Abstract

Background: Akkerendam Nature Reserve is the second oldest proclaimed municipal nature reserve in the Northern Cape, yet to date no vegetation map has been produced. The possible expansion of the reserve is under consideration.Objectives: To produce a vegetation map, classification and description of the vegetation of the reserve and proposed expansion area, and assess how the vegetation has changed over the past century.Method: Braun Blanquet methodology was used to produce a vegetation map. To quantify vegetation change, (1) relevés (a plot of phytosociological data) composed from Acocks’ species lists, recorded in 1954 and 1956, were compared with the phytosociological table, and (2) recent repeat photographs (2016) were compared to four images taken by Pole Evans (ca. 1920).Results: Three plant communities were identified within the reserve and expansion area; however, four subcommunities are only found in the proposed expansion area. Relevés compiled from Acocks’ species lists were absorbed into the phytosociological table indicating that no significant vegetation change has taken place in the last approximately 60 years. This study found 222 species in common with Acocks’ species lists; however, he did not list the alien invasive species Prosopis glandulosa. Comparison of repeat photographs with images taken nearly a century earlier suggests that, except for the impact of recent fires, the composition remained relatively similar.Conclusion: The phytosociological approach adopted has provided a map of the vegetation units of the study area, while the historical comparisons indicate that the vegetation of Akkerendam Nature Reserve has not undergone significant change over the last 100 years.

Highlights

  • 1.4 Tenaxia stricta – Dicerothamnus rhinocerotis Mountain Renosterveld Subcommunity 1.4 is found at high altitudes on the top of the Hantam Mountain on Land type Ib, in the proposed expansion area

  • 1.7 Felicia filifolia – Dicerothamnus rhinocerotis Mountain Renosterveld Subcommunity 1.7 is found on the slopes of the Hantam Mountain only in the proposed expansion area at altitudes of about 1500 m to 1600 m a.s.l

  • 2.1 Ursinia pilifera – Pteronia glauca – Eriocephalus ericoides Hantam Karoo Subcommunity 2.1 is situated on the middle to lower slopes of the Hantam Mountain within the AKNR and proposed area of expansion at an altitude of approximately 1100 m a.s.l

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Summary

Introduction

1.3 Passerina truncata – Dicerothamnus rhinocerotis Mountain Renosterveld Dark brown, dolerite-derived, soils underlie Subcommunity 1.3, which is found on Land type Ib at a high altitude of between 1561 m and 1640 m a.s.l. Subcommunity 1.3 is situated on the top of the Hantam Mountain, only in a few isolated patches within AKNR, but mainly within the proposed expansion area. 1.4 Tenaxia stricta – Dicerothamnus rhinocerotis Mountain Renosterveld Subcommunity 1.4 is found at high altitudes (approximately 1600 m a.s.l.) on the top of the Hantam Mountain on Land type Ib, in the proposed expansion area.

Results
Conclusion
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