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Productive Capacity Criteria and Indicators for Rangeland Ecosystems

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Title: Productive Capacity Criteria and Indicators for Rangeland Ecosystems


1
Productive Capacity Criteria and Indicators for
Rangeland Ecosystems
  • Gary R. Evans
  • R. Dennis Child
  • 4 February 2003
  • SRM Meeting in Casper, WY

2
Basic Assumption
  • Sustainability implies that
  • Rangeland will provide goods and services for the
    current and future generations.
  • Future generations can obtain their desired mix.
  • The mix of goods and services desired by society
    at any particular time will be diverse.

3
Our Approach
  • The team focused on consumptive uses (traditional
    and non-traditional).
  • Some standard ecological indicators like net
    primary productivity were included.
  • Recognized that non-consumptive uses influence an
    ecosystems productive capacity and included some
    to understand potential trends.

4
Our Approach
  • Recognized that some uses are mutually exclusive
    Others are compatible to some degree.
  • When examining the mix of goods and services
    found on rangeland that there is seldom a simple
    linear exchange ratio. (i.e. mixed species
    grazing.)

5
Scale
  • Multi-scale measurements are required. Data
    must be gathered within specified contexts and
    over both large temporal and spatial scales.
  • Bailey Ecoregions could define the broadest
    scale.
  • Major Land Resource Areas (MLRA) and Ecological
    Site Descriptions (ESD) to correlate existing
    survey data.

6
Questions Considered
  • What products, goods, and services are being
    produced that can be monitored?
  • What products, goods, and services will be
    desired by future generations?
  • How can issues of fragility and resiliency be
    considered?
  • Should natural processes be monitored to account
    for change in productive capacity?
  • Is it important to assess societal costs/benefits

7
Maintenance of Productive Capacity
  • Indicators selected
  • Above Ground Biomass
  • Rangeland Annual Productivity
  • Percent Available Rangeland that is Grazed
  • Number of Livestock on Rangeland
  • Presence and Density of Wildlife
  • Annual Removal of Commercially Harvested Biomass

8
Indicator 1 - Above ground biomass.
  • Annual above ground biomass is a direct measure
    of biomass production available to potential
    grazers of rangelands. It is a state variable
    measured in terms of mass/unit area.
  • Importance Most of the traditional data
    available have been collected in terms of the
    annual growth increment of herbaceous and shrub
    species of interest on rangelands. These data
    sets provide invaluable data on the trends in
    above ground biomass production and form the core
    subsets of data for indicator 2.
  • In some ecosystems, like temperate grasslands,
    annual above ground biomass are still the best
    available data, and will evolve toward measures
    of NPP in the future.

9
Indicator 1 - Continued.
  • Geographic Variation Rangeland vegetation types
    are highly variable in annual biomass production
    because of variation in precipitation,
    temperature and soil fertility. Annual sampling
    is needed to account for these short and
    long-term climate patterns and discriminatory
    analysis is needed to separate them from
    management impacts.

10
Indicator 1 - Continued
  • Scale Both ecoregion scales and the ecologic
    site description scale are useful in monitoring
    rangeland productive capacity.
  • Data Data collecting, reporting methods and
    reporting procedures exist at national and
    regional levels. However, data collection
    methods are not standardized at either scale.
    Above ground biomass is collected in a variety of
    ways including
  • Destructive above ground biomass sampling
  • Weight estimate and regression procedures
  • Clarity This indicator readily translates to
    map or GIS graphic forms for informing broad
    audiences.

11
Indicator 2 Rangeland Annual Productivity .
  • Rangeland Annual Productivity is measured as net
    primary productivity (NPP) and is the rate at
    which energy is converted to biomass within an
    ecosystem. It is a flow or ecosystem process
    measure in terms of g/unit area/time. NPP
    includes both above and below ground biomass.
    ANPP is the ecosystem measure of the amount of
    above ground biomass produced over time.

12
Indicator 2 Continued.
  • Importance Primary productivity is the
    foundation for measuring the productivity
    capacity of terrestrial ecosystems, and is key to
    understanding ecosystem sustainability.
  • Sunlight is the engine that drives all
    productivity through the process of converting
    light energy and CO2 to energy in the form of
    sugars. These carbon compounds provide the food
    base far all secondary production in ecosystems.
    Changes in productivity affect the kind, amount,
    and distribution of life.
  • Geographic Variation Annual above ground
    biomass and net primary productivity vary widely
    by vegetation type, which varies widely by
    region.

13
Indicator 2 - Continued
  • Scale Rangeland productivity is highly
    variable spatially and temporally. The
    indicators are meaningful when sample sizes are
    large enough to provide the necessary statistical
    power to detect change. Further interpretation
    can be enhanced through an understanding of
    climate and land use changes.
  • Data NPP is measured in 4 primary ways.
  • The direct, destructive sampling of above and
    below ground biomass.
  • Root/shoot coefficients
  • CO2 flux at the atmosphere/vegetation interface.
  • Modeling

14
Indicator 3 - Percent Available Rangeland that
is Grazed
  • Provides information on land use patterns that
    may shift production from one commodity to
    another.
  • Importance Used with other indicators to
    characterize the primary production consumed by
    livestock. It is an indicator of the net area
    used to produce livestock forage to the total
    rangeland within the ecoregion and the nation.
  • Geographic variation Gives consistent
    information across geographic regions.

15
Indicator 3 - Continued
  • Scale Meaningful at different scales and will
    likely become a measure that is aggregated from
    management records at the management unit to the
    ecoregion.
  • Data Conceptually feasible or initially
    promising, but no regional-national methods,
    procedures or data sets currently exist.
    Requires two pieces of data not uniformly
    available.
  • The amount of rangeland at ecoregion scales that
    could be grazed and
  • The determination that these lands are actually
    grazed.
  • This information could be sensitive with many
    landowners and managers and will require careful
    definition.

16
Indicator 4 - Number of livestock on rangeland.
  • A direct measure of the secondary production
    based on rangeland.
  • Importance Domestic livestock found on
    rangelands include cattle, sheep, goats, horses
    and mules, along with a number of minor grazing
    animals like llamas and alpacas. The long-term
    trends in numbers of cattle and sheep that spend
    at least part of the year on rangeland will be
    used.
  • Geographic Variation The number of livestock
    grazing on rangelands is equally meaningful in
    all geographic regions.

17
Indicator 4 - Continued
  • Scale The indicator is meaningful from the
    individual operation to the national level.
  • Data The number of cattle may be determined at
    a scale necessary for regional and national
    assessments. It is assumed that appropriate
    questions can be incorporated into surveys used
    by USDA-NASS. The proportion of the time spent
    on rangeland is not currently determined.

18
Indicator 5 - Presence and density of wildlife.
  • The presence and density of functional groups of
    wildlife provide an additional direct measure of
    secondary production based on rangeland.
  • Importance Enables the use of indicator species
    that characterize secondary productive capacity.
    A complete inventory of major wildlife species is
    not feasible. Initial thoughts on functional
    groups include 1) large herbivores, 2) small
    herbivores, 3) large predators, 4) small
    predators, 5) avian foragers, 6) avian predators,
    7) burrowing reptiles, 8) surface reptiles, 10)
    fresh water fish, 11) pollinators, and 12)
    amphibians.

19
Indicator 5 - Continued
  • Geographic Variation Meaningful, but only by
    ecoregion.
  • Scale Meaningful primarily at the broader
    scales between ecoregions and MLRAs
  • Data Conceptually feasible or initially
    promising, but no regional-national methods,
    procedures or data sets currently exits.
  • Clarity this indicator is potentially
    understandable to broad audiences. People tend to
    care about individual species welfare.

20
Indicator 6 - Annual Removal of Commercially
Harvested Biomass.
  • A highly diverse, yet important, array of
    products are taken on an annual basis from
    rangeland including
  • landscaping and decorative plant materials
  • edible and medicinal plants
  • wood products
  • native hay and
  • native plant seeds.

21
Indicator 6 - Continued.
  • Importance
  • Relatively high local value but may not be
    important nationally.
  • Productive capacity can be altered by changing
    regeneration capacity of some species.
  • Removal may change biodiversity and alter habitat
    in some sites.
  • The impact of the removal of plant material is
    difficult to evaluate. For example, little is
    known about the impact of harvesting seed
    extensively in one location to be planted in
    another location.
  • Government policies and public perceptions
    encouraging native species may increase demand.

22
Indicator 6 - Continued
  • Geographic Variation Ecoregion sampling designs
    will be needed that reflect the unique cultural
    and biological differences and the temporal
    product demand shifts.
  • Data Availability Some data sets exist at the
    region-national level, but methods and procedures
    are not standardized at the regional-national
    level. Most of the currently available data is
    associated with site specific biodiversity
    issues, such as removal and depletion of
    landscaping cacti, high value cedar removal, and
    non-sustainable demands for medicinal herbs.
  • On federal and state lands where harvesting
    activities are permitted there is a higher
    likelihood of monitoring the type and amount of
    material harvested. Private lands are subject to
    industry analysis of product availability. This
    is complicated by the fact that some products
    like mesquite are sold nationally while others
    like cactus for landscaping are sold locally.

23
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