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- Namoi subregion
- 2.1-2.2 Data analysis for the Namoi subregion
- 2.1.5 Surface water – groundwater interactions
- 2.1.5.3 Overview of controls on surface water – groundwater connectivity based on previous...
- 2.1.5.3 Overview of controls on surface water – groundwater connectivity based on previous investigations in the Namoi river basin
There is a degree of subjectivity in categorising a stream reach as connected or disconnected and a flux as gaining, variably gaining-losing or losing due to the dynamic variations in both groundwater and stream stage elevations that change temporally and spatially in response to a range of natural and human factors, some of which are listed below.
2.1.5.3.1 Natural controls
Hydrologic fluxes between surface water and groundwater systems are partly controlled by:
- the depth of the unconsolidated alluvial sediments
- the difference in elevation between the watertable adjacent to the stream and the corresponding stream stage
- the permeability and hydraulic conductivity of aquifer and streambed sediments
- the subsurface extent of transmissive versus confining layers existing between the upper aquifer and stream sediments
- aquifer–stream geometry
- climate and hydrological factors which influence the rainfall–runoff and recharge–discharge dynamics (including droughts and flooding), which in turn control groundwater and stream stage elevations.
2.1.5.3.2 Human controls
Human factors will have a measurable control on groundwater and stream stage elevations, with hydraulic gradients continually responding to these factors. Human factors include:
- river regulation
- surface and groundwater extractions
- land and water use.
The shallow aquifers of the Upper Namoi and Peel rivers have been identified by Barrett (2012) as highly connected to the adjacent streams, with more than 70% of the groundwater extraction volumes estimated to be derived from streamflow (Broadstock, 2009). In these areas groundwater recharge and resource availability is highly dependent on surface water flows (Green et al., 2011), and groundwater extraction bores are commonly located within a few kilometres of connected aquifer–stream systems.
Groundwater extraction from aquifers in hydraulic connection with a stream may result in a reversal of flux direction, with the direction of flow dependent on the difference between the groundwater elevation and stream stage. Gaining streams may become variably gaining-losing streams as groundwater elevation and stream stage relationships fluctuate under the influence of groundwater extractions. A lowered watertable, relative to stream height, results in the loss of streamflows to the underlying groundwater system (induced recharge). Eventually, a gaining stream may become a losing reach if the watertable continues to be lowered and there are insufficient volumes of groundwater recharge to compensate for the volumes of groundwater extracted. A time lag exists between the commencement of groundwater extraction and the impact on streamflow. As the distance between an extraction bore and stream increases, so does the lag in the timing between the start of pumping and the impact on streamflow (CSIRO and SKM, 2012b). A time lag also exists between the onset of groundwater extractions upgradient, and the resultant impact on throughflow down gradient, at the end of a river basin.
The impact of groundwater extractions on the adjacent stream was demonstrated by Ivkovic et al. (2009), who used a lumped parameter model to simulate the influence of groundwater extractions in the Coxs creek basin using 15 years of streamflow data. The model indicated that groundwater extractions from 1988 to 2003 had the effect of reducing baseflow discharges by approximately 82% of the volume of groundwater extracted (for rates up to 9000 ML/year), although the actual yearly reductions might be more or less depending on the particular climatic period. The remaining 18% of the total volume of groundwater extraction was assumed to affect the available volumes of subsurface throughflow, ultimately impacting on downstream flows. At extraction rates above 9000 ML/year, the model findings indicated that the stream would transition to a disconnected stream reach. Similar findings have been made for the Lower Namoi river basin. CSIRO (2007) reported that the Lower Namoi River has changed from a substantial gaining river prior to irrigated agricultural development to now become a largely losing river. They estimated that the current level of groundwater extraction in the Namoi river basin (as of 2007) would eventually reduce mean streamflow by a total of 99 GL/year.
Product Finalisation date
- 2.1.1 Geography
- 2.1.2 Geology
- 2.1.3 Hydrogeology and groundwater quality
- 2.1.4 Surface water hydrology and water quality
- 2.1.5 Surface water – groundwater interactions
- 2.1.5.1 Observed data
- 2.1.5.2 Previous catchment-scale investigations on stream-aquifer interactions
- 2.1.5.3 Overview of controls on surface water – groundwater connectivity based on previous investigations in the Namoi river basin
- 2.1.5.4 Statistical analysis and interpolation
- 2.1.5.5 Gaps
- References
- Datasets
- 2.1.6 Water management for coal resource developments
- 2.1.6.1 Boggabri Coal Mine (baseline) and Boggabri Coal Expansion Project (ACRD)
- 2.1.6.2 Narrabri North Mine (baseline)
- 2.1.6.3 Narrabri South Project (ACRD)
- 2.1.6.4 Rocglen Mine (baseline)
- 2.1.6.5 Sunnyside Mine (baseline)
- 2.1.6.6 Tarrawonga Mine (baseline) and Tarrawonga Coal Expansion Project (ACRD)
- 2.1.6.7 Caroona Coal Project (ACRD)
- 2.1.6.8 Maules Creek Project (ACRD)
- 2.1.6.9 Watermark Coal Project (ACRD)
- 2.1.6.10 Vickery Coal Project (ACRD)
- 2.1.6.11 Narrabri Gas Project (ACRD)
- 2.1.6.12 Mine footprints
- References
- Datasets
- Citation
- Acknowledgements
- Currency of scientific results
- Contributors to the Technical Programme
- About this technical product