4_FSI_Practice_Standard_666_1017T.pdf
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666-CPS-1
NRCS, NHCP NRCS, KY
September 2015 October 2017
Conservation practice standards are reviewed periodically and updated if needed. To obtain the current version of this standard, contact your Natural Resources Conservation Service State office or visit the Field Office Technical Guide.
Natural Resources Conservation Service
CONSERVATION PRACTICE STANDARD
FOREST STAND IMPROVEMENT
Code 666
(Ac.)
DEFINITION
The manipulation of species composition, stand structure, or stand density by cutting or killing selected trees or understory vegetation to achieve desired forest conditions or obtain ecosystem services.
PURPOSE
• Improve and sustain forest health and productivity
• Reduce damage from pests and moisture stress
• Initiate forest stand regeneration
• Reduce fire risk and hazard and facilitate prescribed burning
• Restore or maintain natural plant communities
• Improve wildlife and pollinator habitat
• Alter quantity, quality, and timing of water yield
• Increase or maintain carbon storage
CONDITIONS WHERE PRACTICE APPLIES
All land where the quantity and quality of trees can be enhanced.
This standard is not applicable for Alley Cropping, Code 311, Multi-story Cropping, Code 379, Windbreak Shelterbelt establishment, Code 380, operation and maintenance, and Windbreak/Shelterbelt Renovation, Code 650.
CRITERIA
General Criteria Applicable to All Purposes
Describe the extent or size and orientation of treatment area(s).
Identify and retain preferred tree and understory species to achieve all planned purposes and landowner objectives.
Use available guidelines for species and species groups to determine spacing, density, size-class distribution, number of trees, and amount of understory species to be retained. Schedule treatments to avoid overstocked conditions using approved silvicultural/ stocking guides.
Describe the current and desired future condition of each stand that will be treated. Include the species, cover type, and size-class distribution. Stocking will be described in terms of crop trees per acre, basal area per acre, trees per acre, between-tree spacing, or by any other appropriate and professionally accepted density or stocking protocol.
http://www.nrcs.usda.gov/wps/portal/nrcs/sitenav/national/states/ http://www.nrcs.usda.gov/wps/portal/nrcs/main/national/technical/fotg/
666-CPS-2
NRCS, NHCP NRCS, KY
September 2015 October 2017
Refer to WIN-PST criteria in NRCS Conservation Practice Standard (CPS) Code 595, Integrated Pest Management, and comply with applicable State and local laws if an herbicide will be used.
Time tree felling to avoid buildup of insect or disease populations.
Implement forest stand improvement activities in ways that avoid or minimize soil erosion, compaction, rutting, and damage to remaining vegetation, and that maintain hydrologic conditions. Protect site resources by selecting the method, felling direction and timing of tree felling, and heavy equipment operation. For temporary access use NRCS CPS Code 655, Forest Trails and Landings, to protect soil and site resources from vehicle impacts.
Use NRCS CPS Code 560, Access Road, for more heavily used roads associated with forest stand improvement activities.
Where slash and debris will be generated, use NRCS CPS Code 384, Woody Residue Treatment, to appropriately treat slash and debris, as necessary, to assure that it will not present an unacceptable fire, safety, environmental, or pest hazard. Remaining woody material will be placed so that it does not interfere with the intended purpose or other management activities. Do not burn vegetative residues except where fire hazard or threats from diseases and insects are of concern or when other management objectives are best achieved through burning. When slash and other debris will be burned onsite use NRCS CPS Code 338, Prescribed Burning.
Comply with State best management practices for water quality.
Additional Criteria to Improve and Sustain Forest Health and Productivity
Treatments, including woody biomass removal, will be sustainable and will not compromise soil organic matter, the recruitment and retention of coarse woody debris, or wildlife habitat. If needed, use NRCS CPS 384, Woody Residue Treatment. If applicable, use biomass harvesting guidelines (The Forest Guild, 2010) and/or State guidance.
Manipulate stand characteristics to mitigate risk of insects and disease. Examples of stand manipulations include creating a diversity of tree species and a mosaic of age classes.
Additional Criteria to Reduce Fire Risk and Hazard and Facilitate Prescribed Burning
Reduce stocking rates and alter spatial arrangement of trees to minimize crown-to-crown spread of fire.
Use criteria for wildfire risk and damage reduction, including reduction of ladder fuels, in NRCS CPS Codes 383, Fuel Break; 384, Woody Residue Treatment; or 394, Firebreak, as appropriate.
Additional Criteria to Improve Wildlife and Pollinator Habitat
Manage for specific or a variety of cover types, species, size-classes, and stocking rates at the appropriate scale that meet desired wildlife habitat requirements.
Create, recruit, and maintain sufficient snags, nest, cavity, and den trees, and down woody material to meet requirements of desired species.
Use habitat creation and maintenance criteria in NRCS CPS Codes 647, Early Successional Habitat Development/Management; Code 643, Restoration and Management of Rare and Declining Habitats;
Code 645, Upland Wildlife Habitat Management; or Code 644, Wetland Wildlife Habitat Management, as appropriate, to manage wildlife-related activities.
666-CPS-3
NRCS, NHCP NRCS, KY
September 2015 October 2017
Refer to Upland Wildlife Habitat Management, Code 645, and Kentucky Wildlife Habitat Evaluation Procedure (KWHEP) for strategies to enhance or manipulate forest stands for wildlife -– KY Field Office Technical Guide (FOTG) – Section IV – Tools – Wildlife.
For pollinator habitat maintain an open understory and encourage forest gaps that support diverse forbs and shrubs that provide pollen and nectar for pollinators. In addition, retain very early and early blooming flowering tree species during harvest activities, especially near edges of fields and openings. Refer to the Kentucky Pollinator Handbook for information regarding species and habitat for pollinators in forestry settings – KY Field Office Technical Guide (FOTG) – Section IV – Tools – Pollinators.
Additional Criteria to Alter Quantity, Quality and Timing of Water Yield
Create a mosaic of age classes to increase water yield and stabilize seasonal water yield from watersheds.
Create openings in the forest canopy to allow more light to reach the ground, stimulating understory vegetation and diversifying plant species composition and vertical structure. These improvements will increase rainfall infiltration and reduce runoff thereby reducing soil erosion and improving water quality.
Additional Criteria to Increase Carbon Storage
Manage for tree species and stocking rates that have higher rates of growth and potential for carbon sequestration.
CONSIDERATIONS
Considerations for Wildlife and Pollinator Habitat
State Wildlife Habitat Guidelines, Wildlife Habitat Evaluation Procedure, and Forestland Assessment Scorecard are useful tools in planning forest stand Improvement.
Consider removing vines from crop trees but retaining vines with wildlife value (e.g., grape and poison ivy) on non-crop trees.
Increase quantity and quality of important mast (seeds, catkins, fruits, and nuts) sources for wildlife through crop tree management and other techniques.
Improve horizontal diversity or patchiness (of different age class units) across the forest for a variety of wildlife.
Improve or maintain vertical structure or vegetative layering in treated stands.
Favor declining wildlife species by providing appropriately sized treatment areas or blocks of habitat.
Time forest stand improvement activities to minimize disturbance of seasonal pollinator and wildlife activities, such as nesting, movement, etc.
Manage for a variety of native tree species and stocking rates that create light conditions that meet desired wildlife and pollinator species food and cover requirements
• Maintain a good balance of white oaks and red oaks
• Ensure that overstory and understory diversity will be provided to maximize benefits
• Maintain 2 to 4 cavity trees per acre or identify similar number of larger low quality trees to remain for cavity development after the thinning operation
666-CPS-4
NRCS, NHCP NRCS, KY
September 2015 October 2017
• Minimize improvement activities that disturb seasonal wildlife activities
• When selecting trees to cut or kill leave a variety of height classes to improve or maintain vertical structure in treated stands
• Appropriately sized temporary forest openings may be necessary to create early successional habitat necessary for many declining wildlife species
Considerations for Improving and Sustaining Forest Health and Productivity
Consider crop tree management (Perkey et al. 1994) when making decisions about which trees to retain and which to cut, kill cut, or kill.
If available use sanitation-salvage and risk-rating criteria to determine trees to remove during forest stand improvement operations (see Thinning and Sanitation in Donaldson and Seybold 1998).
Silvicultural objectives and harvest-regeneration strategies may change over time and may be limited by prior management.
Consider enlisting the assistance of a professional forester when seeking to rehabilitate degraded stands that have been repeatedly subjected to exploitative harvesting (high-grading). Often a complex site-specific treatment plan must be developed to overcome repeated exploitative timber harvest.
Successful regeneration of desirable species is usually dependent upon timely application of forest stand improvement and other practices, such as prescribed burning, site preparation, tree and shrub establishment, prescribed grazing, and access control.
The extent, timing, size of treatment area, or intensity of the practice application, should be adjusted to minimize cumulative effects (onsite and offsite), such as hydrologic and stream alteration, habitat fragmentation, nutrient cycling, biodiversity, and visual resources.
Consider retaining at least 1/4 to 1/3 of the slash, tops, and limbs after harvest to protect site productivity.
When using whole-tree harvesting systems minimize the removal of needles or leaves by harvesting in the dormant season, retaining fine woody materials onsite, or leaving felled trees onsite to allow for needle or leaf drop.
Consider controlling invasive plants if they are encountered while conducting forest stand improvement.
Use NRCS CPS Codes 314, Brush Management; or 315, Herbaceous Weed control, as appropriate.
Invasive or noxious woody vegetation should be monitored and controlled by either mechanical or chemical methods. Consider the extent of invasive species infestation and the impact of completing forest stand improvement on the stand. Opening of the overstory canopy and subsequent increase in light, may potentially increase the infestation. See Brush Management (314) for control of woody nvasives and Herbaceous Weed Control (315) for control of herbaceous invasives.
When available, report the minimum criteria (diameter at breast height, log length, etc.) for commercial forest products (sawtimber, pulpwood, etc.) in order to know when to direct a client to a professional forester.
Consider advising landowners to secure a written contract with a service provider that specifically describes the extent of activity, duration of activity, liability and responsibilities of each party, and amount and timing of payments for services provided.
For purposes other than improving wildlife habitat, the practice should be timed to minimize the disturbance of seasonal pollinator(s) and wildlife nesting activities.
666-CPS-5
NRCS, NHCP NRCS, KY
September 2015 October 2017
Consider removing vines from crop trees but retaining vines with wildlife value (e.g. grape and poison ivy) on non-crop trees.
Excessive removal of ladder fuels may eliminate advanced regeneration and vertical structure.
Advise clients of responsibilities of wildfire control and encourage consideration of the development of a wildfire control plan including “defensible” space, access routes, fire-season water source, and location of wildfire control facilities
Considerations for Increasing Carbon Storage
To increase carbon storage, consider shifting from even-aged to uneven-aged management to increase the retention of carbon onsite. Use regeneration methods that encourage advanced regeneration and retention of mature trees, such as shelterwood, to retain carbon onsite for longer periods. Consider retaining snags and downed woody debris for additional onsite carbon storage, and adopt techniques for maintaining soil quality, including organic carbon retention.
To grow trees that can store carbon in durable manufactured products, consider lengthening rotations to retain mature trees longer and grow to larger sizes; also consider using crop tree management techniques (Perkey et al. 1994) to concentrate growth on suitable long-lived species.
Considerations for Visual Quality
When forest stand improvement is being used to improve visual quality consider leaving trees that are attractive in shape and structure or flower and are appropriate to the site, especially around structures, roads, and home sites.
PLANS AND SPECIFICATIONS
Plans and specifications for applying this practice shall be prepared for each site and recorded using approved specification sheets, implementation requirements (job sheets), technical notes, and narrative statements in the conservation plan, or other acceptable documentation. Clearly state the goals and objectives of the forest stand improvement. Specific stand-stocking guidelines will clearly document both the pre- and post-treatment stand condition.
All conservation plans recommending this practice will complement plans and specifications prepared by:
• Kentucky Division of Forestry (KDF) staff
• Technical Service Providers (TSPs) certified in the forestry category and Conservation Activity Plan (CAP) 106 Forest Management Plan
• Private consultant forester in good standing with the Association of Consulting foresters (ACF) or Society of American Foresters (SAF).
At a minimum, the following will be identified (as appropriate):
• Landowner goals/objectives
• Type of treatment
• Treatment acreage / orientation/aspect
• Treatment location
• Existing conditions
• Preferred tree and understory species
• Expected outcomes/Desired future condition
• Treatment specifications
666-CPS-6
NRCS, NHCP NRCS, KY
September 2015 October 2017
• Spacing, density, size class, number and amounts of trees and understory species to be retained
• Stocking guidelines shall contain stocking in terms of basal area, spacing or trees per acre by species and size class distribution.
• The harvest-regeneration strategy will be identified for all planned forest improvement harvesting:
o Uneven-aged management systems (e.g., single-tree selection, group selection, coppice selection) o Even-aged management (e.g., clear-cut, seed-tree, shelterwood, coppice)
• Treatment dates
• Win-PST Soil/Pesticide Interaction Hazard Ratings when herbicide treatments are to be used
• Operation and maintenance
OPERATION AND MAINTENANCE
Prepare an Operation and Maintenance plan for the site and review it with the operator. The plan will describe actions that must be taken to ensure that the practice is applied correctly during its design life.
As a minimum, include periodic inspections for assessment of insects, disease, and other pests, storm damage, and damage by trespass. Use NRCS CPS Code 655, Forest Trails and Landings, to control erosion on forest roads, skid trails, landings, and adjacent areas by installing/maintaining vegetative and structural practices. Treatments needed for pests—see Additional Criteria to Improve and Sustain Forest Health and Productivity section in this document. Treatments needed for storm damage—use NRCS CPS Code 384, Woody Residue Treatment, to appropriately treat slash and debris. Treatments for damage by trespass: use NRCS CPS Code 472, Access Control, to prevent future damage.
These follow-up inspections are helpful in determining the need for additional treatment by forest stand improvement.
REFERENCES
Clatterbuck, W.K. 2006. Treatments for Improving Degraded Hardwood Stands. Univ. of KY CES pub.
FOR-104. Available at: http://www2.ca.uky.edu/forestryextension/Publications/FOR_FORFS/for104.pdf (verified January 21, 2015).
Donaldson, S., and S.J. Seybold. 1998. Thinning and Sanitation: Tools for the Management of Bark Beetles in the Lake Tahoe Basin. NV Cooperative Extension Service Fact Sheet 98-42. Available at:
http://www.unce.unr.edu/publications/files/ho/other/fs9842.pdf (verified January 21, 2015).
Firewise Communities. Available at: http://www.firewise.org/ (verified January21, 2015).
Gartner, T., J. Mulligan, S. Rowan, and J. Gunn, eds. 2013. Natural Infrastructure: Investing in Forested Landscapes for Source Water Protection in the United States. World Resources Institute. Available at:
http://www.wri.org/publication/natural-infrastructure (verified 21 January 2015).
Heiligmann, R.B. 1998. Controlling Undesirable Trees, Shrubs and Vines in your Woodland. Ohio St.
Univ. Exten. Pub. F-45-97. Available at: http://ohioline.osu.edu/for-fact/0045.html (verified January, 21, 2015).
Kenefic, L.S., and R.D. Nyland. 2005. Proceedings of the Conference on Diameter-Limit Cutting in Northeastern Forests. Gen. Tech. Report NE-342, USFS, NE Res. Sta. Available at:
http://www.fs.fed.us/ne/newtown_square/publications/technical_reports/pdfs/2006/ne_gtr342.pdf (verified January 21, 2015).
Perkey, A.W., B.L. Wilkins, and H.C. Smith. 1994. Crop Tree Management in Eastern Hardwoods.
USDA-Forest Service, NE Area S&PF, Pub. NA-TP-19-93. Available at:
http://www.na.fs.fed.us/pubs/ctm/ctm_index.html (verified January 21, 2015).
http://www2.ca.uky.edu/forestryextension/Publications/FOR_FORFS/for104.pdf http://www.unce.unr.edu/publications/files/ho/other/fs9842.pdf http://www.firewise.org/ http://www.wri.org/publication/natural-infrastructure http://ohioline.osu.edu/for-fact/0045.html http://www.fs.fed.us/ne/newtown_square/publications/technical_reports/pdfs/2006/ne_gtr342.pdf http://www.na.fs.fed.us/pubs/ctm/ctm_index.html
666-CPS-7
NRCS, NHCP NRCS, KY
September 2015 October 2017
The Forest Guild. 2010. Forest Biomass Retention and Harvesting Guidelines for the Northeast.
Available at: http://www.forestguild.org/publications/research/2010/FG_Biomass_Guidelines_NE.pdf (verified January 21, 2015).
Stringer, and Merker: “Technical Guide to Crop Tree Release in Hardwood Forests” Professional Hardwood Notes, University of TN Extension, PB1774y 21, 2015).
USDA-NRCS. National Biology Manual, National Forestry Handbook, and National Forestry Manual.
Available on the NRCS eDirectives system: http://directives.sc.egov.usda.gov/default.aspx.
http://www.forestguild.org/publications/research/2010/FG_Biomass_Guidelines_NE.pdf http://directives.sc.egov.usda.gov/default.aspx
| DEFINITION |
| PURPOSE |
| CONDITIONS WHERE PRACTICE APPLIES |
| CRITERIA |
| General Criteria Applicable to All Purposes |
| Additional Criteria to Improve and Sustain Forest Health and Productivity |
| Additional Criteria to Reduce Fire Risk and Hazard and Facilitate Prescribed Burning |
| Additional Criteria to Improve Wildlife and Pollinator Habitat |
| Additional Criteria to Alter Quantity, Quality and Timing of Water Yield |
| Additional Criteria to Increase Carbon Storage |
| CONSIDERATIONS |
| Considerations for Wildlife and Pollinator Habitat |
| Considerations for Improving and Sustaining Forest Health and Productivity |
| Considerations for Increasing Carbon Storage |
| Considerations for Visual Quality |
| PLANS AND SPECIFICATIONS |
| OPERATION AND MAINTENANCE |
| REFERENCES |
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