Pergamon
PII: S0025-326X(97)00063-5
Marine Pollution Bulletin, Vol. 34, No. 11, pp. 857-867, 1997
© 1997 Elsevier Science Ltd
All rights reserved. Printed in Great Britain
0025-326X/97 $17.00+0.00
Polyaromatic Hydrocarbon (PAH)
Distributions in the Seine River and its
Estuary
M. B. FERNANDES*, M.-A. SICRE*:~, A. BOIREAU* and J. TRONCZYNSKI'f
*Laboratoire de Physique et Chimie Marines, Universit~ Pierre et Marie Curie, INSU/CNRS URA 353, 4 Place Jussieu,
75252 Paris Cedex 05, France
tLaboratoire de Chimie des Contaminants et Mod~lisation, IFREMER, Centre de Nantes, BP 1049, 44037 Nantes
Cedex, France
Dissolved and particulate PAHs were quantified through-
out the Seine River and its estuary. Samples were
collected in October 1993, covering a salinity gradient
of 0.2%0 to 34.8%0. Two mooring stations were occupied
at the river mouth to ascertain the influence of tidal cycles
on the dispersal of riverborne PAils. Total particulate
PAH concentrations ranged from 2 to 687 ng 1-1 (or I to
14pgg-1). Concentrations were correlated to the
suspended matter load and distributions could be
explained by estuarine mixing. PAII levels decreased
from ebb to flood tides. PAH concentrations in the
dissolved phase (4 to 36 ng 1-1) were, in general, an order
of magnitude lower than in the particulate phase. The
partition coefficient of individual PAHs (Koc) were
comparable to those previously reported for the RhSne
River suspensions. © 1997 Elsevier Science Ltd
A large variety of organic substances, including
anthropogenic contaminants, are transported into
coastal marine environments via riverine discharge. To
evaluate pollutant impact it is important to estimate and
understand river transport/dispersal of anthropogenic
compounds and their effects on water quality and biota.
The distribution and fate of contaminants in water,
sediment and biota in estuaries are influenced by
numerous factors such as salinity, pH, suspended
particulate matter (SM), tidal currents and seasonal/
meteorological variability (Olsen et al., 1982; Jaffa,
1991).
Polycyclic aromatic hydrocarbons (PAHs) are wide-
spread pollutants in aquatic systems and occur
primarily as a result of anthropogenic inputs. Their
~/Corresponding author. Present address: Centre des Faibles
Radioactivitb, s, Laboratoire Mixte CNRS-CEA, Domaine du CNRS,
Ave. de la Terrasse, 91191 Gif-sur-Yvette Cedex, France.
main sources include both high and low temperature
combustion (e.g. industrial pyrolysis, ship and auto-
mobile exhausts, forest fires, urban coal and oil heating)
(Grimmer et al., 1983a) and the direct release of oil and
its products (Neff, 1979; Grimmer et al., 1981a,b,
1983b). High molecular weight PAHs are generated
mainly by high temperature combustion whereas lower
molecular weight PAHs, e.g. phenanthrene and its
alkylated homologues, may derive from fossil fuel
combustion, but are also major constituents of
petroleum. PAHs are present as mixtures of alkylated
and parent species. The ratio of methyl-phenanthrenes/
phenanthrene (MP/P) is commonly used to ascertain
emission sources. Combustion-generated PAHs are
known to be deficient in substituted homologues (MP/
P< 1), even though combustion temperature affects
their relative abundance (Youngblood and Blumer,
1975). In contrast, alkylated PAHs dominate the
assemblage of unburned fossil organic material (MP/
P > 1) (Youngblood and Blumer, 1975).
PAHs are considered to be hazardous to the
environment. They include highly mutagenic (Guerin
et al., 1978) and carcinogenic four- to seven-ring
compounds (Medical Research Council, 1968). Two-
or three-ring PAHs are less mutagenic (Berichte 1/79
des Umweltbundesamtes, 1979) but can be highly toxic,
e.g. three-ring phenanthrene and its methyl-substituted
homologues are toxic to algal growth (Pulich et al.,
1974). Chronic introduction of PAHs in estuaries can
affect freshwater quality and induce accumulation in the
pelagic and benthic food chains at various trophic levels
leading to long term changes in the biota.
Some PAHs are readily degradable. Their occurrence
on airborne particles, riverine suspensions or sediments
suggests that part of them survive degradation
processes. It has been hypothesized that PAHs adsorbed
onto particles are more readily accessible to degradation
whereas those tightly bound or occluded into particles
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