S.C. Boucher School of Geography and Environmental Science Monash University, Victoria 3800 The Parwan Creek valley is located near Glenmore in the north-west of the region and contains some of the most severe sites of water erosion in Victoria. The Parwan Hydrological Experimental Area was established in 1953 by the Soil Conservation Authority and forms part of the White Elephant Reserve (Hartland and Papworth 1995). Extensive, deep tunnel erosion was recognized by Hexter et al. (1956) as the main problem on the White Elephant Hill. | ![]() Gully erosion in Parwan Valley. |
![]() Prediction of dispersive potential for soils affected by tunnel erosion in the Parwan Experimental Area (after Fitzpatrick et al. 1994). |
The average annual precipitation of 508 mm was shown to be highly variable over 28 years of records and average monthly rainfall was highest in April-May and August-November (Wu et al. 1986). Hexter et al. (1956) noted that prior to European settlement, the area was covered by Eucalyptus spp. trees and thick stands of native grasses. Clearing took place to improve the growth of the grasses that were overgrazed by cattle, rabbits and sheep. Landslides were known to have increased in number after the inherently delicate environmental balance was upset by the above-mentioned activities. Tunnelling appears to have started by direct contact of surface water with the subsoil following extensive sheet erosion and/or along rotted tree stump roots. All tunnels debouched onto the hillslopes rather than the tributary gully wall, thus being of the "continuous gradient" form, and the greatest sinkhole depth reported in Victoria (i.e. 7.6 m) was recorded at this site (Boucher 1990) |
![]() The relation between ESP and Exchangeable Mg/Ca for soils affected by tunnel erosion in the Parwan Experimental Area (after Fitzpatrick et al. 1994). | The level of sodicity varied considerably between profiles with the range of ESP for surface and subsurface soils being 1.0 - 7.1 and 1.4 - 8.9 respectively (Ford et al. 1993). The Exchangeable Mg/Ca values were 0.7 - 4.4 in the surface soils and 2.4 - 18.0 in the subsurface horizons (Ford et al. 1993). The ratios ranged between 0.7 - 4.4 for surface soils and 2.4 - 18.0 for subsurface material (Ford et al. 1993). An important technique in land management has been rabbit control, as the animals inhabit tunnels (Hartland and Papworth 1995, Anon. 1997). |