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Cowlitz Valley Ranger District 180 References ABR, Inc. 2009. Radar Surveys for Marbled Murrelets in Mt. Rainier National Park, Washington, 2009. Unpub. Report prepared for Mt. Rainier National Park, Ashford, Washington, by ABR, Inc., Forest Grove, OR. 17 pp. Aguilar, A.M. 2013. Forest Plan Soils Guidelines Regarding Mechanical Harvesters on Gifford Pinchot National Forest (Draft White Paper). Gifford Pinchot National Forest, Vancouver, WA. Akins, Jocelyn. 2009. Cascades Carnivore Project, Forest Carnivore Monitoring on the Gifford Pinchot National Forest: Year 1 and 2 Progress Report. Unpublished Report prepared for Washington Department of Fish and Wildlife and Gifford Pinchot National Forest. 21 pp. Altman, B. and J. Alexander. 2008. Habitat conservation plan for landbirds in the coniferous forests of western Washington and Oregon. Oregon-Washington Partners in Flight. www.orwapif.org Aubry et al, 2011. Wolverine Distribution and Ecology in the North Cascades Ecosystem 2011 Annual Report. Aubry, K.B., C.M. Senger, R.L. Crawford. 1987. Discovery of Larch Mountain Salamanders Plethodon larsilli in the Central Cascade Range of Washington. Biological Conservation 42: 147-152. Banci, V. 1994. Wolverine. Pages 99-127 in L.F. Ruggiero, K.B. Aubry, S.W. Buskirk, L.J. Lyon, and W.J. Zielinski, tech. eds. The scientific basis for conserving forest carnivores: American marten, fisher, lynx and wolverine in the western United States. USDA Forest Service. General Technical Report RM-254, Fort Collins, CO. Beechie, T.J.; Pess G.; Kennard P.; Bilby R.E.; Bolton S. 2000. Modeling Recovery Rates and Pathways for Woody Debris Recruitment in Northwestern Washington Streams. North American Journal of Fisheries Management 20:436–452. Bilby, R.E., Sullivan, K., Duncan, S.H., 1989, The generation and fate of road-surface sediment in forested watersheds in southwestern Washington: Forest Science, v. 35, p. 453-468. Bjornn, T.C.; Reiser, D.W.. 1991. “Habitat requirements of salmonids in streams.” In: Meehan, W.R.. Influences of forest and rangeland management of salmonid fishes and their habitats. Bethesda, MD: American Fisheries Society: 83-138. Boyd, Diane. 1999. Carnivores-wolves, Chapter 7 in G. Joslin and H. Youmans, coords., Effects of recreation on Rocky Mountain wildlife: a review for Montana. Committee on effects of recreation on wildlife, Montana Chapter of The Wildlife Society. 307pp. Brockway, D., Topik, C., Hemstrom, M., Emmingham, W.H., 1983. Plant Association and Management Guide for the Pacific Silver Fir Zone. Gifford Pinchot National Forest, USDA Forest Service, R6-Ecol-130a-1983. Portland, OR. Brosofske, Kimberly D.; Chen, Jiquan, Naiman, Robert J., and Franklin, Jerry F. 1997. Harvesting Effects on Microclimate Gradients From Small Streams to Uplands in Western Washington. Ecological Applications. 7:1188-1200.

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Page 1: References - a123.g.akamai.neta123.g.akamai.net/7/123/11558/abc123/forestservic.download.akamai...Management Guide for the Pacific Silver Fir Zone. Gifford Pinchot ... Comfort, E.J.;

Cowlitz Valley Ranger District

180

References ABR, Inc. 2009. Radar Surveys for Marbled Murrelets in Mt. Rainier National Park,

Washington, 2009. Unpub. Report prepared for Mt. Rainier National Park, Ashford,

Washington, by ABR, Inc., Forest Grove, OR. 17 pp.

Aguilar, A.M. 2013. Forest Plan Soils Guidelines Regarding Mechanical Harvesters on Gifford

Pinchot National Forest (Draft White Paper). Gifford Pinchot National Forest, Vancouver,

WA.

Akins, Jocelyn. 2009. Cascades Carnivore Project, Forest Carnivore Monitoring on the Gifford

Pinchot National Forest: Year 1 and 2 Progress Report. Unpublished Report prepared for

Washington Department of Fish and Wildlife and Gifford Pinchot National Forest. 21 pp.

Altman, B. and J. Alexander. 2008. Habitat conservation plan for landbirds in the coniferous

forests of western Washington and Oregon. Oregon-Washington Partners in Flight.

www.orwapif.org

Aubry et al, 2011. Wolverine Distribution and Ecology in the North Cascades Ecosystem 2011

Annual Report.

Aubry, K.B., C.M. Senger, R.L. Crawford. 1987. Discovery of Larch Mountain Salamanders

Plethodon larsilli in the Central Cascade Range of Washington. Biological Conservation 42:

147-152.

Banci, V. 1994. Wolverine. Pages 99-127 in L.F. Ruggiero, K.B. Aubry, S.W. Buskirk, L.J.

Lyon, and W.J. Zielinski, tech. eds. The scientific basis for conserving forest carnivores: American marten, fisher, lynx and wolverine in the western United States. USDA

Forest Service. General Technical Report RM-254, Fort Collins, CO.

Beechie, T.J.; Pess G.; Kennard P.; Bilby R.E.; Bolton S. 2000. Modeling Recovery Rates and

Pathways for Woody Debris Recruitment in Northwestern Washington Streams. North

American Journal of Fisheries Management 20:436–452.

Bilby, R.E., Sullivan, K., Duncan, S.H., 1989, The generation and fate of road-surface sediment

in forested watersheds in southwestern Washington: Forest Science, v. 35, p. 453-468.

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of recreation on Rocky Mountain wildlife: a review for Montana. Committee on effects of

recreation on wildlife, Montana Chapter of The Wildlife Society. 307pp.

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Management Guide for the Pacific Silver Fir Zone. Gifford Pinchot National Forest, USDA

Forest Service, R6-Ecol-130a-1983. Portland, OR.

Brosofske, Kimberly D.; Chen, Jiquan, Naiman, Robert J., and Franklin, Jerry F. 1997.

Harvesting Effects on Microclimate Gradients From Small Streams to Uplands in Western

Washington. Ecological Applications. 7:1188-1200.

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Corvalis, OR. 156 pp.

Williams, R.E.; Shaw, III, E.G.; Wargo, P.M.; Sites, W.H. 1986. Armillaria Root Disease. Forest

Insect and Pest Leaflet 78, USDA Forest Service.

Wilson, Todd M.; Forsman, Eric D. 2013. Thinning effects on spotted owl prey and other forest-

dwelling small mammals. In: Anderson, Paul D.; Ronnenberg, Kathryn L., eds. Density

management for the 21st Century: west side story. Gen.Tech. Rep. PNW-GTR-880. Portland,

OR: USDA Forest Service, Pacific Northwest Research Station: 79–90.

Zielinski, W. J., K. M. Slauson, C. R. Carroll, C. J. Kent, and D. G. Kudma. 2001. Status of

American martens in coastal forests of the Pacific states. Journal of Mammalogy 82:478-490.

Zika, P., and A. Jacobson. 2003. An overlooked hybrid Japanese knotweed (Polygonum

cuspidatum x sachalinense; Polygonaceae) in North America. Rhodora 105 (922): 143-152.

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Appendix A: Issues Raised During Scoping

Scoping Comment Received Interdisciplinary Team Response Theme

Treat hazard trees along haul routes The Forest Service cannot require a timber purchaser to treat hazard

trees besides those that pose an imminent threat to thinning

operations and haul.

Roads

Use temporary and spur roads to make timber harvest

economical

The interdisciplinary team is seeking access management solutions

for efficient harvest of timber while still minimizing the extent of new

disturbance in the project area.

Roads

Do not decommission any roads Currently the Forest Service is unable to fully fund the maintenance

of all existing roads on the Forest. Lack of road maintenance poses

environmental and safety risks. It is important to address these

issues through decommissioning or closure and stabilization, where

appropriate, such as where future management activities are not

expected to occur. The line officer has asked the team to consider

only closure and stabilization, not decommissioning, based on public

and interdisciplinary input. A preliminary list of road to propose for

closure is being derived from a variety of criteria based on known

future management needs, aquatic and terrestrial risk posed by the

road, and feasibility to analyze within the scope of this project.

Roads

Create 1-3 acre openings in stands to stimulate early

seral habitat for wildlife/big game; explore “linear

meadow” and Franklin/Johnson Moist Forest Strategy

The Nisqually Thin project area does not contain suitable conditions

to create early-seral openings, given that the area is predominantly in

the LSR land allocation. In addition, adjacent state and private lands

currently offer ample opportunity for big game forage, as they are

generally in an earlier state of forest regeneration along much of the

FS boundary.

Thinning prescription /

Wildlife

Consider winter logging/ easing timing restrictions to Winter closures and timing restrictions will be required for this project

to limit disturbance to endangered species (northern spotted owl,

Economics / Timing

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Scoping Comment Received Interdisciplinary Team Response Theme

make for a more economical thinning project marbled murrelet) and other wildlife, in addition to preventing damage

to soil and water resources during the wet season, as required by

law. Economics are only one facet of the purpose and need of the

project, and a variety of resource concerns must be considered in

implementation.

restrictions

Use smaller (25-50 ft) no-cut buffers in riparian zones

to increase harvest volume and improve riparian

structure

The thinning prescriptions proposed are consistent with direction

provided in the NWFP and Forest Plan for Late Successional

Reserve and Matrix, are consistent with the National Forest

Management Act, and are based on a synthesis of established

silvicultural science. Timber production for economic benefit is only

one goal of the Nisqually Thin project; ultimately the purpose in LSR

is to help stands develop more quickly into “old growth” stands.

Riparian Buffers /

Economics / Thinning

prescription

Thin more heavily overall than what is in proposed

action

The thinning prescriptions proposed are consistent with direction

provided in the NWFP and Forest Plan for Late Successional

Reserve and Matrix, are consistent with the National Forest

Management Act, and are based on a synthesis of established

silvicultural science. Timber production for economic benefit is only

one goal of the Nisqually Thin project; ultimately the purpose in LSR

is to help stands develop more quickly into “old growth” stands.

Thinning prescription/

Economics

Close roads (but do not decommission) Currently the Forest Service is unable to fully fund the maintenance

of all existing roads on the Forest. Lack of road maintenance poses

environmental and safety risks. It is important to address these

issues through decommissioning or closure and stabilization, where

appropriate, such as where future management activities are not

expected to occur. The line officer has asked the team to consider

only closure and stabilization, not decommissioning, based on public

and interdisciplinary input. A preliminary list of road to propose for

closure is being derived from a variety of criteria based on known

Roads

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Scoping Comment Received Interdisciplinary Team Response Theme

future management needs, aquatic and terrestrial risk posed by the

road, and feasibility to analyze within the scope of this project.

Look for as many opportunities to decommission roads

as possible

Currently the Forest Service is unable to fully fund the maintenance

of all existing roads on the Forest. Lack of road maintenance poses

environmental and safety risks. It is important to address these

issues through decommissioning or closure and stabilization, where

appropriate, such as where future management activities are not

expected to occur. The line officer has asked the team to consider

only closure and stabilization, not decommissioning, based on public

and interdisciplinary input. A preliminary list of road to propose for

closure is being derived from a variety of criteria based on known

future management needs, aquatic and terrestrial risk posed by the

road, and feasibility to analyze within the scope of this project.

Roads

Supportive of pre-commercial thinning to improve

health and vigor of younger stands

Pre-commercial treatments will be included in the proposed action Thinning prescription

Supportive of variable density prescription, gaps and

skips, in LSR. Supportive of timber-production oriented

prescription in Matrix. Supportive of leaving quality

down wood and snags in all units.

The thinning prescriptions proposed are consistent with direction

provided in the NWFP and Forest Plan for Late Successional

Reserve and Matrix, are consistent with the National Forest

Management Act, and are based on a synthesis of established

silvicultural science. Timber production for economic benefit is only

one goal of the Nisqually Thin project; ultimately the purpose in LSR

is to help stands develop more quickly into “old growth” stands.

Thinning prescription

Consider closure of trails that receive little use in

project area (Cave Creek #225, Big Creek trail #252

from #251 to Rd 8440 and redesignate remaining

portion of #252 as part of #251, Greenwood Lake

#253, Allen Mountain #269)

The team developed a purpose and need that focused around

thinning and restoration treatments to achieve primarily ecological

objectives. Specific resource concerns were not cited in this

comment.

Recreation

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Scoping Comment Received Interdisciplinary Team Response Theme

Consider improvements to certain trails (#251 trailhead

on FR 8410, trailhead for Cora Lake on FR 8420).

The IDT and line officer see the value of making recreation

improvements in the area of the Nisqually Thin proposal. However,

we felt that these types of projects are somewhat outside the scope

of the goals of this project and would not be practical to analyze.

Recreation

Evaluate safety , access, and use of High Rock

Lookout

The IDT and line officer see the value of making recreation

improvements in the area of the Nisqually Thin proposal. However,

we felt that these types of projects are somewhat outside the scope

of the goals of this project and would not be practical to analyze.

Recreation/Heritage

Revisit watershed prioritization process and evaluate

all needed watershed restoration work for this project

area

The watershed analysis from 2002 is a key reference tool the team is

using to build a list of potential restoration projects. “All” restoration

work needed in this project area cannot not be surveyed and

analyzed for practical reasons, but the team is seeking a suite of

projects that would balance various resource objectives and

restoration concerns.

Restoration

Close/Stabilize and Decommission more roads Currently the Forest Service is unable to fully fund the maintenance

of all existing roads on the Forest. Lack of road maintenance poses

environmental and safety risks. It is important to address these

issues through decommissioning or closure and stabilization, where

appropriate, such as where future management activities are not

expected to occur. The line officer has asked the team to consider

only closure and stabilization, not decommissioning, based on public

and interdisciplinary input. A preliminary list of roads to propose for

closure is being derived from a variety of criteria based on known

future management /access needs, aquatic and terrestrial risk posed

by the road, and feasibility to analyze within the scope of this project.

Roads

Evaluate selection/creating gaps around potential

marbled murrelet nest trees; fully evaluate impacts to

Marbled murrelet is an important wildlife concern in the Nisqually Thin

area, and effects on the murrelet will be evaluated.

Wildlife/Endangered Species

Act

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Scoping Comment Received Interdisciplinary Team Response Theme

murrelet

Thoroughly evaluate thinning effects on Northern

Spotted Owl and Critical Habitat, and potential

interaction with Barred Owl

NSO, critical habitat, and barred owl interactions will all be

considered through this analysis process.

Wildlife/Endangered Species

Act

Use Variable Density Thinning framework for stand

prescriptions in LSR and Matrix; use skips and gaps,

retain down wood and snags, etc.

The thinning prescriptions proposed will be consistent with direction

provided in the NWFP and Forest Plan for Late Successional

Reserve and Matrix, are consistent with the National Forest

Management Act, and are based on a synthesis of established

silvicultural science. Timber production for economic benefit is only

one goal of the Nisqually Thin project; ultimately the purpose in LSR

is to help stands develop more quickly into “old growth” stands.

Thinning prescription

Do not thin in Riparian Reserves unless treatments will

benefit aquatic and riparian resources

The thinning prescriptions proposed are consistent with direction

provided in the NWFP and Forest Plan for Late Successional

Reserve and Matrix, are consistent with the National Forest

Management Act, and are based on a synthesis of established

silvicultural science. Timber production for economic benefit is only

one goal of the Nisqually Thin project; ultimately the purpose in LSR

is to help stands develop more quickly into “old growth” stands.

Aquatic/thinning prescription

Minimize construction of temp roads The interdisciplinary team is seeking access management solutions

for efficient harvest of timber while still minimizing the extent of new

disturbance in the project area.

Roads

Seriously consider climate change in project analysis;

especially re: increased stream temps and earlier peak

flows effect on fish; how to create a more resilient

ecosystem with this project; disclose effects of natural

disturbance versus harvest regarding release of

The analysis will not attempt to quantify carbon emissions or

sequestration. However, the proposal will seek to create resilience in

forest and riparian ecosystems to a variety of climatic conditions and

potential future scenarios.

Climate change

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Scoping Comment Received Interdisciplinary Team Response Theme

carbon

Evaluate cumulative effects. Cumulative effects of the proposed action will be evaluated at the

appropriate temporal and spatial scales for the resources analyzed.

NEPA/Cumulative effects

Evaluate an adequate range of alternatives The IDT is discussing the need for additional alternatives. NEPA/Alternatives

Eliminate all harvest within 0.7 miles of historic or

existing Northern Spotted Owl site centers to

ameliorate potential adverse impacts to NSO

NSO, critical habitat, and barred owl interactions will all be

considered through this analysis process. Harvest buffers/restrictions

based on NSO sites will be evaluated and consulted with FWS, and

will rely on the best available science.

ESA/Wildlife

Consider an alternative that eliminates construction of

temporary roads entirely, or at least removes units 1,

29, and 34 from the unit pool due to high percentage of

temp roads within.

The team is investigating ways to minimize new temporary road

construction wherever possible. After discussing this comment, the

team reviewed units 1, 29, and 34 and

Roads

Establish a minimum 75-ft buffer between 52 road and

unit boundary to mitigate visual impacts

This suggestion will be included as design criteria to protect visual

quality.

Recreation/Visual

Creation/preservation of snags and down wood should

only be in Purpose and Need if there is certainty that

these activities will occur – since these activities are

dependent on uncertain funding, they should not be

displayed as a positive benefit or mitigation for sale-

related impacts

The planning and NEPA for any project does not ensure its

implementation on the ground, given the vagaries of federal

appropriations and how and which operations on the National Forest

are funded every year. It is reasonable to expect that creation of

snags and down wood will occur as proposed, based on the

expectation that timber harvest in the Nisqually Thin area would be

As of this writing, snags and down wood are not being viewed a

“mitigation” for sale-related impacts, but as a separate component of

the proposed action.

Proposed Action / Effects

analysis

EA should include consideration and protection of

species and habitat occurrences in nearby area (same

The wildlife analysis will include the best data available at the scale

relevant to the species for which we manage. If other agency data is

Wildlife data / analysis

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Scoping Comment Received Interdisciplinary Team Response Theme

townships), as mapped by Washington Dept of Fish

and Wildlife, particularly for elk forage

available and relevant, we will do our best to integrate it into the

analysis.

Encourages practices that will maintain habitat and set

forest stands on a trajectory toward contributing to

NSO and marbled murrelet habitat where possible and

appropriate

A majority of the vegetation prescription must be consistent with

developing late-successional characteristics given that much of the

project lies in LSR. Project design criteria for improving wildlife

habitat where possible will be included.

Wildlife

Commercial thinning harms “countless natural

resources… especially aquatic resources” –

(numerous views and citations opposing timber

harvest are attached to this assertion)

The thinning prescriptions proposed will be consistent with direction

provided in the NWFP and Forest Plan for Late Successional

Reserve and Matrix, are consistent with the National Forest

Management Act, and are based on a synthesis of established

silvicultural science. We understand that public perception of timber

harvest is controversial; however, there is a solid scientific foundation

for use of thinning in this region to enhance ecological values and

provide economic benefit.

Thinning (effects)

Roads damage the proper ecological functioning of the

natural resources in a forest (numerous views and

citations opposing forest road construction are

attached to this assertion); temp roads should be

obliterated after use

We acknowledge that roads can cause impacts to natural resources,

and these will be analyzed and disclosed in the EA. Any temporary

roads needed for the proposed action would be closed and stabilized

following use for harvest. The team is also looking at additional roads

to close and stabilize in the project area to reduce risk to natural

resources.

Roads (effects)

Scoping was conducted improperly / Comment period

is required for pre-decisional EAs

Scoping was conducted through a legal notice at the discretion of the

line officer, and was not intended to limit the time frame for providing

scoping input. The EA had not been drafted, and the proposed action

was not refined. The public has the option of providing input up until

the point at which a decision is made, but we requested scoping

responses be provided within a timeframe that would allow them to

be most helpful to integrate into the analysis.

NEPA/ Scoping process

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Scoping Comment Received Interdisciplinary Team Response Theme

Law requires that USFS obtain a NPDES permit and

disclose that the permit has been obtained

National Pollutant Discharge Elimination System (NPDES) is a permit

program that helps control water pollution by regulating point sources

that discharge pollutants into waters of the United States. The EPA

has revised 40 CFR 122.26(b)(14), its Phase I storm water

regulations, to clarify that storm water discharges from logging roads

do not constitute storm water discharges associated with industrial

activity and that a NPDES permit is not required for these storm

water discharges.

NPDES/ Water quality

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Appendix B: No Commercial Harvest Buffers No commercial harvest buffers for stream and wetlands by harvest unit (Note: stream buffers of

“0” are stream channels that fall within a larger stream buffer of a fish bearing channel).

Harvest Unit Nbr

Harvest Unit Size (ac)

Stream or waterbody

Stream Type

Interim Riparian Reserve width (ft)

No Commercial

Harvest Buffer

Width (ft)

No Commercial

Harvest Buffer in Unit (ac)

Percent Buffer

in Harvest

Unit

Total % of Buffer area in Harvest

Unit

1 125 Big Creek Perennial 360 180 1.2 0.96

125 Wetlands Wetlands 180 60 38.44 30.75 31.71

2 16.9 Big Creek Perennial 360 180 7.3 43.20 43.20

3 17.6 None None 180 0 0 0.00 0.00

4 108.7 Stream 1 Perennial 120 15.3 14.08

108.7 Stream 1a Perennial 180 30 0.56 0.52

108.7 Stream 1b Intermittent 180 30 0.14 0.13

108.7 Berry Creek

Perennial 360

180 1.2 1.10

108.7 Wetlands Wetlands 180 60 4.4 4.05

108.7 Nisqually

River Perennial

360 180 6.4 5.89 25.76

5 19.9 Stream 1 Intermittent 180 30 0.85 4.27

19.9 Stream 2 Intermittent 180 30 0.14 0.70

19.9 Berry Creek

Perennial 360

180 1.87 9.40 14.37

6 40.3 Stream 1 Intermittent 180 30 1.5 3.72

40.3 Stream 2 Intermittent 180 30 1.28 3.18

40.3 Big Creek Perennial 360 180 3.08 7.64 14.54

7 13.7 Stream 5 Intermittent 180 30 0.02 0.15

13.7 Big Creek Perennial 360 180 5 36.50 36.64

8 4.78 Stream 6 Intermittent 180 30 1.25 26.15

4.78 Stream 7 Intermittent 180 30 0.21 4.39 30.54

9 52.85 Stream 1 Intermittent 180 30 0 0.00

52.85 Mesatchee Intermittent 180 180 4.19 7.93 7.93

10 114.52 Stream 1 Perennial 180 30 1.32 1.15

114.52 Stream 2 Intermittent 180 30 0.4 0.35

114.52 Stream 3 Intermittent 180 30 0.19 0.17

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Harvest Unit Nbr

Harvest Unit Size (ac)

Stream or waterbody

Stream Type

Interim Riparian Reserve width (ft)

No Commercial

Harvest Buffer

Width (ft)

No Commercial

Harvest Buffer in Unit (ac)

Percent Buffer

in Harvest

Unit

Total % of Buffer area in Harvest

Unit

114.52 Stream 4 Intermittent 180 60 0.34 0.30

114.52 Stream 5 Intermittent 180 30 0.14 0.12

114.52 Stream 6 Intermittent 180 60 0.47 0.41

114.52 Stream 7 Perennial 180 60 2.46 2.15

114.52 Stream 7a Perennial 180 30 0.26 0.23

114.52 Stream 7b Intermittent 180 30 0.13 0.11

114.52 Stream 8 Intermittent 180 30 0.31 0.27

114.52 Stream 9 Perennial 180 60 0.83 0.72

114.52 Stream 9a Intermittent 180 60 1.45 1.27

114.52 Stream 9b Intermittent 180 60 0.83 0.72

114.52 Stream 9c Intermittent 180 60 0.33 0.29

114.52 Stream 10 Perennial 180 30 0.15 0.13

114.52 Stream 11 Perennial 180 30 0.16 0.14

114.52 Wetland 1 Perennial 180 60 1.6 1.40 9.93

11 17.35 Stream 1 Intermittent 180 60 0.67 3.86

17.35 Stream 2 Intermittent 180 30 0.7 4.03

17.35 Stream 3 Intermittent 180 30 0.71 4.09

17.35 Mesatchee Perennial 360

180 2.69 15.50

17.35 Wetland 1 Perennial 180 60 0 0.00 27.49

12 113.6 Stream 1 Intermittent 180 30 0.41 0.36

113.6 Stream2 Perennial 180 0 0 0.00

113.6 Stream 3 Perennial 180 0 0 0.00

113.6 Stream 4 Perennial 180 0 0 0.00

113.6 Stream 5 Intermittent 180 30 0.38 0.33

113.6 Stream 6 Perennial 180 0 0 0.00

113.6 Stream 7 Intermittent 180 30 0.31 0.27

113.6 Stream 8 Perennial 180 0 0 0.00

113.6 Stream 9 Intermittent 180 0 0 0.00

113.6 Stream 10 Intermittent 180 30 0.35 0.31

113.6 Stream

10a Intermittent 180 30 0.16 0.14

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Harvest Unit Nbr

Harvest Unit Size (ac)

Stream or waterbody

Stream Type

Interim Riparian Reserve width (ft)

No Commercial

Harvest Buffer

Width (ft)

No Commercial

Harvest Buffer in Unit (ac)

Percent Buffer

in Harvest

Unit

Total % of Buffer area in Harvest

Unit

113.6 Stream 11 Intermittent 180 0 0 0.00

113.6 Stream 12 Intermittent 180 30 0.33 0.29

113.6 Stream 13 Intermittent 180 30 0.27 0.24

113.6 Stream 14 Intermittent 180 0 0 0.00

113.6 Mesatchee Perennial 360

180 24.73 21.77

113.6 Wetland 1 Perennial 180 60 0 0.00 23.71

13 151.3 Stream 1 Intermittent 180 30 1 0.66

151.3 Stream 1a Intermittent 180 60 0.44 0.29

151.3 Stream 2 Intermittent 180 60 2.37 1.57

151.3 Stream 3 Intermittent 180 30 2.14 1.41

151.3 Stream 4 Intermittent 180 30 0.86 0.57

151.3 Stream 4a Intermittent 180 30 0.25 0.17

151.3 Stream 6 Intermittent 180 30 1.01 0.67

151.3 Stream 6a Intermittent 180 30 0.52 0.34

151.3 Stream 8 Intermittent 180 30 0.58 0.38

151.3 Stream 10 Intermittent 180 30 0.51 0.34 6.40

14 316.03 Stream 1 Intermittent 180 60 13.51 4.27

316.03 Stream 1a Intermittent 180 30 0.47 0.15

316.03 Stream 1b Intermittent 180 60 4.79 1.52

316.03 Stream 1c Intermittent 180 60 0.16 0.05

316.03 Stream 1d Intermittent 180 30 0.4 0.13

316.03 Stream 2 Intermittent 180 60 2.92 0.92

316.03 Stream 3 Intermittent 180 120 28.55 9.03

316.03 Stream 3a Intermittent 180 60 2.68 0.85

316.03 Stream 3b Intermittent 180 60 0.25 0.08

316.03 Stream 3c Intermittent 180 60 3.12 0.99

316.03 Stream

3c1 Intermittent 180 30 0.29 0.09

316.03 Stream

3c2 Intermittent 180 30 0.31 0.10

316.03 Stream 3d Intermittent 180 60 0.69 0.22

316.03 Stream 3e Intermittent 180 60 0.62 0.20

316.03 Stream 4 Intermittent 180 60 1.38 0.44

316.03 Stream 4a Intermittent 180 30 0.58 0.18

316.03 Stream 5 Intermittent 180 60 0.58 0.18

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Harvest Unit Nbr

Harvest Unit Size (ac)

Stream or waterbody

Stream Type

Interim Riparian Reserve width (ft)

No Commercial

Harvest Buffer

Width (ft)

No Commercial

Harvest Buffer in Unit (ac)

Percent Buffer

in Harvest

Unit

Total % of Buffer area in Harvest

Unit

316.03 Stream 6 Intermittent 180 60 0.12 0.04

316.03 Wetland 1 Perennial 180 60 5.7 1.80

316.03 Wetland 2 Perennial 180 60 2.25 0.71

316.03 Wetland 3 Perennial 180 60 0.58 0.18

316.03 Big Creek Perennial 360 180 14.8 4.68 26.82

15 36.87 Stream 1 Intermittent 180 60 3.96 10.74

36.87 Stream 1a Intermittent 180 60 0.32 0.87

36.87 Stream 1b Intermittent 180 60 0.53 1.44

36.87 Stream 2 Intermittent 180 30 0.62 1.68

36.87 Stream 3 Intermittent 180 30 0.56 1.52 16.25

16 100.43 Stream 1a Perennial 180 30 1.43 1.42

100.43 Stream

1a1 Perennial 180 60 2.12 2.11

100.43 Stream

1a2 Perennial 180 60 1.18 1.17

100.43 Stream

1a3 Intermittent 180 30 0.11 0.11

100.43 Stream 1a1a

Intermittent 180 30 0.07 0.07

100.43 Stream 1b Intermittent 180 30 0.19 0.19

100.43 Stream 1c Intermittent 180 0 0 0.00

100.43 Stream 2 Intermittent 180 30 0.26 0.26

100.43 Stream 3 Intermittent 180 60 0.97 0.97

100.43 Stream 4 Intermittent 180 30 0.02 0.02

100.43 Big Creek Perennial 360 180 6.25 6.22

100.43 Wetland 1 Perennial 180 60 3.63 3.61 16.16

17 80.01 Stream 1 Intermittent 180 30 1.09 1.36

80.01 Stream 2 Intermittent 180 60 0.63 0.79

80.01 Stream 3 Intermittent 180 30 0.5 0.62

80.01 Stream 4 Intermittent 180 60 1.77 2.21

80.01 Stream 5 Intermittent 180 60 8.4 10.50

80.01 Berry Creek

Intermittent 180 180 1.74 2.17 17.66

18 15.48 None - 180 - 0 0.00 0.00

19 59.79 Stream 3 Perennial 180 60 5 8.36

59.79 Stream 3a Intermittent 180 30 0.74 1.24

59.79 Stream

3a1 Intermittent 180 30 0.24 0.40

59.79 Stream 4 Perennial 180 30 0.46 0.77

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Harvest Unit Nbr

Harvest Unit Size (ac)

Stream or waterbody

Stream Type

Interim Riparian Reserve width (ft)

No Commercial

Harvest Buffer

Width (ft)

No Commercial

Harvest Buffer in Unit (ac)

Percent Buffer

in Harvest

Unit

Total % of Buffer area in Harvest

Unit

59.79 Stream 5 Perennial 180 60 4.13 6.91 17.68

20 56.57 Stream 1 Intermittent 180 60 0.62 1.10

56.57 Stream 2 Intermittent 180 30 0.32 0.57

56.57 Berry Creek

Perennial 360

180 0.78 1.38 3.04

21 256.77 Stream 1 Intermittent 180 60 1 0.39

256.77 Stream 2 Intermittent 180 60 2.66 1.04

256.77 Stream 3 Intermittent 180 30 0.49 0.19

256.77 Stream 4 Intermittent 180 30 0.26 0.10

256.77 Stream 5 Perennial 180 60 4.4 1.71

256.77 Stream 5a Intermittent 180 30 0.28 0.11

256.77 Stream 5b Intermittent 180 30 0.05 0.02

256.77 Stream 5c Intermittent 180 30 0.18 0.07

256.77 Stream 5d Perennial 180 60 2.3 0.90

256.77 Stream 6 Intermittent 180 60 3.2 1.25

256.77 Stream 6a Intermittent 180 60 1.76 0.69

256.77 Stream

6a1 Intermittent 180 30 0.11 0.04

256.77 Stream

6a2 Intermittent 180 30 0.03 0.01

256.77 Stream 7 Perennial 180 60 4.88 1.90

256.77 Stream 7a Intermittent 180 60 0.54 0.21

256.77 Stream 7b Perennial 180 30 1.36 0.53

256.77 Stream

7b1 Intermittent 180 30 0.24 0.09

256.77 Stream

7b2 Intermittent 180 60 1.43 0.56

256.77 Stream 8 Intermittent 180 30 0.86 0.33

256.77 Stream 9 Intermittent 180 30 0.64 0.25

256.77 Stream 9a Intermittent 180 60 2.54 0.99

256.77 Stream 10 Intermittent 180 60 5.56 2.17

256.77 Stream

10a Intermittent 180 30 0.13 0.05

256.77 Stream

10b Intermittent 180 60 1.04 0.41

256.77 Stream 11 Intermittent 180 30 1.13 0.44

256.77 Stream

11a Intermittent 180 30 0.56 0.22

256.77 Stream 12 Intermittent 180 30 0.99 0.39

256.77 Stream

12a Intermittent 180 30 0.59 0.23

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Harvest Unit Nbr

Harvest Unit Size (ac)

Stream or waterbody

Stream Type

Interim Riparian Reserve width (ft)

No Commercial

Harvest Buffer

Width (ft)

No Commercial

Harvest Buffer in Unit (ac)

Percent Buffer

in Harvest

Unit

Total % of Buffer area in Harvest

Unit

256.77 Stream 13 Intermittent 180 60 3.98 1.55

256.77 Berry Creek

Perennial 360

180 2.53 0.99

256.77 Wetland 1 Perennial 180 60 3.51 1.37

256.77 Wetland 2 Perennial 180 60 0.73 0.28 19.46

22 53.89 Stream 1 Perennial 180 60 4.33 8.03

53.89 Stream 1a Intermittent 180 60 0.1 0.19

53.89 Stream 1b Intermittent 180 30 0.36 0.67

53.89 Stream 2 Intermittent 180 30 0.07 0.13

53.89 Stream 3 Intermittent 180 30 1.05 1.95 10.97

23 47.21 Stream 1 Intermittent 180 30 0.72 1.53

47.21 Stream 1a Perennial 180 30 1.32 2.80 4.32

24 35.94 Stream 1 Intermittent 180 30 0.71 1.98

35.94 Stream 2 Intermittent 180 60 0.46 1.28

35.94 Stream 3 Perennial 180 60 4.85 13.49

35.94 Stream 3a Intermittent 180 30 0.36 1.00

35.94 Stream 3b Perennial 180 60 0.85 2.37

35.94 Stream 4 Perennial 180 30 0.32 0.89 21.01

25 13.73 Stream 1 Intermittent 180 30 0.11 0.80 0.8

26 41.56 Stream 1 Intermittent 180 60 2.06 4.96

41.56 Stream 2 Perennial 180 60 1.88 4.52

41.56 Rocky Creek

Perennial 180 120 0.13 0.31 9.79

27 35.18 Stream 1 Perennial 180 30 1.36 3.87

35.18 Stream 1a Perennial 180 60 0.22 0.63

35.18 Wetlands Wetlands 180 60 1.22 3.47

35.18 Berry Creek

Perennial 360

180 0.1 0.28 8.24

28 95.13 Stream 1 Intermittent 180 30 0.08 0.08

95.13 Stream 2 Intermittent 180 60 0.71 0.75

95.13 Stream 3 Intermittent 180 60 5.66 5.95

95.13 Stream 3a Intermittent 180 60 0.18 0.19

95.13 Stream 3b Intermittent 180 30 0.86 0.90

95.13 Stream 3c Intermittent 180 60 0.82 0.86

95.13 Stream 3d Intermittent 180 60 1.87 1.97

95.13 Stream 4 Intermittent 180 60 4 4.20

95.13 Stream 4a Intermittent 180 60 0.07 0.07

95.13 Stream 5 Intermittent 180 60 3.18 3.34

95.13 Stream 5a Intermittent 180 60 0.38 0.40

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202

Harvest Unit Nbr

Harvest Unit Size (ac)

Stream or waterbody

Stream Type

Interim Riparian Reserve width (ft)

No Commercial

Harvest Buffer

Width (ft)

No Commercial

Harvest Buffer in Unit (ac)

Percent Buffer

in Harvest

Unit

Total % of Buffer area in Harvest

Unit

95.13 Berry Creek

Perennial 360

180 7.88 8.28

95.13 Wetland 1 Perennial 180 60 1.08 1.14

95.13 Wetland 2 Perennial 180 60 0.6 0.63 28.77

29 446.27 Stream 10 Perennial 180 60 3.58 0.80

446.27 Stream

10a Perennial 180 60 0.35 0.08

446.27 Stream

Complexes

Intermittent and

Perennial 180 30/60 152 34.06

446.27 Wetlands Wetlands 180 60 1.2 0.27 34.41

30 92.13 Stream 10 Perennial 180 60 1.14 1.24

92.13 Stream 13 Intermittent 180 30 2.85 3.09

92.13 Stream

13a Intermittent 180 30 1.63 1.77

92.13 Stream

13b Intermittent 180 30 0.25 0.27

92.13 Stream 14 Intermittent 180 60 0.29 0.31

92.13 Stream

14a Intermittent 180 60 0.98 1.06

92.13 Stream 15 Intermittent 180 30 0.13 0.14

92.13 Wetlands Wetlands 180 60 12.3 13.35 20.00

31 80.97 Stream 1 Perennial 180 30 1.22 1.51

80.97 Stream 1a Perennial 180 30 1.7 2.10

80.97 Stream

1a1 Intermittent 180 60 1.58 1.95 5.56

32 118.79 Stream 1 Intermittent 180 60 1.21 1.02

118.79 Stream 2 Intermittent 180 60 0.72 0.61

118.79 Stream 3 Intermittent 180 30 1.93 1.62

118.79 Stream 3a Intermittent 180 30 0.19 0.16

118.79 Stream 4 Intermittent 180 60 0.94 0.79

118.79 Stream 5 Intermittent 180 60 1.1 0.93

118.79 South Fork Catt Creek

Perennial 360

180 14.13 11.89 17.02

33 69.79 Stream 2 Perennial 180 60 1.6 2.29

69.79 Stream 3 Intermittent 180 30 1 1.43

69.79 Stream 3a Intermittent 180 60 0.43 0.62

69.79 South Fork Catt Creek

Perennial 360

180 21.55 30.88

69.79 Catt Creek Perennial 360 180 3.63 5.20

69.79 Wetland 6 Perennial 180 60 0.48 0.69 41.11

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Harvest Unit Nbr

Harvest Unit Size (ac)

Stream or waterbody

Stream Type

Interim Riparian Reserve width (ft)

No Commercial

Harvest Buffer

Width (ft)

No Commercial

Harvest Buffer in Unit (ac)

Percent Buffer

in Harvest

Unit

Total % of Buffer area in Harvest

Unit

34 106.43 Stream 1 Intermittent 180 60 2.56 2.41

106.43 Stream 2 Intermittent 180 60 3.66 3.44

106.43 Stream 8 Intermittent 180 60 4.65 4.37

106.43 Stream 8a Intermittent 180 30 0 0.00 10.21

35 52.27 Stream 1 Intermittent 180 60 0 0.00

52.27 Stream 3 Intermittent 180 30 0 0.00

52.27 Stream 4 Intermittent 180 60 5.27 10.08

52.27 Stream 4a Intermittent 180 30 0.14 0.27

52.27 Stream 4b Intermittent 180 60 1.09 2.09

52.27 Stream 4c Intermittent 180 60 0.84 1.61

52.27 Stream 4d Intermittent 180 60 0.38 0.73

52.27 Stream 5 Intermittent 180 30 0 0.00

52.27 Catt Creek Perennial 360 180 22.6 43.24 58.01

36 56.87 Stream 1 Intermittent 180 30 1.07 1.88

56.87 Stream 1a Intermittent 180 30 0.13 0.23

56.87 Stream 1b Intermittent 180 30 0.63 1.11

56.87 Stream 1c Intermittent 180 60 1.06 1.86

56.87 Stream 2 Intermittent 180 60 2.56 4.50

56.87 Stream 2a Intermittent 180 30 0.96 1.69

56.87 Stream 3 Intermittent 180 30 0 0.00

56.87 Stream 4 Intermittent 180 60 0.09 0.16

56.87 Stream 4a Intermittent 180 30 0.14 0.25

56.87 Stream 4b Intermittent 180 60 0.33 0.58

56.87 Stream 4c Intermittent 180 30 0.13 0.23

56.87 Catt Creek Perennial 360 180 0.77 1.35 13.84

37 30.79 Stream2 Intermittent 180 30 0 0.00

30.79 Stream 3 Intermittent 180 60 0.22 0.71

30.79 Stream 4 Intermittent 180 30 0.15 0.49

30.79 Stream 4c Intermittent 180 30 0.05 0.16

30.79 Stream 4d Intermittent 180 60 0 0.00

30.79 Stream 5 Intermittent 180 30 0 0.00

30.79 Stream 6 Intermittent 180 60 0.26 0.84

30.79 Stream 7 Intermittent 180 60 0.4 1.30

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204

Harvest Unit Nbr

Harvest Unit Size (ac)

Stream or waterbody

Stream Type

Interim Riparian Reserve width (ft)

No Commercial

Harvest Buffer

Width (ft)

No Commercial

Harvest Buffer in Unit (ac)

Percent Buffer

in Harvest

Unit

Total % of Buffer area in Harvest

Unit

30.79 Stream 8 Intermittent 180 60 0.35 1.14

30.79 Catt Creek Perennial 360 180 21.37 69.41

30.79 Wetland 4 Perennial 180 60 0.07 0.23

30.79 Wetland 5 Perennial 180 60 0.26 0.84

30.79 Wetland 6 Perennial 180 60 0.59 1.92 77.04

38 109.07 Stream 1 Intermittent 180 60 5.47 5.02

109.07 Stream 1a Intermittent 180 30 0.55 0.50

109.07 Stream 3 Intermittent 180 30 1.66 1.52

109.07 Catt Creek Perennial 360 180 5.9 5.41

109.07 South Fork Catt Creek

Perennial 360

180 3.38 3.10 15.55

39 82.78 Stream 1 Intermittent 180 60 0.54 0.65

82.78 Stream 5 Perennial 180 60 3.09 3.73

82.78 Stream 5a Intermittent 180 30 0.26 0.31

82.78 Stream

5a1 Intermittent 180 60 1.5 1.81

82.78 Stream

5a2 Intermittent 180 60 0.8 0.97

82.78 Stream

5a3 Intermittent 180 60 0.5 0.60

82.78 Stream 5b Intermittent 180 30 0.59 0.71

82.78 Stream 7 Intermittent 180 30 0.65 0.79

82.78 Stream 8 Intermittent 180 30 0.74 0.89

82.78 Stream 8a Intermittent 180 30 0.17 0.21

82.78 Stream 9 Intermittent 180 60 1.24 1.50

82.78 Catt Creek Perennial 360 180 11.19 13.52 25.69

40 70.75 Stream 2 Intermittent 180 60 0.83 1.17

70.75 Stream 3 Intermittent 180 60 0.84 1.19

70.75 Stream 4 Intermittent 180 60 3.6 5.09

70.75 Stream 4a Intermittent 180 30 0.11 0.16

70.75 Stream 5 Perennial 180 60 1.55 2.19

70.75 Stream 5a Intermittent 180 60 4.93 6.97

70.75 Stream

5a4 Intermittent 180 30 0.16 0.23

70.75 Stream

5a5 Intermittent 180 30 0.08 0.11

70.75 Stream

5a6 Intermittent 180 30 0.22 0.31

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Harvest Unit Nbr

Harvest Unit Size (ac)

Stream or waterbody

Stream Type

Interim Riparian Reserve width (ft)

No Commercial

Harvest Buffer

Width (ft)

No Commercial

Harvest Buffer in Unit (ac)

Percent Buffer

in Harvest

Unit

Total % of Buffer area in Harvest

Unit

70.75 Stream

5a7 Intermittent 180 30 0 0.00

70.75 Stream 5b Intermittent 180 30 0.94 1.33

70.75 Stream 6 Intermittent 180 30 0.77 1.09 19.83

41 53.92 Stream 1 Intermittent 180 60 3.01 5.58

53.92 Catt Creek Perennial 360 180 8.01 14.86 20.44