gcb12455-sup-003

advertisement
Supporting information
2
Respirometry methods
The acclimation time needed to obtain resting levels of oxygen consumption in the
4
species examined here, 90 min., is shorter thanwhat is necessary forother species, especially
larger fishes or those that are more active. The damselfishes and cardinalfishes investigated
6
here, and in other recent studies (Nilsson et al., 2009; Gardiner et al., 2010; Couturier et al.,
2013;Rummer et al., 2013;) exhibit minimal handling stress and quickly become accustomed
8
to the respirometry chamber. We conducted pilot studies to determine how long it takes for
ṀO2Restvalues to stabilize after fish were placed in the respirometry chamber. Even after a
10
fish had been chased to exhaustion, which would be far more stressful and energetically
costly than handling stress, ṀO2 values stabilized earlier than 2h. See Fig. S1 for chase and
12
post-chase ṀO2 values for three C. atripectoralisindividuals (Rummer, unpublished data).
The pilot data show that the fish return to a low, very stable rate of oxygen
14
consumptionrapidly following disturbance (Fig. S1).
We could not detect significant differences between the average ṀO2Maxand average
16
ṀO2Restof two of our species (D. melanurus and C. quinquelineatus) acclimated to 34°C and,
over the course of the entire study, we observed 5 individual fish that had a ṀO2Max value that
18
was numerically, albeit only slightly below their ṀO2Rest value. We note that resting rates
increased significantly upon acclimation to34°C, if not by 33°C, in all except for one of the
20
species investigated, and thatṀO2Maxvalues had already peaked and fallen in all except for
twospecies. The patterns of change resulted in a very low aerobic scope nearing zero at 34°C.
22
We believe this was the result of the fish being unable to exhibit a maximum swimming
performance and the overall stress of high temperatures. This interpretationisfurther
24
supported by the variability around the means; which is small across all species and
temperatures for both ṀO2Max and ṀO2Rest, except at the highest temperature where the error
1
26
bars are noticeably larger.
28
Latitudinal comparisons and reanalysis of data
It was necessary to re-analyze data from the two previous studies (Nilsson et al., 2009;
30
Gardiner et al., 2010) becauseone higher acclimation temperature (at 33C) was added for the
Heron Island populations andadditional replicates were obtained for the other temperatures to
32
make the latitudinal comparisons more robust. After incorporating the additional replicates
and the additional acclimation temperature for the Heron Island populations, we found that
34
the overall patterns were retained. However, there was less variability around the means, and
with the addition of33°Cdata, it was clear that performance was starting to fall at the higher
36
temperatures, which could be due to an increase in ṀO2Rest, a decrease in ṀO2Max, or both.
Both sets of reanalyzed data – plotted in the same way as we did for the PNG populations – in
38
addition to aerobic scopes for the PNG populations are summarized in Fig. S2.
Re-analysis of the previously published data with the inclusion of the additional
40
replicates and temperature group was also necessary in the present study in order to more
appropriately make comparisons across the three separate data sets. In particular, we aimed to
42
compare the temperatures at which the representatives from each population performed best,
not directly compare values of absolute scope among populations, because the magnitude of
44
the absolute aerobic scope may not be what dictates performance. Therefore,we estimated the
temperatures at which performance is the greatest within populations and then compared those
46
temperaturesamong the different sites.
48
Local adaptation
While we found no evidence for a consistent pattern of local adaptation of aerobic
50
scope to the average and maximum temperatures among the populations we studied, this does
2
not mean that adaptation is irrelevant. High latitude populations may be adapted to the greater
52
range of seasonal temperatures that they experience when compared with low latitude
populations, leading to improved capacity to perform at a range of temperatures, including
54
higher temperatures outside the normal range experienced. This could produce an apparent
mismatch between the average temperatures experienced in high latitude populations and the
56
temperatures where aerobic scope is the greatest. Consequently, our results could indicate that
reef fish populations are more closely adapted to seasonal temperature variation than they are
58
to the average temperatures they experience. There could also be other traits that provide
evidence for local thermal adaptation (e.g. reproductive timing). Furthermore, despite no
60
obvious adaptation of aerobic scope to different temperatures across latitudes, it does not
follow that local adaptation of aerobic scope could not occur once temperatures exceed the
62
natural range. The magnitude of selection and trade-offs in genetic correlations among
traits(Mundayet al., 2013) may be very different at temperatures outside the normal range
64
when compared with temperatures within the normal range. As a consequence, there could be
adaptation to rapid climate change in the future, even in cases where there is no strong
66
evidence for local adaptation to existing natural temperature variation (Mundayet al., 2013).
68
Fig. S1Representative traces from three individual C. atripectoralis chased to exhaustion and
then immediately placed into respirometry chambers where ṀO2 could be monitored until
70
recovery, which was sooner than 2h (Rummer, unpublished data).
72
Fig. S2Absolute aerobic scope (ṀO2Max - ṀO2Rest) for five coral reef fish species from three
populations (see legend for symbols) investigated upon acclimation to 27, 29, 31, 32, 33,
74
and/or 34°C. Note: D. melanurus was only investigated at the equatorial site; whereas,D.
3
aruanus was investigated only at Lizard and Heron Islands.All data are means ±S.E.M., n≥8
76
for each species and each temperature.
78
Supporting References(not cited in main text)
Couturier CS, Stecyk JAW, Rummer JL, Munday PL, Nilsson GE (2013) Species-specific effects of
80
near-future CO2 on the respiratory performance of two tropical prey fish and their predator.
Comparative Biochemistry and Physiology, Part A: Molecular and Integrative
82
Physiology,166, 482-489.
Rummer JL, Stecyk JAW, Couturier CS, Watson S-A, Nilsson GE, Munday PL (2013) Elevated CO2
84
enhances aerobic scope of a coral reef fish. Conservation Physiology,1.
Munday PL, Warner RR, Munro K, Pandolfi JM, Marshall DJ (2013) Predicting evolutionary
86
responses to climate change in the sea. Ecology Letters, doi: 10.1111/ele.12185.
4
Download