Skip to main content

Is Oxygenation Related to the Decomposition of Organic Matter in Cryoconite Holes?

Abstract

Cryoconite is a sediment occurring on glacier surfaces worldwide which reduces ice albedo and concentrates glacier surface meltwater into small reservoirs called cryoconite holes. It consists of mineral and biogenic matter, including active microorganisms. This study presents an experimental insight into the influence of sediment oxygenation on the cryoconite ability to produce and decomposition of organic matter. Samples were collected from five glaciers in the Arctic and the European mainland. Cryoconite from three glaciers was incubated in stagnant and mechanically mixed conditions to imitate inter-hole water–sediment mixing by meltwater occurring on glaciers in Northern Hemisphere, and its effect on oxygen profiles and organic matter content. Moreover, we investigated short-term changes of oxygen conditions in cryoconite from four glaciers in illuminated and dark conditions. An anaerobic zone was present or approaching zero oxygen in all illuminated cryoconite samples, varying in depth depending on the origin of cryoconite: from 1500 µm from Steindalsbreen (Scandinavian Peninsula) and Forni Glacier (The Alps) to 3100 µm from Russell Glacier and Longyearbreen (Arctic) after incubation. Organic matter content varied between glaciers from 6.11% on Longyearbreen to 16.36% on Russell Glacier. The mixed sediment from the Forni Glacier had less organic matter than stagnant, the sediment from Longyearbreen followed this trend, but the difference was not statistically significant, while the sediment from Ebenferner did not differ between groups. Our results have implications for the understanding of biogeochemical processes on glacier surfaces, the adaptation of organisms to changing physical conditions due to abrupt sediment mixing, but also on the estimation of productivity of supraglacial systems.

Highlights

  • Anaerobic zones are common in cryoconite from the Northern Hemisphere glaciers

  • Effects of oxygenation on organic matter decomposition differ between regions

  • Cryoconite microorganisms are adapted to abrupt, stochastic processes

Introduction

Understanding the productivity of ecosystems around the world is important for the predictions of ongoing global changes (Plass 1956; Chapin III and others 2008). Fragile Arctic and mountain ecosystems are the most subjected to changes related to the recent melting of glaciers and other components of the cryosphere (Kaplan and New 2006). Oxygen availability in the ecosystem might be a direct representation of its productivity by comparing the balance of photosynthesis (oxygen production) and respiration (oxygen consumption) (for example, Odum 1956; Mulholland and others 2005). During aerobic respiration, the oxygen molecule has a higher reduction potential than the other terminal electron acceptor used in anaerobic respiration. Therefore, during anaerobic conditions, the decomposition of organic matter in the environment should be significantly slower (for example, Reddy and Patrick 1975; Kristensen and others 1995). However, this process directly depends on external factors, not only the presence of oxygen itself. Therefore, the aerobic respiration will not always result in increased organic matter decomposition. For instance, Henrichs and Reeburgh (1987) showed that the labile form of organic matter might be decomposed at similar rates during aerobic and anaerobic conditions in marine sediments. Similarly, the insignificance of bottom-water oxygenation in the organic matter preservation was shown by Pedersen and others (1992), while suggesting the importance of hydrodynamic factors. Therefore, the question of whether oxygenation increases decomposition, which has broad implication in the determination of flow of elements, remains still open. Previous research on the decomposition of organic matter in aerobic and anaerobic conditions has been carried out mostly in environments that are characterised by high complexity (for example, Canfield 1994; Hedges and Keil 1995). Here, we provide an experimental insight into understanding of the process of organic matter (OM) mineralisation in a relatively simple system occurring worldwide—cryoconite holes, which are biodiversity hotspots on glaciers. Taking into account that glaciers cover 10% of land surface and they are an important biotic and abiotic component of polar and mountainous ecosystems, the recognition of biogeochemical processes on glaciers is important to anticipate future changes in glacier adjacent habitats.

The cryoconite—dark biotic and inorganic matter on the ice surface, is a key element in nutrient cycling on glaciers (Figure 1; Säwström and others 2002; Cameron and others 2012; Stibal and others 2015). Its texture, size and composition are highly variable around the world ranging from loose sediments to spherical cryoconite granules (Rozwalak and others 2021). Cryoconite can be found dispersed across the ablation zone of glacier surfaces. However, depending on meteorological conditions and glacier topography, it may reduce albedo and melt the ice (Cook and others 2020), creating water-filled cavities called ‘cryoconite holes’ (Figure 1; McIntyre 1984; Hodson and others 2008). The continuous water flow through the cryoconite holes in the summer (with the exception of non-maritime glaciers in continental Antarctica, where cryoconite holes are constantly covered with an ice-lid; Fountain and others 2004) may result in an increased aeration of the sediment and increased supply of small particles of minerals or organic matter (Pautler and others 2013; McCutcheon and others 2021). Cyanobacteria, along with some eukaryotic algae, are responsible for most carbon and nitrogen fixation in the sediment (Stibal and Tranter 2007; Cameron and others 2012; Edwards and others 2013). Although their ecological opposite—heterotrophic bacteria constitute the majority of all heterotrophs: based on microbial counts (Margesin and others 2002) and relative reads of 16S rRNA gene copy number (Pittino and others 2018). The former dominates in the upper layer of sediment, while the latter dominates in the deeper layer (Telling and others 2012; Poniecka and others 2020). Even at the scale of cryoconite granule ecological communities assemble along the abiotic gradients: outer photic layers are dominated by photoautotrophs, while the dark interior is dominated by heterotrophs (Segawa and others 2020). Recent studies by Poniecka and others (2018) and Segawa and others (2020) showed that this spatial differentiation in microorganism distribution is directly reflected by the changes in aerobic conditions as a result of both differences in oxygen production (also related to the penetration of solar radiation) and consumption by organisms.

Figure 1
figure 1

In situ cryoconite holes from: A–GrIS, B–Longyearbreen, C–Forni Glacier.

We used two approaches to test whether the oxygenation of the sediment as a simulation of water flow on a glacier may result in increased decomposition of organic matter: indirect—by measuring oxygen along with a depth of the cryoconite thickness, and direct—by measuring the changes of OM. Taking into account that aeration of cryoconite after mixing is relatively short (Poniecka and others 2018), daily aeration of cryoconite in long-term could result in the decrease in OM, because of the high advantage of aerobic respiration in terms of energy efficiency. We measured oxygen in vertical profiles to determine whether the difference in the OM would be due to oxygen supply or stress experienced by the photoautotrophic community. The above actions could help to understand whether oxygen availability in the environment is one of the main factors which influence the organic matter decomposition on the glacier’s surface. Moreover, we present an insight into the understanding of the formation of anaerobic zones in cryoconite on four glaciers different in their biotic (photoautotrophic community composition, organic matter content) and abiotic (altitude, glacier thermal regime, cryoconite granule size) parameters. Finally, we present and discuss potential factors related to water flow through cryoconite holes that may influence the Net Ecosystem Productivity (NEP) of glaciers.

Material and Methods

Cryoconite Collection

The cryoconite samples for testing the effect of oxygenation on organic matter decomposition were collected on the three glaciers: one in Svalbard (Longyearbreen) and two in The Alps (Forni Glacier and Ebenferner). Moreover, to determine oxygen conditions in cryoconite, sediment was collected from four glaciers located in different altitudes, latitudes and elevation, differing in morphology, thermal regime and geological settings: Russell Glacier of Greenland Ice Sheet (hereafter GrIS), Longyearbreen (Svalbard), Steindalsbreen (Scandinavian Peninsula; Northern Norway), Forni (the Alps; Ortles Cevedale group). Detailed information on the sampled glaciers is presented in Table 1. The material was collected by a clean plastic pipette or stainless spoon into the plastic bags or 50-cm3 falcon tubes, then frozen and kept at -20ºC until further analysis. To reflect the biological and geological diversity of the sediment on the glacier scale, the final pooled sample consisted of material collected from several cryoconite holes.

Table 1 Sediment-Related Features of cryoconite used for determination of oxygen conditions

Experiment design

Initially, we incubated cryoconite to determine the variance in oxygen production and consumption between sampled glaciers (hereafter, the light conditions experiment). To do so, slowly melted and homogenised cryoconite was transferred to the beakers (7 beakers for each glacier, in each beaker 1 cm3 of cryoconite). These incubations were kept in dark conditions to acclimatise, in a cold room at 1–3 ºC. After 48 h, the oxygen concentration was measured in the vertical profiles (see “Oxygen measurements” Section for details). Next, the beakers were incubated for seven days in a 24 h/0 h light–dark cycle (The Russell Glacier, Longyearbreen and Steindalsbreen) or 12 h/12 h light–dark cycle (Forni Glacier) in order to reflect natural light availability. Then, the oxygen measurements were repeated in each beaker. Since the vegetative period on glaciers is rather short, we assumed that microbial communities in fully melted and open cryoconite holes are highly active from the beginning of the season, when the first holes form. Therefore, we considered a time span of one week sufficient to detect any significant changes in their activity.

A second experiment tested the effect of a mechanical disturbance of sediment to organic matter decomposition (Longyearbreen, Forni Glacier and Ebenferner) and oxygen conditions (Longyearbreen, Forni Glacier) (hereafter mechanical disturbance experiment). In the control group, 10 beakers per glacier were kept in stable condition (not mixed and not oxygenated), while in the experimental group 10 beakers per glacier were mixed (oxygenated) thoroughly and rapidly aerated by ambient air using Pasteur pipette for 15 s or mixed with glass rod once a day (all treatments have been treated by the same method at the same time). The beakers were incubated for eight weeks in a 12/12 h dark–light cycle for Forni Glacier and in a 24 h/0 h cycle for Longyearbreen. Moreover, independently, the sediment from Ebenferner was kept in similar conditions by eight weeks in a 24 h/0 h cycle. After this experiment, the organic matter content of each beaker was measured and compared with the organic matter content at the start of the experiment.

All above experiments were carried out in beakers with a capacity of 5 cm3, with a final sediment thickness of 4–6 mm. The outside of the beaker surrounding the cryoconite layer was covered with aluminium foil to mimic the light-reflecting ice surrounding cryoconite holes. Sediment was mixed with demineralised water with no microbial medium added. The water level was kept constant at approximately 3 cm by trickling in additional demineralised water down the beaker wall as required throughout the experiment. The photon flux density during incubation in the light conditions was equal to 50 μmol quanta s−1 m−2 of photosynthetically active radiation, while in the rest it was about 30 μmol quanta s−1 m−2.

Oxygen Measurements

Oxygen concentrations in the cryoconite were measured by a Clark-type oxygen micro-cathode (Revsbech 2021) with a tip diameter of 200 μm (Unisense, Denmark). In the light conditions experiment, the measurements began in the water ca. 500 µm above the sediment and continued every 200 μm until the anoxic layer was reached. At least four measurements were taken in the anoxic layer to assure that we did not encounter a local oxygen minimum. In the mechanical disturbance experiment (for Longyearbreen and Forni Glacier), the oxygen was measured from 3000 µm above the water and continued every 500 μm, until a depth of 4 mm into the sediment.

Prior to every measurement, the probe was left for 10 s which allowed the signal to stabilise. Afterwards, two to three measurements were made every 3 s. In the authors’ previous measurements, the procedure was repeated three times in each beaker per treatment, once in the middle of the beaker and twice close to the beaker wall to attempt to capture spatial variability in a community activity. However, the data clearly showed low spatial variation, thus in the mechanical disturbance experiment, only one profile was measured in the middle of the beaker. In total, 112 and 40 profiles were taken for the light and mechanical disturbances experiments. The measurements were logged using a Unisense Microsensor Multimeter and SensorTrace Profiling software (Unisense, Denmark).

Estimation of Organic Matter Content, Cyanobacteria and Algae Biomass, and Granules Size

After the light conditions experiment, the sediment in each beaker was separately homogenised and split into two portions, one for organic matter estimation, and the other for algae and cyanobacteria biomass estimation, whereas before the mechanical disturbance experiment, five replicates were taken from pooled sediment of each glacier to assess the organic matter content before incubation, which was compared with the final organic matter content in each tested beaker after eight weeks of incubations. The organic matter content was measured as a percentage weight loss through combustion at 550 °C for 3 h, following drying at 50 °C for 24 h (Wang and others 2011).

Biomass of algae for each incubated sediment was conducted in 5 technical replications. During qualitative analyses of cyanobacteria and algae were conducted under a light microscope, the taxonomy of species was based on Hindák (1996), Komárek and Anagnostidis (2005), Coesel and Meesters (2007). Quantitative analyses, individual cells or filaments, were done with a Nikon Eclipse TE2000-S digital microscope equipped with a Nikon DS-Fi1 camera. Calculating the biomass of phototrophs was conducted on the basis of cell volume measurements as presented in Pliński and others (1984). Only dominant taxa (> 0.0002 mg L−1) in particular cryoconite were taken into account for biomass analyses.

One pooled sample of cryoconite was analysed to measure the cryoconite granules' size. The sediment was suspended in the water and about 3 ml of it was transferred to a Petri dish with a pasture pipette. Then, all the visible granules were measured using a stereomicroscope with a camera (OLYMPUS SZ camera and Quick PHOTO CAMERA 3.0 software).

Statistical Methods

Altogether, two clear outliers resulting from measurement errors were removed from further analyses. Those measurements of oxygen concentration were higher than the other two measurements in technical replication by 500% and 2400%. For each experiment, the oxygen concentrations were averaged within each depth, then for all three profiles in a beaker (if present). As the oxygen concentrations did not reach zero but only approached it as a consequence of measuring error, a threshold for anaerobic conditions was set at 0.05 μmol L−1. To assess the total amount of oxygen in the measured zone of the beaker, we decided to use the definite integral of oxygen concentration as an approximated function of depth. To do it, we converted micrometre as depth to microlitre assuming that each measurement represented a ‘slice’ of the beaker with 10-µm depth. This approximation let us calculate the relative difference in oxygen amount, because all measurement in each experiment was done with the same method. Therefore, this approximation might be used only for comparison within experiments in this study, while it cannot be used in the direct comparison of oxygen amount with the other ecosystems.

In the mechanical disturbance experiment, the sediment coming from the Forni Glacier after about 4 weeks started to turn orange-brown, and the hydrogen sulphide smell was detectable. It was impossible to verify whether this originated from organisms in the sediment or was a result of contamination, thus the data about final oxygen measurements were removed from further analysis, while the organic matter data should be treated carefully during interpretation, the latter one might be partially related to the changes which were in the first 4 weeks of the experiment.

Linear mixed models were used to test whether the total oxygen amount and depth of the aerobic zone are different in dark and light conditions (possible applications of LMMs are presented in Jiang 2007). The first model (L1) included the depth at which the anaerobic zone started as the response variable, treatment (light vs dark) as a fixed effect and sample ID nested in glacier ID as random intercept effects. The second model (L2) included the total amount of oxygen (calculated as above) as the response variable, treatment (light vs dark) as a fixed effect and sample ID nested in glacier ID as random intercept effects. The total amount of oxygen was square-root transformed before the analysis to improve the normality of the model residuals. To assess whether oxygen amount and anaerobic zone depth differed in mechanical disturbances a two-sided t test was performed. Then, to test the differences between organic matter content in mixed and stagnated groups, we performed a Wilcoxon rank-sum test separately for each glacier. The choice of the test depended on the distribution of the variable and the homogeneity of the variance in the tested groups.

Linear mixed models were implemented in R 3.6.3 software (R Core Team 2020), using the glmmTMB package (Brooks and others 2017) and built-in functions. The identity-link function was used for Gaussian family models. Likelihood-ratio test was performed for models to identify whether the built model has significantly different goodness of fit than the null model. Finally, all models were checked for any violation of assumptions based on diagnostic plots.

Results

Profiles of oxygen concentrations are presented in Figures 2 and 3. In the light conditions experiment the oxygen concentration progressively decreased and reached an anaerobic status in all samples (Figure 2). The median depth of the anaerobic zone was 1800 µm (IQR = 650) in dark conditions and 1900 µm in light conditions (IQR = 1400). Results of model L1 have shown that the aerobic zone was deeper in the light condition than the dark (χ2 = 15.954, df = 1, p < 0.001). For the dark treatment, total oxygen amount was 0.265 µmol with 95% confidence interval (CI) [0.232, 0.297], while for the light it was 0.685 µmol 95% CI [0.528, 0.842]. Differences in the total oxygen amount between glaciers and treatments are presented in Figure 3. Model L2 showed that oxygen amount was higher in light treatment than in dark (χ2 = 32.98, df = 1, p < 0.001).

Figure 2
figure 2

Oxygen concentration profiles in the sediment for light and dark treatment separately for each glacier. Dots represent the mean value of oxygen concentration per each depth within the glacier-treatment sample, while whiskers represent standard error of the mean. The dashed line indicates the sediment surface.

Figure 3
figure 3

Total oxygen amount in a profile between treatments and glaciers based on raw data. Boxes denote 25th, 50th, and 75th percentiles while whiskers represent the lowest and highest datum within the 1.5 interquartile range of the lower and upper quartile. The dots represent jittered observation on the x- and y-axis.

In the mechanical disturbance experiment (Longyearbreen), the anaerobic zone was mostly absent; however, we stopped measuring oxygen at about 1 mm above the bottom of a beaker to avoid destroying the fragile sensor, so it is possible that we did not reach the anaerobic zone, which could be limited to the deepest 1 mm of sediment (Figure 4). The mean oxygen amount per beaker for the stagnant treatment was equal to 31.1 µmol 95% CI [28.9, 33.3], whereas for the mixed one it was 27.9 µmol 95% CI [25.9, 29.9]. The amount of oxygen in the stagnant treatment did not differ from that of the mixed (t = 0.82, df = 18, p = 0.43).

Figure 4
figure 4

Oxygen profiles and the comparison of organic matter decomposition between mixed and non-mixed treatment in mechanical disturbance experiment. Profiles: Dots represent the mean value of oxygen concentration per each depth within the glacier-treatment sample, while whiskers represent standard error of the mean. The dashed line indicates the sediment surface. Boxplots: Boxes denote 25th, 50th, and 75th percentiles, while whiskers represent the lowest and highest datum within the 1.5 interquartile range of the lower and upper quartile. The dots represent jittered observation on the x- and y-axis.

The difference in OM content between the start and the end of the experiment varied between glaciers (Figure 4). On the Arctic glacier—the Longyearbreen—organic matter content tended to be lower in the mixed sediments, but the difference was not significant (W = 27, p = 0.0887). In samples from Forni, the organic matter content was lower in the mixed than in non-mixed treatment (Forni: W = 17.5, p = 0.0155), whereas in Ebenferner samples there was no difference between groups (W = 50.5, p = 1).

Sediment from Russell Glacier consisted predominantly of granular cryoconite largely overgrown by filamentous cyanobacteria. The Longyearbreen cryoconite consisted of bright, large oval granules with smooth edges or granules degraded into fine particles looking like mud. Cryoconite from Steindalsbreen and Forni consisted mostly of irregularly shaped granules with some loose mineral particles. Summary of cryoconite granular size, mean organic matter content and photoautotrophic composition is provided in Table 1 and Supplementary Figures 1 and 2 (Except Ebenferner).

In each sample set, the biomass was dominated by a specific composition of photoautotroph species (Supplementary Figure 2). On GrIS, the dominant species counted was Porphyrosiphon natarisii Kützing ex Gomont 1892—filamentous cyanobacteria with very thick, firm, lamellated, brown sheaths. The biggest granules were observed in Longyearbreen, where the green algae Klebsormidium sp. dominated, occurring primarily as individual cells, not forming filaments. Filamentous species that occurred in the cryoconite from Forni were dominated by cyanobacteria Wilmottia murrayi (W. et G.S.West) together with Klebsormidium sp. forming filamentous structures. On Steindalsbreen, the dominant phototrophs were Klebsormidium sp. and Leptolyngbya sp. 3, but due to small cell size had a small share in the total biomass of photoautotrophic organisms in the sediment. Count data of cells are presented in Supplementary Table 2 (Except Ebenferner).

Discussion

Cryoconite samples used in this study came from five glaciers that differ in their topography and geographical position (the Arctic, subarctic and alpine regions). They also differ in organic matter content, photoautotrophic community composition, as well as dimensions of the cryoconite granules, and thus the size of pores between the sediment particles (Segawa and others 2017; Rozwalak and others 2021). The cryoconite variety is reflected in the oxygen conditions in the vertical profiles, both in the depth of the aerobic zone and in the total oxygen amount (Figures 2 and 3). Most samples became anoxic, but the depth at which this occurred varied between samples as well as between experimental treatments. The total oxygen amount was universally greater in the light samples, which testifies that our method of sample collection, preservation and incubation allow survival of phototropic community members. The results were consistent with those presented by Poniecka and others (2018) for GrIS as well Segawa and others (2020) for Ürümqi Glacier no. 1 in Central Asia. The maximum depth of the aerobic zone was no more than 1500 µm for Forni Glacier and Steindalsbreen cryoconite, while for the GrIS and Longyearbreen it reached 3100 µm depth (Figure 2). Neither organic matter content, photoautotrophic biomass nor its combination can clearly explain the difference between oxygen profiles inter glaciers. It proves that oxygen conditions in cryoconite are under the control of multiple factors. Nevertheless, the anaerobic zone occurs in the cryoconite from the Northern Hemisphere, and observed changes in OM content between glaciers and regions in both mixed and stagnant conditions have broad implications in understanding ecological and evolutionary processes shaping microbial communities on glaciers.

Implication for NEP of Cryoconite

In the samples from Forni Glacier, the decomposition of organic matter was higher in mixed treatment, for Longyearbreen the trend was consistent but not significant, while for Ebenferner differences between groups were not present (Figure 4). Our results suggest that intense water flow through cryoconite, which results in a mechanical disturbance of the benthic environment, could influence the decomposition of organic matter by aeration of the sediment, but this process has to be modulated by sediment-related factors. Canfield (1994), based on the observation of marine ecosystems, stressed that the advantage of aerobic OM decomposition or its lack does not have to be mutually exclusive, but it directly depends on the circumstance of organic matter deposition and its chemical composition. Kristensen and others (1995) showed that oxygen has a significant effect on the decomposition of old and complex organic matter, but not on fresh and labile organic form. These results were also supported by Hulthe and others (1998) on aged plant material buried in coastal sediment. Complex organic matter, unlike small particles that can be transported into bacterial cells, requires extracellular hydrolysis, which is an additional step depending on the aerobic conditions outside the cell and thus limits the degradation process under anaerobic conditions (Kristensen and others 1995; Qu and others 2021). Therefore, the diverse response of cryoconite to oxygenation by mechanical disturbance could be due to different microbial communities as well chemical and structural composition of deposited organic matter on the particular glaciers. On glaciers, where circumstances favour aerobic decomposition, final productivity of a glacier could be under the control of factors related to glacier features, which directly influence water flow and so oxygenation of the sediment (Figure 5). Further research is needed to reveal which external factors have the major effect on the above process on glaciers.

Figure 5
figure 5

Scheme presenting potential relationships influencing NEP of cryoconite by modulation of oxygen amount in the sediment.

Adaptation of Cryoconite Organisms to the Fast-Changing Environment

Lack of difference in oxygen conditions between mixed and non-mixed sediment, suggests that even if light availability is a key limiting factor of the photoautotrophic growth (Bagshaw and others 2016; Perkins and others 2017), the cryoconite photoautotrophs are adapted to live in such a fast-changing environment. It is also indirectly evident from the minor differences in oxygen conditions between mixed and stagnant sediment measured for Longyearbreen. It may indirectly testify that the evolution of microorganisms in glacial ecosystems was driven by stochastic processes. If the ancestors of glacier organisms were under the influence of stochastic processes, they might be selected directionally for diverse metabolism, while weakening the strength of the selection factor. Such adaptation has been also indirectly shown in Poniecka and others (2018), where the aerobic zone became anaerobic within 120 min after perturbation. Moreover, based on cryoconite from the Karakoram and the Alps, Franzetti and others (2016) used molecular tools to show that microbial communities in cryoconite holes are capable of using different carbon sources. Similar results were also found in microcosm experiments from Antarctica and the Himalaya (Sanyal and others 2018), and in incubations of Greenland, Svalbard and Antarctic samples (Poniecka and others 2020). These findings suggest the complexity of metabolic pathways in cryoconite which, contrary to our expectations, testify to the adaptation of these organisms to live in such conditions.

Conclusion

Cryoconite holes, although considered simple, turned out to be a complex system in which the decomposition of organic matter regulated by oxygen varies greatly between glaciers in the Northern Hemisphere. One of the main factors which likely shapes cryoconite productivity is water flow through sediment, which in turn can be modified by weather and topography of glacier. Moreover, sediment-related features like cryoconite granule size and morphology, microorganism community and chemical composition potentially modulate the decomposition of organic matter itself. Therefore, the cryoconite holes seems to be a good model in further research related to biogeochemical processes, abiotic–biotic relations connected with spatial changes, such as evolution in a fast-changing environment or decomposition of organic matter by microbial communities.

References

  • Bagshaw EA, Wadham JL, Tranter M, Perkins R, Morgan A, Williamson CJ, Fountain AG, Fitzsimons S, Dubnick A. 2016. Response of Antarctic cryoconite microbial communities to light. FEMS Microbiology Ecology: 92.

  • Brooks ME, Kristensen K, van Benthem KJ, Magnusson A, Berg CW, Nielsen A, Skaug HJ, Maechler M, Bolker BM. 2017. glmmTMB Balances Speed and Flexibility Among Packages for Zero-inflated Generalized Linear Mixed Modeling. The R Journal 9: 378–400. https://journal.r-project.org/archive/2017/RJ-2017-066/index.html

  • Cameron KA, Hodson AJ, Osborn M. 2012. Carbon and nitrogen biogeochemical cycling potentials of supraglacial cryoconite communities. Polar Biology 35:1375–1393.

    Article  Google Scholar 

  • Canfield DE. 1994. Factors influencing organic carbon preservation in marine sediments. Chemical Geology 114:315–329.

    CAS  Article  Google Scholar 

  • Chapin FS III, Randerson JT, McGuire AD, Foley JA, Field CB. 2008. Changing feedbacks in the climate–biosphere system. Frontiers in Ecology and the Environment 6:313–320.

    Article  Google Scholar 

  • Coesel PFM, Meesters KJ. 2007. Desmids of the Lowlands. Mesotaeniaceae and Desmidiaceae of the European Lowlands: KNNV Publishing, zeist, the Netherlands. p 351p.

    Book  Google Scholar 

  • Cook JM, Tedstone AJ, Williamson C, McCutcheon J, Hodson AJ, Dayal A, Skiles M, Hofer S, Bryant R, McAree O, McGonigle A, Ryan J, Anesio AM, Irvine-Fynn TDL, Hubbard A, Hanna A, Flanner M, Mayanna S, Benning LG, van As D, Yallop M, McQuaid JB, Gribbin T, Tranter M. 2020. Glacier algae accelerate melt rates on the south-western Greenland Ice Sheet. The Cryosphere 14:309–330.

    Article  Google Scholar 

  • Edwards A, Pachebat JA, Swain M, Hegarty M, Hodson AJ, Irvine-Fynn TD, Rassner SME, Sattler B. 2013. A metagenomic snapshot of taxonomic and functional diversity in an alpine glacier cryoconite ecosystem. Environmental Research Letters 8: 035003.

  • Fountain AG, Tranter M, Nylen TH, Lewis KJ, Mueller DR. 2004. Evolution of cryoconite holes and their contribution to meltwater runoff from glaciers in the McMurdo Dry Valleys, Antarctica. Journal of Glaciology 50:35–45.

    Article  Google Scholar 

  • Franzetti A, Tagliaferri I, Gandolfi I, Bestetti G, Minora U, Mayer C, Azzoni RS, Diolaiuti G, Smiraglia C, Ambrosini R. 2016. Light-dependent microbial metabolisms drive carbon fluxes on glacier surfaces. The ISME Journal 10:2984–2988.

    CAS  Article  Google Scholar 

  • Hedges JI, Keil RG. 1995. Sedimentary organic matter preservation: an assessment and speculative synthesis. Marine Chemistry 49:81–115.

    CAS  Article  Google Scholar 

  • Henrichs SM, Reeburgh WS. 1987. Anaerobic mineralization of marine sediment organic matter: rates and the role of anaerobic processes in the oceanic carbon economy. Geomicrobiology Journal 5:191–237.

    CAS  Article  Google Scholar 

  • Hindák F. 1996. Key to the unbranched filamentous green algae (Ulotrichineae, Ulotrichales, Chlorophyceae). Bulletin Slovenskej botanickej spoločnosti pri SAV. Bratislava. 77p.

  • Hodson A, Anesio AM, Tranter M, Fountain A, Osborn M, Priscu J, Laybourn-Parry J, Sattler B. 2008. Glacial ecosystems. Ecological Monographs 78:41–67.

    Article  Google Scholar 

  • Hulthe G, Hulth S, Hall PO. 1998. Effect of oxygen on degradation rate of refractory and labile organic matter in continental margin sediments. Geochimica Et Cosmochimica Acta 62:1319–1328.

    CAS  Article  Google Scholar 

  • Jiang J. 2007. Linear and generalized linear mixed models and their applications. New York, USA: Springer. p 257p.

    Google Scholar 

  • Kaplan JO, New M. 2006. Arctic climate change with a 2 °C global warming: Timing, climate patterns and vegetation change. Climatic Change 79:213–241.

    CAS  Article  Google Scholar 

  • Komárek J, Anagnostidis K. 2005. Cyanoprocaryota; Oscillatoriales II. A. B. Büdel, L. Krienitz, G. Gärtner, & M. Schagerl, editors. Süβwasserfora von Mitteleuropa 19. Müchen: Spektrum Akademischer Verlag. p1–759.

  • Kristensen E, Ahmed SI, Devol AH. 1995. Aerobic and anaerobic decomposition of organic matter in marine sediment: which is fastest? Limnology and Oceanography 40:1430–1437.

    CAS  Article  Google Scholar 

  • Margesin R, Zacke G, Schinner F. 2002. Characterization of heterotrophic microorganisms in alpine glacier cryoconite. Arctic, Antarctic, and Alpine Research 34:88–93.

    Article  Google Scholar 

  • McCutcheon J, Lutz S, Williamson C, Cook JM, Tedstone AJ, Vanderstraeten A, Wilson SA, Stockdale A, Bonneville S, Anesio AM, Yallop ML, McQuaid JB, Tranter M, Benning LG. 2021. Mineral phosphorus drives glacier algal blooms on the Greenland Ice Sheet. Nature Communications 12:1–11.

    Article  Google Scholar 

  • McIntyre NF. 1984. Cryoconite hole thermodynamics. Canadian Journal of Earth Sciences 21:152–156.

    Article  Google Scholar 

  • Mulholland PJ, Houser JN, Maloney KO. 2005. Stream diurnal dissolved oxygen profiles as indicators of in-stream metabolism and disturbance effects: Fort Benning as a case study. Ecological Indicators 5:243–252.

    CAS  Article  Google Scholar 

  • Odum HT. 1956. Primary production in flowing waters 1. Limnology and Oceanography 1:102–117.

    Article  Google Scholar 

  • Pautler BG, Dubnick A, Sharp MJ, Simpson AJ, Simpson MJ. 2013. Comparison of cryoconite organic matter composition from Arctic and Antarctic glaciers at the molecular-level. Geochimica Et Cosmochimica Acta 104:1–18.

    CAS  Article  Google Scholar 

  • Pedersen TF, Shimmield GB, Price NB. 1992. Lack of enhanced preservation of organic matter in sediments under the oxygen minimum on the Oman Margin. Geochimica Et Cosmochimica Acta 56:545–551.

    CAS  Article  Google Scholar 

  • Perkins RG, Bagshaw E, Mol L, Williamson CJ, Fagan D, Gamble M, Yallop ML. 2017. Photoacclimation by Arctic cryoconite phototrophs. FEMS microbiology ecology 93: fix018.

  • Pittino F, Maglio M, Gandolfi I, Azzoni RS, Diolaiuti G, Ambrosini R, Franzetti A. 2018. Bacterial communities of cryoconite holes of a temperate alpine glacier show both seasonal trends and year-to-year variability. Annals of Glaciology 59:1–9.

    Article  Google Scholar 

  • Pliński M, Picińska J, Targoński L. 1984. Method defining the biomass of marine phytoplankton by means of computers. Zeszyty Naukowe Wydziału Biologii i Nauk o Ziemii Uniwersytety Gdańskiego 10:129–155.

    Google Scholar 

  • Poniecka EA, Bagshaw EA, Sass H, Segar A, Webster G, Williamson C, Anesio AM, Tranter M. 2020. Physiological capabilities of cryoconite hole microorganisms. Frontiers in Microbiology 11:1783.

    Article  Google Scholar 

  • Poniecka EA, Bagshaw EA, Tranter M, Sass H, Williamson CJ, Anesio AM, Black and Bloom Team. 2018. Rapid development of anoxic niches in supraglacial ecosystems. Arctic, Antarctic, and Alpine Research 50:S100015.

    Article  Google Scholar 

  • Plass GN. 1956. The carbon dioxide theory of climatic change. Tellus 8:140–154.

    Article  Google Scholar 

  • Qu J, Sun Y, Awasthi MK, Liu Y, Xu X, Meng X, Zhang H. 2021. Effect of different aerobic hydrolysis time on the anaerobic digestion characteristics and energy consumption analysis. Bioresource Technology: 320, 124332.

  • R Core Team. 2020. R: A language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria. https://www.R-project.org/.

  • Reddy KR, Patrick WH Jr. 1975. Effect of alternate aerobic and anaerobic conditions on redox potential, organic matter decomposition and nitrogen loss in a flooded soil. Soil Biology and Biochemistry 7:87–94.

    CAS  Article  Google Scholar 

  • Revsbech NP. 2021. Simple sensors that work in diverse natural environments: The micro-Clark sensor and biosensor family. Sensors and Actuators B: Chemical 329: 129168.

  • Rozwalak P, Podkowa P, Buda J, Niedzielski P, Kawecki S, Ambrosini R, Azzoni RS, Baccolo G, Ceballos JL, Cook J, Di Mauro B, Ficetola GF, Franzetti A, Ignatiuk D, Klimaszyk P, Łokas E, Ono M, Parnikoza I, Pietryka M, Pittino F, Poniecka E, Porazinska DL, Richter D, Schmidt SK, Sommers P, Souza-Kasprzyk J, Stibal M, Szczuciński W, Uetake J, Wejnerowski Ł, Yde JC, Takeuchi N, Zawierucha, K. 2021. Cryoconite–From minerals and organic matter to bioengineered sediments on glacier's surfaces. Science of The Total Environment 150874.

  • Sanyal A, Antony R, Samui G, Thamban M. 2018. Microbial communities and their potential for degradation of dissolved organic carbon in cryoconite hole environments of Himalaya and Antarctica. Microbiological Research 208:32–42.

    CAS  Article  Google Scholar 

  • Säwström C, Mumford P, Marshall W, Hodson A, Laybourn-Parry J. 2002. The microbial communities and primary productivity of cryoconite holes in an Arctic glacier (Svalbard 79 N). Polar Biology 25:591–596.

    Article  Google Scholar 

  • Segawa T, Takeuchi N, Mori H, Rathnayake RM, Li Z, Akiyoshi A, Satoh H, Ishii S. 2020. Redox stratification within cryoconite granules influences the nitrogen cycle on glaciers. FEMS Microbiology Ecology 96: fiaa199.

  • Segawa T, Yonezawa T, Edwards A, Akiyoshi A, Tanaka S, Uetake J, Irvine-Fynn T, Fukui K, Li Z, Takeuchi N. 2017. Biogeography of cryoconite forming cyanobacteria on polar and Asian glaciers. Journal of Biogeography 44:2849–2861.

    Article  Google Scholar 

  • Stibal M, Tranter M. 2007. Laboratory investigation of inorganic carbon uptake by cryoconite debris from Werenskioldbreen, Svalbard. Journal of Geophysical Research: Biogeosciences: 112(G4).

  • Stibal M, Schostag M, Cameron KA, Hansen LH, Chandler DM, Wadham JL, Jacobsen CS. 2015. Different bulk and active bacterial communities in cryoconite from the margin and interior of the G reenland ice sheet. Environmental Microbiology Reports 7:293–300.

    CAS  Article  Google Scholar 

  • Telling J, Anesio AM, Tranter M, Stibal M, Hawkings J, Irvine-Fynn T, Hodson A, Butler C, Yallop M, Wadham J. 2012. Controls on the autochthonous production and respiration of organic matter in cryoconite holes on high Arctic glaciers. Journal of Geophysical Research: Biogeosciences 117(G1).

  • Wang Q, Li Y, Wang Y. 2011. Optimizing the weight loss-on-ignition methodology to quantify organic and carbonate carbon of sediments from diverse sources. Environmental Monitoring and Assessment 174:241–257.

    CAS  Article  Google Scholar 

Download references

Acknowledgements

We are grateful to Joseph Cook for the collection of samples on Russell Glacier on the Greenland Ice Sheet and Darek Ignatiuk for the collection of samples from Longyearbreen in 2020. We also thank Francesca Pittino for help during field works and Szymon Kawecki for taking photographs of cryoconite. Studies on oxygen concentration, organic matter content and functioning of cryoconite ecosystems were supported via grant NCN 2018/31/B/NZ8/00198 awarded to KZ. AN was also supported by the Institute of Geophysics, Polish Academy of Sciences within statutory activities no. 3841/E-41/S/2020 of the Ministry of Science and Higher Education of Poland. The collection of samples from the Ebenferner was supported by the Polish Ministry of Science and Higher Education as a research project under Diamond Grant 0005/DIA/2019/48.

Author information

Authors and Affiliations

Authors

Corresponding author

Correspondence to Jakub Buda.

Additional information

Author contributions: KZ, JB, EAP designed the study; KZ, JB, PR, EAP, PK performed laboratory analysis; DR, MP, identified algae taxa; JB analysed data; JB, KZ wrote the original draft; KZ, JB, RA, AF collected material for analysis; KZ received funding. All authors corrected, reviewed and edited manuscript.

Supplementary Information

Below is the link to the electronic supplementary material.

Supplementary file1 (PDF 412 kb)

Rights and permissions

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/.

Reprints and Permissions

About this article

Verify currency and authenticity via CrossMark

Cite this article

Buda, J., Poniecka, E.A., Rozwalak, P. et al. Is Oxygenation Related to the Decomposition of Organic Matter in Cryoconite Holes?. Ecosystems (2021). https://doi.org/10.1007/s10021-021-00729-2

Download citation

  • Received:

  • Accepted:

  • Published:

  • DOI: https://doi.org/10.1007/s10021-021-00729-2

Keywords

  • aerobic
  • anaerobic
  • decay
  • glacier
  • photoautotrophs
  • supraglacial