Article Review: Sunlight Controls Fate of DOC (Cory, et al., 2014)

    Austin, TX
    June 1, 2019


    Title: Sunlight Controls Water ColumnHypothetical 'cylinder' of water between the surface of the ocean and the ocean bottom. Processing of Carbon in Arctic Fresh Waters

    Authors: Rose Cory, Collin Ward, Byron Crump, George Kling

    Journal: Science

    Date: August, 2014


    In my previous post, I addressed the different means by which dissolved organic carbon (DOC) is oxidized into carbon dioxide in Arctic watersheds. The scientists I’m working with this summer – Drs. Rose Cory, George Kling, and Byron Crump -- are concerned with the specifics of this process. The thought here is that if more is learned about how organic material released from permafrost is broken down into greenhouse gases, climate models can be modified to better account for the permafrost positive feedback loop.

    In this article review, I will focus on important work they published in 2014.1


    Background

    The factors at work in oxidizing Arctic DOC are quite complicated and not very well understood. As previously mentioned, the main culprits for DOC oxidation in the Arctic are bacterial respiration and photooxidation. Prior to the work of Cory, et al., bacteria were given most of the credit.

    Purpose

    Cory and her colleagues wanted to further investigate the respective roles of bacterial respiration and photooxidation in the oxidation of Arctic DOC. No prior study had simultaneously evaluated both bacterial and sunlight-driven DOC oxidation pathways.

    Experimental Setup

    The scientists collected water samples from a wide variety of streams, rivers, and lakes in the Kuparuk River basin on the North Slope of Alaska during the summers of 2011-2013.

    Field sites on the North Slope
    Field sites on the North Slope of Alaska used in the study. Image Source: Cory, et. al., 2014.
    Samples from each location were divided into two test groups: bacterial respiration and photooxidation. Bacterial respiration samples were incubated in small containers in the dark for five to seven days at 6-7℃, this temperature range being the average for non-frozen water across the many sampling sites. The goal here was to evaluate oxidation of DOC due to bacteria alone (no light). Photooxidation samples, on the other hand, were first filtered to remove the bacteria. They were then placed in small containers and exposed to either simulated light or natural sunlight for 12 hours at 10-16℃.

    Diagram of experimental design
    Diagram of thhttps://www.polartrec.com/files/styles/thumbnail/public/members/1557/images/sagriver.jpg?itok=j_NMD6-we experimental design implemented by the group. Image Source: Sara Nason, Science in the Classroom.
    Oxygen consumption within the samples was evaluated using mass spectrometry. Production of carbon dioxide was quantified using an infrared CO2 detector. For bacterial respiration, CO2 production was also measured indirectly through oxygen consumption, as for every 1 mol of oxygen consumed, bacterial respiration serves to yield 1 mole of carbon dioxide. Using this logic, partial photooxidation was also evaluated for samples. Partial photooxidation (i.e. oxidation of DOC, but not completely to CO2) serves to consume oxygen but not yield CO2. Accordingly, any oxygen consumed in excess of the 1:1 ratio between O2 consumed and CO2 produced could be attributed to partial photooxidation.

    The group used fluorescence spectroscopy to quantify how much light was being absorbed by sunlight-exposed samples. But water in the Arctic is contained in streams, rivers, and lakes, not small containers. If a water column is deeper, more of the water in the column (and its contained DOC) is protected from sunlight. Accordingly, the group needed to also quantify the actual light availability in the water at all of their test sites - how much light decreases with depth in the water column - which they did using a Compact-Optical Profiling System (C-OPS). This system is slowly lowered into the water column and measures absorbance as it descends. Combining this data with the absorbance, O2 consumption, and CO2 consumption data for their samples, they were able to calculate total amount of DOC degradation due to sunlight at their test sites. In the end, they were able to effectively determine rates of water column breakdown of DOC by sunlight and bacteria.

    Results

    The results of this experiment indicate that 55% of the DOC broken down in the waters of the Kuparuk basin is completely oxidized to CO2, while 45% is partially photooxidized. Importantly, the group found that light was involved at least 70% of DOC processing at all of their study sites. In other words, conflicting with the prevailing notion at the time, rates of photochemical oxidation drastically exceeded rates of bacterial respiration in Arctic streams, rivers, and lakes.

    The below graphic summarizes results for three important study sites: Imnavait Creek (a headwater stream), Toolik Lake (further downstream), and a Sagavanirktok River site (even further downstream). For each site, the pie chart illustrates the relative importance of different DOC oxidation processes - photo-mineralization (complete photooxidation) vs. partial photooxidation vs. bacterial respiration.

    Fates of DOC
    Fates of DOC at three field sites on the North Slope of Alaska. Image Source: Cory, et al., 2014.

    Discussion

    The group suggests three major reasons for why photochemical processing of DOC is more important than bacterial respiration in Arctic watersheds. First, evidence from their dark bacterial respiration experiments suggests that rates of bacterial respiration in cold Arctic waters are on the low side when compared to other locations on the planet. Second, their areal spectroscopic measurements indicate that DOC in Arctic waters is more susceptible to breakdown by light than DOC in other locations on the planet. Third, Arctic waters are generally on the shallower side and completely unshaded, serving to substantially increase DOC exposure to sunlight.

    The authors also offer an explanation for the trends in the above pie charts, comparing upstream and downstream environments.

    • Trend 1: Dominance of photo-mineralization (complete photooxidation) of DOC in headwater streams (e.g. Imnavait Creek).
    • Trend 2: Increased importance of partial photooxidation in sites further downstream (e.g Toolik Lake and Sagavanirktok River site).

    As the authors explain, when DOC enters a watershed, easily photooxidized components are completely oxidized readily and leave the stream as CO2. This explains dominance of complete photooxidation in headwater streams, consisting of DOC with little prior light exposure. Freed of easily photooxidized components, downstream DOC is less susceptible to complete photooxidation. Accordingly, as you move downstream, partial photooxidation begins to dominate over complete photooxidation.

    Sagavanirktok River
    Sagavanirktok River on the North Slope of Alaska. Image Source: Micah Bochart.

    The Gist of It All

    This work is very important in helping the scientific community better understand the factors that are affecting oxidation of DOC in the Arctic and the relative rates at which these things are happening. This directly helps scientists improve climate models to better account for the permafrost positive feedback loop. Here’s a great video featuring scientists Rose Cory, Jason Dobkowski, and Collin Ward explaining this work, with footage from the actual study sites used:


    Comment below!


    1. Cory, R. M., et al. “Sunlight Controls Water ColumnHypothetical 'cylinder' of water between the surface of the ocean and the ocean bottom. Processing of Carbon in Arctic Fresh Waters.” Science, vol. 345, no. 6199, 2014, pp. 925–928. ↩︎

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