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Contamination of the deep-sea

Authors:
~ Pergamon
PII: S0025--326X(96)0009ff-2
Contamination of the Deep-Sea
Marine Pollution Bulletin,
Vol. 34, No. 5, pp. 288-289, 1997
© 1997 Published by Elsevier Science Ltd
All rights reserved. Printed in Great Britain
0025~326X/97 $17.00+0.00
K. H. BALLSCHMITER*, O. FROESCHEIS*, W. M. JARMANt and G. CAILLET:~
*Universitdt Ulm, Analytische Chemie, Postfach 4066, D-7900 Ulm, Germany
t University of California, Institute of Marine Sciences, Earth and Marine Science Bldg, Santa Cruz, CA 95060, USA
~Moss Landing Marine Laboratories, POB 450, Moss Landing, CA 95039, USA
The deep-sea is not as clean as one supposes; it may
even turn out to be the ultimate waste basket for a large
group of persistent semivolatile contaminants (e.g.
persistent congeners of the PCBs, the polychlorinated
diphenyl ethers, the persistent organochlorine pesti-
cides, and DDT and related compounds). The deep-sea
floor, due to its inaccessibility to man, is often
considered as an appropriate place for waste tailings
from mines as it has recently been argued by Ellis and
Ellis (1994) in their Viewpoint. As pointed out by Theil
(1995) in his Correspondence, this viewpoint may hold
for geological aspects, it surely does not for biology and
environmental chemistry.
Except for the case of chemosynthetic organisms, the
biota of the abyss have relied on the input of organic
carbon pre-synthesized by photosynthesis from the
oceans surface since the beginning of life; starting with
the soil bacteria and ending with fish of the rattail
family (Jumars and Gallagher, 1982). The general
aspects of organic carbon flow to the bottom of the
sea whether as the carcass of a dead whale, the faecal
pellets of the fish and shrimps, or as the colloidal matter
called the marine snow have been studied in the past
(Bruland and Silver, 1981; Silver and Bruland, 1981;
Rowe, 1983; Alldredge and Silver, 1988; Theil, 1995).
A more recent addition to this carbon flow to the
bottom includes the final environmental fate of
persistent organic molecules that are semivolatile and
practically water insoluble. Their physical and chemical
properties require, under the aspect of a long-term
multiphase distribution, that they will end up in an
environmental compartment avoiding the water phase.
For this reason persistent organic compounds exhibit
the phenomenon of bio- and geoaccumulation (Ball-
schmiter, 1992); thus, these compounds will move with
any particulates or organic matter from the ocean
surface to the ocean floor. Now their persistence comes
into play. As unmetabolizable organics they will be
recycled in the biophase of the abyss.
One may draw an analogy to the final fate of
persistent volatiles such as freon. Gaseous freon rises
into the atmosphere and catalyses the destruction of
stratospheric ozone, which filters out cancer-causing
ultraviolet radiation from the sun (Manahan, 1990).
Our atmosphere provides the ultimate sink for
persistent halogenated compounds, like freon, due to
their volatility. It is therefore safe to assume that
semivolatile compounds like PCBs, have an ultimate
sink as well. Terrestrially, our soils provide this
environmental fate, while in the global oceanic system,
the sea floor and its living inhabitants provide OCs their
final resting ground.
Reality follows this predicted scheme as first
analytical results of the enrichment of persistent
organics in the deep-sea biota indicate. We have
analysed surface and deep-sea fish of the eastern
North Atlantic and found an enrichment up to a
factor of about 600 for the DDT group for the deep-sea
specimen (Table 1) relative to surface living species. It is
a result of the compressing of the content of persistent
compounds in the water column and their selective
fractionation into the biological lipids of organisms
living on or near the sea floor. Preliminary results of
specimens collected from the Monterey Bay Submarine
Canyon indicate a similar pattern. Van Dover et al.
(1992) found evidence of sewage derived organic matter
from ocean dumping off the coast of New Jersey in
deep-sea invertebrates and fish by examining stable
isotope ratios in their tissues. Stegeman et al. (1986)
reported elevated monooxygenase induction (enzymes
that catalyze transformation of foreign compounds)
TABLE l
Organochlorine contaminants in the livers of fish collected from the
North Atlantic. Concentration reported as mg kg-1 lipid.
Madeira
Parrot fish Black scabbard
Coastal Deep-sea
HCB 2 17
~~-PCB* 110 5800
~-DDT** 15 9200
~"~-Chlordane*** 8 520
Adapted from Kr/imer
et al.
(1984).
*~-~;PCB=Sum of PCBs 28, 52, 101, 138, 153, and 180.
**~~-DDT=Sum of p,p'-DDT, p,p'-DDE, p,p'-DDD, and p,p'-
DDMU.
***~"~-Chlordane=Sum of heptachlor,
cis-chlordane, trans-chlor-
dane,
trans-nonachlor
and oxychlordane.
288
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Aquesta tesi doctoral està subjecta a la llicència Reconeixement-CompartIgual 3.0. Espanya de Creative Commons. Esta tesis doctoral está sujeta a la licencia Reconocimiento-CompartirIgual 3.0. España de Creative Commons. This doctoral thesis is licensed under the Creative Commons Attribution-ShareAlike 3.0. Spain License.
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