globalchange  > 气候变化事实与影响
DOI: doi:10.1038/nclimate2616
论文题名:
Physiological advantages of dwarfing in surviving extinctions in high-CO2 oceans
作者: Vittorio Garilli
刊名: Nature Climate Change
ISSN: 1758-950X
EISSN: 1758-7070
出版年: 2015-04-20
卷: Volume:5, 页码:Pages:678;682 (2015)
语种: 英语
英文关键词: Ecology
英文摘要:

Excessive CO2 in the present-day ocean–atmosphere system is causing ocean acidification, and is likely to cause a severe biodiversity decline in the future1, mirroring effects in many past mass extinctions2, 3, 4. Fossil records demonstrate that organisms surviving such events were often smaller than those before5, 6, a phenomenon called the Lilliput effect7. Here, we show that two gastropod species adapted to acidified seawater at shallow-water CO2 seeps were smaller than those found in normal pH conditions and had higher mass-specific energy consumption but significantly lower whole-animal metabolic energy demand. These physiological changes allowed the animals to maintain calcification and to partially repair shell dissolution. These observations of the long-term chronic effects of increased CO2 levels forewarn of changes we can expect in marine ecosystems as CO2 emissions continue to rise unchecked, and support the hypothesis that ocean acidification contributed to past extinction events. The ability to adapt through dwarfing can confer physiological advantages as the rate of CO2 emissions continues to increase.

The present rate of ocean acidification is a global concern because many of the mass extinction events that affected evolution of life on Earth are associated with evidence for elevated CO2 and global warming, triggered by large-scale continental volcanism3. These include the largest known extinction event, which occurred in the late Permian2, 8, where atmospheric CO2 levels are estimated to have increased by a factor of four to six9, 10, and the Late Triassic event that saw a doubling in CO2 levels4 and was the most severe extinction to have affected extant groups such as scleractinian corals11. Evidence that ocean acidification due to volcanism played a significant role in past marine extinctions comes from analyses of physiological selectivity12, and changes in shell mineralogy and lithology13. In the immediate aftermath of the mass extinction events, many of the survivors were smaller than before5 (for example, brachiopods14, gastropods14, bivalves and shelled cephalopods6); a phenomenon termed the ‘Lilliput effect7. After the most severe Late Permian extinction, gastropod species remained relatively small for millions of years15. One hypothesis is that this dwarfing was an adaptation to ocean acidification to mitigate against the increased energetic cost of carbonate secretion8. Calcifiers use the ion transporter Ca2+ATPase to build shells/skeletons which pumps protons out of the extracellular calcifying medium, increasing the internal pH and favouring calcification. This is an energetically expensive process16, the cost of which increases for animals exposed to high pCO2 conditions. For instance, scleractinian corals have an extra metabolic cost of about 10% per 0.1 unit decrease in seawater pH (ref. 17). It is possible that faced with an increase in calcification costs, some species may adapt by decreasing in size18.

Areas with naturally high levels of CO2 provide opportunities to study the adaptation of organisms exposed to chronic hypercapnia19, 20. At such sites, increased CO2 levels cause biodiversity loss on sufficiently large spatial and temporal scales to reveal ocean acidification effects at the ecosystem level21, 22. Off Vulcano Island, Sicily23, seep gas composition is 97–98% CO2, which acidifies the surrounding waters down to pHT 5.64 (where pHT is the pH value based on the total hydrogen ion concentration scale) near the main seeps, rising to ambient levels of pHT 8.2 over a distance of around 400 m (ref. 23). Traces of other hydrothermal gases (H2, CH4 and H2S) are also present near the seeps but become undetectable around 5 m away23. Seawater temperature and oxygen levels reach ambient values a few tens of metres from the main seep area. At about 100 m from the main seeps the nassariid gastropods Nassarius corniculus and Cyclope neritea are abundant on coarse sand and gravel (Fig. 1). These species are widespread in coastal lagoons and salt marshes in the Mediterranean as well as at shallow-water hydrothermal seeps (for example, off Milos24 and Pantelleria25). We know that populations of C. neritea and N. corniculus had developed at the CO2 seeps because their shells had paucispiral protoconches indicating these snails lack a planktotrophic larval stage (see Supplementary Information for more details). Seawater off Vulcano has been acidified since the late Pleistocene epoch23 and a dwarf population of N. corniculus has been present for at least 30 years25, providing an opportunity to study chronic effects of ocean acidification on gastropods submitted to high CO2 levels over multiple generations.

Figure 1: Shells of the investigated species.
Shells of the investigated species.

ad, Samples of Cyclope neritea (a,c) and Nassarius corniculus (b,d) living at CO2 seeps (a,b) showing shell dissolution and apex truncation when compared to shells collected at reference site C1, ambient pH (c,d).

Sampling sites.

For shell morphometric parameters, scanning electronic microscopy analyses, gross calcification and metabolic rate measurements, Nassarius corniculus and Cyclope neritea were collected in September and November 2011 at CO2 seeps off Vulcano Island (northern Sicily, Aeolian Archipelago, Tyrrhenian Sea), and at reference site C1 in the Stagnone of Marsala (western Sicily; Supplementary Fig. 1). Specimens of N. corniculus were also collected at two other reference sites—Lampedusa Island (C2; southern Sicily) and San Giovanni Li Cuti (C3; eastern Sicily)—and their shell morphometric parameters were measured.

Seawater carbonate chemistry.

Seawater carbonate chemistry variations at CO2 seeps were frequently measured during our previous studies (for example, ref. 22). Total alkalinity (AT) and pH expressed in total scale (pHT) were measured during the 2–3 day sample collections in September and November 2011, and routinely during aquarium experiments (Supplementary Information). Parameters of the carbonate system were calculated from pHT, mean AT, temperature and mean salinity (38) using the free-access CO2SYS package. pH variation at CO2 seeps was measured over a 24-h cycle using a multiparametric probe (556 MPS YSI) positioned at 2 m depth.

Shell morphometric and scanning electron microscopy analyses.

Samples were preserved in 70% ethanol after collection. Morphometric parameters, such as total shell height (Ht), shell maximum width (W), shell width at the suture between last and penultimate whorl (Ws), last whorl height (Hlw), aperture height (Ha) and thickness of the outer lip (Olt), were measured on adult C. neritea and N. corniculus shells collected at CO2 seeps and the three reference sites C1–C3 using a stereomicroscope. Nassarius corniculus shell macro- and microstructures were investigated using a LEO 420 scanning electron microscope on samples from Vulcano and the reference site C1.

Aquarium experiments and gross calcification (GC).

After collection, both in September and November 2011, samples were transported to the IAEA-MESL laboratory in Monaco. They were maintained in flow-through aquaria containing sediments collected from sampling sites. C. neritea were divided per site of collection at field pH (sites C1, pHT 8.0 and CO2 seep, pHT 7.2–7.3) whereas N. corniculus were incubated using a two-way orthogonal experimental design (acclimation state/Origin × pH) to measure the GC rates of samples collected within and outside the vents at crossed pH treatments. Half of the N. corniculus from both sites were incubated at temperature and pH conditions similar to in situ values (CO2 seep: pHT 7.2–7.3; site C1: pHT 8.0; Supplementary Table 1), whereas the remaining specimens were incubated at pHT 7.2–7.3 and pHT 8.0 for specimens from reference and CO2 seep sites, respectively. After two weeks, samples were transferred in separated 6 litre aquaria (two to three replicate tanks for each site/pH treatment) and their GC were measured with the radiotracer 45Ca (Supplementary Information).

Metabolic rates.

Metabolic oxygen consumption (MO2) was determined for C. neritea and N. corniculus from both CO2 seeps and reference site C1 within 24 h of collection. During individual incubations, gastropods were allowed to acclimatize to the respirometry chambers, receiving fully oxygenated water from their site of collection at pHNBS 6.5 or pHNBS 8.1 for individuals collected at CO2 seeps and reference site C1, respectively. After 1 h acclimatization the chambers were closed, measurement run for another hour and the decrease in pO2 within each respirometer stop-flow chamber measured using a polarographic O2 electrode (E-5046 electrode, Radiometer) connected to an oxygen meter (Strathkelvin Oxygen Meter 781). Then, specimens were killed to measure their shell-free wet-body mass for use as a covariate in GLM analysis of MO2.

Statistical analysis.

Univariate data on shell morphometric parameters (Supplementary Information), GC and metabolic rates were analysed using GLM in SPSS 21.0; data are presented as mean ± s.d. Pair-wise comparisons between treatments were performed using a priori contrasts based on estimated marginal means and Tukeys LSD tests. Conformity to assumptions of GLM was confirmed by homogeneity of variances testing and inspection of analytical residuals; transformations were used when necessary. Multivariate analyses of overall organism shape were conducted using PERMANOVA in PRIMER version 6.1 (see Supplementary Information for all details and results).

  1. Mora, C. et al. Biotic and human vulnerability to projected changes in ocean biogeochemistry over the 21st century. PLoS Biol. 11, e1001682 (2013).
  2. Benton, M. J. & Twitchett, R. J. How to kill (almost) all life: The end-Permian extinction event. Trends Ecol. Evol. 18, 358365 (2003).
  3. Kidder, D. L. & Worsley, T. R. Phanerozoic Large Igneous Provinces (LIPs), HEATT (HalineEuxinic Acidic Thermal Transgression) episodes, and mass extinctions. Palaeogeogr. Palaeoclimatol. Palaeoecol. 295, 162191 (2010).
  4. McElwain, J. C., Beerling, D. J. & Woodward, F. I. Fossil plants and global warming at the Triassic–Jurassic boundary. Science 285, 13861390 (1999).
  5. Twitchett, R. J. The Lilliput effect in the aftermath of the end-Permian extinction event. Palaeogeogr. Palaeoclimatol. Palaeoecol. 252, 132144 (2007).
  6. Morten, S. D. & Twitchett, R. J. Fluctuations in the body size of marine invertebrates through the Pliensbachian–Toarcian extinction event. Palaeogeogr. Palaeoclimatol. Palaeoecol. 284, 2938 (2009).
  7. Urbanek, A. Biotic crises in the history of Upper Silurian graptoloids: A palaeobiological model. Historical Biol. 7, 2950 (1993). URL:
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资源类型: 期刊论文
标识符: http://119.78.100.158/handle/2HF3EXSE/4778
Appears in Collections:气候变化事实与影响
科学计划与规划
气候变化与战略

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Vittorio Garilli. Physiological advantages of dwarfing in surviving extinctions in high-CO2 oceans[J]. Nature Climate Change,2015-04-20,Volume:5:Pages:678;682 (2015).
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