In Vitro Activities in Mussel Hemocytes as Biomarkers of Environmental
Quality: A Case Study in the Abra Estuary (Biscay Bay)
M. P. CAJARAVILLE,
1
I. OLABARRIETA, AND I. MARIGOMEZ
Zitologi eta Histologi Laborategia, Biologia Zelularra eta Zientzia Morfologikoen Saila, Euskal Herriko Unibertsitatea, 644 PK, E-48080 Bilbo,
Basque Country, Spain
Received January 9, 1996
Mussels, Mytilus galloprovincialis, were collected from six
coastal sites of dissimilar water quality (Zierbena, Santurtzi,
Arrigunaga, Galea, Men ˜ akoz, and Plentzia) at Biscay Bay in Sep-
tember 1991, January 1992, June 1992, and September 1992. The
extent of hemocyte infiltration in connective tissue of the digestive
gland was quantified by stereology on histological sections in
terms of volume density of hemocytes (HVD). HVD was elevated
in mussels collected from Plentzia (the less polluted site) in Janu-
ary 1992 and September 1992, while such increases occurred in
January 1992 in Santurtzi and Arrigunaga and in September
1991 and September 1992 in Galea. Conversely, HVD was re-
duced in Arrigunaga in September 1991 and in Galea in January
1992. Moreover, HVD was kept unchanged through the year in
mussels collected from Men ˜ akoz and Zierbena. On the basis of
this preliminary in vivo study, hemocytic activities of mussels col-
lected in September 1994 from Arrigunaga and Plentzia were
further investigated by means of four in vitro immunotoxicity
assays: (a) the trypan blue exclusion assay, indicative of cell vi-
ability; (b) the zymosan phagocytosis assay, indicative of phago-
cytic activity; (c) the diaminobenzidine–manganese (DAB–Mn
2+
)
oxidation assay for estimating reactive oxygen intermediate (ROI)
production; and (d) the neutral red (NR) uptake assay, indicative
of endocytic ability. These in vitro tests indicated some significant
differences between Plentzia and Arrigunaga. Hemocytes from
mussels collected in Plentzia exhibited a higher capability to
phagocytose zymosan while, conversely, hemocytes from mussels
collected in Arrigunaga endocytosed more NR and produced
more ROI under nonstimulated conditions. These differences in
the in vitro hemocytic activities of mussels from Plentzia (nonpol-
luted) and Arrigunaga (moderately polluted) suggest that in vitro
assays may be used as biomarkers of environmental quality in
coastal and estuarine areas. © 1996 Academic Press
INTRODUCTION
In vitro toxicology has bloomed during very recent years and
the examination of cell cultures has partially replaced the rou-
tine sacrifice of experimental animals (Fry, 1993). Such a trend
is also noted in the field of environmental toxicology and tox-
icity tests with fishes or invertebrates are currently being sub-
stituted by in vitro testing of the toxicity of chemicals (Alvarez
and Friedl, 1992; Zahn and Braunbeck, 1993; Seibert et al.,
1994). Moreover, the in vitro testing approach could be also
valuable for environmental monitoring programs based on the
use of sentinel organisms, which could provide primary cul-
tures of target cells whose functional responses could be used
as measures of environmental quality (Anderson, 1988; Dunier
and Siwicki, 1993).
Bivalve molluscs and specially mussels are widely used as
sentinels in monitoring programs of marine environmental
quality (Goldberg, 1986). Chemical analysis of their tissues,
measurement of biomarkers of exposure to specific chemicals,
and measurement of pollution effects are increasingly per-
formed in environmental monitoring programs (Widdows and
Donkin, 1989; Rainbow, 1993). In most cases, sentinel mussels
are killed to conduct these analyses and relatively large
samples are required to attain feasible conclusions on water
quality. Alternatively, in vitro assays might provide useful bio-
markers of either exposure to pollutants or their biological
effect (Anderson, 1993).
Particularly, some functional responses of hemocytes and
brown cells of molluscs have been proposed to develop in vitro
toxicity assays indicative of the condition of sentinel mussels
(Cheng, 1988a,b; Zaroogian et al., 1992; Zaroogian and Yev-
ich, 1993) and, therefore, of the environmental quality of their
habitat. Although the field of immunotoxicology of bivalve
molluscs was in its infancy one decade ago (Anderson, 1988),
it has grown up during the past years due to its interest for
fisheries, aquaculture, and ecotoxicology (Anderson, 1993).
Cell viability, phagocytic and endocytic activities, lysosomal
enzyme activities, production of oxygen free radicals, and rela-
tive proportion of hemocyte types have been quantified in vitro
after in vivo exposure to chemical pollutants (McCormick-Ray,
1987; Cheng, 1988a,b; 1990; Sami et al., 1992; Coles et al.,
1994). Nevertheless, different chemicals or even different
doses of the same chemical may provoke different hemocytic
responses which, additionally, might be modified by either
environmental factors or concurrence of other chemicals
(Anderson, 1993; Auffret and Oubella, 1994).
1
To whom correspondence should be addressed.
ECOTOXICOLOGY AND ENVIRONMENTAL SAFETY 35, 253–260 (1996)
ARTICLE NO. 0108
253
0147-6513/96 $18.00
Copyright © 1996 by Academic Press
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