Botanic gardens - science, innovation and pushing boundaries - Journal of Botanic Gardens Conservation International
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Journal of Botanic Gardens Conservation International Volume 9 • Number 1 • January 2012 Botanic gardens - science, innovation and pushing boundaries
Volume 9 • Number 1 EDITORIAL SARA OLDFIELD 02 18 EXCITING HORTICULTURAL EDITORS CHALLENGES AT THE OMAN BOTANIC GARDEN IAN OLIVER, KHALID AL-FARSI, ABDULLAH AL-HOSNI, SALIM AL-MAKMARI, SARAH KNEEBONE 03 PLANTS FOR THE FUTURE – Suzanne Sharrock Sara Oldfield A FUTURE FOR OUR PLANET Director of Global Secretary General Programmes TOWARDS A PROTOCOL FOR GENETIC MANAGEMENT OF EX Cover Photo: Royal Botanic Gardens, Kew (BGCI) Design: John Morgan, Seascape SITU LIVING PLANT COLLECTIONS 21 STÉPHANIE SAMAIN & www.seascapedesign.co.uk EDUARDO CIRES THE ASSISTED MIGRATION DEBATE – BOTANIC GARDENS TO THE RESCUE? BGjournal is published by Botanic Gardens Conservation MARIA HÄLLFORS, ELINA VAARA & International (BGCI). It is published twice a year and is sent SUSANNA LEHVÄVIRTA to all BGCI members. Membership is open to all interested individuals, institutions and organisations that support the aims of BGCI (see inside back cover for Membership application form). Further details available from: • Botanic Gardens Conservation International, Descanso House, 199 Kew Road, Richmond, Surrey TW9 3BW UK. Tel: +44 (0)20 8332 5953, Fax: +44 (0)20 8332 5956 E-mail: info@bgci.org, www.bgci.org 07 • BGCI-Russia, c/o Main Botanical Gardens, Botanicheskaya st., 4, Moscow 127276, Russia. BARCODE WALES: DNA Tel: +7 (095) 219 6160 / 5377, Fax: +7 (095) 218 0525, BARCODING THE NATION’S 25 E-mail: seed@aha.ru, www.bgci.ru NATIVE FLOWERING PLANTS AND • BGCI-Netherlands, c/o Delft University of Technology Julianalaan 67, NL-2628 BC Delft, Netherlands CONIFERS NATASHA DE VERE DREAMING OF SHEEP-EATING Tel: +31 15 278 4714 Fax: +31 15 278 2355 PLANTS MATTHEW JEBB E-mail: l.j.w.vandenwollenberg@tudelft.nl www.botanischetuin.tudelft.nl • BGCI-Canarias, c/o Jardín Botánico Canario Viera y Clavijo, Apartado de Correos 14, Tafira Alta 35017, Las Palmas de Gran Canaria, Gran Canaria, Spain. Tel: +34 928 21 95 80/82/83, Fax: +34 928 21 95 81, E-mail: jmlopez@grancanaria.es • BGCI-China, 723 Xingke Rd., Guangzhou 510650 China. Tel:(86)20-37252692. email: Xiangying.Wen@bgci.org www.bgci.org/china • BGCI-Colombia, c/o Jardín Botánico de Bogotá, 11 Jose Celestino Mutis, Av. No. 61-13 – A.A. 59887, Santa Fe de Bogotá, D.C., Colombia. Tel: +57 630 0949, Fax: +57 630 5075, E-mail: jardin@gaitana.interred.net.co, GeoCAT - AN OPEN SOURCE 28 www.humboldt.org.co/jardinesdecolombia/html/la_red.htm TOOL FOR RAPID RED LIST • BGCI(US) Inc, c/o Chicago Botanic Garden, ASSESSMENTS GROWING THE SOCIAL ROLE OF 1000 Lake Cook Road, Glencoe, Illinois 60022, USA. E-mail: usa@bgci.org, www.bgci.org/usa STEVEN BACHMAN & JUSTIN MOAT BOTANIC GARDENS BGCI BGCI is a worldwide membership organisation established in 1987. Its mission is to mobilise botanic gardens and engage partners in securing plant diversity for the well-being of people and the planet. BGCI is an independent organisation registered in the United Kingdom as a charity (Charity Reg No 1098834) and a company limited by guarantee, No 4673175. BGCI is a tax-exempt 501(c)(3) non-profit organisation in the USA and is a registered non-profit organisation in Russia. Opinions expressed in this publication do not necessarily reflect the views of the Boards or staff of BGCI or of its members 14 32 FROM FREEZING TO THE FIELD— SAFEGUARDING AUSTRALIA’S IN VITRO METHODS ASSISTING FLORA THROUGH THE PLANT CONSERVATION AUSTRALIAN SEED BANK VALERIE PENCE PARTNERSHIP LUCY SUTHERLAND 01 BGCI • 2012 • BGjournal • Vol 9 (1)
EDITORIAL CELEBRATING INNOVATION IN BOTANIC GARDENS he study and cultivation of plant botanic gardens that will be launched in T diversity by botanic gardens is firmly rooted in the past but innovative new approaches look to the May this year with an ambitious action plan to restore 100 priority sites around the world. This scheme is a response to future. Advances in science and the urgent need to prevent the further technology are providing new loss of ecosystem services and to opportunities to understand plant support international biodiversity policy diversity and develop solutions to objective. Availability of appropriate current environmental problems. This plant material is one of the prerequisites issue of BGjournal celebrates innovation for meeting this objective. Botanic in botanic gardens – pushing the gardens collectively hold around one boundaries of scientific knowledge and third of all plant species and thus its practical application. It also considers provide a vital store for restoration. the engagement of gardens with their The Australian Seed Bank Partnership visitors to share the science and make described by Sutherland is an exciting environmental knowledge more new approach strengthening Australia’s accessible and relevant to wider capacity to restore and connect audiences. landscapes and ecosystems through seed-based restoration. The paper by Scientific research has been an Samain and Cires provides an example important component of the work in of how material in collections can be botanic gardens for over 500 years. evaluated to show its appropriateness Documented plant collections continue for restoration in the wild. The authors to provide living laboratories and models remind us that to be of conservation of ecological interactions. From value, living collections must be observation of whole plants to genetic genetically representative and they and DNA analysis new techniques are describe the first comprehensive study grow all the native species of Oman is enabling deeper understanding of the of three plant groups sampled in the wild described by Oliver, Al-Farsi, Al-Hosni, plants in collections that have important and in living collections. Al-Makmari and Kneebone. implications for management of diversity in the wild. The application of new Restoration needs to take into account I hope you enjoy the richness of ideas techniques for identifying plant species changing climatic conditions and the presented in this issue of BGjournal! is described by de Vere; for somewhat controversial question of BGCI will strive to share the best of documenting their conservation status assisted migration is tackled by Hallfors, botanic garden innovations, and at times by Bachman and Moat, for conserving Vaara and Lehvavirta in their article that provocative, ideas. Please let us know in vitro by Valerie Pence and highlights the responsibility, skills and your thoughts and ideas for future communicating with the public by opportunities that botanic gardens have debate as we collectively secure planet Matthew Jebb. in this emerging field. diversity for people and the planet. The ex situ collections of plant material The creation of new botanic gardens and expertise within botanic gardens are allows the opportunity for research to increasingly being used to support be fully integrated with garden design, species reintroduction and ecological management of living collections, restoration programmes. BGCI is education and training from the outset. currently involved in the development of Exciting progress is the development of Sara Oldfield the Ecological Restoration Alliance of the Oman Botanic Garden that aims to Secretary General, BGCI 02 BGCI • 2012 • BGjournal • Vol 9 (1) • 02
Authors: Stéphanie Samain and Eduardo Cires PLANTS FOR THE FUTURE – A FUTURE FOR OUR PLANET TOWARDS A PROTOCOL FOR GENETIC MANAGEMENT OF EX SITU LIVING PLANT COLLECTIONS There is an urgent need for worldwide assessment of Introduction genetic diversity of ex situ living plant collections and t is estimated that one third of all plant comparison with wild populations, especially for I species are threatened with extinction and yet plants continue to be underrepresented in conservation threatened species. The Botanical Garden of Ghent debates and policies. However, global initiatives, such as the Global Strategy University, Belgium is addressing this need. for Plant Conservation (GSPC) are aiming to bring a significant change. As stated in Target 8 of the GSPC, at least 75% of threatened plant species should be present in ex situ collections. Botanical gardens play a key role in conservation of plant diversity, but only about 30% of globally threatened plant species are currently held in their living collections (Oldfield, 2010). To be of conservation value, living collections must be genetically representative. Although information on genetic diversity in ex situ collections is scarce, it is thought that diversity is low in collections of numerous species. Moreover, besides the many studies and initiatives for specific taxa, our knowledge about the genetic diversity of threatened plant species in general is quite limited. This lack of insight into genetic diversity of threatened wild plant species contrasts with the broad knowledge about crops and their wild relatives. This fact is also reflected by GSPC Target 9, which specifically states that 70% of the genetic diversity of crops, including their wild relatives and other socio-economically valuable plant species, should be conserved. We still have a long way to go to understanding genetic diversity in threatened plants, conserving an important part of this diversity in ex situ collections, defining which percentage of genetic diversity Esteban Martínez climbing a tree to collect a newly discovered Hydrangea species on the volcano Tacaná in might be feasible and/or desirable to aim Chiapas state in southeast Mexico near the border with Guatemala. Stems with leaves of this species are for, and finally making this available for visible on all the trunks (Marie-Stéphanie Samain). conservation and restoration projects. 03 BGCI • 2012 • BGjournal • Vol 9 (1) • 03-06
Angiosperm groups with different life histories and growth forms. A range of genomic tools will be applied to wild and ex situ individuals of selected species of the flagship groups Hydrangea, Magnolia and Cactaceae to enable rapid characterization of genetic variation, providing 1) support for specific conservation actions, and 2) general guidelines and a protocol on genetic management for acquiring accessions for ex situ collections, in order to be used by collectors and botanical gardens worldwide in the framework of the achievement of Target 8 of the GSPC. Sampling and lab work A happy team of botanists and local children after discovering a new Hydrangea species on the volcano The three plant groups being studied are Tacaná in Chiapas state in southeast Mexico near the border with Guatemala (Paco Najarro). considered as priority groups for BGCI, the IUCN/SSC Global Trees Specialist Setting the stage habitat destruction narrowing genetic Group and the International Organization diversity and subsequent evolution for Succulent Plant Study (IOS), with The GSPC 2011-2020 states that: (= genetic erosion), 2) collection bias whom we cooperate. These groups are (‘easy’ localities, selection of rather well-studied taxonomically and morphological variation which is not are also very important in the “ Without plants there is no life. The functioning of the planet, and our survival, depends necessarily reflected by genetic variation), 3) cultivation bottleneck (accessions dying because of unsuitable conditions). horticultural trade, with especially Cactaceae also suffering from illegal harvest and trade. Despite the fact that Hence, the establishment of a protocol these groups are a priority for upon plants. ” Achieving Target 8 of the GSPC depends on the existence of genetically guiding genetic management during the different steps (wild population – ex situ collection – reintroduction) is essential for implementation of Target 8 of the GSPC conservation, the genetic diversity within ex situ collections is almost entirely unknown, and has not been compared with wild populations. There is clearly an representative collections, and these are and, ultimately, for safeguarding the urgent need for this research. essential for recovery and restoration future of our planet. work. Our focus should therefore be on assessing and ensuring the conservation Towards an assessment for value of ex situ collections (Sharrock et flagship groups: Hydrangea, al., 2010). Magnolia and Cactaceae Assessments of a representative sample The Botanical Garden and the Research of plant species will provide a basis for Group Spermatophytes of Ghent an initial estimation of a baseline, and to University (Belgium) are increasingly monitor progress towards this target. involved in conservation of the plant Therefore, toolkits under this target need groups which are housed in their living to include protocols for genetic collections and studied in ongoing management of ex situ collections and projects, such as Peperomia (Samain et consequent reintroductions. al., 2010), Hydrangea (Red List project in cooperation with BGCI, including a One of the suggested milestones to serve specific conservation project in Mexico), as a step towards the 2020 target is that and Aristolochia (Rivera Hernández & ex situ collections of all critically Samain, 2011). Our strategy, to combine endangered species should be fundamental botanical research with genetically representative of the species conservational efforts, has also led to the (SBSTTA, 2010). However, preliminary establishment of a project, initiated in observations and data suggest that this 2011, which will be continued and currently is not the case in many accelerated thanks to the support of the collections, as the genetic diversity from Fondation Franklinia. Within this project wild population to ex situ collections we aim to compare genetic diversity ‘gradually’ decreases (= genetic between wild populations and ex situ Collecting Hydrangea aspera with local botany students bottleneck) as a consequence of 1) collections of three unrelated on mountain Taiping Shan, Taiwan ( Eduardo Cires). 04 BGCI • 2012 • BGjournal • Vol 9 (1)
Characteristic RFLP Microsatellite AFLP ISSR PCR sequencing Genomic abundance High Medium Very high Medium Very high Part of genome surveyed Low copy coding regions Whole genome Whole genome Whole genome Whole genome Amount of DNA required High Low Medium Low Low Type of polymorphism Single base changes, Changes in length Single base changes, Single base changes, Single base changes, insertion, deletion of repeats insertion, deletion insertion, deletion insertion, deletion Level of polymorphism Medium High Very high High Very high Inheritance Codominant Codominant Dominant Dominant – Ease of use Labour intensive Easy Difficult initially Easy Easy Automation possible Low High Medium Medium High Cost of automation High High High Medium High Development costs Medium High Low Low High Reproducibility (reliability) High High High Medium to high High Level of training required Low Low/Medium Medium Low High Cloning and/or sequencing Yes Yes No No Yes Radioactive detection Yes/No Yes/No Yes/No No Yes/No Proprietary rights status No No (some licensed) Licensed Licensed No (some licensed) Table 1. Comparative assessment of some of the salient characteristics of different molecular genetic screening techniques: RFLP (or Restriction fragment length polymorphism), Microsatellites or simple sequence repeats (SSRs), AFLP (or Amplified fragment length polymorphism), ISSR (or Inter Simple Sequence Repeat) and PCR sequencing. “ Around one-third of the much reduced, but we believe it is not Field work has already been or will be useful to include samples without performed in countries and areas where globally threatened species that documented origin, as their value, for the Research Group has extensive field are found in botanic garden example in reintroduction projects, is experience and local cooperation highly doubtful. Additionally, Magnolia partners (Latin America and East Asia). collections are recorded in only and Hydrangea individuals are plants Within the wild populations, a ” one collection. with life spans of several hundred years, representative sample of individuals will predating fragmentation events, so we be collected, meanwhile in the ex situ will obtain reliable genetic information collections we aim to include an equal Global and/or local Red Lists are that may help genetic restoration number of accessions from as many available for each group (Magnolia: projects (e.g. López et al., 2008). gardens as possible. In addition, our Cicuzza et al., 2007; Cactaceae: e.g. work on Hydrangea will also help to build IUCN, 2011) or are being prepared Availability in botanical garden collections new living collections, e.g. in Mexico, (Hydrangea s.l.). These groups represent has been checked via the PlantSearch supported by the Mohamed Bin Zayed different unrelated families of module on the BGCI website Species Conservation Fund. Angiosperms, with different habitat (http://www.bgci.org/plant_search.php) or Molecular tools provide valuable data on preferences and a range of life history via direct and ongoing communication diversity through their ability to detect traits. Within each group, taxa are with gardens. A final selection criterion is variation at the DNA level. Identification selected based on: 1) presence in a that most of the species are ‘Vulnerable’, is of fundamental importance in diversity representative number of public and ‘Endangered’ or ‘Critically Endangered’ studies in a variety of different ways. For accessible private ex situ collections according to IUCN Red List categories evaluation of species diversity, it is (botanical gardens, arboreta, etc.), 2) and criteria, hence they are priority essential that individuals can be well-documented origin of the species for conservation and for use in classified accurately. The identification of accessions, and 3) availability of material recovery and restoration work. taxonomic units and endangered verified by specialists. Because of the Furthermore, the genetic diversity of these species, whose genetic constitution is second criterion, the quantity of useful rare species will be compared with some distinct from their more abundant accessions available for the research is more common or widespread species. relatives, is important in the development of appropriate conservation strategies. Taking advantage of current molecular techniques, relatively quick assessments Try another molecular Did we detect enough Can we divide the population of genetic diversity in plants can be No Yes marker and/or primers genetic variability? into k independent groups performed using well-sampled material a priori? and ready-made protocols, as long as the most limiting factor, funding, is Yes available. For each flagship species, No Flow chart representing the different molecular techniques (e.g. main strategies to assess RFLP, microsatellites, AFLP, ISSR, PCR the genetic diversity in the Are these groups sequencing) are currently being tested Yes consistent with the No flagship groups studied. Reinforcing the sampling and/or developed, with comparisons of genetic parameters? cost versus data yielded, ease of use, Asian populations and applicability for conservation American populations Identification of priority Choose those n populations to be ex situ populations which best conserved represent each group BGCI • 2012 • BGjournal • Vol 9 (1)
research (Table 1). For the elaboration of conserved), 4) indication of the number these techniques, either in-house of samples that needs to be collected in experience has been developed or the wild to obtain a genetically collaboration with experienced research representative collection, 5) testing the groups has been set up. hypothesis that endangered species with narrow distribution are genetically Outlook – Connecting the dots limited, 6) conservation of flagship species, and finally, 7) reports and To our knowledge, this is the first publications in cooperation with e.g. comprehensive study of this kind, with a BGCI, the IUCN/SSC Global Trees constant evaluation of the different Specialist Group and the IOS. techniques, in order to assess the Last but not least, it has already become progress of the project (see Figure 1). clear during this pilot year 2011 that this Marie-Stéphanie Samain preparing herbarium The expected results can be subdivided study will lead to further international specimens of a new Hydrangea species of Los in two levels: i) specific results for each cooperation with many interested Tuxtlas, state of Veracruz, Mexico (Esteban Martínez). group: they will provide insight into gardens and researchers. genetic diversity and history, providing a , López, D.M., Bock, B.C. and Bedoya, basis for further conservation work; ii) G. 2008. Genetic structure in remnant comparison of different unrelated groups with different life histories and growth forms: this approach will lead to a “ We expect to form a scientific network studying genetic diversity in plants for populations of an endangered Andean Magnolia. Biotropica 40: 375-379. general overview of the genetic diversity , Oldfield, S. 2010. Plant conservation: available in wild populations and ex situ conservation purposes under the facing tough choices. Bioscience 30: collections, as well as of the specific 778-779. problems involved with decreasing genetic diversity from the wild to the collection, information which will be auspices of BGCI. ” Please feel free to contact us if you , Rivera Hernández, J.E. and Samain, M.S. 2011. Where has Aristolochia extremely useful for implementation of would like to cooperate, exchange tricaudata (Aristolochiaceae) gone? Target 8 of the GSPC. experiences, or if you have comments New record of a critically endangered or questions. species in Oaxaca, Mexico. Revista Some important specific outcomes are Mexicana de Biodiversidad 82: 281- listed here: 1) assessment of percentage References 286. of genetic diversity present in ex situ collections worldwide for the three plant , Cicuzza, D., Newton, A. and Oldfield, , Samain, M.S., Dugardin, C. and groups under study, 2) identification of S. 2007. The red list of Magnoliaceae. Goetghebeur, P. 2010. Peperomia priority populations for ex situ Fauna & Flora International. reference collection: an ex situ living conservation, 3) definition of a Cambridge, UK. plant collection for scientific research. genetically representative collection Proceedings of the 4th Global Botanic (compared to Target 9 of the GSPC , IUCN, 2011. IUCN red list of Gardens Congress, June 2010. stating that 70% of the genetic diversity threatened species. of crops and other socio-economical http://www.iucnredlist.org/ (Accessed , SBSTTA, 2010. Progress in the valuable plant species should be January 2012). implementation of Global Strategy for Plant Conservation and development of a consolidated update beyond 2010. UNEP/CBD/SBSTTA/14/INF/16. , Sharrock, S., Hird, A., Kramer, A. and Oldfield, S. (Comp.) 2010. Saving plants, saving the planet: Botanic Gardens and the implementation of GSPC Target 8. BGCI, Richmond, UK. Marie-Stéphanie Samain and Eduardo Cires Ghent University Research Group Spermatophytes & Botanical Garden K.L. Ledeganckstraat 35 B-9000 Gent E-mail: MarieStephanie.Samain Mountain Wawu Shan, Sichuan, China, location of several Hydrangea specimens (Eduardo Cires). @UGent.be 06 BGCI • 2012 • BGjournal • Vol 9 (1)
Author: Natasha de Vere BARCODE WALES: DNA BARCODING THE NATION’S NATIVE FLOWERING PLANTS AND CONIFERS DNA-based identification systems can help to identify and monitor species and provide a platform for a wide range of applications where accurate species identification is required. DNA-barcoding at the NBGW laboratory. he ability to identify plant species Correct identification is also vital in order DNA barcoding uses short sections of DNA T is fundamental to our understanding of the world around us. To conserve plants, their habitats and for us to use plants for food, medicine or materials. Identification of plants often relies on morphological examination, but to act as a unique identifier for species. The aim of DNA barcoding is to have global agreement on the regions of DNA and ecosystems we need to be able to around the world there is a shortage of protocols used for different groups of living identify and monitor species. taxonomic experts able to identify things in order to create an international species. Beyond this, it is often desirable resource for species identification. To begin to be able to identify species from with, reference DNA databases are “ Objective 1 of the Global Strategy for Plant Conservation is that: “plant diversity is well material where morphological approaches are difficult or impossible to use; for example, from pollen, roots, developed using species identified by a taxonomic expert; unknown DNA sequences can then be compared to these seeds, or fragments of tissue. In these to make an identification. Open Science is understood, documented and situations DNA-based identification key, DNA barcodes, their associated systems can be used and in 2003 Paul information and protocols for their recognized. ” Hebert coined the term ‘DNA barcoding’ (Hebert et al., 2003). development should be available to everyone, from researchers, regulatory authorities to the general public. 07 BGCI • 2012 • BGjournal • Vol 9 (1) • 07-10
barcodes need to have access to this information, along with a scan of the herbarium voucher. Where fresh material is collected for DNA barcoding an associated herbarium voucher must always be made. The only exception to this is for endangered species where creating a voucher is not possible on conservation grounds; in this case a photograph is used instead. We also need to DNA barcode more than one specimen for each species to allow for errors and any variation between individuals within the species. The level of variation within the species should be low however, as the idea behind DNA barcoding is to use regions of DNA that Tephroseris integrifolia ssp. maritima. differ between species but which are the same within a species. For our Barcode There are now initiatives throughout the bryophytes and at the National Botanic Wales project we aim to DNA barcode at world for DNA barcoding species from all Garden of Wales, we are DNA barcoding least three samples for each species of the kingdoms of life, such as the the native flowering plants and conifers using the DNA barcode markers rbcL International Barcode of Life initiative of Wales, with our partners at the and matK. (IBOL), which works across 25 countries National Museum Wales (Hollingsworth and aims to DNA barcode 5 million et al., 2011). Over the last three years we have specimens from 500,000 species within sampled 4,272 plant specimens, 3,637 five years. The Consortium of the from the National Museum Wales Barcode of Life (CBOL) is devoted to promoting DNA barcoding as a global standard for DNA-based species “ Botanic gardens are increasingly using DNA barcoding as an identification tool for plants herbarium (NMW) and 635 freshly collected from throughout Wales. We have 5,723 DNA barcodes, 3,304 for identification and the Barcode of Life rbcL and 2,419 for matK. Of the 1,143 Data System (BOLD) provides a key repository for DNA barcodes and their associated data (Ratnasingham and Hebert, 2007). In 2009, the Plant Working in their collections. Barcode Wales ” species of Wales we have DNA barcoded 98% using rbcL and 90% with rbcL and matK. Our first scientific publication describing our results and Group of CBOL proposed two sections of Wales has 1,143 native and protocols will be available soon (de Vere genes within the chloroplast genome, archaeophyte (species introduced before et al., in press) and all of our DNA rbcL and matK, for plant DNA barcoding, 1500 AD) flowering plants and conifers, barcodes, along with their associated with the suggestion that more markers found within 455 genera, 95 families and collection information and scans of their may be required (CBOL Plant Working 34 orders. In order to create a reference herbarium vouchers will be accessible Group, 2009). In December 2011 the database of DNA barcodes for these, it shortly on the Barcode of Life Data nuclear gene ITS was announced as the is vital to start with correctly identified System in the Plants of Wales project. official barcode for fungi during the 4th source material. Taxonomist, Dr Tim International Barcode of Life Conference Rich, from the National Museum Wales is in Adelaide, Australia. responsible for checking every species that we DNA barcode. We have Projects are now underway to DNA concentrated on using herbarium barcode the world's plant species. For specimens for DNA barcoding. The example, the New York Botanic Garden herbaria of the world provide an is DNA barcoding the world's trees, incredibly valuable resource of plant whilst the Universities of Adelaide and species that have been collected and British Columbia are working on grasses. identified by expert taxonomists. We Some projects are concentrating on have developed special protocols for floristic regions: Korea University is extracting DNA from herbarium working on the flora of Korea, the specimens to make full use of this University of Johannesburg on the flora resource. of the Kruger National Park, the Smithsonian Institute on tropical forestry For the resulting DNA barcodes to be of plots and institutions throughout China most use, it is very important that along are working together to DNA barcode with the DNA sequence there is a full their flora. The Royal Botanic Garden record of when, where and by whom the Edinburgh is DNA barcoding British plant was collected. All users of the DNA The herbarium at the National Museum of Wales. 08 BGCI • 2012 • BGjournal • Vol 9 (1)
The Barcode Wales project provides a al., 2011). DNA sequences obtained for Many of our applications use ‘next valuable resource for researchers wanting DNA barcoding have also been used to generation’ DNA sequencing as this to identify species using DNA-based create phylogenetic trees for allows us to analyse samples containing approaches. Our DNA barcodes for Wales phylogenetic community ecology mixtures of plant species. Our PhD also provide a stock of barcodes that can research (Kress et al., 2009). student, Hannah Garbett, co-supervised be incorporated into other projects. The by Dr Tatiana Tatarinova (Glamorgan 1,143 species of Wales represents 77% of At the National Botanic Garden of Wales University) is developing bioinformatic the native flowering plants of the UK. We we have started to develop applications tools that will help to analyse these large have just begun DNA barcoding the rest that use our DNA barcodes for Wales in and complicated datasets. As well as of the UK flora, working with the Royal collaboration with partners around the using our DNA barcodes for species Botanic Garden Edinburgh. world. We have worked with Dr Sandra identification we are working with Prof. Ronca (Aberystwyth University) and Prof. Pete Hollingsworth (Royal Botanic Mike Wilkinson (University of Adelaide) Garden Edinburgh) to create the first “ Once the native flora of the UK is complete we will begin on to track the movements of pollinators in threatened habitats by DNA barcoding pollen found on their bodies. We are complete national phylogeny of the flowering plants of the UK. the non-native species. Applications ” working with Dr Joel Allainguillaume (University of the West of England) to use DNA barcoding to carry out Public engagement DNA barcoding is not only a resource for ecological surveys and Dr Neil Loader scientists; it is also an excellent way to The range of applications using plant (Swansea University) on reconstructing engage people with their native flora and DNA barcoding is as broad as our landscapes from plant remains in peat plant sciences research. At the National imaginations, with some great cores. We are also using our DNA Botanic Garden of Wales we are applications already being developed. barcodes for human health in a project particularly interested in projects that link Ecological applications include with Jenny Hawkins and Prof. Les Baillie arts and science. We have worked with understanding below-ground biodiversity of the Welsh School of Pharmacy (Cardiff botanical artist, Emma Tuck, on a by DNA barcoding roots (Kesanakurti et University). For her PhD research, Jenny contemporary art exhibition and al., 2011), reconstructing past is collecting honey samples from community artist, Pod Clare, on a landscapes using plant remains throughout the UK and testing their Barcode Wales mosaic created by (Sonstebo et al., 2010) and identifying ability to fight the hospital infections community groups from throughout invasive species (Bleeker et al., 2008). MRSA and Clostridium difficile. She will Wales. We are currently working with DNA barcoding has been used to verify then DNA barcode the honey to find out Prof. Andrea Liggins (Swansea the contents of plant products including what plant species the bees visited to University) on a photographic exhibition medicinal plants (Chen et al., 2010), make it. We hope to use this to pinpoint to be shown in botanic gardens and berries (Jaakola et al., 2010), olive oil active phytochemicals donated by the universities throughout China on native (Kumar et al., 2011), tea (Stoeckle et al., plant species that contribute to the Welsh plants and their DNA barcodes. 2011) and kitchen spices (De Mattia et honey’s anti-microbial properties. Collecting specimens for DNA barcoding. 09 BGCI • 2012 • BGjournal • Vol 9 (1)
Barcode Wales is also a mechanism for training the next generation of plant scientists. The workforce assembling the DNA barcodes for the Barcode Wales and Barcode UK projects are undergraduate students who spend a year at the Garden as part of their degree. Their work is supplemented with work experience students from A-level to postgraduate who spend from two weeks to a few months at the Garden. The Barcode Wales project provides the Emma Tuck’s Decode exhibition at NBGW. most complete coverage of DNA barcodes of any national flora, offering a and Wilkinson, M.J. (in press) DNA Proceedings of the National Academy platform for a wide range of applications barcoding the native flowering plants of Sciences of the United States of where accurate species identification is and conifers of Wales. Plos One. America 106: 18621-18626. required. It also provides a hub for multi- disciplinary research across the arts, , Hebert, P.D.N., Cywinska, A., Ball, , Kumar, S., Kahlon, T., and Chaudhary, sciences and social sciences and a S.L., and DeWaard, J.R. 2003. S. 2011. A rapid screening for vehicle for training plant science Biological identifications through DNA adulterants in olive oil using DNA students and volunteers. The DNA barcodes. Proceedings of the Royal barcodes. Food Chemistry 127: 1335- barcodes and their associated Society of London Series B-Biological 1341. information are Open Access to make a Sciences 270: 313-321. resource available to everyone. , Ratnasingham, S., and Hebert, P.D.N. , Hollingsworth, P.M., Graham, S.W., 2007. BOLD: The Barcode of Life Data References and Little, D.P. 2011. Choosing and System (www.barcodinglife.org). Using a Plant DNA Barcode. Plos One Molecular Ecology Notes 7: 355-364. , Bleeker, W., Klausmeyer, S., 6: e19254. Peintinger, M., and Dienst, M. 2008. , Sonstebo, J.H., Gielly, L., Brysting, A.K., DNA sequences identify invasive alien , Jaakola, L., Suokas, M., and Elven, R., Edwards, M., Haile, J., Cardamine at Lake Constance. Haggman, H. 2010. Novel approaches Willerslev, E., Coissac, E., Rioux, D., Biological Conservation 141: 692-698. based on DNA barcoding and high- Sannier, J., Taberlet, P., and Brochmann, resolution melting of amplicons for C. 2010. Using next-generation , CBOL Plant Working Group. 2009. authenticity analyses of berry species. sequencing for molecular reconstruction A DNA barcode for land plants. Food Chemistry 123: 494-500. of past Arctic vegetation and climate. Proceedings of the National Academy Molecular Ecology Resources 10: 1009- of Sciences of the United States of , Kesanakurti, P.R., Fazekas, A.J., 1018. America 106: 12794-12797. Burgess, K.S., Percy, D.M., Newmaster, S.G., Graham, S.W., , Stoeckle, M.Y., Gamble, C.C., Kirpekar, , Chen, S., Yao, H., Han, J., Liu, C., Barrett, S.C.H., Hajibabaei, M., and R., Young, G., Ahmed, S., and Little, D.P. Song, J., Shi, L., Zhu, Y., Ma, X., Gao, Husband, B.C. 2011. Spatial patterns 2011. Commercial Teas Highlight Plant T., Pang, X., Luo, K., Li, Y., Li, X., Jia, of plant diversity below-ground as DNA Barcode Identification Successes X., Lin, Y., and Leon, C. 2010. revealed by DNA barcoding. Molecular and Obstacles. Sci. Rep. 1: 42. Validation of the ITS2 Region as a Ecology 20: 1289-1302. Novel DNA Barcode for Identifying Natasha de Vere Medicinal Plant Species. Plos One 5: , Kress, W.J., Erickson, D.L., Andrew National Botanic Garden e8613. Jones, F., Swenson, N.G., Perez, R., of Wales Sanjur, O., and Bermingham, E. 2009. Llanarthne, Carmarthenshire, , De Mattia, F., Bruni, I., Galimberti, A., Plant DNA barcodes and a community SA32 8HG, UK Cattaneo, F., Casiraghi, M., and Labra, phylogeny of a tropical forest Email: ndevere@gardenofwales. M. 2011. A comparative study of dynamics plot in Panama. org.uk different DNA barcoding markers for the identification of some members of Lamiacaea. Food Research Further information International 44: 693-702. National Botanic Garden of Wales http://www.gardenofwales.org.uk/science/barcode-wales/ , de Vere, N., Rich, T.C.G., Ford, C.R., Consortium for the Barcode of Life http://www.barcodeoflife.org/ Trinder, S.A., Long, C., Moore, C.W., International Barcode of Life Initiative http://ibol.org/ Satterthwaite, D., Davies, H., Barcode of Life Data System http://www.boldsystems.org Allainguillaume, J., Ronca, S., 4th International Barcode of Life Conference http://www.dnabarcodes2011.org Tatarinova, T., Garbett, H., Walker, K. 10 BGCI • 2012 • BGjournal • Vol 9 (1)
Authors: Steven Bachman and Justin Moat GeoCAT - AN OPEN SOURCE TOOL FOR RAPID RED LIST ASSESSMENTS The combination of botanical collection data and the latest web mapping technology is providing better tools to support the work of conservation scientists. The Royal Botanic Gardens, Kew have developed GeoCAT – the Geospatial Conservation Assessment Tool - to help ease and speed up the process of Red List assessment for plants. Plants and the Red List There are as many as 380,000 species of plants presently known and he IUCN Red List is well known to around a thousand new species are T many as the most authoritative source of information on extinction risk for the world’s organisms. The annual described as new to science every year1. There are more species in a single family of plants such as grasses (Poaceae) than release highlights the familiar creatures: the polar bear, the orang-utan, the rhino, the gorilla - the celebrity species of the there are all known mammals (5,488). With that in mind it is no wonder that so far only around 4% of the world’s flora have “ Only around 4% of the world’s plants have been assessed for their conservation conservation world. And each year we are been assigned a category of threat on the reminded again that many species are slipping toward extinction, usually as a result of pressures from human activities. global Red List. Although significant activity on Red Listing for plants is taking place around the world, often in botanic status at the global level. ” resources into practical conservation But when was the last time you remember gardens, the sheer scale of the task is effort if we don’t know where or what to a species of plant being mentioned? All daunting. focus on? The good news is that too often plants fall under the radar when progress is being made. Not only is raw it comes to the Red List, although they are Despite attempts from the botanical information on plants becoming being assessed and they are as community to accelerate the production increasingly available through data threatened as the ‘better known’ groups of Red List assessments, such as the sharing platforms such as the Global such as mammals (see the Sampled Red ambitious Target 2 of the Global Strategy Biodiversity Information Facility (GBIF), List Index – Plants Under Pressure a for Plant Conservation2 ‘an assessment but automated and semi-automated global assessment 2010). So why is there of conservation status of all known plant tools are now available to allow such a shortfall? The sheer number of species’ we are still falling short. The scientists and experts to harness that species, in comparison to the number of implications of this are very significant. data to answer important questions like available scientists, is the main problem. How can we even begin to focus our – how endangered is my species? 11 1 http://www.ipni.org/stats.html BGCI • 2012 • BGjournal • Vol 9 (1) • 11-13 2 http://www.plants2020.net/gspc-targets/
With these powerful analytic tools we can more rapidly assess species and more effectively prioritise conservation action. With the development of tools such as GeoCAT, the target of assessing all species may just become more achievable. Introducing GeoCAT The Royal Botanic Gardens, Kew has long been associated with the Red List process, being key players in the development of the original Red Data books of endangered plants and continuing with major contributions of plant assessments to the present day Red List. The Geographical Information Systems (GIS) Unit at Kew has a more Screenshot from GeoCAT – illustrating multiple data sources, and the metadata window allowing you to view specific interest in the application of GIS the underlying data for each point. techniques for Red List assessment, in particular the geographic components of GeoCAT is a rapid assessment tool that Geographic range measures an assessment. Innovations within the utilises primary plant occurrence data to used in the Red List field of GIS over the last few decades produce measurements relating to the have allowed for the first time the geographic range of a species. These One aspect of Red Listing that has been production of tools to aid Red List are then compared with the IUCN Red particularly challenging so far is the assessment such as the CAT List categories and criteria and provide calculation of geospatial measurements (Conservation Assessment Tools) evidence to support a full Red List included in the criteria – in other words project3. Released in 2007, CAT is an assessment. It is important to note that it criteria related to the geography of a extension to the ArcView GIS software is an expert driven system i.e. it is species. Geospatial aspects of the Red system and allows automatic calculation assumed that the user of the tool has List criteria mostly relate to Criterion B - of measures used in Red List good knowledge of the species being Geographic Range, but also appear as assessment. With the recent explosion of assessed as well as a thorough elements throughout the other web mapping innovations such as understanding of the Red List categories categories A – D. Two different measures Google Earth and Google Maps it was and criteria (IUCN 2001). of geographic range: extent of clear that these conservation tools needed to be brought into this new era, which led to the development of GeoCAT. GeoCAT (accessible at this URL: http://geocat.kew.org/) is a web based tool developed through a collaboration of the Royal Botanic Gardens, Kew, IUCN and ViBRANT that supports the Red Listing process. If you want a quick way to find out more you can watch the video here: http://vimeo.com/22739331. The GeoCAT home page - http://geocat.kew.org/. Screenshot of extent of occurrence (EOO) and area of occupancy (AOO) analysis. When the analysis is enabled the results are displayed showing area in km2 and corresponding Red List category. 3 http://www.kew.org/science-research-data/kew-in- 12 depth/gis/resources-and-publications/tools/cat/ BGCI • 2012 • BGjournal • Vol 9 (1)
occurrence (EOO) and area of • Upload your own data - where assessment. Perhaps then we will see occupancy (AOO) are used in the Red occurrence data has already been plants in the spotlight for the next edition List criteria. Extent of occurrence (EOO) gathered, for example, in a specimen of the Red List. is a measure of the geographic range database or spreadsheet, it is size of a species. IUCN guidelines possible to import this data directly to References suggest a minimum convex polygon the map editor. Data simply needs to (MCP) can be used to calculate this be converted to comma separated , Bachman, S., Moat, J., Hill, A.W., value. A MCP is defined as the smallest values format following a standard de la Torre, J. and Scott, B. 2011. polygon in which no internal angle structure. Supporting Red List threat exceeds 180˚ and contains all sites of assessments with GeoCAT: geospatial occurrence. This value represents the • Manual add - you may have specific conservation assessment tool. spread of risk for a species such that knowledge regarding the distribution ZooKeys 150: 117–126 doi: species with a large extent will be more of a species. The user can add points 10.3897/zookeys.150.210 robust to threatening processes. An directly to the map with a single click. alternative approach for depicting a , Brummitt, N., Bachman, S.P. and species range is to show the area where With data on the map the user can then Moat, J. 2008. Using the Red List as a species occurs or area of occupancy edit by adjusting points, removing them a barometer for plant diversity. (AOO). A simple way to measure this and by examining the original data e.g. Endangered Species Research. value is to overlay the distribution with a inspecting a Flickr image to see if it really doi: 10.3354/esr0013 grid and sum the area of square grid is the species it is labelled as. From here, cells the species occupies at the click of a button the analysis can , IUCN. 2001. IUCN Red List Categories be enabled. Based on the points on the and Criteria: Version 3.1. IUCN How it works - calculating map, the extent of occurrence (EOO) and Species Survival Commission. IUCN, geographic range of species for area of occupancy (AOO) values are Gland, Switzerland and Cambridge, Red List assessments instantly calculated and the values are UK: 30 p compared with the thresholds set in the GeoCAT is driven by primary occurrence IUCN Criteria. For example if the extent , Plants under pressure a global data. For hundreds of years botanists is less than 5,000 km2 then it meets the assessment. The first report of the have been travelling to the ends of the threshold for the Endangered (EN) IUCN Sampled Red List Index for earth to take cuttings from plants as category. From here a simple report can Plants. Royal Botanic Gardens, Kew, scientific specimens. Herbarium be generated and the data can be saved UK. 2010 specimens are verifiable records that or exported to other formats such as http://www.kew.org/science- show where and when a particular KML for visualisation in other packages conservation/search-rescue/mapping- species was collected. By combining such as Google Earth. As mentioned plants/plants-at-risk/index.htm these records at the species level we previously it should be noted that this immediately have an indication of the does not represent a full Red List Steve Bachman and Justin Moat geographic range of a species and it is assessment, it provides evidence that Royal Botanic Gardens Kew, this data that GeoCAT analyses to fulfils part of the criteria. Richmond, determine the two measures of extent of Surrey occurrence (EOO) and area of occupancy Impact and benefits TW9 3AB, (AOO). A benefit of GeoCAT is that as UK well as data being provided by the user GeoCAT is a good example of the Email: s.bachman@kew.org e.g. from a database of their own innovative work presently being carried specimens, it can also be imported from out in botanic gardens, in this case to existing online sources such as GBIF and directly support plant conservation. Flickr. The images in Flickr need to be Specifically GeoCAT provides the labelled with the species name and potential to speed up the Red Listing ‘geotagged’ or ‘georeferenced’ i.e. process for plants and offers hope that assigned a latitude and longitude co- global targets such as the Global ordinate so we know where it was taken. Strategy for Plant Conservation may be reached. By utilising existing data it is an The data can be entered in three ways: evidence based approach that can be used immediately as much occurrence • Import from online sources - existing data is already available. The tool is sources of primary data can be open and free to use so there are no queried. By adding a search term e.g. restrictions in terms of accessibility aside a scientific name or a common name from a connection to the internet. It you can query two sources of online provides a platform that can be built on data: GBIF and Flickr. Any matching in the future to make other aspects of record that has been georeferenced the Red List criteria automated. In short, can be added directly to the map it could be the first step towards a fully editor. automated data driven Red List 13 BGCI • 2012 • BGjournal • Vol 9 (1)
Author: Valerie Pence FROM FREEZING TO THE FIELD— IN VITRO METHODS ASSISTING PLANT CONSERVATION When seeds are few and cuttings difficult, tissue culture can provide an alternative conservation pathway Above: The rockhouse habitat that is home to the Cumberland sandwort experimental population (Valerie Pence) Left: A storage tank in CREW’s CryoBioBank (CREW). primarily at species for which traditional (Sarasan, et al., 2006). The PRD approaches are not adequate. Thus, collaborates with a number of other when seeds are few and cuttings are not institutions, including botanical gardens workable, tissue culture can provide an in the Center for Plant Conservation alternative method for propagation. network (Center for Plant Conservation When seeds are lacking or are 2012), government agencies, NGOs, and “recalcitrant” (sensitive to the drying research stations. These institutions necessary for traditional seed-banking), often identify plants for which in vitro freezing tissues from in vitro cultures can approaches could be useful and then be an additional tool for banking valuable provide the starting material (seeds or genetic material from rare taxa. The PRD shoot tips) to CREW for propagation. has developed protocols for the in vitro Introduction propagation and/or preservation of over ff the main public path of the 50 rare species, providing materials for restoration projects and tissues for long- “ Over 100 botanic gardens around the world have tissue O Cincinnati Zoo & Botanical Garden, in the corner of the park, term storage in liquid nitrogen in CREW’s CryoBioBank. culture and micropropagation one can find the Carl H. Lindner Family Center for Conservation and Research of Endangered Wildlife (CREW). From this small, two-story building, plant and Propagation for restoration Propagation is a key element in facilities. ” (BGCI GardenSearch database, 2012) animal research is being conducted that providing plants for recovery projects. The Autumn buttercup (Ranunculus is impacting rare species across the For many endangered species, aestivalis) is one such species, known country, and beyond. CREW’s Plant traditional propagation by seed or from one site in south central Utah in the Research Division (PRD)’s particular cuttings can meet propagation needs, Sevier River Valley. When it became focus is using in vitro (tissue culture) but for species with few or no seeds or obvious that the population was methods for propagating and preserving few individuals, plant tissue culture can declining, The Nature Conservancy endangered plants. The work is directed be used to supplement these methods bought the property in order to protect 14 BGCI • 2012 • BGjournal • Vol 9 (1) • 14-17
Todsen’s pennyroyal growing at White Sands Missile Base (Doug Winget). and northern Tennessee. Like the Autumn buttercup, CREW initiated several genetically different tissue culture lines from seeds that had been collected by researchers at the Missouri Botanical Garden. Shoots were produced, rooted, and plants transferred back to soil. In order to demonstrate the feasibility of using tissue culture propagated plants for the recovery of this species, an experimental out-planting was made at a rockhouse site in southern Kentucky in collaboration with the U.S. Forest Service. Plants were planted in different areas of the rockhouse, in order to evaluate the microhabitats within the rockhouse, which differed in light and moisture levels. Over the course of six years, plants at several of the microsites have grown and reproduced well, indicating the viability of these methods, were initiated from each seedling. As should they be needed to help preserve with most tissue culture systems, the the species in the future. A genetic shoots can be maintained and multiplied study is also underway to analyze the in culture by dividing and sub-culturing genetic diversity of this new, the shoots onto fresh medium every 6-8 experimental population. weeks. By changing the components of the medium, the shoots can be By combining the laboratory strengths of stimulated to form roots, and once CREW with the field expertise of rooted, the shoots are then ready to be collaborators in botanical gardens, moved back into soil. This is a clonal governmental agencies, and non-profit method of propagation, but each genetic organizations, the work at CREW is line initiated from a separate seed is being integrated into conservation maintained separately, creating a efforts for species recovery and collection of genetically distinct lines in demonstrating that tissue culture tissue culture. propagation can be an important tool for conservation and restoration. When the plants were rooted, they were sent to the Arboretum at Flagstaff, where they were carefully removed from their culture tubes and acclimatized to soil and to real-life conditions in a greenhouse. At that point they were Cumberland sandwort flowering in culture ready to face life out in the wild. In 2007, (Valerie Pence). a group of buttercups, originally propagated at CREW, was planted back the plant. Over the past decade, five out at the Sevier Preserve, and, while organizations, including CREW, The none of the plants from the original Arboretum at Flagstaff, The Nature population have been seen in recent Conservancy, U.S. Fish & Wildlife years, a group of the CREW-propagated Service, and Utah State University, have plants are surviving and flowering. come together in a partnership to work on studying and restoring this species Another such species is the Cumberland (Pence et al., 2008). A small number of sandwort (Minuartia cumberlandensis), a seeds were collected at the site and sent small plant that grows only in sandstone to CREW where they were germinated rockhouse habitats in the Daniel Boone in vitro, and shoot propagating cultures National Forest of southern Kentucky The Autumn buttercup (Valerie Pence). 15 BGCI • 2012 • BGjournal • Vol 9 (1)
Resources for the Future of state and federally endangered banking (Pence, 2011). For these plants, species from Kentucky, Indiana, and banking tissues from in vitro cultures in In a similar fashion, the PRD is utilizing in Ohio, including such species as Short’s liquid nitrogen can provide an alternative vitro methods to provide tissues for goldenrod (Solidago shortii) and Running method for long-term germplasm long-term liquid nitrogen storage, when buffalo clover (Trifolium stoloniferum). storage. At CREW, multiple genotypes of seed banking is not a workable option Because not all endangered plants are several species are being collected, put for a species (Engelmann, 2004). This seed plants, there is a Pteridophyte into culture, and then cryopreserved, in work centers on the CryoBioBank (CBB), (Fern) Bank and a Bryophyte (Moss) order to maintain a back-up to the CREW’s liquid nitrogen storage facility. Bank, which contain spores, as well as genetic diversity of these species, The plant collections, or “Frozen tissues of gametophytes and should they decline or be lost in the wild. Garden” within the CryoBioBank include sporophytes. The Endangered Plant These include three endangered seeds, spores, and tissues of about 150 Tissue Bank contains samples of tissues pawpaws endemic to Florida, the Four- plant species in four distinct collections, from in vitro cultures of endangered petal pawpaw (Asimina tetramera), all stored at -196oC (-320oF). plants that are grown at CREW. Material is continually added to the collection, The small Cumberland sandwort flower Seeds and spores are prepared for and some samples are over 20 years old. (Brian Jorg). freezing by simple drying, but tissues, Recently, samples of pollen from the such as shoot tips and embryos, require American chestnut (Castanea dentata) more elaborate procedures. were shown to be viable after 15 years of Concentrated solutions of sugar and other storage in liquid nitrogen, while shoot chemicals, known as cryoprotectants, tips of the Cumberland sandwort were remove water from the tissues and protect recovered after 10 years in liquid the cells from damage during the freezing nitrogen. and thawing processes. The extremely low temperatures of liquid nitrogen Perhaps one of the most important uses provide stability for the tissues, of the CryoBioBank is to preserve maintaining them in a state of suspended tissues from endangered species that fall animation for decades. into the category of “exceptional” species. These are plants that either The CryoBioBanks's Frozen Garden is produce few or no seeds, or their seeds made up of four distinct collections. are sensitive to drying and cannot be put The Regional Seed Bank includes seeds through the rigors of normal seed- A second planting of CREW propagated Autumn buttercups took place in 2010 in Utah (Valerie Pence). 16 BGCI • 2012 • BGjournal • Vol 9 (1)
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