Increasing extraction and regulation
of river water as well as pollution threaten this
species. Habitat: Occurs in rocky
rapids and cascades in altitudes of 900-1,200 m. Prefers
deeper waters (30-60 cm) over cobbles. Reproduction:
Oviparous. Distinct pairing during breeding. Hides
eggs in gravel. Breeds during summer and is a partial
spawner. Aquarium Care: Good oxygenated
water from a power filter. Sand or gravel substrate
with smooth rocks or pebbles. Their dorsal and pectoral
fins are sharp and can cause wounds if not handled
carefully. Sexual Differences: Usually
in the form of a different shaped caudal fin. Diet:
Feeds on benthic invertebrates such as mayfly and
caddis fly nymphs, blackfly and midge larvae and small
snails. In the aquarium feed algae foods, fly larvae
foods, bloodworm, and flake food. Etymology:
The specific name bifurcus: Latin for two-pronged,
referring to shape of caudal fin, “forked with
large lobes”. Remarks:
The distribution range of Chiloglanis bifurcus
is entirely within privately owned land without any
formal conservation protection. The two remaining
subpopulations need to be given priority for conservation
efforts as this species is critically endangered (IUCN
2017).
Common
Name:
Incomati suckermouth
Synonyms:
None
Family:
Mochokidae
Distribution:
Africa:
Crocodile-Incomati basin. Type locality:
Crocodile River, Incomati River system, Montrose Farm,
Nelspruit District, Southern Africa.
Size:
7.0cm. (2¾ins)
Temp:
23-26°C (73-79°F)
p.H.
6.5-7.2.
IUCN
Red List
Incomati
Suckermouth (Chiloglanis bifurcus) is endemic
to the Upper Crocodile River and Elands River of the
Inkomati River System, South Africa (Jubb & Le Roux
1969; Gaigher 1969; Kleynhans 1982, 1984, 1986; Skelton
1987; Kleynhans et al. 1992) and in the Upper Mlumati
River in Swaziland (Monadjem et al. 2003, Bills et al.
2004). The population has declined since 1984 with the
construction of the Kwena Dam (formerly Braam Raubenheimer
Dam) in the Crocodile River for irrigation purposes.
Flow regulation is particularly relevant in this regard
and is thought to be the main driver of the elimination
of the subpopulation in the Crocodile River below this
dam. The chemical spill from the SAPPI Paper Mill at
Ngodwana (23 September 1989) into the Elands River,
further accelerated the decline of this species. More
recently, deteriorating water quality from Machadodorp
has impacted on this species. These declines have been
exacerbated by the introduction of invasive alien fish
species (Roux and Selepe 2013). These declines have
been observed, through continuous biomonitoring of the
species and the determination of the Ecostatus of the
Inkomati Catchment by nature conservation officials
(MTPA – Mpumalanga Tourism and Parks Agency).
Based on the trends of the catch per unit effort (CPUE)
and relative abundance of this species a 90% population
reduction has been observed over the past 10 years (estimated
generation length of 3-5 years) (Kleynhans 1984, 1989;
Roux & Selepe 2013; Roux et al. 2016). There has
also been a decline in the area of occupancy (AOO),
extent of occurrence (EOO) and a loss of habitat quality.
It therefore qualifies as Critically
Endangered under criteria A2ace (IUCN
2017).
Reference:
Ferraris, C.J. Jr.,
2007. Checklist of catfishes, recent and fossil (Osteichthyes:
Siluriformes), and catalogue of siluriform primary
types. Zootaxa 1418:1-628. Froese, R. and D. Pauly. Editors.
2017. FishBase. World Wide Web electronic publication.
www.fishbase.org, ( 10/2017 ). Roux, F. & Hoffman, A. 2017.
Chiloglanis bifurcus. The IUCN Red List of
Threatened Species 2017. Skelton, P.H., 1993. A complete guide
to the freshwater fishes of southern Africa. Southern
Book Publishers. 388 p. www.iNaturalist
2018.
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