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Water Column Processes

It is recognized that filtration is operational, that colloidal-bound PCB congeners are not retained by the filter, and that operational dissolved measurements may be biased positively by colloidal material. Techniques to measure truly dissolved PCBs include gas sparging, differential diffusion into membrane-bound lipids (e.g., semipermeable membrane devices, [230]), and selective adsorption (e.g. non-equilibrium solid phase microextraction [231, 232]). Unfortunately, none of these techniques has sufficient sensitivity to reliably and unambiguously measure truly dissolved PCB congeners at the levels present in the Great Lakes. [Pg.40]

The first published measurements of PCBs in the Great Lakes surface waters are those of Veith et al. [233], who reported total PCB concentrations in western Lake Superior (at the Duluth EPA laboratory intake) of 0.8 ng L-1 in 1972. An initial attempt to survey PCB levels in the Great Lakes was that of Glooschenko et al. [234], who sampled Lakes Superior and Huron in late July and early August, 1974. Two liters of surface water (lm depth) was [Pg.40]

Lake Location Sampling year Sampling month mean t-PCB ng/L t-PCB SD min t-PCB ng/L max t-PCB ng/L N Method Refs. [Pg.41]

Lake Location Sampling Sampling mean t- t-PCB min t-PCB max t-PCB N Method Refs. [Pg.42]


Gaillard, J.-F. and Treguer, P. (1997). Antares I France JGOFS in the Indian Sector of the Southern Ocean Benthic and water column processes. Deep-Sea Res. 1144, 951-1176. [Pg.275]

Maldonado, C., Bayona, J.M., 2002. Organochlorine compounds in the north-western Black Sea water Distribution and water column process. Est. Coast. Shelf Sci. 54, 527-540. [Pg.716]

Gallinari M., Ragueneau O., Corrin L., DeMaster D., and Treguer P. (2002) The importance of water column processes on the dissolution properties of biogenic silica in deep-sea sediments I. Solubility. Geochim. Cosmochim. Acta 66, 2701-2717. [Pg.3562]

Colloids are ubiquitous in natural waters they are present in relatively large concentrations (> 10 cm ) in fresh surface waters, in groundwaters, in oceans, and in interstitial soil and sediment waters. The solid-water interface established by these particles plays a commanding role in regulating the concentrations of most reactive elements and of many pollutants in soil and natural water systems and in the coupling of various hydrochemical cycles. Wells and Goldberg (1994) estimate that the total surface area of the small colloidal (5-200 nm) fraction alone is > 18 m per m of seawater in the upper water column. Processes with colloids are also of importance in technical systems, above all in water technology. [Pg.818]

In this study, all three of these types of measurements are available to estimate the sediment-water flux of NH4 and the first two techniques are available for estimation of HPOJ exchange. In addition to providing information about the influence of sediment-water fluxes on water-column processes, a comparison of the different estimates can be used to further elucidate transport-reaction processes near the sediment-water interface. [Pg.309]

In shallow, coastal regions runoff from land or movement upward from the sediments are potentially major sources of NFLj, NOs and DON for water column processes. In certain regions, atmospheric deposition (both wet and dry) may also supply bioavailable nitrogen to the system. However, in... [Pg.547]

C. Maldonado, J.M. Bayona, and L. Bodineau, Sources, distribution and water column processes of aliphatic and polycyclic aromatic hydrocarbons in the northwestern Black Sea water. Environ. Sci. Technol. 33 (1999) 2693-2702. [Pg.558]

Once the particle-reactive species have been scavenged, subsequent packaging and/or aggregation can result in the flux of particles and particle-reactive species from the water column. Thorium provides a unique way to study the environmental pathways and the biogeochemical processes that affect particle-reactive species. The four useful thorium isotopes are Th = A x yx), °Th... [Pg.46]

Joly observed elevated "Ra activities in deep-sea sediments that he attributed to water column scavenging and removal processes. This hypothesis was later challenged with the hrst seawater °Th measurements (parent of "Ra), and these new results conhrmed that radium was instead actively migrating across the marine sediment-water interface. This seabed source stimulated much activity to use radium as a tracer for ocean circulation. Unfortunately, the utility of Ra as a deep ocean circulation tracer never came to full fruition as biological cycling has been repeatedly shown to have a strong and unpredictable effect on the vertical distribution of this isotope. [Pg.48]

As a starting point we can view the ocean as one large reservoir to which materials are continuously added and removed (Fig. 10-17). The major sources of material include rivers and winds, which carry dissolved and particulate materials from the continents to the sea. The major removal process is the formation of marine sediments both by settling of particles through the water column as well as by precipitation of insoluble solid phases. For many ele-... [Pg.255]

Fig. 14-6 Profiles of potential temperature and phosphate at 21 29 N, 122 15 W in the Pacific Ocean and a schematic representation of the oceanic processes controlling the P distribution. The dominant processes shown are (1) upwelling of nutrient-rich waters, (2) biological productivity and the sinking of biogenic particles, (3) regeneration of P by the decomposition of organic matter within the water column and surface sediments, (4) decomposition of particles below the main thermocline, (5) slow exchange between surface and deep waters, and (6) incorporation of P into the bottom sediments. Fig. 14-6 Profiles of potential temperature and phosphate at 21 29 N, 122 15 W in the Pacific Ocean and a schematic representation of the oceanic processes controlling the P distribution. The dominant processes shown are (1) upwelling of nutrient-rich waters, (2) biological productivity and the sinking of biogenic particles, (3) regeneration of P by the decomposition of organic matter within the water column and surface sediments, (4) decomposition of particles below the main thermocline, (5) slow exchange between surface and deep waters, and (6) incorporation of P into the bottom sediments.
The ultimate result is that not only Fe, but most metals that interact strongly with organic matter or oxide adsorbents, are likely to settle out of the water column in estuaries. Not only does this process reduce the metal flux reaching the ocean, but 50% of the time the current at the bottom of an estuary actually facilitates the movement of metals upstream. [Pg.404]

Many sea trials of dispersant chemicals to demonstrate the effectiveness of specific products or to elucidate the processes of oil dispersion into the water column have been described. Most tests have proved inconclusive, leading many to believe that dispersant chemicals are only marginally effective. Tests in a wave basin have been conducted to measure dispersant effectiveness under closely controlled conditions [261]. These tests show that dispersed oil plumes may be irregular and concentrated over small volumes, so extensive plume sampling was required to obtain accurate dispersant effectiveness measurements. In large-scale sea trials, dispersants have been shown effective, but only when sufficient sampling of the water column was done to detect small concentrated dispersed oil plumes and when it was known that the dispersant was applied primarily to the thick floating oil. [Pg.300]

Th is extremely insoluble and adheres to the surface of particles in the ocean soon after it forms from the decay of Because these particles continuously settle from the water column, °Th is rapidly removed from the oceans to the seafloor. The combined process of surface adsorption, followed by particle settling, is termed scavenging. Measurement of the very low °Th concentrations in seawater that result from this... [Pg.499]


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