AndreaBozzo/ceres-open-data-index huggingface dataset:
Indigofera oxyrachis potential habitat grid


## **Abstract** 
The dataset was compiled by the Geological and Bioregional Assessment Program from source data referenced within the dataset and/or metadata. Indigofera oxyrachis potential habitat grid


## **Attribution** 
Geological and Bioregional Assessment Program


## **History** 
This dataset was created by intersecting WildNet observations with the Queensland regional ecosystem layers. All REs intersecting with these points were considered potential habitat and burned into a 500 m reference grid.

Organization: Bioregional Assessment Program
Defence Aviation Area Regulations

Defence Aviation Area Regulations. Correct as of May 2021. This file shows height constraints on development and activities around Australian Department of Defence Airfields.

Note: This file is a guide only and should not be used for detailed planning. Always refer to the Australian Department Defence for development approval.

Part 11A of the Defence Regulations, 2016 provides a legal framework for controlling activities which may be dangerous to aviation around a number of declared Defence Aviation Areas (DAA).

The Defence Regulations can be downloaded at https://www.legislation.gov.au/Details/F2018C00183.

The Defence Aviation Areas website is https://www.defence.gov.au/id/AviationAreas.asp.

The DAA replaces the Defence (Areas Control) Regulations 1989 (DACR) which were repealed on 25 March 2018 but closely replicate the controls available to Defence under the DACR. 

The regulations apply to permanent structures such as buildings and communication towers, and temporary structures such as cranes within approximately 15 kilometres of DAA. Vegetation, including trees and plants used for landscaping, and gas plumes emanating from an exhaust stack are also covered. The regulations also apply to any object hazardous to aircraft or aviation-related communications, navigation or surveillance regardless of whether the DAA height controls are triggered.    

Maps attached to each DAA declaration for each declared Defence Aviation Area show the heights at which proposed structures need to be referred to Defence for approval.


Tags: Airfields, Boundaries, Construction, DAAR, Defence, Defence Aviation Areas Regulations, Location, Planning and Cadastre, Structures, airfields, construction, regulations, structures
Organization: Department of Defence
Denitrification measurements of sediments using cores and chambers: comparison of fluxes and denitrification efficiencies

Denitrification is a microbial process that takes place on and within sediment and results in the transformation of dissolved inorganic nitrogen to nitrogen gas (N2), which is subsequently lost to the atmosphere.  In coastal waters denitrification is an important pathway for the removal of excess nitrogen.  Rates of denitrification are typically quantified using either in situ benthic chambers or sediment cores incubated in the laboratory.  This study assesses if these two approaches give similar fluxes and denitrification efficiencies.  This dataset gives fluxes of: i) dissolved oxygen (DO); ii) nitrogen gas (N2); iii) dissolved inorganic nitrogen (DIN); iv) nitrate (NO3-); v); nitrite (NO2-) and vi) ammonium (NH4+) between the sediment and the water column.  Results are obtained using core cylinders incubated in the laboratory and in situ benthic chambers.  Fluxes are expressed as µmol m-2 of seafloor surface day-1.  Denitrification efficiency is also reported and represents the flux of N2 as a proportion of the total flux of DIN.  Studies were carried out in Port Phillip Bay at Clifton Springs and Williamstown, Victoria in March and May 2004, respectively. The flux of oxygen, ammonium, nitrate, nitrite and the denitrification efficiency was found to differ between in situ benthic chambers and laboratory incubated sediment cores.  Additional experiments were conducted to assess if the abundance of macrofauna in sediments of core cylinders and benthic chambers differed; and ii) if physical disturbance associated with the collection and transport of core cylinders could account for the observed differences.

Tags: Aquatic Habitat, Benthic Habitat, Biosphere, Denitrification Rate, Ecological Dynamics, Environmental Impacts, Eutrophication, Human Dimensions, Hydrosphere, Invertebrates, Land Surface, Marine Biology, Marine Invertebrates, Nitrate, Nitrite, Nutrients, Ocean Chemistry, Oceans, Oxygen, Oxygen Demand, Port Phillip Bay, Soils, Water Quality, Zoology, benthic chambers, macrofauna, nutrient flux, sediment cores
Organization: School of BioSciences, The University of Melbourne
Derwent Estuary Ambient Water Quality monitoring program - Site B1

Site B1 is sampled monthly by the Derwent Estuary Program as part of the  Derwent Ambient Water Quality monitoring program.
Since 2003, ambient water quality monitoring has been carried out on a monthly basis at up to 28 sites throughout the Derwent estuary by Norske Skog Boyer, Nyrstar Hobart and the State Government. Monitoring is carried out by three different boat-based sampling parties, but is co-ordinated to occur on the same day each month. 
At each site, in-situ field measurements are taken using calibrated sensors for temperature, salinity, pH, dissolved oxygen and turbidity. Water clarity is also measured using a secchi disk. Surface and bottom water samples are collected for analysis of true color, total suspended solids(TSS), total  and dissolved nutrients, organic carbon and zinc. at most sites, depth integrated samples are also collected for chlorophyll a using a plastic tube. Bottom samples in the Middle and Outer estuary are collected using a niskin bottle. Pumps are used in the upper estuary site to fill up the bottles. All water samples are analysed at Analytical Service Tasmania, a National Association of Testing Authorities-accredited laboratory. Monitoring site depth is 2 meters

Tags: Ammonia, Chlorophyll, Conductivity, Derwent Estuary, Hydrolab Vertical Profiler, Niskin Bottles, Nitrate, Nitrite, Nitrogen Compounds, Ocean Chemistry, Ocean Optics, Oceans, Oxygen, Ph, Phosphate, Phosphorous Compounds, Salinity, Secchi Depth, Secchi Disks, Suspended Solids, Trace Metals, True Colour, Turbidity, Water Quality, Water Temperature
Organization: Environment Protection Authority Tasmania
Cost of Salinity to Local Infrastructure 1996-97 – Total cost of the general infrastructure component (buildings etc derived from population) based on the best estimate as described in the project reports. Costs are estimates of the impact of the extent of salinity projected to occur in 2020

    

This dataset contains 14 national surfaces, represented by 1km grids, relating
to the cost of salinity damage to local infrastructrure. The infrastructure
cost impacts are limited to those that occur at the location of salinity
problem, downstream and other offsite impacts are not covered. All dollar
values are given in 1996/97 Australian dollars. Each is described as
follows:1. Total cost ($) to all infrastructure (buildings, road, rail and
bridges) based on the low, abesta and high estimates of the impact of the
current (2000) extent of salinity.2. Total cost ($) to all infrastructure
(buildings, road, rail and bridges) based on the low, abesta and high
estimates of the impact of predicted 2020 extent of salinity3. Total cost ($)
the general infrastructure component (buildings etc., derived from population)
as the abesta estimate of the impact of the current (2000) extent of
salinity.4. Total cost ($) the general infrastructure component (buildings
etc., derived from population) based on the abesta estimate of the impact of
the predicted 2020 extent of salinity5. Total cost ($) the road component of
infrastructure based on the abesta estimate of the impact of the current
(2000) extent of salinity.6. Total cost ($) the road component of
infrastructure based on the abesta estimate of the impact of the predicted
2020 extent of salinity7. Total cost ($) the rail component of infrastructure
based on the abesta estimate of the impact of the current (2000) extent of
salinity.8. Total cost ($) the rail component of infrastructure based on the
abesta estimate of the impact of the predicted 2020 extent of salinity9. Total
cost ($) the bridge component of infrastructure based on the abesta estimate
of the impact of the current (2000) extent of salinity.10. Total cost ($) the
bridge component of infrastructure based on the abesta estimate of the impact
of the predicted 2020 extent of salinity11. Total cost ($) increase to local
infrastructure based on the abesta estimate of the impact of the predicted
2020 extent of salinity

See [further metadata](http://data.daff.gov.au/anrdl/metadata_files/pa_csli_r9cl
__08012a05.xml) for more detail.



Tags: economics, farming, humanenvironment, utilities, waterquality
Organization: Australian Bureau of Agricultural and Resource Economics and Sciences
Derwent Estuary Ambient Water Quality monitoring program - Site B3

Site B3 is sampled monthly by the Derwent Estuary Program as part of the  Derwent Ambient Water Quality monitoring program.
Since 2003, ambient water quality monitoring has been carried out on a monthly basis at up to 28 sites throughout the Derwent estuary by Norske Skog Boyer, Nyrstar Hobart and the State Government. Monitoring is carried out by three different boat-based sampling parties, but is co-ordinated to occur on the same day each month. 
At each site, in-situ field measurements are taken using calibrated sensors for temperature, salinity, pH, dissolved oxygen and turbidity. Water clarity is also measured using a secchi disk. Surface and bottom water samples are collected for analysis of true color, total suspended solids(TSS), total  and dissolved nutrients, organic carbon and zinc. at most sites, depth integrated samples are also collected for chlorophyll a using a plastic tube. Bottom samples in the Middle and Outer estuary are collected using a niskin bottle. Pumps are used in the upper estuary site to fill up the bottles. All water samples are analysed at Analytical Service Tasmania, a National Association of Testing Authorities-accredited laboratory. Monitoring site depth is 2 meters

Tags: Ammonia, Chlorophyll, Conductivity, Derwent Estuary, Hydrolab Vertical Profiler, Niskin Bottles, Nitrate, Nitrite, Nitrogen Compounds, Ocean Chemistry, Ocean Optics, Oceans, Oxygen, Ph, Phosphate, Phosphorous Compounds, Salinity, Secchi Depth, Secchi Disks, Suspended Solids, Trace Metals, True Colour, Turbidity, Water Quality, Water Temperature
Organization: Environment Protection Authority Tasmania
Derwent Estuary Ambient Water Quality monitoring program - Site B5

Site B5 is sampled monthly by the Derwent Estuary Program as part of the  Derwent Ambient Water Quality monitoring program.
Since 2003, ambient water quality monitoring has been carried out on a monthly basis at up to 28 sites throughout the Derwent estuary by Norske Skog Boyer, Nyrstar Hobart and the State Government. Monitoring is carried out by three different boat-based sampling parties, but is co-ordinated to occur on the same day each month. 
At each site, in-situ field measurements are taken using calibrated sensors for temperature, salinity, pH, dissolved oxygen and turbidity. Water clarity is also measured using a secchi disk. Surface and bottom water samples are collected for analysis of true color, total suspended solids(TSS), total  and dissolved nutrients, organic carbon and zinc. at most sites, depth integrated samples are also collected for chlorophyll a using a plastic tube. Bottom samples in the Middle and Outer estuary are collected using a niskin bottle. Pumps are used in the upper estuary site to fill up the bottles. All water samples are analysed at Analytical Service Tasmania, a National Association of Testing Authorities-accredited laboratory. Monitoring site depth is 2 meters

Tags: Ammonia, Chlorophyll, Conductivity, Derwent Estuary, Hydrolab Vertical Profiler, Niskin Bottles, Nitrate, Nitrite, Nitrogen Compounds, Ocean Chemistry, Ocean Optics, Oceans, Oxygen, Ph, Phosphate, Phosphorous Compounds, Salinity, Secchi Depth, Secchi Disks, Suspended Solids, Trace Metals, True Colour, Turbidity, Water Quality, Water Temperature
Organization: Environment Protection Authority Tasmania
Derwent Estuary Ambient Water Quality monitoring program - Site C

Site C is sampled monthly by the Derwent Estuary Program as part of the  Derwent Ambient Water Quality monitoring program.
Since 2003, ambient water quality monitoring has been carried out on a monthly basis at up to 28 sites throughout the Derwent estuary by Norske Skog Boyer, Nyrstar Hobart and the State Government. Monitoring is carried out by three different boat-based sampling parties, but is co-ordinated to occur on the same day each month. 
At each site, in-situ field measurements are taken using calibrated sensors for temperature, salinity, pH, dissolved oxygen and turbidity. Water clarity is also measured using a secchi disk. Surface and bottom water samples are collected for analysis of true color, total suspended solids(TSS), total  and dissolved nutrients, organic carbon and zinc. at most sites, depth integrated samples are also collected for chlorophyll a using a plastic tube. Bottom samples in the Middle and Outer estuary are collected using a niskin bottle. Pumps are used in the upper estuary site to fill up the bottles. All water samples are analysed at Analytical Service Tasmania, a National Association of Testing Authorities-accredited laboratory. Monitoring site depth is 2 meters

Tags: Ammonia, Chlorophyll, Conductivity, Derwent Estuary, Hydrolab Vertical Profiler, Niskin Bottles, Nitrate, Nitrite, Nitrogen Compounds, Ocean Chemistry, Ocean Optics, Oceans, Oxygen, Ph, Phosphate, Phosphorous Compounds, Salinity, Secchi Depth, Secchi Disks, Suspended Solids, Trace Metals, True Colour, Turbidity, Water Quality, Water Temperature
Organization: Environment Protection Authority Tasmania
Current values collected through the water column using an Acoustic Doppler Current Profiler (ADCP) in the centre of Jervis Bay: Summer Deployment

The record describes data collected from a summer deployment of an Acoustic Doppler Current Profiler (ADCP) moored in the central part of Jervis Bay, New South Wales (35o 05'S, 150o 44'E). An ADCP measures how fast water is moving across an entire water column. Anchored to the seafloor it can measure current speed not just at the bottom, but also at equal intervals all the way up to the surface. For this experiment, the ADCP was moored on the seabed, in a frame, with sensors looking upwards and approximately 0.5m above the seabed. 

Over the summer deployment, 13th December 1990 to 15th January 1991, the ADCP was set-up with a 15 minute sampling interval and currents were measured over 1m depth bins. Bin numbers and currents are referenced as a height above the seabed (due to the uncertainty in defining water depth because of tides and air pressure). As such Bin #1 is centered at 1.5m above the transducer face or 2.0m above the seabed. Bin #2 is centered at 3m above the seabed, Bin #3 at 4m and so on.  

Three resources are provided: 1) A schematic of depth bin locations for the summer deployment, 2) Unfiltered east/west and north/south current values for every 15 minutes of the experiment, and 3) Low-pass filtered east/west and north/south hourly current values to remove tidal period motion. The filter has a half amplitude response at 32 hours and 48 hourly weights.

This child record relates to the parent, b146e140-2ae6-11dd-a735-00188b4c0af8. A pdf outlining the structure and hierarchy of all metadata records relating to this project is available to download through this record. Also available is a pdf of a published working paper documenting this experiment and the results.

Tags: Ocean Circulation, Oceans, Tidal Components, Tidal Currents, Tides, Water Masses, Wind-driven Circulation
Organization: Australian Defence Force Academy (ADFA)
Derwent Estuary Ambient Water Quality monitoring program - Site CB

Site CB is sampled monthly by the Derwent Estuary Program as part of the  Derwent Ambient Water Quality monitoring program.
Since 2003, ambient water quality monitoring has been carried out on a monthly basis at up to 28 sites throughout the Derwent estuary by Norske Skog Boyer, Nyrstar Hobart and the State Government. Monitoring is carried out by three different boat-based sampling parties, but is co-ordinated to occur on the same day each month. 
At each site, in-situ field measurements are taken using calibrated sensors for temperature, salinity, pH, dissolved oxygen and turbidity. Water clarity is also measured using a secchi disk. Surface and bottom water samples are collected for analysis of true color, total suspended solids(TSS), total  and dissolved nutrients, organic carbon and zinc. at most sites, depth integrated samples are also collected for chlorophyll a using a plastic tube. Bottom samples in the Middle and Outer estuary are collected using a niskin bottle. Pumps are used in the upper estuary site to fill up the bottles. All water samples are analysed at Analytical Service Tasmania, a National Association of Testing Authorities-accredited laboratory. Monitoring site depth is 2 meters

Tags: Ammonia, Chlorophyll, Conductivity, Derwent Estuary, Hydrolab Vertical Profiler, Niskin Bottles, Nitrate, Nitrite, Nitrogen Compounds, Ocean Chemistry, Ocean Optics, Oceans, Oxygen, Ph, Phosphate, Phosphorous Compounds, Salinity, Secchi Depth, Secchi Disks, Suspended Solids, Trace Metals, True Colour, Turbidity, Water Quality, Water Temperature
Organization: Environment Protection Authority Tasmania
Derwent Estuary Ambient Water Quality monitoring program - Site E

Site E is sampled monthly by the Derwent Estuary Program as part of the  Derwent Ambient Water Quality monitoring program.
Since 2003, ambient water quality monitoring has been carried out on a monthly basis at up to 28 sites throughout the Derwent estuary by Norske Skog Boyer, Nyrstar Hobart and the State Government. Monitoring is carried out by three different boat-based sampling parties, but is co-ordinated to occur on the same day each month. 
At each site, in-situ field measurements are taken using calibrated sensors for temperature, salinity, pH, dissolved oxygen and turbidity. Water clarity is also measured using a secchi disk. Surface and bottom water samples are collected for analysis of true color, total suspended solids(TSS), total  and dissolved nutrients, organic carbon and zinc. at most sites, depth integrated samples are also collected for chlorophyll a using a plastic tube. Bottom samples in the Middle and Outer estuary are collected using a niskin bottle. Pumps are used in the upper estuary site to fill up the bottles. All water samples are analysed at Analytical Service Tasmania, a National Association of Testing Authorities-accredited laboratory. Monitoring site depth is 2 meters

Tags: Ammonia, Chlorophyll, Conductivity, Derwent Estuary, Hydrolab Vertical Profiler, Niskin Bottles, Nitrate, Nitrite, Nitrogen Compounds, Ocean Chemistry, Ocean Optics, Oceans, Oxygen, Ph, Phosphate, Phosphorous Compounds, Salinity, Secchi Depth, Secchi Disks, Suspended Solids, Trace Metals, True Colour, Turbidity, Water Quality, Water Temperature
Organization: Environment Protection Authority Tasmania
Derwent Estuary Ambient Water Quality monitoring program - Site G2

Site G2 is sampled monthly by the Derwent Estuary Program as part of the  Derwent Ambient Water Quality monitoring program.
Since 2003, ambient water quality monitoring has been carried out on a monthly basis at up to 28 sites throughout the Derwent estuary by Norske Skog Boyer, Nyrstar Hobart and the State Government. Monitoring is carried out by three different boat-based sampling parties, but is co-ordinated to occur on the same day each month. 
At each site, in-situ field measurements are taken using calibrated sensors for temperature, salinity, pH, dissolved oxygen and turbidity. Water clarity is also measured using a secchi disk. Surface and bottom water samples are collected for analysis of true color, total suspended solids(TSS), total  and dissolved nutrients, organic carbon and zinc. at most sites, depth integrated samples are also collected for chlorophyll a using a plastic tube. Bottom samples in the Middle and Outer estuary are collected using a niskin bottle. Pumps are used in the upper estuary site to fill up the bottles. All water samples are analysed at Analytical Service Tasmania, a National Association of Testing Authorities-accredited laboratory. Monitoring site depth is 2 meters

Tags: Ammonia, Chlorophyll, Conductivity, Derwent Estuary, Hydrolab Vertical Profiler, Niskin Bottles, Nitrate, Nitrite, Nitrogen Compounds, Ocean Chemistry, Ocean Optics, Oceans, Oxygen, Ph, Phosphate, Phosphorous Compounds, Salinity, Secchi Depth, Secchi Disks, Suspended Solids, Trace Metals, True Colour, Turbidity, Water Quality, Water Temperature
Organization: Environment Protection Authority Tasmania
Cost of Salinity to Local Infrastructure 1996-97 – Total cost of the rail component of infrastructure based on the best estimate as described in the project reports. Costs are estimates of the impact of the current (2000) extent of salinity

    

This dataset contains 14 national surfaces, represented by 1km grids, relating
to the cost of salinity damage to local infrastructrure. The infrastructure
cost impacts are limited to those that occur at the location of salinity
problem, downstream and other offsite impacts are not covered. All dollar
values are given in 1996/97 Australian dollars. Each is described as
follows:1. Total cost ($) to all infrastructure (buildings, road, rail and
bridges) based on the low, abesta and high estimates of the impact of the
current (2000) extent of salinity.2. Total cost ($) to all infrastructure
(buildings, road, rail and bridges) based on the low, abesta and high
estimates of the impact of predicted 2020 extent of salinity3. Total cost ($)
the general infrastructure component (buildings etc., derived from population)
as the abesta estimate of the impact of the current (2000) extent of
salinity.4. Total cost ($) the general infrastructure component (buildings
etc., derived from population) based on the abesta estimate of the impact of
the predicted 2020 extent of salinity5. Total cost ($) the road component of
infrastructure based on the abesta estimate of the impact of the current
(2000) extent of salinity.6. Total cost ($) the road component of
infrastructure based on the abesta estimate of the impact of the predicted
2020 extent of salinity7. Total cost ($) the rail component of infrastructure
based on the abesta estimate of the impact of the current (2000) extent of
salinity.8. Total cost ($) the rail component of infrastructure based on the
abesta estimate of the impact of the predicted 2020 extent of salinity9. Total
cost ($) the bridge component of infrastructure based on the abesta estimate
of the impact of the current (2000) extent of salinity.10. Total cost ($) the
bridge component of infrastructure based on the abesta estimate of the impact
of the predicted 2020 extent of salinity11. Total cost ($) increase to local
infrastructure based on the abesta estimate of the impact of the predicted
2020 extent of salinity

See [further metadata](http://data.daff.gov.au/anrdl/metadata_files/pa_csli_r9cl
__08012a08.xml) for more detail.



Tags: economics, farming, humanenvironment, utilities, waterquality
Organization: Australian Bureau of Agricultural and Resource Economics and Sciences