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Carbon fluxes, measurement

The dynamics of these models depend strictly on carbon fluxes, but the fluxes are poorly measured or are calculated from carbon reservoir size and assumptions about the residence time of the carbon in the reservoir. In addition, model fluxes are linear functions while in reality few, if any, probably are linear. [Pg.418]

Fig. 10-15 Organic carbon fluxes with depth in the water column normalized to mean annual primary production rates at the sites of sediment trap deployment. The undulating line indicates the base of the euphotic zone the horizontal error bars reflect variations in mean annual productivity as well as replicate flux measurements during the same season or over several seasons vertical error bars are depth ranges of several sediment trap deployments and uncertainities in the exact depth location. (Reproduced with permission from E. Suess (1980). Particulate organic carbon flux in the oceans - surface productivity and oxygen utilization, Nature 288 260-263, Macmillan Magazines.)... Fig. 10-15 Organic carbon fluxes with depth in the water column normalized to mean annual primary production rates at the sites of sediment trap deployment. The undulating line indicates the base of the euphotic zone the horizontal error bars reflect variations in mean annual productivity as well as replicate flux measurements during the same season or over several seasons vertical error bars are depth ranges of several sediment trap deployments and uncertainities in the exact depth location. (Reproduced with permission from E. Suess (1980). Particulate organic carbon flux in the oceans - surface productivity and oxygen utilization, Nature 288 260-263, Macmillan Magazines.)...
Sano and Williams (1996) calculated present-day volcanic carbon flux from subduction zones to be 3.1 x 10 mol/year based on He and C isotopes and C02/ He ratios of volcanic gases and fumaroles in circum-Pacific volcanic regions. Williams et al. (1992) and Brantley and Koepenich (1995) reported that the global CO2 flux by subaerial volcanoes is (0.5-2.0) x lO mol/m.y. and (2-3) x 10 mol/m.y. (maximum value), respectively. Le Guern (1982) has compiled several measurements from terrestrial individual volcanoes to derive a CO2 flux of ca. 2 x 10 mol/m.y. Le Cloarec and Marty (1991) and Marty and Jambon (1987) estimated a volcanic gas carbon flux of 3.3 X 10 mol/m.y. based on C/S ratio of volcanic gas and sulfur flux. Gerlach (1991) estimated about 1.8 x 10 mol/m.y. based on an extrapolation of measured flux. Thus, from previous estimates it is considered that the volcanic gas carbon flux from subduction zones is similar to or lower than that of hydrothermal solution from back-arc basins. [Pg.417]

The fluxes of POC determined by the " Th method applied to the world s oceans are summarized in Table 1. Where possible we have tabulated the ratio of Th-derived POC export to independent estimates of primary production. As noted above, this ratio, termed the 77i ratio (Buesseler 1998), is important in the euphotic zone carbon balance as it represents the leakage of POC out of the euphotic zone (The ThE ratio is so named to evoke the e ratio, which is defined as the ratio of POC flux measured with sediment traps to primary production). [Pg.476]

Measurements of radionuclides in seawater have been used to study a variety of processes, including ocean mixing, cycling of materials, and carbon flux (by proxy). These measurements provide information on both process rates and mechanisms. Because of the unique and well-understood source functions of these elements, models of radionuclide behavior have often led to new understanding of the behavior of other chemically similar elements in the ocean. [Pg.53]

Measurements of radionuclides are also used to determine removal mechanisms and controls for carbon and metal cycling in the ocean. For example, the removal of Th from the euphotic zone is closely coupled to the vertical flux of particulate organic carbon. The deficiency of Th with respect to its parent—near-surface waters is used to estimate the export flux of particulate organic carbon (Buesseler, 1991). Measurements of Th and in the upper water column provided the primary data relahng to particulate carbon fluxes during JGOFS. [Pg.40]

Carbon and Phosphorus Burial Efficiencies. The estimate of diatom carbon demand (12-15 g/m2 per year) is consistent with the flux of carbon to the sediment surface. With sediment-trap fluxes corrected for resuspension, we measured a total annual deposition flux of 12.5 g of C/m2. In comparison, Eadie et al. (24) obtained 23 g of C/m2 for a 100-m station, based on three midsummer metalimnion deployments. Of our total, 83% of the carbon was associated with diatoms, and the primary diatom carbon flux was 10.3 g of C/m2. Thus, about 15-30% of the diatom carbon was regenerated in the water column during sedimentation. Approximately 10% of the diatom flux reached the sediment surface encapsulated in copepod fecal pellets the remaining 90% was unpackaged. [Pg.316]

Figure 7. Deposition to the sediment surface of Little Rock Lake in 1989 as measured by sedimentation traps. A, mass flux B, carbon flux bars represent fluxes, lines are particle concentrations of carbon (percent) and C, Hgflux bars represent flux, lines are particle concentrations of Hg in nanograms per gram. (Adapted with permission from reference 21. Copyright 1991 D. Reidel... Figure 7. Deposition to the sediment surface of Little Rock Lake in 1989 as measured by sedimentation traps. A, mass flux B, carbon flux bars represent fluxes, lines are particle concentrations of carbon (percent) and C, Hgflux bars represent flux, lines are particle concentrations of Hg in nanograms per gram. (Adapted with permission from reference 21. Copyright 1991 D. Reidel...
The turnover time (x) of a reservoir is its mixing or refresh rate, and is the time it would take for the reservoir to completely empty if there were no further inputs. For soils, it is a measure of the first-order kinetics for decay (x = Ilk). At steady state, it is calculated as the inventory divided by the total inputs (or total outputs) to the reservoir. To calculate the turnover time for a soil C reservoir at steady state, we would divide the mass of SOM (C) by the total carbon fluxes (.S ) from the reservoir or x = C/S. Fluxes would include decomposition to C02 and leaching of dissolved organic. [Pg.231]

Few studies exist where mass fluxes of Phaeocystis cell carbon have been quantified along with POC export. We compiled the existing data sets to evaluate the contribution of Phaeocystis spp. cell carbon to vertical carbon flux. Phaeocystis pouchetii blooms are regularly observed in North Norwegian fjords (Heimdal 1974 Eilertsen et al. 1981 Riebesell et al. 1995 Reigstad et al. 2000 Wassmann et al. 2005). Due to the close vicinity of Tromsp, many years of observations from the water column as well as from sediment trap measurements (without fixatives) are available from these localities. [Pg.223]

Despite occasionally high concentrations and dominance of Phaeocystis spp. in the water column, calculations based on sediment-trap measurements suggest low daily loss rates, implying high retention of Phaeocystis cell carbon in the upper 50-100 m. Unless deep mixing accelerates vertical export, the contribution to the vertical carbon flux at 100 m is on average 3%. The conclusion is that Phaeocystis cell carbon does not contribute significantly to vertical carbon export. [Pg.226]

As mentioned in the introduction, one goal of some experiments was to examine, to which extent the chemical erosion of doped materials is reduced. For example, the methane formation by plasma exposure of NS31 (Si-doped CFC with 1.0-1.5% Si) was reduced by a factor of two in comparison to graphite. The interpretation of this result (as of others, e.g., C flux from W) is very complex. We have to be aware that the measurements were done in a carbon machine and we have to take into account the carbon fluxes onto... [Pg.331]


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See also in sourсe #XX -- [ Pg.42 ]




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