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Association of loganin contents with the genetic
characterization of natural populations of Palicourea rigida
Kunth determined by AFLP molecular markers
Michele dos Santos da Silva, Ana Maria Soares Pereira,
Lucas Junqueira de Freitas Morel, Suzelei de Castro França,
Bianca Waléria Bertoni*
Universidade de Ribeirão Preto, UNAERP, Unidade de Biotecnologia, Av. Costábile Romano, 2201 Ribeirânia, CEP: 14096-900 Ribeirão
Preto, SP, Brazil
a r t i c l e i n f o
Article history:
Received 4 June 2013
Accepted 24 August 2013
Available online 24 September 2013
Keywords:
Genetic diversity
Chemical variability
Cerrado
Rubiaceae
a b s t r a c t
Extracts of the medicinal plant Palicourea rigida Kunth, popularly known as douradinha, are
widely used for treating urinary tract disorders. Unfortunately, nowadays this is one of the
species endemic to Brazilian Cerrado that is at greatest risk of extinction.
The aim of the this work was to use AFLP molecular markers to determine the genetic
structure and diversity of eight natural populations of P. rigida and to associate their ge-
netic characteristics with loganin production in order to obtain provide relevant infor-
mation to promote programs for the conservation of this valuable medicinal plant.
A total of 120 polymorphic bands were scored and higher proportion of genetic diversity
was found in inter-populations (64%) rather than in intra-populations (36%). Fst value was
found to be significantly greater than zero (0.3601), demonstrating the complex genetic
structure of P. rigida populations. Accessions collected from Cristalina, GO, showed higher
percentage of polymorphic loci (65.5%) and the highest genetic diversity. Analysis of
Molecular variance (AMOVA) demonstrated 63.9% of intra-population genetic variation.
The lowest genetic variability was detected among accessions from the population found
in Sacramento, MG. No spatial standard was observed for P. rigida population, suggesting a
partially isolated island model. It was observed a minor but significant positive correlation
(r ¼ 0.22) between chemical and genetic matrices. The association between chemical and
genetic data indicated that environmental factors promoted the loganin production in
populations growing in Luziânia, GO, and therefore accessions from those populations
should be considered as prime material for initiating the conservation process of P. rigida.
Ó 2013 Elsevier Ltd. All rights reserved.
1. Introduction
Palicoura rigida Kunth is one of the species endemic to Brazilian Cerrado that is at greatest risk of extinction. According to
Siqueira (2004), ecological data show evidence of the susceptibility of such species to temperature changes, indicating that they
probably will be extinguished if the temperature of the planet increases by 1.8–2 C. Moreover, because of its widely reported
efficacy in the treatment of renal affections, this plant has been indiscriminately collected by inhabitants from the Cerrado biome
(Rodrigues and Carvalho, 2001), thus compromising its survival. The medicinal effectiveness of P. rigida leaf extracts has been
* Corresponding author. Tel./fax: þ55 1636036727.
E-mail address: bbertoni@unaerp.br (B.W. Bertoni).
Contents lists available at ScienceDirect
Biochemical Systematics and Ecology
journal homepage: www.elsevier.com/locate/biochemsyseco
0305-1978/$ – see front matter Ó 2013 Elsevier Ltd. All rights reserved.
http://dx.doi.org/10.1016/j.bse.2013.08.032
Biochemical Systematics and Ecology 51 (2013) 189–194
attributed to loganin, an iridoid with analgesic and anti-inflammatory activity that is produced by the plant tissues (Xu et al.,
2006; Park et al., 2010). Morel et al. (2011) have recently described that natural populations of that species produce variable
concentrations of loganin.
Considering the above-mentioned findings obtained in this work, AFLP molecular markers were used to determine the
genetic structure and diversity of eight natural populations of P. rigida. Additionally, the genetic characteristics of the plants
were associated to their loganin production in order to provide relevant information to promote programs for the conser-
vation of this valuable medicinal plant.
2. Materials and methods
2.1. Plant material
Leaves of P. rigida were collected during the month of March 2009 from eight natural populations located in Altinópolis
and Rifaina (SP), Perdizes, Sacramento and Uberlândia (MG), Catalão, Cristalina and Luiziânia (GO). The collection sites were
geo-referenced by using a Global Positioning System (Table 1). The plant material was stored in the Herbarium of Medicinal
Plants at the University of Ribeirão Preto – UNAERP (voucher HPMU – 1416).
2.2. DNA extraction and AFLP analysis
Leaf tissues were used for DNA isolation by using the CTAB method (Doyle and Doyle, 1990). Quantity was estimated by
spectrophotometry and quality was evaluated by using 0.8%-agarose gel electrophoresis in 1Â TBE buffer.
Amplified fragment length analysis (AFLsP) was carried out according to protocol proposed by Vos et al. (1995) for genetic
diversity determination. Restriction enzymes EcoRI and Mse I (New England Biolabs, Ipswich, MA, USA) were used for double
digestion of 200 ng of genomic DNA. The resulting fragments were ligated to specific adapter sequences to complement the
ends cleaved by both enzymes. Ligation reaction was kept at 37 C for 3 h by using MJ RESEARCH PTC-100 thermal cycler.
After restriction and ligation reactions, the DNA was pre-amplified with primers containing one selective base, i.e., EcoRI-
A/MseI-A. The PCR products from pre-amplification were used as template for the second reaction – the selective amplifi-
cation. Ten combinations of 2 or 3 selective nucleotides were site-specifically attached to the 30-terminal of the primers used.
Pre-amplification reaction used the following: 1 ml EcoRI þ (1 oligo) (25 ng/ml); 1 ml MseI þ (1 oligo) (25 ng/ml); 0.8 ml
dNTPs 2.5 mM, 2 ml 10Â Buffer B (Promega), 1.2 ml MgCl2 (25 mM), 0.6 ml Taq DNA polymerase (5 un/ml) (Promega) and 2 ml of
ligated DNA.
Amplification was carried out as follows: 1) 94 C for 2 min, 2) 94 C for 1 min, 3) 56 C for 1 min, 4) 72 C for 1 min, 5) 72 C
for 5 min; steps 2 to 4 were repeated 26 times. Amplification products were diluted 4 times and stored at 20 C.
AFLP-PCR was performed as follows: 1 ml EcoRI þ (3 oligo) (25 ng/ml); 1.2 ml MseI þ (3 oligo) (25 ng/ml); 0.4 ml dNTPs 2.5 mM;
2 ml 10Â Buffer B (Promega); 1.2 ml MgCl2 (25 mM), 0.2 ml Taq DNA polymerase (5 un/ml) (Promega) and 1.5 ml pre-amplified DNA.
Selective amplification was carried out as follows: 1) 94 C for 2 min; 2) 94 C for 30 s; 3) 65 C for 30 s; 4) 72 C for 1 min;
5) 94 C for 30 s; 6) 56 C for 30 s; 7) 72 C for 1 min; 8) 72 C for 2 min, steps 2 to 4 were repeated 12 times and steps 5 to 7
repeated 23 times. Amplification products were stored at 20 C.
After selective amplification, the product of each reaction was mixed with 8 ml of loading buffer. Next, the samples were
denatured at 95 C for 5 min and immediately transferred to ice.
AFLP products were separated in denaturing polyacrylamide gel (6%) with TBE 1Â buffer at constant voltage of 80 W and
maximum temperature of 50 C during 4 h. The gel was stained with AgNO3 and visualized with Na2CO3 according to protocol
described by Creste et al. (2001).
2.3. Extraction and quantification of loganin
To confirm identification of the loganin sample, HPLC analyses were performed by using standard loganin (Merck).
Leaves (100 mg) collected from each population were separately ground (40 mesh), and the powdered material was
extracted by using ultrasound-assisted extraction with 3 mL MeOH:H2O (v/v) for 45 min. An aliquot of 1 mL was filtered and
Table 1
Places of collection of P. rigida – codes and geographic coordinates.
Mean values Code n Latitude Longitude Altitude (m)
Rifaina (SP) R 20 À20
100
À47
280
954
Uberlândia (MG) UB 25 À19
150
À47
430
985
Luziânia (GO) LU 20 À16
210
À47
500
947
Catalão (GO) CA 20 À17
490
À47
460
940
Altinópolis (SP) ALT 21 À21
030
À47
290
626
Sacramento (MG) SC 21 À20
010
À47
240
647
Cristalina (GO) CR 21 À16
590
À47
140
922
Perdizes (MG) P 20 À19
310
À47
050
942
n ¼ number of accessions collected.
M.dosS. da Silva et al. / Biochemical Systematics and Ecology 51 (2013) 189–194190
analyzed with HPLC, with gradient mobile phase of (MeOH:(H2O þ CH3COOH 0.1%) 10:90 (0 min) to (MeOH:(H2O þ CH3COOH
0.1%) 50:50 (50 min) (Tian et al., 2007; Quian et al., 2007).
2.4. Statistical analysis
Binary data obtained from AFLP were used to estimate allele frequencies and were submitted to analysis of molecular
variance (AMOVA) for decomposition of the total genetic variance between and within the populations, as proposed by
Excoffier et al. (1992). Nei’s diversity index (1978) was used in UPGMA clustering analysis (Ferreira and Grattapaglia, 1998) to
demonstrate the genetic correlation between the populations investigated. The software packages GENES (Cruz, 2006),
POPGENE (Yeh et al., 1999) and TFPGA (Miller, 1997) were used to carry out the analysis.
Chemical analyses were performed in triplicate and the experimental design was completely randomized.
Data were submitted to analysis of variance (ANOVA) by using the software SISVAR (Variance Analysis System, Federal
University of Viçosa, MG, Brazil) (Ferreira, 2003), with means being compared by using Scott–Knott’s multiple-range tests (Scott
and Knott, 1974) at P 0.05. This analysis was performed to cluster individual samples into groups depending on the loganin
contents found in accessions collected in Luziânia, GO. Nei’s genetic index (1978) was used to calculate the genetic distance
among individuals and a dendrogram was created from a binary matrix by using the software POPGENE (Yeh et al., 1999).
The genetic similarity among the accessions collected in Luziânia were calculated with the Jaccard coefficient by using the
NTSYS-pc version 2.01 software package (Rohlf, 2000). Both analyses used the Un-weighted Pair Group Method with
Arithmetic Mean (UPGMA) clustering method. The support values for the degree of confidence at the nodes of the
dendrogram were analyzed by using the bootstrap re-sampling technique 1000 times. Matrices were correlated with Mantel
statistics Z test by using the software GENES (Cruz, 2006).
3. Results and discussion
A total of 120 polymorphic bands of variable number of base pairs (75–350) were produced by 3 combinations of primers.
The minimum and maximum numbers of polymorphic bands per primer were 20 and 59, respectively (Table 2).
The genetic characterization of the eight populations, determined by allele frequencies, is shown in Table 3. Among the 169
accessions investigated, the mean number of allele was 1545 and the mean percentage of polymorphic loci reached 54.5%. The
P. rigida population from Cristalina presented the highest percentage of polymorphism (65.5%), followed by those from
Uberlândia (64.9%), Altinópolis (62.5%), Luiziânia (56.9%), Catalão (54.9%), Perdizes (45.7%), Rifâina (43.0%), and Sacramento
(42.8%). Nei’s genetic distances (h) ranged from 0.2678 to 0.1494 and Shannon’s index (I) from 0.4882 to 0.2228, whereas the
population from Sacramento presented the lower diversity in both analyzed indexes.
Analysis of Molecular variance (AMOVA) demonstrated 63.9% of intra-population genetic variation.
The FST value of 0.3601 (p  0.001), as stated by Sole-Cava (2001), revealed that this species has a complex genetic
structure (Table 4). According to Frankham et al. (2007), FST value greater than 0.15 is usually an indicative of population
fragmentation, that is, the higher this factor the lower the ability of dispersion, increasing the likelihood that these pop-
ulations will become endogamous. The authors also reported that inbreeding and loss of genetic diversity are inevitable in
small populations, reducing reproduction and survival rates in the short time. Moreover, endogamous populations have their
capacity of evolving reduced in response to environmental changes in the long time, which increases the risk of extinction.
Geographically distant populations like those from Cristalina (GO) and Perdizes (MG) as well as those from Catalão (GO)
and Altinópolis (SP), with geographic distances of 283 and 359 km and genetic distances ranging from 0.0528 to 0.0633,
respectively, were grouped (Fig. 1 and Table 5).
No spatial pattern was observed because there was no significant correlation between genetic and geographic distances
determined by the Mantel matrix correlation coefficient based on 1000 permutations. According to Diniz-Filho (2000), these
results show that the genetic structure of P. rigida populations follows the partially isolated island model, evolving in the
genetic space independently. A model of isolation by distance in which bordering populations would be genetically more
similar was not evidenced.
The low gene flow (Nm ¼ 0.855) among P. rigida populations resulted in a relatively high FST value (0.3601). This result
suggests that the number of migrants per generation is inferior to 1, and that P. rigida populations are more susceptible to
genetic drift.
Table 2
AFLP markers selected for molecular analysis of P. rigida.
Primer combinations Total of bands Number of polymorphic bands Polymorphism (%)
E-AGA þ M-TTC 50 20 60
E-AAT þ M-TT 41 41 100
E-AG þ TA 60 59 98
Total 151 120 79
Mean values 50 40 80
M.dosS. da Silva et al. / Biochemical Systematics and Ecology 51 (2013) 189–194 191
The results indicated that the AFLP technique was an efficient tool to determine the genetic diversity among the 8 pop-
ulations of P. rigida investigated. Many works using AFLP molecular markers have equally validated the potential of this
method for determining both diversity and genetic structure of plant populations, such as studies by Zhuravlev et al. (2008)
with Jatropha curcas, Ribeiro et al. (2010) with Maytenus ilicifolia and Zang et al. (2010) with Glycyrrhiza uralenseis.
All accessions with high yields of loganin were from Luiziânia. Analysis of molecular variance clustered accessions of that
population into 4 groups with significant difference in mean concentration of loganin. Group A had 5% of the accessions with
high yields of loganin (205.14 mg/g PS); in Group B, 20% of the accessions contained medium yields of loganin (161.27 mg/g
PS); in Group C, 55% of the accessions also presented medium contents (96.04 mg/g PS); and 20% of the accessions in Group D
contained low yields of loganin (45.19 mg/g PS).
In the Luiziânia population, within a distance of 10 m, accessions producing either high, medium or low contents of
loganin were collected. It was observed a minor but significant positive correlation (r ¼ 0.22) between chemical and genetic
matrices. The dendrogram presented in Fig. 2 shows a tendency to cluster accessions with medium contents of loganin,
whereas the dendrogram in Fig. 3 shows that Group A is genetically more distant (0.2957) from the other two groups, with
Groups B and C being more closely related (0.0410).
According to Dixon et al. (2006), natural products are synthesized by long and complex biosynthesis pathways that are
controlled by a network of genes. The translation of genotype into chemotype is dependent on gene interactions and envi-
ronmental factors. There are several studies describing the chemical profile of medicinal plants and others reporting their
genetic data, but only a few works associate chemical and genetic information. Hu et al. (2007), established a variation pattern
Table 3
Basic descriptive statistics for AFLP analysis of P. rigida populations.
Populations n na h I P
Rifaina (SP) 20 1.4305 0.1707 0.2485 43.05
Uberlândia (MG) 25 1.6490 0.2391 0.3530 64.90
Luziânia (GO) 21 1.5695 0.2107 0.3125 56.95
Catalão (GO) 20 1.5497 0.2145 0.3139 54.97
Altinópolis (SP) 21 1.6291 0.2521 0.3670 62.91
Sacramento (MG) 21 1.4238 0.1494 0.2228 42.38
Cristalina (GO) 21 1.6556 0.2678 0.2444 65.56
Perdizes (MG) 20 1.4570 0.1649 0.4882 45.70
Total 169 1.8609 0.3323 0.4882 –
Mean sample size (n), number of observed alleles per locus (na) Neis’ índex (h); Shannon’s index (I); percentage of polymorphic loci (P). POPGENE data (Yeh
et al., 1999).
Table 4
Total genetic variance analysis (AMOVA) between and within populations of P. rigida based on binary data obtained from AFLP results.
Source of variation D.F. S. Q. S. Q. M. Variance components % of total variation p Fst value
Between populations 7 1370.8093 195.8299 8.557 36.0071 0.001 0.3601
Within populations 161 2448.3505 15.2071 15.2071 63.9929 – –
Total 168 3819.1598 22.7331
DF ¼ degrees of freedom; SQ ¼ sum of squares; SQM ¼ sum of mean squares; p ¼ level of significance for estimation of genetic variation based on 1000
permutations.
Fig. 1. UPGMA dendrogram based on Nei’s (1978) genetic distance between P. rigida populations using TFPGA software.
M.dosS. da Silva et al. / Biochemical Systematics and Ecology 51 (2013) 189–194192
between the chemical and genetic diversities of Vitex rotundifolia, whereas Zang et al. (2012) investigated the association of
chemical and genetic diversities of Centella asiatica, reporting no such a correlation and attributing the diversity among
populations to environmental factors.
However, the present study has shown evidence of a correlation between chemical and genetic data and that environ-
mental factors select genes that affect the loganin production of accessions from Luziânia population. However, the present
study has shown evidence of a correlation between chemical and genetic data and that environmental factors select genes
that affect the loganin production of accessions from Luziânia population. Lerin et al. (2007) compared genetic variability and
chemical diversity of essential oils in Salvia spp. and they found a cluster tendency indicating a strong influence of genetic
basis on the chemical composition, attributing this result to adaptations to edaphoclimatic conditions favoring some alleles at
the expense of others.
Our data show that a conservation program through a germplasm bank should be undertaken with the introduction of
greater number of individuals from the Luziania population in relation to the other populations studied.
Table 5
Genetic distance (Nei, 1978) below diagonal and geographic distance (Km) above diagonal.
R UB LU CA ALT SA CR P
R *** 104 425 262 94.09 18.97 354 79.90
UB 0.1162 *** 324 160 200 90.37 258 72.52
LU 0.1918 0.1386 *** 162 520 408 92.59 360
CA 0.0948 0.0935 0.1011 *** 359 247 109 200
ALT 0.0710 0.0825 0.1209 0.0633 *** 112 453 176
SA 0.0906 0.1277 0.1805 0.1142 0.1030 *** 336 67.19
CR 0.0890 0.1123 0.1049 0.0546 0.0593 0.1080 *** 283
P 0.0922 0.1548 0.1654 0.0908 0.1145 0.1171 0.0528 ***
Data obtained using the software POPGENE and TRACKMAKER.
Fig. 2. UPGMA dendrogram based on AFLP data, showing the genetic relationships between P. rigida accessions from Luiziânia using NTSYS software. Group A
(high yields); B (medium yields); C (also presented medium contents); D (low yields) of loganin.
M.dosS. da Silva et al. / Biochemical Systematics and Ecology 51 (2013) 189–194 193
Acknowledgments
This research was supported by the State of São Paulo Research Foundation (FAPESP) under project number 07/58503-3.
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M.dosS. da Silva et al. / Biochemical Systematics and Ecology 51 (2013) 189–194194

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Association of loganin contents with the genetic characterization of natural populations of Palicourea rigida Kunth determined by AFLP molecular markers

  • 1. Association of loganin contents with the genetic characterization of natural populations of Palicourea rigida Kunth determined by AFLP molecular markers Michele dos Santos da Silva, Ana Maria Soares Pereira, Lucas Junqueira de Freitas Morel, Suzelei de Castro França, Bianca Waléria Bertoni* Universidade de Ribeirão Preto, UNAERP, Unidade de Biotecnologia, Av. Costábile Romano, 2201 Ribeirânia, CEP: 14096-900 Ribeirão Preto, SP, Brazil a r t i c l e i n f o Article history: Received 4 June 2013 Accepted 24 August 2013 Available online 24 September 2013 Keywords: Genetic diversity Chemical variability Cerrado Rubiaceae a b s t r a c t Extracts of the medicinal plant Palicourea rigida Kunth, popularly known as douradinha, are widely used for treating urinary tract disorders. Unfortunately, nowadays this is one of the species endemic to Brazilian Cerrado that is at greatest risk of extinction. The aim of the this work was to use AFLP molecular markers to determine the genetic structure and diversity of eight natural populations of P. rigida and to associate their ge- netic characteristics with loganin production in order to obtain provide relevant infor- mation to promote programs for the conservation of this valuable medicinal plant. A total of 120 polymorphic bands were scored and higher proportion of genetic diversity was found in inter-populations (64%) rather than in intra-populations (36%). Fst value was found to be significantly greater than zero (0.3601), demonstrating the complex genetic structure of P. rigida populations. Accessions collected from Cristalina, GO, showed higher percentage of polymorphic loci (65.5%) and the highest genetic diversity. Analysis of Molecular variance (AMOVA) demonstrated 63.9% of intra-population genetic variation. The lowest genetic variability was detected among accessions from the population found in Sacramento, MG. No spatial standard was observed for P. rigida population, suggesting a partially isolated island model. It was observed a minor but significant positive correlation (r ¼ 0.22) between chemical and genetic matrices. The association between chemical and genetic data indicated that environmental factors promoted the loganin production in populations growing in Luziânia, GO, and therefore accessions from those populations should be considered as prime material for initiating the conservation process of P. rigida. Ó 2013 Elsevier Ltd. All rights reserved. 1. Introduction Palicoura rigida Kunth is one of the species endemic to Brazilian Cerrado that is at greatest risk of extinction. According to Siqueira (2004), ecological data show evidence of the susceptibility of such species to temperature changes, indicating that they probably will be extinguished if the temperature of the planet increases by 1.8–2 C. Moreover, because of its widely reported efficacy in the treatment of renal affections, this plant has been indiscriminately collected by inhabitants from the Cerrado biome (Rodrigues and Carvalho, 2001), thus compromising its survival. The medicinal effectiveness of P. rigida leaf extracts has been * Corresponding author. Tel./fax: þ55 1636036727. E-mail address: bbertoni@unaerp.br (B.W. Bertoni). Contents lists available at ScienceDirect Biochemical Systematics and Ecology journal homepage: www.elsevier.com/locate/biochemsyseco 0305-1978/$ – see front matter Ó 2013 Elsevier Ltd. All rights reserved. http://dx.doi.org/10.1016/j.bse.2013.08.032 Biochemical Systematics and Ecology 51 (2013) 189–194
  • 2. attributed to loganin, an iridoid with analgesic and anti-inflammatory activity that is produced by the plant tissues (Xu et al., 2006; Park et al., 2010). Morel et al. (2011) have recently described that natural populations of that species produce variable concentrations of loganin. Considering the above-mentioned findings obtained in this work, AFLP molecular markers were used to determine the genetic structure and diversity of eight natural populations of P. rigida. Additionally, the genetic characteristics of the plants were associated to their loganin production in order to provide relevant information to promote programs for the conser- vation of this valuable medicinal plant. 2. Materials and methods 2.1. Plant material Leaves of P. rigida were collected during the month of March 2009 from eight natural populations located in Altinópolis and Rifaina (SP), Perdizes, Sacramento and Uberlândia (MG), Catalão, Cristalina and Luiziânia (GO). The collection sites were geo-referenced by using a Global Positioning System (Table 1). The plant material was stored in the Herbarium of Medicinal Plants at the University of Ribeirão Preto – UNAERP (voucher HPMU – 1416). 2.2. DNA extraction and AFLP analysis Leaf tissues were used for DNA isolation by using the CTAB method (Doyle and Doyle, 1990). Quantity was estimated by spectrophotometry and quality was evaluated by using 0.8%-agarose gel electrophoresis in 1Â TBE buffer. Amplified fragment length analysis (AFLsP) was carried out according to protocol proposed by Vos et al. (1995) for genetic diversity determination. Restriction enzymes EcoRI and Mse I (New England Biolabs, Ipswich, MA, USA) were used for double digestion of 200 ng of genomic DNA. The resulting fragments were ligated to specific adapter sequences to complement the ends cleaved by both enzymes. Ligation reaction was kept at 37 C for 3 h by using MJ RESEARCH PTC-100 thermal cycler. After restriction and ligation reactions, the DNA was pre-amplified with primers containing one selective base, i.e., EcoRI- A/MseI-A. The PCR products from pre-amplification were used as template for the second reaction – the selective amplifi- cation. Ten combinations of 2 or 3 selective nucleotides were site-specifically attached to the 30-terminal of the primers used. Pre-amplification reaction used the following: 1 ml EcoRI þ (1 oligo) (25 ng/ml); 1 ml MseI þ (1 oligo) (25 ng/ml); 0.8 ml dNTPs 2.5 mM, 2 ml 10Â Buffer B (Promega), 1.2 ml MgCl2 (25 mM), 0.6 ml Taq DNA polymerase (5 un/ml) (Promega) and 2 ml of ligated DNA. Amplification was carried out as follows: 1) 94 C for 2 min, 2) 94 C for 1 min, 3) 56 C for 1 min, 4) 72 C for 1 min, 5) 72 C for 5 min; steps 2 to 4 were repeated 26 times. Amplification products were diluted 4 times and stored at 20 C. AFLP-PCR was performed as follows: 1 ml EcoRI þ (3 oligo) (25 ng/ml); 1.2 ml MseI þ (3 oligo) (25 ng/ml); 0.4 ml dNTPs 2.5 mM; 2 ml 10Â Buffer B (Promega); 1.2 ml MgCl2 (25 mM), 0.2 ml Taq DNA polymerase (5 un/ml) (Promega) and 1.5 ml pre-amplified DNA. Selective amplification was carried out as follows: 1) 94 C for 2 min; 2) 94 C for 30 s; 3) 65 C for 30 s; 4) 72 C for 1 min; 5) 94 C for 30 s; 6) 56 C for 30 s; 7) 72 C for 1 min; 8) 72 C for 2 min, steps 2 to 4 were repeated 12 times and steps 5 to 7 repeated 23 times. Amplification products were stored at 20 C. After selective amplification, the product of each reaction was mixed with 8 ml of loading buffer. Next, the samples were denatured at 95 C for 5 min and immediately transferred to ice. AFLP products were separated in denaturing polyacrylamide gel (6%) with TBE 1Â buffer at constant voltage of 80 W and maximum temperature of 50 C during 4 h. The gel was stained with AgNO3 and visualized with Na2CO3 according to protocol described by Creste et al. (2001). 2.3. Extraction and quantification of loganin To confirm identification of the loganin sample, HPLC analyses were performed by using standard loganin (Merck). Leaves (100 mg) collected from each population were separately ground (40 mesh), and the powdered material was extracted by using ultrasound-assisted extraction with 3 mL MeOH:H2O (v/v) for 45 min. An aliquot of 1 mL was filtered and Table 1 Places of collection of P. rigida – codes and geographic coordinates. Mean values Code n Latitude Longitude Altitude (m) Rifaina (SP) R 20 À20 100 À47 280 954 Uberlândia (MG) UB 25 À19 150 À47 430 985 Luziânia (GO) LU 20 À16 210 À47 500 947 Catalão (GO) CA 20 À17 490 À47 460 940 Altinópolis (SP) ALT 21 À21 030 À47 290 626 Sacramento (MG) SC 21 À20 010 À47 240 647 Cristalina (GO) CR 21 À16 590 À47 140 922 Perdizes (MG) P 20 À19 310 À47 050 942 n ¼ number of accessions collected. M.dosS. da Silva et al. / Biochemical Systematics and Ecology 51 (2013) 189–194190
  • 3. analyzed with HPLC, with gradient mobile phase of (MeOH:(H2O þ CH3COOH 0.1%) 10:90 (0 min) to (MeOH:(H2O þ CH3COOH 0.1%) 50:50 (50 min) (Tian et al., 2007; Quian et al., 2007). 2.4. Statistical analysis Binary data obtained from AFLP were used to estimate allele frequencies and were submitted to analysis of molecular variance (AMOVA) for decomposition of the total genetic variance between and within the populations, as proposed by Excoffier et al. (1992). Nei’s diversity index (1978) was used in UPGMA clustering analysis (Ferreira and Grattapaglia, 1998) to demonstrate the genetic correlation between the populations investigated. The software packages GENES (Cruz, 2006), POPGENE (Yeh et al., 1999) and TFPGA (Miller, 1997) were used to carry out the analysis. Chemical analyses were performed in triplicate and the experimental design was completely randomized. Data were submitted to analysis of variance (ANOVA) by using the software SISVAR (Variance Analysis System, Federal University of Viçosa, MG, Brazil) (Ferreira, 2003), with means being compared by using Scott–Knott’s multiple-range tests (Scott and Knott, 1974) at P 0.05. This analysis was performed to cluster individual samples into groups depending on the loganin contents found in accessions collected in Luziânia, GO. Nei’s genetic index (1978) was used to calculate the genetic distance among individuals and a dendrogram was created from a binary matrix by using the software POPGENE (Yeh et al., 1999). The genetic similarity among the accessions collected in Luziânia were calculated with the Jaccard coefficient by using the NTSYS-pc version 2.01 software package (Rohlf, 2000). Both analyses used the Un-weighted Pair Group Method with Arithmetic Mean (UPGMA) clustering method. The support values for the degree of confidence at the nodes of the dendrogram were analyzed by using the bootstrap re-sampling technique 1000 times. Matrices were correlated with Mantel statistics Z test by using the software GENES (Cruz, 2006). 3. Results and discussion A total of 120 polymorphic bands of variable number of base pairs (75–350) were produced by 3 combinations of primers. The minimum and maximum numbers of polymorphic bands per primer were 20 and 59, respectively (Table 2). The genetic characterization of the eight populations, determined by allele frequencies, is shown in Table 3. Among the 169 accessions investigated, the mean number of allele was 1545 and the mean percentage of polymorphic loci reached 54.5%. The P. rigida population from Cristalina presented the highest percentage of polymorphism (65.5%), followed by those from Uberlândia (64.9%), Altinópolis (62.5%), Luiziânia (56.9%), Catalão (54.9%), Perdizes (45.7%), Rifâina (43.0%), and Sacramento (42.8%). Nei’s genetic distances (h) ranged from 0.2678 to 0.1494 and Shannon’s index (I) from 0.4882 to 0.2228, whereas the population from Sacramento presented the lower diversity in both analyzed indexes. Analysis of Molecular variance (AMOVA) demonstrated 63.9% of intra-population genetic variation. The FST value of 0.3601 (p 0.001), as stated by Sole-Cava (2001), revealed that this species has a complex genetic structure (Table 4). According to Frankham et al. (2007), FST value greater than 0.15 is usually an indicative of population fragmentation, that is, the higher this factor the lower the ability of dispersion, increasing the likelihood that these pop- ulations will become endogamous. The authors also reported that inbreeding and loss of genetic diversity are inevitable in small populations, reducing reproduction and survival rates in the short time. Moreover, endogamous populations have their capacity of evolving reduced in response to environmental changes in the long time, which increases the risk of extinction. Geographically distant populations like those from Cristalina (GO) and Perdizes (MG) as well as those from Catalão (GO) and Altinópolis (SP), with geographic distances of 283 and 359 km and genetic distances ranging from 0.0528 to 0.0633, respectively, were grouped (Fig. 1 and Table 5). No spatial pattern was observed because there was no significant correlation between genetic and geographic distances determined by the Mantel matrix correlation coefficient based on 1000 permutations. According to Diniz-Filho (2000), these results show that the genetic structure of P. rigida populations follows the partially isolated island model, evolving in the genetic space independently. A model of isolation by distance in which bordering populations would be genetically more similar was not evidenced. The low gene flow (Nm ¼ 0.855) among P. rigida populations resulted in a relatively high FST value (0.3601). This result suggests that the number of migrants per generation is inferior to 1, and that P. rigida populations are more susceptible to genetic drift. Table 2 AFLP markers selected for molecular analysis of P. rigida. Primer combinations Total of bands Number of polymorphic bands Polymorphism (%) E-AGA þ M-TTC 50 20 60 E-AAT þ M-TT 41 41 100 E-AG þ TA 60 59 98 Total 151 120 79 Mean values 50 40 80 M.dosS. da Silva et al. / Biochemical Systematics and Ecology 51 (2013) 189–194 191
  • 4. The results indicated that the AFLP technique was an efficient tool to determine the genetic diversity among the 8 pop- ulations of P. rigida investigated. Many works using AFLP molecular markers have equally validated the potential of this method for determining both diversity and genetic structure of plant populations, such as studies by Zhuravlev et al. (2008) with Jatropha curcas, Ribeiro et al. (2010) with Maytenus ilicifolia and Zang et al. (2010) with Glycyrrhiza uralenseis. All accessions with high yields of loganin were from Luiziânia. Analysis of molecular variance clustered accessions of that population into 4 groups with significant difference in mean concentration of loganin. Group A had 5% of the accessions with high yields of loganin (205.14 mg/g PS); in Group B, 20% of the accessions contained medium yields of loganin (161.27 mg/g PS); in Group C, 55% of the accessions also presented medium contents (96.04 mg/g PS); and 20% of the accessions in Group D contained low yields of loganin (45.19 mg/g PS). In the Luiziânia population, within a distance of 10 m, accessions producing either high, medium or low contents of loganin were collected. It was observed a minor but significant positive correlation (r ¼ 0.22) between chemical and genetic matrices. The dendrogram presented in Fig. 2 shows a tendency to cluster accessions with medium contents of loganin, whereas the dendrogram in Fig. 3 shows that Group A is genetically more distant (0.2957) from the other two groups, with Groups B and C being more closely related (0.0410). According to Dixon et al. (2006), natural products are synthesized by long and complex biosynthesis pathways that are controlled by a network of genes. The translation of genotype into chemotype is dependent on gene interactions and envi- ronmental factors. There are several studies describing the chemical profile of medicinal plants and others reporting their genetic data, but only a few works associate chemical and genetic information. Hu et al. (2007), established a variation pattern Table 3 Basic descriptive statistics for AFLP analysis of P. rigida populations. Populations n na h I P Rifaina (SP) 20 1.4305 0.1707 0.2485 43.05 Uberlândia (MG) 25 1.6490 0.2391 0.3530 64.90 Luziânia (GO) 21 1.5695 0.2107 0.3125 56.95 Catalão (GO) 20 1.5497 0.2145 0.3139 54.97 Altinópolis (SP) 21 1.6291 0.2521 0.3670 62.91 Sacramento (MG) 21 1.4238 0.1494 0.2228 42.38 Cristalina (GO) 21 1.6556 0.2678 0.2444 65.56 Perdizes (MG) 20 1.4570 0.1649 0.4882 45.70 Total 169 1.8609 0.3323 0.4882 – Mean sample size (n), number of observed alleles per locus (na) Neis’ índex (h); Shannon’s index (I); percentage of polymorphic loci (P). POPGENE data (Yeh et al., 1999). Table 4 Total genetic variance analysis (AMOVA) between and within populations of P. rigida based on binary data obtained from AFLP results. Source of variation D.F. S. Q. S. Q. M. Variance components % of total variation p Fst value Between populations 7 1370.8093 195.8299 8.557 36.0071 0.001 0.3601 Within populations 161 2448.3505 15.2071 15.2071 63.9929 – – Total 168 3819.1598 22.7331 DF ¼ degrees of freedom; SQ ¼ sum of squares; SQM ¼ sum of mean squares; p ¼ level of significance for estimation of genetic variation based on 1000 permutations. Fig. 1. UPGMA dendrogram based on Nei’s (1978) genetic distance between P. rigida populations using TFPGA software. M.dosS. da Silva et al. / Biochemical Systematics and Ecology 51 (2013) 189–194192
  • 5. between the chemical and genetic diversities of Vitex rotundifolia, whereas Zang et al. (2012) investigated the association of chemical and genetic diversities of Centella asiatica, reporting no such a correlation and attributing the diversity among populations to environmental factors. However, the present study has shown evidence of a correlation between chemical and genetic data and that environ- mental factors select genes that affect the loganin production of accessions from Luziânia population. However, the present study has shown evidence of a correlation between chemical and genetic data and that environmental factors select genes that affect the loganin production of accessions from Luziânia population. Lerin et al. (2007) compared genetic variability and chemical diversity of essential oils in Salvia spp. and they found a cluster tendency indicating a strong influence of genetic basis on the chemical composition, attributing this result to adaptations to edaphoclimatic conditions favoring some alleles at the expense of others. Our data show that a conservation program through a germplasm bank should be undertaken with the introduction of greater number of individuals from the Luziania population in relation to the other populations studied. Table 5 Genetic distance (Nei, 1978) below diagonal and geographic distance (Km) above diagonal. R UB LU CA ALT SA CR P R *** 104 425 262 94.09 18.97 354 79.90 UB 0.1162 *** 324 160 200 90.37 258 72.52 LU 0.1918 0.1386 *** 162 520 408 92.59 360 CA 0.0948 0.0935 0.1011 *** 359 247 109 200 ALT 0.0710 0.0825 0.1209 0.0633 *** 112 453 176 SA 0.0906 0.1277 0.1805 0.1142 0.1030 *** 336 67.19 CR 0.0890 0.1123 0.1049 0.0546 0.0593 0.1080 *** 283 P 0.0922 0.1548 0.1654 0.0908 0.1145 0.1171 0.0528 *** Data obtained using the software POPGENE and TRACKMAKER. Fig. 2. UPGMA dendrogram based on AFLP data, showing the genetic relationships between P. rigida accessions from Luiziânia using NTSYS software. Group A (high yields); B (medium yields); C (also presented medium contents); D (low yields) of loganin. M.dosS. da Silva et al. / Biochemical Systematics and Ecology 51 (2013) 189–194 193
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