Algal Calcification and Silification Secondary article Article Contents . Calcification Colin Brownlee, Marine Biological Association of the UK, Plymouth, UK Alison R Taylor, Marine Biological Association of the UK, Plymouth, UK . Silification The algae represent major producers of calcium carbonate and silica among the world’s biota. Calcification involves the precipitation of CaCO3 from Ca2 1 and CO32 ions. Algal calcification may account for up to half of global oceanic CaCO3 production. Silicification is less widespread among algal groups, which transform dissolved silicate to skeletal material. Diatoms play a key role in marine silica cycling. Diatomaceous deposits have long been exploited for building and filling materials, and the low-temperature, low-pressure biogenic formation of silica has potential for biotechnological application in novel industrial processes. Calcification Overview Calcification is widespread among plant, animal, algal and prokaryotic groups and occurs with varying degrees of sophistication and complexity. Calcification involves the precipitation of CaCO3 from Ca2 1 and CO23 2 ions in solution. In most cases this involves the generation of microenvironments that allow supersaturation of CaCO3. Although many terrestrial and freshwater organisms are able to produce CaCO3, most of the world’s CaCO3 is produced in the oceans. Calcification has been widespread among the biota since at least the Cambrian era and probably evolved considerably earlier than this. Various explanations exist for the origin of calcification. As Ca2 1 levels increased in the early oceans, the precipitation of phosphate by Ca2 1 inside cells would become problematic, leading to selection of organisms that were able to extrude Ca2 1 from inside their cells to the external medium (Degens and Itterkkot, 1986). Grazing pressure and competition would also provide evolutionary driving forces for the development of biomineralized structures for defence and structural support of increasingly complex multicellular organisms. The most striking feature of calcification in the oceans is that it occurs almost exclusively by biogenic processes. Ca2 1 and CO23 2 inputs into the oceans occur through weathering of rocks, geothermal activity and hydrothermal seepage (Westbroek et al., 1993). The ocean is in fact supersaturated with Ca2 1 and CO23 2 . However, spontaneous chemical precipitation is largely absent owing to the high concentrations of inhibitory ions in seawater and the presence of crystal poisons produced by the biota. Among the algae, calcification can be found in both freshwater and marine species. The brackish-water giantcelled Charophyte alga Chara produces bands of CaCO3 along the length of its surface and has provided a good model for the study of the transport processes involved in external calcification (see Figure 1). A variety of marine multicellular macrophyte algae also produce CaCO3, including Corallina spp. and Halimeda spp. However, the most abundant calcifying algae are the free-living unicellular members of the Haptophyte division collectively known as the coccolithophores (see Figure 2). These are primarily marine and occur in all of the world’s oceans, sometimes forming vast monospecific blooms under appropriate conditions. Geological and economic importance Marine biogenic calcification and its connection to photosynthesis is an important though little understood process in the global carbon cycle. Three major classes of organisms are responsible for the bulk of oceanic calcification. These are the corals, foraminifera and the coccolithophorid phytoplankton. Many species of coral and forams form symbiotic associations with photosynthetic dinoflagellate algae (zooxanthellae). Although these symbiotic algae have been shown in many studies to enhance the process of calcification, they do not have a direct role in CaCO3 production, which is carried out by specialized cells of the host species. In terms of total CaCO3 production, the pelagic foraminifera and coccolithophores together probably represent the bulk of modern-day global CaCO3 production. While accurate estimates of the relative contributions of these organisms are lacking, it is likely that the coccolithophores represent up to half of all current global oceanic CaCO3 production. The oceans represent a significant sink for atmospheric CO2, removing approximately 30% of anthropogenic CO2 emissions. In this context oceanic calcification plays a significant role in the formation of a sink for inorganic ENCYCLOPEDIA OF LIFE SCIENCES / & 2002 Macmillan Publishers Ltd, Nature Publishing Group / www.els.net 1 Algal Calcification and Silification Ca2+ (a) (b) CaCO3 CaCO3 CO2 Ca2+ Alkaline H+ CO2 1 H2OKH2CO3KHCO32 1 H 1 KCO23 2 1 2H 1 [I] H+ A significant, and perhaps surprising, feature of oceanic calcification is that it is potentially a net producer of CO2, whereas dissolution of CaCO3 during rock weathering comprises a sink for atmospheric CO2 levels (eqn [II]) HCO3 H+ H+ HCO3 Acid CO2 CO2 HCO3 Chloroplast C Out carbon. Bicarbonate comprises more than 90% of the total dissolved inorganic carbon (DIC) in the oceans and most evidence suggests that this is the main carbon source for calcification. Marine photosynthesis and respiration are linked to calcification and CaCO3 dissolution, respectively, with significant effects on the alkalinity and pH of the oceans. DIC speciation occurs according to the reaction [I]. V In C Out Figure 1 Alternative models for the mechanism of external calcifying band production in the giant-celled alga Chara. In (a), calcification is driven by the diffusion of H 1 into the cell in localized regions, producing localized alkalinization of the cell surface and precipitation of CaCO3. In an adjacent region, H 1 is actively pumped out of the cell producing localized acidification of the cell surface. In (b), calcification is driven by the extrusion of Ca2 1 in exchange for H 1 in the alkaline zone. CO2 diffusion from the cell’s interior provides the carbon source for CO23 2 formation and CaCO3 precipitation. In both models, H 1 extrusion in the acidic zone facilitates the production of CO2 from HCO32 which can be used by photosynthesis in the chloroplasts (green). Ca2+ + 2HCO3– Calcification CaCO3 + H2O + CO2 CaCO3 dissolution [II] Photosynthesis requires CO2 and it is not surprising that the major calcifiers have direct associations with photosynthesis. CaCO3 production is largely limited to the upper photic zone of the ocean, while particulate inorganic carbon in the form of CaCO3 sinks to the deep ocean. The sinking is facilitated by zooplankton grazing and the formation of faecal pellets. In deeper waters, below the lysocline up to 90% of this CaCO3 gradually redissolves. The remainder contributes to vast calcareous sediments. Over much longer geological time scales ( 100 My) tectonic activity results in the subduction of sediments, and release of CO2 during volcanic activity or uplifting of sediments and weathering and dissolution of carbonates and recycling of DIC back to the oceans (Varekamp et al., 1992). The preservation of coccoliths in the sedimentary record has led to their use as palaeoclimate proxies. Coccolithophores also produce a wide range of long-chain alkene and alkenone hydrocarbons that are also preserved in the Figure 2 Model for fluxes of Ca2 1 , HCO32 and H 1 during calcification in coccolithophores. (a) Scanning electron micrograph of heterococcoliths on the surface of Coccolithus pelagicus cells (cell diameter=20 mm). (b) Ca2 1 and HCO32 uptake into a Golgi-derived compartment leads to the production of CaCO3 and H 1 during calcite precipitation. H 1 production can be used to counter the alkalinizing effect of CO2 production from HCO32 in the chloroplast (green) and removal of CO2 by photosynthesis. 2 ENCYCLOPEDIA OF LIFE SCIENCES / & 2002 Macmillan Publishers Ltd, Nature Publishing Group / www.els.net Algal Calcification and Silification sedimentary record (Grossi et al., 2000). Good evidence exists that the alkenone composition of coccolithophore populations varies with sea surface temperature, allowing studies of past coccolithophore abundance and palaeotemperature. Despite the obvious widespread uses of chalk, limestone and quartz in construction, chemical and other industries, the biotechnological applications of coccolithophores have been largely unexplored. Knowledge of the molecular processes involved in the production of highly ordered crystal structures such as coccoliths will undoubtedly improve understanding of the control of microscale ordered crystal growth. Mechanisms Different groups of algae form CaCO3 in strikingly different ways, and the cellular sites of calcification can be either internal or external, suggesting that calcification mechanisms evolved independently in different groups. The partial reaction of calcification (eqn [III]) indicates a potential physiological role for calcification in providing a source of H 1 that may be used in the production of CO2 from HCO32 (McConnaughey and Whelan, 1997) or for any other H 1 -requiring process. HCO32 KH 1 1 CO23 2 [III] In the marine environment, CO2 is present in micromolar concentrations, which may be lower than the dissociation constant (Km) for the photosynthetic carbon-fixing enzyme ribulose bisphosphate carboxylase oxygenase (Rubisco). Phytoplankton species that rely on CO2 diffusion to supply photosynthesis may be rate-limited by the CO2 concentration and diffusion to the site of Rubisco in the chloroplast. Several species of aquatic algae appear to have evolved mechanisms that allow utilization of external HCO32 as the external carbon substrate for photosynthesis (Raven, 1997). If taken in to the cell, this can be used as a source of CO2, facilitated by the action of carbonic anhydrase (CA) in the chloroplast (eqn [IV]). HCO32 KCO2 1 OH [IV] However, this process may become limited by the availability of H 1 , which will be needed to maintain cellular pH homeostasis. The giant-celled brackish-water alga Chara deposits distinct bands of external CaCO3 along its length. These correspond to extracellular alkaline regions that are separated from one another by acidic bands (Figure 1). Two hypotheses have been forwarded for the mechanism of banding and calcification in Chara (McConnaughey and Whelan, 1997). Each mechanism clearly involves the spatial separation of H 1 extrusion regions from those involved in H 1 uptake. In both models H 1 ions produced during calcification are ultimately used to generate CO2 from HCO32 . Calcifying macroalgae such as Halimeda and Corallina also produce CaCO3 in alkaline extracellular spaces. However, the spatial separation of H 1 uptake and efflux into different zones is less clear in these organisms. Coccolithophorid phytoplankton produce CaCO3 in the form of elaborate crystalline structures known as coccoliths (Figure 2). Two distinct classes of coccoliths have been identified. Holococcoliths are simple single-crystalline structures, while heterococcoliths are more complex multicomponent structures (Young et al., 1999). Current evidence suggests that holococcoliths are formed on the external cell surface while heterococcoliths are produced in intracellular compartments (coccolith vesicle) (Young et al., 1999). Certain species (e.g. Coccolithus pelagicus) have both hetrococcolith-and holococcolith-producing phases, while others (e.g. Emiliania huxleyi) produce only heterococcoliths. Various functions have been assigned to coccoliths, ranging from protection against grazing, regulation of depth in the water column, or modification of optical properties to favour photosynthesis. However, the frequent correlation of calcification rates with photosynthesis and the often observed continual production and shedding of coccoliths suggests that coccolithophore calcification production may have at least a partial metabolic role. Heterococcoliths develop inside intracellular vesicles derived from the Golgi cisternae. Calcification occurs in a highly ordered manner from a protein base plate (Young et al., 1999). As the coccolith matures, the vesicle moves towards the cell periphery and the mature coccolith is extruded in a single exocytotic event and attaches to the external cell surface. Estimates of coccolith formation in E. huxleyi have shown that approximately one coccolith can be formed per hour (Paasche, 1964). Under conditions that promote high rates of calcification, carbon is fixed into CaCO3 at the same molar rate as in photosynthetic carbon fixation, i.e. the ratio of calcification to photosynthesis is unity (Paasche, 1964). Figure 2 summarizes current knowledge of the main fluxes of carbon and Ca2 1 in coccolithophore calcification. The precise routes of uptake of DIC and Ca2 1 are still unresolved. Uptake of HCO32 to the coccolith vesicle and chloroplast can potentially occur passively without expenditure of cellular energy. However, the uptake of Ca2 1 into the coccolith vesicle may be subject to considerable energetic barriers, particularly if significant fluxes of Ca2 1 occur through the cytoplasm en route to the coccolith vesicle, since the cytoplasmic Ca2 1 concentration is kept extremely low (around 100 nmol L 2 1) in all eukaryotic cells. This energetic barrier could be overcome by utilization of alternative transport routes and/or by binding of Ca2 1 to polysaccharides or proteins. While Ca2 1 -binding proteins and polysaccharides have been characterized in some detail in E. huxleyi and Pleurochrysis carterii (e.g. Corstjens et al., 1998), these so far appear to be involved in the regulation of CaCO3 precipitation within the coccolith vesicle rather than the influx of Ca2 1 to this organelle. So far no transport protein ENCYCLOPEDIA OF LIFE SCIENCES / & 2002 Macmillan Publishers Ltd, Nature Publishing Group / www.els.net 3 Algal Calcification and Silification has been specifically identified that is exclusively involved in calcification in coccolithophores. Characterization of the pathways and transporters for DIC and Ca2 1 is eagerly awaited. Silification Overview Silica is the second most abundant element in the earth’s crust. It is surprising, therefore, that few algal groups utilize silicon to any great extent. Of these, all transform dissolved silicate to particulate skeletal material. Cell wall silica deposition has been recorded in some marine macroalgae. However, unicellular algae are responsible for the majority of biogenic silicification. Only four groups of these phytoplankton produce silicified skeletal material: silicoflagellates, chrysophyta, xanthrophyta and – by far the most significant producer of biogenic silica – the bacillariophyta or diatoms. Diatoms contribute approximately 25% of world net primary productivity and up to 50% of marine primary productivity, reflected by their dominance in productive ocean upwelling and shelf areas. This in turn dominates the marine silicon cycle. The archive of diatom frustules found in sedimentary deposits has important applications in palaeogeology and hydrocarbon exploration, and the sedimentary deposits themselves are an important raw material for industrial use. The study of the mechanisms of biogenic silica deposition is likely to reveal biotechnological applications in the future and is therefore a critical area of future research. Geological and economic importance Diatoms play a key role in marine silicon cycling (Tréguer et al., 1995) and, because diatom growth has an absolute requirement for silicate, Si(OH)24 2 availability is critical in determining primary productivity and therefore CO2 fluxes in large areas of ocean (Dugdale and Wilkerson, 1998). It is estimated that over 30 million km2 of ocean floor are covered with sedimentary deposits of diatom shells. Diatomite is a low-density and highly porous opaline silica sedimentary rock formed by the compaction of diatom frustule deposits between 50 and 80 million years ago in both marine and freshwater locations. Some commercial deposits of diatomite may contain up to 90% SiO2 and have been utilized in many industrial applications. The high porosity, low permeability, high stability and chemical inertness of diatomite have been exploited for centuries in its use as a building material, filler and additive to mortar. Diatomite continues to be used today as a fine filler in ceramics and construction materials. Alfred Nobel implemented one of the earliest commercial applications of diatomite with his discovery that highly explosive nitro4 glycerine could be stabilized by absorption into diatomite, thereby producing dynamite. While the discovery of dynamite played a key role in the industrial revolution, it has largely been superseded by modern explosives. Given that industrial synthesis of silica-based materials requires high temperature and pressure, the biogenic formation of silica under ambient conditions has great potential for biotechnological applications such as controlled nanoscale crystal formation, large-scale silica harvesting and novel means of industrial silica production. While research is gathering momentum in these applications, naturally occurring diatomite and diatomaceous earth continue to be an important raw material for biotechnology and filtration applications, particularly in the water purification and brewing industry. A more recent application has been in pest control during post-harvest storage of cereals, when treatment of cereals with nontoxic diatomaceous powder appears to cause a high mortality in a number of food-spoilage beetles. A robust taxonomic key of the diatoms is possible because of the unique and stable silica frustule morphotypes of diatom species. This is particularly useful in the analysis of cores from diatomaceous deposits, which provide palaeoenvironmental and geochronological information. The silica microfossils within sediment samples can be assessed for the species composition and diversity. Such profiles can be used to reconstruct the environmental conditions prevailing at the time of deposition. Particular examples include the use of diatom microfossils in extrapolation of quaternary climate and hydrology from lake cores in East Africa (Gasse et al., 1996). Species composition is directly related to lakes’ patterns of level and salinity and consequently reflects long-term climate variation. While the majority of these studies deal with long-term changes, there is scope for shorter, decadal, reconstructions of diatom-inferred salinity to provide a detailed view of drought conditions; an example is Moon Lake in North Dakota (Laird et al., 1996). Stable-isotope fractionation by diatoms during biogenic silica formation has been exploited to reconstruct primary productivity from ocean sediment cores (DeLa Rocha et al., 1998). Core profiles from diatomaceous deposits are also crucial for predictive hydrocarbon exploration. Characteristic diatoms from different cores can be correlated with biostratigraphy. Heavy oil and gas deposits are also frequently associated with such deposits. Mechanism Silicon is an essential element for diatom growth. Silicon availability in aquatic habitats varies considerably, largely as a product of rock weathering, river inputs and dissolution of biogenic silica sediments. The most dominant soluble form for biogenic silification is monomeric undissociated silicic acid, Si(OH)4, although the less ENCYCLOPEDIA OF LIFE SCIENCES / & 2002 Macmillan Publishers Ltd, Nature Publishing Group / www.els.net Algal Calcification and Silification abundant anion (SiO(OH)32 ) may be utilized by some diatom species. In the euphotic zone of aquatic ecosystems, silicic acid is present in concentrations ranging from submicromolar up to 200 mmol L 2 1 with 1–20 mmol L 2 1 being common. While uptake of Si(OH)4 can occur passively across the lipid membrane, active transport is necessary to satisfy the demands of silification. Active uptake of silicic acid is implied by studies of tracer uptake and effects of metabolic inhibitors. Carrier-mediated silicon uptake is indicated for a wide range of diatom species fitting Michelis–Menten kinetics. Typically the Km for Si(OH)4 lies in the range 0.3 to 4 mmol L 2 1 for marine diatoms. The observation that dissipation of the Na 1 gradient across the plasma membrane inhibits Si(OH)4 uptake supports a model for secondary active transport in marine diatoms whereby silicon uptake is coupled to a favourable Na 1 gradient. Silicon uptake is closely governed by metabolic demand and cell cycle, with maximal rates associated with periods of cell wall deposition. Uptake rates are also variable depending on the availability of external silicon, with maximal surge uptake occurring on reintroduction of a silicon source after a period of silicon starvation. While silica deposition and cell division can occur close to maximal rates at silicon concentrations that are limiting for silicon uptake, diatoms can accumulate soluble silicon between 20 and 400 mmol L 2 1, exceeding the solubility for silicon and in some cases enough to synthesize an entire frustule without further silicon input. While storage in specialized vesicles or by association with intracellular organic silicon-binding components has been proposed, the mechanism for maintaining these supersaturated internal pools of silicon is unclear. Likewise, the internal silicon pool size is known to be influenced by a number of metabolic and environmental variables, yet the precise mechanism underlying this regulation remains unknown. Recent progress has been made in the cloning and functional expression of cDNAs coding diatom silicic acid transporters (Hildebrand et al., 1997). The clones derived from Cylindrotheca fusiformis can be heterologously expressed in Xenopus oocytes, where they enable Na 1 dependent uptake of germanium-68 (a silicon analogue tracer). These clones encode the diatom SIT gene family of unique conserved integral membrane domains and less conserved carboxyl-terminal portion, indicating that they most likely encode silicic acid transporters with different cellular locations and/or affinities. This is supported by the fact that different SITs exhibit different levels of mRNA abundance during silification and cell division. Overall, however, SIT gene expression patterns during silification and cell division in Cylindrotheca fusiformis correlate well with transport activity characterized in other diatoms. Removal of silicon allows diatom cells to reach maturity, but they fail to undergo cell division. Synthesis of both protein and DNA is inhibited within a few hours of silicon starvation, whereas photosynthesis and glycolysis are only slightly reduced during this time. Silicon-starved cells increase production of lipid, which appears as oil droplets. Resupply of Si(OH)4 triggers a rapid and specific increase in DNA polymerase and cells resume cell division. Silicon starvation has been used as a tool to synchronize diatom cultures. Polycondensation of Si(OH)4 to form a cell wall is energetically favourable compared to synthesis of cell wall cellulose or to calcification. It has been estimated that 1 ATP is required for every silicon taken up and deposited, Figure 3 (a) Scanning electron micrograph showing complete silica frustules of the diatom Thallassiosira eccentrica (cell diameter 5 50 mm). (b) Working model of silica biogenesis in a diatom. Na 1 -dependent silicate uptake is mediated by specialized silica transporters (SIT) at the plasma membrane. Once inside the cell, the soluble silica is delivered to the silica deposition vesicle (SDV), possibly involving isoforms of the SITs. Silica polycondensation occurs under acidic conditions within the SDV to form insoluble amorphous silica. Soluble silica may be stored in intracellular pools, the size of which is sensitive to silica demand and metabolism. Silifin proteins are thought to play a key role in regulating the formation of insoluble silica within the SDV. Frustulins are a separate group of proteins that together with polysaccharides and lipids are likely to play a role in stabilization of the mature silica wall structure. On maturity, the complete valve is released onto the cell surface by exocytosis. ENCYCLOPEDIA OF LIFE SCIENCES / & 2002 Macmillan Publishers Ltd, Nature Publishing Group / www.els.net 5 Algal Calcification and Silification which represents only 2% of the cellular energy budget to produce 20% of cell dry weight (Raven, 1983). This compares very favourably to calcification (see above) and is likely to have been a major evolutionary advantage. While the morphology and ultrastructure of silica deposition have been described in detail for a number of diatom species, little is known about the mechanisms of deposition at the molecular level. In an analogous way to coccolithophorid calcification (see above), silica polymerization occurs intracellularly within a specialized membrane-bound compartment, known as the silica deposition vesicle (SDV), that lies close to the plasma membrane. The membrane of the SDV, the silicalemma, extends with, and remains closely attached to, the mineralized structure within. The SDV is an acidic compartment, which favours mineralization and prevents dissolution of the newly formed frustule (Figure 3). The most promising recent work has focused on the organic components of the amorphous silica walls of diatoms. Some of these appear to have a regulatory role in silica deposition and wall patterning and others promote stability of the mature wall. Diatom cell walls are rich in hydroxylated amino acids that may play a role in promoting silica polymerization. A group of polycationic peptides (silaffins), in tandem with long-chain polyamines, that rapidly induce silica nanosphere formation in vitro are thought to play a key role in directing silica deposition inside the acidic SDV (Kroger et al., 1999). Additionally, a group of Ca2 1 -binding glycoproteins (frustulins) that is associated with mature valves may act as a protective layer to retard dissolution in the slightly basic, undersaturated extracellular environment. References Corstjens PLAM, van der Kooij A, Linschooten C et al. (1998) GPA, a calcium binding protein in the coccolithophorid Emiliania huxleyi (Prymnesiophycae). Journal of Phycology 34: 622–630. Degens ET and Itterkkot V (1986) Ca2 1 stress, biological response and particle aggregation in the aquatic habitat. Netherlands Journal of Sea Research 20: 109–116. DeLa Rocha CL, Brzezinski MA, DeNiro MJ and Shemesh A (1998) Silicon-isotope composition of diatoms as an indicator of past oceanic change. Nature 395: 680–683. 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McConnaughey TA and Whelan JF (1997) Calcification generates protons for nutrient and bicarbonate uptake. Earth Science Reviews 42: 95–117. Paasche E (1964) A tracer study of the inorganic carbon uptake during coccolith formation and photosynthesis in the coccolithophorid Coccolithus huxleyi. Physiologia Plantarum, Supplement III: 1–82. Raven JA (1983) Transport and function of silicon in plants. Biological Reviews 58: 179–207. Raven JA (1997) Putting the C in phycology. Journal of Phycology 32: 319–333. Tréguer P, Nelson DM, Van Bennekom AJ et al. (1995) The silica balance in the world ocean: a reestimate. Science 268: 375–379. Varekamp JC, Kruelen R, Poorter RPE, Vanbergen MJ (1992) Carbon sources in ARC volcanism, with implications for the carbon cycle. Terra Nova 4: 363–373. Westbroek P, Brown CW, van Bleisjwijk J et al. (1993) A model systems approach to biological climate forcing. The example of Emiliania huxleyi. Global and Planetary Change 8: 27–46. Young JR, Davis SA, Bown PR and Mann S (1999) Coccolith ultrastructure and biomineralization. Journal of Structural Biology 126: 195–215. Further Reading Bhattacharyya P and Volcani BE (1980) Sodium-dependent silicate transport in the apochlorotic marine diatom Nitzschia alba. Proceedings of the National Academy of Sciences of the USA 77: 6386–6390. Borowitzka MA (1982) Morphological and cytological aspects of algal calcification. International Review of Cytology 74: 127–162. Green JC and Leadbeater BSC (eds) The Haptophyte Algae, pp. 321–334. Oxford: Clarendon Press. Mann S (1997) Biomineralization: the formidable part of bioinorganic chemistry. Journal of the Chemical Society, Dalton Transactions 21: 3953–3961. Martin-Jézéquel V, Hildebrand M and Brzezinski MA (2000) Silicon metabolism in diatoms: implications for growth. Journal of Phycology 36: 821–840. Pickett-Heaps J, Schmid A-MM and Edgar LA (1990) The cell biology of diatom valve formation. Progress in Phycological Research 7: 1–168. Round FE, Crawford RM and Mann DG (1990) The Diatoms: Biology and Morphology of the Genera. Cambridge: Cambridge University Press. Siegenthaler U and Sarmiento JL (1993) Atmospheric carbon dioxide and the ocean. Nature 365: 119–125. Simkiss K and Wilbur KM (1989) Biomineralization: Cell Biology and Mineral Deposition. San Diego: Academic Press. Stoermer EF and Smol JP (eds) (1999) The Diatoms: Applications for the Environmental and Earth Sciences. Cambridge: Cambridge University Press. ENCYCLOPEDIA OF LIFE SCIENCES / & 2002 Macmillan Publishers Ltd, Nature Publishing Group / www.els.net