Intertidal habitat mapping for ecosystem goods and services : Waikato estuaries / prepared by: Hazel Needham, Michael Townsend, Judi Hewitt, Sarah Hailes (National Institute of Water & Atmospheric Research Ltd).

By: Needham, Hazel [author.].
Contributor(s): Townsend, Michael, 1980- [author.] | Hewitt, J. E. (Judith Elaine), 1955- [author.] | Hailes, Sarah F. (Sarah Frances) [author.] | Waikato (N.Z.). Regional Council (1989-1992) [issuing body.].
Material type: materialTypeLabelBookSeries: Waikato Regional Council technical report (2011): 2013/52.Description: 1 online resource : colour illustrations.Subject(s): WETLANDS | ECOSYSTEM SERVICES | INTERTIDAL ECOLOGY | COASTAL MAPPING | WETLAND MAPPING | ESTUARIES | WAIKATO | NEW ZEALANDAdditional physical formats: Intertidal habitat mapping for ecosystem goods and servicesHoldings: ELECTRONIC Online resources: Waikato Regional Council website | Intertidal habitat mapping for ecosystem goods and services National Digital Heritage Archive Open Access Summary: In January 2013, Waikato Regional Council contracted the National Institute of Water and Atmospheric Research (NIWA), to develop rapid assessment techniques for mapping of intertidal habitats associated with the provision of ecosystem goods and services. Assessment techniques were successfully trialled for mapping the intertidal area of Tairua Estuary. This report documents the application and adaptation of the habitat mapping methodology for thirteen estuaries and harbours within the Waikato region: Otahu River, Whangamata Harbour, Wharekawa Harbour, Purangi River, Whitianga Harbour, Whangapoua Harbour, Kennedy Bay, Waikawau Bay, Port Charles, Colville Bay, Coromandel Harbour, Te Kouma Harbour and Manaia Harbour. Field based observations of intertidal areas in each of the 13 study locations were undertaken to rapidly identify habitat characteristics linked to the provisioning of ecosystem goods and services. As much of the intertidal area in each estuary that could feasibly be covered given spring low tides was covered. Handheld global positioning systems (GPS) were used to demark boundaries between habitats, and geo-referenced photographs were collected inside each habitat type. All data were processed and converted into GIS map layers. Sediment information from each study location was also detailed for each habitat polygon using five broad categories (mud, sand, shell-hash, sandy mud/muddy sand mixture, and gravel mixture). Sediments were classified based on visual observations, textural analysis and sinking depth underfoot. Sediment samples were collected from each estuary for quantitative verification at a later date. There were three habitats defined by the characteristics/dominance of the flora: seagrass, mangroves and pneumatophores (the aerial roots of mangroves). There were 12 habitats defined by characteristics/dominance of the fauna: cockles, pipi, cockles and pipi, Wedge shell (Macomona), oysters, crustacean burrows, crabs and cockles, tubeworms and cockles, snails (Amphibola), ‘low density deposit feeders’ (our baseline/LD deposit feeding community composition), ‘mounds and pits’ (similarly dominated by deposit feeders but featuring a distinct surface topography) and ‘low fauna’ (where macrofauna were extremely sparse).
Tags from this library: No tags from this library for this title. Log in to add tags.
Item type Current location Call number Copy number Status Date due Barcode
PDF PDF WELLINGTON
ONLINE
ELECTRONIC 1 Not for loan 390659

Includes bibliographical references.

In January 2013, Waikato Regional Council contracted the National Institute of Water and Atmospheric Research (NIWA), to develop rapid assessment techniques for mapping of intertidal habitats associated with the provision of ecosystem goods and services. Assessment techniques were successfully trialled for mapping the intertidal area of Tairua Estuary.

This report documents the application and adaptation of the habitat mapping methodology for thirteen estuaries and harbours within the Waikato region: Otahu River, Whangamata Harbour, Wharekawa Harbour, Purangi River, Whitianga Harbour, Whangapoua Harbour, Kennedy Bay, Waikawau Bay, Port Charles, Colville Bay, Coromandel Harbour, Te Kouma Harbour and Manaia Harbour.

Field based observations of intertidal areas in each of the 13 study locations were undertaken to rapidly identify habitat characteristics linked to the provisioning of ecosystem goods and services. As much of the intertidal area in each estuary that could feasibly be covered given spring low tides was covered. Handheld global positioning systems (GPS) were used to demark boundaries between habitats, and geo-referenced photographs were collected inside each habitat type. All data were processed and converted into GIS map layers.

Sediment information from each study location was also detailed for each habitat polygon using five broad categories (mud, sand, shell-hash, sandy mud/muddy sand mixture, and gravel mixture). Sediments were classified based on visual observations, textural analysis and sinking depth underfoot. Sediment samples were collected from each estuary for quantitative verification at a later date.

There were three habitats defined by the characteristics/dominance of the flora: seagrass, mangroves and pneumatophores (the aerial roots of mangroves).

There were 12 habitats defined by characteristics/dominance of the fauna: cockles, pipi, cockles and pipi, Wedge shell (Macomona), oysters, crustacean burrows, crabs and cockles, tubeworms and cockles, snails (Amphibola), ‘low density deposit feeders’ (our baseline/LD deposit feeding community composition), ‘mounds and pits’ (similarly dominated by deposit feeders but featuring a distinct surface topography) and ‘low fauna’ (where macrofauna were extremely sparse).

ELECTRONIC

There are no comments on this title.

to post a comment.

Powered by Koha