Biomineral production in marine organisms employs transient phases of amorphous calcium carbonate (ACC) in the construction of crystalline shells. Increasing seawater pCO2 leads to ocean acidification (OA) with a reduction in oceanic carbonate concentration which could have a negative impact on shell formation and therefore survival. We demonstrate significant changes in the hydrated and dehydrated forms of ACC in the aragonite and calcite layers of Mytilus edulis shells cultured under acidification conditions (1000 μatm pCO2) compared to present day conditions (380 μatm pCO2). In OA conditions, Mytilus edulis has more ACC at crystalisation sites. Here, we use the high-spatial resolution of synchrotron X-ray Photo Emission Electron Microscopy (XPEEM) combined with X-ray Absorption Spectroscopy (XAS) to investigate the influence of OA on the ACC formation in the shells of adult Mytilus edulis. Electron Backscatter Diffraction (EBSD) confirms that OA reduces crystallographic control of shell formation. The results demonstrate that OA induces more ACC formation and less crystallographic control in mussels suggesting that ACC is used as a repair mechanism to combat shell damage under OA. However, the resultant reduced crystallographic control in mussels raises concerns for shell protective function under predation and changing environments.
Marine organisms, such as molluscs1 and echinoderms2,3, use amorphous calcium carbonate (ACC) as a transient phase in the formation of crystalline shell structures, moulding a solid crystalline shell from the inherent disorder of ACC4. Phase transitions in biogenic calcium carbonate are therefore important in our understanding of how calcifying organisms produce protective shells. Molluscs and other marine organisms can maintain ACC, even in mature biominerals, as a means of moving high concentrations of insoluble material (CaCO3) to crystalisation sites for continued growth and repair4. However, even though ACC is a precursor to aragonite and calcite production for shell formation5,6,7, the transformation of ACC into ordered crystalline polymorphs is not well understood. The least stable transient form of ACC is dehydrated5 with 1/3 of a water molecule, on average, loosely bound to each CaCO34. Under super saturation, this unstable dehydrated form of ACC becomes hydrated with each CaCO3 binding to a water molecule. The more stable hydrated ACC can then be transported and deposited by precipitation through dehydration to form crystalline aragonite or calcite for shell formation4,6. In the larvae of molluscs, Mercenaria mercenaria and Crassostrea gigas, ACC is an important precursor to aragonite formation in early postset juvenile shells6. However, for the sea urchin, Strongylocentrotus purpuratus, hydrated ACC is coincident with crystalline calcite5 implying that a direct transformation process is unlikely and a complex control for growth and repair is employed4.
Increasing carbon dioxide (pCO2) concentrations leading to ocean acidification (OA) have the potential to alter biomineralisation pathways in molluscs, producing changes in shell structure with implications for the survival of molluscs8. Current projections for increases in atmospheric CO2 concentration predict a range of 855–1130 μatm by the year 21009 with the potential for a reduction in ocean carbonate saturation states10. Increasing seawater pCO2 can then result in a decrease in the concentration of carbonate impacting intracellular precipitation of amorphous calcium carbonate1 with diminished shell ultrastructure8. Changes in shell ultrastructure would impact organism control and mechanisms involved in the shell production.
This study examines the influence of OA on ACC formation in the mussel shell. The common blue mussel Mytilus edulis is a globally economically important food resource11 that produces a shell comprising two polymorphs of calcium carbonate: aragonite (nacreous layer) and calcite (prismatic layer)8. High-resolution X-Ray Photo Emission Electron Microscopy (XPEEM) combined with X-ray Absorption Spectroscopy (XAS) is used to identify mineral phases throughout the Mytilus edulis shell structure cultured under current (380 μatm pCO2) and OA scenarios (1000 μatm pCO2). The structural phases from the outermost calcite prismatic layer to the innermost aragonite nacreous layer of the shell are determined using Electron Backscatter Diffraction (EBSD). The results demonstrate that OA induces more ACC formation and less crystallographic control in mussels.
XPEEM Ca-L edge analysis of the ACC
There are distinct differences in shell morphology from the outermost to the innermost regions separated by an interface shown in the XPEEM images in Fig. 1. The XPEEM results confirm that the shell structure comprises different polymorphs of CaCO3 with the outermost layer comprising prismatic calcite and the innermost area aragonite tablets12. Figure 1 shows high-resolution XPEEM images, recorded at the Ca L3 edge, for three representative areas of the Mytilus edulis shell structure covering the outermost (calcite, near seawater) to the innermost (aragonite, near mussel tissue) region. XPEEM combined with XAS is a powerful element-specific probe of local electronic structure with a spatial resolution of ~30 nm13. Figure 2 shows spatially resolved XAS spectra over the Ca L2,3 edges from four separate regions of the shell depicted in the XPEEM images (Fig. 1), labelled as outer calcite, interface calcite, interface aragonite and inner aragonite, for mussels grown under present day and OA conditions. In each XAS spectrum at least 6 features are visible and labelled 1–6. These features show a very close resemblance to calculated XAS spectra over the Ca L2,3 edges or Ca2+ ions in octahedral symmetry13,14,15. We first note that Ca XAS spectra for aragonite regions shown in Fig. 1 are very similar to those reported for synthetic aragonite16 except that peak 2 is more intense. However, the spectra for calcite reported in this study do not show the intense feature at the binding energy of peak 5 reported in previous studies3,5,16. The reason for this discrepancy is not clear, but we rule out beam damage since no changes in the spectra were observed with time. The changes in the peak intensities in these spectra are a reliable indicator of the relative abundance of aragonite, calcite and ACC in the shell structures under present day and OA conditions.
ACC deposition under OA
Comparison of the Ca XAS spectra for aragonite and calcite layers in shells grown under present day (380 μatm pCO2) and OA (1000 μatm pCO2) conditions reveals a number of notable changes in the spectra. In mussel shells grown under OA conditions, compared to present day conditions, peak 2 has a marked reduction in intensity. The change in intensity of peak 4 is more difficult to determine, due to the appearance of the low energy shoulder on peak 3, but the analysis reveals a clear reduction in intensity. These changes can be quantified using the ratio of the peak intensities to the background level (Fig. 2, supplementary information Fig. 1). Peak 2 has a ratio ranging from 1.28 to 1.53 and peak 4 has ratio of 0.84 to 0.98 for shells grown under present day conditions. Under OA conditions Peak 2 has a ratio ranging from 0.99 to 1.17 and peak 4 has a ratio from 0.67 to 0.69. A qualitative comparison of the Ca XAS spectra grown under OA conditions in this study (solid black lines in Fig. 2) with those reported for ACC3,5,16 reveals a close similarity to the Ca XAS spectra reported for ACC. A quantitative comparison of the changes in the intensity of peak 2 and peak 4, with the quantitative changes reported3, also demonstrates the presence of ACC in the shells grown under OA conditions. Furthermore, peaks 1 and 3 are significantly broader for the spectra recorded from those shells grown under OA conditions in agreement with Rez and Blackwell (2011)14 (Fig. 2). The changes in these peak intensities therefore indicate the presence of ACC for those shells grown under OA conditions. Finally, we note that the feature marked with a dotted line at a photon energy of 349.7 eV in Fig. 2(a) gradually increase in intensity from the outer calcite to the inner aragonite indicating a gradual change in Ca coordination across the shell16.
EBSD analysis of crystallographic orientation
The EBSD analyses support the XPEEM results confirming that the shell structure comprises two different polymorphs of CaCO3 (Fig. 3). The crystallographic orientation from the outer calcite to the inner aragonite for shells grown under present day (380 μatm pCO2) and future projected OA conditions (1000 μatm pCO2) determined using EBSD is shown in Fig. 3. The mussel shells grown under OA have a thinner aragonite layer compared to those mussel shells grown under present day conditions confirmed through phase analysis (Fig. 3iii). Diffraction intensity maps (Fig. 3ai,bi) also indicate that mussel shells grown under OA do not diffract as well as those grown in present day conditions. In addition, crystallographic orientation appears to be less constrained in the calcite areas of those mussel shells grown under OA compared to those shells grown under present day conditions (Fig. 3aiii,biii); represented by increased variation in colour change in the crystallographic orientation maps (Fig. 3bii) corresponding to the colour keys. The reduction in crystallographic control is confirmed by the inverse pole figures (Fig. 3), which indicate the crystallographic preferred orientation (CPO) or spread of data points (orientations) within the crystallographic orientation map (Fig. 3ii). Calcite has a crystallographic orientation angle spread of 40° in those shells cultured under OA compared to 15° in those mussel shells grown under present day conditions (Fig. 3). In contrast, aragonite is more constrained in those mussel shells grown under OA compared to present day conditions, with inverse pole figures indicating a crystallographic orientation spread of 20° compared to 35° respectively (Fig. 3). The diffraction intensity was compared by examining the grey values of the diffraction intensity maps (Fig. 3ai,bi). Aragonite and calcite produced poorer diffraction i.e. higher (darker) grey values of 231.3 ± 31.0 and 228.2 ± 11.6 (Mean ± standard deviation of pixel grey value) in those shells grown under OA compared to 161.7 ± 31.0 and 164.4 ± 28.3 in those shells grown under present day conditions (Supplementary information, Fig. 2).
XAS spectra of the Ca-L2,3 edges of a synthetic aragonite and calcite have been compared previously15, with notable differences. The XAS spectra reported in this study are the first Ca-L2,3 edges for biogenic aragonite and calcite comparison in the mussel M. edulis, both appearing as previously reported spectra for synthetic calcite15. The similarities in XAS spectra reported for biogenic aragonite and calcite might be due to distortions of the oxygen octahedra in M. edulis shells which differ to those presented in other studies or perhaps calcite may not be in an entirely pure phase; this may be expected as organisms exhibit exquisite control over biomineral formation for biological functions4,8. Nevertheless the changes in the spectra observed for shells grown under present day conditions and shells grown under ocean acidification (OA) conditions are clear in both the aragonite and calcite areas as illustrated in Fig. 3 where calcite and aragonite are readily distinguished by EBSD. Gong et al. (2012)5 defined three types of Ca L-edge XAS spectra for the sea urchin Stronylocentrotus pupuratus spicule: hydrated ACC, dehydrated ACC and crystalline calcite with all three types co-existing within the spicule. As noted, previously reported studies demonstrated that a loss of intensity in peak 2 and 4 along with a small shift in the spectral weight of peak 3 (e.g. marked by the solid vertical line in Fig. 2(a)) indicates the presence of hydrated ACC. Furthermore, a less pronounced loss of intensity in peak 2 indicated the presence of dehydrated ACC14,15.
ACC is an important transient phase in mollusc shell formation enabling the crystallisation of the shell1,4. Changes to the availability of ACC within shells grown under OA would impact the ability of the mollusc to produce a protective crystalline shell. Hydrated ACC is present in greater concentrations in mussel shells grown under OA conditions, compared to present day conditions, this is confirmed by XAS spectra indicating a marked reduction in peak 2 and the reduction in peak intensity ratio (<1) for peaks 2 and 4. A comparison with the changes in the reference spectra of 3,15 confirms that the XAS spectra support hydrated ACC presence to a higher degree in shells grown under OA conditions. The presence of more hydrated ACC would imply less crystalline order in shells of Mytilus edulis grown under OA conditions. It has been suggested that the structural water presented with hydrated ACC is less important for stabilisation, but more important for lowering the energy barrier for precipitation of ACC17. Precipitation of hydrated ACC in those shells grown under OA conditions could then be an energetically cost-effective means of producing ACC17 for shell repair4. The increases in the availability of hydrated ACC provide an insight into the ability of the mussel to continue shell formation and repair under future OA.
EBSD analyses indicate less constraint over crystallographic orientation of calcite in those mussel shells grown under OA (Fig. 3b) compared to present day conditions, in agreement to previous Mytilus edulis studies8. Diffraction intensity maps indicate less diffraction of the CaCO3 in those mussel shells grown under OA. The higher (darker) grey values represent reduced diffraction intensity in those shells grown under OA. Poorer diffraction in those shells grown under OA would indicate less crystalline structure12, which supports the findings of the XPEEM analyses with more ACC present in those shells. The EBSD analyses complement the findings of the XPEEM analyses, which indicate that shells grown under OA conditions contain more hydrated ACC throughout all phases of the shell CaCO3 polymorphs.
When cultured under OA conditions, mussels have less control over the crystallographic orientation of their shell components. The results demonstrate that OA induces more ACC formation in mussel shells. The hydrated ACC in the shell may act as a less energetic means of ACC precipitation for shell production or repair4. However, the reduced crystallographic control in mussels raises concerns for shell protective function under predation and changing environments.
Mussel collection and culture
Mussels (M. edulis) were obtained from the Loch Fyne, Argyll, Scotland (Loch Fyne Oysters Ltd) during October 2012. Mussels were placed into experimental tanks (six L) supplied with natural filtered (1 μm and UV) seawater at Loch Fyne temperatures and ambient (~380 μatm) and OA (1000 μtm) pCO28. Mussels were fed 10 ml of cultured microalgae (five species of zooplankton, Nannochloropsis sp., Tetraselmis sp., Isochrysis sp., Pavlova sp., Thalassiosira weissflogii (stock from Reefphtyo, UK,) per tank every other day. M. edulis were grown from one year old juveniles for four months of experimental culture, following established protocols8.
Experimental culture was conducted at 380 and 1000 μatm pCO2, under seasonal temperatures and day length (light) of the collection site (Loch Fyne, Scotland). CO2 was mixed into air lines supplying all experimental tanks, following established protocols8,12,18. Water changes combining seawater and freshwater allowed for maintained experimental conditions similar to those experienced at the collection site in Loch Fyne where freshwater attributes result in existing reduced total alkalinity and carbonate saturation states8,12. Seawater salinity, temperature and dissolved oxygen (DO) were checked daily and recorded once a week (YSI Pro2030). Seawater samples were collected (once per month)8,12,19 and total alkalinity (AT) was determined using standard semi - automated8,12,19, combining the spectrometric analysis using bromocresol indicator8,12,20 and dissolved inorganic carbon (DIC) using an Automated Infra Red Inorganic Carbon Analyzer (AIRICA, Marianda instruments). Certified seawater references materials for oceanic CO2 (Batch 123, Scripps Institution of Oceanography, University of California, San Diego) were used as standards to quantify the error of analysis (Measured TA μmol kg−1, 2141 ± 54 μmolkg-1, CRM value 2225.21 ± 0.14 μmolkg-1)19. Seawater AT, DIC, salinity, temperature and pCO2 were used to calculate other seawater parameters using CO2Sys21 (Supplementary information, Table 1). Seawater samples in triplicate for three areas surrounding the natural Loch Fyne culture have also been analysed for carbonate chemistry (Supplementary information, Table 1)8,12.
Mussel shells were cleaned, dried (60 °C for 48 hours) and embedded in epoxy resin (EpoxyCure, Buehler) blocks. Embedded shells were sliced transversely using a diamond trim saw blade to section the whole length of the shell. New growth was determined through calcein staining of growth bands at the start of experimental culture as detailed in8,22; any growth prior to this stained growth band was named old growth which occurred prior to experimental culture. The new growth at the outer edge of the shell (containing newest calcite) and towards the newest aragonite formation (containing both newest aragonite and older calcite) was sectioned and mounted in a resin block before polishing the cut edge of the shell. Resin blocks were ultra-polished using aluminium oxide (0.3 and 1 μm) and colloidal silica (0.6 μm). The sections of ~2 mm were then prepared as thin sections into discs and polished through to 0.06 mm colloidal silica.
Photo Emission Electron Microscopy
Ultra-polished shell sections of Mytilus edulis shell were coated with 1.2 nm platinum (Pt). Sections only from the newest shell growth were examined using XPEEM to ensure grown during 4 months of experimental culture. Shells grown at 380 μatm and 1000 μatm pCO2 were imaged across the width of the shell from the internal part of the mussel shell containing aragonite to the external calcite. XPEEM images were recorded at the Ca L3 edge. A step size of 0.1 eV for energies between 340–344, 0.05 eV for energies between 344–345 and 0.1 eV for energies between 354–355 was used throughout imaging of shell samples to acquire data. Spectra were normalised at the pre-edge and a linear background subtracted, pixels were analysed typically from 5E4 to 2E5 pixels. The spectra shown are from one specimen for each treatment. Multiple areas on the same specimens were analysed to confirm the trends between treatments and two specimens were analysed for each treatment.
Electron Backscatter Diffraction
Calcite and aragonite crystallographic orientation of the samples was examined using EBSD with a beam voltage of 20 kV under low vacuum mode (~50 Pa) on the FEI Quanta 200 F Environmental SEM with the stage tilted to 70° to examine backscatter Kikuchi patterns23. Crystallographic orientation was imaged from the outermost calcite to the innermost aragonite at the centre of the section of shell taken from the new growth of the mussel. Crystallographic orientation maps were produced through OIM Analysis 6.2 software. EBSD results are presented as crystallographic inverse pole figures indicating spread or constraint in crystallographic orientation, the colour key indicates strength of CPO or texture. The orientation maps are also presented with each colour representing a particular crystallographic orientation (confidence index <0.1 removed).
Data availability: The dataset relating to the figures in this manuscript is available at: DOI: 10.5525/gla. researchdata.259
How to cite this article: Fitzer, S. C. et al. Biomineral shell formation under ocean acidification: a shift from order to chaos. Sci. Rep. 6, 21076; doi: 10.1038/srep21076 (2016).
Huning, A. et al. Impacts of seawater acidification on mantle gene expression patterns of the Baltic Sea blue mussel: implications for shell formation and energy metabolism. Marine Biology 160, 1845–1861 (2013).
Beniash, E., Aizenberg, J., Addadi, L. & Weiner, S. Amorphous calcium carbonate transforms into calcite during sea urchin larval spicule growth. Proceedings of the Royal Society B-Biological Sciences 264, 461–465 (1997).
Politi, Y. et al. Transformation mechanism of amorphous calcium carbonate into calcite in the sea urchin larval spicule. Proceedings of the National Academy of Sciences of the United States of America 105, 17362–17366 (2008).
Addadi, L., Raz, S. & Weiner, S. Taking advantage of disorder: Amorphous calcium carbonate and its roles in biomineralization. Advanced Materials 15, 959–970 (2003).
Gong, Y. U. T. et al. Phase transitions in biogenic amorphous calcium carbonate. PNAS 109, 6088–6093 (2012).
Weiss, I. M., Tuross, N., Addadi, L. & Weiner, S. Mollusc larval shell formation: Amorphous calcium carbonate is a precursor phase for aragonite. Journal of Experimental Zoology 293, 478–491 (2002).
Radha, A. V., Forbes, T. Z., Killian, C. E., Gilbert, P. U. P. A. & Navrotsky, A. Transformation and crystallization energetics of synthetic and biogenic amorphous calcium carbonate. Proceedings of the National Academy of Sciences of the United States of America 107, 16438–16443 (2010).
Fitzer, S. C., Phoenix, V. R., Cusack, M. & Kamenos, N. A. Ocean acidification impacts mussel control on biomineralisation. Sci. Rep . 4, 6218 (2014).
IPPC. Summary for policymakers. in Climate Change 2007: Impacts, Adaptation and Vulnerability. Contribution of Working Group II to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change (eds. Parry, M., Canziani, O., Palutikof, J., Van der Linden, P. & Hanson, C. ) 81–82 (Cambridge, 2007).
Doney, S. C., Fabry, V. J., Feely, R. A. & Kleypas, J. A. Ocean acidification: the other CO2 problem. Annual Review of Marine Science 1, 169–192 (2009).
FAO. Food and Agriculture Organization of the United Nations Annual report. Fishery and Aquaculture Statistics (2012).
Fitzer, S. C., Cusack, M., Phoenix, V. R. & Kamenos, N. A. Ocean acidification reduces the crystallographic control in juvenile mussel shells. Journal of Structural Biology 188, 39–45 (2014).
Krüger, P. & Natoli, C. R. X-ray absorption spectra at the Ca L2,3 edge calculated within multichannel multiple scattering theory. Physical Review B 70, 245120 (2004).
Rez, P. & Blackwell, A. Ca L23 spectrum in amorphous and crystalline phases of calcium carbonate. The Journal of Physical Chemistry B 115, 11193–11198 (2011).
DeVol, R. et al. Oxygen Spectroscopy and Polarization-Dependent Imaging Contrast (PIC)-Mapping of Calcium Carbonate Minerals and Biominerals. Journal of Physical Chemistry B 118, 8449–8457 (2014).
de Groot, F. M. F., Fuggle, J. C., Thole, B. T. & Sawatsky, G. A. L2,3 x-ray absroption edgesof d0 compounds: K+, Ca2+,SC3+ and Ti4+ in Oh (octahedral) symmetry. Physical Review B 41, 928–937 (1990).
Ihli, J. et al. Dehydration and crystallization of amorphous calcium carbonate in solution and in air. Nature Communications 5, 3169 (2014).
Findlay, H. S., Kendall, M. A., Spicer, J. I., Turley, C. & Widdicombe, S. Novel microcosm system for investigating the effects of elevated carbon dioxide and temperature on intertidal organisms. Aquatic Biology 3, 51–62 (2008).
Dickson, A. G., Sabine, C. L. & Christian, J. R. Guide to best practises for ocean CO2measurements (2007).
Yao, W. S. & Byrne, R. H. Simplified seawater alkalinity analysis: Use of linear array spectrometers. Deep-Sea Research Part I-Oceanographic Research Papers 45, 1383–1392 (1998).
Riebesell, U., Fabry, V. J., Hansson, L. & Gattuso, J.-P. Guide to best practices for ocean acidification research and data reporting, (Publications Office of European Union, Luxembourg, 2007).
Mahe, K., Bellamy, E., Lartaud, F. & de Rafelis, M. Calcein and manganese experiments for marking the shell of the common cockle (Cerastoderma edule): tidal rhythm validation of increments formation. Aquatic Living Resources 23, 239–245 (2010).
Perez-Huerta, A. & Cusack, M. Optimizing Electron Backscatter Diffraction of Carbonate Biominerals-Resin Type and Carbon Coating. Microscopy and Microanalysis 15, 197–203 (2009).
This study was funded by the Leverhulme Trust project entitled ‘Biomineralisation: protein and mineral response to ocean acidification’ awarded to M.C., N.K., V.P. and M.C. also gratefully acknowledges BBSRC BB/E025110/1. XPEEM analysis was funded by Diamond Light Source grant SI-9515 entitled ‘ACC formation under environmental ocean acidification’ awarded to M.C., S.C.F. and P.C. We are grateful to Loch Fyne Oysters for providing the mussels for this study.
The authors declare no competing financial interests.
Electronic supplementary material
About this article
Cite this article
Fitzer, S., Chung, P., Maccherozzi, F. et al. Biomineral shell formation under ocean acidification: a shift from order to chaos. Sci Rep 6, 21076 (2016). https://doi.org/10.1038/srep21076
Global Change Biology (2021)
Differential responses in anti-predation traits of the native oyster Ostrea edulis and invasive Magallana gigas to ocean acidification and warming
Marine Ecology Progress Series (2021)
Identification, characterization and expression analyses of cholinesterases genes in Yesso scallop (Patinopecten yessoensis) reveal molecular function allocation in responses to ocean acidification
Aquatic Toxicology (2021)
Evolutionary Applications (2021)
Biological Impact of Ocean Acidification in the Canadian Arctic: Widespread Severe Pteropod Shell Dissolution in Amundsen Gulf
Frontiers in Marine Science (2021)