Aquatic Environment and Biodiversity Annual Review 2012

Aquatic Environment and Biodiversity Annual Review 2012 Aquatic Environment and Biodiversity Annual Review 2012

25.10.2013 Views

AEBAR 2012: Marine Biodiversity ecosystem-based approach to management (Thrush et al. 1997, 2000), with potential benefits for marine conservation and management. Ecosystem modelling of species distribution (and habitats) with respect to known and projected environmental parameters will improve predictability for both broad and fine-scale biodiversity distribution. This has already resulted in improved definition of environmental classifications addressing biodiversity assessment. It is also important to make progress in establishing the links between biodiversity and the long-term viability of fish stocks under various harvesting strategies. It is also important that modellers consider processes from all ecosystem function perspectives i.e., top-down effects such as predation (e.g. trophic modelling), bottom-up effects such as the environment (e.g., habitat classification based on environmental variable), and wasp-waisted systems where there are major effects in both directions. Projects ZBD2002-06A: Impacts of terrestrial run-off on the biodiversity of rocky reefs Completed. (Schwarz et al. 2006). ZBD2004-02: Ecosystem scale trophic relationships of fish on the Chatham Rise. Completed. (Connell et al. 2010, Dunn 2009, Dunn et al. in press, Dunn et al. 2010a, b, c, Eakin et al. 2009, Forman and Dunn 2010, Horn et al. 2010, Stevens and Dunn 2010. Follow-up research on isotope signatures to improve the trophic data from ZBD2004-02 has been incorporated into the NIWA’s Coast and Ocean programme and trophic modelling is underway in this programme. ZBD2004-08 Sea-grass meadows as biodiversity and connectivity hotspots. This contract links closely with the MBIE project Coastal Conservation Management (CO1X0907). National scale sampling across North and South Island seagrass meadows in a range of estuarine and coastal settings has shown that seagrass meadows overall consistently supported higher species richness, biomass, and productivity of invertebrates (infaunal and epifaunal). Associated sampling of small fish assemblages found that while seagrass meadows provided a nursery function to a number of species, this function was most pronounced in northern New Zealand systems, where relatively high numbers of juvenile snapper, trevally, spotties, parore, and garfish/piper were caught. However, there was strongly spatial variation across different estuary and coast settings (MBIE91B). ZBD2004-19 Ecological function and critical trophic linkages in New Zealand softsediment habitats. Project completed. (see Lohrer et al. 2010.) ZBD2005-05 Effects of climate variation and human impacts on the structure and functioning of New Zealand shelf ecosystems. The project is a multidisciplinary study to utilise archeological, paleoecological, and historical data to retrospectively model ecosystem states during different historical and prehistoric time periods. The project is collaborating with the international History of Marine Animal Populations (HMAP) project, itself a part of the Census of Marine Life (CoML) programme. The data have been used as inputs to a mass balance model of the shelf ecosystem starting with the present day Hauraki Gulf. A short video about the NZ Taking Stock project was made by HMAP staff and is currently available on the HMAP website http://hmapcoml.org/projects/nz/. Several presentations have been made at NZ and international conferences as results have emerged. ZBD2008-01 Inshore biogenic habitats. Existing knowledge on biogenic habitat-formers in the

AEBAR 2012: Marine Biodiversity Over 600 targets of interest were identified and marked on marine charts, with more than 200 of these targets being biogenic in nature. Fieldwork has been completed to verify and quantify biodiversity in biogenic habitats using Ocean Survey 20/20 vessel days on Tangaroa and a new MSI project to extend the survey potential of the project. New biogenic habitats have been identified, including extensive worm tube ‘meadows’ off the east coast of the South Island (“the Hay Paddock” and “Wire-weed”), with associated relatively high epi-faunal invertebrate diversity compared to adjacent bare sediments. Over 60 new species were also collected (dominated by sponges), along with range extensions of many other species. Analyses are underway for key selected areas included in the Tangaroa voyages, including offshore North Taranaki Bight, Ranfurly Bank, the polychaete meadows mentioned above, and the Otago Peninsula bryozoan fields. IPA2009-11. Trophic Review. This project publishes a report prepared on the feeding habits of New Zealand fishes 1960 to 2000 (Stevens et al. 2011) Other research relevant or specifically linked to the projects above, is listed in Table 11.2. Table 11.2: Other research linked to ecosystem scale understanding of biodiversity in the marine environment. MPI ENV2006-04 Ecosystem indicators for New Zealand fisheries ENV2007-04 Climate and oceanographic trends relevant to New Zealand fisheries ENV2007-06 Trophic relationships of commercial middle depth species on the Chatham Rise CRI Core C01X501 coasts & oceans productivity plankton-mesopelagic fish trophic relations Chatham Rise purposes IO 2. Second Fisheries Oceanography voyage to Chatham Rise: mesopelagics and hyperbenthics OTHER AUT deepsea and subtidal food web dynamics; offshore & coastal biodiversity post graduate studies 11.3.3. Progress on Science Objective 3. The role of biodiversity in the functional ecology of nearshore and offshore communities. An identified outcome of the Biodiversity Strategy is that by 2020 “New Zealand’s natural marine habitats and ecosystems are maintained in a healthy functioning state. Degraded marine habitats are recovering.” Sustaining ecosystem integrity in marine habitats requires a thorough understanding of the ecological and anthropogenic drivers affecting biodiversity and ecosystem function, and the ability to manage human impacts in marine environments. Near-shore environments range from wetlands to estuaries, coasts and continental shelf ecosystems, they contain a variety of habitats and often contain species that are particularly important, either for cultural, recreational, and commercial reasons, or because the species exerts disproportionate influence on community structure and ecosystem function. Near-shore ecosystems are the multi-use ecosystems most subjected to multiple stressors. Due to ocean-coast and land-coast interactions these ecosystems will be subjected to the greatest range of stresses associated with global warming. Nearshore environments may also contain habitats that are particularly important for biodiversity in other environments, for instance by providing larval/juvenile nursery areas or by exporting nutrients. The MPI Biodiversity Programme has directed funds into research examining the implications of environmental and human impacts on the functional ecology of these key species and habitats. Near-shore ecosystems are complex and changes in diversity and community composition may be driven by multiple variables. Interactions between variables are likely to be non-linear, with disturbance thresholds and the potential for multiple stable states. As a consequence, it is often difficult to distinguish ‘natural’ from ‘anthropogenic’ impacts affecting ecosystem dynamics. MPI 260

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

ecosystem-based approach to management (Thrush et al. 1997, 2000), with potential benefits for<br />

marine conservation <strong>and</strong> management. Ecosystem modelling of species distribution (<strong>and</strong> habitats)<br />

with respect to known <strong>and</strong> projected environmental parameters will improve predictability for both<br />

broad <strong>and</strong> fine-scale biodiversity distribution. This has already resulted in improved definition of<br />

environmental classifications addressing biodiversity assessment. It is also important to make<br />

progress in establishing the links between biodiversity <strong>and</strong> the long-term viability of fish stocks under<br />

various harvesting strategies. It is also important that modellers consider processes from all ecosystem<br />

function perspectives i.e., top-down effects such as predation (e.g. trophic modelling), bottom-up<br />

effects such as the environment (e.g., habitat classification based on environmental variable), <strong>and</strong><br />

wasp-waisted systems where there are major effects in both directions.<br />

Projects<br />

ZBD2002-06A: Impacts of terrestrial run-off on the biodiversity of rocky reefs Completed.<br />

(Schwarz et al. 2006).<br />

ZBD2004-02: Ecosystem scale trophic relationships of fish on the Chatham Rise. Completed.<br />

(Connell et al. 2010, Dunn 2009, Dunn et al. in press, Dunn et al. 2010a, b, c, Eakin et al.<br />

2009, Forman <strong>and</strong> Dunn 2010, Horn et al. 2010, Stevens <strong>and</strong> Dunn 2010. Follow-up research<br />

on isotope signatures to improve the trophic data from ZBD2004-02 has been incorporated<br />

into the NIWA’s Coast <strong>and</strong> Ocean programme <strong>and</strong> trophic modelling is underway in this<br />

programme.<br />

ZBD2004-08 Sea-grass meadows as biodiversity <strong>and</strong> connectivity hotspots.<br />

This contract links closely with the MBIE project Coastal Conservation Management<br />

(CO1X0907). National scale sampling across North <strong>and</strong> South Isl<strong>and</strong> seagrass meadows in a<br />

range of estuarine <strong>and</strong> coastal settings has shown that seagrass meadows overall consistently<br />

supported higher species richness, biomass, <strong>and</strong> productivity of invertebrates (infaunal <strong>and</strong><br />

epifaunal). Associated sampling of small fish assemblages found that while seagrass meadows<br />

provided a nursery function to a number of species, this function was most pronounced in<br />

northern New Zeal<strong>and</strong> systems, where relatively high numbers of juvenile snapper, trevally,<br />

spotties, parore, <strong>and</strong> garfish/piper were caught. However, there was strongly spatial variation<br />

across different estuary <strong>and</strong> coast settings (MBIE91B).<br />

ZBD2004-19 Ecological function <strong>and</strong> critical trophic linkages in New Zeal<strong>and</strong> softsediment<br />

habitats. Project completed. (see Lohrer et al. 2010.)<br />

ZBD2005-05 Effects of climate variation <strong>and</strong> human impacts on the structure <strong>and</strong> functioning of<br />

New Zeal<strong>and</strong> shelf ecosystems.<br />

The project is a multidisciplinary study to utilise archeological, paleoecological, <strong>and</strong> historical<br />

data to retrospectively model ecosystem states during different historical <strong>and</strong> prehistoric time<br />

periods. The project is collaborating with the international History of Marine Animal<br />

Populations (HMAP) project, itself a part of the Census of Marine Life (CoML) programme.<br />

The data have been used as inputs to a mass balance model of the shelf ecosystem starting<br />

with the present day Hauraki Gulf. A short video about the NZ Taking Stock project was<br />

made by HMAP staff <strong>and</strong> is currently available on the HMAP website<br />

http://hmapcoml.org/projects/nz/. Several presentations have been made at NZ <strong>and</strong><br />

international conferences as results have emerged.<br />

ZBD2008-01 Inshore biogenic habitats.<br />

Existing knowledge on biogenic habitat-formers in the

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