the construction of dna barcode library for mangrove ... · the construction of dna barcode library...

1
The construction of DNA barcode library for mangrove ecosystem in China Xinnian Li, Zixiao Guo, Wei Xie, Xiaomeng Mao, Lu Liu and Suhua Shi State Key Laboratory of Biocontrol, School of Life Science, Sun Yat-Sen University, Guangzhou, China ABSTRACT Mangrove is the most characteristic ecosystem among the global wetlands, which severs as the last ecological barrier between land and sea. Mangrove ecosystem covers 60-75% of global tropical and subtropical coasts, and played key roles in ameliorating the impact of flooding, promoting sedimentation, supporting coastal food webs, and sequestering carbon. Sheltering by the woody plants that called mangrove trees, many animals live in mangrove forests, including arthropods, crustaceans, fish, mammals and birds. In the past decades, mangrove ecosystem, however, lost approximately half its area, mainly due to human disturbance and over- exploitation. There is an urgent requirement to conserve and restore the biodiversity of this valuable ecosystem, which accordingly calls for demand of fast and accurate identification of species inhabiting there. For the sake of development of DNA barcoding technology, we could resolve the contradiction between expanding need for identifying life species and reducing supply of experienced taxonomists. We thus employ this technology to build the DNA barcode library for important taxa in mangrove forests in mainland China. Supporting by the national key research and development plan, we project to collect samples and imaging records for mangrove species (37 in total in China), mangrove associate plants, benthic fauna, fungi and functional microbe across the southern china coasts from Zhejiang, Fujian, Guangdong, Guangxi to Hainan provinces. More than 300 species would be sampled and more than 2,000 barcoding sequences obtained. We also plan to acquire the super-barcodes for the 37 mangrove species using genome skimming methods. These data should provide fundament for the DNA barcode library of not only mangrove ecosystem but also the whole marine life in China. BACKGROUND The mangrove ecosystem is a rich sink for diversity in flora, fauna as well as microbial flora, making it an important biological germplasm bank. However, mangroves are largely endangered, e.g. being vulnerable to the future sea level rising and intensified coastal construction (Guo et la., 2017). For the interest of effective conservation of mangrove ecosystem, the rapid identification of species in mangrove forests is under urgent request. With the decreasing cost of DNA sequencing, genomes of mangrove species are sequenced at accelerating speed (Xu et al., 2017) for the objects including conservation. However, the DNA barcoding technology is still the ideal method for fast identification for its convenience and low cost.. This project aims to establish the DNA barcodes library for species living in mangrove forests, with key attentions paid to the mangrove plant species. Benthic fauna and functional microbe, particularly economic animals are also covered. Fig. 1 Examples of collected mangrove species. (1)Aerial view of a mangrove forest in Hainan, China. (2) Rhizophora stylosa; (3) R. mangle; (4) Aegiceras corniculatum; (5) R. apiculata; (6) R. mucronata; (7) Lumnitzera racemosa; (8) Acanthus ilicifolius; (9) Aca. ebracteatus; (10) Excoecaria agallocha; (11) Acrostichum aureum; (12) Acr. speciosum; (13) Thespecia populnea; (14) Scaevola hainanensis; (15) Nypa fruticans; (16) Cerbera manghas; (17) Barringtonia racemosa; (18) Xylocarpus granatum; (19) Sonneratia ovata; (20) S. × hainanensis; (21) Bruguiera gymnorrhiza; (22) Kandelia obovata. Fig.2 Examples of collected insect species (1) Papilio polytes; (2) Dysphania militaris; (3) Leptosia nina; (4) Rhyothemis variegate aria; (5) Ampelophaga rubiginosa; (6) Eristalinus quinquelineatus; (7) Hybomitra lasiophthalma; (8) Diplonychus esakii; (9) Sinochlora longifissa; (10) Chalcocelis albiguttatus; (11) Creatonotos gangis; (12) Phaedyma columella; (13) Anomala dimidiate. RESULTS In the series of field trips to Dongzhai Harbor, Qinglan Harbor, Tanmen, Dongchang and Sanya River estuary, we have collected 217 specimens of mangrove plant species, including 33 true mangrove, 24 semi-mangrove and nine coastal terrestrial plants. The specimens were prepared by a process of suppress, drying, disinfect, mounting and labeling, and then saved in the Herbarium of Sun Yat-Sen University. We picked used corresponding primers to amplify the chloroplast DNA regions of rbcL, trnH-psbA and matK (CBOL Plant Working Group, 2009,) as well as nuclear DNA regions of ITS1, 5.8SrRNA and ITS2 (Chen et al., 2010). Molecular experiments to amplify DNA fragments of rbcL, psbA-trnH, ITS and 5.8SrRNA were conducted with high success ratio, while much more efforts were required to amply matK. We designed three pairs of primers to amplify matK, and two of them produced products with favourable lengths ( ideally shorter than 800bp ) in some mangrove species (Table ). The primers anchoring at nuclear DNA (i.e., ITS1, ITS2 and 5.8SrRNA) were not applicable to hybrids and hybrid species, due to the high heterozygosity. We also collected 325 specimens of 145 insect species, which live in mangrove forests. For each species, two forms of specimens were made, one dry specimens was wing-spreaded for photo-recording and the other specimen was saved in alcohol for later DNA isolation. The cytochrome C oxidase subunit I (COI) (Herbert et al., 2002) was used as barcode for the insects. At this stage, 308 sequences have been identified. 1. Guo Z, Li X, He Z, et al. Extremely low genetic diversity across mangrove taxa reflects past sea level changes and hints at poor future responses. Glob Change Biol. 2017;00:1–8. https://doi.org/10.1111/gcb.13968 2. Xu, S., He, Z., et al. The origin, diversification and adaptation of a major mangrove clade (Rhizophoreae) revealed by whole genome sequencing. National Science Review. https://doi.org/10.1093/nsr/nwx065 3. CBOL Plant Working Group. A DNA barcode for land plants. PNAS. 2009, 106 (31):12794-12797. 4. Chen S, Yao H, Han, J, et. al. Validation of the ITS2 Region as a Novel DNA Barcode for identifying Medicinal Plant Species Plos ONE. 2010, 5(1): e8613. 5. Herbert P. D. N., Biological identifications through DNA barcodes. Proc. R. Soc. Lond. B. 2002. DOI 10.1098/rspb.2002.2218 Funding Sources Poster ID: 850 References

Upload: nguyenque

Post on 11-Aug-2019

234 views

Category:

Documents


0 download

TRANSCRIPT

Page 1: The construction of DNA barcode library for mangrove ... · The construction of DNA barcode library for mangrove ecosystem in China Xinnian Li, Zixiao Guo, Wei Xie, Xiaomeng Mao,

The construction of DNA barcode library for

mangrove ecosystem in ChinaXinnian Li, Zixiao Guo, Wei Xie, Xiaomeng Mao, Lu Liu and Suhua Shi

State Key Laboratory of Biocontrol, School of Life Science, Sun Yat-Sen University, Guangzhou, China

ABSTRACT Mangrove is the most characteristic ecosystem among the global wetlands, which severs as the last ecological

barrier between land and sea. Mangrove ecosystem covers 60-75% of global tropical and subtropical coasts, and played key roles in

ameliorating the impact of flooding, promoting sedimentation, supporting coastal food webs, and sequestering carbon. Sheltering by the

woody plants that called mangrove trees, many animals live in mangrove forests, including arthropods, crustaceans, fish, mammals and

birds. In the past decades, mangrove ecosystem, however, lost approximately half its area, mainly due to human disturbance and over-

exploitation. There is an urgent requirement to conserve and restore the biodiversity of this valuable ecosystem, which accordingly calls

for demand of fast and accurate identification of species inhabiting there. For the sake of development of DNA barcoding technology, we

could resolve the contradiction between expanding need for identifying life species and reducing supply of experienced taxonomists. We

thus employ this technology to build the DNA barcode library for important taxa in mangrove forests in mainland China. Supporting by the

national key research and development plan, we project to collect samples and imaging records for mangrove species (37 in total in

China), mangrove associate plants, benthic fauna, fungi and functional microbe across the southern china coasts from Zhejiang, Fujian,

Guangdong, Guangxi to Hainan provinces. More than 300 species would be sampled and more than 2,000 barcoding sequences

obtained. We also plan to acquire the super-barcodes for the 37 mangrove species using genome skimming methods. These data should

provide fundament for the DNA barcode library of not only mangrove ecosystem but also the whole marine life in China.

BACKGROUNDThe mangrove ecosystem is a rich sink for diversity in flora,

fauna as well as microbial flora, making it an important biological

germplasm bank. However, mangroves are largely endangered, e.g.

being vulnerable to the future sea level rising and intensified coastal

construction (Guo et la., 2017). For the interest of effective

conservation of mangrove ecosystem, the rapid identification of

species in mangrove forests is under urgent request. With the

decreasing cost of DNA sequencing, genomes of mangrove species

are sequenced at accelerating speed (Xu et al., 2017) for the

objects including conservation. However, the DNA barcoding

technology is still the ideal method for fast identification for its

convenience and low cost.. This project aims to establish the DNA

barcodes library for species living in mangrove forests, with key

attentions paid to the mangrove plant species. Benthic fauna and

functional microbe, particularly economic animals are also covered.

Fig. 1 Examples of collected mangrove species. (1)Aerial view of a mangrove

forest in Hainan, China. (2) Rhizophora stylosa; (3) R. mangle; (4) Aegiceras

corniculatum; (5) R. apiculata; (6) R. mucronata; (7) Lumnitzera racemosa; (8)

Acanthus ilicifolius; (9) Aca. ebracteatus; (10) Excoecaria agallocha; (11)

Acrostichum aureum; (12) Acr. speciosum; (13) Thespecia populnea; (14)

Scaevola hainanensis; (15) Nypa fruticans; (16) Cerbera manghas; (17)

Barringtonia racemosa; (18) Xylocarpus granatum; (19) Sonneratia ovata; (20) S.

× hainanensis; (21) Bruguiera gymnorrhiza; (22) Kandelia obovata.

Fig.2 Examples of collected insect species (1) Papilio polytes; (2) Dysphania

militaris; (3) Leptosia nina; (4) Rhyothemis variegate aria; (5) Ampelophaga

rubiginosa; (6) Eristalinus quinquelineatus; (7) Hybomitra lasiophthalma; (8)

Diplonychus esakii; (9) Sinochlora longifissa; (10) Chalcocelis albiguttatus; (11)

Creatonotos gangis; (12) Phaedyma columella; (13) Anomala dimidiate.

RESULTSIn the series of field trips to Dongzhai Harbor, Qinglan Harbor,

Tanmen, Dongchang and Sanya River estuary, we have collected

217 specimens of mangrove plant species, including 33 true

mangrove, 24 semi-mangrove and nine coastal terrestrial plants.

The specimens were prepared by a process of suppress, drying,

disinfect, mounting and labeling, and then saved in the Herbarium

of Sun Yat-Sen University.

We picked used corresponding primers to amplify the

chloroplast DNA regions of rbcL, trnH-psbA and matK (CBOL

Plant Working Group, 2009,) as well as nuclear DNA regions of

ITS1, 5.8SrRNA and ITS2 (Chen et al., 2010). Molecular

experiments to amplify DNA fragments of rbcL, psbA-trnH, ITS

and 5.8SrRNA were conducted with high success ratio, while

much more efforts were required to amply matK. We designed

three pairs of primers to amplify matK, and two of them produced

products with favourable lengths ( ideally shorter than 800bp ) in

some mangrove species (Table ). The primers anchoring at

nuclear DNA (i.e., ITS1, ITS2 and 5.8SrRNA) were not applicable

to hybrids and hybrid species, due to the high heterozygosity.

We also collected 325 specimens of 145 insect species, which

live in mangrove forests. For each species, two forms of

specimens were made, one dry specimens was wing-spreaded for

photo-recording and the other specimen was saved in alcohol for

later DNA isolation. The cytochrome C oxidase subunit I (COI)

(Herbert et al., 2002) was used as barcode for the insects. At this

stage, 308 sequences have been identified.

1. Guo Z, Li X, He Z, et al. Extremely low genetic diversity across mangrove taxa reflects past sea level changes and hints at poor future responses. Glob Change Biol. 2017;00:1–8. https://doi.org/10.1111/gcb.139682. Xu, S., He, Z., et al. The origin, diversification and adaptation of a major mangrove clade (Rhizophoreae) revealed by whole genome sequencing. National Science Review. https://doi.org/10.1093/nsr/nwx0653. CBOL Plant Working Group. A DNA barcode for land plants. PNAS. 2009, 106 (31):12794-12797.4. Chen S, Yao H, Han, J, et. al. Validation of the ITS2 Region as a Novel DNA Barcode for identifying Medicinal Plant Species Plos ONE. 2010, 5(1): e8613.

5. Herbert P. D. N., Biological identifications through DNA barcodes. Proc. R. Soc. Lond. B. 2002. DOI 10.1098/rspb.2002.2218

Funding Sources

Poster ID: 850

References