Source: SMK PLANTS submitted to NRP
NOVEL USE OF PLANT TISSUE CULTURE FOR SITE-ADAPTED, ACID SOIL, HEAVY METAL TOLERANT, NATIVE PLANTS USEFUL FOR MINE LAND REVEGETATION.
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
COMPLETE
Funding Source
Reporting Frequency
Annual
Accession No.
0210017
Grant No.
2007-33610-17997
Cumulative Award Amt.
$80,000.00
Proposal No.
2007-00354
Multistate No.
(N/A)
Project Start Date
May 15, 2007
Project End Date
Jan 14, 2009
Grant Year
2007
Program Code
[8.4]- (N/A)
Recipient Organization
SMK PLANTS
5477 GENE SARAZEN DR.
BILLINGS,MT 59106
Performing Department
(N/A)
Non Technical Summary
There is a need for locally-adapted native plants which are tolerant of very low soil pH and elevated heavy metal concentrations to re-vegetate acid mine land in the Rocky Mountain west. Large numbers of acid and heavy metal tolerant (AHMT) plants are necessary because of the immense area of acid mine land that needs to be reclaimed. In Montana alone there are about 6000 abandoned hard rock mines and milling sites. Mining wastes have contaminated over 3,000 miles of rivers in Western states. AHMT plants will be of value even on amended or cover-soiled sites as plant roots often extend into un-amended soil. Researchers have experimented with seed collected from such sites as a way to produce AHMT locally adapted native plants. However, many desirable native plants are difficult to propagate by seed or by vegetative production (e.g. cuttings). Plant tissue culture is a way to overcome these problems, but few of the most desired plants and no AHMT plants have ever been cultured before. The purpose of this research is to produce AHMT plants using plant tissue culture. SMK Plants will collect plant material for AHM sites, develop tissue culture propagation methods for these plants, and seek to attain commercial production rates to provide cost competitive AHMT plants for mine land reclamation. Revegetation of mined land with these plants will benefit society by reducing wind and water erosion which in turn will reduce toxic materials in the air we breathe and the water we drink.
Animal Health Component
100%
Research Effort Categories
Basic
(N/A)
Applied
100%
Developmental
(N/A)
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
1330110202050%
1332420102050%
Goals / Objectives
The objective of this research is determine the feasibility of using plant tissue culture to produce large numbers of site-adapted, native plant species useful for acid/heavy metal (AHM) contaminated mine sites. First, SMK Plants will select a range of plant species determined to be valuable for revegetating a representative AHM contaminated mine site in Montana. Second, we will secure suitable AHM contaminated site(s) that contain the plant species for collection. Third, we will utilize the plant tissue culture, or micro-propagation, process to determine if plant tissue culture can be used to propagate nursery quality plants of these collections in quantities for commercial revegetation operations.
Project Methods
With the aid of highly respected consultants in the reclamation field, SMK Plants will select the species to be studied and secure the AHM site in Montana for collection. The plant tissue culture process will involve protocols developed and/or utilized by SMK Plants for propagating field collected native species. It will proceed as follows: (1) Collect portions of plants(explants) of the selected species. Identify each plant or population with GPS coordinates and physical markers; (2) To ensure that the plants from which the explants are taken are in fact AHMT, take soil samples from the root zone of the plants from which the explants were taken and have them analyzed; (3) Disinfest and establish each of the selected plants in clean (i.e. no fungal or microbial contaminants) culture; (4)Establish shoot cultures and determine media and growing conditions to achieve a commercial multiplication rate for each of the selected plants, i.e. 4 to 6 X in 4 to 6 weeks; (5) Test in vitro rooting method to achieve rooting within 6 weeks after transferring to rooting media. Finally, produce 1000 tissue cultured plants for each species and determine the unit cost of production.

Progress 05/15/07 to 05/14/08

Outputs
OUTPUTS: Accomplishments in Phase I include: Collection of plant material from 15 desirable plant species from 5 unique sites in Southwestern Montana. These sites include key riparian sites, upland sites and one steep slope mountain site. Establishing an outstanding collaboration with the Reclamation Research Group LLC, Bozeman, Montana, and beginning greenhouse production of three species with Westscape Wholesale Nursery, Belgrade, Montana. Of the 15 plant species collected,6 are growing in clean culture, of which 3 are in greenhouse rooting trials, and 3 are under multiplication. Meeting our 1000 plant goal by March 2008 for three of the 4 plant species currently in culture. We now have robust estimates of their unit cost of production. Submission of our Phase II proposal, which included a detailed Commercialization Plan which was reviewed by Purdue University and professionals in Montana. PARTICIPANTS: Nothing significant to report during this reporting period. TARGET AUDIENCES: Nothing significant to report during this reporting period. PROJECT MODIFICATIONS: Nothing significant to report during this reporting period.

Impacts
Though we were not successful in getting 9 of the plant species we collected into clean culture, we have more species in culture than we promised in our Phase I proposal. These include key ecosystem components such as a nitrogen-fixer, riparian shrub, and a much in demand grass. Many of the 15 species collected in May did not survive the initiation process. This was unexpected since young, actively growing tissue is often used for tissue culture initiation. Of particular note is that some species for which tissue culture protocols had previously been devised and in use, did poorly when collected from AHM sites. These results emphasize the need to treat each species growing on AHM sites as new to the tissue culture process, regardless of the previous work done for that species. Contamination and survival was low for most cultures, indicating the sterilization method disinfested the explants but may have also damaged the explants. To address this problem, three collection methods were tested during the third collection trip. In general (all other factors combined), survival differed between: plant collection season, seeds versus shoot collection, and explant collection procedure. Using these factors we have adjusted our methods which will improve our future initiation success and will be used in Phase II of this project. Production of 1,000 shoot was easily accomplished well within seven months for three species. Three other species of importance did not have sufficient initial cultures for the multiplication and rooting trials, but will continued to be cultured and further studied. The outcomes of this project can be summarized as follows: A wide variety of potentially useful native plants are found growing and thriving on heavily contaminated former hard rock mining sites in Montana. These plants are found on both riparian and upland, dryland sites. All of the sites we chose and worked on had soils with low (acid) soil pH and elevated heavy metal concentrations. Explants from some of these plants (6 of the 15 we collected) can be collected from live plants growing on acid, heavy metal contaminated (AHM), disinfested, initiated into clean, sterile culture, and coaxed to produce shoots and roots. That is, we were able to regenerate whole, healthy plants which are clones of the mother plant and are likely to have the same tolerance as the mother plant. The cost of producing acid, heavy metal tolerant (AHMT), locally adapted, native plants is similar to that of common ornamental perennial plants and is likely to be economical for use in hard rock mine land reclamation/restoration. The rationale and general methodology we used to produce AHMT native plants can likely be used to produce other adapted native plants for reclamation/restoration of other types of degraded sites. Some examples of other degraded sites are; coal bed methane impacted sites, coal mine spoils, hydrocarbon-contaminated grasslands, bauxite mines, phosphate mines, and other sites contaminated with industrial wastes.

Publications

  • No publications reported this period