Cross-amplification and Characterization of Polymorphic Microsatellite Markers From Acacia (Senegalia) mellifera and Acacia brevispica to Acacia senegal (L.) Willd.
Abstract:The NERC and CEH trade marks and logos ('the Trademarks') are registered trademarks of NERC in the UK and other countries, and may not be used without the prior written consent of the Trademark owner.Cross-amplification and characterization of polymorphic microsatellite markers from Acacia (Senegalia) mellifera and Acacia brevispica to Acacia senegal (L.) Willd. to 0.800 (Ame03). Cross amplification of these loci represents a potential source of codominant marker and will be useful in the study of genetic dive… Show more
“…DNA quantification was performed through Bio-photometer readings and comparison with low DNA mass ladder (Invitrogen) in 1 % agarose gel. Polymerase chain reaction (PCR) amplifications of 12 polymorphic microsatellite loci (Assoumane et al 2009;Omondi et al 2010a) for all the individuals and populations were performed following the procedure described by Hanaoka et al (2012). Capillary fragment electrophoresis of PCR products were scored against an internal standard (600 Liz size standards) on an ABI 3500 genetic analyser, and genotype data scored using GeneMapper 5.0 software (Applied Biosystems, CA, USA).…”
Acacia senegal is endemic to dry forest and woodland ecosystems of Sub-Saharan Africa and provides both ecological and socio-economic benefits. However, these ecosystems are threatened by escalating human disturbances and fragmentation. To investigate the human impacts on genetic diversity and structure of A. senegal, we studied genetic variability and differentiation of 330 individual trees from 11 natural A. senegal populations, grouped into lightly and heavily disturbed, using 12 polymorphic nuclear microsatellite markers. Gene diversity (H E ) ranged from H E = 0.570 to H E = 0.632. Significant differences (P \ 0.05) between the levels of disturbances are reported for mean gene diversity, number of alleles and allelic richness with lightly disturbed populations showing higher values. Overall, the indirect estimates of average outcrossing rates ranged from 0.794 (Kiserian) to 0.999 (Kampi ya Moto) with a mean of 0.997 suggesting a predominantly outcrossing species. There was no significant relationship (P [ 0.05) detected between genetic and geographic distances, showing lack of isolation by distance. Analysis of population structure using unweighted pair group method with arithmetic mean and Bayesian model suggests presence of three gene pools as most probable, although most individuals showed mixed ancestry. The diversity and genetic structure reported in this study revealed negative impacts of human disturbance on A. senegal within this ecosystem. We recommend in-situ conservation strategies to safeguard the woodland ecosystem from further deforestation.
“…DNA quantification was performed through Bio-photometer readings and comparison with low DNA mass ladder (Invitrogen) in 1 % agarose gel. Polymerase chain reaction (PCR) amplifications of 12 polymorphic microsatellite loci (Assoumane et al 2009;Omondi et al 2010a) for all the individuals and populations were performed following the procedure described by Hanaoka et al (2012). Capillary fragment electrophoresis of PCR products were scored against an internal standard (600 Liz size standards) on an ABI 3500 genetic analyser, and genotype data scored using GeneMapper 5.0 software (Applied Biosystems, CA, USA).…”
Acacia senegal is endemic to dry forest and woodland ecosystems of Sub-Saharan Africa and provides both ecological and socio-economic benefits. However, these ecosystems are threatened by escalating human disturbances and fragmentation. To investigate the human impacts on genetic diversity and structure of A. senegal, we studied genetic variability and differentiation of 330 individual trees from 11 natural A. senegal populations, grouped into lightly and heavily disturbed, using 12 polymorphic nuclear microsatellite markers. Gene diversity (H E ) ranged from H E = 0.570 to H E = 0.632. Significant differences (P \ 0.05) between the levels of disturbances are reported for mean gene diversity, number of alleles and allelic richness with lightly disturbed populations showing higher values. Overall, the indirect estimates of average outcrossing rates ranged from 0.794 (Kiserian) to 0.999 (Kampi ya Moto) with a mean of 0.997 suggesting a predominantly outcrossing species. There was no significant relationship (P [ 0.05) detected between genetic and geographic distances, showing lack of isolation by distance. Analysis of population structure using unweighted pair group method with arithmetic mean and Bayesian model suggests presence of three gene pools as most probable, although most individuals showed mixed ancestry. The diversity and genetic structure reported in this study revealed negative impacts of human disturbance on A. senegal within this ecosystem. We recommend in-situ conservation strategies to safeguard the woodland ecosystem from further deforestation.
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