| Abstract | [Summary]: This study is the continuation of previous research that examined the effects of vegetation management on woodland communities in the Traprock region and will contribute to an understanding of the ‘biodiversity potential’ of managed land units on properties (including open paddocks, scattered treed areas, and remnant woodland) identified previously. In order to determine ‘biodiversity potential’, a number of grazing exclosures were established on selected properties with the aim to monitor biodiversity changes over-time following the removal of grazing.
Eighteen study sites across 10 properties in the Traprock region were selected for this study. The design consisted of: 2 vegetation types (grassy box (Eucalyptus melliodora, E. microcarpa, or E. moluccana) woodland (L) and ironbark (E. crebra) /gum (E. dealbata) (U) woodland); 3 mature (overstorey) tree densities (<6 trees/ha [low](L); 6-20 trees/ha [medium](M); >20 trees/ha [high](H), and; 3 exclosures (full exclosure (1) [2.5m complete fence], partial exclosure (2) [1.5m three-wire fence], open (3) [corner makers]). Exclosure plots were erected in January/February 2005 and sampled in April 2005 (two months after exclosure establishment), February 2006 (12 months after exclosure establishment), February 2007 (2 years after exclosure establishment), and February 2007 (3 years after exclosure establishment). Within each 6 x 6 m exclosure plot, a central 2 x 2 m quadrat was sampled for plant species cover. Above-ground vegetation (‘biomass’) was clipped in a separate 0.25m2 sample and dry weight determined. Overstorey cover and recruitment were determined within each 6 x 6 m exclosure plot. Stand structural characteristics, including foliage projective cover of distinct strata, and cover of litter, logs and rocks, and general habitat condition were also determined at each site.
Preliminary patterns in floristic composition were determined using non-metric Multidimensional Scaling (nMDS). Two-way crossed Analysis of Similarity (ANOSIM) determined whether there were significant differences in floristic composition between exclosure types and mature tree density classes. nMDS was also used to assess patterns in cover data for growth forms. Two-way crossed Analysis of Variance (ANOVA) was used to determine if groups (density class, exclosure type and the interaction of density and exclosure) differed significantly for total, native, exotic, growth-form, perennial, and annual species richness and above-ground biomass. In addition, Spearman-rank correlations were performed to determine if biomass and estimates of ground cover were related.
A total of 151 plant species was recorded across all treatments with an average richness across treatments of 17 species per 4m2. No differences were apparent in overall plant composition (cover) between the exclosure treatments one year following grazing exclusion (ANOSIM, pr > 0.05). nMDS ordinations show no distinction between exclosure treatments, but patterns were observed in mature tree density treatments within vegetation types as found in previous research. Stand structure (cover of strata) showed much the same pattern as floristic composition.
There were generally no detectable differences (p > 0.05) in plant above-ground biomass between exclosures, although significant differences between tree density classes was indicated with a significantly higher plant biomass in low density treatments compared to high density for both vegetation types. Correlation results showed that estimates of grass cover provide a good indication of above-ground biomass (p<0.05). There were some differences between density classes for growth-form species richness, exotic species richness and annual species richness, however exclosure treatments did not differ. Overall, there were no differences in total or native species richness between groups.
While the distinction between vegetation type and mature tree density is observed in species composition, plant biomass and species richness, the exclusion of grazing (native and exotic) has not significantly altered composition after 3 years. The patterns in floristic composition are associated with different mature tree densities and vegetation type, which are consistent with earlier findings. There is some evidence to suggest that plant above-ground biomass has responded to the removal of grazing in open paddock areas, although this is not consistent across mature tree density treatments. It is suggested that a longer period of exclusion will be necessary to detect changes (if any) in plant species composition. |
|---|