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Aquatic Environment and Biodiversity Annual Review 2012

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AEBAR <strong>2012</strong>: Marine <strong>Biodiversity</strong><br />

acidity), which may physically dissolve CaCO3 shells <strong>and</strong>/or skeletons <strong>and</strong> affect the<br />

shell/skeleton generation, as well as influencing many other physiological processes. Flow on<br />

effects to the viability of populations <strong>and</strong> the economic benefit that can be derived from<br />

commercially important species are likely. There is very little information on how key NZ<br />

calcifying species will respond to this change.<br />

This project is using laboratory experiments to quantify responses of key New Zeal<strong>and</strong> mollusc<br />

species (paua, Haliotus iris, cockles, Austrovenus stutchburyi, <strong>and</strong> oysters Tiostrea chiliensis) to<br />

levels of ocean CO2 saturation predicted to occur in NZ waters over the following decades.<br />

Results will be combined with information on the role of these key species in influencing<br />

ecosystem structure <strong>and</strong> function, to assess local <strong>and</strong> ecosystem-scale implications of acidification<br />

of NZ coastal waters expected in the following decades.<br />

ZBD2010-41. Potential effects of ocean acidification on habitat forming deep-sea corals in the New<br />

Zeal<strong>and</strong> region.<br />

Specific Objectives of this research were to 1. Determine the carbonate mineralogy of selected<br />

deep-sea corals found in the New Zeal<strong>and</strong> region, 2. Assess the distribution of deep-sea coral<br />

species in the region relative to improved knowledge of current <strong>and</strong> predicted aragonite (ASH)<br />

<strong>and</strong> calcite saturation horizons (CSH), <strong>and</strong> 3. Assess potential locations vulnerable to deepwater<br />

upwelling <strong>and</strong> areas of key deep-water fishery habitat. Through a literature search <strong>and</strong> analysis,<br />

the project aimed to determine the most appropriate tools to age corals <strong>and</strong> measure the effects of<br />

ocean acidification on deep-sea habitat-forming corals, <strong>and</strong> recommend the best approach for<br />

future assessments of the direct effects of declining ocean pH on these key fauna.<br />

Under Objective 1, new results of investigations into the carbonate mineralogy of selected deepsea<br />

corals found in the New Zeal<strong>and</strong> region were presented, <strong>and</strong> previous work on coral<br />

mineralogy summarised. The mineralogy <strong>and</strong> trace element concentration (Sr <strong>and</strong> Mg) of the five<br />

branching stony coral species (Order: Scleractinia) Goniocorella dumosa, Solenosmilia<br />

variabilis, Enallopsammia rostrata, Madrepora oculata, <strong>and</strong> the endemic Oculina virgosa, <strong>and</strong><br />

for the key habitat forming gorgonian coral species (Order: Alcyonacea) Keratoisis spp.,<br />

Lepidisis spp., Paragorgia spp. <strong>and</strong> Primnoa sp., was ascertained. Stony branching corals are all<br />

aragonitic with high Sr <strong>and</strong> low Mg while most of the gorgonian corals are made of high Mg <strong>and</strong><br />

low Sr, with high Mg calcite (>8 mol% Mg). The gorgonian sea fan, Primnoa sp., is aragonitic.<br />

Under Specific Objective 2, up to date position <strong>and</strong> depth data were used to produce distribution<br />

maps for the study species. Data compare well with previous publications from biodiversity<br />

research, research trawl, <strong>and</strong> observer sampling effort on wide regional distribution, but<br />

individual species display variations within the region. The peak depth distributions are unimodal<br />

at about 800-1000 m for most of the above species, but G. dumoas, E. rostrata, <strong>and</strong> Lepidisis<br />

spp. show bi-modal distributions <strong>and</strong> O. virgosa occurs primarily in shallow depths. In the<br />

second year of the project these distribution data will be compared with existing <strong>and</strong> predicted<br />

aragonite <strong>and</strong> calcite saturation horizons, particularly in areas of key deepwater fishery habitat.<br />

Also under Specific Objective 2, on-going opportunistic water sampling analyses are being<br />

carried out to determine alkalinity <strong>and</strong> dissolved inorganic carbon (DIC), <strong>and</strong> modelling to<br />

determine aragonite (ASH) <strong>and</strong> calcite saturation horizon (CSH) data is in progress. The aim is to<br />

compare water carbonate chemistry with regional biogeochemistry models <strong>and</strong> future scenarios<br />

to identify areas potentially at risk from ocean acidification.<br />

Under Specific Objective 3, at-sea sampling of live corals for aquarium studies has been carried<br />

out to investigate the feasibility of keeping the corals alive for growth <strong>and</strong> ocean acidification<br />

experiments. The corals collected in April, <strong>2012</strong> are still alive in the laboratory <strong>and</strong> include one<br />

small colony of S. variabilis. A literature search <strong>and</strong> analysis to determine the most appropriate<br />

tools to age <strong>and</strong> measure the effects of ocean acidification on deep-sea habitat-forming corals is<br />

268

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