183 Sixth, while satellite image evidence indicated to Mr Palmer that closed shrublands and understorey shrubs were cleared along parts of the pasture forest interface on the property between April and September 2006, analysis of forest cover changes within these alleged cleared areas from historical aerial photographs showed that, with the exception of small patches of possible blackberry infestation, closed shrubland and understorey shrub cover did not develop in these areas until after January 1990, and that emergent trees and tall shrubs present before 1990 appeared to have either been retained or had succumbed to dieback and death following disposal of saline mine water.
184 Seventh, evidence from interpretation of historical aerial photographs indicated that total vegetation cover on the property had increased between 1993 and 2003 by growth of shrubland and regrowth along most of the pasture forest interface and within the understorey of the existing forest and woodland. This change coincided with use of the property for disposal of saline waste water. In his opinion the saline mine water irrigation appeared to have promoted the growth of dense stands of salt tolerant trees and shrubs such as Black She-Oak (Allocasuarina littoralis) and Red Gum (Eucalyptus tereticornis) in dieback affected areas.
185 Eighth, from the analysis of the aerial photographs it could be concluded that all of the tree and shrub understorey in the alleged cleared areas identified by Mr Palmer and Ms Ridge had grown after 1990, with the exception of a small patch of likely blackberry infestation along the riparian zone.
186 Ninth, aerial photographs and interview evidence from clearing contractors indicated that clearing of weeds and native vegetation was undertaken within 20 m of a stream and within a protected riparian zone contrary to instructions to avoid such areas. The occurrence of regenerating blackberry within this area indicated that the clearing may have been exempt under the Noxious Weeds Act 1993. A portion of this area provided a farm access track and was exempt from clearing as "routine agricultural management activities".
187 Tenth, no clear evidence was provided that any of the large overstorey trees that were cleared were living at the time of felling. Interview and ground survey evidence suggested that the only large trees felled were dead trees. Soil Services reports indicated that saline mine water disposal on the property between 1993 and 2003 had killed large numbers of trees. The results of plot surveys and site inspections also showed an abnormally high level of dead trees in the forest canopy in uncleared areas adjoining parts of the pasture forest interface.
188 Eleventh, in relation to the evidence of the size distribution of trees in the cleared and uncleared survey plots, while it was likely that this data was not representative of tree size distribution within the cleared areas due to sampling errors, the estimated mean size of trees predicted to have been removed using the modelling developed earlier by Dr Smith was broadly consistent with the expected mean for stands of trees regenerating after 1990 and thus consistent with "regrowth".
189 Finally, aerial photograph interpretation and ground surveys reveal that forest and shrub cover on the property had been modified in the past by a combination of clearing for agriculture, selective timber harvesting, poisoning, slashing, weed invasion, grazing and fire, and therefore, that, in his opinion, the regrowth clearing exemption should be applicable.