Another important element affecting
calcification rates of corals is the calcium carbonate saturation state of the mineral aragonite (Cohen et al., 2009; Gattuso et al., 1998; Marshall & Clode, 2002).
Our novel technique involved analysing coccolithophore skeletal remains and applying observations from modern specimens to estimate, for the first time,
calcification rates of fossil coccolithophores.»
Moreover, using the average emission scenario (IS92a) of the Intergovernmental Panel on Climate Change, we predict that
the calcification rate of scleractinian - dominated communities may decrease by 21 % between the pre-industrial period (year 1880) and the time at which pCO2 will double (year 2065).
Not exact matches
Emerging evidence for variability in the coral
calcification response to acidification, geographical variation in bleaching susceptibility and recovery, responses to past climate change, and potential
rates of adaptation to rapid warming supports an alternative scenario in which reef degradation occurs with greater temporal and spatial heterogeneity than current projections suggest.
Dr Sarah O'Dea, from Ocean and Earth Science at the University
of Southampton and lead author
of the study, says: «Our results show that climate change significantly altered coccolithophore
calcification rates at the PETM and has the potential to be just as significant, perhaps even more so, today.
Previous studies showed that the coral
calcification process has a diel rhythmic cycle
of increasing
rates towards midday, and then decreasing towards dusk (Gutner - Hoch et al., 2016; Schneider et al., 2009).
Hence, it could be suggested that the small differences in the
calcification rates observed between 100 mg / L and 200 mg / L calcium additions during the day could be a result
of relatively mediocre photosynthetic activities
of the endo - symbionts, but this should be further studied.
The
calcification rate values (µmol CaCO3 h − 1 cm − 2) were calculated according to the equation: Δ A T 2 ∗ V chamber − V coral T ∗ A coral where ΔAT is the difference in Total Alkalinity (AT) measured between the beginning and the end the incubation period, V is the volume
of the chamber or the coral fragment, T is the duration
of the incubation and A is the coral surface area.
In addition, reductions in
calcification from lowered pH in surface waters could reduce phytoplankton sinking
rates through loss
of ballast (Hofmann and Schellnhuber, 2009), though this effect will depend on the ratio
of the fraction
of ballasted vs. un-ballasted fractions
of the sinking POC.
Reduced food supply owing to lower POC fluxes could exacerbate these impacts because the metabolic cost
of increased
rates of calcification become greater as pH declines (Wood et al., 2008).
Following the concept that seawater Ωarag is a function
of CO 3 2 − and calcium ion -LRB-[Ca2 +]-RRB- concentrations (Cyronak, Schulz & Jokiel, 2016), Longdon et al. (2000) and Marshall & Clode (2002) showed that exposing scleractinian corals to seawater with high calcium concentrations induces high
calcification rates.
This decreases the
rate and amount
of calcification among many marine organisms that build external skeletons and shells, ranging from plankton to shellfish to reef - building corals.
In addition, the effect
of the high calcium concentration was stronger in the
calcification rates during day compared to the night (Fig. 2).
In the Nature study you state that previous work has not determined the impact
of acidification on the ability
of individual species to calcify because they measured net
calcification (that is, gross
calcification minus dissolution) thus failing to disentangle the relative contributions
of gross
calcification (the amount
of carbonate deposited by an animal over time) and dissolution
rates.
Since you state that a decrease in net
calcification could result from a decrease in gross
calcification, an increase in dissolution
rates, or both, you distinguish between these responses and get to the conclusion that the impact
of ocean acidification on a creature's net
calcification may be largely controlled by the status
of its protective organic cover and that the net slowdown in skeletal growth under increased CO2 occurs not because these organisms are unable to calcify, but rather because their unprotected skeleton is dissolving faster.
The study, which evaluated the
calcification in the arteries
of Egyptian mummies found high
rates of atherosclerosis.
There are several feedbacks between decreasing the
rate of calcification that organisms do in the ocean, and the carbon cycle.
The reef flat at Moorea displayed a higher
rate of organic production and a lower
rate of calcification compared to previous measurements carried out during austral summer.
Our data suggest that the
rate of calcification during the last glacial maximum might have been 114 %
of the preindustrial
rate.
In addition, they state that there was «no significant correlation between
calcification rate and seawater aragonite saturation (Ωarag)» and «no evidence
of CO2 impact on bleaching.»
Lower
calcification rates would reduce the alkalinity pump, reduce surface CO2 and increase the buffering capacity
of surface waters.
Accordingly numerous studies have reported that greater
rates of photosynthesis correlate with greater
rates of calcification.
The team found that
rates of reef
calcification were 40 percent lower in 2008 and 2009 than they were during the same season in 1975 and 1976.
As such, ocean acidification could represent an abrupt climate impact when thresholds are crossed below which organisms lose the ability to create their shells by
calcification, or pH changes affect survival
rates (see the Extinctions section below for more discussion
of these issues).
* The rising CO2 content
of the atmosphere may induce very small changes in the well - buffered ocean chemistry (pH) that could slightly reduce coral
calcification rates; but potential positive effects
of hydrospheric CO2 enrichment may more than compensate for this modest negative phenomenon.
In order to establish a cause - and - effect relationship between acidification and decreased
calcification, a team led by Carnegie's Ken Caldeira and including Jacob Silverman (the lead author) and Kenneth Schneider, formerly
of Carnegie, compared measurements
of the
rate of calcification in one segment
of Australia's Great Barrier Reef called Bird Island that were taken in between 1975 and 1979 to those made at the neighboring Lizard Island in 2008 and 2009.
Other potentially confounding factors are
calcification, diagenesis, and the nature
of the growth -
rate - limiting factor, e.g. light vs nutrients.
All coastal engineering communities support intense metabolic processes, including high primary production, respiration and
calcification rates, thereby affecting CO2, CO3 −, and alkalinity concentrations and surface water pH. However, many metabolically intense coastal habitats are experiencing global declines in their abundance at
rates in excess
of 1 % per year (Duarte et al. 2008; Ermgassen et al. 2013).
A growing number
of studies have demonstrated adverse impacts on marine organisms, including decreases in
rates of coral
calcification, reduced ability
of algae and zooplankton to maintain protective shells, and reduced survival
of larval marine shellfish and fish [13], [14], [15].
Coastal ecosystems may show acidification or basification, depending on the balance between the invasion
of coastal waters by anthropogenic CO2, watershed export
of alkalinity, organic matter and CO2, and changes in the balance between primary production, respiration and
calcification rates in response to changes in nutrient inputs and losses
of ecosystem components.
Work from another team led by Caldeira found that
rates of reef
calcification were 40 percent lower in 2008 and 2009 than they were during the same season in 1975 and 1976.
In this study, averaged across all generation points, each coccolithophore cell increased its
calcification rate (26 %) and calcium carbonate quota (26 %) in the future ocean treatment (figures 2a and 3a), and the total concentration
of calcium carbonate in the culture (PIC l − 1) increased 18 % in the future ocean condition (table 4).
These responses include impacts on
calcification rates [18,19], immune function [20], reproduction and carryover effects in larval and juvenile stages
of invertebrates [21], enhanced productivity in phytobenthos [22 — 25] but reduced
calcification and growth in calcareous algae [26 — 28].
These geologically ancient, long - lived, slow - growing and fragile reefs will suffer reduced
calcification rates and, as the aragonite saturation horizon moves towards the ocean surface, large parts
of the oceans will cease to support them by 2100 (Feely et al., 2004; Orr et al., 2005; Raven et al., 2005; Guinotte et al., 2006).