Table 1.

Summary of previous fringing vegetation mapping in the Peel-Harvey area at scales 1:50000 or larger.

 
Parameter/study
McComb et al., 1995
Siemon et al., 1993
Woodcock, 1992
Trudgen, 1991
Kinnaird et al., 1979
Time of data acquisition
1957- 1994 at 10 year intervals 3- 4 January 1992 not stated, probably around 1991  not stated, probably around 1990 unknown
Type of data
scanned B&W and colour aerial photography colour aerial photography, scale 1:20 000 not stated, probably aerial photographs colour aerial photography, scale 1:25 000 unknown
Method
visual photointerpretation, on- screen digitizing visual photointerpretation, overlays digitized not stated, probably visual interpretation visual photointerpretation
not stated
Format of the final map
digital digital polygons, hand drawn vegetation symbols black  and white analog colour analog analog, possibly computer methods were used in generating the map
Scale
1: 25000 approx. 1:15 000 1:2000  1:25000  not stated, approx. 1: 50000 ?
Smallest area mapped (resolution)
2m by 2m  not stated, but from the map approx. 15 by 15 m not stated, but from the map approx. 10 by 10m not stated, but from the map approx. 10 by 10m not stated, from the map approx. 30 by 30m
Purpose for mapping
historical changes in saltmarsh flats baseline information on the vegetation fringing Serpentine River amongst others: “to map vegetation showing the location of trees (approx. light and dominant species), density of cover, main understorey species, presence of rush beds and weed species list as much flora as possible, assess significance, document populations of rare and geographically restricted species  not stated the title of the map is: “Peel Inlet Management Authority Vegetation Plan”. 
Coverage (approx.% of current study area)
90%  5%  20% 15%  100%
Major vegetation associations/units
saltmarsh only saltmarsh, estuarine fringing forest, fringing vegetation, sandy rise vegetation, freshwater fringing vegetation and disturbance related plant assemblages. down to dominant species level, also uses Semeniuk (1990) geomorphological classification: Beach Ridge Complex, Elongate Fluvial Delta Complex, Erosional Sandy Shore, Spit- Lagoon Complex, Tidal Shoal  the strand, Q4 and Q3 Age Quindalup dunes, Peppermint Units, Tuart Units, Spearwood dunes, Limestone areas, Intergrades, Limestone to Spearwood dunes, Yoongarillup Plain - Seasonally Damp to Wetland Areas, Q2 and Q1 Age Quindalup Dunes  Tuart woodland, saline wetland complex, Marri- Jarrah woodland, floodgum woodland, closed scrub, Melaleuca preissiana open woodland, samphire herblands and sedge, swamp paperbark low woodland
Final accuracy, general comments
80%  not stated, final map should have had a scale smaller than the aerial photography used for the study not stated  not stated not stated
Detailed species list and/or description
only for transects within saltmarsh included included included not stated
Summary/ recommendations
decline of saltmarsh in quantity and quality severe erosion of river banks caused by livestock. Sparsity of understorey. Many plant communities are of regional importance. Severe weed invasion. The majority of native vegetation of the Serpentine River catchment has been lost variety, related to the management of weeds, fire etc. very detailed map down to dominant species. “No balance been struck between conservation and exploitation”. Vegetation of very high conservation value   not stated
   
   .