Introduction
Ice algae within or attached to the sea-ice bottom provide an important food source in arctic marine food webs from sympagic and pelagic zooplankton to marine mammals as well as seabirds (Søreide and others, Reference Søreide, Leu, Berge, Graeve and Falk-Petersen2010; Daase and others, Reference Daase2013; Van Leeuwe and others, Reference Van Leeuwe2018; others therein). Although their contributions as primary producers appear to vary regionally from <1% in seasonal ice-covered shelf areas up to ~60% in the central deep Arctic Ocean (Gosselin and others, Reference Gosselin, Levasseur, Wheeler, Horner and Booth1997; Lee and others, Reference Lee2015; Song and others, Reference Song2016), ice algae play an ecologically critical role as a primary food source for the arctic marine ecosystem in spring (Lee and others, Reference Lee2011; Leu and others, Reference Leu2015). Ice algal blooms are prominent prior to the pelagic spring bloom in the early arctic summer (Apollonio, Reference Apollonio1965; Legendre and others, Reference Legendre1992; Michel and others, Reference Michel, Legendre, Ingram, Gosselin and Levasseur1996; Lee and others, Reference Lee, Whitledge and Kang2008; Leu and others, Reference Leu2015). A potential fall bloom after the phytoplankton blooms in late summer can also extend the short arctic summer production period and provide late-season food complements before the long dark winter (Lee and others, Reference Lee2011). These spring and fall blooms of ice algae prolong the production season of overwintering grazers in the Arctic Ocean (Michel and others, Reference Michel, Legendre, Ingram, Gosselin and Levasseur1996; Lee and others, Reference Lee, Whitledge and Kang2008, Reference Lee2011; Fernández-Méndez and others, Reference Fernández-Méndez2014). Moreover, the diatom-dominant ice algal community contains large amounts of high-quality polyunsaturated fatty acids which can be critical for successful egg production, hatching and larval development of sympagic herbivores (Leu and others, Reference Leu, Wiktor, Søreide, Berge and Falk-Petersen2010).
The bottom-ice algal community is generally the most productive sea-ice community in landfast ice zone fringing the Arctic Ocean (e.g., Smith and others, Reference Smith, Clement, Cota and Li1987; Renaud and others, Reference Renaud2007; Lee and others, Reference Lee, Whitledge and Kang2008; Campbell and others, Reference Campbell2016). Greater than 90% of chlorophyll-a (Chl-a) biomass of ice algae can be accumulated at the bottommost 0.03–0.05 m of the landfast sea ice (Smith and others, Reference Smith, Harrison, Harris and Herman1990; Lee and others, Reference Lee, Whitledge and Kang2008, Reference Lee, Jin and Whitledge2010; Campbell and others, Reference Campbell2016).
Recent changes in sea-ice conditions could have negative or positive impacts on ice-related organisms in the Arctic Ocean (Barber and others, Reference Barber2015; Tedesco and others, Reference Tedesco, Vichi and Scoccimarro2019). Moreover, greater precipitation and earlier snow-melt onset projected for the Arctic (Lynch and others, Reference Lynch, Curry, Brunner and Maslanik2004) could change the timing of ice algal spring blooms (Lavoie and others, Reference Lavoie, Denman and Michel2005; Lee and others, Reference Lee, Whitledge and Kang2008). However, the response of the bottom-ice algae to these changes in sea-ice and snow conditions could be diverse with latitudinal dependency (Castellani and others, Reference Castellani, Losch, Lange and Flores2017; Tedesco and others, Reference Tedesco, Vichi and Scoccimarro2019). Currently, a relatively sparse number of in situ field observations of ice algal production hinder our understanding of their responses to the current and ongoing environmental changes in previously ice-covered regions (Gradinger, Reference Gradinger2009; Lee and others, Reference Lee, Jin and Whitledge2010). The objectives of this study are to: (1) describe the environmental characteristics of the landfast sea-ice zone near Cambridge Bay in Dease Strait, Canada; (2) estimate the primary production and the relative contribution of bottom-ice algae and pelagic phytoplankton during spring; and (3) evaluate the characteristics in macromolecular composition of ice algae and phytoplankton.
Material and methods
Study area
Ice and water samples were collected from the first year sea ice near the Finlayson islands located in Kitikmeot Sea of the Canadian Arctic from 26 April to 12 May 2017. Four stations were selected for regular sampling along a transect crossing a narrow constricted waterway based on Dalman and others (Reference Dalman2019), who observed evidence for an enhanced ocean-ice nutrient supply towards the centre of the Finlayson Islands (Fig. 1). However, due to logistical issues, not all stations were sampled consistently throughout the program. Sampling stations 1 through 4 started at a 33 km distance from Cambridge Bay, Nunavut (Fig. 1).
Fig. 1. Location of study area in Dease Strait, 2017.
Sampling
A hyperspectral cosine sensor (Satlantic HyperOCR) was employed to measure under-ice transmitted spectral irradiance. The sensor was positioned 1.5 m south of a 25 cm auger hole using an under-ice arm and snow was placed in the hole to minimize stray light contamination of the measurements. Spectral irradiance was integrated over 400–700 nm to obtain the estimates of transmitted photosynthetically active radiation. Because we did not measure light intensity at our incubation sites, the measured intensities were only used as a relative reference. Snow depths were measured from ten different locations around our sampling sites before collecting ice core samples. Sea-ice samples were extracted using a Mark II Kovacs core barrel (inner diameter = 9 cm) and sea-ice thickness was measured from the ice core hole. Bottom 0.1 m sections were collected in dark-insulated cooler jugs and transported to the laboratory for further processing and analyses. Two ice core bottoms collected from each sampling station were melted together slowly (without the addition of filtered sea water) in the dark at room temperature overnight. Surface water samples for phytoplankton were collected from the auger hole with a polypropylene bucket after removing all the fragments of the ice and stored in sterile LDPE collapsible water collection bottles. All the bottles were transported to the laboratory in a dark insulated box. Salinities of melted ice and sea water samples were measured with a YSI model 30 salinity meter (YSI, Yellow Springs, Ohio). The instrument was calibrated with 50 mS cm−1 conductivity standard (YSI Catalog# 3169) with an accuracy of ±0.1. To measure bulk nutrient concentrations (ammonium, nitrate + nitrite, phosphate and silicate), 500 mL of melted ice and water samples were filtered through 47 mm GF/F filters (nominal pore size = 0.7 μm). A total of 50 mL of each filtrate was placed in labelled conical tubes and stored in a −20°C freezer until analysis within 2 months using an Auto analyser (Quaatro, Bran + Luebbe, Germany) in the National Institute of Fisheries Science, South Korea.
Chl-a analysis
To measure the total Chl-a concentration of ice algae and phytoplankton, 50–200 mL of melted ice and water samples were filtered onto 25 mm GF/F filters. To determine size-fractionated Chl-a concentration, samples were passed sequentially through 20 and 2 μm Nucleopore filters (47 mm) and Whatman GF/F filters. Filters were stored in a freezer (below −80°C) until analysis using a Turner Designs model 10-AU fluorometer calibrated with commercially purified Chl-a standard after a 24 h extraction in 90% acetone at 4°C (Parsons and others, Reference Parsons, Maita and Lalli1984).
Analysis of macromolecular components in ice algae and phytoplankton
Subsamples of 100–150 mL melted ice and 1 L surface water samples were filtered onto 47 mm GF/F filters for the determination of macromolecular components of bottom-ice algae and phytoplankton samples. Filtered samples were stored at −60°C for later analysis at the Pusan National University in South Korea following methods from Bhavya and others (Reference Bhavya2019).
Carbon and nitrogen uptake measurements of ice algae and phytoplankton using stable isotope tracers (13c and 15n)
Immediately after extraction, the bottom 0.1 m sections of two additional ice cores were cut into several pieces and placed in 1 L polycarbonate incubation bottles for in situ incubation using stable isotope tracers following the method of Lee and others (Reference Lee, Whitledge and Kang2008). Each bottle containing one bottom core was topped up with 400 mL of cold filtered (GF/F) sea water for buffering and labelled carbon (NaH13CO3) with either nitrate (K15NO3) or ammonium (15NH4Cl) substrates was added. The uptake rates of ice algae were corrected for the volume of added filtered sea water. After isotope inoculations, the bottles were put back to the original position through the auger hole and then the incubation hole was covered with ice chunks and snow. In situ field incubations were performed for 3–4 h during the daytime. After the field incubation, incubation bottles were transported and the ice samples were thawed in the dark at room temperature within a couple of hours without adding any inhibitor. No significant uptake under the dark condition before filtering samples was observed based on the previous results from incubation experiments conducted at Barrow, Alaska (Lee and others, Reference Lee, Whitledge and Kang2008). Immediately after the samples were completely melted, 100 mL of incubated samples were filtered onto 25 mm GF/F filters. The filters were immediately frozen and stored in the freezer at −20°C until the preparation for mass spectrometric analysis at the Alaska Stable Isotope Facility (ASIF).
For phytoplankton incubation, water samples from underneath the sea ice were collected from the auger hole. After the inoculation of each stable isotope (NaH13CO3 and K15NO3 or 15NH4Cl), polycarbonate incubation bottles were tied to an anchor rope and lowered 1 m below the ice bottom for 3–4 h incubation. After in situ incubation, the bottles were transported to the laboratory in a dark insulated box and 150 mL of incubated water samples were filtered onto 25 mm GF/F filters. The filters were immediately frozen and stored in the freezer at −20°C for mass spectrometric analysis at the ASIF. The carbon and nitrogen uptake rates of bottom-ice algae and phytoplankton were calculated according to Hama and others (Reference Hama1983) and Dugdale and Goering (Reference Dugdale and Goering1967).
Results
Environmental factors
Snow depth and sea-ice thickness at sample sites averaged (±SD) 0.04 ± 0.01 and 1.49 ± 0.17 m, respectively, over the study period (Table 1). Generally, a thinner sea-ice thickness was observed at st.1 (1.34 ± 0.02 m) relative to that at the other stations. The average salinity of melted ice samples and surface waters were 7.4 ± 2.6 and 26.7 ± 2.5, respectively, with low variation over the study period. Light intensity below the sea ice ranged from 15.5 to 48.4 μmol m−2 s−1 with an average of 29.3 ± 8.1 μmol m−2 s−1. The average concentrations of ammonium, nitrate + nitrite, phosphate and silicate were 1.13 ± 0.33, 1.79 ± 0.42, 1.14 ± 0.36, and 2.18 ± 0.72 μM at the bottom section of sea-ice samples, respectively (Fig. 2). Surface sea water ammonium, nitrate + nitrite, phosphate and silicate concentrations averaged 0.96 ± 0.83, 2.96 ± 0.50, 0.74 ± 0.11 and 7.31 ± 1.38 μM, respectively (Fig. 3). Overall, higher phosphate concentrations were observed in the bottom 0.1 m section, whereas higher nitrate + nitrite and silicate concentrations were found in the water samples. However, no statistically significant difference of nutrients among the sampling stations was found in the bottom 0.1 m section of sea ice and surface sea water during this study period.
Fig. 2. The bulk nutrient concentrations at the bottom 0.1 m section of the sea ice at each sampling day in Dease Strait, 2017.
Fig. 3. The nutrient concentrations in surface water at each sampling day in Dease Strait, 2017.
Table 1. Environmental conditions of each sampling station over the study period in Dease Strait in 2017
Chl-a concentrations of bottom-ice algae and phytoplankton
Total Chl-a concentration of bottom-ice algae in the lowermost 0.1 m ranged from 8.95 to 65.33 μg L−1 with a mean of 31.78 ± 16.28 μg L−1 in this study (Fig. 4). Relatively higher Chl-a concentrations were observed at st.1 over the study, except on 28 April. In comparison, total Chl-a concentration of phytoplankton ranged from 0.29 at st.1 to 6.72 μg L−1 at st.3 with a mean of 1.27 ± 1.55 μg L−1, which was substantially lower than those of bottom-ice algae (Fig. 4). The different size-fractionated Chl-a composition of bottom-ice algae was not distinctly different among the four stations during this study. Overall, microalgal cells (>20 μm) accounted for 72 ± 8% of the bottom-ice algal community, followed by nanoalgal cells (2–20 μm, 26 ± 8%) and picoalgal cells (0.7–2 μm, 2 ± 1%) based on the size-fractionated Chl-a concentrations (Fig. 5). For the surface phytoplankton community, microalgal cells accounted for 51 ± 13%, followed by nanoalgal (43 ± 11%) and picoalgal cells (6 ± 6%) (Fig. 5).
Fig. 4. The Chl-a concentrations for bottom-ice algae (a) and phytoplankton (b) at each sampling day in Dease Strait, 2017.
Fig. 5. The contributions of size-fractionated Chl-a concentration to the total Chl-a concentration of bottom-ice algae (a) and phytoplankton (b) at each sampling day in Dease Strait, 2017.
Carbon and nitrogen uptake rates of bottom-ice algae and phytoplankton
The hourly carbon uptake rate of bottom-ice algae ranged from 0.21 to 2.17 mg C m−3 h−1 with an average of 0.97 ± 0.60 mg C m−3 h−1 from our productivity stations during the study period from 28 April to 12 May 2017 (Fig. 6). The maximum rate of bottom-ice algae at st.4 on 6 May (i.e., the 2.17 mg C m−3 h−1) appears to be an outlier. Without this outlier, there is a clear trend in the carbon uptake rate of bottom-ice algae from within the tidal strait to outside the tidal strait. In comparison, the rate of phytoplankton production ranged from 0.02 to 1.19 mg C m−3 h−1 with an average of 0.22 ± 0.37 mg C m−3 h−1 (Fig. 6b). Carbon uptake rates of bottom-ice algae were significantly (t test, p < 0.05, df = 16) higher than those of phytoplankton during the study. However, the assimilation rates for bottom-ice algae were relatively lower than those of phytoplankton. The assimilation rates for bottom-ice algae ranged from 0.01 to 0.09 mg C mg−1 Chl-a −1 h−1 (0.03 ± 0.03 mg C mg−1 Chl-a −1 h−1). In comparison, the assimilation rates of phytoplankton ranged from 0.01 to 0.30 mg C mg−1 Chl-a −1 h−1 (0.14 ± 0.09 mg C mg−1 Chl-a −1 h−1).
Fig. 6. The hourly carbon uptake rates for bottom-ice algae (a) and phytoplankton (b) at each sampling day in Dease Strait, 2017.
Nitrate and ammonium uptake rates of bottom-ice algae ranged from 0.38 to 4.31 mg N m−3 h−1 with an average of 2.22 ± 1.38 mg N m−3 h−1 and 1.09 to 3.41 mg N m−3 h−1 with an average of 2.80 ± 0.92 mg N m−3 h−1, respectively (Fig. 7). Generally, nitrate uptake rates of bottom-ice algae were different among stations, whereas the ammonium uptake rates did not greatly differ. The nitrate and ammonium uptake rate of phytoplankton ranged from 0.13 to 1.74 mg N m−3 h−1 with an average of 0.48 ± 0.51 mg N m−3 h−1 and 0.19 to 2.49 mg N m−3 h−1 with an average of 0.68 ± 0.71 mg N m−3 h−1, respectively (Fig. 8). Based on the nitrate and ammonium uptake rates measured in this study, relative nitrogen preference index (RPI; McCarthy and others, Reference McCarthy, Taylor and Taft1977) and f-ratios (nitrate uptake/sum of nitrate and ammonium uptake; Dugdale and Goering, Reference Dugdale and Goering1967) were calculated for the bottom-ice algae and phytoplankton. The RPINH4 averaged 1.7 ± 0.5 and 2.6 ± 0.7, and the mean f-ratios were 0.41 ± 0.11 and 0.41 ± 0.15 for bottom-ice algae and phytoplankton, respectively.
Fig. 7. The nitrate (a) and ammonium (b) uptake rates for bottom-ice algae at each sampling day in Dease Strait, 2017.
Fig. 8. The nitrate (a) and ammonium (b) uptake rates for phytoplankton at each sampling day in Dease Strait, 2017.
Macromolecular compositions of bottom-ice algae and phytoplankton
Averaged concentrations of total carbohydrates, proteins and lipids of particulate organic matter (POM) from the bottom-ice algal cores were 1.90 ± 0.66, 1.72 ± 0.70 and 4.14 ± 1.40 mg L−1, respectively (Fig. 9). Similar to the Chl-a concentration and carbon uptake rate, the average concentration of proteins and lipids were observed to be greater at st.1 than those at other stations, with the exception of carbohydrates. However, the relative contribution of each macromolecule to bottom-ice algae composition was similar among the different stations. In comparison, the concentrations of each macromolecule of POM from the under-ice water column (phytoplankton) were 0.34 ± 0.18, 0.08 ± 0.04 and 0.16 ± 0.08 mg L−1 for total carbohydrates, proteins and lipids, respectively (Fig. 10). Overall, the concentrations of each macromolecule measured in bottom-ice algae were significantly (t test, p < 0.05, df values for carbohydrates, proteins and lipids were 24, 19 and 19, respectively) higher than those of phytoplankton. The dominant component among the biochemical composition of bottom-ice algae was lipids, contributing 53 ± 7% to the ice algal POM, followed by carbohydrates (25 ± 6%) and proteins (22 ± 4%) (Fig. 9), whereas carbohydrates accounted for 59 ± 6% in phytoplankton POM, followed by lipids (27 ± 5%) and proteins (14 ± 5%) (Fig. 10).
Fig. 9. The carbohydrates (a), proteins (b) and lipids (c) concentrations and the average composition of each biochemical component of ice algae (d) during this study period in Dease Strait, 2017.
Fig. 10. The carbohydrates (a), proteins (b) and lipids (c) concentrations and the average composition of each biochemical component of phytoplankton (d) during this study period in Dease Strait, 2017.
Discussion
Chl-a concentrations of bottom-ice algae and phytoplankton
Microalgal cells (>20 μm) were the dominant size class (72 ± 8%) contributing to ice algal Chl-a concentration. These results are similar to that (78% microalgal Chl-a contribution) observed at Barrow, Alaska during the spring season in 2003 (Lee and others, Reference Lee, Whitledge and Kang2008), and the general case for the Arctic Ocean where the microalgal diatom Nitszchia frigida tends to dominate ice algal communities in numbers and biomass (Poulin and others, Reference Poulin2011; Van Leeuwe and others, Reference Van Leeuwe2018). In contrast, the relative microalgal cell abundance range of 6–38% observed in Campbell and others (Reference Campbell, Mundy, Belzile, Delaforge and Rysgaard2018) for the same region suggests the potential for significant interannual or spatial changes in algal community composition. Indeed, additional studies in the same region have reported a contribution of large pennate cells to the bottom-ice algal cell composition to be 45 to >80% (Dalman and others, Reference Dalman2019; Pogorzelec (Reference Pogorzelec2019)).
A large variation in bottom-ice areal Chl-a concentrations was observed across our sample sites, especially for st.1 and st.4 that were statistically different (t test, p < 0.05, df = 10). Mean Chl-a concentrations were 4.46 ± 1.94 and 2.19 ± 0.65 mg m−2 at st.1 and st.4, respectively. Although st.1 and st.4 are separated by only 5 km, water depths (st.1 ≈ 33 m, st.4 ≈ 80 m) differ greatly because of a sill located at st.1. The shallow sill between the islands constricts the tidal flow of water across the waterway, resulting in greater current speeds in excess of 0.2 m s–1 (Dalman and others, Reference Dalman2019). This tidal current likely increases the exchange of nutrients to the ice bottom and potential for the bottom-ice algal biomass accumulation at st.1. Moreover, tidal effects can also increase the transfer of heat and momentum between the ocean and sea-ice bottom (Widell and others, Reference Widell, Fer and Haugan2006), resulting in the observed thinner ice cover at st.1.
A comparison of bottom-ice Chl-a concentrations from various landfast sea-ice sites in the Arctic region shows that the average bottom-ice Chl-a concentration observed in our study falls within the lower end of the range previously reported for the Kitikmeot Sea (Campbell and others, Reference Campbell2016; Dalman and others, Reference Dalman2019; Table 2). We note that the lower Chl-a concentration of bottom-ice algae in our study could be influenced by the non-buffered melting process for bottom Chl-a concentration. However, maximum bottom-ice areal Chl-a concentrations in this study were relatively lower than those previously reported for other areas of the North American Arctic (Table 2). Although light availability controls ice algal bloom onset and early bloom development in spring, nutrient access is the primary factor determining the maximum potential for ice algal biomass accumulation (Cota and others, Reference Cota1987; Smith and others, Reference Smith, Harrison, Harris and Herman1990; Mock and Gradinger, Reference Mock and Gradinger1999). This is particularly true for the thin snow depths examined in our study. The ranges of N:P and N:Si ratio in the ice bottom were 1.63–4.22 (2.71 ± 0.75) and 0.70–2.20 (1.44 ± 0.45), respectively, during our study period. These ratios are lower than the Redfield stoichiometric ratio (mol:mol) of 106C:16N:15Si:1P, which represents the mean cellular composition of marine diatoms (Brzezinski, Reference Brzezinski1985). Rózańska and others (Reference Rózańska, Gosselin, Poulin, Wiktor and Michel2009) suggested the low N:P (1.5–2.0) and N:Si (0.3) ratios in surface waters could represent potential limiting conditions for bottom-ice algae. Moreover, Campbell and others (Reference Campbell2016) reported the nutrient ratios of N:P and N:Si of the bottom ice at 0.20 ± 0.19 and 0.20 ± 0.15, respectively, in Dease Strait. In the studies of Rózańska and others (Reference Rózańska, Gosselin, Poulin, Wiktor and Michel2009) and Campbell and others (Reference Campbell2016), only nitrate + nitrite concentrations were considered for their N:P and N:Si ratios. The lower ratios including NH4 concentrations in our study are consistent with nitrogen deficiency conditions for ice algal growth as suggested in both Campbell and others (Reference Campbell2016) and Dalman and others (Reference Dalman2019). The unique aspect of our study is the inclusion of ammonium concentrations to examine the role of recycled production in the system.
Table 2. Comparison of Chl-a concentration and carbon uptake rate of bottom-ice algae in the landfast sea ice among the different Arctic regions
a No-buffered melting procedure for Chl-a concentration and carbon uptake rate.
Nitrogen and carbon uptake rates of bottom-ice algae and phytoplankton
The ammonium RPI (RPINH4) of bottom-ice algae (1.7 ± 0.5) and phytoplankton (2.6 ± 0.7) in this study indicate that ammonium was potentially preferred compared to nitrate throughout the study period (McCarthy and others, Reference McCarthy, Taylor and Taft1977). Harrison and others (Reference Harrison, Thompson and Calderwood1990) also found higher RPINH4 (>1) of ice algae at Barrow Strait and in the Canadian Arctic. However, the RPI should be used carefully because it could be weakly related to the physiological preferences of marine algae (Dortch, Reference Dortch1990; Stolte and Riegman, Reference Stolte and Riegman1996; Underwood and Kromkamp, Reference Underwood and Kromkamp1999). Stolte and Riegman (Reference Stolte and Riegman1996) pointed out that the RPI could be used reasonably for comparing the utilization of a nitrogen compound under similar concentrations of ammonium and nitrate. Since the average concentrations of ammonium and nitrate in bottom ice and surface water were not considerably different during our observation period, the relative ammonium preference for bottom-ice algae and phytoplankton is assumed reasonable for our study (Stolte and Riegman, Reference Stolte and Riegman1996; Andersson and others, Reference Andersson, van Rijswijk and Middelburg2006).
The f-ratio is often used to present on the fraction of new (nitrate-based) production by an algal community and can be a function of the ice algal bloom stage (Harrison and others, Reference Harrison, Thompson and Calderwood1990; Lee and others, Reference Lee, Whitledge and Kang2008). In Barrow Strait of the Canadian Arctic, Harrison and others (Reference Harrison, Thompson and Calderwood1990) observed a large range in f-ratio varying from 0.89 at an early bloom stage to 0.08 at a late to post-bloom stage of bottom-ice algae. In general, microalgae prefer ammonium because it is a readily available form of nitrogen source (Dugdale and Goering, Reference Dugdale and Goering1967; McCarthy, Reference McCarthy and Morris1980; Alexander and Chapman, Reference Alexander and Chapman1981) and algae require energy to convert nitrate into ammonium in their cell bodies (Dortch and Postel, Reference Dortch, Postel, Landry and Hickey1989). The low f-ratios in our study demonstrate that a considerable amount of primary production of bottom-ice algae in the Dease Strait region is based on a regenerated production rather than on new production. The stagnant circulation of the region driven by high riverine input (McLaughlin and others, Reference McLaughlin, Carmack, Ingram, Williams and Michel2006) and the associated limited input of new nutrients from nearby modified Pacific waters (e.g., Carmack and others, Reference Carmack, Macdonald and Jasper2004) are the likely cause of the local nitrogen-deplete conditions. These depleted conditions also influenced carbon-based production.
The assimilation rates for bottom-ice algae and phytoplankton are considerably lower in this study than in earlier studies reported in Alaskan Arctic, Barents and Greenland seas (Table 3). In particular, higher assimilation rates for phytoplankton than that of ice algae were observed in this study, which is contrary to the pattern reported by Gosselin and others (Reference Gosselin, Levasseur, Wheeler, Horner and Booth1997). However, similar observations have been made for phytoplankton and bottom-ice algae near Barrow, Alaska (Lee and others, Reference Lee, Whitledge and Kang2008). Although the Chl-a concentration of bottom-ice algae was substantially higher than that of phytoplankton, the significantly higher assimilation rates observed in phytoplankton imply that the photosynthetic efficiency of bottom-ice algae was less than that of phytoplankton. This lower assimilation efficiency of bottom-ice algae also could indicate a greater nutrient limitation on their production compared to phytoplankton since a greater nutrient demand would be associated with the higher ice algal biomass (Cota and others, Reference Cota1987). Indeed carbon uptake rates of bottom-ice algae were noticeably lower in our study than that of previous studies conducted from the Canadian Arctic Archipelago (Table 2). The ranges of carbon uptake rate in the high Canadian Arctic (Resolute Passage) by Smith and others (Reference Smith, Anning, Clement and Cota1988) and Smith and Herman (Reference Smith and Herman1991) were 21–463 and 20–157 mg C m−2 d−1 during the spring times in 1985–1986 and 1987–1988, respectively. Nozais and others (Reference Nozais, Gosselin, Michel and Tita2001) and Michel and others (Reference Michel, Nielsen, Nozais and Gosselin2002) also reported higher carbon uptake rates ranging from 26 to 317 mg C m−2 d−1 and 2 to 153 mg C m−2 d−1 at the Baffin Bay located in Canadian Arctic, respectively.
Table 3. Comparison of assimilation rates of ice algae and phytoplankton among the different Arctic regions
Unit: mg C mg−1 Chl-a −1 h−1. N.D. represents no data.
The high RPINH4 value, and low f-ratios, assimilation rates and carbon-based production estimates all strongly support the limitation of nitrogen in the Kitikmeot Sea, particularly for the ice algal bloom during spring. The observed lipid-dominant macromolecular composition of the bottom-ice algae further supports this conclusion. Aaronson and others (Reference Aaronson, Berner, Dubinsky, Shelef and Soeder1980) reported that the total lipid content of rapidly growing ice algae varies from 1 to 45% of the cell dry weight. The quantitative lipids of ice algae are influenced by environmental factors, mainly irradiance (Iwamoto and others, Reference Iwamoto, Yonekawa, AsAI and Nagahashi1955; Orcutt and Patterson, Reference Orcutt and Patterson1975; Fisher and Schwarzenbach, Reference Fisher and Schwarzenbach1978) and nutrients (Werner, Reference Werner1977; Shifrin and Chisholm, Reference Shifrin and Chisholm1981). Temperature could be one of the major factors for the more lipid accumulation in ice algae (Smith and Morris, Reference Smith and Morris1980; Guschina and Harwood, Reference Guschina and Harwood2006) compared to phytoplankton. However, the difference in temperature between bottom ice and underneath surface water could be insignificant (Lee and others, Reference Lee, Whitledge and Kang2008) and thus temperature was ruled out for further discussion in this study. Generally, high lipid concentrations of ice algae can be explained by nutrient limitation (Lizotte and Sullivan, Reference Lizotte and Sullivan1992; Pogorzelec and others, Reference Pogorzelec2017), increasing irradiance (Smith and others, Reference Smith, Clement and Head1989) or stationary growth phase (Morris, Reference Morris1981). Smith and others (Reference Smith, Gosselin and Taguchi1997) found an increasing carbon allocation into lipids in arctic ice algae as their growth was slowed by nutrient depletion. There were no major changes in sea-ice thickness and light availability under sea ice during our short sampling period in 2017. Indeed, no strong relationship was observed between macromolecular compositions and the two environmental factors. The protein:carbohydrate ratio in ice algae can be an indication for the nitrogen availability condition. Our values, which were <1 (0.92 ± 0.35) indicate nitrogen deplete conditions (Mayzaud and others, Reference Mayzaud, Chanut and Ackman1989; Lizotte and Sullivan, Reference Lizotte and Sullivan1992; Danovaro and others, Reference Danovaro2000), in line with our earlier conclusions. It is noted that the lipid-dominant bottom-ice algal community observed in our study is consistent with that of Pogorzelec and others (Reference Pogorzelec2017) who found the transition in carbon allocation of bottom-ice algae from protein into lipid content under increasing light and depleting nutrient conditions for the same study region.
In contrast to the bottom-ice algal community, under-ice phytoplankton were carbohydrate-dominant during our study. In the northern Chukchi Sea, Kim and others (Reference Kim2014) and Yun and others (Reference Yun2015) reported higher lipid contents (>50%) than those of other macromolecular classes in phytoplankton, while in the Laptev and East Siberian seas, Ahn and others (Reference Ahn2019) observed carbohydrate-dominant phytoplankton. In fact, previous studies report that phytoplankton can produce more carbohydrates or lipids depending on nutrient conditions (Shifrin and Chisholm, Reference Shifrin and Chisholm1981; Harrison and others, Reference Harrison, Thompson and Calderwood1990; Hu, Reference Hu and Richmond2004; Ahn and others, Reference Ahn2019). Phytoplankton produce carbohydrates as a prime reserve product under nutrient-deplete conditions, whereas photosynthetic products can be diverted from the carbohydrates into lipid synthesis as secondary reserve materials under prolonged nutrient depletion conditions (Fogg and Thake, Reference Fogg and Thake1987; Hu, Reference Hu and Richmond2004; Ahn and others, Reference Ahn2019). Therefore, these data further support that phytoplankton were under less nitrogen-limiting conditions compared to that of the bottom-ice algal community during our springtime study.
Summary and Conclusions
In this study, we summarized the physical, chemical and biological characteristics of the bottom landfast sea ice near Cambridge Bay in Kitikmeot Sea during the late spring season from 26 April to 12 May 2017. Our results strongly support that the region is nitrogen-deplete with low algal biomass standing stocks and a low potential for new primary production. With an averaged f-ratio of 0.41, ammonium was demonstrated to be a major nitrogen source for the growth demand of both bottom-ice algae and phytoplankton communities. However, lower assimilation rates and a greater lipid-dominant biochemical composition suggest bottom-ice algae were under greater nutrient limitation in a likely post-bloom state relative to the more carbohydrate-dominant phytoplankton that had yet to undergo their spring bloom. To better understand and verify these findings, more seasonal field observations with a sufficient spatial resolution and longer duration in the Kitikmeot Sea are suggested since we found a significant spatial difference in Chl-a concentrations and our sampling period likely encompassed a post-bloom state of the bottom-ice algal spring bloom. The distinctively different biochemical compositions of bottom-ice algae and phytoplankton could be important with respect to its nutritional content for the foodweb. It is noted that lipids-dominant bottom-ice algae could be effective for a long-term energy reserve, whereas carbohydrates-rich phytoplankton could provide a short-term energy gain to potential grazers (Taipale and others, Reference Taipale2016; Ahn and others, Reference Ahn2019).
Acknowledgements
This research was supported by grants from the Korea Polar Research Institute for ‘Carbon assimilation rate and organic carbon cycle in sea ice-algal ecosystem’ (KOPRI; PE19170), the National Research Foundation of Korea (NRF) grant funded by the Korea government (MSIT; NRF-2019R1A2C1003515), Natural Sciences and Engineering Council of Canada (NSERC) Discovery and Northern Research Supplement grants to CJM, and field instruments supported by the Canada Foundation for Innovation. Lodging and laboratory access in Cambridge Bay, Nunavut, was supported by Polar Knowledge Canada through the Canadian High Arctic Research Station. We would like to express a particular gratitude to Dr. B. Else for logistical assistance assistance and as lead PI for a MEOPAR grant that partially supported the fieldwork. We thank the Ekaluktutiak Hunters and Trappers Organization and the community of Cambridge Bay, Nunavut, CA for supporting the research conducted during the 2017 ICE-CAMPS field campaign.
Open access
