Shrub Willow Living Snow Fences show potential for snow trapping and reduced drift length shortly after planting

Similar documents
Capstone Seminar Justin P. Heavey M.S. Candidate Department of Forest and Natural Resource Management Major Professor: Dr.

STRUCTURE AND FUNCTION OF LIVING SNOW FENCES IN NEW YORK STATE

Protocol for Pre-Installation field Measurements for Prospective Living Snow Fence Sites in New York State

Justin P. Heavey Dr. Timothy A. Volk. Living snow fences show potential for large storage capacity and reduced drift length shortly after planting

Field Measurements and Analysis of Effectiveness of Operationally-Mature Snow Fence Vegetation in New York State

A windbreak across a large field distributes snow throughout the field, providing winter protection and moisture for crop production.

Commercial Production & Harvesting of Shrub Willow Crops in NY State

Species Matrix for New York State

Windbreaks: An Agroforestry Practice

Windbreak Design. United States Department of Agriculture June 2002 Planning/Designing/Maintaining Windbreak/Shelterbelt 1. Windbreak / Shelterbelt

Materials: a piece of sandpaper, a piece of wood to sandpaper, a stone to sandpaper

Willow Biomass Silviculture With Mini-rotations

Windbreaks, hedgerows and shelterbelts

Transportation Agency Tool to Analyze Benefits of Living Snow Fences

Living Snow Fence Training in Buffalo, NY (May 13, 2010)

Silviculture and Harvesting Abstracts

3. Planning a shelterbelt

Assessing the Use of Shrub-Willows for Living Snow Fences in Minnesota

Introduction to Windbreaks

UM Research on Alternatives to Delivered Fuels. Gary Wyatt, Extension Educator Diomy Zamora, Extension Educator

Planning Field Shelterbelts for the Prairies

Soil CO 2 Flux in Short Rotation Willow Biomass Crop Across 21- year Chronosequence as Affected by Continuous Production and Tear Out Treatments

Review of Literature on Living Snow Fences

COPPICE SILVICULTURE: SOME ALTERNATIVES AND APPLICATIONS

Planting Trees Along Local Streets

Chapter 5 Renewable Energy. Helping to Sustainably Power the Town of Veteran into the Future

Living snow fences Monday, June 13, 2011

Windbreaks. Some Basic Whats, Whys and Hows. Richard Straight US Forest Service USDA National Agroforestry Center

A Summary of Existing Living Snow Fence Programs in North America

Shelter Woods and Woodland Grazing. Malcolm Young, Forestry Consultant

Willow Biomass Production, Potential and Benefits

Windbreaks For Rural Living

Opportunities Using Trees for Vegetative Environmental Buffers

Category V: Undersized trees 78,070 48,015 49,727. Density Classes (stems/ha)

Shelterbelts for Livestock Farms in Alberta Overview

The effect of vegetative buffers on wind and dispersion of particulate matter around poultry barns

24 Dimensions International

What are they? What do they look like? How do they work? What are the benefits? How do you design them? Where do you put them?

6 93 Corridor TUNNEL CROSS SECTION 42.0' 24.0' WITH 21.0' WITHOUT 1.5' 6.0' 12.0' 12.0' 6.0' 4.0' 0.5' CLEARANCE ENVELOPE (36' W x 16.

MU Guide PUBLISHED BY UNIVERSITY EXTENSION, UNIVERSITY OF MISSOURI-COLUMBIA

How Urban Green Infrastructure Can Affect Air Pollution and Health

A Summary of Agroforestry Systems for Connecticut and New England

3/8/2015. What You Will Learn: Intermediate Use Areas: Considerations and Tools. Time line for Forestry Activities

Discovering Profits in Unlikely Places: Agroforestry Opportunities for Added Income

Arkansas Voluntary Smoke Management Guidelines for Row Crop Burning

THE FOREST NURSERY: ITS CHARACTER AND OPERATIONS

AgroParisTech, Paris cedex 05, France 2. Canadian Wood Fibre Centre, NRCan. 3. SUNY, Syracuse

Is anyone else ready for this kind of weather?

ALBERTA TREE NURSERY AND HORTICULTURE CENTRE

Memorandum of Understanding (MOU) Living Snow Fence Partnership Program

CC338 Trees and Shrubs in the Conservation Reserve Program

Planning Commission November 20, 2013 URBAN FORESTRY LANDSCAPING CODE UPDATES

BEAUTIFUL LIVING WINDBREAKS

University of Missouri sees biomass as future for campus energy generation

Low-Impact Site and Green Building Exterior Management Plan (Policies for a Green and Sustainable Campus)

Defining Forests. forestry hardwood log native forest old-growth forest. E-unit: Defining Forests Page 1

Produce Multiple Benefits

USDA Biomass Crop Assistance Program Project Area 10 - Northern New York Willow Annual Report 2014

Windbreaks for odour dispersion

CHARTER TOWNSHIP OF PORT HURON

COLORADO STATE FOREST SERVICE. Orientation for Master Volunteer Forest Steward

Siting and Taxing Wind Farms in Illinois

2018 Product Use Guide

Stream Restoration Planting for Success

Canada s Use of Buffer Zones for Risk Mitigation

MINUTES TOWN OF HORSEHEADS PLANNING BOARD MEETING April 4, 2018

Memorandum of Understanding (MOU) Living Snow Fence Partnership Program

Opportunities Using Trees for Vegetative Environmental Buffers

Above- and Below-ground Biomass and Soil Organic Carbon Inventories of Willow Biomass Crops Across a 19-year Chronosequence

Success Stories from Canadian Forests

Estimates of Sustainably Produced Biomass Feedstocks in New York Timothy A. Volk SUNY-ESF

SILVICULTURE & WILDLIFE HABITAT MANAGEMENT

ENVIRONMENTAL IMPACTS AND SUSTAINABILITY

The Fight against Soil Erosion in Minnesota-the Conservation Reserve Program at the Front Line

PERENNIAL CROPS FOR BIO-FUELS AND CONSERVATION

Habitat as a predictor of Warbler usage.

3.0 ROAD, BRIDGE AND FACILITY DESIGN

MODELING SURVIVAL AND CONSEQUENT REPLACEMENT NEEDS IN A STREET TREE POPULATION 1

Financial Perspectives on the Use of Vegetative Environmental Buffers for Swine Odor Management

A permit may be issued upon the completion of the revisions and conditions noted below under the items of this prior-to permit issuance letter.

Biofiltration is. The average odor. Treating Odor Emissions from Buildings Biofilters

Planting the Standard Windbreak

# Central States Tower/ Verizon Wireless Special Use Permit & Zoning Variation Project Review for Planning and Zoning Commission

MITIGATION IDEAS MITIGATION MEASURES BY HAZARD TYPE

TECHNICAL NOTES. Lyn R. Townsend, Regional Forester, WNTC SEPTEMBER 15, 1986 Dennis J. Robinson, State Forester, Spokane SO Revised September 29, 2003

Community Advisory Panel Meeting #

Directions from Lillington: Take HWY 401 North to Chalybeate Rd. on right travel approximately 1 mile down and property will be on the left

00-09: The use of wood chips for energy

Introduction to Photovoltaic (PV) Facilities

Guidance for Filling Out An Application for an Earth Moving Permit / Dust Control Plan. Section 1 Applicant Information

2018 Engenia Herbicide Stewardship Training

Permeability across the entire site within the General Residential Zone is a minimum of 30%.

Agricultural Improvement Fund

EDUCATION POSITIONS HELD AFFILIATIONS

Energy, Economics and Sustainability

TRANSFORM 66 Outside the Beltway Project Update March 2018

Canadian biomass harvester

EC1726 Application Blank and Information on Clarke-McNary Seedling Trees

Unit E: Basic Principles of Soil Science. Lesson 7: Understanding Soil Erosion and Management Practices

SILVICULTURE OF PURE, DOUBLE-COHORT STANDS. ESRM 323 Smith, et al. Chpt. 13, 14

Transcription:

Shrub Willow Living Snow Fences show potential for snow trapping and reduced drift length shortly after planting Justin P. Heavey and Timothy A. Volk State University of New York - College of Environmental Science and Forestry Syracuse, NY International Poplar Symposium VI Vancouver, BC July 2014

Rows of trees or shrubs Planted along roadways Same function as structural snow fences Trap blowing snow in drifts

Support USDOT NYSDOT Developing and Implementing a Living Snow Fence Program for New York State

A Living Alternative Structural Snow Fences Effective immediately Lifecycle 1-15 years Capacity = Height and Porosity Constant over time Living Snow Fences Some years after planting 20-30 years or more Capacity = Height and Porosity Changes as plants grow

How Do Snow Fences Work? Large Open Area

Problem Blowing, Drifting, Icing & Reduced Visibility Cost of Plowing, Salting & Road Maintenance Travel Delays, Road closures & Accidents

Opportunity Reduce Cost of Snow Control $2.3 billion annually in the US $300 million annually in New York State Improve Road Safety Driving conditions Accidents rates Save lives Provide Additional Benefits Travel time savings Environmental benefits Aesthetics Value-added products

Plant Growth & Drift Length Small plants Small snow storage capacity Fences fill to capacity Long drift length (35H) 35H Same quantity of blowing snow Larger plants More snow storage capacity Fences do not fill to capacity Shorter drift length (<35H) <35H

Objectives 1. Measure Fence Height Porosity Site and climate variables 2. Model Snow storage capacity of fences Snow transport (blowing snow at each site) Downwind drift length

18 Living Snow Fences 10 shrub willow 6 conifer 1 corn and honeysuckle 1-11 years after planting

Height Over Time 1 m - 8 m increased linearly over time (P < 0.001) Height of conifer fences was similar to willow at various YAP

Porosity Over Time 40% - 60% ideal - anything <80% sufficient Willow ranged from 90% to 10% - effective 3 YAP Conifer did not change - generally lower than willow

Capacity versus Transport Fence Capacity (Snow Storage Available) Height and Porosity Snow Transport (Blowing Snow in Avg. Year) Fallen snow and % relocated by wind Units of t/m (tons of snow per linear meter of fence)

Capacity Over Time Increased linearly with fence height 1-400 t/m Max. Snow Transport = 20 t/m 3-11 YAP Capacity = 2x to 100x transport

Drift Length and C/T Ratio Drift length is a function of Snow storage capacity relative to annual snow transport Capacity/Transport Ratio (X:1) As C/T increases, drift length decreases Drifts build up to height of fence before out towards road

Drift Length and C/T Ratio (Time) C/T ratio increases over time as fences grow 0-4 YAP: C/T 1:1-10:1 Drift length decreases rapidly 5-11 YAP: C/T 10:1-100:1 Drift length <10 m 5 Years After Planting

Required Setback Distance Distance between fence and road Chosen based on estimated drift length??? Estimated Drift Length: <10 m Observed Setback Distances: 10-100 m Published Recommendations: 30-180 m

Implications Dynamics of LSF over time have not been well researched or publicized Large C/T ratio = shorter drift lengths More potential sites where planting space is limited (common in northeast) Need for improved design standards

Drift Edge Effective willow snow fence 3 years after planting Limited ROW space 10 m setback Drift length safely contained

Shrub Willow Fences Ideal plant characteristics Numerous stems per plant (porosity) Rapid growth rate (capacity) Coppice ability, tolerance of high planting density Relatively low costs... Other shrub species Large conifer trees Structural fences Numerous Applications Windbreaks Noise & visual screens Buffers Best practices well developed SUNY ESF 2007-2013

Conclusion Shrub willows make highly effective LSF.. Snow trapping just 3 years after planting Large storage capacity thereafter Large capacity = shorter drift lengths Reduced setback requirements More potential sites This is leading to best practices and improved design standards that account for plant growth and snow trapping over time

www.esf.edu/willow/lsf