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International Journal of Environmental Research
University of Tehran
ISSN: 1735-6865 EISSN: 2008-2304
Vol. 1, Num. 4, 2007, pp. 321-324
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International Journal of Environmental Research, Vol. 1, No. 4, 2007, pp.321-324
Genetic study of Persian gazelle of Sohrein, Zanjan
Aeini, B. 1, Farahmand, H. 2 , Karami, M. 2* and Hartl, G. B.3
1Graduate School of the Environment and Energy, Science and Research Campus,IAU, Tehran, Iran
2College of Natural Resources, University of Tehran, Karaj, Iran
3Zoological Institute, Christian-Albrechts-University, Kiel, Germany
*Corresponding author: Email-mkarami@chamran.ut.ac.ir
Received 15 May 2007; Revised 20 July 2007; Accepted 12 Aug. 2007
Code Number: er07042
ABSTRACT
Persian gazelle (Gazelle subgutturosa) is one of the most important species in the world with its wide distribution in Iran The greatest number of this species in Iran is associated with the gazelles in Sohrain plain in Sorkhabad protected region in Zanjan province. Considering the significance of this species in the region and the fact that no genetic studies have been conducted to determine the status of this species, such genetic investigations were carried out in this study, 54 samples of the species hunted in 2005 were applied in this study. The samples were subjected for sequencing on D-LOOP region of the mtDNA. The results of this study indicated 17 polymorphism sites and 6 haplotypes in the region Haplotype type 1 and 5 with 72 and 1.85 percent presented the highest and lowest frequency in the population of gazelles. Based on the results obtained, the degree of variety of haplotypes in the population of gazelles of Sohrain region was estimated at 0.46 and nucleotide diversitywas 0.84%. Based on theresults ofthisstudyone can predict thatpopulation could be endangered owing to genetic depletion.
Key words: Mitochondrial DNA, Persion gazelle, haplotypes, Sohrein, Zanjan
INTRODUCTION
About half of the species of plants and animals
currently residing on the earth planet are expected
to become extinct in less than a century. This
drastic loss of biodiversity has been termed an
extinction spasm and it is largely the result of
anthropogenetic activity (Wright, 1977).
Conservation genetics is both a theoretical and an
applied science. Many population genetics and
quantitative genetics theories have been proposed
based on studies done on the populations of model
organisms. Ideal model organisms, such as fruit
flies and rodents, are inexpensive to maintain and
reproduce very quickly in the laboratory.
Conclusions obtained from experiments on these
model organism populations can then be applied
to endangered populations of animals found in
captivity and in the wild (Hedrick, 2001).
One objective for conservation geneticists is
to describe the genetic variation found in plants and animals. Genetic variation is critical to
maintaining the biodiversity found in species,
populations, and ecosystems and can be defined
by allelic diversity and by the percent of
heterozygosity found in a population. The percent
heterozygosity in an individual or a population
describes the number of genes or DNA regions
found that have more than one allele. An allele is
one of two or more different forms of a gene or
DNA region. A population with many different
alleles may be better capable of dealing with
changes in its surroundings such as the
introduction of a new disease. By definition,
endangered organisms have small populations and
therefore may have experienced a reduction in
the level of genetic variation found in their
populations (Conway, 2001). The objective method
of this study was investigation of intraspecific
genetic variation for (Gazella subgutturosa) Sohrein, Zanjan region. This study is based on DLOOP
for prediction of genetic depletion of this
population.
MATERIALS & METHODS
In 2005 a tissue sample was provided from the 54 gazelles in order to study DNA. After sampling out of their tissues, the samples were sent to Kiel University in Germany for genetic study purposes.
DNA extraction and purification
Total genomic DNA was isolated from the tissue of gazella. Standard procedures for isolation and purification of DNA were followed as described in Sambrook, (2002). The DNA was quantified using comparison between known concentrations of DNA and gazella genomic DNA by gel electrophoresis, and also using a spectrophotometer according to the manufacturer’s instructions (Hofer Scientific). The DNA from tissue was stored at -20°C for further analysis.
PCR condition
A PCR reaction was carried out on the gazella genome for obtained D-loop region in the mtDNA using designated primers. The 25 mL PCR reaction consisted of 10–15 ng of gazella tissue genomic DNA (template), 1X PCR buffer, 2 mM MgCl2, 0.2 mM of dNTPs, 2 pmol of each primer, and 2.5 units of Taq polymerase (AB-gene). Cycling conditions were 5 min at 948°C followed by 30 cycles of 1 min at 92°C, 1 min at 92°C, and 60 s at 58°C, and finally followed by 10 min at 72°C, using a Hybaid Omnigene Thermocycler. The PCR products were sequenced using automated sequencer ABI Prism 377.
As per the protocol QIAquik the centrifuge method was applied to purify and clean the PCR products. (Kit Protocol Company QIAquick, 2001). In brief: the products were obtained from the PCR after the investigation was made on the gel in order to determine the sequence by an automatic DNA-Sequencing so that haplotypes were specified by a study at the sequence in D-LOOP.
RESULTS & DISCUSSION
In this study 481 bp of D-LOOP region in the mtDNA were successfully isolated and sequenced. Vigorous analysis amount samples study in this region showed 17 polymorphism sites population, of which 11 of the mutations were transitions with 3.5% divergence while 6 were deletions/insertions (Table 1).
A point means, this position is identical to the first line.The number of the tissue samples extracted from 54 gazelles is shown in (Table 2) where haplotype type 1 and 5 with 72 and 1.85 percent presented the highest and lowest frequency in the population of gazelles. Haplotype diversity was 0.46 and nucleotide diversity was 0.84%. Data are indicatire of rare haplotypes.
As the above results show, the largest numbers of gazelles in the region of Sohrain, Zanjan, bear type1 of haplotypes and 72 percent ofthesegazelles have the same haplotypes (Table 3). The mitochondrial DNA D-loop is hypervariable fragment sequence which is well known molecular marker in population geneticinvestigation (Hedrick, 2004). One case study showed that fragment sequence polymorphism was examined in 27 Mongolian gazelles from Mongolia, Russia, and China. Intraspecific polymorphism of the D-loop fragment examined was demonstrated. All haplotypes described were unique.
Table 1. Genetic variability of the D-LOOPobtained in using sequencing method
Sequences |
23 |
125 |
142 |
148 |
156 |
157 |
158 |
159 |
160 |
161 |
285 |
310 |
320 |
324 |
329 |
341 |
393 |
1 |
T |
A |
G |
G |
*0 |
0 |
0 |
0 |
0 |
A |
C |
T |
T |
C |
T |
G |
C |
2 |
. |
G |
. |
. |
. |
. |
. |
. |
. |
. |
. |
. |
. |
. |
. |
. |
. |
3 |
. |
G |
A |
. |
. |
. |
. |
. |
. |
. |
. |
. |
. |
. |
. |
. |
. |
4 |
C |
. |
. |
A |
. |
. |
. |
. |
. |
0 |
T |
C |
C |
T |
C |
. |
T |
5 |
C |
. |
. |
A |
G |
G |
. |
. |
. |
0 |
T |
C |
C |
T |
C |
A |
T |
6 |
C |
. |
. |
A |
G |
G |
G |
G |
G |
0 |
T |
C |
C |
T |
C |
A |
T |
*0 is a gap
Table 2. Number of haplotypes collected from the Persian gazelle in the region of Sahrein, Zanjan
Gazelles |
Haplotypes |
39 |
1 |
1 |
2 |
1 |
3 |
7 |
4 |
1 |
5 |
5 |
6 |
Table 3. Percentage of haplotypes obtained in thepopulation of Sohrein gazelles
Percent |
Haplotypes |
72.22 |
1 |
1.85 |
2 |
1.85 |
3 |
12.96 |
4 |
1.85 |
5 |
9.25 |
6 |
The average nucleotide diversity (pi) for the mtDNA fragment investigated constituted 5.85 +/ - 2.92% .A relatively high number of insertions and deletions was observed. In particular, a haplotype with the 77-bp insertion was described. The data obtained point to high genetic diversity of Mongolian populations. There was not any correlation between the distribution of haplotypes examined and geographical location of the animal tissue sampling sites (Sorokin, et al.,2005). when we compared this result with Persian gazelles from Sohrein, Zanjan we find out that the average nucleotide diversity from Persian gazelles were 3.5% that it is very closed to Mongolian gazelles while 6 were deletions/insertions that shows low genetic diversity of Persian gazelles which is different with Mongolian gazelles. In the other study on the mitochondrial DNA (mtDNA) control region sequences from six Kenyan Grant’s gazelle (Gazella granti) populations were highly divergent among locations. A similar level of divergence separates Grant’s gazelles from a closely related species, the Soemmering’s gazelle (G. soemmeringii). Nuclear microsatellite repeat number variation at two loci also indicated substantial population genetic differentiation. Despite high levels of sequence divergence populations of Grant’s gazelles were more closely related to each other than to Soemmering’s and Thompson’s gazelles (G. thomsoni) as measured by nucleotide sequence divergence at the mtDNA protein coding cytochrome b gene and the nuclear alpha-lactalbumin gene. This pattern of extensive differentiation is hypothesized to haveresultedfrom recently established contacts between formerly allopatric populations (Arctander, 1996). According to the this issue that the same Persian gazelles can be likely found in other parts of Iran the same investigation as that one experimented above can be conducted to determine whether Persian gazelles have suffered the phenomena (allopatric) similarly to the Grant gazelles or not. Investigating other areas of mt DNA and comparing its results with other data one can find out whether in other regions exist other low genetic varieties not. Meanwhile in a study on a species of the Arabic gazelle in Saudi Arabia Using 375 base pairs of mitochondrial DNA (mtDNA) cytochrome b gene derived from museum samples collected from the wild prior to the presumed extinction of this species, we show that G. saudiya is the sister taxon of the African dorcas gazelle (G. dorcas). Reciprocal monophyly of G. saudiya mtDNA haplotypes with G. dorcas, coupled with morphological distinctiveness, suggests that it is an evolutionarily significant unit. These data indicate that captive populations identified previously as potential sources of G. saudiyafor captive breeding appear incorrectly designated and are irrelevant to the conservation of G. saudiya. The polymerase chain reaction-restriction fragment length polymorphism (PCR-RFLP) analysis of several private collections of living gazelles in Saudi Arabia provides no evidence for the survival of G. saudiya. We recommend that field surveys be undertaken to establish whether G. saudiya is indeed extinct in the wild and that other private collections within the Arabian Peninsula be screened genetically. We urge caution when captive animals of unknown provenance are used to investigate the phylogenetics of cryptic species groups (Rebert, et al., 2001).
CONCLUSION
Determining the present sequence in the area of controlling mt DNA reproduced by means of PCR technique reveal the low variety of haplotypes and nucleotides in Sohrin gazelles. The haplotypes type 1, involves 72 percent of the gazelle populations in Sohrein, Zanjan. In other words, 72 percent of the population of this species bear a similar species of haplotypes. The results of the present study on the Persian gazelle from Sohrein, Zanjan show a low genetic variety in D-LOOP but it is too soon to judge whether this species has emptied with genetic features, or not. In addition to this information we suggest studies in the field of philogenetics. However the mtDNA data should be combined with ecological knowledge befor any suggestion.
REFERENCES
- Arctander, P., Kat, P., Aman, R., Siegismund, H., (1996). Extreme genetic differences among population of Gazella granti, Grants gazelle in Kenya. Heredity, 76 (5), 465-475.
- Conway, W., (2001). Conservation Genetics Sessions Guide. Senior Conservationist, Wildlife Conservation Society. Spring Symposium, 4-5.
- Hedrick, P. W., (2001). Conservation Genetics Sessions Guide. Ullman Professor, Department of Biology, Arizona State University, Spring Symposium, 10-12.
- Hedrick, P. W., (2004). Recent development in conservation genetic. Forest Ecol. Manag. 197, 3-19.
- Rebert, L., William, M., Benito, F., Osama, B., Michael, w., (2001). Phylogenetic Reanalysis of the Saudi Gazella and Its Implications for Conservation. Conserv. Biol., 15 (4), 1123.
- Sambrook, J.,(2002). Molecular Cloning:A Laboratory Manual. Published by CSHL Press, Chapter 8.
- Sorokin, P. A., Kiriliuk, V. E., Lushchekina, A. A., Kholodova, M. V., (2005). Genetic diversity of Mongolian gazelle Procapra guttorosa. Russ. J. Genet., 41 (10), 1345-1349.
- Wright, S., (1977). Evolution and the genetics of Population.Vol3.Experimental results and evolutionary deductions.Univercity of Chicago Press.
Copyright 2007 - Graduate Faculty of Environment University of Tehran
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