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PREWORK

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Title: PREWORK


1
PRE-WORK SELECTING THE DESIGNATED MONITORING
AREA (DMA)
2
  • If you have an important point to make, don't try
    to be subtle or clever. Use a pile driver. Hit
    the point once. Then come back and hit it again.
    Then hit it a third time a tremendous whack.
  • --Sir Winston Churchill

3
Riparian Management Process
  • Step 1 Inventory/assess existing potential
    condition
  • Step 2 Define/stratify sub-areas to complex
    level
  • Step 3 Select DMAs (Designated Monitoring Areas)
  • Step 4 Establish Site Spec. Desired Conditions,
    Objectives, Indicators (MIM)
  • Step 5 Develop/adapt grazing strategy
    implement
  • Step 6 Monitor annual grazing use indicators
    each year condition indicators every 3-6
    years (MIM)
  • Step 7 Adapt grazing strategy, annual grazing
    use indicators /or criteria as needed to
    meet desired conditions

4
Step 1. Inventory/assess existing potential
condition
  • Use all previous inventories, monitoring, etc.
  • Look for reference areas
  • Obtain and use local classifications

5
Potential
  • The highest ecological status an area can attain
    with little influence by man

5
6
What does potential look like?
The Natural Conditions Database (Overton et.a.
1995)
Data for Granitic Streams in Central Idaho
Wilderness Areas (from 7406 observations)
7
Determining Potential Using References
Big Creek Inside
Big Creek Outside
8
Big Creek Box Whisker Plot - GGW
9
Bear Valley, Idaho late 80s
Trampled
Unstable banks/channels

What can it become?
Loss of hydric vegetation
10
Percent Fines Comparison to Reference Through
Time
BV7a Bear Valley Creek at Riparian Pasture
11
Step 2. Stratify to Riparian Complex
  • Valley Type
  • Dominant soil family type
  • Stream gradient (profile)
  • Vegetation patterns along the stream
  • Map the Riparian Complexes
  • Level II Riparian Area Evaluation R4 Integrated
    Riparian Evaluation Guide

12
Riparian Complex(s)
  • DMAs should be selected and monitoring conducted
    within the same Riparian Complex (Winward 2000).
  • Riparian complexes are defined by overall
    geomorphology, substrate characteristics, stream
    gradient, and vegetation patterns along the
    stream.
  • They develop and function in response to
    interacting features of valley bottom gradient
    substrate or soil characteristics valley bottom
    width elevation and climate.
  • Similar in definition to a valley segment but are
    polygon or area features

13
Stratify Complexes
14
Valley Bottom Classification

Rosgen 1996
15
Type VI - fault control
Type V U-shaped

Type VIII Wide, gentle slope
Type VII Dissected fluvial slopes
Rosgen 1996
16
Valley Types - Example (Rosgen 1996)
  • II - Broad V-shape or narrow u-shape in colluvial
    valleys
  • B channel type
  • lt4 gradient
  • Cobble and boulder
  • Cryoplanated uplands with colluvial slopes. in
    narrow valley

17
Same Pasture two valley types two different
complexes
Narrow V-shaped valley
Broad V-shape or narrow u-shape in colluvial
valleys
18
Rosgen Stream Types
Rosgen, 1996
19
Channel Type Example B channel
  • Moderately entrenched, moderate gradient, riffle
    dominated channel, with infrequently spaced
    pools.
  • Moderate relief, colluvial deposition, and/or
    structural.
  • Narrow, gently sloping valleys.

20
Inflection on profile reflects valley change
21
Riparian Vegetation Patterns
22
Imagery Identify Vegetative Patterns
Morgan Creek
Blue Creek
DMA
23
Step 3. Locate DMA in the Field
  • What kind of DMA is it? Representative, Critical,
    or Reference
  • Use existing information local knowledge to
    determine which complex(s) best meet the criteria
    for a DMA (use pattern maps, extensive field
    recon. info, PFC Assess., condition/value
    ratings, levels 1 2 from R4 IREG)

24
Designated Monitoring Area - DMA
  • 3 Kinds of DMAs
  • Representative DMA Reach chosen to be
    representative of a riparian complex typifies a
    larger area
  • Critical DMA Reach is not representative but
    important enough that specific data is needed at
    the site
  • Reference DMA Reach chosen to obtain data for
    use in helping to establish initial desired
    conditions for a similar area/complex

25
DMAs must
  • Have the potential to respond quickly to changes
    in management (that can be measured)
  • Be able to help answer key monitoring questions
  • Need to be selected by an ID Team of specialists
  • Should not be compounded with other activities

26
Representative DMAs
  • Representative of grazing (or other
    uses/impacts) specific to the riparian area
  • Where livestock are actually using the riparian
    area or other key activities/impacts are
    occurring (e.g. road impacts or fire effects)

27
Representative DMAs
  • Should be selected within a complex (similar
    geomorphology, substrate, gradient, veg pattern)
    (Winward 2000)
  • Should be selected to best represent influences
    of major activities in that complex (Winward
    2000)

28
Additional Thoughts on DMA Selection
  • Select those areas that are most critical in
    influencing target riparian resources that
    overlap with grazing use
  • Sensitive aquatic species habitat?
  • Critical overwintering/rearing or spawning
    habitat for fish?

29
Additional Thoughts on DMA Selection
  • Multiple complexes in one watershed or allotment
    are very common? Use the most sensitive
    complex(s)!

Telephone Draw
30
(No Transcript)
31
Premise for Representative DMAs
  • If proper management occurs on the DMA, the
    remainder of the pasture or use area will also be
    managed within requirements BUT, they should not
    be placed in livestock concentration zones (near
    fences, at bottlenecks, in watergaps, etc.)

32
How many DMAs do you need?
  • Depends on the nature of resource issues,
    monitoring questions, budget, and priorities
  • One DMA per/pasture good rule to start with
  • Use the most sensitive complex

33
The Red Face Test on DMAs
  • The ID team must provide a clear comprehensive
    rationale for the decision to place a DMA in a
    particular location and be able to articulate
    what the DMA is representative of (if it is a
    Rep. DMA) and what monitoring question it is
    designed to address!
  • Document this!

34
Thoughts to Ponder on DMA Selection
  • If the DMA is not carefully selected, all
    subsequent data collected at the site may be, at
    best, of limited value or at worst, completely
    useless
  • A poorly selected DMA represents a substantial
    waste of money and resources including
    opportunity costs

35
Meadow-Forest Sequences
Which complex is the most sensitive to grazing
effects? Where should it be located in that
complex?
36
Where to put the DMA in this Unit?
BLM - Scotchman Creek cutthroat trout
37
Scotchman DMAs
  • Most sensitive unit Meadows
  • Reference DMA fenced exclosure
  • Randomly selected Representative reach

Reference
Representative - Critical
38
Summit Creek DMA
Complexes?
39
Gradient Breaks Summit Creek
.0014
.00097
40
Good DMA for grazing impacts?
Ephemeral stream with no livestock use NOT a
good DMA
41
Stream banks must NOT be in boulder or bedrock
Or dominated by rock larger than cobble in size
42
Good DMA for grazing impacts?
Heavy timber no livestock use Not a good DMA
43
Good DMA for grazing impacts?
No not a perennial stream and no livestock use!
44
Good DMA for grazing impacts?
No unavailable to livestock
45
Good DMA?
Sheep Allotment in non-use during the past 6
years - Is a reference DMA
46
Good DMA for grazing impacts?
No site is a water gap
47
Good DMA for grazing impacts?
Yes, to compare effects of grazing using an
exclosure as an initial reference
48
Good DMA for grazing impacts?
Yes site meets all criteria
49
Good DMA?
Not for grazing since recreation impacts compound
grazing effects. This could be a good site to
monitor ORV impacts on the streambanks channel
works as a CRITICAL DMA
50
WF Morgan Creek Is this the correct DMA
location?
  • Stream is dominated by shrubs, except at this
    point just upstream of a beaver dam.
  • There is a hunter camp adjacent to the site.
  • Livestock concentrate at this convenient watering
    location.
  • The stream channel is mostly B3, but locally
    here it is C4.

51
Where is the DMA?
Its Here, Why?
This is the only spawning reach in the pasture
a critical reach.
52
Step 4 Establish Site Spec. Desired Conditions,
Objectives, Indicators (MIM)
  • Use SMART to establish objectives (Specific,
    Measurable, Achievable, Relevant, Trackable).
  • Objectives dictate monitoring approach what is
    the question?
  • Use outline in Appendix B (MIM) to select initial
    monitoring indicators appropriate for the stream

53
Identify Site Specific Objectives
  • Effective to write an objective for a complex or
    reach indicate that progress will be measured
    at a specific Designated Monitoring Area
  • Example
  • Mammoth Creek (MA9) Complex (2006)
  • -Decrease GGW 15
  • -Increase the composition of obligate fac wet
    plants on the greenline from 45 to 80
  • -Improve of stable banks from 65 to 80 by
    2013 (as monitored at DMA 1).

54
Final Thoughts on Pre-work/stratification and
DMA Selection
  • Dont rush into Monitoring w/MIM!
  • Spend an appropriate amount of time and effort on
    determining existing and potential conditions,
    stratification, objective setting, and DMA
    selection
  • Document your DMA selection rationale
  • The Ready, Fire, Aim sequence does not work
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