https://vital.seals.ac.za/vital/access/manager/Index ${session.getAttribute("locale")} 5 https://vital.seals.ac.za/vital/access/manager/Repository/vital:28685 Wed 12 May 2021 22:29:29 SAST ]]> https://vital.seals.ac.za/vital/access/manager/Repository/vital:878 Wed 12 May 2021 18:44:03 SAST ]]> https://vital.seals.ac.za/vital/access/manager/Repository/vital:21201 Wed 12 May 2021 17:57:45 SAST ]]> https://vital.seals.ac.za/vital/access/manager/Repository/vital:42472 Wed 12 May 2021 15:04:05 SAST ]]> https://vital.seals.ac.za/vital/access/manager/Repository/vital:41163 Wed 12 May 2021 13:49:36 SAST ]]> https://vital.seals.ac.za/vital/access/manager/Repository/vital:36442 Thu 13 May 2021 11:51:29 SAST ]]> https://vital.seals.ac.za/vital/access/manager/Repository/vital:3148 Thu 13 May 2021 05:05:28 SAST ]]> https://vital.seals.ac.za/vital/access/manager/Repository/vital:28754 Thu 13 May 2021 04:19:32 SAST ]]> https://vital.seals.ac.za/vital/access/manager/Repository/vital:37253 Thu 13 May 2021 04:18:53 SAST ]]> https://vital.seals.ac.za/vital/access/manager/Repository/vital:4760 0.20; F = 11.04; df = 2), with the highest mean number of plant species (32.5 ± 3.4). This was followed by the medium condition class (Kammiesbos) (26.5 ± 9.0) and poor condition class (Companjesdrift) (22.5 ± 8.9). On average, species composition was not evenly distributed across the peat basins (p> 0.21; F = 0.94; df = 2), since 77.8% of the Shannon-Weiner evenness index obtained were less than one. However, there were variations in plant species richness across six peat basins as confirmed by Oneway ANOVA test (p= 0.0008, F = 1241.6, df = 4). Key environmental variables that influenced plant species distribution and structure were erosion and grazing intensity, potassium, phosphorus, soil pH and calcium. Total species variance accounted for in the first two axes for ground cover and plant height were 40.7% and 56.4% respectively. Alien species (e.g. Acacia mearnsii and Conyza scabrida) were common in degraded peat basins, whereas good condition peat basins supported indigenous species (e.g., Cyperus denudatus, Chrysanthemoides monolifera and Digitaria eriantha). Analysis of aerial images revealed a general progressive decrease in the peatland area between 1942 and 1969 in the good (Krugersland) and poor (Companjesdrift) condition class, with a marginal increase from 1969 to 2003. Peatland area in the good and poor condition class decreased by 5.3% and 8.3% respectively between 1942 and 1969, with a marginal increase of 1.5% and 4.1% respectively from 1969 to 2003. Annual net rate of change in peatland area over the 61 year period was -0.32% (good condition class) and - 0.79% (poor condition class). Transformed lands were impacted by drivers of change such as alien invasives, agricultural activities, erosion and sediment transport. The area under alien invasives increased by 50% between 1942 and 2003, with an annual net rate of change of +0.82 (good condition class) and +1.63% (poor condition class).]]> Thu 13 May 2021 04:18:43 SAST ]]> https://vital.seals.ac.za/vital/access/manager/Repository/vital:2943 Thu 13 May 2021 02:14:28 SAST ]]> https://vital.seals.ac.za/vital/access/manager/Repository/vital:25035 Thu 13 May 2021 01:41:43 SAST ]]> https://vital.seals.ac.za/vital/access/manager/Repository/vital:36524 Thu 13 May 2021 01:41:06 SAST ]]>