IRRIGATION AUSTRALIA WEBSITE Channel Seepage Management Tool

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Remote non-invasive techniques

Direct and point seepage measurements techniques and subsurface characterisation identify seepage distribution and measure rates by directly measuring a physical property at a single location. For example, groundwater monitoring of water levels in a bore allows a direct measure of the watertable, and infiltration tests are direct measures of the soil properties at a point.

Geophysical surveys
, in contrast, use remote sensing, high-density sampling of subsurface and near-surface properties to provide continuous data along the channel.

Remote sensing: summary

Pages in this section include:

Remote sensing: summary

  Remote sensing: principle, method
  Remote sensing: applicability, practical implementation, experience from the trials, indicative costs

This page provides a summary of the remote sensing channel seepage identification and measurement technique.

Principle

Remote sensing refers to data recording by a sensor which measures energy emitted or reflected by objects located at some distance from the sensor Remote sensing techniques infer channel seepage based on soil moisture, vegetation vigour and soil profile properties adjacent to the channel.

In particular, airborne night thermal infrared imagery can provide an indication of shallow soil saturation resulting from lateral channel seepage, which may be a precursor to water logging and soil degradation.

There are no documented studies of remote sensing being used to quantify channel seepage, although it is now being used for detecting seepage locations.

More information

Method Top button

Remote sensing assumes that channel seepage has a surface expression adjacent to the channel.

This may be detected as increased soil moisture, vegetation vigour and water status. Techniques are limited to detecting seepage that migrates laterally through channel banks and surfaces near the channel toe.

Data must be of sufficient resolution to allow definition of seepage zones. Ground resolutions of less than 10m are required. The regions most useful for channel seepage detection include visible, reflected (near) infrared and thermal infrared. Source data should be multispectral (i.e. have data collected from more than one distinct region of the electromagnetic spectrum). Distinct data from the infrared region is expected to be the most beneficial as this area of the spectrum is strongly absorbed by water and is able to most distinctly separate areas of varying soil moisture and plant water and growth status.

Remote sensing data can be evaluated in conjunction with other spatial data such as that from EM surveys and soil survey assessments.

Increased surface moisture and vegetation growth due to channel seepage are likely to be evident during late summer and early autumn when surrounding areas (apart from irrigation) would be distinctly drier. This is likely to be the optimum data collection time. Imagery from more than one date would be useful to remove the seasonal variations such as irrigation or rainfall.

Remotely sensed image data sources may include:
  • Digital infrared aerial photography
  • Airborne high-resolution sensor data
  • Satellite imagery
More information

Applicability Top button
  • Remote sensing offers considerable potential for effective identification of seepage zones of large lengths of a channel system without interfering with channel operations. Quantification needs to be based on further analysis.
  • Remote sensing is appropriate for investigations where the primary aim is identification of land degradation associated with channel seepage. It should not be used if it is known that the seepage mechanism is predominantly vertical, which is likely to occur at sites with a deep watertable.
  • Remote sensing is most useful in environments where lateral seepage is predominant. Sites with a high watertable, shallow impermeable layer or bank seepage have conditions that can cause seepage to have a surface expression.
Remote sensing is a tool for targeting potential seepage sites, although a drawback is that it assumes seepage will have a surface expression as moist soil or associated vegetation adjacent to the channel.

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Practical implementation Top button

Remote sensing is relatively expensive and requires specialist technical input at the planning, data gathering, processing and interpretation stages. However, it can rapidly acquire data over long distances of channel, and along with geophysical surveys it is likely to be a key part of future large-scale channel seepage investigations.

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Indicative costs Top button

Costs vary widely depending on the source data used. As an indication of the likely data collection costs, suitable quality airborne infrared data (3-5m resolution) for three lengths of channel (10-20km each) were quoted at around $11,000. Data processing costs, including integration with a GIS system are in addition to these costs and likely to be in the order of $5,000-10,000.

More information

Related pages Top button

For a more detailed description of the remote sensing technique see:

Remote sensing: principle, method
Remote sensing: applicability, practical implementation, experience from the trials, indicative costs
   

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Page last reviewed on 7/3/04