globalchange  > 气候变化事实与影响
DOI: doi:10.1038/nclimate2241
论文题名:
Biomineralization control related to population density under ocean acidification
作者: Stefano Goffredo
刊名: Nature Climate Change
ISSN: 1758-1304X
EISSN: 1758-7424
出版年: 2014-05-25
卷: Volume:4, 页码:Pages:593;597 (2014)
语种: 英语
英文关键词: Climate-change ecology
英文摘要:

Anthropogenic CO2 is a major driver of present environmental change in most ecosystems1, and the related ocean acidification is threatening marine biota2. With increasing pCO2, calcification rates of several species decrease3, although cases of upregulation are observed4. Here, we show that biological control over mineralization relates to species abundance along a natural pH gradient. As pCO2 increased, the mineralogy of a scleractinian coral (Balanophyllia europaea) and a mollusc (Vermetus triqueter) did not change. In contrast, two calcifying algae (Padina pavonica and Acetabularia acetabulum) reduced and changed mineralization with increasing pCO2, from aragonite to the less soluble calcium sulphates and whewellite, respectively. As pCO2 increased, the coral and mollusc abundance was severely reduced, with both species disappearing at pH < 7.8. Conversely, the two calcifying and a non-calcifying algae (Lobophora variegata) showed less severe or no reductions with increasing pCO2, and were all found at the lowest pH site. The mineralization response to decreasing pH suggests a link with the degree of control over the biomineralization process by the organism, as only species with lower control managed to thrive in the lowest pH.

Several studies on the influence of pH on crystallography and texture of calcified regions are ex situ, short-term experiments on isolated organisms5, providing important information, but unrepresentative of natural ecosystems and failing to assess long-term effects6. There is a great need for long-term analyses on ocean acidification effects on marine ecosystems acclimated to high pCO2, as found around CO2 vents. Vents are not perfect predictors of future oceans, owing to pH variability, proximity of unaffected populations, and co-varying environmental parameters7. However, vents acidify sea water on sufficiently large temporal and spatial scales to integrate ecosystem processes6, acting as ‘natural laboratories’. In Papua New Guinea vents, reductions in coral diversity, recruitment and abundance, and shifts in competitive interactions, are found8. In Mediterranean vents, decreased diversity, biomass, trophic complexity and abundance in many calcifying and non-calcifying organisms, and increases in macroalgae and seagrasses, are observed7, 9, 10.

We assessed, along a natural pH gradient, the effect of pCO2 on the mineralization and abundances of the aragonitic scleractinian B. europaea, the aragonitic tube-forming gastropod V. triqueter, the brown alga P. pavonica, which deposits aragonite on the thalli surface, the green alga A. acetabulum, whose cups’ outer surfaces are calcified with aragonite and a small amount of whewellite (calcium oxalate), and the non-mineralized brown alga L. variegata. The mineralization is biologically controlled in V. triqueter (that is, mineral is deposited in confined nucleation sites under complete biological control with minimal environmental effects), biologically induced in P. pavonica and A. acetabulum (that is, it is strongly affected by the environment with minimal biological control), whereas B. europaea may represent an intermediate and still controversial situation11. We aimed to assess changes in the mineralization and abundance of species along a pCO2 gradient in relation to their control over biomineralization.

Mean pH, CO2, saturation of calcite (Ωcalc), and of aragonite (Ωarag) differed among Sites (Kruskal–Wallis test/analysis of variance, p < 0.001). The median pH values were 8.1 (Site 1), 7.9 (Site 2), 7.8 (Site 3) and 7.7 (Site 4), with increasing variability towards Site 4 (Fig. 1 and Supplementary Fig. 1 and Table 1).

Figure 1: Range in pH total scale and mean percentage of cover for Balanophyllia europaea, Vermetus triqueter, Padina pavonica, Acetabularia acetabulum and Lobophora variegata along the pCO2 gradient.
Range in pH total scale and mean percentage of cover for Balanophyllia europaea, Vermetus triqueter, Padina pavonica, Acetabularia acetabulum and Lobophora variegata along the pCO2 gradient.

pH measures were 103–110 per site. Horizontal bars indicate the median pH. Error bars are 95% confidence intervals (CI).

Study site.

Fieldwork was conducted at Panarea, Italy (Supplementary Video and Fig. 1), where hydrothermally stable CO2 emissions acidify sea water, generating a pH gradient (see Supplementary Information for details).

Carbonate chemistry.

Four sampling Sites were selected (Fig. 1 and Supplementary Fig. 1): a control site (Site 1), two intermediate pCO2 sites (Site 2 and Site 3), and a high pCO2 site (Site 4). pH (NBS scale), temperature and salinity were measured at each Site during several surveys between July 2010 and May 2013 with a multi-parametric probe (600R, YSI Incorporated) powered from a small boat and operated by SCUBA divers. Bottom-water samples for determination of total alkalinity were collected and analysed using standard methods (see Supplementary Information for details). Further temperature data were recorded every three hours by sensors (Thermochron iButton, DS1921G, Maxim Integrated Products) attached in each Site from July 2010 to May 2013. Measured pH was converted to the total scale using CO2SYS software. Median pH (back-transformed hydrogen ion concentrations) were calculated for each Site. The pH, total alkalinity, salinity and temperature were used to calculate other carbonate system parameters using the software CO2SYS (Supplementary Information).

Benthic survey.

Photographs of benthos (5 to 10 per Site, 50 × 50 cm for the animals, 21.0 × 29.7 cm for the algae) were used to measure the percentage of cover for B. europaea, V. triqueter, P. pavonica, A. acetabulumand L. variegata at each Site. See Supplementary Information for details.

Vent gas.

Gas was sampled during five surveys (June 2011–May 2013) and analysed at the Laboratory of Fluid and Rock Geochemistry of the University of Florence using standard methods (Supplementary Information). Water samples were collected and tested for dissolved H2S (Supplementary Information).

Statistical analyses.

Analysis of variance and the post hoc Fisher least significant difference test were used to test for differences among Sites using arcsine and log-transformation for percentage of cover and environmental data, respectively, when necessary. Otherwise, the non-parametric Kruskal–Wallis and Spearman’s rank correlation coefficients were used. All analyses were performed using SPSS v.20.

Biomineralization.

Samples were randomly collected by SCUBA divers at all Sites and were prepared for analyses with standard methods (Supplementary Information). Microscopic observations and mechanical and spectroscopic measurements required the preparation of cross-sections of the samples (Supplementary Information). X-ray powder diffraction and Fourier transform infrared spectroscopy patterns on small amounts of powdered samples were collected using standard methods (Supplementary Information). Attenuated total reflection Fourier transform infrared spectra of sample cross-sections were acquired with standard methods (Supplementary Information). The organic matter content in the sample was determined by thermogravimetric analysis (Supplementary Information). Microstructures were observed using optical and scanning electronic microscopes (SEM; Supplementary Information). The mechanical properties of shell-tubes and skeletons were measured with standard nano-indentation techniques (Supplementary Information).

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  2. Orr, J. C. et al. Anthropogenic ocean acidification over the twenty-first century and its impact on calcifying organisms. Nature 437, 681686 (2005).
  3. Fabry, V. J., Seibel, B. A., Feely, R. A. & Orr, J. C. Impacts of ocean acidification on marine fauna and ecosystem processes. ICES J. Mar. Sci. 65, 414432 (2008).
  4. Rodolfo-Metalpa, R., Martin, S., Ferrier-Pages, C. & Gattuso, J. P. Response of Mediterranean corals to ocean acidification. Biogeosciences Discuss. 6, 71037131 (2010).
  5. Hahn, S. et al. Marine bivalve shell geochemistry and ultrastructure from modern low pH environments: environmental effect versus experimental bias. Biogeosciences 9, 18971914 (2012).
  6. Barry, J. P., Hall-Spencer, J. M. & Tyrrell, T. Guide to Best Practices for Ocean Acidification Research and Data Reporting (Publications Office of the European Union, 2010).
  7. Hall-Spencer, J. M. et al. Volcanic carbon dioxide vents show ecosystem effects of ocean acidification. Nature 454, 9699 (2008).
  8. Fabricius, K. E. et al. Losers and winners in coral reefs acclimatized to elevated carbon dioxide concentrations. Nature Clim. Change 1, 165169 (2011).
  9. Cigliano, M., Gambi, M. C., Rodolfo-Metalpa, R., Patti, F. P. & Hall-Spencer, J. M. Effects of ocean acidification on invertebrate settlement at volcanic CO2 vents. Mar. Biol. 157, 24892502 (2010).
  10. Porzio, L., Buia, M. C. & Hall-Spencer, J. M. Effects of ocean acidification on macroalgal communities. J. Exp. Mar. Biol. Ecol. 400, 278287 (2011).
  11. Lowenstam, H. A. & Weiner, S. On Biomineralization (Oxford Univ. Press, 1989).
  12. Holcomb, M., Cohen, A. L., Gabitov, R. I. & Hutter, J. L. Compositional and morphological features of aragonite precipitated experimentally from seawater and biogenically by corals. Geochim. Cosmochim. Acta 73, 41664179 (2009).
URL: http://www.nature.com/nclimate/journal/v4/n7/full/nclimate2241.html
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资源类型: 期刊论文
标识符: http://119.78.100.158/handle/2HF3EXSE/5126
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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Stefano Goffredo. Biomineralization control related to population density under ocean acidification[J]. Nature Climate Change,2014-05-25,Volume:4:Pages:593;597 (2014).
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