Feedback Mechanism in a Chaparral Watershed Following Wildfire 1

Total Page:16

File Type:pdf, Size:1020Kb

Feedback Mechanism in a Chaparral Watershed Following Wildfire 1 This file was created by scanning the printed publication. Errors identified by the software have been corrected; however, some errors may remain. Feedback Mechanism in a Chaparral Watershed Following Wildfire 1 Burchard H. Heede2 The Problem watershed and in the channels fol­ tion is 1100 m; bedrock geology con­ lowing wildfire in chaparral, to proj­ sists predominantly of deeply weath­ Natural recovery of vegetation fol­ ect future developments, and to dis­ ered coarse-textured Precambrian lowing wildfire in chaparral water­ cuss management implications. granite. In spite of relatively high an­ sheds leads to changes in microto­ nual precipitation (677 mm), the cli­ pography. Because chaparral does mate must be considered semiarid. not regrow uniformly, a mosaic pat­ Past Work Only 33% of the annual precipitation tern results. This regrowth often falls in summer when extremely high forms barriers to sediment delivery Much has been written about temperatures (reaching 43° C) reduce from uphill bare sites (Heede 1988). \\'ildfires in chaparral watersheds, as the effective precipitation substan­ Soils derived from coarse-grained well as the catastrophic conse­ tially. The vegetation cover consists granites, which contain very little quences. But to this writer's knowl­ of chaparral that has regrown since binding materials are highly erodible. edge, none of the studies spanned an intensive wildfire 29 years ago. Thus, relatively large volumes of relatively long time periods-two Today, about 95% of the original sediment are deposited at the uphill decades or more. Thus, immediate plant canopy has been restored. edge of the vegetation barriers, or fire effects were the focus of these El Oso Creek is an ephemeral buffer strips. Since these mounds and investigations. In contrast, Heede et stream. Following the wildfire, im­ other ground surface undulations al. (1988) reported on sediment deliv­ mense amounts of sediment were remain uncompacted for relatively ery linkages in a chaparral watershed deposited in the channels during long time spans, at least three dec­ covering a period of 26 years. They subsequent intense storms. Although ades in our case, their stability de­ showed that postfire developments the total deposits were estimated at 6 3 pends on the soundness of the buffer are complex and can only be inter­ 2.5x10 m , based on seismographic strips. preted if both the watershed and the investigations,3 it is believed that If an intense storm follows a wild­ channel network are investigated. part of this amount originated from fire, another type of sedimentation The essence of their findings was that earlier fires. In the main channel, fills occurs in the channel network. Be­ the watershed and the channel net­ up to 25 m were found. cause deep, loose and coarse sedi­ work were not in the same geomor­ ment deposits favor subsurface phological stage. While sediment de­ flows, most surface flows are small livery from the watershed to the Methods and immense volumes of sediments stream channels had ceased, sedi­ are deposited in the channels. ment movements continued within Prefire and sequential postfire aer­ The objectives of this paper are to the channel network. ial photographs were used to deter­ identify sediment processes on the mine qualitatively the development 1Poster paper presented at the confer­ ence, Effects of Fire in Management of Study Area 3Laird, J. R.: Harvey, M.D. 1986. Com­ Southwestern Natural Resources (Tucson. plex-response of a drainage basin to geo­ AZ. November 14-17. 1988). El Oso Creek watershed (drainage morphologically-effective fire. Tempe, AZ: 2Research Hydrologist, Rocky Mountain 2 U.S .Department of Agriculture, Forest Serv­ area, 2.5 km ) is located in central Forest and Range Experiment Station, For­ ice, Rocky Mountain Forest and Range Ex­ estry Sciences Laboratory, Arizona State Arizona on the east flank of the periment Station. 799 p. (unpublished re­ University Campus. Tempe, AZ 85287-1304. Mazatzal Mountains. Average eleva- port). 246 of vegetation and erosion conditions. mined. Latest developments were troughs (fig. 2). Sheet metal strips at Relative chaparral densities could be verified on the ground. each side of the troughs assured this obtained. The loci and extent of ero­ Ten microwatersheds, ranging in catch. Collector tanks made possible sion and deposition as well as their size from 0.01 to 0.2 ha, were selected volumetric determinations of flows changes with time were also deter- to represent a range of vegetation and sediment concentrations. conditions on different lithologies, elevations, and slope angles for the measurement of overland flow and Results sediment delivery (fig. 1). These mi­ crowatersheds also have different Judging from the first postfire ground cover characteristics. The photographs, storms following the term microwatershed was used, be­ intense wildfire must have led to in­ cause they are larger in size than creased overland flows and immense those used in traditional plot studies, volumes of sediment delivered into and the boundaries consisted of the stream network. This postfire be­ natural overland flow divides wher­ havior is demonstrated by our field ever possible. Where divides were research on erosion pavements (table not sufficiently pronounced, artificial 1). Now, nearly three decades after watershed boundaries were created the fire, overland flow from bare using sheet metal strips sunken into sites (erosion pavements) still aver­ ···,;/"'.'j~t the ground surface. ages more than 100 times that from "' ·!·.·.;. Ground cover characteristics were chaparral buffer strips. It must be ',?·:;~~:;.~ represented by erosion pavement (3 assumed that immediately after the -~"f/ffi~._r.t~.f . ~ ·,~,. microwatersheds) and erosion pave­ fire, this difference was considerably --~~~~~-~ ment with a vegetation buffer strip larger. DeBano (1966) has shown Figure 1.-Uphill view of part of an installa­ uphill from the measuring station (3 wildfires induce hydrophobic soil tion below a chaparral buffer strip; (A) microwatersheds) (fig. 2). The buffer conditions, which cause non-wetta­ chaparral buffer strip; (8) collector trough strips consisted of relatively dense bility of the soils and increase over­ for overland flow; (C) conveyance pipe; (0) chaparral stands, 2.5 to 4.0 m wide. land flow and sediment transport. supercritical flume; (E) flume for intake to sediment pumping sampler. Pipe in fore­ Overland flow and sediment were On our bare microwatersheds, ground leads to a collector tank. caught by 4-m-long sheet metal sediment delivery was on the aver­ age over 300 times larger than on bare microwatersheds with buffer strips (table 1). Due to the hydropho­ bic soil properties immediately fol­ lowing the fire, sediment deliveries during the early postfire storms also must have been much larger than those of today' s bare areas. Increased infiltration into soils under the buffer strips greatly re­ duced overland flow and caused substantial accumulations of sedi­ ment uphill from the strips. Deposit depths up to 0.45 m were measured (fig. 3). With future depth increases, water withdrawal by the loose, coarse, granite-derived sediments also will increase, and increasingly stronger overland flows will be re­ quired to move the sediment. As the first postfire photographs show, the tributary channels were Figure 2.-Looking across a microwatershed of erosion pavement with chaparral buffer strip clogged by sediment and the main at the downhill border. channel lost depth and widened con- 247 siderably. Apparently, stream com­ Conclusion available sediments, should a wild­ petence was not sufficient to move fire strike the watershed in the fu­ the incoming material through the The localized sediment accumula­ ture. This possible chain of events system; thus deposition occurred. tions behind buffer strips represent constitutes a negative feedback Today, practically all channel banks an enormous reservoir of easily mechanism as follows: are lined by chaparral buffer strips. Even south aspects along El Oso / buffer strip loss ~ Creek developed strips of substantial width (15 to 25m). Greater soil depth sediment depositions massive erosion and higher soil moisture seem to fa­ vor this development. Now that sediment movement "'- regrowth of strips / from the slopes has largely stabi­ lized, relatively clear water reaches the channels. When clear waters en­ ter the clogged tributary channels, the available free water energies be­ gin to move the sediment. Channel scour has started in the headwaters and is proceeding downstream. Flow entering the main channel is ab­ sorbed by the deep and porous sedi­ ment deposits, and the incoming sediment is deposited as in-channel fans (fig. 4). These fans are still growing due to lack of surficial flows with sufficient transport capac­ ity. As more deposition occurs, the storage sites widen, surficial flow depth decreases, and even more sedi­ ment is stored. Figure 3. -Excavation of the loose sediment deposits uphill from a buffer strip. The de­ posits increase in depth downhill. Approxi­ mate depth of this excavation is 0.40 m. Figure 4.-An in-channel fan of sediment formed by flows from a tributary. Long arrow de­ Retractable tape measure (arrow) in the notes direction of tributary flow. Short arrow shows flow direction in the main channel of El excavation denotes scale. Oso Creek. 248 Thus, discouragingly, the restora­ Heede, B. H.; Harvey, M.D.; Laird, J. tion of a burned chaparral watershed R. 1988. Sediment delivery link­ sets the stage for the next cata­ ages in a chaparral watershed fol­ strophic event, should an unusual lowing a wildfire. Environmental storm follow a fire. Management 12(3): 349-358. During three postfire decades, sediment redepositions in the stream network have not led to channel res­ toration, except in the headwater reaches of the tributaries. Large vol­ umes of sediment are still ready for transport by an exceptional flow. Hence, long-term instability charac­ terizes the main channel. Management Implications This research suggests that con­ ducting relatively frequent pre­ scribed fires with low intensities could reduce the rates and time frames at which sediment is deliv­ ered to the channels.
Recommended publications
  • Riparian Vegetation Management
    Engineering in the Water Environment Good Practice Guide Riparian Vegetation Management Second edition, June 2009 Your comments SEPA is committed to ensuring its Good Practice Guides are useful and relevant to those carrying out activities in Scotland’s water environment. We welcome your comments on this Good Practice Guide so that we can improve future editions. A feedback form and details on how to send your comments to us can be found at the back of this guide in Appendix 1. Acknowledgements This document was produced in association with Northern Ecological Services (NES). Page 1 of 47 Engineering in the Water Environment Good Practice Guide: Riparian Vegetation Management Second edition, June 2009 (Document reference: WAT-SG-44) Contents 1 Introduction 3 1.1 What’s included in this Guide? 3 2 Importance of riparian vegetation 6 3 Establishing/creating vegetation 8 3.1 Soft or green engineering techniques 8 3.2 Seeding and planting of bare soil 10 3.3 Creating buffer strips 11 3.4 Planting trees and shrubs 15 3.5 Marginal vegetation 18 3.6 Urban watercourses 21 4 Managing vegetation 24 4.1 Management of grasses and herbs 24 4.2 Management of heath and bog 27 4.3 Management of adjacent wetlands 28 4.4 Management of non-native plant species 29 4.5 Management of scrub and hedgerows 31 4.6 Management of individual trees 31 4.7 Management of trees – riparian woodland 33 4.8 Management of trees – conifer plantations 35 4.9 Large woody debris 37 4.10 Marginal vegetation 37 4.11 Urban watercourses 40 4.12 Use of herbicides 40 4.13 Environmental management of vegetation 41 4.14 Vegetation management plans 41 5 Sources of further information 42 5.1 Publications 42 5.2 Websites 44 Appendix 1: Feedback form – Good Practice Guide WAT-SG-44 45 Page 2 of 47 1 Introduction This document is one of a series of good practice guides produced by SEPA to help people involved in the selection of sustainable engineering solutions that minimise harm to the water environment.
    [Show full text]
  • Riparian Buffer Restoration
    Pennsylvania Stormwater Best Management Practices Manual Chapter 6 BMP 6.7.1: Riparian Buffer Restoration A riparian buffer is a permanent area of trees and shrubs located adjacent to streams, lakes, ponds, and wetlands. Riparian forests are the most beneficial type of buffer for they provide ecological and water quality benefits. Restoration of this ecologically sensitive habitat is a responsive action to past activities that may have eliminated any vegetation. Key Design Elements Potential Applications Residential: Yes Commercial: Yes Ultra Urban: Yes Industrial: Yes Retrofit: Yes Highway/Road: Limited · Reestablish buffer areas along perennial, intermittent, and ephemeral streams · Plant native, diverse tree and shrub vegetation Stormwater Functions · Buffer width is dependant on project preferred function (water quality, habitat creation, etc.) · Minimum recommended buffer width is 35’ from top of stream Volume Reduction: Medium bank, with 100’ preferred. Recharge: Medium · Create a short-term maintenance and long-term maintenance Peak Rate Control: Low/Med. plan Water Quality: Med./High · Mature forest as a vegetative target · Clear, well-marked boundary Water Quality Functions TSS: 65% TP: 50% NO3: 50% 363-0300-002 / December 30, 2006 Page 191 of 257 Pennsylvania Stormwater Best Management Practices Manual Chapter 6 Description The USDA Forest Service estimates that over one-third of the rivers and streams in Pennsylvania have had their riparian areas degraded or altered. This fact is sobering when one considers the important stormwater functions that riparian buffers provide. The non-structural BMP, Riparian Forest Buffer Protection, addresses the importance of protecting the three-zone system of existing riparian buffers. The values of riparian buffers – economic, environmental, recreational, aesthetic, etc.
    [Show full text]
  • An Agroforestry Project: Sustainable Tree-Shrub-Grass Buffer Strips
    Volume 78 Article 5 1-1-1991 An Agroforestry Project: Sustainable Tree-Shrub- Grass Buffer Strips Along Waterways Richard Schultz Iowa State University Joe Colletti Iowa State University Carl Mize Iowa State University Andy Skadberg Iowa State University Bruce Menzel Iowa State University Follow this and additional works at: https://lib.dr.iastate.edu/amesforester Part of the Forest Sciences Commons Recommended Citation Schultz, Richard; Colletti, Joe; Mize, Carl; Skadberg, Andy; and Menzel, Bruce (1991) "An Agroforestry Project: Sustainable Tree- Shrub-Grass Buffer Strips Along Waterways," Ames Forester: Vol. 78 , Article 5. Available at: https://lib.dr.iastate.edu/amesforester/vol78/iss1/5 This Article is brought to you for free and open access by the Journals at Iowa State University Digital Repository. It has been accepted for inclusion in Ames Forester by an authorized editor of Iowa State University Digital Repository. For more information, please contact [email protected]. AN AGROFORESTRY PROJECT: susTAINABLE TREE-SHFIUB-GRASS BUFFEFI STRIPS ALONG WATERWAYS BY F]lCHAF]D SCHULTZ, JOE COLLETTl, CAFZL MIZE, ANDY SKADBEFIG, AND BFIUCE MENZEL Introduction the streambank, the aquatic ecosystem, and for providing wildlife habitat for terrestrial Iowa is a mosaic landscape of agricultural animals. crops, pasture lands, native woodlands. prai- rie remnants, wetlands, and a network of A cooperative project on a private farm was streams and rivers. With settlement and the started in the spring of 1990. An interdiscipli- increased mecha- naryteam fromthe nization of agricul- Departments of ture, many natural Forestry, a as ` sgffi se.>< isee`s±gg // //,i/// i/// i/ // // //////i1/,,,,,74,i,,;,,#,// ,z/ /// Agronomy, Geol- woodland corri- `x,`,`/`se*/a <.*ng ng`'` -i- dors along these `asJz '3¥sezl , ` i ogy and Atmo- i // /// streams and rivers spheric Sciences, i$3& and Animal Ecol- were removed.
    [Show full text]
  • Buffering the Buffer, by Leslie M. Reid, And
    Buffering the Buffer1 Leslie M. Reid2 and Sue Hilton3 Abstract: Riparian buffer strips are a widely accepted tool for helping to sustain ¥ Maintenance of the aquatic food web through provision aquatic ecosystems and to protect downstream resources and values in forested of leaves, branches, and insects areas, but controversy persists over how wide a buffer strip is necessary. The physical integrity of stream channels is expected to be sustained if the ¥ Maintenance of appropriate levels of predation and characteristics and rates of tree fall along buffered reaches are similar to those in competition through support of appropriate riparian undisturbed forests. Although most tree-fall-related sediment and woody debris ecosystems inputs to Caspar Creek are generated by trees falling from within a tree’s height of the channel, about 30 percent of those tree falls are triggered by trees falling ¥ Maintenance of water quality through filtering of from upslope of the contributing tree, suggesting that the core zone over which sediment, chemicals, and nutrients from upslope sources natural rates of tree fall would need to be sustained is wider than the one-tree- height’s-width previously assumed. Furthermore, an additional width of “fringe” ¥ Maintenance of an appropriate water temperature buffer is necessary to sustain appropriate tree-fall rates within the core buffer. regime through provision of shade and regulation of air Analysis of the distribution of tree falls in buffer strips and un-reentered stream- temperature and humidity side forests along the North Fork of Caspar Creek suggests that rates of tree fall are abnormally high for a distance of at least 200 m from a clearcut edge, a ¥ Maintenance of bank stability through provision of root distance equivalent to nearly four times the current canopy height.
    [Show full text]
  • Template for Pdfs.Pmd
    2.12 Stream temperature and buffers Buffers can help maintain cooler water temperatures in small streams if the vegetation provides adequate shade on the water surface. This can be beneficial for coldwater aquatic species and for water quality. Stream shade is comprised of topographic shade provided by nearby hills, bank shade, and vegetative shade. Streams with vegetation removed usually have undesirable summer temperature increases from 5 to 11oC. Aspect, channel morphology, and groundwater input may affect temperatures more than buffers. Key Design Considerations • Incorporate topography and bank shade in the design. • Trees and shrubs provide the most shade but unmowed or ungrazed grass buffers can provide shade on streams less than 8 feet in width. • Buffer shading effectiveness decreases as stream width increases. • Windthrow may be common in buffers retained after timber harvest and wider buffers may be necessary. • Buffers may need to be wider (150 to 1000 ft) to maintain other microclimatic factors (e.g., soil temperature, humidity). 2.12 Biodiversity 2.12 References Anbumozhi, V.; Radhakrishnan, J.; Yamaji, E. 2005. Impact of riparian buffer zones on water quality and associated management considerations. Ecological Engineering. 24: 517-523. Barton, D.R.; Taylor, W.D.; Biette, R.M. 1985. Dimensions of riparian buffer strips required to maintain trout habitat in southern Ontario streams. North American Journal of Fisheries Management. 5: 364- 378. Beschta, R.L. 1997. Riparian shade and stream temperature: an alternative perspective. Rangelands. 19: 25-28. Blann, K.; Nerbonne, J.F.; Vondracek, B. 2002. Relationships of riparian buffer type to water temperature in the Driftless area ecoregion of Minnesota.
    [Show full text]
  • Adoption of Conservation Buffers: Barriers and Strategies
    United States Department of Adoption of Conservation Agriculture Buffers: Barriers and Natural Strategies Resources Conservation Service Social Sciences Institute October 2002 Adoption of Conservation Buffers Front cover photo courtesy of NRCS Photo Gallery http://photogallery.nrcs.usda.gov/ Acknowledgments Supporting data for this publication includes social science research studies, reports from the Conservation Technology Information Center, and summaries of field interviews. I would especially like to thank NRCS technical specialists David Buland, Jim Cropper, David Faulkner, Aaron Hinkston, Jim Robinson, Gary Wells, and Bruce Wight for their time and expertise. Sandy Hodge, State Specialist-Public Policy, Community Development Extension Program, University of Missouri, graciously assisted me with her time and technical materials, including photos. Thanks also to Frank Clearfield, director, Social Sciences Institute, and to Peter Smith, director, NRCS Resource Economics and Social Sciences Adoption of Conservation Buf Division, for taking the time to help edit and modify this document, and Mary Mattinson, Suzi Self, and Wendy Pierce, NRCS National Cartography and Geospatial Center, for editing and preparing the document for publication. Gail Brant Sociologist Social Sciences Institute fers Adoption of Conservation Buffers Adoption of Conservation Buffers: Barriers and Strategies Contents Introduction .................................................................................................................................................................
    [Show full text]
  • Chapter 3B Contour Buffer Strips
    Chapter 3b Contour Buffer Strips Definition of contour Design considerations buffer strips Location and layout Contour buffer strips are narrow strips of permanent, herbaceous vegetative cover established across the Buffer strip width The actual width of the contour buffer strip is deter­ slope and alternated down the slope with wider mined by the purpose or purposes identified, the type cropped strips (fig. 3b–1). of vegetation to be established, and its effectiveness. Where more than one purpose is being served, the Contour buffer strips are most suitable on slopes most restrictive criteria governs. ranging from 4 to 8 percent where slope lengths are less than the critical slope length beyond which con­ Minimum widths for various purposes and types of touring loses its effectiveness. Critical slope length is vegetation are stated in the contour buffer strip prac­ determined by using the Revised Universal Soil Loss tice standard for your area. Generally, contour buffer equation (RUSLE) or other approved erosion predic­ strips are a minimum of 15 feet wide for grasses or tion technology. grass legume mixtures and 30 feet for legumes alone. Experience has shown that by increasing the mini­ The practice is not suited to long slopes where lengths mum width to 20 feet, flow velociy through the buffer exceed critical slope length by more than 1.5 times is reduced even further thus reducing the risk of unless other practices, such as terraces or diversions, erosion immediately below the buffer. are installed to intercept the flow. Contour buffer strips are more effective in trapping Width of cultivated strips Since contour buffer strips are established in conjunc­ sediment and filtering pollutants and less likely to fail tion with contour cropped strips, the spacing between in areas where storm energy intensities are low to buffer strips is determined by the purpose(s) being moderate and where 10-year erosion index (EI) values served and the criteria stated in the practice standard.
    [Show full text]
  • Buffer Strip Function and Design Ïïï
    ÒÒÒ BUFFER STRIP FUNCTION AND DESIGN ÏÏÏ An Annotated Bibliography Compiled for the Region III Forest Practices Riparian Management Committee by James D. Durst and James M. Ferguson Alaska Department of Fish and Game, Habitat and Restoration Division SUMMARY Natural forests adjacent to water bodies can contribute all of the ten habitat components listed in the FRPA, AS 41.17.115, which were discussed in the Introduction. The relative importance of each component to maintaining fish habitat and water quality varies with differences in the physical and other characteristics of the water body, such as stream width (or lake size), gradient, incision depth, bank characteristics, and average, seasonal, and peak flow. Research has demonstrated the importance of maintaining forested conditions along water bodies that are naturally forested. In the 1990s, this research began to be incorporated into forest practices-related laws and regulations. In Alaska, the FRPA, Tongass Timber Reform Act, and Tongass Land Management Plan (TLMP) revision each prescribe mandatory buffers for certain types of fish-bearing (and, in the case of TLMP, some non-fish-bearing) water bodies. Buffer widths vary, based on different water body classifications, which are in turn based on different physical stream characteristics, and the presence of anadromous fish. The TLMP standards use the classification of Paustian (1992). These buffers were designed for the relatively small stream systems found in Southeast Alaska. Murphy (1995) provides a good summary of buffer-related research conducted in Alaska, and riparian management recommendations that have been applied in Southeast Alaska. The Tongass Land Management Plan (1997) and the FRPA revisions of 1999 update Murphy’s summary of existing buffer standards.
    [Show full text]
  • Upper Catchment Issues
    UPPER CATCHMENT ISSUES TASMANIA First edition feature — Upper Catchment Issues in the North Eastern Highlands Journal of The Community Based Risk Assessment Group of Tasmania Vol. 1 No. 1 ISSN 1444-9560 Upper Catchment Issues - Tasmania Disclaimer: Articles from any person, group or organization are accepted for publication at the discretion of the Editor, and the opinions expressed therein may not necessarily reflect the views of the Editor. Copyright: Readers of this publication are reminded that all material appearing in The Journal, including any specially composed article, is covered under the copyright laws of Australia and may not be reproduced or copied in any form or part whatsoever or used for any promotional or advertising purpose without the written consent of the Editors, author or artist. Submissions — Guide for intending authors We welcome submissions on topics concerning any aspect of upper catchment issues. Consult a current issue of the journal for style and layout of submissions. Intending authors are reminded that a very diverse audience reads the Journal and so highly technical or specialised terminology should be carefully explained. Finally, responsibility for spelling, punctuation and referencing shall remain with the author. Submissions should be addressed to: The editor, 8 Lenborough Street Beauty Point Tasmania 7270 Deadlines for Submissions Australia Desktop Publishing: January, 7 Resource Publications (ABN 66 828 584 972) 9 Lenborough Street Beauty Point, Tasmania, 7270 Phone: (03) 6383 4594 Fax: (03) 6383
    [Show full text]
  • The Massachusetts Vegetated Buffer Manual
    TThhee MMaassssaacchhuusseettttss BBuuffffeerr MMaannuuaall Using Vegetated Buffers to Protect our Lakes and Rivers Prepared by the Berkshire Regional Planning Commission For The Massachusetts Department of Environmental Protection 2003 Massachusetts Vegetated Buffer Manual About The Massachusetts Buffer Manual In 2001 the Berkshire Regional Planning Commission was awarded a Nonpoint Source Pollution grant to conduct a demonstration and outreach project. The goal of this project was to promote the bene- fits of vegetated buffers. The three main objectives to achieve this goal were to 1) create a buffer guidance document, 2) plant five buffer demonstration sites and 3) talk about vegetated buffers to the public. This document, three of the buffers seen in Chapter 2 and several presentations made to lake groups and conservation commissioners are direct outcomes of this project. Russ Cohen of the Riverways Program was our partner and co-presenter for three of our "on the road" presentations. Many thanks, Russ. Acknowledgements To our Partners: A very special thank you goes out to our project partners, without whose contributions the Buffer Project would not have been made possible. These plant specialists, landscape professionals and nurseries have voluntarily contributed their time, expertise and materials to our demonstration projects and to this document. Their support is greatly appreciated. Robert Akroyd, landscape architect, Greylock Design Associates Rachel Fletcher and Monica Fadding, Housatonic River Walk Rick Harrington, landscaper, Good Lookin' Lawns Dorthe Hviid, horticulturist, Berkshire Botanical Garden Dennis Mareb, owner, Windy Hill Farm Christine McGrath, landscape architect, Okerstrom Lang, Ltd. Craig Okerstrom Lang, landscape architect, Okerstrom Lang, Ltd. Greg Ward, owner, Ward's Nursery and Garden Center Raina Weber, plant propagation, Project Native (an undertaking of the Railroad St.
    [Show full text]
  • Consultation on Sustainable Forest Management in Québec
    Consultation on sustainable forest management in Québec Consultation paper Sustainable forest management strategy and Provisions proposed for the future regulation on sustainable forest management Consultation on sustainable forest management in Québec Consultation paper Sustainable forest management strategy and Provisions proposed for the future regulation on sustainable forest management For additional information, please contact: Direction des communications Ministère des Ressources naturelles et de la Faune 5700, 4e Avenue Ouest, C 409 Québec (Québec) G1H 6R1 Telephone : 418 627-8600 Elsewhere in Québec: 1 866 248-6936 Fax: 418 644-6513 [email protected] Cover photographs Ministère des Ressources naturelles et de la Faune Lower left: Pourvoirie Poulin de Courval, Roch Théroux This publication is available on the Internet at: www.mrnf.gouv.qc.ca Ce document est également disponible en français. Legal Deposit – Bibliothèque et Archives nationales du Québec, 2010 Ministère des Ressources naturelles et de la Faune, 2010 ISBN 978-2-550-60087-9 (Printed version) ISBN 978-2-550-60088-6 (PDF) Code de diffusion : 2010-2007 © Gouvernement du Québec MESSAGE FROM THE MINISTER In recent months, Québec has been pursuing a full-scale revision of its forest regime. This major ongoing process passed a crucial stage on March 23, 2010, when the Members of the National Assembly gave unanimous assent to the Sustainable Forest Development Act. This sent a clear message that our government is committed to taking charge of the management and conservation of Québec’s forest heritage to ensure as many benefits as possible for citizens and, in addition, to make Québec an international leader in sustainable forest management.
    [Show full text]
  • AGROFORESTRY and GRASS BUFFER INFLUENCES on MICROCLIMATE Ranjith P
    AGROFORESTRY AND GRASS BUFFER INFLUENCES ON MICROCLIMATE Ranjith P. Udawatta Peter P. Motavalli Research Assistant Professor Associate Professor Neil I. Fox Kelly A. Nelson Assistant Professor Research Agronomist Introduction: Agroforestry practices have been considered to be more environmentally friendlier than row- crop agriculture due to improvements in soil and water quality. Research shows that agroforestry and grass buffers on corn-soybean watersheds reduce non point source pollution in runoff and improve soil properties (Udawatta et al., 2002; Seobi et al., 2005; Udawatta et al., 2006). These improvements have been attributed to organic matter addition, roots of the permanent vegetation, nutrient uptake, water use, and changes in soil parameters. The permanent vegetation within the buffers may also change microclimate and thus directly and indirectly influence evapotranspiration, soil water dynamics, soil enzyme activities, carbon sequestration, and nutrient dynamics. Research shows that larger trees act as a barrier to wind speed and thereby reduce evapotranspiration and crop damage from crop fields as compared to open fields (Bird, 1998). Studies speculate that reduced energy levels under buffers and adjacent areas promote more soil moisture storage, less evaporation, and diverse microbial activity. Studies on windbreaks have shown increased crop yields, yield quality, on the leeward side (Bird, 1998; Huth et al., 2002), however this varies with crop, windbreak type, geography, moisture and soil properties (Brandle, et al., 2004). The objective of this study was to evaluate Figure 1. Grass buffer (grass only) and agroforestry differences in microclimatic parameters (grass+trees) buffer watersheds with 0.5 m interval among crop, grass buffer, and agroforestry contour lines (black), buffers (gray), grass waterways buffer areas.
    [Show full text]