Astragalus lehmannianus Bunge (Fabaceae) is a vulnerable perennial herb in China that is distributed only on stationary and semi‐stationary dunes on the southern margin of the Gurbantunggut Desert in Xinjiang Uygur Autonomous Region (XJ), northwestern China (Fu, ; Shen, ). This species is threatened by anthropological disturbances and has been listed in the first group of key protected plants in XJ (Li, ). An extensive field survey covering the distribution area of A. lehmannianus in China was made from 2013 to 2017, and only six populations were confirmed to be extant. Furthermore, the locations of A. lehmannianus populations are fragmented and isolated from each other. Although the biochemistry and seed predation of this species have been reported (Mestechkina et al., ; Han et al., ), genetic information remains unknown.
Fragmented endangered species with restricted geographic distribution tend to have low levels of genetic diversity within populations, and restricted gene flow and increased genetic differentiation among populations (Wall et al., ). If endangered and vulnerable species are unprotected, their lower genetic diversity can significantly decrease the chances of survival in changing environments (Frankham, ). Effective protection of rare and endangered species often takes advantage of the genetic diversity information of the species (Selyutina et al., ).
Microsatellite markers developed in A. holmgreniorum Barneby (King et al., ), A. camptodontus Franch. (Zhang et al., ), A. mongholicus Bunge (Wang et al., ), A. michauxii (Kuntze) F. J. Herm. (Wall et al., ), and A. bibullatus Barneby & E. L. Bridges (Morris et al., ) were not found to be polymorphic for A. lehmannianus in preliminary tests. Therefore, we developed 12 variable microsatellite markers using the restriction site–associated DNA sequencing (RAD‐Seq) approach from the genome of A. lehmannianus and also tested the transferability of these markers to the congeneric species A. arpilobus Kar. & Kir. and A. oxyglottis Steven ex M. Bieb. These markers will provide useful tools for population genetics and demographic history of current populations of A. lehmannianus and related species. Furthermore, the study of genetic diversity using these markers will contribute to the formulation of conservation strategies for A. lehmannianus.
METHODS AND RESULTS
Total genomic DNA was extracted from dried leaves of A. lehmannianus plants collected from three natural populations in XJ (Jimsar County [G], Fukang City [C], Jimsar County [J]; Appendix 1) on the southern margin of the Gurbantunggut Desert, following the cetyltrimethylammonium bromide (CTAB) method of Doyle and Doyle () with the centrifugal time extended for 3–5 min.
The RAD‐Seq libraries were created by Huashibaiao Biotech Company (Beijing, China) to generate the simple sequence repeat (SSR) information. Our selections were di‐, tri‐, and tetranucleotide motifs with flanking regions larger than 100 bp and a minimum of 10, six, and four repeats, respectively. A total of 165 primer pairs, which were designed using Primer Premier 5.0 (PREMIER Biosoft International, Palo Alto, California, USA) and synthesized by Sangon Biotech (Shanghai, China), were obtained and tested for amplification. We attached the universal M13 sequence (TGTAAAACGACGGCCAGT) tag to the 5′ end of the forward primer using the method described by Schuelke () to label the products with fluorescence. Designed primers were tested on 65 samples of A. lehmannianus. To examine cross‐species amplification, 10 individuals each of A. arpilobus and A. oxyglottis were collected from the Gurbantunggut Desert in the same general locality from which samples of A. lehmannianus were collected. PCR was performed in a total volume of 25 μL containing 1 μL of template DNA with an initial concentration of 100 ng/μL, 7.9 μL of ddH2O, 12.5 μL of 2× Power Taq PCR MasterMix (TIANGEN, Beijing, China), 0.4 μL of TP‐M13 forward primer, and 1.6 μL of each reverse primer and universal M13 sequencing primer labeled with either HEX or 6‐FAM. All candidate primer pairs were tested by a touchdown PCR protocol in the following procedure: 94°C for 4 min; 10 cycles of 94°C for 40 s, 65–55°C (Δ1°C touchdown per cycle) for 50 s, 72°C for 40 s; 30 cycles of 94°C for 40 s, 55°C for 45 s, 72°C for 1 min; and a final extension at 72°C for 6 min. The amplified products were tested on 1.5% agarose gel and 6% polyacrylamide gel. The size of the amplified fragments was measured with an ABI 3730xL Genetic Analyzer (Applied Biosystems, Waltham, Massachusetts, USA), and allele sizes were scored using the software GeneMarker version 1.51 (Applied Biosystems).
Twelve polymorphic microsatellite markers were developed and used on 65 individuals of A. lehmannianus from different populations (Table ). An additional 13 monomorphic microsatellite markers were developed but not used (Appendix 2). Population genetic parameters, including number of alleles, levels of observed and expected heterozygosity, the inbreeding coefficient, and departure from Hardy–Weinberg equilibrium, were calculated using GenAlEx version 6.5 software (Peakall and Smouse, ). Linkage disequilibrium was analyzed with GENEPOP version 4.6.9 (Rousset, ).
Characteristics of the 12 polymorphic microsatellite loci developed in Astragalus lehmannianusLocusa | Primer sequences (5′–3′) | Repeat motif | Allele size range (bp) | Fluorescent dye | GenBank accession no. |
AL23 | F: AGTGCCTGAACAGTTACAAACCAAGA | (TC)20 | 146–162 | 6‐FAM |
|
R: GGAAGAAAATGCAGCCATCA | |||||
AL26 | F: CTATAATAGCGGTGATGAAGGGAAC | (GA)25 | 132–158 | 6‐FAM |
|
R: GTACCCGCGAGAAATCTTGTT | |||||
AL35 | F: GGTTTTAAACGTGAATTTAGTTGCC | (TA)12 | 143–159 | 6‐FAM |
|
R: GTCTTTCTTTTAAAGATGTTTTC | |||||
AL41 | F: CCATAGAGATTTTAGGTTCAG | (TA)20 | 128–156 | HEX |
|
R: CAGTATGTTTTGGTGTATT | |||||
AL42 | F: AACAAGCAATCTATGTGCCCC | (AAT)10 | 139–154 | 6‐FAM |
|
R: TCGAACCTAACTCAGACTGCA | |||||
AL43 | F: CAAGCAACTGTATTGGTGCA | (TA)13 | 144–154 | HEX |
|
R: CCTTCCACTACACATTTCAC | |||||
AL50 | F: CCCATTACAAGATATATTGCC | (AT)16 | 148–164 | 6‐FAM |
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R: GCAAGAATCCTGCCGATTTT | |||||
AL52 | F: TTCAGGAGCACTGCAAAGGTT | (TA)17 | 137–167 | 6‐FAM |
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R: GAGTTAGCATCTAAGAAAACA | |||||
AL53 | F: AATTCCTTTCAGATGGGAGC | (AG)12 | 130–150 | 6‐FAM |
|
R: TTGCTTAAAGCTTGCTGCCT | |||||
AL54 | F: TCAGAGGGTCTAATTGGCTTC | (TA)17 | 130–150 | HEX |
|
R: AGTTAGGCGTTAGCCTTACGT | |||||
AL59 | F: AAAAGGATTGACCAATTCAGC | (CA)15 | 122–156 | 6‐FAM |
|
R: GGAAAGAAGGCAATTATGCTC | |||||
AL65 | F: AAGCGACATTTTGTCCTGTC | (TA)18 | 140–148 | 6‐FAM |
|
R: CGTAAAAAATTAAAAGCGG |
2A touchdown PCR protocol was used rather than locus‐specific annealing temperatures.
The 12 loci were polymorphic in the three populations, with two to 11 alleles (mean 5.17) in population G, two to 10 alleles (mean 4.92) in population C, and one to five alleles (mean 2.83) in population J. The levels of mean observed and expected heterozygosities, respectively, were 0.507 (range 0.107–0.893) and 0.566 (range 0.249–0.827) in population G, 0.547 (range 0.094–0.938) and 0.505 (range 0.253–0.792) in population C, and 0.567 (range 0.000–1.000) and 0.497 (range 0.000–0.800) in population J (Table ). A total of nine loci in population G and eight loci in population C deviated from Hardy–Weinberg equilibrium. This deviation may be due to inbreeding or a low number of samples selected for the study. There was no evidence of linkage disequilibrium between any loci in any of the three populations, indicating that all of the loci were independent and could potentially be used in studies of genetic diversity.
Measures of genetic variation for the 12 polymorphic microsatellite loci in three populations of Astragalus lehmannianus.aLoci | Population G (n = 28) | Population C (n = 32) | Population J (n = 5) | |||||||||
A | H o | He b | Amplification success (%) | A | H o | He b | Amplification success (%) | A | H o | He b | Amplification success (%) | |
AL23 | 7 | 0.357 | 0.783*** | 100 | 5 | 0.381 | 0.371ns | 100 | 2 | 0.800 | 0.480ns | 100 |
AL26 | 4 | 0.250 | 0.336*** | 100 | 4 | 0.188 | 0.253*** | 100 | 2 | 0.800 | 0.480ns | 100 |
AL35 | 3 | 0.143 | 0.249*** | 100 | 4 | 0.375 | 0.322ns | 100 | 1 | 0.000 | 0.000 | 60 |
AL41 | 6 | 0.893 | 0.726** | 100 | 7 | 0.938 | 0.678*** | 100 | 5 | 1.000 | 0.800ns | 100 |
AL42 | 2 | 0.464 | 0.448ns | 100 | 2 | 0.438 | 0.430ns | 100 | 2 | 0.400 | 0.320ns | 100 |
AL43 | 3 | 0.107 | 0.331*** | 100 | 3 | 0.094 | 0.274*** | 100 | 3 | 0.400 | 0.340ns | 100 |
AL50 | 6 | 0.444 | 0.604*** | 96.8 | 7 | 0.594 | 0.628ns | 100 | 3 | 0.400 | 0.460ns | 100 |
AL52 | 9 | 0.393 | 0.814*** | 100 | 7 | 0.125 | 0.604*** | 100 | 3 | 0.000 | 0.640* | 100 |
AL53 | 2 | 0.893 | 0.499*** | 100 | 2 | 0.906 | 0.500*** | 100 | 3 | 0.800 | 0.580ns | 100 |
AL54 | 7 | 0.821 | 0.827ns | 100 | 6 | 0.844 | 0.715*** | 100 | 3 | 0.400 | 0.620ns | 100 |
AL59 | 11 | 0.786 | 0.788ns | 100 | 10 | 0.844 | 0.792* | 100 | 5 | 1.000 | 0.760ns | 100 |
AL65 | 2 | 0.536 | 0.392*** | 100 | 2 | 0.938 | 0.498*** | 100 | 2 | 0.800 | 0.480ns | 100 |
Mean | 5.17 | 0.507 | 0.566 | 99.7 | 4.92 | 0.547 | 0.505 | 100 | 2.83 | 0.567 | 0.497 | 96.7 |
Note
A = observed number of alleles; He = expected heterozygosity; Ho = observed heterozygosity; n = number of individuals sampled.
4Voucher and locality information are provided in Appendix 1.
5Deviation from Hardy–Weinberg equilibrium: *P < 0.05, **P < 0.01, ***P < 0.001, ns = not significant.
Cross‐species amplification using the microsatellites developed for A. lehmannianus was successful for two of the 12 loci (AL42 and AL53) in A. arpilobus and for five of the 12 loci (AL26, AL41, AL50, AL52, and AL54) in A. oxyglottis (Table ). This weakly successful cross‐species amplification may be due to the relatively high genetic differentiation among the three species.
Results of cross‐amplification (allele size ranges) for the 12 polymorphic microsatellite markers developed for Astragalus lehmannianus in two related Astragalus species.aLocus | A. arpilobus | A. oxyglottis |
AL23 | — | — |
AL26 | — | 134–136 |
AL35 | — | — |
AL41 | — | 151–157 |
AL42 | 138–144 | — |
AL43 | — | — |
AL50 | — | 134 |
AL52 | — | 136 |
AL53 | 136 | — |
AL54 | — | 130–148 |
AL59 | — | — |
AL65 | — | — |
Note
— = failed amplification.
7Locality and voucher information are provided in Appendix 1.
CONCLUSIONS
Our results provide 12 microsatellite markers for A. lehmannianus that can serve as a useful resource for estimation of genetic diversity. These newly developed primers can be used for conservation and restoration strategies of this rare species.
ACKNOWLEDGMENTS
The authors thank Yijie Han (Xinjiang Agricultural University, China) for help with field sampling, Professor Wangjin Liao (Beijing Normal University, China) for help with data analysis, and Professors Carol C. Baskin and Jerry M. Baskin (University of Kentucky, USA) for help with polishing the English. This study was supported in part by the National Natural Science Foundation of China (NSFC; U1603231, 31470320).
DATA AVAILABILITY
All sequence information was uploaded to the National Center for Biotechnology Information (NCBI) Sequence Read Archive (accession no. PRJNA547861); primer sequences were uploaded to GenBank (accession no.
AUTHOR CONTRIBUTIONS
M.Y.W., D.Y.T., and X.J.S. conceived and designed the experiments. M.Y.W. performed the experiments. M.Y.W. and X.J.S. analyzed the data. M.Y.W., D.Y.T., and X.J.S. contributed to manuscript preparation. All authors reviewed and approved the manuscript.
APPENDIXLocality and voucher information for the sampled Astragalus populations in this study.
Speciesa | Collection localityb | Locality code | Geographic coordinates | n | Voucher no.c |
Astragalus lehmannianus1,2 Bunge | Jimsar County | G | 44°23′53″N, 88°47′13″E | 28 | XM201720 |
Fukang City | C | 44°22′19″N, 88°08′28″E | 32 | XM201739 | |
Jimsar County | J | 44°25′27″N, 88°56′43″E | 5 | XM201686 | |
A. arpilobus3 Kar. & Kir. | Fukang City | FK | 44°22′45″N, 88°10′02″E | 10 | QJ201811 |
A. oxyglottis3 Steven ex M. Bieb. | Jimsar County | JM | 44°23′25″N, 88°47′33″E | 10 | MY201849 |
Note
n = number of individuals sampled.
1003Samples were used as follows: 1 = individuals used for pre‐screening analyses and genotyping tests; 2 = individuals used for characterization of microsatellites; 3 = individuals used for cross‐amplification tests.
1004All samples were collected from Xinjiang Uygur Autonomous Region in China.
1005Vouchers deposited at Xinjiang Agricultural University (XJA), Xinjiang, Xinjiang Uygur Autonomous Region, China.
APPENDIXCharacteristics of 13 monomorphic microsatellite loci developed and tested in Astragalus lehmannianus.
Locus | Primer sequences (5′–3′) | Repeat motif | Allele size (bp) | GenBank accession no. |
NS‐AL‐08 | F: GACGTATTTGTCCCCCAAAA | (AG)15 | 280 |
|
R: CACTTTTTCTTTTCCTCTTTCTCAA | ||||
NS‐AL‐47 | F: GTCAAAAGCATCGAGTTTCCA | (AG)10 | 115 |
|
R: ATTCGGATGAGATTTCCGTG | ||||
NS‐AL‐49 | F: TTCCAACATGCTCATAACTTC | (GA)10 | 116 |
|
R: TCAACAACGCCATGGACA | ||||
NS‐AL‐62 | F: CCTTTAACGTTGGAAACAA | (GAT)18 | 149 |
|
R: ACAGATGCTGAAGACGTCTCA | ||||
NS‐AL‐70 | F: ATGAAGGGCGTGTTTGTTTC | (TC)10 | 272 |
|
R: CGGGGTCATAGGACTCTCTG | ||||
NS‐AL‐85 | F: GGAATTCCTCGTGCATCTGT | (GT)10 | 270 |
|
R: CAAATTCCCATTCCATCACA | ||||
NS‐AL‐97 | F: ATTTTTATCCCGCACCCTTC | (CT)10 | 268 |
|
R: TGTCATCTTCACCCCATGAA | ||||
NS‐AL‐98 | F: CATTTCCTCTCTCTCCGGC | (CT)10 | 268 |
|
R: AGCCCAGTTCGTTTTCTGTG | ||||
NS‐AL‐121 | F: TCTCATCACTCTCTGCCCCT | (GA)10 | 278 |
|
R: TGGATTTCATATTCTACAACCTTTTG | ||||
NS‐AL‐129 | F: GTACCGAATCCAACTCCGAA | (GA)13 | 277 |
|
R: TCGTTCTGCTTCCTTCGTTT | ||||
NS‐AL‐137 | F: TGATCTTCCAGCATGTTCTCA | (GA)11 | 276 |
|
R: CGTTTGCGAAAACAGATACG | ||||
NS‐AL‐142 | F: GTTTCCATGTGTGTGTGCG | (AG)15 | 275 |
|
R: CCCAAAATAACGAAGCCAAA | ||||
NS‐AL‐143 | F: ACTGGAATTCCCCTTCCAAC | (GT)10 | 275 |
|
R: TGAGGAAGAAGAGGGTCGTG |
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Abstract
Premise
Astragalus lehmannianus (Fabaceae) is a vulnerable species found in the cold deserts of northwestern China. We aimed to characterize polymorphic microsatellite loci for A. lehmannianus to support future studies of population genetic dynamics and conservation management of the species.
Methods and Results
We used next‐generation sequencing to detect polymorphic microsatellites. Twenty‐five potential microsatellite loci were identified, 12 of which were polymorphic and present in the three study populations of A. lehmannianus. Levels of observed and expected heterozygosities were 0.000–1.000 and 0.000–0.827, respectively. Furthermore, two and five of the 12 developed primers were successfully amplified in two congeneric species, A. arpilobus and A. oxyglottis, respectively.
Conclusions
These newly developed microsatellite markers can be used to determine population diversity and to develop conservation strategies in A. lehmannianus.
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1 Xinjiang Key Laboratory of Grassland Resources and Ecology and Ministry of Education Key Laboratory for Western Arid Region Grassland Resources and Ecology, College of Grassland and Environment Sciences, Xinjiang Agricultural University, Ürümqi, People's Republic of China
2 Xinjiang Key Laboratory of Grassland Resources and Ecology and Ministry of Education Key Laboratory for Western Arid Region Grassland Resources and Ecology, College of Grassland and Environment Sciences, Xinjiang Agricultural University, Ürümqi, People's Republic of China; College of Biology and Environmental Sciences, Jishou University, Jishou, People's Republic of China