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ASSESSMENT OF EMERGENCY FIRE REHABILITATION OF FOUR FIRES FROM THE 2000 FIRE SEASON ON THE VALE, OREGON BLM DISTRICT

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Title: ASSESSMENT OF EMERGENCY FIRE REHABILITATION OF FOUR FIRES FROM THE 2000 FIRE SEASON ON THE VALE, OREGON BLM DISTRICT


1
ASSESSMENT OF EMERGENCY FIRE REHABILITATION OF
FOUR FIRES FROM THE 2000 FIRE SEASON ON THE VALE,
OREGON BLM DISTRICT
  • Jack D. Alexander III1, Brenda K. Kury1, and Jean
    Findley2
  • 1Synergy Resource Solutions, Inc., 1755 Hymer
    Ave., Sparks, NV, 89431
  • Phone 775-331-5577, Email jack_at_countgrass.com
  • 2Vale BLM, 100 Oregon Street, Vale, Oregon,
    97918-9630
  • Phone 541-473-6233

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
2
Acknowledgments
  • Synergy Resource Solutions, Inc., would like to
    thank the Vale Bureau of Land Management for the
    opportunity to participate in this study.
  • Jean Findley
  • Tom Hilken
  • Randy Eyre
  • Steve Christensen
  • David Wallace
  • Tom Miles

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
3
Introduction Jackson Fire
Objective Evaluate the success of post-fire
seeding, and determine which seed treatment was
most successful in accomplishing the goals of
rehabilitation
  • The Jackson Fire was discovered on July 14, 2000
    and controlled on August 17, 2000.
  • Before the fire, approximately 35 of the burned
    area was in early-seral stage, dominated with
    introduced annual species.
  • Approximately 35 of the burned area was in
    mid-seral stage, with a minor component of
    perennial species such as bluebunch wheatgrass
    (Pseudoroegneria spicata). The remaining 30 of
    the area was in late-seral stage.
  • Numerous isolated stands of invasive weeds such
    as Scotch thistle (Onopordum acanthium), whitetop
    (Cardaris spp.), hogbite (Chondrilla juncea), and
    knapweed (Centaurea spp.) were also present.
  • Synergy conducted post-fire rehabilitation
    assessments in June 2001 and 2002.
  • Three transects and three photo-plots were
    established in each of 5 seed mix treatments.
  • Three photo-plots were established in burned
    areas that were not seeded.
  • Mulfords milkvetch (Astragalus mulfordiae) is a
    state endangered-listed plant found on two ridges
    in the Jackson fire area 16 additional transects
    (8 paired plots) with photo-plots were
    established.

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
4
Introduction Kern Fire
Objective Evaluate the success of the post-fire
seeding and to determine which seeding treatment
best met rehabilitation objectives.
  • A lightning strike started the Kern Fire on
    August 4, 2000, approximately 30 miles south of
    Vale, Oregon.
  • The fire burned areas dominated by a native
    sagebrush/bunchgrass community with inclusions of
    annual herbaceous species.
  • Pre-burn native communities contained Wyoming big
    sagebrush (Artemesia tridentata ssp.
    wyomingensis), rabbitbrush (Chrysothamnus spp.),
    bluebunch wheatgrass (Pseudoroegneria spicata),
    Thurber needlegrass (Achnatherum thurberina), and
    Sandberg bluegrass (Poa secunda).
  • Cheatgrass (Bromus tectorum) was dispersed
    throughout most vegetation communities and a
    number of pure stands of medusahead (Taeniatherum
    caput-medusae) were present on clay soils.
  • The fire burned a total of 12,068 acres,
    including 11,983 acres of public land. Post-fire
    rehabilitation included seeding 1,800 acres with
    a native perennial seed mixture and 360 acres
    with a non-native perennial seed mixture.
  • Synergy conducted the Kern Fire Post-Fire
    Rehabilitation Assessment in July 2001 and June
    2002.

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
5
Introduction White Mule Fire
Objective Evaluate the overall success of the
post-fire seeding and to determine which seeding
treatment best met rehabilitation objectives.
  • The lightening-caused White Mule fire burned a
    total of 18,158 acres of BLM land south of Rome,
    OR from August 3 to 7, 2000.
  • This area previously burned in 1999 (550 acres),
    1995 (36,046 acres), 1986 (8,500 acres), 1985
    (32,497 acres), and 1983 (53,518 acres).
  • The area is dominated by annual species such as
    cheatgrass, tumble mustard (Sisymbrium
    altissimum), and Russian thistle (Salsola kali).
  • Post-fire rehabilitation included the re-seeding
    of a native seed mix and a non-native seed mix on
    8,151 acres. Wyoming big sagebrush (Artemisia
    tridentata ssp. wyomingensis) and forage kochia
    (Kochia prostrata) were aerially seeded on 3,593
    acres.
  • Synergy conducted the post-fire rehabilitation
    assessments in July 2001 and June 2002.

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
6
Introduction Wild Horse Springs Fire
Objective Evaluate the overall success of the
post-fire seeding and to determine which seeding
treatment best met rehabilitation objectives.
  • The Wild Horse Springs Fire burned near Bully
    Creek, near Vale OR.
  • The fire burned 1,235 acres of BLM land and a
    total of 1,873 acres.
  • Synergy conducted the post-fire rehabilitation
    assessments in June 2001 and 2002.

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
7
Methods Seed Mixes
N Native Seed Mix, I Introduced Seed Mix, x
only one seed mix used, seed treated or untreated
with Germ-N-8. Grasses were drill seeded. A
variety of shrubs were aerially seeded at each
fire.
Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
8
Methods Site Selection
  • Study sites were placed to represent areas with
    varying degrees of seeding success. This study
    was not designed to have random samples.
  • All study sites were placed in areas with
    evidence of seedling establishment.
  • Photo-plots (by default the 0-meter point for
    density transects) were placed in areas with
    seedlings of seeded species. Portions of the
    project area had little or no seedling
    establishment.
  • Transects were intentionally placed where
    seedlings had established. This biased the data
    to reflect higher than average seedling
    establishment.
  • The project did not have sufficient budget to
    perform a statistically valid sample of the
    entire area, therefore, sites were selected to
    provide data representative of areas with
    successful seeding.
  • 4 paired plots (8 plots per ridge) were
    established on the treated and untreated areas in
    the Jackson fire to determine the impact of the
    fire and seeding on Mulford's milkvetch.
  • Some areas with Mulford's milkvetch were seeded,
    but portions of two ridges in the treated
    (seeded) area were left unseeded because of
    concern of the effects of seed drills on
    Mulford's milkvetch.
  • Synergy collected two types of monitoring data at
    each site density and photo-plots to evaluate
    the efficacy of the various seed mixes in burned
    areas.

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
9
Methods Photo-Plots
  • Photographs provide a quick, qualitative
    assessment of sites and a means of making
    comparisons between sites and at the same site
    over time. Photographs allow non-technical
    assessment of a small plot. Photo-plots are
    accepted by BLM as a qualitative method of data
    collection.

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
10
Methods - Density
  • Synergy used TR 4400-4, Sampling Vegetation
    Attributes, to develop density protocol used for
    the Jackson Post-Fire Rehabilitation Assessment.
  • Developing efficient protocol was one of the
    tasks for 2001.
  • Several quadrat sizes were used to test for
    optimal sampling efficiency in 2001.
  • In 2002, two quadrat sizes were used
    0.1x0.5-meter and 0.5x1.0-meter.
  • 2002 data were collected at the same study areas
    established for sampling in 2001.
  • This study was not designed to provide a
    statistically valid sample.
  • Observers collected three types of density data
    during this study
  • Fifty quadrats placed in a stratified random
    manner along 10 belts within a 25x50-meter grid
    (data collected separately by plant maturity and
    species)
  • One 0.75x75-meter belt transect that counted
    number of adults and seedlings (not separated by
    species)
  • Ten 0.5x25-meter belts along the X-axis tape that
    counted only mature grasses and forbs.
  • All three types of density sampling for each site
    used the same 25x75-meter grid.

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
11
Methods Density (Contd)
  • A 75-meter tape formed the Y-axis and a 25-meter
    tape formed the X-axis. Random numbers were used
    to determine sample transect starting points
    along the Y-axis and quadrat locations along the
    X-axis. Ten coordinates were randomly selected
    for Y-axis coordinates. Five X-axis coordinates
    were randomly selected for each of the 10 Y-axis
    legs.
  • A plot rod was used to outline plot boundaries.
  • The plot rod measured 0.5-meters on the
    horizontal leg and was marked in 0.1-meter
    increments. As the plot rod passed over each
    plant, one observer counted individual mature
    plants and seedlings of each species using a hand
    counter (clicker).
  • Individuals were counted only if rooted within
    the quadrat.
  • The number of mature and seedlings of each
    species on the density data sheets.
  • Perennial species were sampled at all 50 quadrats
    (5 quadrats on each of 10 legs).
  • Annual species were sampled at 25 quadrats (5
    quadrats on each of 5 transects on the Y-axis
    the first, third, fifth, seventh, and ninth
    legs).

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
12
Methods Density (Contd)
  • In 2001, quadrat size varied according to
    community structure and species sampled.
  • In 2002, only the two most efficient quadrat
    sizes from 2001 were used.
  • Annuals and forbs were sampled within a
    0.1x0.5-meter plot nested in the lower-left
    corner of the 0.5x0.1-meter quadrat used for
    perennials.
  • Quadrat size 0.5x1.0-meter was used to sample
    Mulford's milkvetch and perennial species on all
    Mulford's milkvetch transects.
  • In the second set of density data, observers
    sampled a 0.75x75-meter belt quadrat along the
    right side of the Y-axis tape at each density
    transect.
  • This sample was not separated by species, instead
    observers counted two classes (seedlings and
    adults or resprouts) of all perennial grass
    species.
  • These data were collected to provide an
    additional indication of seedling density.
  • The 0.75x75-meter belt included clumps of
    seedlings that may have been missed in the
    smaller quadrats.
  • These data have not been analyzed due to budget
    restrictions.

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
13
Methods Density (Contd)
  • In the third set of density data, observers
    identified adult plants (by species), within a
    0.5x25-meter belt quadrat along the left side of
    each X-axis leg.
  • These data were collected to indicate the number
    of adults that survived the fire.
  • These adults may have been too widely scattered
    to be well represented in the 0.5x1-meter
    quadrats.
  • Data from comparison of the 0.5x25-meter belts to
    data from 0.5x1-meter quadrats would allow
    additional analysis of plot size.
  • These data have not been analyzed due to budget
    restrictions.
  • Sampling for Mulford's milkvetch was accomplished
    by stretching a transect tape 25 meters to form
    the Y-axis and a second tape 25 meters to form
    the X-axis.
  • Coordinates were uniformly selected to sample
    both Mulford's milkvetch and perennial species
    every 5 meters, beginning at the 5-meter mark,
    and Mulford's milkvetch only every 5 meters
    beginning at the 2-meter mark.
  • Mulford's milkvetch was sampled the entire length
    of the axes perennial species were sampled every
    5 meters using a 1x0.5-meter quadrat.
  • These data have not been analyzed due to budget
    restrictions.

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
14
Methods Plot Rod
0.5 m
0.1 m
Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
15
Summary
  • Data analysis was not included in the funding for
    this project.
  • No seeding success objectives were established
    during the fire reclamation design process.
  • BLM was generally disappointed with the lack of
    seedling establishment.
  • This is particularly true in light of the fact
    that the sample site selection ignored large
    areas where seedling success was marginal or
    essentially none.

Sagebrush mariposa lily Calochortus macrocarpus
Indian ricegrass Achnatherum hymenoides
RESULTS Data analysis was not included in the
funding for this project. A preliminary summary
of the data is provided. Data were summarized by
the average number of seeded species per year and
per square-meter for each seed mix. Data are
represented by transect total (i.e., 1 1
transect had a certain number of seedlings per
square-meter). No seeding success objectives
were established during the fire reclamation
design process. However, BLM was generally
disappointed with the results of these seedings.
This is particularly true in light of the fact
that the sample site selection ignored large
areas where seedling success was very marginal or
essentially none.
Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
16
Summary Density at All Fires
  • A preliminary summary of the data is provided.
    Data were summarized by the average number of
    seeded species per year and per square-meter for
    each seed mix. Data are represented by transect
    total (i.e., 1 1 transect had a certain number
    of seedlings per square-meter). SSeedling
    plants of the seeded species (regardless of mix)
    MMature plants of the seeded species (regardless
    of mix).

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
17
Summary Milkvetch Density
  • Data were summarized by the average number of
    seeded species and Mulfords milkvetch plants per
    year and per square-meter for each seed mix.
    Data are represented by transect total (i.e., 1
    1 transect had a certain number of seedlings per
    square-meter). SSeedling plants of the seeded
    species (regardless of mix) MMature plants of
    the seeded species (regardless of mix).

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
18
Observations
  • Initial establishment of seeded species was low.
  • Recruitment of seeded species from seedlings to
    mature plants was low on all evaluated sites.
  • Sites with a higher seral stage prior to the
    fires of 2000 appeared to have increased seeding
    success.
  • No differences were observed in the success of
    the different seed mixes.

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
19
Recommendations
  • This study was not designed to determine cause of
    seedling success or failure.
  • Site observation indicates two main factors
    drought conditions in 2 years following seeding
    and presence of invasive annual species (most
    notably cheatgrass) may have negatively impacted
    seeding successes.
  • Seeding success was correlated to precipitation
    levels (i.e., low precipitation levels yielded
    low seedling success).
  • Additional data analyses are necessary to
    completely understand the interactions of seeded
    species at each fire.
  • A correlation should be developed between initial
    seedling establishment and short- and long-term
    plant persistence.
  • Analyses should be completed to determine the
    most appropriate plot size.

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
20
For More Information
  • Please Contact
  • Synergy Resource Solutions, Inc.
  • Jack D. Alexander III
  • 1755 Hymer Avenue
  • Sparks, NV 89431
  • 775-331-5577
  • www.countgrass.com jack_at_countgrass.com

Synergy Resource Solutions, Inc.
www.countgrass.com Vale Bureau of
Land Management - www.or.blm.gov
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