Aquaculture Africa 2021

March 25 - 28, 2022

Alexandria, Egypt

GENETIC DIVERSITY OF TWO SOUTHERN AFRICAN CICHLIDS Oreochromis andersonii AND O. macrochir IN THE ZAMBEZI AND CONGO RIVER BASINS

Ian Bbole*, Jin-Liang Zhao, Shou-Jie Tang, Cyprian Katongo

 

Department of Fisheries

P.O Box 910243

Mongu, Western Province

Zambia

 

ibbole@gmail.com

 



 Oreochromis andersonii  and  O. macrochir are two i mportant cichlid species native to Southern  Africa. We describe  their  genetic population structure in the Upper Zambezi River, Kafue River, and Lake Ban gweulu representing part of the Congo and Zambezi River Basins. Microsatellite g enetic markers were employed to analyse the genetic population structure of the two species using 177 tissue samples.

 The average allele richness of  O. andersonii was highe r in the Zambezi River (10.500) than in  the Kafue River (9.583) though not statistically different. For  O. macrochir ,  it was highest in the Zambezi River (11.170) followed by the Kafue River (9.781) and  least in Lake Bangweulu (7.067) and their differences were  significant. The gene diversity indices; gene diversity (hs), observed heterozygosity (HO ), expected heterozygosity (H E) were high and similar in  O. andersonii  populations. However, in  O. macrochir HE was significantly lower in Lake Bangweulu (0.6 78) compared to the Kafue River (0.799) and Zambezi River (0.802) populations. Popul ation differentiation estimated  by R ST and DEST revealed high differentiation in both species (R ST = 0.598, D EST  = 0.777  for  O. andersonii ; R ST = 0.379, D EST = 0.710 for  O. macrochir ). The highest source of variation was among populations  (84.71%) for  O. andersonii  and within populations  (67.09%) for  O. macrochir . Comparisons of population pairs revealed a close genetic  similarity between the Zambezi River and Lake Bangweulu populations of  O. macrochir . Bottlenecks were obs erved in both species using the Two-Phase Model (T.P.M.) indicative of a recent genetic loss or reduction in ef fective population size.

 Though our results indicate that the populations of both spec ies still maintain sufficiently high levels of genetic diversity in the sampled areas, the bottlenecks observed are a source of concern. We recommend a more robust stud y of genetic diversity of these species in all sec tions of these river systems and t hat some key conservation sites should be identified to protect the gene pool of these native species.