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4. TRACE FOSSILS
changes in temperature, turbulence,
oxygen content, etc.) result in a physio-
logically stressful environment for nu-
merous organism groups.
It is commonly held that most inver-
tebrates originated in marine environ-
ments (Whitfield, 1976) and represen-
tatives of some groups subsequently
adapted to brackish and freshwater
conditions. The physiological mecha-
nisms involved in the adaptive process
centre on the capability of the organ-
isms to control osmotic flooding
(osmo-
regulation) and the ionic concentration
of body fluids (ionic regulation) due to
lower salt concentrations (Croghan,
1983). The extent to which these adap-
tations occur in different organism
groups is highly variable and thus their
SHOREFACE
MODEL
Psilonichnus
I
&&shore
1
lchnofacies
Skolithos
lchnofacies
Lower
Transltbn
-
Minimum
wave
base
Cruziana
lchnofacies
1
m%e
i
1
t
ii
Maximum
'
Many
tube
dwellers are
passive
wave
base
carnivores rather than suspension feeders.
Figure
5
ldealised shoreface model for
ichnofacies, based mainly on facies obser-
vations in the Cretaceous interior Seaway.
For organism behaviour or feeding strategy,
dashed intervals reflect a presence,
whereas solid lines indicate a dominance.
Deposit-feeding strategies are character-
istic of lower offshore to lower shoreface
settings; associated grazing and foraging
tracemakers typical of lower offshore set-
tings mostly supplant the suspension
feeders and passive carnivores of shallower
settings, reflecting increased water depths
and decreased energy levels, among other
parameters (Frey
eta/.,
1990).
distribution in relation to salinity gradi-
ents shows marked differences. There-
fore, based on physiological criteria,
freshwater and fully saline faunas con-
stitute somewhat stable end members.
The freshwater fauna is impoverished
and is dominated by relatively few
groups, most notably branchiopods
(freshwater crustaceans) and insects
(Croghan, 1983). By sharp contrast, the
brackish water fauna is characterized
by opportunistic euryhaline (tolerant to
wide ranges of salinities) species and
consists of numerous elements, in-
cluding
1) a freshwater component con-
sisting of euryhaline species restricted
to low salinity, 2) a marine component
comprising euryhaline species, 3) a
brackish component consisting of
species that penetrate neither fresh nor
fully saline waters, and 4) a migratory
component comprising species that
spend only a portion of their life cycles
in brackish water (Perkins, 1974).
Investigations on modern brackish
water environments indicate that al-
though their biotic component is highly
variable, the following generalizations
may have significant ecological and pa-
leoecological ramifications. l) Brackish
waters are generally reduced in
species numbers with respect to both
freshwater and fully saline water
(Dorjes and Howard, 1975). 2)
Whereas the number of freshwater
species decreases rapidly even with
slight increases in salinity, the reduc-
tion of marine species is more gradual.
Therefore, the brackish water fauna
can be considered more as an impov-
erished marine assemblage than a true
mixture of freshwater and marine ele-
ments. 3) With reduced salinities, the
marine macrofauna decreases more
rapidly than the microfauna
(Remane
and Schieper, 1971). 4) lnfaunal organ-
isms are more abundant in low-salinity
waters than are epifaunal organisms
(Sanders et
a/., 1965). 5) With de-
creasing salinity, the reduction of
species in groups forming a calcareous
skeleton is greater than in their coun-
terparts lacking such a skeleton
(Remane and Schlieper, 1971). 6)
Many marine organisms undergo a
size reduction when subjected to less
saline water (Milne, 1940). 7) There is
a distinct shift in the bathymetric range
of marine organisms when subjected to
salinity reductions
(Remane and
Schieper, 1971). Thus the influence of
salinity gradients can hardly be di-
vorced from the ichnocoenose concept
as suggested'by Bromley and Asgaard
(1991).
Such trends reflect a stressful envi-
ronment, and successful colonization
depends (aside from physiological con-
straints) on the ability of the organisms
to develop an effective adaptive stra-
tegy. Sediments of estuaries and other
brackish water environments are effec-
tive at dampening the influence of
salinity fluctuations within the substrate
(Sanders et
a/., 1965). Therefore, the
deep
infaunal habitat serves as a
refuge to buffer the organism against
rapid and extreme salinity variations.
As a result, burrowing organisms are
able to penetrate a greater distance up
an estuary than epifaunal (animals
living on the substrate surface) organ-
isms, which are subjected to fluctuating
salinities of the overlying water column
(Alexander et
a/., 1935).
Although an unfortunate paucity of
studies deals specifically with biogenic
structures in modern brackish water en-
vironments, work by Howard and Frey
(1973) on estuaries of the Georgia
coast indicates that
1) the diversity and
abundance of biogenic structures in-
creases seaward,
2)
distinct biogenic
structures and bioturbate textures are
also more diverse and abundant along
the margins of the estuaries than in the
deeper channels,
3)
distinct burrows
and dwelling tubes characterize most
muds whereas sandy muds or muddy
sands may exhibit both distinct burrows
and various types of bioturbate tex-
tures, and 4) coarser sediments tend to
lack biogenic sedimentary structures. In
addition, they also recognized that the
entire suite of estuarine biogenic struc-
tures generally consists of both vertical
and horizontal burrows or burrow
systems and thus does not fall conve-
niently into any of Seilacher's (1967)
universal ichnofacies. Instead, the as-
semblage tends to be composed of a
mixture of structures typical of both the
Skolithos and Cruziana ichnofacies.
This assemblage is characterized by
burrows that, if preserved, would
consist of Skolithos, Monocraterion,
Thalassinoides, Ophiomorpha,
Pla-
nolites, and Palaeophycus (Howard
and Frey, 1973). Burrows typical of
freshwater deposits
(i.e., Scoyenia
and insect perturbations) were not ob-
served. Similarly, although sediments