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Correspondence: Alia L. Khan (firstname.lastname@example.org)
Here, we present radiative forcing (RF) estimates by snow algae in the Antarctic Peninsula (AP) region from multi-year measurements of solar radiation and ground-based hyperspectral characterization of red and green snow algae collected during a brief field expedition in austral summer 2018. Our analysis includes pigment content from samples at three bloom sites. Algal biomass in the snow and albedo reduction are well-correlated across the visible spectrum. Relative to clean snow, visibly green patches reduce snow albedo by ∼40 % and red patches by ∼20 %. However, red communities absorb considerably more light per milligram of pigment compared to green communities, particularly in green wavelengths. Based on our study results, it should be possible to differentiate red and green algae using Sentinel-2 bands in blue, green and red wavelengths. Instantaneous RF averages were double for green (180 W m−2) vs. red communities (88 W m−2), with a maximum of 228 W m−2. Based on multi-year solar radiation measurements at Palmer Station, this translated to a mean daily RF of ∼26 W m−2 (green) and ∼13 W m−2 (red) during peak growing season – on par with midlatitude dust attributions capable of advancing snowmelt. This results in ∼2522 m3 of snow melted by green-colored algae and ∼1218 m3 of snow melted by red-colored algae annually over the summer, suggesting snow algae play a significant role in snowmelt in the AP regions where they occur. We suggest impacts of RF by snow algae on snowmelt be accounted for in future estimates of Antarctic ice-free expansion in the AP region.
Snow algae blooms are common in coastal snowpacks of the northern Antarctic Peninsula (AP) and adjacent islands during austral summer. Over the past 50 years, the AP has warmed significantly (Turner et al., 2005), and although a recent slowing of this trend has been observed due to natural variability (Turner et al., 2016), it remains one of the most rapidly warming regions on the planet (Hansen et al., 2010; Steig et al., 2009; Turner et al., 2009, 2014; Vaughan et al., 2003). This intense warming is likely to increase snowmelt availability, potentially impacting red and green snow algae blooms, which are sensitive to light (Rivas et al., 2016), water and temperature (Hoham and Remias, 2020). Colored pigments such as astaxanthin protect the snow algae from harsh light conditions (Bidigare et al., 1993; Gorton et al., 2001). Algal pigments are not just protective; they also play a functional role in melting snow and ice (Dial et al., 2018). Significant changes have been identified in the regional sensitivity of moss growth to past temperature rises, including microbial productivity, moss bank vertical growth and mass accumulation, suggesting Antarctic terrestrial ecosystems will alter rapidly under future warming (Amesbury et al., 2017; Gutt et al., 2018). An `Antarctic greening' is therefore possible, following well-documented Arctic observations (i.e., Myers-Smith et al., 2020).
Snowpacks serve as habitats and nutrient reservoirs for microbes across the global cryosphere (e.g., Hisakawa et al., 2015; Hodson et al., 2017; Lutz et al., 2016; Remias et al., 2005; Segawa et al., 2018). Meltwater can stimulate a return to an active growing state through the ionic pulse, when there is a flushing and mass loading of ions and nutrients at the onset of snowmelt (e.g., Williams and Melack, 1991). In coastal Antarctic snowmelt, nutrient cycling is influenced by inputs from penguin and seal excreta, which help to fertilize local glacial, terrestrial and aquatic ecosystems (Hodson, 2006). The input of snowmelt into coastal regions could have significant impacts on marine primary production, such as during high-melt years, which has been shown to increase primary production in the ocean (Dierssen et al., 2002).
Both biotic and abiotic light-absorbing particles (LAPs) (Skiles et al., 2018) lead to a reduction in surface albedo. LAPs are generally comprised of dust (e.g., Bryant et al., 2013; Painter et al., 2012; Skiles and Painter, 2019), black carbon (e.g., Khan et al., 2019; Rowe et al., 2019), volcanic ashes (Flanner et al., 2007) and snow algae (e.g., Ganey et al., 2017; Lutz et al., 2016). LAPs influence spectral albedo of snow in the visible spectrum, 400–700 nm (Warren and Wiscombe, 1980). Spectral albedo is further dependent on physical snow properties such as specific surface area, i.e., grain size and shape (e.g., Cordero et al., 2014), liquid water content, surface roughness, snow depth, albedo of underlying ground (for thin snowpacks), and snow density (Flanner et al., 2007). Aged snow that has collected LAPs typically has an albedo around 0.5–0.7 and in extreme cases of organic LAP content can range below 0.2 (Khan et al., 2017). Arctic red snow algae blooms can reduce surface albedo up to 13 % (Lutz et al., 2016). Snow darkening by LAPs and the associated radiative forcing (RF) have the potential to impact the long-term climate, while accelerating snow melt and changes in regional hydrology in the near term. Given their anthropogenic association, they are not expected to diminish in the future (Skiles et al., 2018). However, unlike other LAPs (Flanner et al., 2007), the “bioalbedo” feedback (Cook et al., 2017) from microbes living and growing on the surface of the cryosphere is not currently accounted for in global climate models, and only one study has assessed the role of red snow algae in RF, in Alaska (Ganey et al., 2017). Furthermore, living organisms such as snow algae reduce surface albedo differently than LAPs, due to their life cycle response to light (Bidigare et al., 1993; Rivas et al., 2016), the functional role of their pigments in melting snow and ice (Dial et al., 2018), and their strong absorption features as opposed to LAPs' broad absorption across the visible wavelengths.
In our study region, the snow algae are comprised of green algae (Chlorophyta), but the taxonomies are unstable. Based on findings on nearby Adelaide Island, they are likely a combination of Chloromonas, Chlamydomonas and Chlorella genuses (Davey et al., 2019). In this study, we did not have the opportunity to analyze the community composition of our samples, but we plan to include this in future work.
Recent developments in multi-spectral satellite-based instrumentation have advanced our ability to monitor and map Antarctica's terrestrial biosphere (Fretwell et al., 2011). Algorithms for retrieval of aerosol and snow and ice properties in polar and midlatitude regions are actively developing, e.g., Stamnes et al. (2007). However, detection of biological constituents remains challenging due to the presence of other LAPs, such as dust (Huovinen et al., 2018). Snow algae were first mapped in the Sierra Nevada in CA, USA, using the chlorophyll absorption feature at 680 nm (Painter et al., 2001). Red ∕ green band ratios have since been applied to SPOT (Takeuchi et al., 2006) and Landsat-8 imagery (Ganey et al., 2017; Hisakawa et al., 2015), which appears to work well in regions with limited exposure of bare rock and soil. On the Greenland Ice Sheet, Wang et al. (2018) used Sentinel-3 imagery to map the spatial pattern of glacier algae using the reflectance ratios between 709 and 673 nm. Within the AP region, spectral mixture analysis with Sentinel-2 imagery has been shown to more reliably classify snow algae than band ratios when other LAPs are present (Huovinen et al., 2018), and a mosaic comprised of satellite images from multiple years has identified green snow as a terrestrial carbon sink (Gray et al., 2020).
Snow algae can be used to monitor climate impacts since their habitat is highly responsive to environmental conditions (Hoham and Remias, 2020). Here we present ground-based observations of surface spectral albedo and corresponding algal biomass from three coastal snow sites in the South Shetland Islands of Antarctica at the height of the austral 2018 growing season. In this study we targeted patches of snow that are free of snow algae and colored algae as visibly red, visibly green and mixed (visibly red and green) in order to calculate RF and develop algorithms for eventual remote sensing of snow algae in order to monitor their response to climactic change (Fig. 1). The categories are based purely on the visible snow algae color. We build on these pioneering studies described above by presenting new approaches to spectrally distinguish red from green snow algae and further evaluate the RF of snow algae based on environmental conditions in this part of Antarctica. The following analysis considers the reflectance measurements in terms of albedo, RF and the variability in reflectance in relationship to pigment concentration and light absorption. Finally, we evaluate several approaches to estimate pigment concentration that can be applicable to a variety of high-spatial-resolution satellites, including Sentinel-2.
Field observations were conducted at two sites on King George Island (KGI), the largest of the South Shetland Islands, and one site on northern Nelson Island (NI), southwest of KGI in January 2018. The first site on KGI was located near Fildes/Maxwell Bay between the Chilean Prof. Julio Escudero Station and the Chinese Great Wall Station. It is approximately 200 m above mean high tide, with slightly less frequent wildlife traffic than the other two sites. The second KGI site was located in Collins Bay adjacent to Collins Glacier and is approximately 100 m above mean high tide, with more frequent seal, penguin and other bird activity. Both KGI sites were flat, low-sloping southeast-facing beaches (Fig. 1). The third site on Nelson Island is a low-sloping northwest-facing beach at the edge of Nelson Glacier with frequent seal and penguin activity due to the location approximately 25 m above mean high tide. The weather conditions were uniformly cloudy at Fildes and Nelson and clear at Collins Bay. Only the algae-free site at Nelson was on a glacier; the rest were coastal snowpacks. Both Nelson and Collins were near glacier edges.
Optically thick (>30 cm) snowpacks were prioritized for spectral albedo data acquisition and corresponding snow algae sampling in order to minimize the impact of the underlying ground on spectral albedo. Sites were also selected based on where it was possible to sample (1) a control site with relatively clean snow having no visible snow algae, (2) green snow algae, (3) red snow algae, and (4) mixed-phase green and red algae. At each site, duplicates of each snow type were measured with the spectrometer (except at Nelson Island where only one mixed site was observed). All samples were collected around noon local Chilean time, when the seasonal snowpack was also receiving the most incoming solar radiation. As evidenced in Fig. 1, this can also result in snowmelt ponding. While the snowpack contained a lot of water, large areas of melt ponding were avoided for spectral measurements. Snow depth was measured at each observation site and reported to the nearest centimeter if less than 1 m (Table 1).
Abbreviations: F: Fildes; C: Collins; N: Nelson; Chl: chlorophyll a in
melted snow; ChP: sum of chlorophyll a and phaeopigments per snow surface
area; IRF: instantaneous RF assuming a clear sky; αvis: albedo in visible (400–700 nm); αnir: albedo in
near infrared (700–1300 nm); ord. day: ordinal day in 2018; elevation was
not available (NA) for Collins site.
a Due to the shallow snow depth (7–8 cm), the albedo is likely influenced by dark underlying surface compared to optically deep snow and these stations were excluded from near-infrared (NIR) albedo calculations where algal pigments do not significantly absorb.
b This station had unrealistically high albedo given its type and spectral shape and was not included in the RF and spectral analyses in the paper.
Surface snow samples (top 10 cm) were collected at each site in plastic bags, melted at room temperature and filtered through 0.45 µm pore size Nuclepore filters. The filters were immediately frozen (−20 ∘C) and then shipped frozen to a laboratory in Valdivia, Chile, where they were fluorometrically analyzed (Turner Designs TD-700), using 90 % acetone for pigment extraction for chlorophyll a and phaeopigment analysis according to standard procedures (Parsons et al., 1984). Pigment was considered to be the sum of chlorophyll a determined fluorometrically and the amount attributed to phaeopigments (ChP). The amount of phaeopigment in the samples was quite high (2.34 times higher than chlorophyll a), but was well-correlated to chlorophyll a concentration (Fig. 2, r2=0.97, m=2.34).
Phaeopigments are a degradation product of algal chlorophyll pigments, and the high amounts could be related to a combination of environmental and methodological factors. The cold temperatures of the Antarctic may allow for pigment degradation products of algae to remain in the snow longer than in other types of environments. Secondly, snow algae are known to have high amounts of chlorophyll b at levels up about half the amount of chlorophyll a (Davey et al., 2019). Fluorometric methods can underestimate chlorophyll a and substantially overestimate phaeopigments in phytoplankton when chlorophyll b is present (Vernet and Lorenzen, 1987). Finally, higher-than-normal phaeopigments can also occur due to issues in shipping and storing samples over time. For all of these reasons, we have chosen to add the amount of chlorophyll a and phaeopigments together in this paper and refer to this as ChP. Davey et al. (2019, Table 1) reported the dry cell mass (DCM) pigment composition of snow algae communities on nearby Adelaide Island with green communities mostly comprised of chlorophyll a (42 %), followed by chlorophyll b (19 %), lutein (7 %), β-carotene (5 %) and astaxanthin-esters (4 %). Red communities were mostly comprised of astaxanthin-esters and astaxanthin-like esters (60 %), chlorophyll a (24 %), chlorophyll b (11 %), lutein (<1 %), and xanthophyll (5 %).
Pigment measurements were calculated in volumetric units of melted snow and hence vary with the depth and volume of snow excavated from the site. Following Painter et al. (2001) and Thomas (1972), the top 10 cm was selected for this analysis. However, the distribution of algae with depth in the snow is not well-documented and the pigment measurements will be more or less dilute depending on the excavation depth. Hence it cannot be compared across regions. We are unaware of a community standard for determining excavation depths and published studies have used depths varying from 5–10 cm (Davey et al., 2019; Grinde, 1983), and the algae may be covered by varying depths of snow, which could be several meters thick although scouring from strong blizzards may later expose sites and facilitate dispersal of the cells (Ling and Seppelt, 1993). In order to rectify this and make our data relevant to other studies and future work, we standardized these values to represent the amount of integrated pigment per surface area of snow (mg ChP m−2). This more standardized metric is also considered more appropriate for conducting comparisons to snow albedo measured above the snow surface. We also recommend researchers excavate appropriately deep in the snow to harvest the majority of the algae with depth. For this conversion, we calculated area-weighted ChP following Eq. (1) using a mean snow density of 610 kg m−3, and excavated snow depth was generally 10 cm (0.10 m), except for select samples at Nelson that were 7–8 cm (0.07 m). In the formulation, “dry” refers to native snow and “melt” refers to melted snow, following Eq. (1):
This parameter could underestimate the amount of integrated pigment, if there were significant algae beneath the excavated snow layer. However, the 10 cm excavation depth selected in this study was the depth at which color was no longer present in the samples, and hence most of the algae were believed to be harvested within the top layer. Cell counts were not conducted in this study.
Spectral reflectance measurements were collected with an Analytical Spectral Devices (ASD) FieldSpec® 4 hyperspectral spectroradiometer (Malvern Panalytical, USA) between 350 and 2500 nm. The sensor was equipped with a light-diffusing fore optic remote cosine receptor (RCR) to measure planar irradiance. We selected three different locations and collected spectral measurements for two samples each of green, red and mixed snow algae patches and two algae-free or “clean” snow areas, for a total of 24 measurement sites (two of each of the four types across the three sites). Overall coastal snowpack in this region and at this time of year are generally comprised of dense wet snow, although snow density was not recorded. Snow density in Eq. (1) is based on average observations from similar study sites in the AP region in January 2020. Areas with snowmelt ponding were avoided. The RCR was placed upward to collect the downwelling planar irradiance incident upon the snow surface (Ed) and the upwelling planar irradiance reflected from the snow (Eu). Measurements were collected in triplicate. The operator was located in a direction 90–135∘ away from the sun to minimize solar glint and self-shadowing (Mobley, 1999). Snow conditions did not allow for a tripod, so nadir orientation was determined by practice with a level and by visual assistance of an observer. Since the measurements were carried out under heavily overcast conditions where irradiance is dominated by the diffuse insolation with no solar azimuthal dependence, the influence of slight tilt when measuring the downwelling irradiance (i.e., the cosine error) is expected to be minor (<0.5 %) (Castagna et al., 2019). The reflectance measurements were taken prior to excavation of snow sample for laboratory analysis.
Post-processing of the data involved computing spectral reflectance, R(λ), as the ratio of the upwelling flux normalized to the downwelling flux for each wavelength (λ). The mean of the three measurements was calculated for each site. Ambient light conditions were too low in the short-wave infrared wavelengths for getting adequate signal-to-noise ratio for our measurements. In post-processing, reflectance values were truncated at 1350 nm for this analysis. This value represents the limit often used for RF calculations in other studies (Bryant et al., 2013). In addition, empirical correction coefficients were used to correct for temperature-related radiometric inter-channel steps using the procedure and MATLAB code from Hueni et al. (2016). This removed the step function near 1000 nm for most of the spectra, although not fully for all spectra. However, this discontinuity does not significantly impact results or albedo calculations. Albedo was calculated as the integrated R in two different intervals: visible (400–700 nm) and infrared (700–1300 nm). Quality assurance was conducted for each spectrum, and one station (Fildes 5, mixed algae) was removed from the data analysis because the spectral magnitude of R was considered unrealistically high with the highest infrared albedo measured in the study (i.e., higher than clean snow) that was not consistent with the spectral shape and pigment content compared to the expected values at the other stations. For the remote sensing analyses, R(λ) was convolved with the published spectral response functions (SRFs) for the Sentinel-2 sensor from the European Space Agency Sentinel – 2 Spectral Response Function (S2-SRF) technical document (European Space Agency, 2017) to obtain an estimate of bands that would be observed by the sensor after proper atmospheric correction centered at wavelengths in each part of the spectrum: blue (Band 2, 492 nm), green (Band 3, 560 nm), red (Band 4, 664 nm) and near infrared (Band 5, 704 nm). Following Painter et al. (2001) and Gray et al. (2020), a scaled integral of Sentinel-2's Band 4 relative to a continuum formed by the line between Bands 3 and 5 (RContB4). This continuum band can be visualized in Fig. S2 in Gray et al. (2020) and is numerically calculated with reflectance from the adjacent bands (here Bands 3 and 5) as follows:
The scaled integral of the band depth, IB4, was then calculated as
The absorptance, A(λ), which is unitless, attributed to each snow sample can be calculated from the reflectance as the amount of light that was absorbed (i.e., not reflected) from the snow where
To estimate the photosynthetic absorptance attributed to algae, Aalg(λ), we account for relative absorption compared to clean snow and remove the absorption due to effects of non-pigmented algal constituents and other factors such as water and impurities. We subtracted the absorptance measured at 709 nm where chlorophyll and accessory pigments have low absorption following methods in bio-optical studies of seagrass and other vegetation (Zimmerman, 2003).
Albedo, α, is a measure of the diffuse reflectance of solar radiation from the snow surface that was estimated over two different wavelength regions for all the sample sites following
where N is the number of wavelengths and calculated as the integral over two different wavelength regions: visible (400–700 nm), αvis, and near infrared (700–1300 nm), αnir.
Net RF is calculated as the net flux upward (down minus up) in watts per square meter and is calculated as
This term depends on the amount of radiation reaching the snow surface, which is a function of time of year, time of day and amount of cloud cover. Here, we follow previous studies to estimate the additional RF caused by the addition of algae compared to clean snow (Myhre et al., 2013) and replace the “1” with the reflectance of clean snow. Two different analyses of RF calculating instantaneous and interannual RF. We calculated instantaneous RF as
For comparability to other studies using clear-sky remote sensing imagery, we calculated IRF for clear-sky solar irradiance normal to insolation at each site, ∼62∘ S 58∘ W, on the date each site was visited in January 2018 at 13:00 local solar mean time using https://www.pvlighthouse.com.au (last access: 6 June 2020; Ganey et al., 2017).
Because of the variability and prevalence of cloud cover in this region, we also conducted long-term flux analysis to determine what the forcing would be using realistic cloud cover for the region. Following from Bryant et al. (2013), a daily RF, , was estimated to provide the general magnitude of the forcing that might be expected given realistic cloud forcing and typical concentrations of snow algae. Hourly measurements of spectral irradiance were made at Palmer Station, Antarctica (64∘46′ S, 64∘03′ W, 21 m above sea level) with a SUV-100 spectroradiometer from Biospherical Inc. (Booth et al., 1994) processed between 400–600 nm from 1990–1997 (Dierssen et al., 2000). Irradiance was extrapolated to photosynthetically available radiation (PAR) (400–700 nm) with a site-specific relationship using the radiative transfer model SBDart (Gautier and Landsfeld, 1997) run with different clouds and atmospheric and albedo conditions following
Measurements of Ed were also compared to clear-sky formulations from the radiative transfer model with different surface albedo properties from 100 % snow, 100 % ocean, and 50 % snow and 50 % ocean. Modeled estimates of daily clear-sky PAR are ∼14 % higher estimated with snow compared to ocean. Since snow and sea ice are generally absent from Palmer Station during summer months, the radiative transfer modeling of clear-sky irradiance was best approximated with an effective albedo of 100 % ocean during these months (Fig. 3) and used in the analysis. Since algae are found on coastal snow and glacial margins during summer months, using a 100 % snow albedo for radiative transfer simulations may overestimate the clear-sky flux.
The formulation does not have exact spectral weighting between albedo and irradiance because the daily insolation was already calculated for integrated photosynthetically available radiation (PAR) following Dierssen et al. (2000). The flux was estimated using average albedos and daily irradiance following
where Ed,vis (W m−2) is the daily average irradiance integrated across visible wavelengths (400–700 nm). Algal albedo avis,algae values were estimated as the individual means for the green and red algae, respectively, across all sites and avis,clean is the mean for the clean snow sites.
Statistical tests were conducted in MATLAB®. Arithmetic means were calculated and shown with plus or minus the standard deviation, unless otherwise indicated. A one-way repeated-measure analysis of variance (ANOVA) was used to evaluate the impact of different types of snow on the albedo with a significance level of 0.05. The central mark on the boxplot indicates the median, and the bottom and top edges of the box indicate the 25th and 75th percentiles, respectively. The whiskers extend to the most extreme data points not considered outliers, and the outliers are plotted individually using the “+” symbol. Model II simple linear regression analyses were conducted to account for uncertainty in both the x and y variables.
Spectral reflectance varied across all sites in a consistent manner with snow and algae composition (Fig. 4a–d). The reflectance of visibly clean snow was greater than 0.80 in visible wavelengths and decreased into the near-infrared (NIR) wavelengths typical of snow spectra (Ganey et al., 2017). For most of the clean-snow spectra, the reflectance was spectrally flat across the visible wavelengths consistent with “white” snow. Several of the stations at Collins Bay, however, exhibited increasing reflectance across blue and green wavelengths possibly due to the presence of impurities like dust (Mauro et al., 2015) or other detrital matter. For all of the sites, the addition of light-absorbing algal pigments decreased reflectance in visible wavelengths. The spectral reflectance of green snow algae was consistently lower than red algae, and mixed algae fell in between the two types. Albedo integrated across visible wavelengths (400–700 nm) ranged from 0.31 at a green snow algae site on Nelson Island to 0.87 from a clean snow site at Collins Bay on King George Island (Table 1, Fig. 4e). The lowest (average ± standard deviation) albedo in the visible wavelengths was for green snow algae patches (0.44±0.12), followed by mixed snow algae patches (0.58±0.064) and red snow algae patches (0.65±0.09), and the highest albedo was at the clean snow sites (0.85±0.043). A one-way between-subject ANOVA conducted to compare the effect of snow algae on visible albedo found a significant effect at the p<0.05 level for the four conditions [, ].
In contrast to visible wavelengths, no impact of algae on near-infrared wavelengths was observed. All of the spectra tended to be very similar in near-infrared wavelengths from 700–1300 nm with local minima related to water absorption features with the exception of two stations. The very low albedos in the NIR observed in the green snow algae patches on Nelson Island may have been influenced by the underlying ground due to a thin snowpack at these locations (7 and 8 cm, Table 1). The optical signal from the dark underlying ground likely contributed to lower values in the NIR wavelengths (∼0.29). With the exception of these two optically shallow stations, the NIR albedos from 700–1300 nm were similar across the different snow types such that the mean NIR albedo calculated from 700–1300 nm ranged only from 0.45–0.46 (Fig. 4f, Table 1). A one-way between-subject ANOVA conducted to compare the effect of snow algae on NIR albedo was not significant at the p<0.05 level for the four conditions [, p=0.86]. This result is consistent with light absorption by photosynthetic pigments influencing the visible or PAR and having no impact on the NIR albedo. The 15 % reduction in NIR albedo due to thin snow at the Nelson sites, however, illustrates the challenges in remote sensing LAPs in snow, such as black carbon compared to thin snow (Warren, 2013).
The 20 % reduction of visible albedo by red snow algae observed in this Antarctic study is roughly in the same range as Lutz et al. (2016), who reported a 13 % albedo reduction caused by red snow algae in the Arctic. However, measurements in this study were collected from coastal Antarctic snowpacks, whereas the study in the Arctic was conducted on glaciers, which could lead to overall albedo differences due to dissimilarities in physical snow conditions. Our spectral measurements were most similar to those of Ganey et al. (2017), who show a similar decrease in reflectance in visible wavelengths and minimal impact in NIR wavelengths. In contrast, Gray et al. (2020) show a marked difference in visible and NIR reflectance for two measurements of hemispherical directional reflectance (HDRF) shown in their Fig. 2 but less so in the spectra in Fig. 2 in their Supplement. Painter et al. (2001) found a slight decrease in albedo in the NIR that was not observed for the thick snow samples assessed here. Differences in NIR reflectance will be impacted by snow thickness and liquid water content of snow, but our results show no significant difference due to the presence of snow algae itself.
The concentration of pigments followed a large range across sites from less than detection limits in clean snow to nearly 100 mg ChP m−2 found in a green snow algae patch on Nelson Island (Table 1). Consistent with past studies on Antarctic snow algae (Davey et al., 2019), pigment concentrations were overall much higher in green patches compared to red ones. Our chlorophyll a plus phaeopigment concentrations ranged from 0.001 to 0.03 mg ChP m−2 in visibly “clean” snow, 0.12 to 7.82 mg ChP m−2 in red snow patches, 4.22 to 14.38 mg ChP m−2 in mixed snow algae, and 8.82 to 141.78 mg ChP m−2 in green snow algae patches (Table 1).
The estimated absorptance (A) by snow algae reveals distinct patterns of broad absorption in the blue or soret band (400–500 nm) and a secondary peak in red wavelengths (678 nm) common to all algal groups (Fig. 5a). For these groups, green and mixed algae have a higher magnitude of A than red algae due to enhanced pigment concentrations in green algae. The spectral shape of A normalized at 440 nm reveals that absorption by red algae is higher in the green wavelengths (500–570 nm) compared to green algae (Fig. 5b). This spectral difference is due to the enhanced concentrations of the ancillary carotenoid pigment astaxanthin (Davey et al., 2019) which absorbs in far blue and into green wavelengths of light, leading to a red color. The red color of astaxanthin has also been shown to play an adaptive role in melting snow and ice in order to make water and nutrients available for algal growth (Dial et al., 2018). Enhanced absorption due to carotenoids at 550 nm provides a means to discriminate between red and green algae using the reflectance spectrum (see below). When absorption is normalized to pigment concentration, the red algae absorb considerably more per milligram of ChP compared to mixed or green algae (Fig. 5c). This difference is partly due to red algae having less chlorophyll a compared to carotenoids (Davey et al., 2019). When normalized by an estimate of both ChP and ancillary pigment (red dotted line Fig. 5c), pigment-specific A is 3 times lower but still higher than that for green algae. Differences in algal light absorption can also arise from differences in light adaptation, size, packaging within the cell and other factors (Kirk, 1991). A more thorough study on algal light utilization in relationship to these factors in different types of snow algae is warranted. Future work will better elucidate whether the reduction of albedo is higher for green patches due to pigment concentrations or cell abundance.
The impact of snow algae on RF is dependent on a variety of environmental factors including the location, seasonality, day length, duration of algal bloom and atmospheric conditions including cloudiness of the region. Here, we evaluate radiative forcing in two ways: (1) using clear-sky instantaneous estimates of solar radiation and (2) using long-term measurements of daily radiative forcing at this location. The latter approach is particularly important because it represents a more conservative and realistic treatment of the impact of algae in this region based on the local cloud climatology. Importantly, these results are not dependent on the specific areal extent of each type of algae, but they represent the radiative forcing per patch of algae detected in any location in the region and can be scaled to the average radiation available during a particular time in the growing season.
The instantaneous RF (IRF) produced under clear skies was greater than 200 W m−2 at high algal concentrations (Fig. 6a). The average IRF for green communities is more than double that of red communities (Table 1). These results from Antarctica are similar to the only other estimates we could find of IRF, by red snow algae on an Alaskan ice field (Ganey et al., 2017), but here the relationship between IRF and pigment concentration was found to be logarithmic (Fig. 6b), explaining 70 % of the variability in IRF. Although the role of microbes in surface darkening has been documented on the Greenland Ice Sheet, e.g., Stibal et al. (2017), the associated RF has not been explicitly reported (Skiles et al., 2018). To our knowledge, Ganey et al. (2017) is the only other study to document the RF due to snow algae. Thus, our results are some of the first studies to document the RF by snow algae in Antarctica and using realistic environmental conditions in the region.
Clouds are extremely prevalent in this region of the Antarctic and clear-sky IRFs do not accurately represent the daily RF caused by snow algae. These sites, for example, were all measured under cloud-covered conditions that were prevalent throughout the sampling period. Following a previous study on dust (Bryant et al., 2013), mean daily RF was calculated based on historical hourly measurements of PAR at Palmer Station (Dierssen et al., 2000; Fig. 6c). Since algae had little impact on NIR albedo, the use of PAR (400–700 nm) is considered suitable for this analysis. As shown, daily PAR varied considerably from clear-sky conditions, with the austral spring tending to be clearer relative to austral Fall (Fig. 6c). The calculated average RF per square meter patch of green and red snow algae varied throughout the course of the growing season with the mean RF by green algae close to 20 W m−2 with a maximum up to 60 W m−2 (Fig. 6d). Mean daily RF was highest around ordinal day 300 and declined after day 350. Gray et al. (2020) estimated a 122 d growing season. Here, we report daily radiative forcing over a 118 d growing season from ordinal day 352 (18 December in non-leap years) to ordinal day 105 (15 April in non-leap years), and found the mean RF is 26 W m−2 for green algae and 13 W m−2 for red algae. Maximums approached 40 W m−2 for green algae and 20 W m−2 for red algae at the height of the summer (Fig. 6e). Bryant et al. (2013) found that annual forcing from dust in snow ranged interannually from 20 to 80 W m−2. Further, a snowmelt radiative transfer modeling study that simulated the dust-influenced snow cover evolution found that a daily mean average RF of 30 W m2 advanced seasonal snowmelt by 30 d (Skiles and Painter, 2019). Hence, our mean daily RF results of 26 W m−2 during the austral summer growing season for green algae suggest snow algae in the polar regions is on par with that from dust in more temperate regions and has the potential to drastically alter snowmelt and regional hydrology, warranting further investigation.
The growing season for snow algae has not been well-documented in this region. However, the requirement for liquid water for growth suggests the prevalence of snow algae may be greater in late summer and early austral fall as the region warms. As shown, the radiative impact will be less in this time of the year (ordinal day 0–60) due to declining day length and relative increase in cloud cover. However, snow algae observations have also been shown to increase under cloudy skies vs. days with intense sunlight due to a decrease in the degree to which the algae associate with the water surface, thereby increasing the number of algae being removed from the top layer of snow by meltwater runoff during days with intense solar radiation (Grinde, 1983). Therefore, the timing and duration of red and green snow algae presence and their impact on RF in this region of Antarctica should be further explored. Lastly, previous results of low concentrations of BC in snow in the AP region (Khan et al., 2019) and elsewhere on the continent suggest BC is not a driver of RF in the region outside of the proximity of field stations.
Many different heritage algorithms have been proposed for assessing algal pigment concentration from the reflectance spectrum. Our data show that light absorption by the snow algae is highly correlated to the logarithm of pigment concentration (Fig. 7a). Similar to ocean microalgae (Dierssen and Randolph, 2013), the relationships follow a logarithmic function with pigment concentration. As shown in Fig. 7a, the amount of blue reflectance (Sentinel Band 2 490 nm) explains 85 % of the variability of the logarithm of ChP. For remote sensing purposes, using the absolute magnitude of reflectance is problematic due to issues with atmospheric correction and impurities. The amount of blue absorption relative to green (R560–R490) is also a similarly good predictor of ChP pigment and is more robust to such issues whereby the difference between Band 4 (560 nm) and Band 3 (490 nm) explains 83 % of the variability in pigment (Fig. 7b). Following Painter et al. (2001) and Gray et al. (2020), we also relate our pigment concentration to a scaled integral of Sentinel Band 4 (Eq. 2). Linear regression of the scaled integral of Sentinel-2's Band 4 (664 nm) relative to Bands 3 (560 nm) and 5 (704 nm) provides predictive power to estimate higher concentrations of ChP (>0.5 mg m−2) and can be applied when IB4 is >0 (Fig. 7c). However, the relationship is not consistent across the full range of data shown. Gray et al. (2020) also note that red algae can alter the derived relationship compared to green algae.
Differentiation of green and red algae can be optically achieved by exploiting the differences in green and red band reflectance. Differencing between Sentinel Bands 3 and 4 using red and green algae spectra shows smaller values compared to green algae or clean snow. Figure 7d and e illustrate how the difference in these three populations (red, green and clean snow) can be separated with the bands in Sentinel-2. However, we note this study lacks spectra from low concentrations of green algae where the red and green algae populations would overlap.
Due to persistent cloud cover in this region, we were unable to obtain suitable imagery concurring with our sampling time. While we have focused on Sentinel-2 because of its high spatial and temporal resolution and heritage approaches for remote sensing of snow algae, these approaches could be easily converted to other sensors with different spatial and spectral resolutions. The approaches using only blue, green and red bands are robust and could be applied to other sensors like Landsat-OLI and PlanetScope. Additional spectral capabilities from sensors like WorldView-2 and WorldView-3 and hyperspectral sensors could provide the opportunity to further quantify ancillary pigments and other ecological parameters of the algae.
Snow algae are highly dependent on their habitat conditions (e.g., radiation, water availability and temperature) and are generally dormant over winter, coming to life as snow begins to melt because the water brings nutrients, often from guano deposits within the snow. Therefore, it is likely that the snow algae growing season is responsive to climatic changes. As demonstrated here and in previous studies, snow algae reduce surface albedo by absorbing more solar radiation than the surrounding snow and ice. This potential bioalbedo feedback (Cook et al., 2017) is not currently accounted for in global climate models. Furthermore, it could be significant in polar climates where marginal snowpack areas are extensive and retreating (Benning et al., 2014; Hodson et al., 2017; Tedesco et al., 2016).
Finally, we present a cursory calculation of the overall RF by red and green snow algae in the AP region by taking the Gray et al. (2020) green snow algae surface area estimate of 1.9 km2 for the northern AP and our average daily RF calculation of 26 W m−2 by green snow algae and 13 W m−2 for red snow algae. This results in a total daily RF by green snow algae of 50 and 24 MJ by red algae. Although the timing and duration of snow algae blooms are not well-documented, if we assume a 118 d growing season from 18 December to 15 April, this translates to a seasonal increase in energy absorbed at the snow surface of 51×107 MJ per season by green snow algae and 25×107 MJ per season by red snow algae over the northern AP study region. Furthermore, if 334 000 J is needed to melt 1 kg of snow (Cohen, 1994), this results in roughly 1.53 Mt or 2522 m3 of snow melted by green-colored algae and 0.74 Mt or 1218 m3 of snow melted by red-colored algae, a serious impact on snow in the algae-covered regions versus adjacent areas. Compared to the total annual regional melt it should be noted that we think the spatial and temporal distributions of green and red snow algae are not equal throughout the growing season and should also be further investigated. As the climate warms, the spatiotemporal distribution of red and green algae along the northern AP will change, likely growing in latitudinal and landward extent, increasing the RF effect. Lastly, the impacts of RF by snow algae on snowmelt in the AP region are not currently accounted for in estimates of Antarctic ice-free habitat expansion (e.g., Huss and Farinotti, 2014; Lee et al., 2017). Our calculations above suggest snow algae play a significant role in snowmelt in the AP regions where they occur, which could be amplified in the future as the climate warms.
This study builds on past studies, providing additional insight into the spectral differences in Antarctic snow impacted by red and green algae, as well as presenting some of the first RF estimates of red and green coastal Antarctic snow algae using realistic solar forcing. The cloudiness of the region makes it extremely challenging to accurately model in terms of radiative transfer and from satellites that require clear skies. We show, however, that even with cloud cover, the mean daily RF in visible wavelengths due to the presence of snow algae is on par with that published for dust impacts in Colorado and much greater than BC impacts in the Arctic (Painter et al., 2012; Skiles et al., 2018; Skiles and Painter, 2019). Further, the average IRF and mean daily RF for green communities is more than double that of red communities. These values suggest the impact on long-term RF in polar ecosystems through altered snowmelt and regional hydrology, as well as the need to map and monitor red and green snow algae communities.
We also demonstrate the potential to map the spatial and temporal distributions of red and green snow algae using optical signatures of enhanced green absorption by the red algae compared to the green. Future studies could further explore the range of green and red algal pigment concentrations and applicability of these approaches to satellite imagery. Eventually, these mapping algorithms may be used to track expansion of algal bloom extent and pigment content and determine other climate and ecosystem factors controlling algal growth. The ultimate benefit of using satellite imagery will be the ability to monitor spatial and temporal changes across larger areas of the cryosphere. The expansion of these techniques to estimate ancillary pigment concentrations will also be possible with future hyperspectral sensors, e.g., NASA's Plankton Aerosol and ocean Ecosystem (PACE) and Surface Biology and Geology (SBG) missions.
The AP experienced significant warming in the last several decades of the 20th century, with the hottest day on record (18.4 ∘C) recently recorded at Esperanza Station on 6 February 2020 in the AP region (Robinson et al., 2020). The warming trend and persistently warmer conditions in the AP could be resulting in more snow algae growth in coastal areas, which in turn could have a positive feedback on surface albedo and melting. The potential feedback from the RF of red and green snow algae outlined here should be accounted for in global climate models in order to properly account for snowmelt and ice edge retreat, which could be significant in this region of Antarctica, especially as the climate continues to warm. Additionally, it is likely that the snow algae bloom season is being extended due to warming temperatures. These data may eventually be used for algorithms that could help facilitate an understanding of the spatial and temporal variability of red and green snow algae in this changing region. Furthermore, snow algae contribute to net primary productivity (NPP) and carbon biogeochemistry. Further research can explore methods relating pigment concentrations with NPP of snow algae. This study contributes to the understanding of this natural phenomenon in the cryosphere and the feedbacks to radiative forcing in the AP.
All data for this publication are included in this paper, with the exception of the spectral albedo data which are available as dataset ID 601412, https://doi.org/10.15784/601412 (Khan, 2020), through the US Antarctic Data Center for Data archiving: https://www.usap-dc.org/view/dataset/601412 (last access: 21 December 2020).
ALK conceived of the study and collected the snow samples. ALK and HD analyzed the spectral albedo and pigment data and conducted the absorptance and radiative forcing analyses. HD provided the Palmer Station irradiance data. ALK, TS and RRC contributed to the study design. JH analyzed the chlorophyll samples. ALK, TS and HD contributed to the data analysis, algorithm development and interpretation. All authors contributed to writing and editing of the manuscript.
The authors declare that they have no conflict of interest.
Alia L. Khan was supported by a Fulbright Scholarship with the Chilean Antarctic program. ALK and TS were supported by a Landsat Science Team award to T. Scambos, USGS contract no. 140G0118C0005. Heidi Dierssen acknowledges funding from NASA Ocean Biology and Biogeochemistry PACE Science Team; RRC acknowledges the support of the Consejo Nacional de Ciencia y Tecnología (CONICYT, Preis Fondecyt 1191932 & 1171690) and the Chilean Antarctic Institute (INACH, Preis RT32-15 & RT70-18). Juan Höfer was supported by CONICYT (FONDAP-IDEAL 15150003) and FONDECYT (POSTDOCTORADO 3180152). The authors appreciate help from Edgardo Sepulveda and Nicole Torres, as well as preliminary discussions on this work with Pete Convey at the British Antarctic Survey and Matthew Davey at Cambridge University.
This research has been supported by the Fulbright U.S. Scholar Program (Chilean Antarctic Institute), the United States Geological Survey (grant no. 140G0118C0005), NASA (grant no. Ocean Biology and Biogeochemistry PACE Science Team), the Consejo Nacional de Ciencia y Tecnología (CONICYT) (grant nos. 1191932 and 1171690), the Chilean Antarctic Institute (INACH) (grant nos. RT32-15 and RT70-18) and the CONICYT (grant nos. 15150003 and 3180152).
This paper was edited by Christian Haas and reviewed by Yangyang Liu and one anonymous referee.
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