Hydrological transformations induced by climate warming are causing Arctic annual fluvial energy to shift from skewed (snowmelt-dominated) to multimodal (snowmelt- and rainfall-dominated) distributions. We integrated decade-long hydrometeorological and biogeochemical data from the High Arctic to show that shifts in the timing and magnitude of annual discharge patterns and stream power budgets are causing Arctic material transfer regimes to undergo fundamental changes. Increased late summer rainfall enhanced terrestrial-aquatic connectivity for dissolved and particulate material fluxes. Permafrost disturbances (<3% of the watersheds’ areal extent) reduced watershed-scale dissolved organic carbon export, offsetting concurrent increased export in undisturbed watersheds. To overcome the watersheds’ buffering capacity for transferring particulate material (30 ± 9 Watt), rainfall events had to increase by an order of magnitude, indicating the landscape is primed for accelerated geomorphological change when future rainfall magnitudes and consequent pluvial responses exceed the current buffering capacity of the terrestrial-aquatic continuum.
Despite recent advances in our understanding of terrestrial-aquatic connectivity in permafrost-underlain watersheds1,2,3, few studies directly link the controls and changes in High Arctic terrestrial-aquatic connectivity to climate warming-induced changes in hydrology1,3,4,5,6. As the Arctic warms and precipitation patterns change7,8, shifts in the timing and magnitude of fluvial energy (e.g., stream power) in response to rainfall inputs will alter landscape connectivity in watersheds by increasing the late-season delivery of organic (e.g., organic carbon; OC) and inorganic (e.g., sediment, major ions) terrestrial materials into downstream aquatic ecosystems9,10,11. The impacts of shifts in the timing and magnitude of fluvial energy coupled with terrestrial ecosystem changes are scarcely documented in these environments due to a lack of integrated longer-term (≥10 years) biogeochemical records12 and the remote nature of the High Arctic13. Accurate biogeochemical budgets across full hydrological seasons are critical reference points for earth system models and are required to predict the strength and timing of climate feedback mechanisms in the Arctic, including the permafrost carbon feedback1,2,3,5,14. Therefore, quantifying the impacts of the altered timing and magnitude of hydrological connectivity in these environments is necessary to parameterize earth system models that predict global change15.
The increasing importance of the under-studied and under-represented “shoulder seasons” (early-spring and late-fall) in annual Arctic biogeochemical budgets has been recently highlighted5, but is not quantified for most Arctic rivers. In particular, little is known about the role late-summer rainfall plays in coupling hillslopes with stream networks. Projected increases in the magnitude and frequency of summer rainfall events7,8 are expected to elevate terrestrial-aquatic fluxes of organic and inorganic material in Arctic watersheds5,9,11,16. This is because the majority of rainfall events occur when suspended sediment (SS), dissolved and particulate organic carbon (DOC and POC, respectively), nutrients, and major ions are readily available for transport due to active layer depths and terrestrial biological productivity being at their annual maximums17,18,19. However, few hydrological and biogeochemical records capture the full Arctic thaw season due to the logistical constraints imposed by working in remote locations12. The impact of changes in temperature and precipitation on permafrost systems is further complicated by the increasing frequency of thaw-induced geomorphological disturbance (e.g., thermokarst, active layer detachments, retrogressive thaw slumps, surface subsidence), which alter Arctic landscapes, local hydrology, biogeochemistry, and terrestrial-aquatic connectivity20,21,22,23. Permafrost disturbances that hydro-geomorphologically couple with fluvial systems amplify the effect of climate change through disproportionate increases in the mobilization and delivery of terrestrial material into stream networks24,25.
Here we use data from the hydrological and biogeochemical research program at the Cape Bounty Arctic Watershed Observatory (CBAWO; 2003–2019), located in the Canadian High Arctic (74°54′N, 109°35′W; Supplementary Fig. 1), to integrate changes in the timing and magnitude of fluvial energy with organic and inorganic matter quantities and transfer along the terrestrial-aquatic continuum. We used fluxes of terrestrially sourced materials (e.g., SS, POC, DOC, major ions; 2003–2017) combined with optical dissolved organic matter (DOM) indices that indicate DOM origin (2012–2017) to infer connectivity along the terrestrial-aquatic continuum. Further, we assessed the watershed-scale impacts of localized active layer detachments (ALDs; 2007–2008) on material flux in the decade following their initiation relative to concurrent Arctic greening and shifts in the timing and magnitude of fluvial energy. Through these integrated analyses, we demonstrate shifts in the timing of higher fluvial energy to later in the thaw season and reduced influence of the snowmelt phase on material transfer. Our findings highlight the increasing importance of rainfall in driving connectivity along the High Arctic terrestrial-aquatic continuum, providing a framework to improve earth system models and demonstrating why it is increasingly important for the research community to shift our focus to capturing the late-fall shoulder season5.
Results and discussion
Shifting magnitude and distribution of fluvial energy
The primary control on Arctic hydrology is seasonal phase changes in water form and movement, characterized by a short summer flow season between spring “break-up” (2–3 weeks following daily mean air temperatures consistently >0 °C) and fall “freeze-up” (daily mean air temperatures consistently <0 °C26; length of summer thaw season 81 ± 11 days at the CBAWO; mean ± 1 SD unless stated otherwise). Arctic streams and rivers have distinct nival hydrological regimes (Supplementary Fig. 2a), which are characterized by one major spring snowmelt flood period (freshet) and a rapid transition to low-flow (baseflow) during the summer as the watershed snowpack is exhausted (main CBAWO rivers: 22 ± 5 days; headwater-slope streams: 17 ± 5 days). Summer baseflow is often punctuated by rainfall-generated (pluvial) discharge, with the magnitude of peak pluvial discharge largely controlled by both the timing and magnitude of rainfall and antecedent soil moisture. At the CBAWO, rainfall events are generally of low intensity with minimal hydrological significance compared to freshet, resulting in a nival-dominated (skewed distribution) hydrological regime (Fig. 1; Supplementary Fig. 2b). In absence of late-summer rainfall, baseflow wanes through fall freeze-up with little-to-no surface runoff during winter27.
The unique seasonality of Arctic hydrology varies with latitude and is closely linked to regional weather, and in particular regional air temperature26. Mean regional summer (June-August; JJA) temperatures at our study site warmed ~ 2 °C between 1948 and 2019 (Mould Bay, NT; Fig. 2a). The timing and duration of the summer flow season at the CBAWO varied with summer air temperatures (p < 0.05). Locally, above average summer temperatures coincided with: (i) earlier first day of nival runoff and a longer summer flow season (Fig. 2c, d; p < 0.05); (ii) decreased watershed snow water equivalent10; (iii) a general reduction in maximum nival stream power from 68.0 ± 14.6 W to 42.2 ± 19.0 W; and (iv) reduced influence of the snowmelt phase on material transfer (e.g., decreased sediment flux per unit of nival runoff)10.
The timing and magnitude of peak nival runoff at the CBAWO is strongly controlled by snow accumulation in river channels (≥4 m locally). In years rainfall had minimal hydrological significance in summer/fall (n = 8; Table 1; Fig. 1; Supplementary Fig. 2b), the majority of the annual available stream power was expended by the formation of channelized runoff through the snowpack, largely in isolation from the stream bed (Supplementary Fig. 3a). This runoff channel formation expended 49 ± 15% of the annual available stream power within the first 10 days of flow (Fig. 1b). On average, the entire nival period (22 ± 5 days) expended 76 ± 13% of annual available stream power (Fig. 1b). In the warmest summer of our record (2012; 4.1 ± 3.8 °C), one-third of the annual available stream power was expended in the first 6 days of flow before surface runoff made full contact with the channel bed28; 86% of the annual available stream power was expended during the entire nival period (29 days) the same year.
In years with proportionately more summer/fall pluvial runoff (n = 4), the timing of seasonal stream power shifted from a nival-dominated (skewed) to a nival- and pluvial-dominated (multimodal) hydrological regime (Fig. 1; Supplementary Fig. 2c). The three largest recorded pluvial events during the 17-year record at CBAWO redistributed hydrological energy to later in the summer (July-August) at all watershed scales (0.2–10 km2) and resulted in high stream powers exceeding that of the nival peak in respective years: (i) a rain-on-snow event (late June 2007; 0.19 mm h−1; 54 h; ≤2 year recurrence interval or >50% chance of exceedance in any given year); (ii) consecutive low-intensity rainfall (July 2007; ≤0.09–0.33 mm h−1, <38 h, ≤2 year recurrence interval); and (iii) consecutive high-magnitude rainfall events (July 2009; 0.31–0.39 mm h−1, 30–75 h, 8–100 year recurrence interval or <12% chance of exceedance in any given year) (Fig. 1; Supplementary Figs. 4 and 5). These pluvial responses delivered 25 ± 12% of annual available stream power to the system during only 2–5 days of runoff per event (Fig. 1b). In comparison, the entire nival period (22 ± 5 days) delivered 68 ± 15% of annual available stream power in the same years (Fig. 1b; Supplementary Fig. 4).
It is important to note that, despite the CBAWO being the longest integrative data set from the Canadian High Arctic, we have hydrological observations for only 39% of recorded rain events (Supplementary Fig. 5). This highlights the need for longer sampling seasons and/or sampling methods designed to capture late-fall shoulder season rainfall events. Nevertheless, longer-term hydrological records from circum-Arctic streams and rivers (including a northern Canadian latitudinal gradient) suggest the shift from a nival-dominated to a nival- and pluvial-dominated discharge regime is ubiquitous across both large and small watersheds of the High and Low Arctic, although the effects were dampened across larger watersheds and watersheds in the Low Arctic received proportionately more rainfall in general (8.0 to 2.95 million km2 watersheds; Supplementary Figs. 6–8). In combination with our measurements from the CBAWO, these data show Arctic systems are already transitioning to a nival- and pluvial-dominated (multimodal) hydrological regime.
Timing and magnitude of fluvial energy controls terrestrial-aquatic connectivity
Shifts in the timing and magnitude of annual discharge patterns and stream power budgets are causing Arctic material transfer regimes to undergo fundamental changes. The term “watershed continuum” describes source-to-sink controls on material (e.g., sediment and nutrients) erosion, transfer, and deposition. The watershed continuum can be defined as a “cascading system” composed of a chain of subsystems dynamically linked by a cascade of mass and energy29 (e.g., surface runoff from headwater-slope streams becomes part of the input into the main channel system). Internal regulators (e.g., channel slope, morphology, length) and thresholds are critical for determining if materials and energy are dissipated, stored within a subsystem, or conveyed to the adjacent subsystem. Hydrology is a key driver of the watershed continuum. Terrestrial-aquatic connectivity at the CBAWO follows a temporary storage-remobilization regime along the watershed continuum. The channel slope and morphology (alternating step-pool, riffle-pool, and braided reaches) favor energy dissipation and sediment deposition, temporarily storing materials on channel bars and the channel bed28. This material is readily available for remobilization once the fluvial energy increases and overcomes the channel’s buffering capacity threshold.
Our data show warmer and wetter thaw seasons result in increased stream power during the summer and fall shoulder season and (Fig. 1b), in turn, elevated potential for lateral (terrestrial to stream channel) and longitudinal (upstream to downstream) material fluxes along the watershed continuum due to increased terrestrial-aquatic hydrological connectivity. The nival period, when the majority of stream power (76 ± 13% at our study site) is traditionally expended, is characterized by low terrestrial-aquatic hydrological connectivity due to shallow active layer thaw depths (0–5 cm) and variable snow cover (typically 0.1–1.5 m thick) limiting interaction between channelized runoff and terrestrial surfaces (Fig. 3 and Supplementary Fig. 3a). Therefore, the majority of material export during the nival period is sourced from surface runoff processes (e.g., terrestrial surface materials, temporary channel stores)28. Conversely, pluvial runoff couples the terrestrial-aquatic continuum at a time when: (i) the seasonal active layer is deepening (mean JJA active layer depth 0.8 ± 0.3 m), increasing subsurface drainage connectivity6,30; and (ii) vegetation productivity is at its peak, increasing above-ground biomass and available organic material from modern terrestrial vegetation31 (Fig. 3; Supplementary Fig. 3c). Given that the potential for export of terrigenous material is higher during late summer/fall, increased proportions of annual available stream power expended during pluvial events disproportionately increases the erosion and delivery of terrestrial material into the downstream aquatic ecosystem9,10.
Optical DOM indices measured at the CBAWO support increased levels of terrigenous DOM export during pluvial responses compared to the nival and baseflow periods (2012–2017; Fig. 4; Supplementary Figs. 9 and 10). In headwater catchments, mean α350 values were highest during pluvial events (Fig. 4d; Supplementary Fig. 9a); α350 values are correlated with lignin phenols (unique biomarkers of vascular plants) and serve as an indicator for terrigenous DOM32,33. Concurrent higher growing degree day (GDD; Fig. 3) and DOM freshness index (β:α) values during pluvial responses further support that this DOM was recently-produced in the surrounding terrestrial environment (Fig. 4e; Supplementary Fig. 9c). The lack of vegetative productivity during the nival period, coupled with lower potential for terrestrial interaction and lower DOM β:α values, indicate increased α350 values during nival periods compared to baseflow are likely the result of mobilization of terrigenous material from prior growing seasons.
Our results also indicate that the maximum pluvial stream power generated by varying rainfall magnitudes dictates whether terrestrial-aquatic pathways export proportionately more dissolved or particulate material. Low-intensity, short duration rainfall events with resultant stream powers <30 ± 9 W primarily transfer dissolved material (62 ± 25% of the total pluvial flux in only 15 ± 4% of the active flow season; 4–13 days). These data suggest that low- to intermediate hydrological events effectively couple the watershed-scale terrestrial-aquatic continuum for dissolved material and drive the majority of dissolved material export in these streams34. In contrast, higher magnitude rainfall events with resultant stream power >30 ± 9 W transfer primarily particulate material (79 ± 19% of the total pluvial flux in 20 ± 2% of the active flow season). Spectral slope ratios (SR) of chromophoric DOM indicated that pluvial runoff from rainfall events with higher intensities, longer durations, and/or less frequent recurrence intervals led to higher average molecular weight DOM in the stream networks35 (Supplementary Fig. 11). These patterns suggest that higher pluvial stream powers, exceeding a threshold of 30 ± 9 W, are necessary to: (i) initiate channel bank erosion in the upper watershed and (ii) connect terrestrial-aquatic pathways along the full watershed continuum for particulate terrigenous materials. It is important to note that the scale of pluvial responses was strongly controlled by antecedent conditions. For example, consecutive low-intensity, longer-duration rainfall events (<0.2 mm h-1, 24–75 h, <2-year recurrence) can produce higher stream powers >30 W.
Baseflow periods had the lowest stream powers (0.05 ± 0.02 W in headwaters and 3.0 ± 2.2 W in main streams), with limited hydrological connectivity and terrestrial to aquatic material flux9,10 (Supplementary Fig. 3b). Surface flow in headwater-slope streams often rapidly ceased following snow exhaustion by late June or early July, transitioning to a subsurface flow regime hydrologically coupling the subsurface of terrestrial slopes with the stream network. Our DOM data show baseflow periods, despite having the least terrestrial-aquatic connectivity, had the most in-stream biological activity. In the main streams, biological/autochthonous index (BIX) values were higher during the lower-energy baseflow periods, suggesting greater proportions of recently-produced autochthonous DOM36. While BIX values indicated DOM was primarily of allochthonous origin throughout our study (range 0.50–0.78), significantly higher BIX values during baseflow periods (Supplementary Fig. 9b) indicate proportionally less allochthonous DOM input from the surrounding landscape due to limited (sub)surface input and/or more autochthonous internal DOM cycling. Dissolved nutrient input from thawing active layer soils during the late season, which is supported by increased major ion concentrations (Supplementary Fig. 10d), may further stimulate increased primary productivity within the stream network37 at a time when water temperatures are at their annual maximums (up to 18.2 °C locally). The enhanced BIX values in the main streams were less evident when stream powers exceeded ~25 W, suggesting a threshold where autochthonous DOM production is reduced and/or the autochthonous DOM signal is masked by increased allochthonous DOM input. As the hydrological season continues to lengthen and both air and river temperatures increase, in-stream productivity and increased DOM processing during baseflow periods will also likely increase, further impacting C processing potentials in this landscape38.
Combined, our results show lower magnitude rainfall events are important mechanisms for supplying Arctic rivers with dissolved and particulate terrestrial material9,34. However, the low magnitude rainfall events are unable to overcome energy thresholds needed to transport particulate material downstream to watershed outlets. This results in the temporary storage of particulate material within steam channels, where it can be processed and become available for microbial use during low energy hydrological periods. When higher magnitude pluvial events overcame our measured energy thresholds (stream powers >30 W), particulate material from eroded channel banks and disturbed hillslopes was directly coupled downstream with the watershed outlet10,28. At this site, rainfall magnitudes great enough to produce runoff energy to overcome stream power thresholds only occur on an 8 to 100-year recurrence interval (<12% chance of exceedance in any given year). The projected increase in the magnitude and frequency of summer rainfall events in the Arctic7,8 suggests these stream power thresholds will be met with greater frequency, resulting in future increased lateral particulate export.
Relative influence of permafrost related geomorphological disturbance
In addition to shifts in the timing and magnitude of fluvial energy, climate warming is causing thaw-induced geomorphological disturbance across the Arctic20,39. Thaw-induced geomorphological disturbances are anticipated to occur in over 20% of the permafrost zone, thawing an additional 80 ± 19 Pg C by 2300 compared to gradual thaw processes alone (e.g., active layer deepening) and greatly enhancing the permafrost carbon feedback20. These disturbances increase the delivery of terrestrial materials to aquatic systems24,25, but the longer-term persistence (>2–5 years) of these impacts remain relatively unknown. The paired watersheds in this study were impacted by localized ALDs in 2007–2008, disturbing 1.2–2.7% of the watersheds’ areal extent (Supplementary Fig. 1). The ALDs (100+) varied from small hydrologically (dis)connected patches on headwater-slopes and along channel banks to long (>100 m) linear features that directly coupled with main watershed streams; prior to 2007 there was no evidence of recent terrestrial disturbance at the CBAWO. Given that warming July-August temperatures are anticipated to increase the initiation of permafrost disturbance in the High Arctic22, our data provide a unique opportunity to compare the relative influence of changing hydrology versus permafrost thaw-induced geomorphological disturbance on the terrestrial-aquatic continuum in the decade following ALD formation (2007–2017).
We show that despite disturbances covering a relatively small areal extent (<2.7%) of the watershed, processes that reduce DOC availability and transport following permafrost disturbances were strong enough to offset concurrent watershed-scale processes that increased DOC export from vegetated geomorphologically undisturbed headwater-slope streams. DOC concentrations from these undisturbed slopes increased during our study period (Supplementary Fig. 12a; GS). This increase was likely due to combinations of greening (+0.19 to +1.3% yr−1 NDVI between 1985–201540) as a result of longer growing seasons leading to increased vegetation biomass41 and warmer summer temperatures causing higher concentrations of DOM to be released to aquatic ecosystems42 (Supplementary Figs. 9 and 10). Future changes in Arctic vegetation biomass and productivity with continued climate warming are spatially variable and complex to predict43,44,45 and hydrological changes such as changes to the timing of snowmelt may delay vegetation growth in some Arctic systems46,47. In contrast to the increased DOC concentrations observed in the undisturbed headwater-slope stream, geomorphological disturbance from ALDs resulted in a decline in interannual DOC concentrations at all watershed scales (Supplementary Fig. 12). This was likely due to a combination of: (i) the geomorphological evolution and stabilization of internal channels within ALDs9, (ii) enhanced DOC processing within the stream network48; and (iii) preferential sorption of available DOC to newly exposed mineral soils49,50.
At all watershed scales the ALDs led to a shift in the primary form of C export from a DOC- to a POC-dominated flux, with the magnitude and persistence of impact increasing with the areal extent of watershed disturbance (Fig. 5). Our results show that hydrologically-coupled ALDs need to physically disturb as little as 1.2–2.7% of the watershed area (≤12 km2) to trigger this change in fluvial C export from DOC- to POC-dominated in High Arctic systems. Despite this shift in the form of C export, localized ALDs did not increase the downstream, multiyear watershed-scale flux of particulate material due to fluvial energy limitations causing temporary channel storage10. This temporarily stored POC may be made accessible for additional processing during summer baseflow as discussed in the above section.
The lack of multiyear increase in the watershed-scale particulate flux post ALDs was primarily due to insufficient fluvial energy to overcome the thresholds for terrestrial-aquatic connectivity at a time when the additional POC sources are thawed and readily available for mobilization (summer and fall). In this setting, nival runoff is ineffective at mobilizing additional POC exposed by localized ALDs due to limited access to terrestrial material at times of high fluvial energy. To fully couple the POC continuum from disturbed sources to downstream at the catchment outlet, summer rainfall events had to result in stream powers >30 W in the main streams. Pluvial responses with less energy rapidly mobilize and exhaust temporary in-channel particulate stores28, but are an important mechanism resupplying channel stores with newly mobilized/eroded terrestrial material9. This suggests that, at the watershed-scale, the effect of thaw-induced geomorphological disturbance on particulate material export is smaller than the shift toward a multimodal hydrological regime in this environment. Furthermore, disturbed sites are more vulnerable to rain-induced surface thaw51, which could further accelerate the additional release of terrestrial materials following future rainfall. Hence, we conclude terrestrial disturbance primes Arctic watersheds for accelerated geomorphological change when future rainfall magnitudes and consequent pluvial responses exceed the current buffering capacity of the terrestrial-aquatic continuum (30 ± 9 W).
In watersheds with a terrestrial disturbance area <1.2%, only high magnitude rainfall events were able to effectively couple particulate flux from headwater channel banks and slopes to the watershed outlet10 (8–100-year recurrence interval; July 2009; Fig. 5b). It is likely these thresholds differ with increasing watershed area, location of the disturbance within watersheds, hydro-geomorphological connectivity, differing types of geomorphological permafrost disturbance (e.g., retrogressive thaw slumps, thermokarst, thermo-erosion), variability in permafrost conditions (sporadic, discontinuous, continuous), watershed characteristics (e.g., OM content, channel type, vegetation distribution), and continued changes in climate and hydrology. However, as the magnitude and frequency of permafrost thaw-induced geomorphological disturbance intensifies due to climate change, our results suggest hydrologically-coupled disturbances will become an increasingly important mechanism for delivering POC from terrestrial environments into stream networks52.
Overall, our results show localized ALDs at our site played a stronger role in altering watershed C export along the terrestrial-aquatic continuum than Arctic greening, but a weaker role than increased magnitude and frequency of pluvial events in this energy-limited High Arctic system. In higher-energy Arctic systems, or in instances where permafrost thaw and disturbance are geomorphologically more active (e.g., RTS) or lead to the formation of a talik (former permafrost remaining thawed year-round), geomorphological disturbance itself may play a stronger role in altering C export potentials20,25,53,54. However, fluvial energy limitations in the High Arctic indicate channel bank disturbance and hydro-geomorphologically coupled ALDs on terrestrial hillslopes will only result in increased watershed C export if they are coupled with sufficient stream power from pluvial runoff during the summer and fall shoulder season.
Implications for upscaling to larger watersheds and the circum-Arctic
Given that watershed attributes in low-order headwater catchments like those at the CBAWO dictate stream chemistry within larger river systems, it is critical to examine changes at the headwater-scale to better integrate and predict changes at larger watershed and pan-Arctic scales5,55,56. Our field observations show that the timing and magnitude of available fluvial energy is the key mechanism determining the role stream networks play in transporting and cycling terrigenous C and OM in High Arctic watersheds underlain by continuous permafrost. Our identified energy threshold (30 ± 9 W in the CBAWO main streams), which was necessary to fully connect the terrestrial-aquatic continuum at the watershed-scale, may explain disparities in the literature concerning the role inland waters play in cycling terrestrial C. Arctic aquatic systems where energy thresholds exceed the watersheds’ buffering capacity, including the continuum of headwaters to larger river networks, are heavily influenced by allochthonous input and terrestrial connectivity1. Lower-energy systems such as small lowland ponds, which represent ~25% of northern surface water area, lack the energy needed to hydrologically connect the terrestrial-aquatic continuum, and therefore primarily internally cycle autochthonous C and play a minor to negligible role in the mineralization of terrestrial C57.
In this study, we found evidence of shifts in timing of fluvial energy from a skewed to a multimodal distribution in both large and small circum-arctic watersheds, which aligns with global climate model projections of amplified Arctic warming, decreased winter precipitation, and increased magnitude and frequency of summer rainfall7,8. Given that the seasonality of Arctic hydrology is closely linked to regional weather, we can expect the timing and magnitude of this fluvial energy shift to vary among sites. While the spring freshet has been previously recognized as a strong driver of terrestrial-aquatic material export in Arctic inland waters58,59, we identify the increasing role of rainfall events to enhance terrestrial-aquatic connectivity during periods with the highest annual terrestrial vegetation biomass and deepest active layer depths (Fig. 3). Rain events have also been recently shown to stimulate increased permafrost thaw in Low Arctic systems51,60, further altering hydrological pathways and terrestrial-aquatic connectivity along the continuum. We further show clear evidence that rainfall events are under-sampled and under-represented in Arctic systems. One option for better capturing rain events is to develop site-specific annual rating curves from integrative parameters measured with in situ optical sensors (e.g., turbidity, major ions, DOM), enabling our understanding of these rainfall events and the late season baseflow we miss each year5.
Localized ALDs offset the increased DOC export from undisturbed vegetated hillslopes during our study despite covering <2.7% of the watershed areal extent. This indicates changes in C export following permafrost thaw-induced geomorphological disturbance, which occurs in a relatively small area of the watershed, outpaces and offsets changes in C export due to watershed-wide processes such as greening. We identified a threshold where hydrologically-coupled ALDs need to geomorphologically disturb as little as 1.2–2.7% of the watershed area (≤12 km2) to trigger a fundamental shift in C export regimes from DOC- to POC-dominated. We conclude that ALDs have primed the watershed for accelerated geomorphological change when future rainfall magnitudes and consequent pluvial responses exceed the current buffering capacity of the terrestrial-aquatic continuum in this energy-limited system. It is important to note impacts from ALDs and other localized geomorphologic disturbances might be asynchronous and not additive as the watershed contributing area increases, further highlighting the importance of examining low-order headwater catchments to accurately upscale to larger watershed and pan-Arctic scales.
This research was conducted at the Cape Bounty Arctic Watershed Observatory (CBAWO; 2003–2019), located on the south-central coast of Melville Island in the Canadian High Arctic (74°54’N, 109°35’W, Supplementary Fig. 1). This setting is underlain by continuous permafrost (~500 m) and characterized by a polar desert climate (mean annual atmospheric temperature ± 1σ: −14.8 ± 1.3 °C) with limited annual precipitation and runoff (<150 mm yr−1). Mean summer (Jun-Aug; JJA) air temperature was 2.7 ± 2.5 °C (2003–2019). Temperature and rainfall data were obtained from local (2003–2019) and regional (1948–2019) meteorological stations proximal to the CBAWO (Supplementary Fig. 1a). Local rainfall data were used to construct a 72-h intensity-duration-frequency curve for the CBAWO (Gumbel EV1 distribution) to estimate the recurrence interval for each rainfall event (Supplementary Fig. 5).
The CBAWO is comprised of paired watersheds for the West and East (unofficial names; WR and ER, respectively). The West watershed is 8.0 km2 and has instrumented headwater slope streams (PT: Ptarmigan and GS: Goose; both ~0.2 km2 watershed area), and the East watershed is 11.6 km2 (Supplementary Table 1). Both watersheds are non-glacial and have second-order low-sinuosity channels with short reaches of braided, riffle- and step-pool morphology along their lengths. Both rivers have a seasonal, snow-limited flow regime where channel runoff typically begins in early to mid-June and ends in late-August to early-September during freeze-up. Late season rainfall events punctuate baseflow runoff, with pluvial responses largely controlled by the timing and magnitude of rainfall and antecedent soil moisture conditions. Surface runoff in the upper ER watershed occurs as diffuse flow over vegetated water tracks, hydrologically connecting ponds along the terrestrial-aquatic continuum. Water tracks in the WR watershed are limited to headwater-slope inputs, with the majority of runoff in channelized gravel bed streams.
Instrumentation, datalogger, and analytical method specifications are documented in the Supplementary Methods and Supplementary Table 2. For coherence among records and to provide the finest temporal resolution across all years, we reprocessed all variables from raw data into daily means. To normalize hydrological seasons irrespective of interannual variation in hydrometeorological conditions, we temporally normalized data to the first day of flow instead of calendar dates. All statistical analyses were conducted in Matlab versions R2016a and 2020a software. Correlations were calculated using Pearson’s r linear correlation coefficients (Supplementary Tables 3-6). Differences between variables: (i) between watersheds and (ii) between hydrological periods were determined using a combination of ANOVA analyses (Supplementary Table 7) and two-samples t tests (Supplementary Figs. 9–10). Differences in annual stream power distributions were tested using two-sample Kolmogorov–Smirnov tests (Supplementary Table 8). Results from all statistical analyses were considered significant at the α = 0.05 level when p < 0.05.
Daily JJA active layer depths (Fig. 3) were estimated using ground temperature data collected between 2012–2019 from a 7-m borehole (Supplementary Fig. 1a). Daily active layer depth estimates were calculated using a linear regression of temperatures recorded at 0.3 m and 1.3 m depth, with the depth at which the temperature was 0 °C being the assumed thaw boundary. This method assumed linear decreases in ground temperature within the 1.3 m depth range. Actual active layer depths may vary with local soil moisture and ice content conditions; however, values estimated using linear regression (0.0–1.20 m during JJA) were consistent with mean seasonal maximum active layer depths manually measured using a probe (0.7–1.1 m spatially across both watersheds). Growing degree days (GDD) were calculated as:
where Tmax and Tmin are the daily maximum and minimum temperatures, respectively, and Tbase is the base temperature representative of the threshold temperature above which plants are productive (≥ 5 °C).
Stream power represents the rate of energy expenditure along a riverbed and banks:
where stream power (Ω; Watts or kg m−2 s−3) is the product of water density calculated from measured water temperatures (ρ; kg m−3), acceleration due to gravity (g; 9.8 m s−2), discharge (Q; m3 s−1), and channel slope (s). We applied a 5 m buffer on either side of the middle of the channel in ArcGIS® to represent the channel area, from which the watershed’s average slope was calculated (Supplementary Table 1).
Discharge, stream power, DOM optical data, SS, DOC, POC, major ions, and DIN are available in the Supplementary Information. Climate, SS, and Q data for the main watersheds are available as Supplementary Information in Beel et al. (2018). Q, SS, POC, DOC, and major ions from headwater-slope streams are available as Supplementary Information in Beel et al. (2020). This data is also available through the Polar Data Catalog (www.polardata.ca).
Tank, S. E. et al. Landscape matters: predicting the biogeochemical effects of permafrost thaw on aquatic networks with a state factor approach. Perma. Periglac. Process. 31, 358–370 (2020).
Vonk, J. E., Tank, S. E. & Walvoord, M. A. Integrating hydrology and biogeochemistry across frozen landscapes. Nat. Comm. 10, 5377 (2019).
Tank, S. E., Fellman, J. B., Hood, E. & Kritzberg, E. S. Beyond respiration: controls on lateral carbon fluxes across the terrestrial-aquatic interface. Limnol. Oceanogr. Lett. 3, 76–88 (2018).
Juhls, B. et al. Identifying drivers of seasonality in Lena River biogeochemistry and dissolved organic matter fluxes. Front. Environ. Sci. 8, 53 (2020).
Shogren, A. J., Zarnestke, J. P., Abbott, B. W., Lannucci, F., Bowden, W. B. We cannot shrug off the shoulder seasons: addressing knowledge and data gaps in an Arctic Headwater. Environ. Res. Lett., in press, https://doi.org/10.1088/1748-9326/ab9d3c (2020).
Frey, K. E. & McClelland, J. W. Impacts of permafrost degradation on arctic river biogeochemistry. Hydrol. Process. 23, 169–182 (2009).
Bintanja, R. The impact of Arctic warming on increased rainfall. Sci. Rep. 8, 16001 (2018).
Bintanja, R. & Andry, O. Towards a rain-dominated Arctic. Nat. Clim. Change 7, 263–267 (2017).
Beel, C. R. et al. Differential impact of thermal and physical permafrost disturbance on High Arctic dissolved and particulate fluvial fluxes. Sci. Rep. 10, 11836 (2020).
Beel, C. R., Lamoureux, S. F., Orwin, J. F. Fluvial response to a period of hydrometeorological change and landscape disturbance in the Canadian High Arctic. Geophys. Res. Lett., 45 https://doi.org/10.1029/2018GL079660 (2018).
Coch, C. et al. Summer rainfall, dissolved organic carbon, solute, and sediment fluxes in a small Arctic coastal catchment on Herschel Island (Yukon Territory, Canada). Arct. Sci. 4, 750–780 (2018).
Laudon, H. et al. Save northern high-latitude catchments. Nat. Geosci. 10, 324–325 (2017).
Metcalfe, D. B. et al. Patchy field sampling biases understanding of climate change impacts across the Arctic. Nat. Ecol. Evol. 2, 1443–1448 (2018).
Schuur, E. A. G. et al. Climate change and the permafrost carbon feedback. Nature 520, 171–179 (2015).
Kicklighter, D. W. et al. Insights and issues with simulating terrestrial DOC loading of Arctic river networks. Ecol. Appl. 23, 1817–1836 (2013).
Heslop, J. K., et al. Diverging pond dissolved organic matter characteristics yield similar CO2 flux potentials in a disturbed High Arctic landscape. Environ. Res. Lett. https://doi.org/10.1088/1748-9326/abc913 (2020).
Hobbie, J. E. et al. Ecosystem responses to climate change at a Low Arctic and a High Arctic long-term research site. Ambio 46, S160–S173 (2017).
Guo, L., Ping, C. L. & Macdonald, R. W. Mobilization pathways of organic carbon from permafrost to arctic rivers in a changing climate. Geophys. Res. Lett. 34, 13 (2007).
Judd, K. E. & Kling, G. W. Production and export of dissolved C in arctic tundra mesocosms: the roles of vegetation and water flow. Biogeochem 60, 213–234 (2002).
Turetsky, M. R. et al. Carbon release through abrupt permafrost thaw. Nat. Geosci. 13, 138–143 (2020).
Farquharson, L. et al. Climate Change Drives Widespread and Rapid Thermokarst Development in Very Cold Permafrost in the Canadian High Arctic. Geophys. Res. Lett. 46, 6681–6689 (2019).
Lewkowicz, A. G. & Way, R. G. Extremes of summer climate trigger thousands of thermokarst landslides in a High Arctic environment. Nat. Commun. 10, 1329 (2019).
Rodenhizer, H. et al. Carbon thaw rate doubles when accounting for subsidence in a permafrost warming experiment. JGR Biogeosci. 125, e2019JG005528 (2020).
Rudy, A. C. A., Lamoureux, S. F., Kokelj, S. V., Smith, I. R. & England, J. H. Accelerating thermokarst transforms ice-cored terrain triggering a downstream cascade to the ocean. Geophys. Res. Lett. 44, 11080–11087 (2017).
Abbott, B. W., Jones, J. B., Godsey, S. E., Larouche, J. R. & Bowden, W. B. Patterns and persistence of hydrologic carbon and nutrient export from collapsing upland permafrost. Biogeosciences 12, 3725–3740 (2015).
Olsson, P. et al. Five stages of the alaskan arctic cold season with ecosystem implications. Arct., Antarct., Alp. Res. 35, 74–81 (2003).
Woo, M. Permafrost Hydrology. ISBN 978-3-642-23462-0
Favaro, E. & Lamoureux, S. F. Downstream patterns of suspended sediment transport in a High Arctic river influenced by permafrost disturbance and recent climate change. Geomorph 246, 359–369 (2015).
Chorley, R. J. and Kennedy, B. A. Physical geography: a systems approach. London (Prentice‐Hall International), Pp. 370 (1971).
Keller, K., Blum, J. D. & Kling, G. W. Stream geochemistry as an indicator of increasing permafrost thaw depth in an arctic watershed. Chem. Geol. 273, 76–81 (2010).
Elmendorf, S. C. et al. Plot-scale evidence of tundra vegetation change and links to recent summer warming. Nat. Clim. Change 2, 453–457 (2012).
Spencer, R. G. M. et al. Dissolved organic carbon and chromophoric dissolved organic matter properties of rivers in the USA. J. Geophys. Res. 117, G03001 (2012).
Mann, P. J. et al. Pan-Arctic trends in terrestrial dissolved organic matter from optical measurements. Front. Earth. Sci. 4, 25 (2016).
Doyle, M. W. et al. Effective discharge analysis of ecological processes in streams. Water Resour. Res. 41, 16 (2005).
Helms, J. R. et al. Absorption spectral slopes and slope ratios as indicators of molecular weight, source, and photobleaching of chromophoric dissolved organic matter. Limnol. Oceanogr. 53, 955–969 (2008).
Huguet, A. et al. Properties of fluorescent dissolved organic matter in the Gironde Estuary. Org. Geochem. 40, 706–719 (2008).
Wauthy, M. & Rautio, M. Permafrost thaw stimulates primary producers but has a moderate effect on primary consumers in subarctic ponds. Ecosphere 11, e03099 (2020).
Cole, J. J. et al. Plumbing the global carbon cycle: integrating inland waters into the terrestrial carbon budget. Ecosystems, 10, 172–175 (2007).
Olefeldt, D. et al. Circumpolar distribution and carbon storage of thermokarst landscapes. Nat. Comm. 7, 13043 (2016).
Edwards, R. & Treitz, P. Vegetation greening trends at two sites in the Canadian Arctic: 1984-2015. Arct., Antarct. Alp. Res 49, 601–619 (2017).
Arndt, K. A. et al. Arctic greening associated with lengthening growing seasons in Northern Alaska. Environ. Res. Lett. 14, 125018 (2019).
O’Donnell, J. A. et al. DOM composition and transformation in boreal forest soils: The effects of temperature and organic‐horizon decomposition state. J. Geophys. Res. 121, 2727–2744 (2016).
Bjorkman, A. D. et al. Status and trends in Arctic vegetation: evidence from experimental warming and long-term monitoring. Ambio 49, 678–692 (2020).
Myers-Smith, I. H. et al. Complexity revealed in the greening of the Arctic. Nat. Clim. Change 10, 106–117 (2020).
Frost, G. V. et al. Tundra greenness. Arctic Report Card 2019. Richter-Menge, J., Druckenmiller, M. L., and Jeffries, M., eds., http://www.arctic.noaa.gov/Report-Card (2019).
Semenchuk, P. R. et al. High Arctic plant phenology is determined by snowmelt patterns but duration of phenological periods is fixed: an example of periodicity. Environ. Res. Lett., 11, 125006 (2016).
Bjorkman, A. D., Elmendorf, S. C., Beamish, A. L., Vellend, M. & Henry, G. H. R. Contrasting effects of warming and increased snowfall on Arctic tundra plant phenology over the past two decades. Glob. Change Biol. 21, 4651–4661 (2015).
Drake, T. W. et al. The ephemeral signature of permafrost carbon in an Arctic fluvial network. JGR Biogeosci. 123, 1475–1485 (2018).
Littlefair, C. A., Tank, S. E. & Kokelj, S. V. Retrogressive thaw slumps temper dissolved organic carbon delivery to streams of the Peel Plateau, NWT, Canada. Biogeosciences 14, 5487–5505 (2017).
Kalbitz, K., Schwesig, D., Rethemeyer, J. & Matzner, E. Stabilization of dissolved organic matter by sorption to the mineral soil. Soil Biol. Biochem. 37, 1319–1331 (2005).
Douglas, T. A., Turetsky, M. R. & Koven, C. D. Increased rainfall stimulates permafrost thaw across a variety of interior Alaskan boreal ecosystems. Npj Clim. Atmos. Sci. 3, 28 (2020).
Shakil, S. et al. Particulate dominance of organic carbon mobilization from thaw slumps on the Peel Plateau, NT: quantification and implications for stream systems and permafrost carbon release. Environ. Res. Lett. 15, 114019 (2020).
Walter Anthony, K. et al. 21st-century modeled permafrost carbon emissions accelerated by abrupt thaw beneath lakes. Nat. Comm. 9, 3262 (2018).
Bowden, W. B. et al. Sediment and nutrient delivery from thermokarst features in the foothills of the North Slope, Alaska: potential impacts on headwater stream ecosystems. J. Geophys. Res. 113, G02026 (2008).
French, D. W. et al. Headwater catchments govern biogeochemistry in america’s largest free‐flowing river network. JGR-Biogeosci. 125, e2020JG005851 (2020).
Raymond, P. A., Saiers, J. E. & Sobczak, W. V. Hydrological and biogeochemical controls on watershed dissolved organic matter transport: pulse‐shunt concept. Ecology 97, 5–16 (2016).
Bogard, M. J. et al. Negligible cycling of terrestrial carbon in many lakes of the arid circumpolar landscape. Nat. Geosci. 12, 180–185 (2019).
Holmes, R. M. et al. Seasonal and annual fluxes of nutrients and organic matter from large rivers to the Arctic Ocean and surrounding seas. Estuar. Coasts 35, 369–382 (2012).
Spencer, R. G. M. et al. Seasonal and spatial variability in dissolved organic matter quantity and composition from the Yukon River basin. Alsk. Glob. Biogeochem. 22, GB4002 (2008).
Neumann, R. B. et al. Warming effects of spring rainfall increase methane emissions from thawing permafrost. Geophys. Res. Lett. 46, 1393–1401 (2019).
We thank: past and present members of the CBAWO team for assisting in data collection; S. Liebner, S. Tank, and M. Turetsky for pre-submission feedback on an earlier version of this manuscript. Financial support was provided by ArcticNet, Government of Canada International Polar Year (IPY) and Natural Resources and Engineering Council (NSERC) grants to S.F.L. and M.J.L. Field logistics were provided by the Polar Continental Shelf Program (PCSP), Natural Resources Canada. We thank the Hamlet of Resolute for their permission and support for conducting research at the CBAWO.
The authors declare no competing interests.
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Beel, C.R., Heslop, J.K., Orwin, J.F. et al. Emerging dominance of summer rainfall driving High Arctic terrestrial-aquatic connectivity. Nat Commun 12, 1448 (2021). https://doi.org/10.1038/s41467-021-21759-3