Small
impoundments represent one of the most widespread anthropogenic changes to the
riverscapes in the Cape Fold Ecoregion (CFE) at the southern tip of Africa - a
region which originally lacked natural standing water bodies. These
impoundments were primarily built for agricultural and livestock farming and have
proliferated with increasing demand for water. Consequently, there are few
free-flowing streams in the CFE. Construction of small impoundments has been
widely documented to have serious ecological and biodiversity impacts,
including changes in hydrologic regimes and fragmentation of historically
connected populations of stream-inhabiting fishes, with adverse effects on
their genetic characteristics. Small impoundments have also created favourable
habitats that have facilitated the proliferation and spread of non-native
species.
While these
negative impacts cannot be denied, observations and preliminary results from a
recent comprehensive survey of the Great Fish River system by researchers and
students from the South African Institute for Aquatic Biodiversity and Rhodes University
are showing that small impoundments can also benefit biodiversity. This survey was
conducted in January 2017 as part of Delsy Sifundza’s MSc research (funded by the
NRF-FBIP Karoo BioGaps Project) to map the distribution and determine the
status of remnant populations of the Eastern Cape Rocky, Sandelia bainsii (Figure 1). The Eastern Cape Rocky is a highly
threatened endemic stream fish which has been listed by the IUCN as Endangered
since 1987 due to rapid decline in population sizes and severe decline in its
historical distribution range.
A picture of the
Eastern Cape Rocky, Sandelia bainsii,
showing the species’ live colour pattern.
Our survey
indicated that the Kat River is the remaining stronghold of the Eastern Cape
Rocky in the Great Fish River system. The survival of this species in the upper
section of the Kat River has been facilitated by the presence of several
impoundments of various sizes (Figure 2) which have prevented the spread of
non-native fishes, such as the sharptooth catfish, small-mouth yellowfish and
banded tilapia which are now dominant in the mainstem Great Fish River. Sandelia bainsii was abundant at sites above
the weirs that formed the upper limit of non-native fishes in the Kat River. In
these river sections, S. bainsii
occurred with three other native fishes of the Great Fish River system: Labeo umbratus (moggel), Enteromius anoplus (chubby head barb)
and Glossogobius callidus (river
goby). Some of these impoundments are therefore likely to have formed effective
barriers that could have protected the genetic integrity of the original L. umbratus genetic lineage in the Great
Fish River which is threatened by potential hybridisation with a genetically
distinct lineage of this species that was introduced into the Great Fish
through the Orange-Fish tunnel Inter-Basin Transfer. The Kat River therefore
represents an important sanctuary of highly threatened endemic fishes of the
eastern CFE and should be prioritised for protection. There is critical need
for building awareness among the communities to prevent the spread non-native
fishes in the Kat River catchment. There is also need for establishing
collaboration between researchers, conservation authorities and the local
farming communities and land owners to identify the weirs that are preventing
the upstream migration of non-native fishes to ensure that they are effectively
secured and protected from potential breach or flood damage.
Research
Team
Miss Delsy Sifundza (MSc candidate,
Department of Ichthyology and Fisheries Science, Rhodes University)
Mr Tadiwa Mutizwa (MSc candidate,
Department of Ichthyology and Fisheries Science, Rhodes University)
Dr Albert Chakona (South African
Institute for Aquatic Biodiversity)
Dr Wilbert Kadye (Department of
Ichthyology and Fisheries Science, Rhodes University)
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