{ "culture": "en-NZ", "name": "", "guid": "", "catalogPath": "", "snippet": "Bay of Plenty Regional Council is monitoring estuarine wetlands throughout the Bay \nof Plenty Region to determine what changes in condition and vegetation are occurring \nover time.", "description": "
Objective Reference - zA304706<\/SPAN><\/P> <\/P> Thirty-three permanent monitoring plots were established in Tauranga Harbour and <\/SPAN><\/P> 17 were established in Whakatāne Harbour at locations identified in Fitzgerald et al.<\/SPAN><\/P> (2019) based on vegetation and habitat mapping completed by Wildland Consultants <\/SPAN><\/P> 2013 and Beadel et al. 1992. Whakatāne Harbour plots were surveyed between 2 and <\/SPAN><\/P> 25 June 2020, Tauranga Harbour plots were surveyed between 8 and 29 June 2020 <\/SPAN><\/P> with the exception of one plot (Plot TAU10) which was surveyed on 19 March 2020. <\/SPAN><\/P> The location of all plots monitored is provided in Table 1 and 2. Each plot was 5 <\/SPAN><\/P> 5 metres and marked with either metal poles (c.10 millimetres diameter, 2 metre<\/SPAN><\/P> length - tops bent over) wooden posts (c.40 millimetres diameter, c.445 millimetres<\/SPAN><\/P> length).<\/SPAN><\/P> Back-up plots were identified by Fitzgerald et al. (2019), these were utilised when the <\/SPAN><\/P> original plot was either inaccessible, no permission was provided, or the plot was <\/SPAN><\/P> dominated by exotic pest plant species (such as pampas (Cortaderia selloana) at plots <\/SPAN><\/P> WHK 2 and 4). Replacement plots were chosen based on similar vegetation structure, <\/SPAN><\/P> relative proximity to the original plot, and accessibility. There were relatively fewer <\/SPAN><\/P> back-up plots for Tauranga Harbour, therefore the replacement plots used were not in <\/SPAN><\/P> the same wetland as the original plots, and were chosen based on similar vegetation <\/SPAN><\/P> structure and accessibility. As per the client\u2019s request back-up plots were not <\/SPAN><\/P> established for Te Hopai Island (Plots TAU2, 3, 4, and 6) and Opureora plots <\/SPAN><\/P> (Plot TAU15) for which access was denied.<\/SPAN><\/P> <\/P> Within each plot the following measurements were undertaken:<\/SPAN><\/P> A five minute bird count as per Hartley (2012). Birds were recorded to a <\/SPAN><\/P> maximum of 100 metres from the observer. In most instances, records were added <\/SPAN><\/P> to ebird (www.ebird.org).<\/SPAN><\/P> At least two photographs were taken as per Clarkson et al. (2004). An additional <\/SPAN><\/P> two photographs were taken at the majority of plots to provide a better visual <\/SPAN><\/P> representation of the plot. These were of the south west corner facing northeastern and of the northern edge of the plot. <\/SPAN><\/P> Two soil samples were collected (using a 5 cm diameter and 7.5 cm deep corer) <\/SPAN><\/P> from just outside the south-western corner (to reduce damage to the plot) <\/SPAN><\/P> following the methods of Clarkson et al. (2004). These were analysed by Hill <\/SPAN><\/P> Laboratories for water content, bulk density, pH, conductivity, total carbon, total <\/SPAN><\/P> nitrogen, and total phosphorus. <\/SPAN><\/P> Foliage samples (five grams of foliage, from the tips of vegetation) were<\/SPAN><\/P> collected for a common species in each plot. These were analysed by Hill <\/SPAN><\/P> Laboratories for total carbon, nitrogen and phosphorous content. <\/SPAN><\/P> Vegetation monitoring followed the methods of Clarkson et al. (2004):<\/SPAN><\/P> - All vascular plant species were identified and recorded. Usnea and other <\/SPAN><\/P> lichens and epiphytes were recorded to the lowest possible taxonomic level.<\/SPAN><\/P> - The percentage cover for each canopy species within the plot regardless of <\/SPAN><\/P> whether rooted in the plot or not was estimated.<\/SPAN><\/P> - The percentage cover of each species in the remaining vegetation layers was <\/SPAN><\/P> estimated. <\/SPAN><\/P> - Any species in the vicinity that were growing in the same vegetation type and <\/SPAN><\/P> were not encountered in the plot were listed. <\/SPAN><\/P> - The maximum and average height of each species in the plot was recorded. <\/SPAN><\/P> Vegetation-based plot indicator scores and condition index as per Clarkson et al.<\/SPAN><\/P> (2004) were calculated. <\/SPAN><\/P> The following physical parameters were measured in each plot from the southwestern (origin) corner:<\/SPAN><\/P> - Redox (ORP) measurements, taken at 5 cm and 15 cm depths with a YSI <\/SPAN><\/P> dissolved oxygen meter (in tidal environments the water table was often too <\/SPAN><\/P> low to measure Redox). <\/SPAN><\/P> - The water table depth was measured (if <30 cm). Note that in tidal <\/SPAN><\/P> environments this only represented the lower tide conditions.<\/SPAN><\/P> - Water temperature, pH, and conductivity. <\/SPAN><\/P> - In 2020-21 a total of 57 additional permanent monitoring plots were established in the 2021 monitoring round, across the following locations: Maketū Estuary (6), Waihī Estuary (10), Ōhiwa Harbour (18), Waiōtahe Estuary (13), and Ōpōtiki Estuary (10).<\/SPAN><\/P> - In 2021-22 a total of 31 additional permanent monitoring plots were established in the 2022 monitoring round across the following locations: Waihī Estuary (11 plots), Ōhiwa Estuary (14 plots), Waiōtahe Estuary (4 plots), and Tauranga Estuary (2 plots).<\/SPAN><\/P> - 7 plots were established within the Waihi Estuary in February 2023 (A4354815).<\/SPAN><\/P><\/DIV><\/DIV><\/DIV>",
"summary": "Bay of Plenty Regional Council is monitoring estuarine wetlands throughout the Bay \nof Plenty Region to determine what changes in condition and vegetation are occurring \nover time.",
"title": "Monitoring Site NERMN - Estuarine Wetland Vegetation",
"tags": [
"NERMN",
"Monitoring Site",
"Estuarine Wetland",
"Vegetation"
],
"type": "",
"typeKeywords": [],
"thumbnail": "",
"url": "",
"minScale": 150000000,
"maxScale": 5000,
"spatialReference": "",
"accessInformation": "Wildlands Consultants on behalf of BOPRC",
"licenseInfo": " Please check with Shay Dean before sharing externally<\/SPAN><\/P><\/DIV><\/DIV><\/DIV>",
"portalUrl": ""
}