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31 March 2014 Development and Characterization of Microsatellite Loci for the Moroccan Endemic Endangered Species Argania spinosa (Sapotaceae)
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Argania spinosa (L.) Skeels is endemic to Morocco and is known worldwide for its oil, which is extremely rich in unsaturated fatty acids and used in the food and cosmetic industries. Argan is the only Sapotaceae species in the region. Argan forest is found primarily in the southwestern part of Morocco and in the Souss-Massa-Drâa region (Msanda et al., 2005); a few populations have also been identified in southwestern Algeria (Kaabèche et al., 2010). Currently, argan is facing critical regeneration problems resulting from overgrazing of young sprouts and trees by goats, coupled with inadequate protection; consequently, argan tree genetic diversity is severely threatened. Molecular analyses of A. spinosa are very recent and still quite limited, mainly due to the lack of species-specific molecular tools. A few studies have tried to evaluate its genetic diversity, first with the analysis of isozymes (El Mousadik and Petit, 1996a) and chloroplast DNA (El Mousadik and Petit, 1996b) and later with interspecific random-amplified polymorphic DNA (RAPDs) and simple sequence repeats (SSRs) initially developed on two different Sapotaceae species (Majourhat et al., 2008). However, only six SSRs were polymorphic, and these exhibited low diversity according to what would be expected in a perennial spontaneous (i.e., natural, nondomesticated) tree. Species-specific codominant molecular markers are thus critically needed.

Here, we developed de novo, highly polymorphic and A. spinosa–specific SSR markers and used them to evaluate the genetic diversity of a collection of geographically diversified argan trees.


Argania spinosa genomic DNA (gDNA) was extracted from young dried leaves and ground using a MM400 mixer mill (Retsch, Düsseldorf, Germany) for 2 min at 30 Hz in 1.5-mL centrifugation tubes with two stainless steel beads (Retsch, no. Fr0120). Between 10 and 20 mg of powder was used for gDNA extraction using the NucleoSpin Plant II DNA extraction kit according to the manufacturer's instructions (Macherey-Nagel, Düren, Germany). DNA concentration was adjusted to 50 ng/µL.

Sixteen DNA samples originating from two populations geographically separated by more than 400 km were used for library construction (Appendix 1). The protocol of Glenn and Schable (2005) was slightly modified to prepare genomic libraries enriched for (GA)15, (GTA)8, and (TTC)8 repeats. Biotin-labeled oligonucleotides were used for library enrichment and Southern analysis, which were performed with the Biotin Luminescent Detection Kit (no. 11 811 592 910, Roche Diagnostics GmbH, Mannheim, Germany) and a Bio-Rad Fluor-S MAX MultiImager (Bio-Rad Laboratories, Hercules, California, USA). Positive colonies containing an insert larger than 400 bp were sequenced by Macrogen (Seoul, Korea) on an ABI 3730xl genetic analyzer (Applied Biosystems, Foster City, California, USA) with BigDye Terminator version 3.1 chemistry (Applied Biosystems). SSR motifs were confirmed in 31 nonredundant sequences. Alternatively, to increase the number of SSR loci, gDNA enrichment and direct sequencing using 454 GS FLX Titanium (Roche, Basel, Switzerland) were conducted as described earlier (Micheneau et al., 2011).

Table 1.

Characterization of 11 Argania spinosa SSR loci, with 150 argan individuals.


A total of 79 primer pairs (31 enriched sequences and 48 sequences developed through next-generation sequencing) were designed with Primer3 (Rozen and Skaletsky, 2000) with the following design parameters: GC content 40–60 (optimum 50), melting temperature (Tm) 55–65°C (optimum 60°C), primer size 18–27 bp (optimum 22 bp), GC clamp 1. A typical pigtail (GTTTCTT-) was added to the 5′ end of the forward or reverse primers. Primers were synthesized at Integrated DNA Technologies (Leuven, Belgium). They were first tested at 55°C on control gDNA. Markers giving no or multiple amplification products were discarded. For the remaining markers, each locus was analyzed on a set of geographically distant argan trees. For this step, amplification was performed using labeled dUTP nucleotides. A 50-µL reaction mixture contained 10 µL of 5× colorless GoTaq reaction buffer (Promega Corporation, Madison, Wisconsin, USA), 10 pmol of each primer, 5 µmol dATP, 5 µmol dCTP, 5 µmol dGTP, 4 µmol dTTP, 0.4 µmol dUTP-DY681 (Dyomics, Jena, Germany), 1.5 unit GoTaq polymerase (Promega Corporation), and 250 ng of gDNA, and was brought to volume with nuclease-free water (Promega Corporation). The amplification program was 94°C for 2 min; followed by 35 cycles at 94°C for 30 s, 55°C for 30 s, and 72°C for 30 s; followed by a final elongation step at 72°C for 7 min and then hold at 10°C. Amplification products were analyzed on a CEQ 8000 fragment analyzer (Beckman Coulter, Brea, California, USA), using MapMarker MM-D1 as size standard (BioVentures, Murfreesboro, Tennessee, USA) and Frag-4 separation method with a separation time of 100 min. Amplifications were performed on iCycler (Bio-Rad Laboratories). Out of the first 79 primer pairs tested, 11 fulfilled selection criteria regarding polymorphism, lack of background amplification, and ease of scoring. A table summarizing the evaluation results of all 79 primer pairs is available as  Appendix S1 (APPS-D-13-00071_AppendixS1.xlsx).

Validated SSR markers were resynthesized by Eurofins MWG Operon (Ebersberg, Germany) and labeled with 6-FAM, Atto 565, or HEX fluorescent dyes. Amplifications were performed in 10-µL volumes using 0.3 unit of GoTaq DNA polymerase (no. M300, Promega Corporation), 2 µL of 5× GoTaq PCR buffer (no. M7921, Promega Corporation), 10×50 ng of gDNA, 0.1 µL of 10 mmol/L dNTP mix (no. R0192, Thermo Fisher Scientific, Waltham, Massachusetts, USA), and 2 pmol of each primer. ASMS markers (Table 1) were amplified individually and further pooled for separation and detection on an ABI 3130xl genetic analyzer (Applied Biosystems), while ASMS2012 markers were multiplexed for amplification in two triplex reactions. All amplifications were performed according to the melting temperatures reported in Table 1.

One hundred fifty argan trees originating from seven populations located in southern Moroccan argan forests and one population from the Oued Grou relict area, in northwestern Morocco, were used for in-depth testing of the newly developed SSRs (Appendix 1). Allele number (A), allelic richness (Ar), and expected (He) and observed (Ho) heterozygosities were calculated using FSTAT software version (Goudet, 1995). Results revealed high allele numbers (Table 1). A total of 136 alleles were scored. A ranged from six (ASMS2012-10) to 18 (ASMS01). Ar varied from 3.992 to 9.085. He and Ho ranged from 0.618 to 0.869 and 0.532 to 0.887, respectively. No significant difference was observed between Ho and He for nine loci, indicating that populations are approaching Hardy-Weinberg equilibrium. A difference has been noticed for loci ASMS19 and ASMS31, where He was higher than Ho, indicating a slight lack of heterozygotes. This might be due to natural selection of loci near the two SSRs or to the presence of null alleles.

Argan tree is considered as a spontaneous natural species with no genetic change due to human selection. The observed levels of genetic diversity are thus explained by the combined effects of mutation, genetic drift, gene flow, and natural selection.


In our study, 150 argan trees were genotyped with 11 SSR markers. Samples originated from eight geographically separated regions with no possibility of natural gene exchange. The 11 microsatellite markers used in this study were very informative and showed a high ability to detect polymorphism within analyzed genotypes. Outcomes of this research provide the first codominant markers specific to A. spinosa and will help in elaborating strategies to better protect this threatened species. They will contribute more efficiently to evaluate the genetic diversity and to understand gene flow among and between argan forest areas. Moreover, developed markers may constitute valuable tools for evaluation of genetic diversity in other Sapotaceae species.



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Appendix 1.

Location information for Moroccan populations of Argania spinosa used in this study.a



[1] The authors thank Wallonie-Bruxelles International (Brussels, Belgium) for financial support; M. Badraoui (director, Institut National de la Recherche Agronomique [INRA] Maroc), Dr. L. Panella (U.S. Department of Agriculture–Agricultural Research Service, Northern Plains Area [USDA-ARS, NPA]), and Dr. J. F. Arnaud (Lille 1 University, Villeneuve d'Ascq, Lille, France) for help and support; M. Benziane, director of the Centre de Recherche Forestière de Rabat (CRF), for his contribution in making contacts for collecting missions; and A. Dekeyser (Centre Wallon de Recherches Agronomiques [CRA-W], Belgium) for his contribution to the initiation of this research.

Yasmina El Bahloul, Nicolas Dauchot, Ikrame Machtoun, Fatima Gaboun, and Pierre Van Cutsem "Development and Characterization of Microsatellite Loci for the Moroccan Endemic Endangered Species Argania spinosa (Sapotaceae)," Applications in Plant Sciences 2(4), (31 March 2014).
Received: 30 August 2013; Accepted: 1 December 2013; Published: 31 March 2014

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