A reach‐scale remote sensing technique to relate wetland inundation to river flow

Knowledge of the relationship between river flow and wetland inundation at a reach-scale is important for effective flow management, particularly, for environmental outcomes. Historical remotely sensed data, such as Landsat TM, provide the potential to determine the relationship between flow and wetland inundation for extended river reaches. In this paper we apply, adapt and evaluate a technique using sets of before-flood and after-flood image pairs to relate river flow to wetland inundation on a 640 km reach of the mid-Murrumbidgee River, Australia. Stratification of the complete reach into relatively uniform sub-reaches on the basis of hydrology and geomorphology was undertaken as a key pre-analysis step. Analysis of flood wave attenuation within each sub-reach showed that flood peaks entering and leaving a reach were highly correlated. Therefore, we argue that a flood peak measured at a single gauge within the reach can be used to provide a reliable indication of the behaviour of similar sized floods within the reach. The remote sensing technique proved capable of producing a model relating wetland inundation thresholds to flood peak discharge for each sub-reach within the extended river reach. Although the model simplifies the complex relationship between river flow and wetland inundation, reliable key wetland inundation flow thresholds were determined. Copyright © 2008 John Wiley & Sons, Ltd.

[1]  L. Smith,et al.  Estimation of Discharge From Three Braided Rivers Using Synthetic Aperture Radar Satellite Imagery: Potential Application to Ungaged Basins , 1996 .

[2]  R. Kingsford Ecological Impacts and Institutional and Economic Drivers for Water Resource Development--a Case Study of the Murrumbidgee River, Australia , 2003 .

[3]  Paul D. Bates,et al.  Remote sensing and flood inundation modelling , 2004 .

[4]  L. Mertes,et al.  Remote sensing of riverine landscapes , 2002 .

[5]  G. Nanson,et al.  A genetic classification of floodplains , 1992 .

[6]  I. Chaubey,et al.  FLOOD PULSE DYNAMICS OF AN UNREGULATED RIVER FLOODPLAIN IN THE SOUTHEASTERN U.S. COASTAL PLAIN , 2000 .

[7]  John Louis,et al.  Relating wetland inundation to river flow using Landsat TM data , 2003 .

[8]  Nick J. Mount,et al.  The effect of altered flow regime on the frequency and duration of bankfull discharge: Murrumbidgee River, Australia , 2005 .

[9]  I. Overton,et al.  Modelling floodplain inundation on a regulated river: integrating GIS, remote sensing and hydrological models , 2005 .

[10]  K. Page,et al.  Stratigraphic architecture resulting from Late Quaternary evolution of the Riverine Plain, south‐eastern Australia , 1996 .

[11]  A remote sensing approach to determine environmental flows for wetlands of the Lower Darling River, New South Wales, Australia , 2001 .

[12]  B. Biggs,et al.  Relationships between benthic biota and hydrological indices in New Zealand streams , 1997 .

[13]  K. Tockner,et al.  An extension of the flood pulse concept. , 2000 .

[14]  Richard T. Kingsford,et al.  Ecological impacts of dams, water diversions and river management on floodplain wetlands in Australia , 2000 .

[15]  P. Frazier,et al.  Floodplain Formation and Sediment Stratigraphy Resulting from Oblique Accretion on the Murrumbidgee River, Australia , 2003 .

[16]  L. B. Leopold,et al.  River flood plains: Some observations on their formation , 1957 .

[17]  K. Page,et al.  Chronology of Murrumbidgee River palaeochannels on the Riverine Plain, southeastern Australia , 1996 .

[18]  S. Bunn,et al.  Sources, sinks and transformations of organic carbon in Australian floodplain rivers , 1999 .

[19]  P. Frazier,et al.  Water body detection and delineation with Landsat TM data. , 2000 .

[20]  W. Junk The flood pulse concept in river-floodplain systems , 1989 .

[21]  Dlwc State of the rivers report: Murrumbidgee Catchment 1994-1995 volume 2 , 1996 .

[22]  S. Schumm River adjustment to altered hydrologic regimen - Murrumbidgee River and paleochannels, Australia , 1968 .