Source: FOREST SERVICE submitted to
GENECOLOGY, GENETIC DIVERSITY AND ADAPTIVE TRAIT VARIATION IN BITTERBRUSH (PURSHIA TRIDENTATA) FROM THE PACIFIC NORTHWEST
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
COMPLETE
Funding Source
Reporting Frequency
Annual
Accession No.
0201729
Grant No.
2005-35101-15341
Cumulative Award Amt.
$369,000.00
Proposal No.
2004-03984
Multistate No.
(N/A)
Project Start Date
Dec 15, 2004
Project End Date
Dec 14, 2008
Grant Year
2005
Program Code
[23.1]- (N/A)
Recipient Organization
FOREST SERVICE
(N/A)
CORVALLIS,OR 97331
Performing Department
(N/A)
Non Technical Summary
The use of native plants in environmental restoration efforts of forest and rangeland ecosystems has increased with our growing awareness of the importance of native species in maintaining biological diversity, sustaining productivity, and preserving ecosystem interactions. The use of adapted plants (those that thrive in a certain environment) in restoration is a requirement of all federal agencies, yet plant movement guidelines have been established for only a few species used in restoration. This study attempts to examine patterns of genetic diversity and adaptation in 140 populations of antelope bitterbrush (Purshia tridentata), a widely planted restoration species from the arid western U.S. Using common garden plantings, we will measure variation in key physical traits (such as plant size) and compare the observed differences between populations with differences found using DNA-based markers. With this comparison, plant movement guidelines based on adaptive traits will be constructed using an existing Conifer Model from forest management and a new Ecoregion-based approach. Results from this study will: (1) identify key traits that show population-level differences; (2) identify physical traits that are potentially important in restoration success; (3) provide land managers with scientifically-based plant movement guidelines for bitterbrush; (4) determine the usefulness of the two models in developing plant transfer guidelines; which will (5) result in a procedure that can be used for testing and developing plant movement guidelines in other restoration species.
Animal Health Component
50%
Research Effort Categories
Basic
40%
Applied
50%
Developmental
10%
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
1210710108020%
1230630108020%
2020630108020%
2020710108020%
2030630108110%
2030710108110%
Goals / Objectives
Examine patterns of genetic diversity and differentiation for antelope bitterbrush (Purshia tridentata) using both a common garden study and with molecular markers. Compare the genetic variation patterns found using the neutral molecular genetic markers with variation patterns of the adaptive traits found in the common gardens. Use the variation patterns from the common garden trial to determine seed transfer guidelines using a Conifer Model (from forest management) and a simpler approach based on Ecoregions. Results will: 1) Provide land managers with scientifically based seed movement guidelines for a key restoration species, thus improving the likelihood of establishment in arid ecosystems; 2) Determine the efficacy of the forest tree model in developing seed transfer guidelines for arid zone shrubs; 3) Improve our understanding of the impact that seed movement plays, and has played, in restoration practices.
Project Methods
A common garden comprised of 200 accessions from 140 locations will be used to examine variation in adaptive traits. Accessions are primarily from Oregon, southern Washington and northern California, but 20 accessions will be more widely located. Two field studies in central Oregon are currently in the ground that will provide data for two to three years. A third study will be established in a greenhouse in 2005 and transplanted into one of the field sites in 2006. The added environmental control of a green house will allow better growth measurements that will enable us to examine growth rhythm traits. Data will be analyzed to determine patterns of clinal and ecotypic variation using an approach developed for forest trees. These analyses can then be used to develop seed movement guidelines. A simpler analysis based on ecoregions will also be examined. Molecular markers (simple sequence repeats) will be developed to characterize cytoplasmic and nuclear neutral genetic variation in this species. The markers will be used to examine 80 populations. By integrating the molecular data with quantitative trait information from the common garden study, these markers will provide estimates of neutral differentiation that are used to identify potentially adaptive traits. A comparison between genetic variation in adaptive (common garden) traits and genetic variation in molecular traits will be used to examine the utility of molecular markers for use in developing seed transfer guidelines.

Progress 12/15/05 to 12/15/06

Outputs
During the summer of 2006, tissue samples were collected from the remaining essential populations. The tissue collections for this project are complete. All of the necessary genomic DNA isolations are finished. We have successfully identified 8 nuclear microsatellite loci and 6 cpDNA loci that are variable. We are currently focusing our efforts on genotyping individuals. Additionally, we are writing a second publication on the molecular portion of this project on the isolation and characterization of the 8 unique nuclear microsatellite loci. The 2nd year (final) measurements were completed at the Corvallis common garden site. We are still analyzing photographs from the first year to get a better understanding of growth rhythm. Flowering and growth were measured again at the two central Oregon common garden sites (year 3). Preliminary analyses are underway on the common garden data. Location differences are present. Growth rate and form variation is mapped to the landscape, but not as strong as some "specialists species" of forest trees. There are also differences in leaf color and plant health that appear to be tied to the collection site. This coming year we hope to get better data on flowering and seed shatter dates to see whether the shatter dates found during field collection are correlated with shatter dates in the common garden. This will answer the question of whether shatter date variation is genetic or environmental.

Impacts
1) Provide land managers with scientifically based seed movement guidelines for a key restoration species, thus improving the likelihood of successful establishment in arid ecosystems; 2) Determine the efficacy of the forest tree model in developing seed transfer guidelines for arid zone shrubs and potentially provide a framework for developing seed movement guidelines for other restoration species. 3) Improve our understanding of the impact that seed movement plays, and has played, in restoration practices, thereby enabling managers to understand the risks of using non-local seed sources.

Publications

  • Horning, ME and RC Cronn. 2006. Length polymorphism scanning is an efficient approach for revealing chloroplast DNA variation. Genome 49: 134-142.
  • Johnson, GR and PC Berrang. 2007. Seed Shatter Dates of Bitterbrush in Oregon. Rangeland Ecology and Management 60 (1): 99-103.


Progress 12/15/04 to 12/14/05

Outputs
This project is finishing its first of three years. In the first year, growth data was collected from three study sites, two in central Oregon (planted in 2004) and one in western Oregon (planted in 2005). The western Oregon site was established to obtained more-detailed data on first year growth rhythms on 220 accessions, while the central Oregon sites will provide longer-term growth and flowering data on 120 accessions. Unfortunately poor field germination at the central Oregon sites reduced the number of accessions with sufficient plant numbers (>10 at a site) to 135, where there were initially 320. Significant seed source differences in growth pattern and seed germination were found in the 2004 measurements and 2005 germination data. First-year growth and form were associated with summer temperatures at their Oregon collection locations to some degree (r = 0.30 to 0.58). The 2005 measurements are currently being analyzed. During the summer of 2005, tissue collections were made at 173 localities totaling 3453 samples. From these samples, we isolated Genomic DNA from 760 individuals representing 38 localities. We have begun characterizing nSSR loci isolated from nine genomic libraries. We have sequenced 334 bacterial colonies, 81 contained an SSR repeat motif. To date, we have characterized 79 unique nSSR loci that may be useful and will undergo further analysis. In a publication identifying cytoplasmic variation (Horning and Cronn 2005, In press for Genome) we identified nine cpDNA haplotypes in 17 accessions. Additionally, we have identified six chloroplast SSR loci that yielded seven haplotypes for nine accessions. Current efforts are focused on identifying the nSSR and cpDNA loci necessary for the final analysis.

Impacts
1) Provide land managers with scientifically based seed movement guidelines for a key restoration species, thus improving the likelihood of successful establishment in arid ecosystems; 2) Determine the efficacy of the forest tree model in developing seed transfer guidelines for arid zone shrubs and potentially provide a framework for developing seed movement guidelines for other restoration species. 3) Improve our understanding of the impact that seed movement plays, and has played, in restoration practices, thereby enabling managers to understand the risks of using non-local seed sources.

Publications

  • Horning, ME and RC Cronn. 2006. Length polymorphism scanning is an efficient approach for revealing chloroplast DNA variation. Genome (in press).
  • Johnson, GR and PC Berrang. 2006. Seed Shatter Dates of Antelope Bitterbrush in Oregon. Rangeland Ecology and Management (submitted).