The DFC Model - Growth Model Users Group

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The DFC Model: a Regulatory Tool

Used in Riparian Forest

Management in Washington

• Steve McConnell

• Upper Columbia United Tribes

• Spokane, WA

• Growth Model Users Group Meeting

• January 11, 2007

Acknowledgements

• NWIFC, CMER, UCUT

• John Heimburg

• Dave Schuett-Hames, Ash Roorbach

• Chris Mendoza, Pete Heide

• Doug Martin, Nancy Sturhan

• Darin Cramer, Dawn Hitchens and Bonnie

Thompson

Presentation Outline

• DFC Model Attributes and Role in

Management

• Desired Future Condition (DFC) management concept

• Key attributes of DFC Rules

• DFC Model role in management

• Model origins and characteristics

• Overview of CMER DFC related studies

DFC Model

• Only growth and yield model used as a regulatory tool

• Derived from ORGANON, SMC version

• A whole stand model

DFC Model

• Utilizes landowner collected data

• Simple enough for lay-persons to use

• Limited number of outputs – only those that pertain directly to what landowners need to know to implement rules

DFC Model Role

• Project stand basal area growth from current age to stand age 140

• Determines if stands will meet DFC Target

• Provides prescriptive details based on site and stand characteristics

• Takes a very complicated set of rules and makes them comprehensible!

Characteristics of DFC Rules for

Riparian Forests

• Fish-bearing streams on private forest lands in western Washington

• Core, Inner and Outer Zones

• Zone widths vary by site class (I-V) and stream size (LE or GT 10’)

• The DFC target is a stand-age-140 basal area target, for each site class

DFC: Desired Future Condition

Characteristics and functions of mature, unmanaged riparian forests

Habitat conditions desirable for salmon recovery

DFC: Desired Future Condition

Goal-oriented management system

• “…The stand conditions of a mature riparian forest, agreed to be 140 years of age …a reference point on a pathway and not an endpoint for stands.”

• Gauged against a stand basal area target

Management Along Westside,

Type F Streams Varies By:

• Site productivity: site class I-V

• Stream-size: LE 10’ vs. GT 10’

• Harvest method:

– no-cut

– thin from below

– leave trees closest to the stream

RMZ’s: a Graphical Depiction

• Zones – core, inner and outer

RMZs: Location, Activities

Allowed and Size

Core Zone : closest to stream, no cutting, always 50’ wide

Inner Zone : some cutting, variable width

(10 to 100 feet)

Outer Zone : furthest from stream, more cutting, variable width (22 to 67 feet)

RMZ Widths, by Stream Size

120

100

80

60

40

20

0

Inner and Outer Zone Widths for Current "DFC"

Rules iz small iz large oz small

Zone and stream size com bination oz large

I

II

III

IV

V

Forest Practices Rules Stand

Age-140 Basal Area Targets

285

Basal Area Target

275

258 300

200

100

0

224

190

I II III

Site Class

IV V

Stand Basal Area for DFC Rules is Calculated from the Area-Adjusted Core+Inner zones

DFC: Desired Future Condition

Management today that puts stands on a trajectory towards

“DFC”

Stand growth and

Rx details derived from the DFC Model

DFC Model Problems

• Three errors in DFC Model calculations were identified, none of them making significant differences to the desktop analysis but possibly affecting implementation

DFC Model Problems

• 1) Stand age 140 BAPA is inflated for stands younger than 35 years,

• 2) An incorrect value is used in for small stream site class 1, 2, and 3 per acre calculations

• 3) For Option 1, the DFC Model gives different inner zone leave tree numbers on the graphical interface than are counted in the inner zone stand table

Desktop Analysis Results

10

8

6

4

2

0

Inner Zone Area vs. the Number of Trees per Acre

Represented by a Single Tree in DFC Model

Calculations for the Thin-from-Below Prescription

Number ofTrees per Acre

Represented by One Tree

Area of Inner Zone

Stands (Acres)

Individual Stands

Sensitivity Analysis (Roorbach)

• Scrunches variability for most input variables, minimizing the difference in stand age 140 Basal Area

• Major Species, DF or WH, makes an important difference in DFC Model outputs– the largest DFC Model related difference found

DFC Model Related Reports

• Desktop analysis

• Riparian stand characteristics

• Sensitivity analysis (Roorbach et al.)

• FPA field check review

• Model and manual problems

• Synthesis

Desktop Analysis: Exploratory

Origins

Initial analyses were:

– unstructured; outcomes were evaluated without specific objectives.

– from a small sample of FPAs from the

Olympic Peninsula,

– from FPAs that were approved just after new rules were developed

Desktop Analysis: Exploratory

Results

• Noticed that projected ba-140 almost always exceeded rule ba target

• Determined that the required 57 ltpa was a constraint to inner zone timber harvest

• Later, determined that the option 2 minimum floor width also constrained timber harvest more than the rule ba target.

Desktop Analysis: Follow-up

Exploratory Study

• Developed a Study Design (was not reviewed by the SRC)

• Developed specific objectives

Desktop Analysis Follow-up:

Study Design

• Selected 150 FPAs from 2003 and 2004, 75 from each year

• Used first DFC worksheet from each FPA

• Developed criteria for rejecting FPAs that lacked data or did not meet criteria

Desktop Analysis Follow-up:

Objectives

• Quantify DFC model-projected BA-140 for each of three riparian prescriptions: 1) nocut, 2) thin-from-below, and 3) leave trees closest to the stream

• Determine the effect of rule components

(required leave trees – option 1, and required floor widths, option 2) on DFC

Model BA-140 projections

Desktop Analysis Results

Core+Inner Zone BA-140 by Rx's, across all Site Classes

366.3

335.9

299.2

500

400

300

200

100

0

150 150 108

Riparian Prescription no-cut

Opt-1

Opt-2

Desktop Analysis Results

500

400

300

200

100

0

Stand Age 140 Basal Area per Acre, by Site Class and Riparian Prescription

1 2 3

Site Class

4 5 no-cut

Opt-1 opt2

Desktop Analysis Results

DFC Model After Thin Leave Trees per Acre, by Rule

Constaint, for the 140 Stands Requiring 60 or fewer

Residual Trees per Acre

One Stand Constrained by basal area

61

60

All other, 138 out of 140 Stands,

59

Constrained by

58 Trees per Acre

57

56

One Stand Constrained by Basal Area

AND Trees per Acre

Individual Stands

Desktop Analysis Results

DFC Model After Thin Leave Trees per Acre, by Rule

Constraint, for the Ten Stands Requiring More Than 60

Residual Trees per Acre

100

90

80

70

60

6 0 . 8

Stands Constrained by TPA

<=

6 1. 5 6 2 . 2

6 3 . 7

Stands Constrained by Basal Area

=>

6 4 . 9

7 0 . 9 7 1. 5

Individual Stands

7 2 . 8 7 3 . 1

9 7 . 0

Desktop Analysis Results

500

400

300

200

100

0

-100

Timber Harvest Constraints for the Thin From Below

Prescription: Trees Per Acre and Basal Area per Acre

7 stands constained by basal area only

142 stands constrained by

trees per acre only

1 stand constrained by basal area

AND trees per acre

Trees per Acre basal area

Riparian Stands, Sorted by Ascending Stand Age 140 Basal Area,

Minus One Tree

3

1

2

2

1

Site

Class

Desktop Analysis Results

Steam

Size

Floor

Width

Average floor width plus and minus one standard deviation

Number of

Stands

Constrained by

Floor Width

Number of

Stands

Constrained by

Basal Area

Target

Tot al

103.0

12.6

Small

80’

0 5 5

Large

Small

Large

100’

80’

100’

102.0

4.0

87.4

7.1

102.6

5.7

80.4

1.8

3

7

20

1

25

7

4

32

Small 80’ 38 2

27

40

Desktop Analysis Results

300

200

100

0

400

Floor Width and Basal Area Credit for Site

Class 2, Large Stream Stands

360.5

120'

0

100'

Individual Stands credit floor

Desktop Analysis: Conclusions

• DFC model projected core+inner zone BA-

140 exceed rule targets, because

• The 57 iz ltpa (opt-1) almost always (95.3% of worksheets reviewed) required leaving more trees than the rule target alone

• The minimum floor widths (opt-2) usually

(63% of worksheets reviewed) required leaving more trees than the rule target alone

Riparian Stand Characteristics

• Applicable only to subset of riparian stands that meet DFC requirements and selected by landowner for harvest

• Provide an overview of characteristics of stands submitted by landowners for management under current rules

• A few highlights only

Site and Stand Analyses:

Site Class

Numbe r of Riparian Stands by Site Class and DNR Re gion

50

40

30

20

10

0

0 1 2 1 0

NW

45

39

25

9

0

4 3

0

OLY PC

DNR Region

2

0 0

9 8

1 1

SPS

3

4

1

2

5

Site and Stand Analyses:

Major Species

Number of Riparian Stands by Major Species and

60

DNR Region

55

50

40

30

20

10

0

1

3

8

38

26

10

9

NW OLY PC SPS

DNR Region

DF

WH

Site and Stand Analyses:

HA BA by Major Species

Core vs. Inner Zone Harvest Age Basal Area by

Major Species

400

350

300

250

200

150

100

50

0

For DF, n = 74 Core Inner

For WH, n = 76 Riparian M anage me nt Zone

DF

WH

Site and Stand Analyses:

Conclusions (Cont.)

• Most stands (88.7) were on Site Class 2 and

Site Class 3

• There was an almost even split in # of FPAs evaluated,by Species (74 DF and 76 WH)

• In core zones, on average, basal area and trees per acre were higher, and percent conifer lower

Site and Stand Analyses:

Conclusions (Cont.)

• Stands with WH as major species had higher tpa, ba, and RD, but lower qmd than stands with Douglas-fir as major species

DFC Field Check Study

• Most stand inventory and site attribute data collected were similar between landowner and CMER Staff

– Stream size

– Major species

– Stand age

– Stand inventory

DFC Field Check Study

• Biggest differences to buffer strip configuration are a result of stream size call,

CMZ delineation and landowner decision on outer zone trees

DFC Field Check Study

• There were methodological findings, for example:

• 1) there is no method prescribed for determining RMZ length and this can lead to a lot of variability,

• 2) the Board Manual and other materials provided to landowners are confusing, difficult to follow and have errors within

Synthesis

• The basal area target is a less important constraint to inner zone timber harvest than is the leave tree requirement or minimum floor width

• Landowners use Option 2 (leave trees closest to the stream) preferentially

Synthesis

• There may be differences in harvest age

Douglas-fir and western hemlock stands in terms of basal area, tpa, relative density, qmd and conifer percent. Possibly there should be different management prescriptions for these.

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