Full text: Technical Commission VIII (B8)

   
  
   
   
  
   
   
   
   
  
   
  
   
   
  
   
   
   
   
  
  
   
  
   
    
    
   
  
  
    
    
   
  
   
    
     
    
  
  
   
     
   
   
  
  
   
   
  
  
   
    
  
  
   
    
   
  
   
   
   
   
   
   
  
     
st condition 
. 
0% for most 
ining surface 
. These data 
tressed state. 
| exceeded a 
surface water 
events in the 
> depends on 
ntation of ET 
aters have a 
lrer. A high 
indicative of 
is vegetation 
ation of this 
is been noted 
er (e.g. flood 
il, 2010b). 
' rates, which 
led with tree 
There was a 
between 1993 
T rates (Table 
| power and 
rs. A decline 
e species has 
s (Kingsford, 
1 2003, which 
| rainfall (516 
crease WAV 
8, which may 
iter associated 
srowth within 
n of both. In 
es and River 
lains wetland 
es to water 
adson, 2003; 
:d data used in 
sments of the 
points in time. 
her contextual 
use when the 
, for example, 
od’ condition, 
considered to 
ition extracted 
sidered to be 
dition may be 
NDVI and ET 
> of only three 
yvement to this 
rovide a more 
)VI within the 
| improve the 
ondition as the 
  
nature of riparian environments increases the complexity of 
these assessments. 
Despite these limitations, the results presented demonstrate the 
potential contribution of satellite-based remotely sensed data to 
improved understanding of water requirements and vegetation 
status within the Barmah Forest. The results show that the 
information provides an important opportunity for monitoring 
vegetation within riparian ecosystems. 
While this study focussed on the Barmah Forest, the nature of 
remotely sensed data enables the methods presented to be easily 
applied across broader landscapes. A significant advantage of 
using satellite-based measurements is that they are affordable, 
repeatable and offer a comprehensive assessment of a landscape 
rather than isolated point-based assessments. These 
characteristics lend themselves to a monitoring system that can 
be used to assess vegetation responses within riparian systems 
over time. This information can also be linked with other data 
sources or surveys (Lawrence and Colloff, 2008; Scott et al., 
2008; Sims and Colloff, 2012), as these complex riparian 
systems require many types of information to make water 
management decisions and assess the impacts of drought, flood 
and environmental flows. 
Remotely sensed data can be easily integrated with other spatial 
information such as vegetation mapping, flood extent mapping 
and digital elevation models. The monitoring potential of 
remotely sensed data (Anderson et al., 2012) can complement 
information provided by assessments of flooding requirements 
of plant species (Bacon et al., 1993; Dexter and Poynter, 2005; 
Fitzsimons et al., 2011; Peake et al, 2011). This suite of 
information can provide a more meaningful evaluation of the 
impacts of changing water availability within riparian systems 
and evaluate management practices. 
5. CONCLUSION 
Improved water management in riparian systems can be 
informed through a greater understanding of how much water is 
used and how much water is required. To achieve this, an 
objective, repeatable and affordable measurement system for 
vegetation status and water use is required. The use of satellite- 
based assessments of water use to support resource management 
and monitoring is advocated by Anderson et al (2012). This 
paper demonstrated the potential contribution of satellite-based 
measurements to improving understanding of water 
requirements and vegetation status within the Barmah Forest. 
Measures of ET and NDVI, analysed in conjunction with 
rainfall and river flow data, provided insights into the response 
of vegetation to changes in water availability, which could be 
used to evaluate impacts of managed water regimes and 
management practices within the riparian system. The data 
could also be used in conjunction with contextual information 
to provide baseline assessments of vegetation condition. The 
results presented in this paper show that remotely sensed data 
can potentially provide important monitoring opportunities 
within riparian ecosystems. 
6. ACKNOWLEDGEMENTS 
This work was supported by the Victorian Department of 
Primary Industries, the Victorian Department of Sustainability 
International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, Volume XXXIX-B8, 2012 
XXII ISPRS Congress, 25 August — 01 September 2012, Melbourne, Australia 
and Environment, the National Water Commission and the CRC 
Irrigation Futures. 
7. REFERENCES 
Allen, R. G., Pruitt, W. O., Wright, J. L., Howell, T. A. 
Ventura, F., Snyder, R., Itenfisu, D., Steduto, P., Berengena, J., 
Yrisarry, J. B., Smith, M., Pereira, L. S., Raes, D., Perrier, A., 
Alves, I., Walter, I. & Elliott, R. (2006) A recommendation on 
standardized surface resistance for hourly calculation of 
reference ET, by the FAO56 Penman-Moneith method. 
Agricultural Water Management, vol. 81, pp. 1-22. 
Allen, R. G., Tasumi, M., Morse, A., Trezza, R., Wright, J. L., 
Bastiaanssen, W., Kramber, W., Lorite, I. & Robison, C. W. 
(2007a) Satellite-Based Energy Balance for Mapping 
Evapotranspiration with Internalized Calibration (METRIC) - 
Applications. Journal of Irrigation and Drainage Engineering, 
vol. 133, pp. 395-406. 
Allen, R. G., Tasumi, M. & Trezza, R. (2007b) Satellite-Based 
Energy Balance for Mapping Evapotranspiration with 
Internalized Calibration (METRIC) - Model. Journal of 
Irrigation and Drainage Engineering, vol. 133, pp. 380-394. 
Anderson, M. C., Allen, R. G., Morse, A. & Kustas, W. P. 
(2012) Use of Landsat thermal imagery in monitoring 
evapotranspiration and managing water resources. Remote 
Sensing of Environment, corrected proof, in press. 
Bacon, P. E., Stone, C., Binns, D. L., Leslie, D. J. & Edwards, 
D. W. (1993) Relationships between water availability and 
Eucalyptus camaldulensis growth in a riparian forest. Journal 
of Hydrology, vol. 150, pp. 541-561. 
Bastiaanssen, W. G. M., Menenti, M., Feddes, R. A. & 
Holtslag, A. A. M. (1998) A remote sensing surface energy 
balance algorithm for land (SEBAL). 1. Formulation. Journal of 
Hydrology, vol. 212-213, pp. 198-212. 
Bastiaanssen, W. G. M., Noordman, E. J. M., Pelgrum, H., 
Davids, G., Thoreson, B. P. & Allen, R. G. (2005) SEBAL 
Model with Remotely Sensed Data to Improve Water-Resources 
Management under Actual Field Conditions. Journal of 
Irrigation and Drainage Engineering, vol. 131, pp. 85-93. 
Berrisford, M. J., Argent, R. M. & Malano, H. M. (2009) 
Causes and Consequences of Unutilised Irrigation Orders in the 
Central River Murray Area. Water Resources Management, vol. 
23, pp. 193-217. 
Chong, J. & Ladson, A. R. (2003) Analysis and Management of 
Unseasonal Flooding in the Barmah-Millewa Forest, Australia. 
River Research and Applications, vol. 19, pp. 161-180. 
Dexter, B. & Poynter, M. (2005) Water, Wood & Wildlife: 
Opportunities for the Riverain Red Gum Forests of the Central 
Murray. Victoria, Prepared for the National Asociation of 
Forest Industries, NSW Forest Productions Association Ltd, 
Timber Communities Australia Ltd, and Victorian Association 
of Forest Industries.
	        
Waiting...

Note to user

Dear user,

In response to current developments in the web technology used by the Goobi viewer, the software no longer supports your browser.

Please use one of the following browsers to display this page correctly.

Thank you.