Comparative environmental tolerances of threatened delta smelt (Hypomesus transpacificus) and introduced wakasagi (H-nipponensis) in an altered California estuary
C. Swanson et al., Comparative environmental tolerances of threatened delta smelt (Hypomesus transpacificus) and introduced wakasagi (H-nipponensis) in an altered California estuary, OECOLOGIA, 123(3), 2000, pp. 384-390
In California's Sacramento-San Joaquin estuary, environmental protection an
d habitat restoration efforts directed at a threatened native osmerid, the
delta smelt (Hypomesus transpacificus), are complicated by the presence of
a morphologically similar non-native congener, the wakasagi (H. nipponensis
), transported to the estuary from upstream reservoirs. In order to better
define delta smelt critical habitat and to evaluate the potential for habit
at overlap by these two species, we compared the tolerances of the two spec
ies to temperature, salinity, and water velocity, environmental factors tha
t vary spatially and temporally within the estuary. For fishes acclimated t
o 17 degrees C and fresh water (0 ppt), we measured critical thermal maxima
and minima, chronic upper salinity tolerance limits, and critical swimming
velocities. Wakasagi had higher critical thermal maxima (29.1 degrees C vs
. 25.4 degrees C for delta smelt), lower critical thermal minima (2.3 degre
es C vs. 7.5 degrees C for delta smelt), higher upper salinity tolerances (
26.8 ppt vs. 19.1 ppt for delta smelt), and swam faster (for 6-6.9 cm SL fi
sh, 43.3 cm s(-1) vs. 28.2 cm s(-1) for delta smelt) than delta smelt. This
suggests that the wide seasonal and year-to-year fluctuations in temperatu
re, salinity, and flow typical in the estuary would not exclude wakasagi, a
lthough their eggs and larvae may be less tolerant. With respect to these f
actors, the native delta smelt may be at a physiological disadvantage, part
icularly in habitats with suboptimal environmental conditions, and may be e
xcluded from shallow-water habitat restoration sites, which are characteriz
ed by poor circulation, low flows, and more environmentally extreme conditi
ons. The low abundance of wakasagi in the estuary recorded to date may indi
cate that factors other than temperature, salinity, and flow determine waka
sagi distribution.