Full description
Water quality and biological data was collected from four tide-dominated river estuaries indicative of catchments with varying levels of human impacts to: 1) assess draft indicator levels for water quality, and 2) investigate biological indicators of estuarine health in NW Tasmania. This data includes sampling from Detention River, Duck Bay, Montagu River and Black RiverLineage
Maintenance and Update Frequency: notPlanned
Statement: Each estuary was visited twice during the course of this study to measure a range of water quality parameters (nutrients, turbidity etc.) and sample estuarine biological assemblages (benthic invertebrates and fish). Estuaries were visited initially in late November/early December 2004, and then approximately four months later in early April 2005. Each estuary was sampled from its mouth (sea-estuary interface) to the uppermost reach of tidal influence that could be easily accessed from the shore or via a small boat. In practice, each eastuar was split into four regions (marine, lover, mid and upper) on the basis of salinity, habitat (particularly the appearance of the benthos) and distance from the mouth. Within each estuary three sites were randomly assigned to each regions, each separated by a distance of a few hundred metres.
Water quality within each of the four estuaries was measured at the first and third site within each regions - a subset of 8 out of a total of 12 designated sites per estuary. During each visit water quality parameters were measured at high and low tide, within the same 24 hour period, to examine the extent to which these parameters varied between tides. The water quality parameters measured in this study were: salinity (ppt), dissolved oxygen concentrations (%DO), turbidity (NTU), and dissolved nutrients including ammonia, nitrate, nitrite and reactive phosphorus (ug/L). Water quality measurements were made mid-channel (i.e. equidistant from either bank) within surface waters <30cm. Salinity, DO, and turbidity were measured in the field using meters. Nutrient levles were determined later in the lab from water samples collected in the field. Dissolved nutrients were collected and analysed using standard protocols by Analytical Services Tasmania.
Benthic macroinvertebrates
The diversity and composition of the soft sediment invertebrate fauna in each estuary was determined using replicated sediment cores collected at each site. All sampling was undertaken at low tide using methods comparable ot those utilised by Edgar et al. (1999). At each site five sediment cores (diameter = 150mm, depth = 100mm) were collected from subtidal sediments using a rough transect (spanning from the low tide mark to a depth of 0.7m where applicable) as a guide. Cores were collected at 0.0, 0.1, 0.2, 0.3, and 0.7m depths. Cores were seived through a 1.0mm sieve in the field and the portion retained was fixed in 10% buffered formalin. Invertebrate taxa were identified to species, where possible, and counted.
Salinity, dissolved oxygen and turbidity were recorded for the bottom waters overlying the area of benthos sampled (probes were generally placed on the sediment). Sediments from each site were collected using five 30cm diameter cores (corresponding with the 5 biological sediment samples collected), and the sediments amalgamated. In the lab, sediment particle-size distribution was determined by wet sieving samples through a nested series of sieves (0.63, 0.125, 0.25, 0.5, 1, 2 and 4mm mesh size). The sediments retained by different sieves were weighed after drying at 50oC. The proportion of fine particulates <0.63mm that passed through the final sieve was calculated by subtracting the total weight of sediments retained on the nested sieves from the initial dried weight of the sediment sample. Sieve fractions were expressed as a % fo the total sediment sample. Organic carbon content of the sediments was calculated by loss of organic carbon on ignition at 500oC. Sediments were first treated with 1M hydrocholoric acid to remove inorganic carbon in the form of carbonates prior to combustion.
Fish biodiversity
Limited fish sampling was conducted in spring, and only in the the lower reaches of the estuaries. Demersal fish assemblages were sampled using a standard 3 x 35mm beach seine, with 13mm mesh size. This precluded sampling in the mid and upper regions of the estuaries due to the size of the net and the retricted nature of the benthic habitats among the sites. Captured fish were identified, counted and then released.
Notes
CreditNatural Heritage Trust (NHT) and National Action Plan (NAP) Project No. 46927
Purpose
The design utilise, broadly contrasts estuaries within catchments relatively free of human impacts (Black and Detention Rivers) with estuaries situated within more degraded catchments (Duck and Montagu Rivers).
The design utilise, broadly contrasts estuaries within catchments relatively free of human impacts (Black and Detention Rivers) with estuaries situated within more degraded catchments (Duck and Montagu Rivers).
Created: 26 03 2015
Data time period: 15 11 2004 to 15 04 2005
text: westlimit=145.40; southlimit=-40.90; eastlimit=145.50; northlimit=-40.80
text: westlimit=145.10; southlimit=-40.80; eastlimit=145.00; northlimit=-40.70000000000001
text: westlimit=144.90; southlimit=-40.80; eastlimit=145.00; northlimit=-40.70000000000001
text: westlimit=145.30; southlimit=-40.90; eastlimit=145.40; northlimit=-40.80
text: uplimit=1; downlimit=0
Subjects
Agricultural and Veterinary Sciences |
ANIMALS/VERTEBRATES |
AQUATIC ECOSYSTEMS |
Aquaculture |
BENTHIC HABITAT |
BIOLOGICAL CLASSIFICATION |
Biological Sciences |
BIOSPHERE |
Benthic macroinvertebrates |
COASTAL PROCESSES |
Concentration of ammonium {NH4} per unit volume of the water body |
Concentration of nitrate and nitrite {NO3 and NO2} per unit volume of the water body |
Concentration of nitrate {NO3} per unit volume of the water body |
Concentration of nitrite {NO2} per unit volume of the water body |
Concentration of oxygen {O2} per unit volume of the water body |
Conservation and Biodiversity |
Degradation |
EARTH SCIENCE |
Ecology |
Environmental Science and Management |
Environmental Sciences |
ESTUARINE HABITAT |
Environmental Management |
FISH |
Fisheries Sciences |
Human impact |
INTERTIDAL ZONE |
Marine and Estuarine Ecology (Incl. Marine Ichthyology) |
NUTRIENTS |
Natural Resource Management |
OCEANS |
OXYGEN |
Practical salinity of the water body |
SALINITY |
TURBIDITY |
Temperate Reef |
Turbidity of the water body |
WATER QUALITY |
Wildlife and Habitat Management |
oceans |
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Other Information
Download data in a range of formats via OGC WFS. (NH1_CMCrawford_Biodiversity_degradation_GV)
url :
https://geoserver.imas.utas.edu.au/geoserver/imas/wfs
MAP - Locations of estuary sampling for assessment of biodiversity and degradation (NH1_CMCrawford_Biodiversity_degradation_GV)
url :
https://geoserver.imas.utas.edu.au/geoserver/imas/wms
Hirst, A. J., Kilpatrick, R., Mount, R. E., Guest, M. A., & Crawford, C. (2005). Biodiversity and degradation of estuaries in north-western Tasmania. Tasmanian Aquaculture and Fisheries Institute, University of Tasmania. (Final project report)
View and download this data through the interactive IMAS Data Portal.
url :
https://data.imas.utas.edu.au/portal/search?uuid=53c0cf81-9188-447d-9d21-8c779ddc5b96
Identifiers
- global : 53c0cf81-9188-447d-9d21-8c779ddc5b96
