Geneva (RW = 0.61 − 0.72 mW m−2) (Fig. 2a), which store ~196 J m−2 of mechanical energy, giving a mean energy residence time of τ = ME/RW ≈ 3.5 days. The sum of the energy sinks (~0.65 mW m−2, equivalent to 0.38% of P10) roughly balances the energy input. The sinks are split between dissipation ($${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{int}}}}}}}}}+{{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{BBL}}}}}}}}}+{{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{BBL}}}}}}}},{{{{{{{\rm{lam}}}}}}}}}=0.58$$ mW m−2, representing ~89% of RW) and mixing ($${{{{{{{{\mathcal{B}}}}}}}}}_{{{{{{{{\rm{int}}}}}}}}}+{{{{{{{{\mathcal{B}}}}}}}}}_{{{{{{{{\rm{BBL}}}}}}}}}=0.072$$, ~11% of RW). The energy sinks are almost equally shared between the water-column interior and the bottom boundary layer, with turbulent dissipation accounting for 0.27 mW m−2 (42% of RW) and 0.20 mW m−2 (30% of RW) in the respective regions, and laminar dissipation in the viscous BBL contributing with 0.11 mW m−2 (17% of RW). Because laminar dissipation ($${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{BBL}}}}}}}}}^{{{{{{{{\rm{lam}}}}}}}}}$$) does not produce mixing, the contribution of water-column turbulence to mixing ($${{{{{{{{\mathcal{B}}}}}}}}}_{{{{{{{{\rm{int}}}}}}}}}\approx 0.046$$ mW m−2) is larger than BBL turbulence ($${{{{{{{{\mathcal{B}}}}}}}}}_{{{{{{{{\rm{BBL}}}}}}}}}\approx 0.026$$ mW m−2).

Unique to our dataset is the one-year temporal coverage, which revealed the key role of seasonal variations in both the energy input rates and the energy pathways down to dissipation and mixing (Fig. 2b,c). This result contrasts previous energy budget analyses circumscribed to short periods, mostly during the stratified seasons. Due to seasonal changes in P10, the wind energy transferred to internal motions was three times larger in winter (1.00 mW m−2) compared to summer (0.32 mW m−2), even though the mean energy transfer efficiency seemed to remain rather stable over the annual cycle at γW ≈ 0.38% (Fig. 2). The water-column interior dissipation pathway reacted weakly to the changes in forcing, with a basal loss rate of ~0.27 mW m−2 throughout the seasons (coherent with the annual average), while the bottom sink damped rapidly the excess energy supplied in winter. Therefore, the water-column interior sinks dominated (~85%) the energy loss in summer, whereas the bottom pathway dominated (~68%) in winter (Fig. 2b, c).

Despite the variations in the energy flux, internal motions maintained a fairly constant energy level year-round and, as a consequence, the energy residence time was substantially longer during summer (6.6 days) compared to winter (2.2 days), indicating a distinct functioning of the system across the seasons. In summer, the energy residence time is close to that expected for a quasi-free oscillating system with a maximum depth of 309 m (~8 days)28, suggesting that stratification allows to transiently store wind energy away from the dissipative bottom environment in form of baroclinic motions. Conversely, the much shorter energy residence time in winter indicates that strong wind pulses dominate the lake’s energetics in this period, through transferring large amounts of energy, which get rapidly dissipated at the BBL. Therefore, instead of the slow continuous relaxation of the stored wind energy described for summer, most winter turbulent fluxes occur via a faster pathway, as a series of short, bottom-locked highly dissipative events. Interestingly, the constancy of the mean mechanical energy content in spite of seasonally variable energy fluxes resembles the properties of self-organized criticality described for a number of complex phenomena and recently attributed to geophysical flows59. According to this concept, turbulence re-organises the flow in such a way that a statistically stable mean state is maintained notwithstanding the variable forcing.

The large contribution of the lake water-column interior to dissipation and mixing on an annual basis and particularly during the summer season challenges the standing view that the bottom boundary layer is the dominant energy sink below the surface layer of stratified lakes28,60, and confirms previous limited evidence derived from observations in large lakes25,33. In addition, our results provide the first evidence that the contribution of the BBL to dissipation and mixing is strongly modulated by the intensity of wind forcing (r = 0.47) and, more important, water-column stability (r = − 0.81; Fig. 2e). The role of wind forcing is explained by strong winds transiently energising the BBL, where dissipation has a strong dependence on the flow velocities ($${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{BBL}}}}}}}}}\propto {u}^{3}$$). The chief role of stratification emerges because it regulates the transition from baroclinic motions during the stratified season to depth-uniform currents in winter, as previously described for other lakes33,61,62. Baroclinic motions retain most of the kinetic energy above the thermocline so that, in deep lakes with a shallow thermocline, near-bed velocities are comparatively reduced during periods of stratification.

The above findings suggest that the energetics of the BBL and their contribution to total dissipation and mixing in such lakes could be affected by changes in stratification and wind conditions, making them particularly sensitive to climate change. Like other perialpine and temperate lakes worldwide1,63,64, Lake Geneva has experienced an overall warming and increased prevalence of stratified conditions over the past decades. To assess the potential impact of these changes in the distribution of energy dissipation and mixing, we quantified the annual occurrence of stratification values above a threshold (Sc > 15 kJ m−2) for which the contribution of BBL dissipation becomes small ( 20%, Fig. 2e) in a historical (> 1980) time-series of density profiles collected monthly to bi-weekly in Lake Geneva (Fig. 6). This analysis revealed a significant increase of the number of days of highly stratified conditions at a rate of 8.6 ± 3.1 days per decade. Simulations of a Representative Concentration Pathway RCP6.0 scenario using a 1-dimensional lake model65 confirmed that this trend will continue over the 21st century (Fig. 6). Interpreted in the light of our results, these projections suggest that turbulence in the deep bottom boundary layers of Lake Geneva (and possibly other deep temperate lakes) could become progressively weaker over the next century, slowing down the exchanges between the sediments and the water-column.

Although our annual energy budget provides an unprecedented temporal description, its significance at the basin scale may be limited, since the measurements were collected at a single location over the shelf break. The local depth was ~30% shallower than the lake mean depth and the depth-integrated quantities (e.g. KE, $${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{int}}}}}}}}}$$) could be underestimated. This is unlikely the case for the stratified periods when KE and dissipation rates decayed rapidly with depth, but may be a concern in winter. In addition, since Lake Geneva lateral dimensions exceed the internal Rossby radius of deformation, internal motions are influenced by Earth’s rotation46, which could impact the distribution of BBL energy between pelagic and near-shore zones. To assess this, we examined a 6-month record of near-bed currents at a central location (Supplementary Fig. 8). The data revealed the presence of anticyclonic near-inertial Poincaré waves, not observed in the shelf break location, and showed that the BBL was overall less energetic with dissipation rates lower by a factor of 5, too low to account for a relevant fraction of the energy input, even in winter. These results confirm that the BBL at lake slopes must represent a major energy sink during the energetic periods, and that the shelf break location of our sampling point allowed to document this contribution. Further, the representativeness of the location is strongly supported by the tight coherence between the estimates of energy input and total dissipation for the different seasons (Fig. 2d), suggesting that, despite the obvious limitations, our energy budget captures the main seasonal variations of wind-driven turbulent fluxes in the stratified interior of Lake Geneva. Together with the interior mixing processes considered here, turbulent mixing in the surface boundary layer –directly driven by the input of kinetic and potential energy from the atmosphere– plays a major in controlling stratification and turbulent fluxes in the upper water -column and the exchange with the atmosphere. Those processes are tightly connected to episodic atmospheric forcing events and their full range of variability is challenging to capture using observations. The availability of novel research infrastructures, such as the LéXPLORE platform42, and the development of autonomous profiling instruments are set to offer new opportunities for improving our understanding of these processes in the near future.

## Conclusions

With an exhaustive field campaign, we described the seasonal energy pathways towards dissipation and mixing in a large lake with unprecedented temporal coverage and resolution. The full-year duration of the measurements unveils a previously overlooked seasonal modulation of the energy sinks and shows that the benthic environment is subjected to highly variable energetic conditions. Stratification isolates the deep benthic layers from wind energy and maintains very weak levels of turbulence in summer, but the same layers, particularly in slope regions, are responsible for damping the strong energy input during the weakly stratified winter season. Seasonal variability in near-bed turbulence has important biogeochemical and ecological implications, because near-bed turbulence controls the sediment-water exchange of heat, environmentally important gases66,67, metals, and nutrients68, influences benthic microbial communities69, and regulates the development and duration of anoxic conditions70. This is particularly relevant as global warming is driving a worldwide increase in the duration and intensity of stratification1,71,72, which, based on the relationship found between water-column stability and BBL dissipation and mixing, could reduce the overall energy levels in the deep boundary layers.

Notwithstanding the seasonal variability of the input, dissipation, and mixing fluxes, the fraction of wind energy transferred to internal motions (RW/P10 ≈ 0.38%) and available for mixing ($${{{{{{{\mathcal{B}}}}}}}}/{P}_{10}\approx 0.04 \%$$) remained remarkably constant throughout the annual cycle. Similar ratios have been reported for lakes of very contrasting morphology and forcing, ranging from the most voluminous lake on Earth, Lake Baikal29 (RW/P10 ≈ 0.2%, $${{{{{{{\mathcal{B}}}}}}}}/{P}_{10}\approx 0.04 \%$$), to mid-sized lakes like Lake Windermere30 in Britain (RW/P10 ≈ 0.13−0.64%, $${{{{{{{\mathcal{B}}}}}}}}/{P}_{10}\approx 0.05 \%$$) and the small Lake Alpnach28 in Switzerland (RW/P10 ≈ 0.7%, $${{{{{{{\mathcal{B}}}}}}}}/{P}_{10}\approx 0.06 \%$$). These results suggest that in spite of the intricate energy pathways, the strong dependence of mixing on wind energy tightly constrains the magnitude of turbulent fluxes in different systems, thus providing a simple rule of thumb to estimate the overall mixing levels of lakes exposed to variable wind forcing and assess the ecological implications73. Altogether, our thorough characterization of the mechanical energy pathways broadens the field-based knowledge on how mixing operates in lakes, offering a valuable benchmark for model development and assessment, which will allow to improve the predictions of the future evolution of these ecosystems.

## Methods

### Meteorological forcing

Meteorological parameters (air temperature, relative humidity, shortwave radiation, wind speed, wind direction, and atmospheric pressure) were recorded every ten minutes since 8 April 2019 with a Campbell Scientific Automatic Weather Station installed on the platform, 5 m above the lake level. Turbulent heat fluxes (latent and sensible) and wind stress (τw) at the lake surface were derived following the Monin-Obukhov similarity theory74,75, whereas radiative fluxes (shortwave and longwave) were derived with formulas calibrated for Swiss lakes76. The multiplicative factor in the longwave absorption formula was specifically calibrated for Lake Geneva to ensure that heat fluxes were coherent with the temporal evolution of heat content in the lake.

### Water-column temperature mooring

Water-column temperature in the upper 30 m was recorded with Minilog-II-T sensors (VEMCO, resolution 0.01 C) mounted at every 2.5 m vertical interval in a sensor chain installed near the platform. Full-depth temperature profiles were also recorded at high frequency (0.2 Hz) with two RBR thermistor chains (accuracy 0.002 C) for two periods (20 June to 18 August 2019 and 24 October 2019 onward). Both chains consisted of 24 thermistors, spaced by 0.25–0.5 m in the top 3 m, by 1 m down to 18 m depth, and by 3 m below.

### Water-column currents

Profiles of horizontal currents were recorded with two RDI Acoustic Doppler Current Profilers (ADCP) from 16 April 2019 to 15 April 2020. Until 8 August 2019, an RDI600 and an RDI300 were installed in a mooring located 8 m below the surface, looking upward and downward, respectively. Thereafter, only the RDI300 was used, installed directly at one of the LéXPLORE moon pools42 looking downward from the lake surface. The RDI300 recorded 300 pings every 15 min over a vertical grid of 53 cells with 2 m thickness, extending down to the lake bottom, and the RDI600 (when available) recorded 1000 pings every 10 min vertical grid of 31 cells with 0.25 m thickness, extending up to the lake surface. Shorter ensemble intervals and smaller cell sizes were used during the first deployment (until 12 June 2019), occasionally yielding poor data quality. For the analysis, the data were averaged with running windows of 2 h in time and 4 m in depth.

### Water-column microstructure and CTD profiles

A total of 447 deep (down to 80–100 m depth) microstructure turbulence profiles were performed approximately weekly on 51 different days between March 2019 and April 2020. Three different Rockland Scientific International Inc. (Canada) instruments were used: two small self-contained microCTD profilers (SN310, SN158) and a VMP-500 (SN028). In addition to high-resolution microstructure temperature sensors (2× FP07 fast thermistors), all three profilers were equipped with accurate conductivity-temperature-depth (CTD) and optical sensors (turbidity, fluorescence). The buoyancy of the instruments was regulated to achieve a free-falling profiling rate of ~35 cm s−1. In addition, full-depth (down to ~105 m) regular CTD profiles were carried out with a Sea&Sun CTD75M probe. In total, 99 CTD profiles were collected on a regular basis (typically weekly or bi-weekly) between February 2019 and April 2020.

### Near-bed currents and temperature

A near-bed moored structure was deployed from 16 August 2019 to 12 August 2020 to record high-resolution near-bed velocities and temperature. Velocities were measured with a high-resolution pulse-coherent ADCP, Aquadopp 2 MHz (Nortek). The instrument was mounted looking downward on a horizontal mast of the mooring structure at 2 mab. The instrument was located 2 m away from the main body of the structure to minimise possible distortion of the measured currents. Every hour, a 1024-datapoint burst of along beam velocities with a vertical spacing of 2 cm was recorded at 2 Hz. Since 17 December 2020, seven RBRsolo T thermistors (accuracy 0.002 C, sampling frequency 2 Hz) were installed along the main vertical mast of the structure between 0 and 3 mab, spaced by 0.5 m.

### Analysis: thermal cycle and lake stability

To characterise the seasonal thermal stratification cycle, a composite annual cycle of temperature, salinity, and potential density (ρ) was computed by merging the mooring, CTD, and microstructure profiler datasets by using a running average with a 30-days Gaussian window in the top 30 m and increasing length at lower depths, where data was not recorded continuously. The water-column Schmidt stability (Sc, i.e. strength of density stratification) was calculated from the running averaged ρ profiles as:

$${{{{{{{\rm{Sc}}}}}}}}=-\frac{1}{{A}_{0}}\int\nolimits_{{z}_{{{{{{{{\rm{bot}}}}}}}}}}^{0}g\rho \ (z-{z}_{v})A\ {{{{{{{\rm{dz}}}}}}}}$$
(1)

where A = A(z) is the hypsometric curve, A0 = 580 km2 is the surface area, zbot is the maximum lake depth (309 m) and zv is the lake’s center of volume. Since CTD profiles at the LéXPLORE location were restricted to 109 m, density profiles were completed down to zbot using deep casts collected by CIPEL monthly to bi-weekly at the deepest location77 (SHL2, Supplementary Fig. 1).

### Analysis: energy input

The downward flux of wind mechanical energy at 10 m (P10) was taken as a reference of wind energy supply to the lake. This was calculated as P10 = τwW10, where τw and W10 are the wind stress modulus and wind speed at 10 m above the lake surface, respectively28. The actual energy transfer was quantified with the rate of wind work (RW), calculated as the correlation between wind stress and near-surface water velocities: RW = τxu0 + τyv0, where τx,y are the zonal and meridional wind stresses and u0, v0 are the zonal and meridional near-surface current velocities derived from ADCP measurements. To ensure that RW provides a measure of the energy transferred to basin-scale internal motions, we followed Shimizu et al. (2008)20 and took u0 and v0 as the velocities at 0.5 m depth reconstructed by projecting the observed velocity profiles into normal vertical modes (see below).

### Analysis: internal motions

The kinetic energy (KE) stored in internal motions was characterised by projecting the ADCP-measured velocities onto normal vertical modes via least-squares fitting78. The shape of the vertical modes was computed by resolving the Taylor-Goldstein equation for the buoyancy frequency79, N2 = − gρ−1(∂ρ/∂z). The N2 profiles and normal modes were computed daily based on the smoothed seasonal ρ profiles. Similarly, the available potential energy of internal motions was computed from temperature mooring measurements by projecting the isothermal displacements δ onto normal modes, where $$\delta =-(T-\overline{T}){(\partial \overline{T}/\partial z)}^{-1}$$ was estimated from the temperature anomalies with respect to the 30-days running averaged profile ($$\overline{T}$$).

### Analysis: interior dissipation and mixing

Water-column profiles of turbulent kinetic energy (TKE, ε) and thermal variance (χ) dissipation rates in the water-column were derived from microstructure measurements by fitting the temperature gradient spectra computed in 2 m-thick overlapping bins (vertical resolution 0.5 m) to the theoretical Kraichnan spectrum following the MLE procedure80, as described in more detail elsewhere73,81. Volume-weighted and depth-integrated areal TKE dissipation rates in interior layers ($${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{int}}}}}}}}}$$), away from the influence of the surface (SBL, zSBL) and bottom boundary layers (BBL, zBBL), were calculated from each individual ε profile as:

$${{{{{{{{\mathcal{E}}}}}}}}}_{int}=\frac{V}{{A}_{0}}\frac{\int\nolimits_{{z}_{{{{{{{{\rm{BBL}}}}}}}}}}^{{z}_{{{{{{{{\rm{SBL}}}}}}}}}}\rho \varepsilon A\ {{{{{{{\rm{dz}}}}}}}}}{\int\nolimits_{{z}_{{{{{{{{\rm{BBL}}}}}}}}}}^{{z}_{{{{{{{{\rm{SBL}}}}}}}}}}A\ {{{{{{{\rm{dz}}}}}}}}}$$
(2)

where $$V=\int\nolimits_{-109{{{{{{{\rm{m}}}}}}}}}^{0}A\ {{{{{{{\rm{dz}}}}}}}}\approx 48.5$$ km3 is the total lake volume above the local bottom depth (~109 m). To avoid the influence of turbulence derived from direct interactions with the atmosphere, zSBL was computed by examining the Thorpe scale of overturns82,83, LT. The buoyancy flux, used to quantify irreversible mixing, was calculated as b = KTN2, where KT = 0.5χ(∂T/∂z)−2 is the turbulent heat diffusivity evaluated with the Osborn and Cox51 model. Note that, strictly speaking, a minus sign should be added to the b definition, as the turbulent buoyancy flux is downgradient, and hence downward for stable stratification. For convenience, we take both b and ε as positive.

### Analysis: BBL dissipation and mixing

In the BBL, a vertical profile of the TKE dissipation rate with 2 cm vertical resolution was computed for each Aquadopp burst following the structure functions method84 with the relevant corrections for the bottom boundary layer85. Depth-integrated dissipation over the bottom Ekman layer (height: hE = κu*f−1, where κ = 0.41 is the Von Kármán constant, u* is the friction velocity and f is the inertial frequency), $${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{BBL}}}}}}}}}$$, was derived from the estimate at 1 mab (ε1 mab, computed as the average within 20 cm of this nominal height) assuming a logarithmic layer behaviour. Following the law-of-the-wall ($$\varepsilon (h)={u}_{* }^{3}/\kappa h$$, where h is the height above the bed), the friction velocity was computed as $${u}_{* }={(h\kappa {\varepsilon }_{{{{{{{{\rm{1mab}}}}}}}}})}^{1/3}$$ with h = 1 mab, and depth-integrated dissipation was obtained as:

$${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{BBL}}}}}}}}}=\int\nolimits_{{{{{{{{\rm{\delta }}}}}}}}}^{{h}_{E}}\rho \frac{{u}_{* }^{3}}{\kappa h}\ {{{{{{{\rm{d}}}}}}}}h=\rho {\varepsilon }_{1{{{{{{{\rm{mab}}}}}}}}}{{{{{{\mathrm{log}}}}}}}\,\frac{{h}_{E}}{\delta }$$
(3)

where $$\delta =11\nu {u}_{* }^{-1}$$ is the thickness of the viscous sub-layer and ν is the water kinematic viscosity. Alternatively, estimates of $${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{BBL}}}}}}}}}$$ were derived from a friction velocity $${u}_{* }^{{{{{{{{\rm{ADCP}}}}}}}}}=\sqrt{{C}_{D,\ 9\ {{{{{{{\rm{mab}}}}}}}}}^{{{{{{{{\rm{ADCP}}}}}}}}}}{u}_{9\ {{{{{{{\rm{mab}}}}}}}}}^{{{{{{{{\rm{ADCP}}}}}}}}}$$ computed using the near-bed velocities at 100 m (9 mab) measured with the surface moored, downward looking ADCP. The drag coefficient ($${C}_{D,\ 9\ {{{{{{{\rm{mab}}}}}}}}}^{{{{{{{{\rm{ADCP}}}}}}}}}$$) was adjusted to match the dissipation rates at 1 mab derived from the structure functions. The best-fitting drag coefficient was $${C}_{D,\ 9\ {{{{{{{\rm{mab}}}}}}}}}^{{{{{{{{\rm{ADCP}}}}}}}}}=0.0032\pm 0.0013$$. In addition to turbulent dissipation, depth-integrated laminar dissipation within the viscous sublayer28,50 was computed as $${{{{{{{{\mathcal{E}}}}}}}}}_{{{{{{{{\rm{BBL}}}}}}}}}^{{{{{{{{\rm{lam}}}}}}}}}=11\rho {u}_{* }^{3}$$.

To estimate the contribution of BBL turbulence to mixing, buoyancy fluxes were obtained following the same procedure described for the profile data, but using an estimate of χ computed from the near-bed high-resolution temperature time-series recorded with the RBR thermistors mounted in the bottom mooring. Briefly, temperature frequency spectra were calculated for each thermistor during each Aquadopp burst. Then, the frequency spectra were transformed into wavenumber (k) spectra (ST(k)) using the mean flow velocity during the burst at the thermistor height following Taylor’s frozen flow hypothesis. By taking the theoretical spectral shape in the inertial sub-range ($${S}_{T}^{I}={C}_{T}\chi {\varepsilon }^{-1/3}{k}^{-5/3}$$, where CT is the Obukhov-Corrsin universal constant typically assumed as CT = 0.4)86, χ was estimated as:

$$\chi =\left\langle \frac{{S}_{T}(k)}{{C}_{T}{\varepsilon }^{-1/3}{k}^{-5/3}}\right\rangle$$
(4)

where the average was performed up to the wavenumber corresponding to a frequency of 0.1 Hz, where the limitation due to the sensors time-response became apparent. BBL stratification, N2, was derived from an average temperature gradient computed from the mean temperature profile over each burst using a linear regression. In order to ensure that Taylor’s frozen flow was met, we only retained the fits where the mean flow velocity was 5 times larger than the root-mean-square of the velocity fluctuations.

## Data availability

The data needed to reproduce the figures and tables in the paper are available at the Eawag Data Institutional Collection43 (https://doi.org/10.25678/0004YA). More data (i.e. longer time series, raw and processed data) and live visualisation are available here: https://www.datalakes-eawag.ch/. The scripts needed to reproduce the analyses are maintained in the following Github repository: https://github.com/bieitofernandez/LakeGeneva.

## References

1. 1.

Kraemer, B. M. et al. Morphometry and average temperature affect lake stratification responses to climate change. Geophys. Res. Lett. 42, 4981–4988 (2015).

2. 2.

Woolway, R. I. et al. Northern hemisphere atmospheric stilling accelerates lake thermal responses to a warming world. Geophys. Res. Lett. 46, 11983–11992 (2019).

3. 3.

O’Reilly, C. M., Alin, S. R., Piisnier, P. D., Cohen, A. S. & McKee, B. A. Climate change decreases aquatic ecosystem productivity of Lake Tanganyika, Africa. Nature 424, 766–768 (2003).

4. 4.

Salmaso, N. & Tolotti, M. Phytoplankton and anthropogenic changes in pelagic environments. Hydrobiologia 848, 251–284 (2021).

5. 5.

MacIntyre, S., Flynn, K. M., Jellison, R. & Romero, J. R. Boundary mixing and nutrient fluxes in Mono Lake, California. Limnol. Oceanogr. 44, 512–529 (1999).

6. 6.

Bouffard, D., Boegman, L., Ackerman, J. D., Valipour, R. & Rao, Y. R. Near-inertial wave driven dissolved oxygen transfer through the thermocline of a large lake. J. Great Lakes Res. 40, 300–307 (2014).

7. 7.

Czikowsky, M. J., MacIntyre, S., Tedford, E. W., Vidal, J. & Miller, S. D. Effects of wind and buoyancy on carbon dioxide distribution and air-water flux of a stratified temperate lake. J. Geophys. Res. Biogeosci. 123, 2305–2322 (2018).

8. 8.

Kirillin, G. & Shatwell, T. Generalized scaling of seasonal thermal stratification in lakes. Earth-Science Rev. 161, 179–190 (2016).

9. 9.

Piccolroaz, S., Toffolon, M. & Majone, B. The role of stratification on lakes’ thermal response: the case of Lake Superior. Water Resour. Res. 51, 7878–7894 (2015).

10. 10.

Loewen, M. R., Ackerman, J. D. & Hamblin, P. F. Environmental implications of stratification and turbulent mixing in a shallow lake basin. Can. J. Fish. Aquat. Sci. 64, 43–57 (2007).

11. 11.

Schwefel, R., Müller, B., Boisgontier, H. & Wüest, A. Global warming affects nutrient upwelling in deep lakes. Aquat. Sci. 81, 50 (2019).

12. 12.

Wüest, A. & Lorke, A. Small scale hydrodynamics in lakes. Annu. Rev. Fluid Mech. 35, 373–412 (2003).

13. 13.

Boegman, L., Imberger, J., Ivey, G. N. & Antenucci, J. P. High-frequency internal waves in large stratified lakes. Limnol. Oceanogr. 48, 895–919 (2003).

14. 14.

De La Fuente, A., Shimizu, K., Nio, Y. & Imberger, J. Nonlinear and weakly nonhydrostatic inviscid evolution of internal gravitational basin-scale waves in a large, deep lake: lake constance. J. Geophys. Res. Ocean. 115, 1–16 (2010).

15. 15.

Antenucci, J. P. & Imberger, J. Energetics of long internal gravity waves in large lakes. Limnol. Oceanogr. 46, 1760–1773 (2001).

16. 16.

Rueda, F. & Schladow, G. Mixing and stratification in lakes of varying horizontal length scales: Scaling arguments and energy partitioning. Limnol. Oceanogr. 54, 2003–2017 (2009).

17. 17.

Münnich, M., Wüest, A. & Imboden, D. M. Observations of the second vertical mode of the internal seiche in an alpine lake. Limnol. Oceanogr. 37, 1705–1719 (1992).

18. 18.

Csanady, G. T. Hydrodynamics of large lakes. Annu Rev Fluid Mech 7, 357–386 (1975).

19. 19.

Gloor, M., Wüest, A. & Imboden, D. M. Dynamics of mixed bottom boundary layers and its implications for diapycnal transport in a stratified, natural water basin. J. Geophys. Res. Ocean. 105, 8629–8646 (2000).

20. 20.

Shimizu, K. & Imberger, J. Energetics and damping of basin-scale internal waves in a strongly stratified lake. Limnol. Oceanogr. 53, 1574–1588 (2008).

21. 21.

Boegman, L., Ivey, G. N. & Imberger, J. The degeneration of internal waves in lakes with sloping topography. Limnol. Oceanogr. 50, 1620–1637 (2005).

22. 22.

Lorke, A., Umlauf, L. & Mohrholz, V. Stratification and mixing on sloping boundaries. Geophys. Res. Lett. 35, L14610 (2008).

23. 23.

Horn, D. A., Imberger, J. & Ivey, G. N. The degeneration of large-scale interfacial gravity waves in lakes. J. Fluid Mech. 434, 181–207 (2001).

24. 24.

Preusse, M., Peeters, F. & Lorke, A. Internal waves and the generation of turbulence in the thermocline of a large lake. Limnol. Oceanogr. 55, 2353–2365 (2010).

25. 25.

Bouffard, D., Boegman, L. & Rao, Y. R. Poincaré wave-induced mixing in a large lake. Limnol. Oceanogr. 57, 1201–1216 (2012).

26. 26.

Deemer, B. R., Henderson, S. M. & Harrison, J. A. Chemical mixing in the bottom boundary layer of a eutrophic reservoir: The effects of internal seiching on nitrogen dynamics. Limnol. Oceanogr. 60, 1642–1655 (2015).

27. 27.

Bouffard, D. & Boegman, L. A diapycnal diffusivity model for stratified environmental flows. Dyn. Atmos. Ocean. 61-62, 14–34 (2013).

28. 28.

Wüest, A., Piepke, G. & Van Senden, D. C. Turbulent kinetic energy balance as a tool for estimating vertical diffusivity in wind-forced stratified waters. Limnol. Oceanogr. 45, 1388–1400 (2000).

29. 29.

Ravens, T. M., Kocsis, O., Wüest, A. & Granin, N. Small-scale turbulence and vertical mixing in Lake Baikal. Limnol. Oceanogr. 45, 159–173 (2000).

30. 30.

Woolway, R. I. & Simpson, J. H. Energy input and dissipation in a temperate lake during the spring transition. Ocean Dyn. 67, 959–971 (2017).

31. 31.

Simpson, J. H. et al. The annual cycle of energy input, modal excitation and physical plus biogenic turbulent dissipation in a temperate lake. Water Resour. Res. 57, 1–20 (2021).

32. 32.

Simpson, J. H., Wiles, P. J. & Lincoln, B. J. Internal seiche modes and bottom boundary-layer dissipation in a temperate lake from acoustic measurements. Limnol. Oceanogr. 56, 1893–1906 (2011).

33. 33.

Choi, J., Troy, C. D., Hsieh, T.-C., Hawley, N. & McCormick, M. J. A year of internal Poincaré waves in southern Lake Michigan. J. Geophys. Res. Ocean. 117, C07014 (2012).

34. 34.

Cannon, D. J. & Troy, C. D. Observations of turbulence and mean flow in the low-energy hypolimnetic boundary layer of a large lake. Limnol. Oceanogr. 63, 2762–2776 (2018).

35. 35.

Simoncelli, S. et al. Sources and scales of near-bottom turbulent mixing in large meromictic Lake Iseo. J. Great Lakes Res. 46, 1581–1594 (2020).

36. 36.

Imberger, J. & Patterson, J. C.A dynamic reservoir simulation model - DYRESM: 5. (Academic Press, 1981).

37. 37.

Hodges, B. R., Imberger, J., Laval, B. & Appt, J. Modeling the Hydrodynamics of Stratified Lakes. Hydroinformatics 2000 Conf.23-27 (2000).

38. 38.

Goudsmit, G.-H., Burchard, H., Peeters, F. & Wüest, A. Application of k-ε turbulence models to enclosed basins: The role of internal seiches. J. Geophys. Res. Ocean. 107, 3230 (2002).

39. 39.

Perroud, M. & Goyette, S. Impact of warmer climate on Lake Geneva water-temperature profiles. Boreal Environ. Res. 15, 255–278 (2010).

40. 40.

Butcher, J. B., Nover, D., Johnson, T. E. & Clark, C. M. Sensitivity of lake thermal and mixing dynamics to climate change. Clim. Change 129, 295–305 (2015).

41. 41.

Vanderkelen, I. et al. Global heat uptake by inland waters. Geophys. Res. Lett. 47, e2020GL087867 (2020).

42. 42.

Wüest, A. et al. LéXPLORE : A floating laboratory on Lake Geneva offering unique lake research opportunities. WIREs Water 8 (2021).

43. 43.

Fernández Castro, B. et al. Data for: Seasonality modulates wind-driven mixing pathways in a large lake [Dataset]. Eawag: Swiss Federal Institute of Aquatic Science. (2021) https://doi.org/10.25678/0004YA.

44. 44.

Schwefel, R., Gaudard, A., Wüest, A. & Bouffard, D. Effects of climate change on deepwater oxygen and winter mixing in a deep lake (Lake Geneva): Comparing observational findings and modeling. Water Resour. Res. 52, 8811–8826 (2016).

45. 45.

Bohle-Carbonell, M. Wind and currents: response patterns of Lake Genera. Ann. Geophys. 9, 82–90 (1991).

46. 46.

Lemmin, U., Mortimer, C. H. & Bäuerle, E. Internal seiche dynamics in Lake Geneva. Limnol. Oceanogr. 50, 207–216 (2005).

47. 47.

Bouffard, D., Ackerman, J. D. & Boegman, L. Factors affecting the development and dynamics of hypoxia in a large shallow stratified lake: Hourly to seasonal patterns. Water Resour. Res. 49, 2380–2394 (2013).

48. 48.

Lemmin, U. & D’Adamo, N. Summertime winds and direct cyclonic circulation: Observations from Lake Geneva. Ann. Geophys. 14, 1207–1220 (1997).

49. 49.

York, D. Least-squares fitting of a straight line. Can. J. Phys. 44, 1079–1086 (1966).

50. 50.

Imboden, D. M. & Wüest, A. Mixing mechanisms in lakes. (eds Lerman, A., Imboden, D. & Gat, J.) Phys. Chem. Lakes, 83-138 (Springer, 1995).

51. 51.

Osborn, T. R. & Cox, C. S. Oceanic fine structure. Geophys. Fluid Dyn. 3, 321–345 (1972).

52. 52.

Osborn, T. R. Estimates of the local rate of vertical diffusion from dissipation measurements. J. Phys. Oceanogr. 10, 83–89 (1980).

53. 53.

Oakey, N. S. Determination of the rate of dissipation of turbulent energy from simultaneous temperature and velocity shear microstructure measurements. J. Phys. Ocean. 12, 256–271 (1982).

54. 54.

Bluteau, C. E., Jones, N. L. & Ivey, G. N. Turbulent mixing efficiency at an energetic ocean site. J. Geophys. Res. Ocean. 118, 4662–4672 (2013).

55. 55.

De Lavergne, C., Madec, G., Le Sommer, J., Nurser, A. J. & Naveira Garabato, A. C. The impact of a variable mixing efficiency on the abyssal overturning. J. Phys. Oceanogr. 46, 663–681 (2016).

56. 56.

Fer, I., Lemmin, U. & Thorpe, S. A. Observations of mixing near the sides of a deep lake in winter. Limnol. Ocean. 47, 535–544 (2002).

57. 57.

Garrett, C. The role of secondary circulation in boundary mixing. J. Geophys. Res. 95, 3181–3188 (1990).

58. 58.

Naveira Garabato, A. C. et al. Rapid mixing and exchange of deep-ocean waters in an abyssal boundary current. Proc. Natl. Acad. Sci. U. S. A. 116, 13233–13238 (2019).

59. 59.

Smyth, W. D. Marginal instability and the efficiency of ocean mixing. J. Phys. Oceanogr. 50, 2141–2150 (2020).

60. 60.

Goudsmit, G.-H., Peeters, F., Gloor, M. & Wüest, A. Boundary versus internal diapycnal mixing in stratified natural waters. J. Geophys. Res. Ocean. 102, 27903–27914 (1997).

61. 61.

Simpson, J. H., Lucas, N. S., Powell, B. & Maberly, S. C. Dissipation and mixing during the onset of stratification in a temperate lake, Windermere. Limnol. Oceanogr. 60, 29–41 (2015).

62. 62.

Austin, J. Observations of near-inertial energy in lake Superior. Limnol. Oceanogr. 58, 715–728 (2013).

63. 63.

Livingstone, D. M. Impact of secular climate change on the thermal structure of a large temperate central European lake. Clim. Change 57, 205–225 (2003).

64. 64.

Yankova, Y., Villiger, J., Pernthaler, J., Schanz, F. & Posch, T. Prolongation, deepening and warming of the metalimnion change habitat conditions of the harmful filamentous cyanobacterium Planktothrix rubescens in a prealpine lake. Hydrobiologia 776, 125–138 (2016).

65. 65.

Råman Vinnå, L., Medhaug, I., Schmid, M. & Bouffard, D. The vulnerability of lakes to climate change along an altitudinal gradient. Commun. Earth Environ. 2, 35 (2021).

66. 66.

Lorke, A., Müller, B., Maerki, M. & Wüest, A. Breathing sediments: The control of diffusive transport across the sediment-water interface by periodic boundary-layer turbulence. Limnol. Oceanogr. 48, 2077–2085 (2003).

67. 67.

Hofmann, H., Federwisch, L. & Peeters, F. Wave-induced release of methane: littoral zones as a source of methane in lakes. Limnol. Oceanogr. 55, 1990–2000 (2010).

68. 68.

Matisoff, G., Watson, S. B., Guo, J., Duewiger, A. & Steely, R. Sediment and nutrient distribution and resuspension in Lake Winnipeg. Sci. Total Environ. 575, 173–186 (2017).

69. 69.

Bryant, L. D., Little, J. C. & Bürgmann, H. Response of sediment microbial community structure in a freshwater reservoir to manipulations in oxygen availability. FEMS Microbiol. Ecol. 80, 248–263 (2012).

70. 70.

Ladwig, R. et al. Lake thermal structure drives interannual variability in summer anoxia dynamics in a eutrophic lake over 37 years. Hydrol. Earth Syst. Sci. 25, 1009–1032 (2021).

71. 71.

Shatwell, T., Thiery, W. & Kirillin, G. Future projections of temperature and mixing regime of European temperate lakes. Hydrol. Earth Syst. Sci. 23, 1533–1551 (2019).

72. 72.

Anderson, E. J. et al. Seasonal overturn and stratification changes drive deep-water warming in one of Earth’s largest lakes. Nat. Commun. 12, 1688 (2021).

73. 73.

Fernández Castro, B. et al. Inhibited vertical mixing and seasonal persistence of a thin cyanobacterial layer in a stratified lake. Aquat. Sci. 83, 38 (2021).

74. 74.

Zeng, X., Zhao, M. & Dickinson, R. E. Intercomparison of bulk aerodynamic algorithms for the computation of sea surface fluxes using TOGA COARE and TAO data. J. Clim. 11, 2628–2644 (1998).

75. 75.

Woolway, R. I. et al. Automated calculation of surface energy fluxes with high-frequency lake buoy data. Environ. Model. Softw. 70, 191–198 (2015).

76. 76.

Fink, G., Schmid, M., Wahl, B., Wolf, T. & Wüest, A. Heat flux modifications related to climate-induced warming of large European lakes. Water Resour. Res. 50, 2072–2085 (2014).

77. 77.

Rimet, F. et al. The Observatory on LAkes (OLA) database: Sixty years of environmental data accessible to the public. J. Limnol. 78, 164–178 (2020).

78. 78.

MacKinnon, J. A. & Gregg, M. C. Shear and baroclinic energy flux on the summer new England shelf. J. Phys. Oceanogr. 33, 1462–1475 (2003).

79. 79.

Kundu, P. K. & Cohen, I. M. Fluid Mechanics. 2nd edn. (Academic Press, San Diego, 2002).

80. 80.

Ruddick, B., Anis, A. & Thompson, K. Maximum likelihood spectral fitting: The Batchelor spectrum. J. Atmos. Ocean. Technol. 17, 1541–1555 (2000).

81. 81.

Piccolroaz, S., Fernández-Castro, B., Toffolon, M. & Dijkstra, H. A. A year-round turbulence microstructure atlas for the deep perialpine. Lake Garda. Sci. Data. 8, 188 (2021).

82. 82.

Thorpe, S. A. Turbulence and mixing in a Scottish Loch. Phil. Trans. R. Soc. Lond. A 286, 125–181 (1977).

83. 83.

Brainerd, K. E. & Gregg, M. C. Surface mixed and mixing layer depths. Deep. Res. Part I 42, 1521–1543 (1995).

84. 84.

Wiles, P. J., Rippeth, T. P., Simpson, J. H. & Hendricks, P. J. A novel technique for measuring the rate of turbulent dissipation in the marine environment. Geophys. Res. Lett. 33, L21608 (2006).

85. 85.

Jabbari, A., Rouhi, A. & Boegman, L. Evaluation of the structure function method to compute turbulent dissipation within boundary layers using numerical simulations. J. Geophys. Res. Ocean. 121, 5888–5897 (2016).

86. 86.

Bluteau, C. E. et al. Determining mixing rates from concurrent temperature and velocity measurements. J. Atmos. Ocean. Technol. 34, 2283–2293 (2017).

## Acknowledgements

Funding for this work was provided by the Swiss National Science Foundation Sinergia grant CRSII2_160726 (A Flexible Underwater Distributed Robotic System for High-Resolution Sensing of Aquatic Ecosystems) and grant 200021_179123 (Primary Production Under Oligotrophication in Lakes). BFC was also supported by the European Union’s Horizon 2020 research and innovation program under the Marie Skłodowska-Curie grant agreement No. 834330 (SO-CUP). CT visiting EFPL was supported by the ENAC Visiting Professor Program. We acknowledge Natacha Pasche and the entire team from the LéXPLORE platform for their administrative and technical support and for the LéXPLORE core dataset. We also acknowledge the five LéXPLORE partner institutions: Eawag, EPFL, University of Geneva, University of Lausanne, and CARRTEL (INRAE-USMB). We are thankful to Tomy Doda, Camille Minaudo, Guillaume Cunillera, Shubham Krishna, Isabel Kiefer, and James Runnalls for their participation in fieldwork. We are grateful to Claudia Ofelio for her artwork on the schematics (Fig. 2) and to A. C. Naveira Garabato and Tom Lorimer for their scientific advice. We acknowledge OLA-IS, AnaEE-France, INRAE of Thonon-les-Bains, CIPEL, for data concerning Lake Geneva-SHL2, and Love Råman Vinnå for carrying the simulations of Lake Geneva dynamics under RCP climate change scenarios.

## Author information

Authors

### Contributions

B.F.C., D.B., C.T., S.L., and A.W. conceived the study and designed the fieldwork. B.F.C., D.B., C.T., H.N.U., S.P., O.S.S., H.E.C. L.S.M., S.B., and A.W. participated in the fieldwork. B.F.C. and S.P. analysed the data. B.F.C. wrote the paper with contributions from all the co-authors.

### Corresponding author

Correspondence to Bieito Fernández Castro.

## Ethics declarations

### Competing interests

The authors declare no competing interests.

Peer review informationCommunications Earth & Environment thanks Murray Mackay and the other, anonymous, reviewer(s) for their contribution to the peer review of this work. Primary Handling Editor: Joe Aslin.

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Fernández Castro, B., Bouffard, D., Troy, C. et al. Seasonality modulates wind-driven mixing pathways in a large lake. Commun Earth Environ 2, 215 (2021). https://doi.org/10.1038/s43247-021-00288-3

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