Accumulation of legacy fallout radionuclides in cryoconite on Isfallsglaciären (Arctic Sweden) and their downstream spatial distribution
The release of legacy contaminants such as fallout radionuclides (FRNs) in response to glacier retreat is a process that has received relatively little attention to date, yet may have consequences as a source of secondary contamination as glaciers melt and down-waste in response to a warming climate. The presence of FRNs in glacier-fed catchments is poorly understood in comparison to other contaminants, yet there is now emerging evidence from multiple regions of the global cryosphere for substantially augmented FRN activities in cryoconite. Here we report concentrated FRNs in both cryoconite and proglacial sediments from the Isfallsglaciären catchment in Arctic Sweden. Activities of some FRNs in cryoconite are 2 orders of magnitude above those found elsewhere in the catchment, and above the activities found in other environmental matrices outside of nuclear exclusion zones. We also describe the presence of the short-lived cosmogenic radionuclide 7Be in cryoconite samples, highlighting the importance of meltwater–sediment interactions in radionuclide accumulation in the ice surface environment. It is currently unknown whether high accumulations of fallout radionuclides in glaciers have the potential to impact local environmental quality through down-wasting and downstream transport of contaminants to the proglacial environment through interaction with sediments and meltwater. We thus recommend that future research in this field focusses on processes of accumulation of FRNs and other environmental contaminants in cryoconite and whether these contaminants are present in quantities harmful for downstream ecosystems.
The Arctic has received considerable attention with respect to environmental change in recent decades as it faces pressures from a changing climate and anthropogenic activities. Long-range atmospheric transport of contaminants from distal sources is a contributor to changing environmental quality in the Arctic, particularly during positive phases of the North Atlantic Oscillation (NAO) (Duncan and Bey, 2004; Macdonald et al., 2005; Stohl, 2006), compounded by the influence of the global distillation process which redistributes some contaminants, whose mobility is influenced by temperature, from warmer to cooler regions (Wania and Mackay, 1995). In addition, the deposition of airborne materials onto glacier surfaces has been shown to impact bare ice albedo through a darkening of the surface (Keegan et al., 2014; Tedstone et al., 2017), acting as a catalyst for increased ice surface melt (Box et al., 2012). The cryosphere has also been recognised as an active component within the biogeochemical cycle of some contaminants (e.g. Vorkamp and Rigét, 2014). Contaminants are deposited onto glacier surfaces following efficient scavenging from the atmosphere by snow (Franz and Eisenreich, 1998; Herbert et al., 2006), and it has been observed that specific anthropogenic substances, such as persistent organic pollutants (POPs), are preferentially accumulated in cold environments and glaciers (Grannas et al., 2013). As snow compacts to form firn and ice, these legacy contaminants are accumulated within the ice column, with glaciers acting as “reservoirs” for contaminants (Steinlin et al., 2015; Miner et al., 2018). However, due to retreat and increased melt rates, glaciers are now releasing these legacy contaminants and behaving as a secondary source (Bizzotto et al., 2009; Bogdal et al., 2009).
Within this context, cryoconite plays a peculiar and unique role. Cryoconite is a particulate matter found on the ice surface which consists of a mixture of organic and inorganic materials, including mineral matter, black carbon, and microbial life (Cook et al., 2016). It often accumulates within holes formed via preferential melting due to the low albedo of cryoconite in comparison to the surrounding ice. Due to the local concentration of nutrients and the availability of seasonal liquid water and solar radiation, cryoconite is a hotspot for microbial life on glaciers (Takeuchi et al., 2001; Zawierucha et al., 2019). Recent studies have highlighted that cryoconite acts as an absorbent that accumulates certain materials, including potential contaminants such as heavy metals (Łokas et al., 2016; Li et al., 2017) and persistent anthropogenic organic chemicals (e.g. Łokas et al., 2016; Baccolo et al., 2017; Li et al., 2017; Weiland-Bräuer et al., 2017). Aided by its interaction with meltwater during the melt season, cryoconite accumulates several atmosphere-derived materials, acting as a temporary sink before the release of these substances into the downstream proglacial environment (Łokas et al., 2014, 2017; Baccolo et al., 2020a). The rich microbial life which flourishes in cryoconite holes also plays an important biogeochemical role, as it has been demonstrated that the bioavailability of carbon, nitrogen, and phosphorus in Antarctica is increased in cryoconite due to its microbial activity (Bagshaw et al., 2013), while augmented levels of heavy metals, including Pb, Cd, Cu, and Zn, have also been found in Arctic cryoconite (Łokas et al., 2016, 2019).
Recently it has been established that cryoconite accumulates fallout radionuclides (FRNs), including products of nuclear weapons testing and nuclear accidents, and natural radionuclides such as 210Pb and cosmogenic 7Be (Appleby, 2008; Taylor et al., 2019). The occurrence of FRNs in glacier-fed catchments remains poorly understood in comparison to other atmospheric contaminants; however a small number of studies to date have reported high activity levels of FRNs in cryoconite in the European Alps (Tieber et al., 2009; Baccolo et al., 2017, 2020b; Wilflinger et al., 2018), the Caucasus (Łokas et al., 2018), Svalbard (Łokas et al., 2016, 2019), Canada (Owens et al., 2019), and Antarctica (Buda et al., 2020). The fate of the radionuclides accumulated in cryoconite remains uncertain, in addition to any potential socio-economic impacts linked to the release of FRNs into glaciated catchments, such as the contamination of downstream ecosystems and natural resources. Furthermore, the processes governing downstream accumulation in proglacial areas, and subsequent dilution in the hydrological system once cryoconite and associated contaminants enter proglacial waters, have not yet been explored.
To contribute to critical knowledge on the downstream transport and accumulation of FRNs in glacial catchments, we present a comparison of radionuclide concentrations and trace elements from cryoconite and proglacial sediments in the Isfallsglaciären catchment of Arctic Sweden, sampled during August 2017. A combination of gamma spectrometry, wavelength-dispersive X-ray fluorescence spectrometry, and elemental analysis of bulk stable carbon and nitrogen isotopes was conducted to establish the activities of radionuclides and stable elements in each sample. Combining the results we report here from Isfallsglaciären with previous observations of FRNs in cryoconite (e.g. Tieber et al., 2009; Baccolo et al., 2017; Łokas et al., 2018; Owens et al., 2019), this work suggesting that the accumulation of FRNs on glaciers is not limited to localised “hotspots” near sites of accidents but is widespread across the global cryosphere. Furthermore we demonstrate that the FRN activities detected in cryoconite on Isfallsglaciären are considerably higher than those found in a range of proglacial sediment settings within the catchment, both highlighting cryoconite's unique ability to accumulate FRNs efficiently and also demonstrating that these activity levels are some of the highest ever recorded outside of nuclear exclusion zones.
Isfallsglaciären is a small ∼1 km2 polythermal valley glacier in the Tarfala Valley of Arctic Sweden. It sits on the eastern flanks of Sweden's highest mountain, Kebnekaise (2096 m a.s.l.), at 67.9∘ N (Fig. 1), and while thinning substantially, it has roughly maintained its terminus position since 1990, prior to which it retreated at an average rate of ∼4 m a−1 between 1916 and 1990 (Ely et al., 2017). The Tarfala Valley is a high-alpine, subarctic environment, characterised by a cold, humid climate (mean annual temperature −3.4 ∘C; mean annual precipitation ∼2000 mm) and a hydrological regime dominated by snow and glacier melt in the summer (Dahlke and Lyon, 2013). The Kebnekaise massif is part of the Seve belt of the Scandinavian Calenonides, with the study site sitting primarily within the Kebne amphibolite outcrop, bounded by the Storglaciären mylonite gneiss at its most distal extent (Baird, 2010). The glacier terminus is split into two lobes by an amphibolite bedrock outcrop. Isfallsglaciären was chosen for this study due to the closed nature of the proglacial catchment, which is constrained by the presence of large latero-frontal Holocene moraines (Fig. 1), the innermost of which were overridden by an advance in 1916 (Karlén, 1973). The ice surface of the north lobe is very steep and heavily crevassed and restricted the collection of cryoconite samples in this study to the south lobe. Glacial meltwater emerges within two braided proglacial outlets from the north and south lobes, which feed into two proglacial lakes, Frontsjön and Isfallssjön, situated within 700 m of the present-day terminus. We targeted Isfallssjön when extracting a lake sediment core as it significantly predates Frontsjön, which formed following glacial retreat past an overdeepening in the forefield after 1959 (Karlén, 1973), and is fed by both of the proglacial outlet streams.
3.1 Sampling strategy and sample preparation
Our sampling strategy was designed to characterise the range of sources contributing to sediment accumulation in the most distal lake, Isfallssjön, and encompasses cryoconite from the snow-free surface of the ablation zone (n=14), sediments within the two braided proglacial outlet streams (n=11), surface sediments from the overridden inner slopes of the north and south moraine (n=10), and sediments from the central foreland (n=2) (Fig. 1). Combined, these samples span 1150 to 1340 m a.s.l. Rockfall also contributes as a sediment source within the catchment; however this material was not sampled due to the active nature of the rockfall, which would make sampling dangerous. All samples were collected between 7 and 17 August 2017, towards the end of the ablation season when snow cover was minimal outside of the accumulation zone. We conducted cryoconite sampling in two transverse profiles to investigate the effects of aspect and distance from the valley side on the accumulation of FRNs and other materials, and we sampled in the proglacial outlets at intervals along the reaches of the two streams to investigate any possible downstream changes in FRN activity concentrations. Each sample was collected in a spatially integrated manner by sampling from five sites within a metre of a central point and stored within new, clean plastic sampling bags or 50 mL tubes. We also retrieved a 38 cm lake sediment core from Isfallssjön using a HTH 90 mm diameter gravity corer, and we extruded the core on-site at 1 cm intervals. Samples were subsequently oven-dried at 100 ∘C for the minimum time required to reach a constant weight and the <75 µm component retrieved for subsequent geochemical analyses. Due to the limited amount of cryoconite available for sampling at each supraglacial site, which varied in mass based on cryoconite type (e.g. in a cryoconite hole, submerged in supraglacial water, distributed on the ice surface), we reserved the entire bulk sample to ensure we had sufficient material for gamma spectrometry. Lake core sections were also preserved in bulk for particle size analysis. Particle size analysis was performed in triplicate on all samples taken from the catchment, using laser diffraction. We use the surface-area-weighted mean particle size, or D [3, 2], for subsequent data analysis presented here as this is the most sensitive measure where fine particulates are common within the size distribution (Malvern, 2015), and relevant where reactivity and bioavailability are of potential importance.
3.2 Gamma spectrometry
Radioactive analyses were carried out in the ISO9001 accredited Consolidated Radio-isotope Facility (CoRIF) at the University of Plymouth, applying an established methodology (e.g. Wynants et al., 2020). Particulate samples for the well detector were packed and sealed into 4 mL plastic vials, and samples for analysis on the planar detector were packed and sealed into 90 mm plastic petri dishes. Sample weighing was conducted on a calibrated balance. Samples were packed within 14 d of return to the laboratory to ensure rapid analysis and were incubated for 22 d prior to analysis to allow the development of secular equilibrium along the 238U decay chain. Gamma counting was conducted using well (GWL-170-15-S; N-type) and planar (GEM-FX8530-S; N-type) spectrometers, both consisting of liquid-nitrogen-cooled, high-purity germanium semiconductor detectors (EG & G ORTEC, Wokingham, UK). The well detector had a full width at half maximum (FWHM) for the 1330 keV line of 60Co of 2.17 keV, and the planar detector had a FWHM of 1.76 keV and a relative efficiency of 50.9 %. The energies, peak widths, and efficiencies of the gamma spectrometers were calibrated using a natural, homogenised soil, with low background activity, which had been spiked with a certified, traceable mixed radioactive solution (80717-669 supplied by Eckert & Ziegler Analytics, Georgia, USA). Calibration relationships were derived using ORTEC GammaVision © software. After incubation, the spiked soils and the samples from Isfallsglaciären, and empty sample containers as blanks, were counted for at least 24 h, and all activities were decay-corrected to the sample collection date. The uncertainties were estimated from the counting statistics and are quoted with a 2σ counting error. Unsupported 210Pb (210Pbun) activities were obtained by the subtraction of 226Ra activity, deduced from the gamma emissions of 214Pb, from the measured total activity of 210Pb (210PbT). Quality control analyses were carried out regularly using soils from the IAEA world-wide proficiency tests, including a moss soil (IAEA-CU-2009-03) and another soil (IAEA-TEL-2012-03) (Table A1).
3.3 Wavelength-dispersive X-ray fluorescence spectrometry
We analysed all samples for a full suite of major and minor elements using wavelength-dispersive X-ray fluorescence (WD XRF) spectrometry. For the proglacial area and lake core, each sample was milled using a Fritsch pulverisette, mixed with a Ceridust 6050M S1000 polypropylene wax binder (Clariant, Switzerland), and pressed into a pellet. The dried cryoconite samples were powdered by hand using a pestle and mortar prior to being packed into 40 mm diameter cups fitted with 6 µm polypropylene spectromembrane (Chemplex, USA). All samples were packed to the same volume and left to settle for 24 h prior to analysis. Analyses were undertaken in the CoRIF lab by WD XRF spectrometry (Axios Max, PANalytical, the Netherlands). The instrument was operated at 4 kW using a Rh target X-ray tube. During sequential analysis of elements, tube settings ranged from 25 kV, 160 mA for low-atomic-weight elements up to 60 kV, 66 mA for higher-atomic-weight elements. All analyses were undertaken using the Omnian analysis application (PANalytical, Netherlands) under a medium of He. This approach offers a rapid and non-destructive means of determining a wide range of elemental concentrations in cryoconite. Repeatability of the approach was assessed by repacking and analysing cryoconite samples in triplicate with the relative standard deviation found to be <10 % across triplicates. Cross comparison to results obtained from a validated inductively coupled plasma optical emission spectrometry (ICP-OES) procedure showed XRF-derived concentrations were in close agreement (within 15 % relative to ICP-OES) for the elements of interest.
3.4 Stable isotope analysis
The dried cryoconite samples were ground by hand using a pestle and mortar. Particulate N and C were determined via elemental analysis (Carlo Erba, EA1110, Italy). The instrument was calibrated using acetanilide, empty pre-combusted capsules were analysed as blanks, and the accuracy of the analyses were checked using the certified reference material PACS-2 (National Research Council of Canada). The results showed that the analyses were accurate to within 10 % of certified values. The ground samples for and analysis were packed into tin capsules and weighed using a calibrated balance. The and ratios were determined at the Isotope Bioscience Laboratory at Ghent University using an elemental analyser (ANCA-SL, Sercon, UK) coupled to an isotope ratio mass spectrometer (20–22, Sercon, UK). The measured δ13C and δ15N values were given relative to the international standards, Vienna PeeDee Belemnite (V-PDB) and AIR, respectively. This calibration was done using the IA-R001 wheat flour laboratory standard ( ‰ and ‰) and an in-house quality assurance organic reference. The average standard deviation on the δ value was determined by measuring five randomly selected samples in triplicate, giving a standard deviation of 0.32 ‰ for 13C and 0.14 ‰ for 15N. For the final analysis of cryoconite, each sample was analysed in duplicate, and an average was taken.
3.5 Constant rate of supply modelling
The sedimentary archive from the proglacial lake core was used to construct a sedimentation chronology using fallout 210Pb supported by known 137Cs date horizons. Reference dates from Chernobyl (1986) and weapons testing (1963 peak and 1952 onset) were used to constrain the chronology following principles outlined in Appleby (2002) in two phases. Due to known disruption of sediment flux from the glacier to Isfallssjön in 1959 with formation of Frontsjön, the constant rate of supply (CRS) model was applied to the core in two sections. This was done to account for any potential change in secondary 210Pbun supply. The CRS model was initially run fitting the 210Pb profile to the lowermost measurement of 241Am, wherein 241Am is known to have been predominantly supplied by global weapons testing fallout (Olszewski et al., 2018). The core was then split at the dated horizon 1959, and the lower section was analysed with a separate CRS model benchmarked to the 1952 onset of 137Cs fallout. Due to low activity concentrations and detection challenges in the lowermost section, the profile tail was modelled using an exponential function fitted (r2=0.99) to three high-precision measurements derived from extended count times, noting the tail represents a small overall proportion of total inventory. Horizon dates and sediment accumulation rates were derived as outlined by Appleby (2002) for each separate model application.
4.1 Cryoconite composition
Fourteen samples of cryoconite were retrieved from the surface of Isfallsglaciären, which are characterised by the range of radionuclide concentrations described in Table A2. The mean activity concentrations of 137Cs, 210Pbun, and 241Am in cryoconite are 3069±941, 9777±780, and 25.8±16.7 Bq kg−1 respectively, reaching a maximum of 4533±350, 14 663±1167, and 74.0±10.2 Bq kg−1. While 210Pb is a natural radioisotope derived from the decay of 222Rn in the atmosphere (Gäggeler et al., 2020), 137Cs and 241Am are anthropogenic FRNs, distributed via atmospheric transport, and are common fission by-products from nuclear reactors and weapons testing (Lindblom, 1969). The anthropogenic radionuclide 137Cs is partially soluble in water, and is a radionuclide of concern in terms of both animal and human health (Van Oostdam et al., 1999). With a half-life of 30.17 years, it is relatively short-lived in the environment, and the 137Cs deposited globally through long-range atmospheric deposition following the Chernobyl accident has decayed by 50 % since 1986 (Olszewski et al., 2018). The half-life of 241Am is considerably longer at 432.2 years and is increasing in the environment due to the short half-life (14 years) of its parent radionuclide 241Pu. 241Am is an alpha emitter and less exchangeable (acid–water soluble) than 137Cs (Kovacheva et al., 2014); however it is potentially harmful if ingested (e.g. Harrison et al., 1994). The primordial radionuclide 40K is also detected in our cryoconite samples at relatively high activities (an average of 1839±168 and a maximum of 2054±207 Bq kg−1). The 40K mean activities found in cryoconite on Isfallsglaciären exceed the maximum activities found on both the Forni and Morteratsch glaciers in the Italian and Swiss Alps (770±200 and 810±55 Bq kg−1 respectively) as reported by Baccolo et al. (2020a), and the considerably higher maximum of 1440±40 Bq kg−1 recorded on the Stubacher Sonnblickkees glacier of the Austrian Alps by Wilfinger et al. (2018). Since 40K is a natural component of rock, the high activities found at Isfallsglaciären are likely related to the geochemical signature of the surrounding catchment geology, and in particular to the abundance of potassium in the rock and sediment.
By considering both the activities of radionuclides and the content of C and N, it is possible to explore the relationship between the organic content of cryoconite and the distribution of radioactivity. The spatial variability of activities for selected natural and anthropogenic radionuclides is illustrated in Fig. 2, with the mass fraction of C and N (% C and % N) measured in the cryoconite samples through bulk stable isotope analysis shown in Fig. 2C. The relationship between organic content and accumulation of some radionuclides is illustrated by the relatively low values of both % N and % C and natural radionuclides 210Pb and 7Be, in the southernmost samples from the upper glacier transect. Higher relative values are found in samples collected to the north. Values of % C and % N cover a wide range of 6.4 %–24.5 % and 0.4 %–1.2 % respectively, with an average ratio of 12.1±1.6 %, which may be attributable to the complex microbial community present in the cryoconite. Typically, micro-organisms mineralise N from the organic matrix to support plant uptake of the nutrient. This is because soil micro-organisms require a cellular ratio of about 8, which is maintained via the N mineralisation. Material in cryoconite holes in Antarctica was found to have a relatively low carbon content of 0.06 %–0.35 %, contributing to ratios in the range 3.5–8.2 (Bagshaw et al., 2013), while samples from the Morteratsch and Forni glaciers had mass ratios of 9.4±1.4 % and 7.2±0.8 % for organic matter respectively and 0.5±0.25 % and 0.2±0.2 % for elemental carbon (Baccolo et al., 2020a). Thus, there are considerable differences in the C and N contents of particulate matter found in cryoconite holes across the cryosphere.
The presence of the cosmogenic radionuclide 7Be in these samples also provides insight into the process of accumulation of radionuclides in cryoconite. Despite being one of the most stable beryllium radioisotopes, the half-life of 7Be is relatively short at 53 d (cf. 1.39 million years for 10Be), yet it is present in all but one of the cryoconite samples, with a mean activity of 1014±599 Bq kg−1. This is at least an order of magnitude higher than the activities of 7Be typically observed in surface soils and fine river sediments in the mid-latitudes (e.g. Smith et al., 2014; Ryken et al., 2016). 7Be demonstrates rapid sorption to sediment particles and has been shown to have an affinity for reducible (e.g. Fe/Mn oxides) and oxidisable (e.g. organic) fractions (Taylor et al., 2012). Finding high activities of 7Be in cryoconite implies a recent accumulation history and supports the role of meltwater – likely sourced from recent snowfall – in providing a crucial link between the radionuclides stored in glacier ice and cryoconite (Baccolo et al., 2020b). The atmospheric deposition of 7Be is affected by a number of factors, including its availability in surface air for scavenging by precipitation (Aldahan et al., 2001). Concentrations of 7Be are generally higher in mid-latitude surface air masses (Kulan et al., 2006), with atmospheric circulation driving the downward transport of 7Be-rich air from the upper troposphere (Aldahan et al., 2001). However, in the polar regions, descent of upper troposphere air is less owing to the stability of the air masses; thus, surface air of polar origin is typically found to have relatively low 7Be activities. It is generally accepted that 7Be is largely transported to the Arctic from the mid-latitudes, with a strong seasonal variation (higher in late winter–spring) that can correspond with transport of contaminants (Feely et al., 1989). Potential 7Be-rich air masses in late winter–spring with corresponding deposition, coupled with summer meltwater production and the concentrating effect of radionuclide exchange at the water–sediment interface described above, may help to explain the relatively high activities found in these cryoconite samples from Arctic Sweden. Routine monitoring of 7Be in precipitation can identify temporal variability linked to atmospheric processes (Taylor et al., 2016). In this regard 7Be could be a useful proxy for transfer of contaminants to the cryosphere in the context of seasonal dynamics of atmospheric circulation (Terzi et al., 2020).
The average inorganic composition of cryoconite based on XRF analysis is shown in Fig. 3. Not unexpectedly, SiO2 is by far the most abundant element in the samples, averaging ∼357 900 ppm, followed by Al2O3 (∼111 400 ppm) and Fe2O3 (∼105 400 ppm). Based on calculating the normalised standard deviation for each element, the element with the highest variance between the 14 cryoconite samples is Cu (0.376), while the least variance between samples (0.034) is found for Fe2O3, one of the most abundant elements found in cryoconite on Isfallsglaciären. The sum of the concentrations of major and trace element oxides detected via XRF spectrometry for the cryoconite samples is between 63.7 % and 79.5 %, and a further 6.8 %–13.5 % can be attributed to C and N based on bulk stable isotope analysis.
The means of selected metal concentrations in cryoconite samples are shown in Table A3. The concentrations for Cu, Fe, Pb, and Zn are elevated over those associated with cryoconite granules found in a glacier in Svalbard (Łokas et al., 2016). These values together with the Al concentrations were used to determine enrichment factors (EFs) from Eq. (1):
where (M) and (Al) are the total concentrations of a metal and of aluminium, and (M)Ref and (Al)Ref are the reference values of the metal and aluminium for the upper continental crust (Wedepohl, 1995). In these samples from Isfallsglaciären the mean of Al concentrations (n=14) was 57 930±3250 mg kg−1. Internationally, the Canadian sediment guidelines for risk to aquatic life (CCME, 1995) can be used to evaluate whether the particulate matter at a site is contaminated or not. In general terms, a sample with an EF falling in the range has minor enrichment, the range indicates moderate enrichment, the range is assessed as moderate to severe enrichment, and EF>10 is classed as severe enrichment. The cryoconite samples have elevated metal concentrations, but only Cr and Pb have concentrations above the probable effect level (PEL). The EF values are clustered in three groups with the highest for Cu and Pb, followed by Cr and Ni, while Fe, Ti, and Zn have the lowest EFs.
A principal component analysis (PCA) was conducted for the cryoconite samples to help explore the variance between the samples, based on gamma spectrometry, particle size analysis, and stable isotope analysis. The PCA scores and loadings for principal components 1 and 2 are depicted in Fig. 4, and no outliers were identified in the data based on the Mahalanobis distance. The PCA loadings (Fig. 3B; Table A4) show that the content of C and N in cryoconite has large positive loadings on principal component 1, while area-weighted particle size (D [3, 2]) has a large positive loading on principal component 2, closely followed by strong negative loadings from δ13C and δ15N. These first two components explain 70 % of the variance in the data, with principal component 1 explaining 47 % and component 2 explaining a further 23 %. Principal components 3, 4, and 5 explain 10 %, 6.4 %, and 5.9 % of the variance respectively, and combined the first five principal components explain 93 % of the variance in the data. Table A4 contains the eigenvector values for principal components 1 to 5, highlighting the influence of 7Be, 40K, and 210Pb on components 3 to 5. While sample numbers are limited, the PCA nevertheless reveals a clustering in cryoconite samples collected from the north side of the southern glacier terminus (Fig. 4a; see Fig. 1C), suggesting that exposure to sunlight may be an influencing factor on the accumulation of FRNs, due to increased melting and/or available energy (see Fig. 2). This in turn may play an important role in organic content of cryoconite by providing energy for flora and microbial life and warrants further investigation in the future. It has previously been shown that a higher proportion of bioavailable C, N, and P is present in cryoconite in comparison to source materials (Bagshaw et al., 2013), highlighting the significant role it plays within biogeochemical cycling. As demonstrated here, other elements are also found in higher concentrations where energy availability is greater, likely due to the microbial activity within cryoconite.
A second PCA was performed to investigate the role of inorganic composition of cryoconite by including major and minor elements detected through XRF analysis (PCA scores and loadings for principal components 1 and 2 are depicted in Fig. 4c and d). In this case the first three components explain 70 % of the variance, and the first six 90 %, with the first principal component explaining 45 % and components 2 to 6 explaining 14 %, 12 %, 9 %, 6.6 %, and 4.3 % of the variance respectively. Examination of the eigenvector values for this PCA illustrate the influence of a negative loading from CaO and Na2O for principal component 1, followed closely by MgO and Cl, with area-weighted particle size (D [3, 2]) again showing a strong negative loading for component 2. CaO, Na2O, MgO, and Cl are all relatively soluble elements, which may explain the clustering of these elements and their role in explaining variance within the samples.
4.2 Catchment-wide distribution of radionuclides
The activities of radionuclides detected within the proglacial area of the Isfallsglaciären catchment are significantly lower than those in cryoconite (Table A1; Fig. 5). This supports the fact that cryoconite is a highly efficient accumulator of radionuclides to the extent that activities are orders of magnitude above those which were deposited and accumulated “off ice”. The deglaciated central forefield has very low levels of FRNs despite having been exposed by the ice before the weapons testing era and Chernobyl; by comparison, the samples of proglacial outwash, which are fed by a regular supply of meltwater and sediment from the glacier, are characterised by much higher activity concentrations of natural radionuclides, particularly for 210Pb and 7Be. Indeed, of the proglacial samples, 7Be is only found in proglacial outwash and lake core sediments, suggesting that the transport of sediment and radionuclides in meltwater is important for their downstream accumulation (Fig. 5) in addition to their accumulation in cryoconite (Baccolo et al., 2020b). The importance of interaction with meltwater, and possible enrichment by runoff of supraglacial sediments such as cryoconite, is further supported by the elevated levels of radionuclides present in the upper portions of the proglacial lake core which are in excess of all other off-ice sediment sources sampled here. Correlation analysis also supports the importance of sediment for accumulation of some FRNs, particularly 40K, in both proglacial and lake core sediments via a negative relationship between FRN activity concentrations and particle size (Fig. 6). This relationship is not present for moraine sediments and thus likely reflects the importance of hydrological sorting of sediments and the presence of fine particles. 241Am is found only in the middle portions of the lake core, corresponding to known dates of nuclear activity which will be discussed further below. These results may reflect a more continuous flux of natural radionuclides from the glacier to the proglacial area, while FRNs, deposited during temporally restricted events, melt out more sporadically due to their storage in defined layers within the snow, firn, and ice. While the activity concentrations of FRNs in moraine sediments are generally low in comparison to cryoconite and proglacial outwash, there is a clear anomaly in the radionuclide concentrations from one sample which contained 74 Bq kg−1 of 210Pb and 207 Bq kg−1 of 137Cs (Fig. 5). This anomaly suggests the possible presence of localised off-ice hotspots, which may be representative of efficient accumulation of FRNs via lichens and mosses from direct atmospheric deposition, as has been reported in other environments (e.g. Sumerling, 1984; Paatero et al., 1998; Kirchner and Daillant, 2002); however we are cautious in our interpretation of this single anomalous sample.
The spatial distribution of radionuclide activity concentrations in the proglacial area of Isfallsglaciären is shown in Fig. 7. 7Be is only present in proglacial outwash; however there is no clear spatial pattern of which samples this has been detected in (Fig. 7a). There is little variation in 137Cs between moraine, forefield, and proglacial outwash sediments; however the anomalous value described above is clearly visible in the moraine sample closest to the northern glacier terminus. There is much more obvious variation in activity concentrations for both 210Pb and 40K, which illustrate a clear difference between the sediments transported in the northern and southern proglacial outlet streams (Fig. 7b). 40K is, for the most part, present in higher levels in moraine sediments (particularly the northern moraine) than the proglacial outwash, in addition to the central forefield sample furthest from the present-day terminus (and most isolated from the braided stream system). 40K is a common element in the Earth's crust, and the relative stability of moraines in comparison to proglacial outwash may allow for increased accumulation of this radionuclide, which has a very long half-life of 1.251 billion years. Potassium is also a relatively soluble element, and thus it may be expected that activity levels would be lowest in areas influenced by a dynamic hydrological system, while levels in areas isolated from water (aside from precipitation) accumulate more 40K. The spatial distribution of 210Pb in the proglacial area of Isfallsglaciären is more complex, with values in sediments from the southern proglacial outlet stream being notably higher than those from the north, and those in moraine sediments. This may be influenced by the glacier surface topography, as the northern terminus lobe is considerably steeper and more crevassed than the southern lobe, which may restrict the ability for cryoconite to accumulate on the surface and meltwater to flow and transfer materials uninterrupted, thus leading to decreased FRN enrichment of supraglacial sediments. The southern proglacial outlet may also have a higher discharge, or be more dynamic in its flow pathways, allowing for accumulation of sediment from a larger sediment source pool.
4.3 Longer-term downstream sediment and contaminant accumulation
The downcore profile of fallout 210Pb against mass depth (reflecting accumulation rates) in lake sediments from Isfallssjön (Fig. 8a) departs from exponential decline, implying periods of enhanced sedimentation. From mass depth ca. 40 g cm−2 (true depth 23 cm) downward, activity concentrations approached the limit of detection wherein selected samples were counted for a longer duration to achieve measurable values to model the tail for CRS modelling (not shown). The 137Cs profile (Fig. 8b) shows a first detectable activity concentration at mass depth 62 g cm−2 (true depth 35 cm). Following Lindblom (1969), this is inferred to represent the onset of early weapons testing in 1952. Subsequent peaks, moving upward, are inferred to represent (i) a mid-1950s spike in atmospheric fallout (mass depth 42–45 g cm−2); (ii) the 1963 peak in fallout (mass depth 35 g cm−2), which is also the first detectable activity concentration of 241Am linked predominantly to global fallout (Bunzl et al., 1995); and finally (iii), at mass depth ca 10–12 g cm−2, increased 137Cs activity concentration associated with fallout from the Chernobyl nuclear accident (Olszewski et al., 2018). Within this well-constrained geochronological framework (Fig. 8c), it can be seen that sedimentation rates (Fig. 8d) were significantly reduced c. 50 years ago, reflecting the post-1959 formation of Frontsjön following terminus retreat (Karlén, 1973), and subsequent “piracy” of proglacial waters from Isfallssjön. A critical question remains about deposition and release of FRNs from the glacial ice during seasonal melt and more recently accelerating retreat due to global warming. The sedimentary data imply a degree of lagged release during the 1960s, with a protracted detection of 241Am (0.4 to 0.5 Bq kg−1) in sediment from mass depth of 33 to 26 g cm−2 representing the period 1963 to 1970. This might relate to release by ice or erosion of surficial sediment from the forefield, i.e. a secondary source. 241Am activity concentration was below detectable limits (< ca. 1.5 Bq kg−1) after 1970, implying that any FRN activity associated with cryoconite has been diluted by other sediment sources during melt, release, and transportation, despite the limited distance between the lake coring site and the glacier.
4.4 Implications for downstream environmental quality
There has been a considerable research effort in understanding the uptake of FRNs within flora and fauna, particularly following the 1986 Chernobyl accident. Mosses, lichens, and fungi are environmental matrices known to efficiently accumulate FRNs (Heinrich, 1992; Steinnes and Njåstad, 1993) and play a crucial role in radionuclide uptake into the food chain, particularly for reindeer and other ruminants (MacDonald et al., 2007). The effect of deposition of 137Cs from atmospheric transport following the Chernobyl accident was considerable for reindeer herding in Sweden, Norway, and other northern countries, due to contamination of the lichen–reindeer–human food chain (Skuterud et al., 2016), and a number of studies have demonstrated the importance of origin (food source) for 137Cs transfer, highlighting the lichen content of diets as a key control on uptake (Ahman et al., 2001; Skuterud et al., 2004). Despite an initially rapid drop in 137Cs in reindeer tissue in Sweden post-Chernobyl (Ahman and Ahman, 1994), concerns around the long-term impacts of exposure to fallout remain. A recent testing campaign by the Swedish Radiation Safety Authority revealed levels of 137Cs of up to 39 706 Bq kg−1 in wild boar in 2017–2018, with as many as 30 % of 229 boar tested exceeding the Swedish limit for meat consumption of 1500 Bq kg−1 (Strålsäkerhetsmyndigheten, 2020). The uptake of 137Cs by lichens and fungi is likely contributing to this persistence of high levels of radioactivity in boar, in addition to the migration of boar into regions affected by Chernobyl. It has been suggested that areas with previous 137Cs contamination may augment 137Cs transfer within the food chain following future contamination events due to the existing 137Cs burden in soils (Ahman et al., 2001). The presence of radionuclides in proglacial sediments in response to ongoing glacial retreat and down-wasting could thus pose an emerging threat for ecosystem health, with the possibility of a knock-on socio-economic impact due to the health considerations of animal–human transfer and stringent controls on limits for sale of produce for human consumption (Kristersson et al., 2017).
The levels of 137Cs detected in cryoconite on Isfallsglaciären are exceptionally high. Indeed, to the best of our knowledge they are some of the highest activity concentrations found in natural environmental matrices outside of nuclear exclusion zones. In light of our findings, and the similarly elevated levels of FRNs detected in cryoconite in other regions of the cryosphere, we recommend an increased research focus on this poorly understood contributor to contamination in proglacial environments, particularly in light of a continued trend of glacier mass loss and meltwater production. We identify a need to establish the presence of FRNs in glacial sediments across a wider spatial range, with a particular focus on regions where glacial meltwater is crucial to downstream water and food security, including the Andes and Himalayas. To more fully understand any potential impact of secondary FRN contamination with glacier retreat, the total mass of cryoconite in glacier catchments must also be considered when assessing whether FRNs are likely to pose any threat to downstream ecosystems. Distribution of hotspots in proglacial environments, and the concentrations of FRNs in downstream sediment sinks, must also be better constrained in order to evaluate implications for both aquatic and terrestrial fauna. Furthermore, we recommend that the bioavailability of FRNs in glacial sediments, including cryoconite, is assessed to understand whether the presence of FRNs in these settings can be taken up in the food chain to levels which are potentially harmful to fauna or for human consumption, or whether downstream dilution and distribution render these harmless. While the risk to distal communities is almost certainly low due to the dilution in rivers, fragile, pioneering ecosystems in newly exposed proglacial zones are more likely to accumulate radionuclides from meltwater and cryoconite transfer and may be candidates for monitoring to evaluate risk to local fauna.
A holistic view of the distribution of radionuclide activities within a glacier catchment, including both the supraglacial and proglacial domains, is described here for the first time. Our study supports that FRNs are accumulated through their interaction with snow, meltwater, and cryoconite, resulting in activity levels in the supraglacial environment that are up to 2 orders of magnitude above those found in the proglacial area. The study sheds light on the influence of authigenic organic matter on radionuclide capture from meltwater in situ in cryoconite, while the presence of 7Be suggests recent accumulation of radionuclides in cryoconite through interaction with a regular supply of meltwater transporting legacy contaminants melting out of snow and ice up-glacier. In addition to describing levels of FRN activity in the supraglacial and proglacial environments, geochronological analysis of downstream sedimentary archives illustrates the melt and sedimentation history of the Isfallsglaciären catchment. The application of nuclear techniques to proglacial lake core chronologies can provide insight into both temporal variability in historical deposition and transport of FRNs and how proglacial sediment accumulation has changed in response to both glacier retreat and a changing flux of meltwater production, both of which have important implications for mitigating downstream impacts of climate change.
Continued glacier retreat will result in further transport of FRNs into the downstream environment through meltwater and sediment flow pathways, but potentially also through direct deposition in the proglacial area under conditions of glacier down-wasting. Such secondary contamination events, resulting from the release of legacy contaminants stored in snow, ice, and cryoconite, may compound the issue of elevated FRN levels found in other environmental matrices such as lichens, mosses, and fungi, which are common in recently deglaciated terrain and known to impact the fauna for whom these are a key food source. This research highlights a need to evaluate not only the activity levels of FRNs in the supraglacial and proglacial environments but also their total mass and spatial distribution and whether FRNs in the proglacial environment are taken up in the food chain in quantities that are potentially harmful. This may, or may not, present an emerging environmental threat to terrestrial and aquatic ecosystems downstream of glaciers. To address this, we recommend an interdisciplinary approach to future research in this field to assess not only the distribution and variability in FRN levels in glaciers, but also the socio-environmental impact of changing quality of glacier-fed waters. In the case of Isfallsglaciären and the wider Kebnekaise area, a priority emerging from our work is to evaluate the potential impacts on FRN uptake in proglacial vegetation, and on grazing fauna such as reindeer, and the wider impact, if any, upon local Sami economy and culture. A continued effort is required to further evaluate the prevalence and spatial variation in both FRNs and other contaminants across the global cryosphere and to better understand both the processes of contaminant accumulation in the supraglacial environment and the downstream impacts of secondary contaminant release.
a . b The samples were collected between 7–17 August 2017 and their analysis started 29 August 2017. c Only n=5 proglacial samples gave a 7Be signal, and 7Be was only detected in the top 1 cm section of the lake core.
Gamma spectrometry, XRF, stable isotope, and particle size analysis data are all available via Pangaea (https://doi.org/10.1594/PANGAEA.935336, Clason, 2021).
CCC, WHB, and SCM devised the study; CCC and NS conducted field sampling. CCC, GEM, AT, and JK conducted preparation and analysis of the samples. PB designed the organic analytical work programme. CCC and WHB led interpretation of the data, and all authors contributed to preparation of the manuscript.
The contact author has declared that neither they nor their co-authors have any competing interests.
Publisher's note: Copernicus Publications remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
We thank Richard Hartley at the University of Plymouth for his help with particle size analysis and Katja Van Nieuland at Ghent University for conducting bulk stable isotope analysis. Sample collection was funded by an INTERACT Transnational Access grant awarded to Caroline C. Clason, and we thank the staff of Tarfala Research Station for providing logistical support during our fieldwork.
This research has been supported by an INTERACT Transnational Access grant (“GRASP: Glacier Recession as a Source of Environmental Pollutants”).
This paper was edited by Elizabeth Bagshaw and reviewed by two anonymous referees.
Åhman, B. and Åhman, G.: Radiocesium in Swedish reindeer after the Chernobyl fallout: Seasonal variations and long-term decline, Health Phys., 66, 503–512, https://doi.org/10.1097/00004032-199405000-00002, 1994.
Åhman, B., Wright, S. M., and Howard, B. J.: Effect of origin of radiocaesium on the transfer from fallout to reindeer meat, Sci. Total Environ., 278, 171–181, https://doi.org/10.1016/S0048-9697(01)00646-5, 2001.
Aldahan, A., Possnert, G., and Vintersved, I.: Atmospheric interactions at northern high latitudes from weekly Be-isotopes in surface air, Appl. Radiat. Isot., 54, 345–353, https://doi.org/10.1016/S0969-8043(00)00163-9, 2001.
Appleby, P. G.: Chronostratigraphic Techniques in Recent Sediments, in: Tracking Environmental Change Using Lake Sediments, Developments in Paleoenvironmental Research, vol. 1, edited by: Smol, J. P. and Last, W. M., Springer, Dordrecht, 2002.
Baccolo, G., Di Mauro, B., Massabò, D., Clemenza, M., Nastasi, M., Delmonte, B., Prata, M., Prati, P., Previtali, E., and Maggi, V.: Cryoconite as a temporary sink for anthropogenic species stored in glaciers, Sci. Rep., 7, 9623, https://doi.org/10.1038/s41598-017-10220-5, 2017.
Baccolo, G., Łokas, E., Gaca, P., Massabò, D., Ambrosini, R., Azzoni, R.S., Clason, C., Di Mauro, B., Franzetti, A., Nastasi, M., Prata, M., Prati, P., Previtali, E., Delmonte, B., and Maggi, V.: Cryoconite: an efficient accumulator of radioactive fallout in glacial environments, The Cryosphere, 14, 657–672, https://doi.org/10.5194/tc-14-657-2020, 2020a.
Baccolo, G., Nastasi, M., Massabo, D., Clason, C., Di Mauro, B., Di Stefano, E., Lokas, E., Prati, P., Previtali, E., Takeuchi, N., Delmonte, B., and Maggi, V.: Artificial and natural radionuclides in cryoconite as tracers of supraglacial dynamics: Insights from the Morteratsch glacier (Swiss Alps), Catena, 191, 104577, https://doi.org/10.1016/j.catena.2020.104577, 2020b.
Bagshaw, E. A., Tranter, M., Fountain, A. G., Welch, K., Basagic, H. J., and Lyons, W. B.: Do cryoconite holes have the potential to be significant sources of C, N, and P to downstream depauperate ecosystems of Taylor Valley, Antarctica?, Arct. Antarct. Alp. Res., 45, 440–457, https://doi.org/10.1657/1938-4246-45.4.440, 2013.
Baird, G. B.: On the Bedrock Geology of the Tarfala Valley: Preliminary Results of 2003 and 2004 Fieldwork, edited by: Jonsson, C., Tarfala Research Station Annual Report 2003–2004, 04B1, Stockholm University, Stockholm, 2010.
Bizzotto, E. C., Villa, S., Vaj, C., and Vighi, M.: Comparison of glacial and non-glacial-fed streams to evaluate the loading of persistent organic pollutants through seasonal snow/ice melt, Chemosphere, 74, 924–930, https://doi.org/10.1016/j.chemosphere.2008.10.013, 2009.
Bogdal, C., Schmid, P., Zennegg, M., Anselmetti, F. S., Scheringer, M., and Hungerbühler, K.: Blast from the past: Melting glaciers as a relevant source for persistent organic pollutants, Environ. Sci. Technol., 43, 8173–8177, https://doi.org/10.1021/es901628x, 2009.
Box, J. E., Fettweis, X., Stroeve, J. C., Tedesco, M., Hall, D. K., and Steffen, K.: Greenland ice sheet albedo feedback: Thermodynamics and atmospheric drivers, The Cryosphere, 6, 821–839, https://doi.org/10.5194/tc-6-821-2012, 2012.
Buda, J., Łokas, E., Pietryka, M., Richter, D., Magowski, W., Iakovenko, N. S., Porazinski, D. L., Budzik, T., Grabiec, M., Grzesiak, J., Klimaszyk, P., Gaca, P., and Zawierucha, K.: Biotope and biocenosis of cryoconite hole ecosystems on Ecology Glacier in the maritime Antarctic, Sci. Total Environ., 724, 138122, https://doi.org/10.1016/j.scitotenv.2020.138112, 2020.
Bunzl, K., Kracke, W., Schimmack, W., and Auerswald, K.: Migration of fallout 239+240Pu, 241Am and 137Cs in the various horizons of a forest soil under pine, J. Environ. Radioact., 28, 17–34, https://doi.org/10.1016/0265-931X(94)00066-6, 1995.
CCME – Canadian Council of Ministers of the Environment: Canadian sediment quality guidelines for the protection of aquatic life, CCME EPC-8E, Summary Tables, Environment Canada, Winnipeg, Canada, 1–5, 1995.
Clason, C: Geochemical analyses of cryoconite and proglacial sediments collected from Isfallsglaciaren, Arctic Sweden, in 2017, PANGAEA [data set], https://doi.org/10.1594/PANGAEA.935336, 2021.
Cook, J., Edwards, A., Takeuchi, N., and Irvine-Fynn, T.: Cryoconite: The dark biological secret of the cryosphere, Prog. Phys. Geogr., 40, 66–111, https://doi.org/10.1177/0309133315616574, 2016.
Dahlke, H. and Lyon, S.: Early melt season snowpack isotopic evolution in the Tarfala valley, northern Sweden, Ann. Glaciol., 54, 149–156, https://doi.org/10.3189/2013AoG62A232, 2013.
Duncan, B. N. and Bey, I.: A modeling study of the export pathways of pollution from Europe: Seasonal and interannual variations (1987–1997), J. Geophys. Res.-Atmos., 109, D0830, https://doi.org/10.1029/2003JD004079, 2004.
Ely, J. C., Graham, C., Barr, I. D., Rea, B. R., Spagnolo, M., and Evans, J.: Using UAV acquired photography and structure from motion techniques for studying glacier landforms: application to the glacial flutes at Isfallsglaciären, Earth Surf. Proc. Land., 42, 877–888, https://doi.org/10.1002/esp.4044, 2017.
Feely, H. W., Larsen, R. J., and Sanderson, C. G.: Factors that cause seasonal variations in Beryllium-7 concentrations in surface air, J. Environ. Radioact., 9, 223–249, https://doi.org/10.1016/0265-931X(89)90046-5, 1989.
Franz, T. P. and Eisenreich, S. J.: Snow scavenging of polychlorinated biphenyls and polycyclic aromatic hydrocarbons in Minnesota, Environ. Sci. Technol., 32, 1771–1778, https://doi.org/10.1021/es970601z, 1998.
Gäggeler, H. W., Tobler, L., Schwikowski, M., and Jenk, T. M.: Application of the radionuclide 210Pb in glaciology – an overview, J. Glaciol., 66, 447–456, https://doi.org/10.1017/jog.2020.19, 2020.
Grannas, A. M., Bogdal, C., Hageman, K. J., Halsall, C., Harner, T., Hung, H., Kallenborn, R., Klán, P., Klánová, J., MacDonald, R. W., Meyer, T., and Wania, F.: The role of the global cryosphere in the fate of organic contaminants, Atmos. Chem. Phys., 13, 3271–3305, https://doi.org/10.5194/acp-13-3271-2013, 2013.
Harrison, J. D., Naylor, G. P. L., and Stather, J. W.: The gastrointestinal absorption of plutonium and americium in rats and guinea pigs after ingestion of dusts from the former nuclear weapons site at Maralinga: implications for human exposure, Sci. Total Environ., 143, 211–220, https://doi.org/10.1016/0048-9697(94)90458-8, 1994.
Heinrich, G.: Uptake and transfer factors of 137Cs by mushrooms, Radiat. Environ. Biophys., 31, 39–49, https://doi.org/10.1007/BF01211511, 1992.
Herbert, B. M. J., Villa, S., and Halsall, C. J.: Chemical interactions with snow: Understanding the behavior and fate of semi-volatile organic compounds in snow, Ecotoxicology and Environmental Safety, 63, 3–16, 2006.
Karlén, W.: Holocene Glacier and Climatic Variations, Kebnekaise Mountains, Swedish Lapland, Geogr. Ann. A, 55, 29–63, https://doi.org/10.1080/04353676.1973.11879879, 1973.
Keegan, K. M., Albert, M. R., McConnell, J. R., and Baker, I.: Climate change and forest fires synergistically drive widespread melt events of the Greenland Ice Sheet, Proc. Natl. Acad. Sci. USA, 111, 7964–7967, https://doi.org/10.1073/pnas.1405397111, 2014.
Kirchner, G. and Daillant, O.: The potential of lichens as long-term biomonitors of natural and artificial radionuclides, Environ. Pollut., 120, 145–150, 2002.
Kovacheva, P., Todorov, B., and Djingova, R.: Geochemical fractionation and bioavailability of 241Am, 60Co and 137Cs in fluvisol soil after sharp temperature variation before the growing season, Cent. Eur. Geol., 57, 153–163, https://doi.org/10.1556/CEuGeol.57.2014.2.3, 2014.
Kristersson, M., Ankarberg, E. H., Rosengren, Å., Lantz, C., and Fogelberg, C. L.: Cesium-137 i livsmedel, Livsmedelsverket riskhanteringsrapport 19, part 1, available at: https://www.livsmedelsverket.se/globalassets/publikationsdatabas/rapporter/2017/2017-nr-19-del-1-cesium-i-livsmedel-riskhanteringsrapport.pdf (last access: 17 November 2021), 2017.
Kulan, A., Aldahan, A., Possnert, G., and Vintersved, I.: Distribution of 7Be in surface air of Europe, Atmos. Environ., 40, 3855–3868, https://doi.org/10.1016/j.atmosenv.2006.02.030, 2006.
Li, Z., Liang, D., Peng, Q., Cui, Z., Huang, J., and Lin, Z.: Interaction between selenium and soil organic matter and its impact on soil selenium bioavailability: A review, Geoderma, 295, 69–79, https://doi.org/10.1016/j.geoderma.2017.02.019, 2017.
Lindblom, G.: Fallout gamma-emitting radionuclides in air, precipitation, and the human body up to spring 1967, Tellus, 21, 127–135, https://doi.org/10.3402/tellusa.v21i1.10063, 1969.
Łokas, E., Bartmiński, P., Wachniew, P., Mietelski, J. W., Kawiak, T., and Środoń, J.: Sources and pathways of artificial radionuclides to soils at a High Arctic site, Environ. Sci. Pollut. Res., 21, 12479–12493, https://doi.org/10.1007/s11356-014-3163-6, 2014.
Łokas, E., Zaborska, A., Kolicka, M., Różycki, M., and Zawierucha, K.: Accumulation of atmospheric radionuclides and heavy metals in cryoconite holes on an Arctic glacier, Chemosphere, 160, 162–172, https://doi.org/10.1016/j.chemosphere.2016.06.051, 2016.
Łokas, E., Wachniew, P., Jodłowski, P., and Gąsiorek, M.: Airborne radionuclides in the proglacial environment as indicators of sources and transfers of soil material, J. Environ. Radioact., 178, 193–202, https://doi.org/10.1016/j.jenvrad.2017.08.018, 2017.
Łokas, E., Zawierucha, K., Cwanek, A., Szufa, K., Gaca, P., Mietelski, J. W., and Tomankiewicz, E.: The sources of high airborne radioactivity in cryoconite holes from the Caucasus (Georgia), Sci. Rep., 8, 10802, https://doi.org/10.1038/s41598-018-29076-4, 2018.
Łokas, E., Zaborska, A., Sobota, I., Gaca, P., Milton, J. A., Kocurek, P., and Cwanek, A: Airborne radionuclides and heavy metals in high Arctic terrestrial environment as the indicators of sources and transfers of contamination, The Cryosphere, 13, 2075–2086, https://doi.org/10.5194/tc-13-2075-2019, 2019.
Macdonald, C. R., Elkin, B. T., and Tracy, B. L.: Radiocesium in caribou and reindeer in northern Canada, Alaska and Greenland from 1958 to 2000, J. Environ. Radioact., 93, 1–25, https://doi.org/10.1016/j.jenvrad.2006.11.003, 2007.
Macdonald, R. W., Harner, T., and Fyfe, J.: Recent climate change in the Arctic and its impact on contaminant pathways and interpretation of temporal trend data, Sci. Total Environ., 342, 5–86, https://doi.org/10.1016/j.scitotenv.2004.12.059, 2005.
Malvern: A basic guide to particle characterization, Malvern Instruments Limited, Worcestershire, UK, 24 pp., 2015.
Miner, K. R., Campbell, S., Gerbi, C., Liljedahl, A., Anderson, T., Perkins, L. B., Bernsen, S., Gatesman, T., and Kreutz, K. J.: Organochlorine pollutants within a polythermal glacier in the interior Eastern Alaska Range, Water, 10, 1157, https://doi.org/10.3390/w10091157, 2018.
Olszewski, G., Andersson, P., Lindahl, P., and Eriksson, M.: On the distribution and inventories of radionuclides in dated sediments around the Swedish coast, J. Environ. Radioact., 186, 142–151, https://doi.org/10.1016/j.jenvrad.2017.09.025, 2018.
Owens, P. N., Blake, W. H., and Millward, G. E.: Extreme levels of fallout radionuclides and other contaminants in glacial sediment (cryoconite) and implications for downstream aquatic ecosystems, Sci. Rep., 9, 12531, https://doi.org/10.1038/s41598-019-48873-z, 2019.
Paatero, J., Jaakkola, T., and Kulmala, S.: Lichen (sp. Cladonia) as a deposition indicator for transuranium elements investigated with the Chernobyl fallout, J. Environ. Radioact., 38, 223–247, https://doi.org/10.1016/S0265-931X(97)00024-6, 1998.
Ryken, N., Al-Barri, B., Taylor, A., Blake, W., Maenhout, P., Sleutel, S., Tack, F. M. G., Dierick, M., Bodé, S., Boeckx, P., and Verdoodt, A.: Quantifying the spatial variation of 7Be depth distributions towards improved erosion rate estimations, Geoderma, 269, 10–18, https://doi.org/10.1016/j.geoderma.2016.01.032, 2016.
Skuterud, L., Pedersen, Ø., Staaland, H., Røed, K. H., Salbu, B., Liken, A., and Hove, K.: Absorption, retention and tissue distribution of radiocaesium in reindeer: effects of diet and radiocaesium source, Radiat. Environ. Biophys., 43, 293–301, https://doi.org/10.1007/s00411-004-0257-4, 2004.
Skuterud, L., Ytre-Eide, M. A., Hevrøy, T. H., and Thørring, H.: Caesium-137 in Norwegian reindeer and Sámi herders – 50 years of studies, in: II International Conference on Radioecological Concentration Processes: II International Conference 50 years later, Seville, Spain, p. 752, 2016.
Smith, H. G., Blake, W. H., and Taylor, A.: Modelling particle residence times in agricultural river basins using a sediment budget model and fallout radionuclide tracers, Earth Surf. Proc. Land., 39, 1944–1959, https://doi.org/10.1002/esp.3589, 2014.
Steinlin, C., Bogdal, C., Pavlova, P. A., Schwikowski, M., Lüthi, M. P., Scheringer, M., Schmid, P., and Hungerbühler, K.: Polychlorinated Biphenyls in a Temperate Alpine Glacier: 2. Model Results of Chemical Fate Processes, Environ. Sci. Technol., 49, 14092–14100, https://doi.org/10.1021/acs.est.5b03304, 2015.
Steinnes, E. and Njåstad, O.: Use of mosses and lichens for regional mapping of 137Cs fallout from the Chernobyl accident, J. Environ. Radioact., 21, 65–73, https://doi.org/10.1016/0265-931X(93)90026-4, 1993.
Stohl, A.: Characteristics of atmospheric transport into the Arctic troposphere, J. Geophys. Res.-Atmos., 111, D1130, https://doi.org/10.1029/2005JD006888, 2006.
Strålsäkerhetsmyndigheten: Cesium-137 i vildsvinskött, available at: https://www.stralsakerhetsmyndigheten.se/omraden/miljoovervakning/radioaktiva-amnen/kostnadsfri-matning-av-cesium-137-i-vildsvinskott/, last access: 29 May 2020.
Sumerling, T. J.: The use of mosses as indicators of airborne radionuclides near a major nuclear installation, Sci. Total Environ., 35, 251–265, https://doi.org/10.1016/0048-9697(84)90007-X, 1984.
Takeuchi, N., Kohshima, S., and Seko, K.: Structure, formation, and darkening process of albedo-reducing material (cryoconite) on a Himalayan glacier: A granular algal mat growing on the glacier, Arct. Antarct. Alp. Res., 33, 115–122, https://doi.org/10.2307/1552211, 2001.
Taylor, A., Blake, W. H., Couldrick, L., and Keith-Roach, M. J.: Sorption behaviour of beryllium-7 and implications for its use as a sediment tracer, Geoderma, 187–188, 16–23, https://doi.org/10.1016/j.geoderma.2012.04.013, 2012.
Taylor, A., Keith-Roach, M. J., Iurian, A. R., Mabit, L., and Blake, W. H.: Temporal variability of beryllium-7 fallout in southwest UK, J. Environ. Radioact., 160, 80–86, https://doi.org/10.1016/j.jenvrad.2016.04.025, 2016.
Taylor, A., Blake, W. H., Iurian, A. R., Millward, G. E., and Mabit, L.: The use of Be-7 as a soil and sediment tracer, in: Assessing Recent Soil Erosion Rates through the Use of Beryllium-7 (Be-7), edited by: Mabit, W. H. and Blake, L., Springer Nature, Switzerland, 1–12, 2019.
Tedstone, A. J., Bamber, J. L., Cook, J. M., Williamson, C. J., Fettweis, X., Hodson, A. J., and Tranter, M.: Dark ice dynamics of the south-west Greenland Ice Sheet, The Cryosphere, 11, 2491–2506, https://doi.org/10.5194/tc-11-2491-2017, 2017.
Terzi, L., Wotawa, G., Schoeppner, M., Kalinowski, M., Saey, P. R. J., Steinmann, P., Luan, L., and Staten, P. W.: Radioisotopes demonstrate changes in global atmospheric circulation possibly caused by global warming, Sci. Rep., 10, 10695, https://doi.org/10.1038/s41598-020-66541-5, 2020.
Tieber, A., Lettner, H., Bossew, P., Hubmer, A., Sattler, B., and Hofmann, W.: Accumulation of anthropogenic radionuclides in cryoconites on Alpine glaciers, J. Environ. Radioact., 100, 590–598, https://doi.org/10.1016/j.jenvrad.2009.04.008, 2009.
Van Oostdam, J., Gilman, A., Dewailly, E., Usher, P., Wheatley, B., Kuhnlein, H., Neve, S., Walker, J., Tracy, B., Feeley, M., and Kwavnick, B.: Human health implications of environmental contaminants in Arctic Canada: a review, Sci. Total Environ., 230, 1–82, https://doi.org/10.1016/S0048-9697(99)00036-4, 1999.
Vorkamp, K. and Rigét, F. F.: A review of new and current-use contaminants in the Arctic environment: Evidence of long-range transport and indications of bioaccumulation, Chemosphere, 111, 379–395, https://doi.org/10.1016/j.chemosphere.2014.04.019, 2014.
Wania, F. and Mackay, D.: A global distribution model for persistent organic chemicals, Sci. Total Environ., 160–161, 211–232, https://doi.org/10.1016/0048-9697(95)04358-8, 1995.
Wedepohl, K., H.: The composition of the continental crust, Geochim. Cosmochim. Ac., 59, 1217–1232, https://doi.org/10.1016/0016-7037(95)00038-2, 1995.
Weiland-Bräuer, N., Fischer, M. A., Schramm, K. W., and Schmitz, R. A.: Polychlorinated biphenyl (PCB)-degrading potential of microbes present in a cryoconite of Jamtalferner glacier, Front. Microbiol., 8, 1105, https://doi.org/10.3389/fmicb.2017.01105, 2017.
Wilflinger, T., Lettner, H., Hubmer, A., Bossew, P., Sattler, B., and Slupetzky, H.: Cryoconites from Alpine glaciers: Radionuclide accumulation and age estimation with Pu and Cs isotopes and 210Pb, J. Environ. Radioact., 186, 90–100, https://doi.org/10.1016/j.jenvrad.2017.06.020, 2018.
Wynants, M., Millward, G., Patrick, A., Taylor, A., Munishi, L., Mtei, K., Brendonck, L., Gilvear, D., Boeckx, P., Ndakidemi, P., and Blake, W. H.: Determining tributary sources of increased sedimentation in East-African Rift Lakes, Sci. Total Environ., 717, 137266, https://doi.org/10.1016/j.scitotenv.2020.137266, 2020.
Zawierucha, K., Buda, J., Fontaneto, D., Ambrosini, R., Franzetti, A., Wierzgoń, M., and Bogdziewicz, M.: Fine-scale spatial heterogeneity of invertebrates within cryoconite holes, Aquat. Ecol., 53, 179–190, https://doi.org/10.1007/s10452-019-09681-9, 2019.