STRATIFICATION PLOT PLACEMENT CONTROLS Strategy for Monitoring Postfire Rehabilitation Treatments PowerPoint PPT Presentation

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Title: STRATIFICATION PLOT PLACEMENT CONTROLS Strategy for Monitoring Postfire Rehabilitation Treatments


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STRATIFICATIONPLOT PLACEMENTCONTROLSStrategy
for Monitoring Post-fire Rehabilitation
Treatments
  • Troy Wirth and David Pyke
  • USGS Biological Resources Division
  • Forest and Rangeland Ecosystem Science Center
  • Corvallis, Oregon

U.S. Department of Interior U.S. Geological Survey
Supported by USGS - BLM Interagency Agreement
HAI040045
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Monitoring Approach
  • Objectives
  • Stratification
  • Control Plots
  • Random Sampling
  • Data Quality
  • Statistical Analysis
  • Repeatable, objective field methods using
    Rangeland Monitoring Database

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Stratification
  • Division of treatment areas into defined
    monitoring units with similar characteristics
  • Decreases variability, increases precision
  • Data collected is then inferred to be
    representative of the entire monitoring unit.
  • Stratification into monitoring units helps to
    determine success at the project level - and
    eventually at a regional scale

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Stratification
  • Monitoring Units may vary across the landscape
    and be separated by other monitoring units.

From Herrick et al 2005b
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Stratification Background Information
  • Aerial photographs
  • Soil Surveys
  • Determine what mapping units cover the treatment
    area
  • Can you identify the soil series within the
    mapping units?
  • What ecological sites are within the mapping
    units?
  • How do you determine the ecological sites?

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Stratification Background Information
  • GIS Layers
  • Digital Elevation Model (DEMs)
  • Land management activities (grazing allotments,
    previous seedings and fires etc.)
  • Fire and treatment perimeters for current project
  • Soils
  • Roads, streams and other geographic features that
    would be avoided

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Stratification Background Information - Resources
  • Web Soil Survey http//websoilsurvey.nrcs.usda.gov
    /app/
  • Soil Data Mart http//soildatamart.nrcs.usda.gov/D
    efault.aspx
  • USGS Seamless Data Distribution
    http//seamless.usgs.gov/
  • Official Soil Series Descriptions
    http//soils.usda.gov/technical/classification/osd
    /index.html

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Stratification Identifying Ecological Sites
  • Each plot must have Ecol. Site identified
  • Not all Monitoring Units are defined by one Ecol
    Site.
  • An ecological site is a distinctive kind of land
    with specific characteristics that differs from
    other kinds of land in its ability to produce a
    distinctive kind and amount of vegetation
    (NRCS).
  • Consist of site characteristics, plant
    communities, site interpretations, and supporting
    information
  • Identify ecological sites using soil and landform
    indicators (soil surveys)

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Soil maps
  • Soils are grouped into soil mapping units because
    we often cannot map soils at the scale at which
    they occur
  • Soil map unit includes one or more dominant soil
    map unit components inclusions (minor map unit
    components)
  • Soil map unit component soil series slope and
    surface texture modifier

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A soil map unit can be
  • An ASSOCIATION of two or more soils that occur
    in a repetitive and predictable pattern (e.g. low
    ridges swales)
  • A COMPLEX of two or more soils that usually do
    not occur in a predictable pattern at a mappable
    scale (e.g. coarse and fine soils in a river
    floodplain)
  • A single soil series (but even these map units
    usually have inclusions too small to be
    mapped). Sometimes call a CONSOCIATION

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Using soils to identify ecological sites
  • An ecological site can include more than one soil
    series, provided that the soils are similar
  • A soil map unit can include more than one
    ecological site. Soil map units often include
    many different soils, with different potentials
    to support plant communities
  • Even a soil series can include more than one
    ecological site. Soil surface texture often
    varies within a soil series. Soil surface texture
    is very important in distinguishing ecological
    sites.

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Stratification Identifying Ecological Sites
  • Determine soil mapping unit
  • Examine soil mapping unit description (220)
  • Determine soil series within mapping unit.

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Stratification Identifying Ecological Sites
Ninemile and Carvix Soil Series
Dig soil pits to identify soil series and
associated ecological sites
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Stratification Identifying Ecological Sites
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Stratification Criteria
  • Treatment type
  • Soil type / ecological site
  • Slope / aspect / elevation
  • Multiple polygons/ minimum size
  • Each stratification criteria doubles number of
    monitoring units (if all are monitored)
  • What criteria will reduce variability the most?

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Example Stratification Treatment perimeter and
DEM
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Example StratificationTreatment perimeter with
slope reclassification
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Example Stratification Treatment perimeter with
slopes lt gt 15 slope
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Example Stratification Soil mapping units
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Example Stratification Soil mapping units within
treatment perimeter
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Example Stratification Sample Areas
121 Mcpan-Chijer complex
181 Starbuck- Mcpan-rock outcrop
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Random Sampling
  • Enables statistical inference to the monitoring
    unit
  • GIS or traditional map grid
  • Can use several types of random sampling (simple,
    stratified, and two-stage random sampling)
  • Establish rejection criteria (slopes/roads/streams
    /rocks etc..)

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Random Point GenerationHawths Tools Features
  • Input layer (polygon/raster)
  • Minimum distance between points
  • Stratified (number of points)
  • Stratified design
  • Polygon unique id
  • Number of points per polygon
  • Density of points per polygon

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  • Hawths Tools Main Screen
  • 1. Generate Random points
  • Use for determining random plot locations
  • Generate Regular points
  • Other uses including separating polygons into
    roughly equal sizes

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Example Stratification (simple)Random point
generation screen
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Controls
  • Was rehabilitation necessary?
  • Plots that receive no treatment
  • No seed
  • No soil surface disturbance (affects bare ground
    and annual exotic abundance)
  • Randomly place within monitoring unit prior to
    treatment implementation
  • If controls are not possible, quantitative
    standards must be specified

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Controls
  • Long-term monitoring controls are highly
    valuable
  • May not be able to distinguish between seeded and
    unseeded plants
  • Help to determine persistence of seeding
  • Helps to determine treatment effect
  • Provides a measure of natural recovery

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