Articles
Behavior of terrestrial dissolved organic matter at the continent-ocean boundary from high-resolution distributions

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Abstract

This paper presents distributions of fluorescent dissolved organic matter (FDOM) in the Columbia River estuary and associated coastal plume as determined by in situ measurement with a fiber optic spectrometer. We interpret these data to represent fluorescence from the humic material associated with terrestrial dissolved organic matter (DOM). We were able to convert FDOM data to quantitative estimates of fluorescent dissolved organic carbon (FDOC) by calibrating our instrument against organic carbon measured by high temperature combustion. The concentration of FDOC in the Columbia River is 140–180 μM, in agreement with DOC data from several previous investigations and our own high-temperature measurements. This result supports the view that humic fluorescence can be used as an analog for terrestrial DOC in some circumstances. The distribution of FDOM in the estuary is nonlinear when plotted against salinity indicating a source within the estuary. The flux of DOC from the river was 1040 mols C sec−1 during our October sampling period. Mass balance calculations show that estuarine source(s) added 14% to this amount. Potential sources of this material are groundwater, intertidal embayments, and in situ production associated with the estuary turbidity maximum (ETM). FDOM-absorbance demonstrates that substantial shifts in fluorescence efficiency occur only in the ETM. This result together with other recent studies suggests that microbial attack of particulate organic carbon in the ETM may be the primary source of excess FDOC in the Columbia estuary. Once FDOM leaves the estuary it mixes into the coastal ocean conservatively with little indication of removal. The presence of three water masses explains most of the variability of FDOM on the shelf. There is a reversal in the slope of the FDOM-salt relationship between Columbia River plume water and deeper shelf water masses. We interpret this bilateral distribution to be the net result of two conservative processes: primary dilution of dissolved fluvial material with coastal surface water and mixing of refractory terrestrial material into the ocean.

Introduction

Terrestrial organic matter is an important component of the carbon budget in coastal areas. This study focuses on the behavior of humic-rich dissolved organic carbon in the Columbia River estuary and associated coastal plume. We image this component as fluorescent dissolved organic material (FDOM) which is part of the pool of dissolved organic matter. DOM is responsible for the color, odor, and binding capacity of natural waters and plays a key role in many natural processes. For example, it is well known that the physiochemical makeup of DOM is the primary attractant during fish migration in brackish and fresh water Wisby and Hasler 1954, Cooper and Hirsch 1982. Moreover, terrestrial DOM has high binding for anthropogenic substances (Patterson et al., 1996) and a knowledge of its behavior allows us to better understand the fate of river-borne contaminants.

When humic material enters the oceans it can be remineralized by a combination of photooxidation and microbial activity Kramer 1979, Amador et al 1989, Kieber et al 1990, Mopper et al 1991, Herndl et al 1993, Miller and Zepp 1995, Amon and Benner 1996a. DOM can also be removed by adsorption onto particles during flocculation (Sholkovitz, 1976). Remineralization creates new ligands that can become a food source for heterotrophic bacteria (Amon and Benner, 1996b) as well as sites for adsorption and further reaction (Kieber et al., 1989). The break down of DOM also releases nutrients and metals to the water column thus supporting the production of marine carbon (Lefèvre et al., 1996). Remineralization of even a small percentage of DOM can have a significant impact on the overall organic carbon budget as the mass flux of fluvial carbon is large compared to local productivity.

It is well known that some terrestrial organic material escapes degradation and resides in the oceans for some time. The most direct evidence for this refractory component is the ligneous material found in all ocean basins (Opsahl and Benner, 1997). There are also higher concentrations of extractable lignins in the deep Atlantic than in the deep Pacific, consistent with a fluvial source. Moreover a refractory terrigenous component is often seen as the most likely explanation for the extreme age of DOC in deep waters Williams and Druffel 1987, Bauer et al 1992. In summary, we know that some fluvial DOM is reactive and that another fraction mixes into the oceans. What is not well understood is the proportioning and reactivity of this material as it enters the oceans. This paper attempts to get at this problem by examining the behavior of terrestrial DOM at the continent-ocean boundary using high-resolution optical data from the Columbia River estuary (Fig. 1) and associated coastal waters.

Section snippets

Methods

Several years ago our laboratory constructed a fiber optic spectrometer that we use as a flow-through chemical analyzer and UV fluorometer (Klinkhammer, 1994). ZAPS (zero angle photon spectrometer) is a fixed-filter instrument that couples a photomultiplier tube and xenon flash lamp through a short (18 cm) bifurcated bundle of fused silica fibers potted in stainless steel tubes. The fiber assembly is external to the pressure case that holds interference filters, xenon lamp, flash power supply,

Arctic calibration

A recently published study in the Arctic demonstrates that we can use a fiber optic spectrometer to estimate DOC in some environments (Guay et al., 1999). This work was done as part of the SCICEX Program that brings together oceanographic research and annual patrols carried out by the US Navy using a nuclear submarine. During 1997 we mounted a ZAPS instrument on the hull of the USS ARCHERFISH. Included in this patrol was a transit at 58 meters water depth between the Beaufort Sea (Canada

Mass-balance of dissolved humic material in the estuary

The distribution of fluorescence in the estuary is nonlinear when plotted against salinity Fig. 5, Fig. 6 and suggests that fluorescent material was being added within the estuary during both years of this study. We can calculate the amount of FDOC added by considering balances for water and salt during this period. Since the input of fresh water from small rivers is negligible, discharge from the estuary (QE) equals Columbia river flow (QR) plus coastal water entering the estuary (QC), QE=QR+QC

Conclusions

FDOM measured with a fiber optic spectrometer can be used as an analog for estimating dissolved organic carbon in some environments. Such data show that the flux of DOC from the Columbia estuary at low flow in the fall of 1997 was 2100 mols C sec−1. A large portion (36%) of this flux was recycled material from the coastal ocean with 50% coming from the river. The high-resolution distribution of FDOM across the estuary measured on several occasions indicates that there is an additional source of

Acknowledgements

We wish to thank the captain and crews of the RV Wecoma and to Fred Jones, the Marine Superintendent. We also thank Paul Stoffregen, Joe Bussell, Kathryn Brooksforce, John Prins, Jay Simpkins, Bob Collier, and Erwin Suess (GEOMAR). A special thanks to Paula Coble and Ron Benner for providing supporting data. ONR contract N00014-92J1299 to GPK funded this work.

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    Present address: Large Lakes Observatory, University of Minnesota, 10 University Dr., 109 RLB, Duluth, MN 55812.

    Present address: Department of Earth Sciences, Cambridge University, Downing Street, Cambridge CB2 3EQ, UK.

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