Riparian Areas 6

Total Page:16

File Type:pdf, Size:1020Kb

Riparian Areas 6 Riparian areas “Most people camp too close to the creek to make good coffee.” 6 — Rube Long he physical, chemical, and biological channel and floodplain, and is connected to makeup of a stream relates to the sur- upstream and downstream ecosystems. Trounding physical features of the watershed Riparian habitat is a combination of three and its geologic origin. Looking at these features areas. Each is distinctive and contributes to the helps us understand stream-watershed relation- entire ecosystem. ships and allows managers to predict the effects Aquatic area: The aquatic area of streams, of human influences on different streams. lakes and wetlands is generally wet. During dry Think of the uplands of a watershed as the periods, aquatic areas have little or no water sides of a funnel, and the stream flowing from flow. Any side channels or oxbows containing the mouth of the funnel. The riparian area is the freshwater ponds are included in this area. sides of the spout surrounding the stream. The Riparian area: The riparian area is a terres- riparian area is the green zone of plants along the trial zone where annual and intermittent water, a stream. Water, nutrients, and sediments from high water table, and wet soils influence vegeta- across the uplands move down- tion and microclimate. hill to support this lush Area of influence: This and productive area. is a transition area between a Streams and riparian area and upland riparian areas develop cover. An area of influence together, each affecting has soil moisture and is the development of the characterized by a noticeable other. Headwater streams change in plant composition and are small, and the riparian abun- areas that surround them are dance. relatively narrow. Larger streams Trees in Vocabulary and rivers flood more often, and this area aquatic area floodwaters carve out wide flood- contribute aquifer plains. The plant communities that shade, leaves, area of influence develop along the edge of the stream are woody debris and edge effect generally distinct from those that cover the insects to a stream. floodplains broader, and somewhat drier floodplains. In the Pacific Oregon Forest Plants along the stream influence the Northwest, the area Practices Act entire stream ecosystem. Riparian areas of influence in- riparian area (Figure 6) have several unique properties. A cludes ground riparian management riparian area is linear, has a water transport covers, shrubs and areas understory trees understory Oregon Department of Fish & Wildlife Riparian areas • 161 (usually deciduous) Stream food chains depend on organic debris on the floodplains, for nutrients. In small headwater streams, 99% of and canopy trees the energy for organisms comes from the vegeta- (usually coniferous) tion along the stream, and only 1% from photo- on hillsides. This synthesis. The leaves, needles, cones, twigs, stair-stepping of wood, and bark dropped into a stream are a vegetation provides a storehouse of readily available organic material variety of wildlife that is processed by aquatic organisms and re- habitat. turned to the system as nutrients and energy. A diverse population of insects depends on this varied food base. Between 60% and 70% of Role of riparian vegetation the debris is retained and processed in the head- Riparian plant communities (Table 1) provide waters by bacteria, fungi, insects, and abrasion, cover for aquatic and terrestrial animals. Shade with very little leaving the system until it has created by the riparian vegetation moderates been at least partially processed. water and air temperatures. This vegetation limits Riparian areas have a high number of edges water contamination, slows water velocities and (habitat transitions) within a very small area. The filters and collects large amounts of sediment and large number of plant and animal species found debris. Uncontrolled sediments can kill fish and in these areas reflects habitat diversity. Since destroy spawning areas. they follow streams, riparian areas are linear, Figure 6. Riparian Habitat 162 • The Stream Scene: Watersheds, Wildlife and People Oregon Department of Fish & Wildlife increasing the amount and importance of edge backwaters act as reservoirs to hold surplus effect. Extensive edge and resulting habitat runoff until peak floods are past. This controls diversity yield an abundance of food and support and reduces downstream flooding. Floodplains a greater diversity of wildlife than nearly any also spread the impact of a flood over a larger other terrestrial habitat. area as vegetation helps collect debris and sedi- ment. Composition of riparian plant communities Floodplains depends on the water pattern (fast or slow mov- Floodplains are an important part of a ripar- ing or dry or wet periods). Both wet and dry ian area. Floodplain vegetation that shades or phases are necessary in this area to complete the directly contributes material to a stream is con- stream’s nutrient cycle and food chain. Flooding sidered part of the riparian area. is critical to the exchange of nutrients and energy between the stream and the riparian area. When healthy, vegetated banks in the ripar- ian area act as natural sponges. They help main- Flooding is critical to the tain soil structure, allow increased infiltration, and reduce bank erosion. exchange of nutrients and Vegetated streambanks also contribute to aquifer (groundwater) recharge. Precipitation is energy between stream and filtered through the riparian soils and enters underground reservoirs called aquifers. Good riparian area. cover slows the flow and increases percolation into underground aquifers. Stored water is then Stream channels rely on natural flooding available during drier periods to maintain and patterns. Frequency of flooding and groundwater improve minimum flow levels. A major benefit supply are the major factors controlling the of this aquifer recharge is maintenance of year- growth of floodplain trees. Floodplains and round streamflow. Table 1. Functions of Riparian Vegetation As They Relate to Aquatic Ecosystems Riparian Vegetation Site Component Function Above ground- Canopy and stems • Shade—controls temperature and instream photosynthetic productivity above channel • Source of large and fine plant detritus • Source of terrestrial insects In channel Large debris derived • Control routing of water and sediment from riparian • Shape habitat—pools, riffles, cover vegetation • Substrate for biological activity Streambanks Roots • Increase bank stability • Create overhanging banks—cover Floodplain Streams and • Retard movement of sediment, water and floated organic low-lying canopy debris in flood flows. Source: William Meehan et al., Influences of Riparian Vegetation on Aquatic Ecosystems With Particular References to Salmo- nid Fishes and Their Food Supply, 1977, p. 137. Oregon Department of Fish & Wildlife Riparian areas • 163 Riparian vegetation uses large amounts of Amphibians and reptiles are another indica- water in transpiration. Often, vegetation needs tor of riparian quality. Nearly all amphibians the most water during the period of lowest depend on aquatic habitats for reproduction and streamflow. At these times, vegetation may overwintering. Certain turtles, snakes, and lizards actually reduce streamflow. also prefer riparian ecosystems. Animal populations in riparian areas are Wildlife in riparian areas affected by the size and diversity of available Riparian ecosystems provide the essentials of wildlife habitat: food, water and cover. In gen- Amphibians and reptiles are eral, the area within 200 yards of a stream is used most heavily by wildlife. In western Oregon, of another indicator of riparian 414 known species of wildlife, 359 use riparian ecosystems extensively and 29 species are tied quality. exclusively to this area. While riparian areas cover less than 1% of the land in eastern Oregon, 280 of 379 species use this area extensively. habitat. Adjacent land-use activities may have a Riparian areas provide migration routes and direct effect on wildlife population size within a corridors between habitats for many animals. riparian area. Woody plant communities in the riparian area Fish populations can be an indicator of provide cover, roosting, nesting and feeding watershed and riparian ecosystem health. Large areas for birds; shelter and food for mammals; woody materials, such as fallen trees and limbs, and increased humidity and shade (thermal create pools and protective cover, which are cover) for all animals. necessary components of fish habitat. This Birds are the most common and conspicuous woody debris also increases the diversity of form of wildlife in a riparian ecosystem. In this invertebrates, which are a basic part of the food important breeding habitat, as many as 550 chain on which fish depend. breeding pairs have been found per 100 acres. Bird density is just one indicator of the produc- tivity of a riparian area. People in riparian areas Mammals of all sizes are found in riparian Since the land along streambanks and floodplains areas. Many rodents are parts of various food is often fairly flat, riparian areas are attractive chains. Some, such as beaver, may modify ripar- locations for roads. Roadbuilding may increase ian communities. The effects of beavers on a sedimentation, which can adversely affect watershed can be both positive and negative. aquatic life, especially fish. Runoff from roads Their actions change watershed hydrology as can carry oil, antifreeze, and other contaminants well as damage cover. A beaver dam
Recommended publications
  • 2019 Data Report for Oneida Lake, Livingston County
    Michigan Lakes– Ours to Protect 2019 Data Report for Oneida Lake, Livingston County Site ID: 470573 42.4676°N, 83.8488°W The CLMP is brought to you by: 1 About this report: This report is a summary of the data that have been collected through the Cooperative Lakes Monitoring Program. The contents have been customized for your lake. The first page is a summary of the Trophic Status Indicators of your lake (Secchi Disk Transparency, Chlorophyll-a, Spring Total Phosphorus, and Summer Total Phosphorus). Where data are available, they have been summarized for the most recent field season, five years prior to the most recent field season, and since the first year your lake has been enrolled in the program. If you did not take 8 or more Secchi disk measurements or 4 or more chlorophyll measurements, there will not be summary data calculated for these parameters. These numbers of measurements are required to ensure that the results are indicative of overall summer conditions. If you enrolled in Dissolved Oxygen/Temperature, the summary page will have a graph of one of the profiles taken during the late summer (typically August or September). If your lake stratifies, we will use a graph showing the earliest time of stratification, because identifying the timing of this condition and the depth at which it occurs is typically the most important use of dissolved oxygen measurements. The back of the summary page will be an explanation of the Trophic Status Index and where your lake fits on that scale. The rest of the report will be aquatic plant summaries, Score the Shore results, and larger graphs, including all Dissolved Oxygen/Temperature Profiles that you recorded.
    [Show full text]
  • Current Insights Into the Effectiveness of Riparian Management, Attainment of Multiple Benefits, and Potential Technical Enhancements
    Published March 8, 2019 Journal of Environmental Quality SPECIAL SECTION RIPARIAN BUFFER MANAGEMENT Current Insights into the Effectiveness of Riparian Management, Attainment of Multiple Benefits, and Potential Technical Enhancements Marc Stutter,* Brian Kronvang, Daire Ó hUallacháin, and Joachim Rozemeijer iparian buffers have been one of the most widely Abstract used management options worldwide when dealing Buffer strips between land and waters are widely applied with protection of surface waters from agricultural dif- measures in diffuse pollution management, with desired Rfuse pollution. Appropriately managed riparian areas offer mul- outcomes across other factors. There remains a need for tiple functions related to improving water quality, biodiversity, evidence of pollution mitigation and wider habitat and societal benefits across scales. This paper synthesizes a collection of 16 and climate adaptation. First, riparian areas offer possibilities new primary studies and review papers to provide the latest for protecting watercourses and lakes from inputs of sediments, insights into riparian management. We focus on the following nutrients, pesticides, and other contaminants by intercepting areas: (i) diffuse pollution removal efficiency of conventional surface runoff, tile drainage, and groundwater from adjoining and saturated buffer strips, (ii) enhancing biodiversity of buffers, agricultural fields. Second, riparian areas also offer unique bio- (iii) edge-of-field technologies for improving nutrient retention, and (iv) potential reuse of nutrients and biomass from buffers. diversity (in turn affecting in-field and in-stream biodiversity) Although some topics represent emerging areas, for other including structurally complex layers of vegetation, making well-studied topics (e.g., diffuse pollution), it remains that them attractive to many wildlife species (Naiman et al., 1993).
    [Show full text]
  • Assessment of Land Use Change and Riparian Zone Status in the Barnegat Bay and Little Egg Harbor Watershed: 1995-2002-2006
    Assessment of Land Use Change and Riparian Zone Status in the Barnegat Bay and Little Egg Harbor Watershed: 1995-2002-2006 Intact forested riparian zone along the upper reaches of the Forked River. Richard G. Lathrop¹ Scott M. Haag² October 2007 ¹Grant F. Walton Center for Remote Sensing and Spatial Analysis ²Institute of Marine and Coastal Science School of Environmental & Biological Sciences-Rutgers University New Brunswick, NJ 08901 1 Assessment of Land Use Change and Riparian Zone Status in the Barnegat Bay and Little Egg Harbor Watershed: 1995-2002-2006 Executive Summary The Barnegat Bay/Little Egg Harbor (BB/LEH) estuary is suffering from eutrophication issues due to nutrient, most importantly nitrogen, loading from both atmospheric as well as watershed sources (Kennish et al, 2007). Urban and agricultural land uses can be an important source of nitrogen loading. As part of our ongoing monitoring efforts, the Grant F. Walton Center for Remote Sensing & Spatial Analysis, with funding provided by the Barnegat Bay National Estuary Program, undertook to map and assess recent land use change in the Barnegat Bay-Little Egg Harbor watershed. Our updated mapping reveals that urban land use increased from approximately 25% in 1995 to approximately 30% of the BB/LEH watershed in 2006. Including all altered land uses (i.e., agriculture and barren lands) puts the percentage of altered land in the BB-LEH watershed at over 33% in 2006. The BB/LEH estuary system is continuing to experience a significant conversion of forested and wetland habitats to urban land cover and thereby exacerbating nutrient loading to the BB-LEH estuary.
    [Show full text]
  • The Buffer Capacity of Riparian Vegetation to Control Water Quality
    water Article The Buffer Capacity of Riparian Vegetation to Control Water Quality in Anthropogenic Catchments from a Legally Protected Area: A Critical View over the Brazilian New Forest Code Carlos Alberto Valera 1,2,3, Teresa Cristina Tarlé Pissarra 2,3 , Marcílio Vieira Martins Filho 2,3 , Renato Farias do Valle Júnior 3,4, Caroline Fávaro Oliveira 3,4, João Paulo Moura 5 , Luís Filipe Sanches Fernandes 3,5 and Fernando António Leal Pacheco 3,6,* 1 Coordenadoria Regional das Promotorias de Justiça do Meio Ambiente das Bacias dos Rios Paranaíba e Baixo Rio Grande, Rua Coronel Antônio Rios, 951, Uberaba MG 38061-150, Brazil; [email protected] 2 Universidade Estadual Paulista, Faculdade de Ciências Agrárias e Veterinárias, Via de Acesso Prof. Paulo Donato Castellane, s/n, Jaboticabal SP 14884-900, Brazil; [email protected] (T.C.T.P.); marcilio.martins-fi[email protected] (M.V.M.F.) 3 POLUS—Grupo de Política de Uso do Solo, Universidade Estadual Paulista (UNESP), Via de Acesso Prof. Paulo Donato Castellane, s/n, Jaboticabal SP 14884-900, Brazil; [email protected] (R.F.d.V.J.); [email protected] (C.F.O.); lfi[email protected] (L.F.S.F.) 4 Instituto Federal do Triângulo Mineiro, Campus Uberaba, Laboratório de Geoprocessamento, Uberaba MG 38064-790, Brazil 5 Centro de Investigação e Tecnologias Agroambientais e Biológicas, Universidade de Trás-os-Montes e Alto Douro, Ap. 1013, 5001-801 Vila Real, Portugal; [email protected] 6 Centro de Química de Vila Real, Universidade de Trás-os-Montes e Alto Douro, Ap. 1013, 5001-801 Vila Real, Portugal * Correspondence: [email protected]; Tel.: +55-351-917519833 Received: 10 February 2019; Accepted: 12 March 2019; Published: 16 March 2019 Abstract: The riparian buffer width on watersheds has been modified over the last decades.
    [Show full text]
  • Riparian Systems
    Riparian Systems January 2007 Fish and Wildlife Habitat Management Leaflet Number 45 Introduction Riparian areas are transitional zones between terres- trial and aquatic systems exhibiting characteristics of both systems. They perform vital ecological functions linking terrestrial and aquatic systems within water- sheds. These functions include protecting aquatic eco- systems by removing sediments from surface runoff, decreasing flooding, maintaining appropriate water conditions for aquatic life, and providing organic ma- terial vital for productivity and structure of aquatic ecosystems. They also provide excellent wildlife hab- itat, offering not only a water source, but food and shelter, as well. NRCS Soils in riparian areas differ from soils in upland areas because they are formed from sediments with differ- ent textures and subjected to fluctuating water levels and degrees of wetness. These sediments are rich in nutrients and organic matter which allow the soils to retain large amounts of moisture, affecting the growth and diversity of the plant communities. Riparian areas typically are vegetated with lush growths of grasses, forbs, shrubs, and trees that are tolerant of periodic flooding. In some regions (Great Plains), however, trees may not be part of the his- toric riparian community. Areas with saline soils or U.S. Fish & Wildlife Service heavy, nearly-anaerobic soils (wet meadow environ- ments and high elevations) also are dominated by her- baceous vegetation. In intermittent waterways, the ri- parian area may be confined to the stream channel. Threats to riparian areas have come from many sourc- es. Riparian forests and bottomlands are fertile and valued farmland and rangeland, as well as prime wa- ter-front property desired by developers.
    [Show full text]
  • Maine and the National Lakes Assessment: Where Does Maine Stand ??
    Maine and the National Lakes Assessment: Where Does Maine Stand ?? With Appgologies to Neil Kamman Basic Components of Surveys *Randomized design to report on – Biological and habitat condition – Recreational condition – Trophic state *1,028 lakes sampled + 124 reference lakes *Standard protocols *Nati onall y consiitsten t and reggyionally relevant analyses Lake Conditions Assessed by Region The NLA represents: • 49,560 “lakes” • 59% natural origin • 41% constructed • 80% < 125 acres in size • 32 of 1028 Lakes were in Maine Maine Lake Sizes 3000 87% <= 125 acres 2500 58% <= 10 acres 12 2000 ber 1500 Num 1000 500 0 <1 1-10 10-100 100-500 500-1000 >1000 Acres 4 National Lakes Assessment: • Biology • Habitat Quality • Ecological integrity • Disturbance and integrity • Trophic State • Chemical stressors • Enrichment • NtiNutrien ts, AidAcid an d DO • Recreational Use • Cyanotoxins • Change over time • Sediments and nutrients National Lakes Assessment: Sampling Approach Condition of the Nation’s Lakes: Habitat • 55 individual habitat attributes captured at each site (550/lake). • MtiMetrics reddduced to four idiindices of hbitthabitat quality: – Human Disturbance on Lakeshores – Ripar ian Zone IiIntegrity – Littoral Zone Integrity – Complexity of Riparian/l/Littoral Interface • Disturbance index scores assessed against nationally consitisten t thres ho lds • Riparian/littoral indices assessed against regionally‐explicit reference conditions (corrects for expected regional differences) Extent of Stressors and Resulting Risk: What Impacts Biological
    [Show full text]
  • The Effects of Riparian Management Zone Delineation on Timber Value and Ecosystem Services in Diverse Forest Biomes Across the United States
    SUNY College of Environmental Science and Forestry Digital Commons @ ESF Dissertations and Theses Summer 8-12-2020 The Effects of Riparian Management Zone Delineation on Timber Value and Ecosystem Services in Diverse Forest Biomes Across the United States. Maneesha Jayasuriya SUNY College of Environmental Science and Forestry, [email protected] Follow this and additional works at: https://digitalcommons.esf.edu/etds Part of the Forest Management Commons Recommended Citation Jayasuriya, Maneesha, "The Effects of Riparian Management Zone Delineation on Timber Value and Ecosystem Services in Diverse Forest Biomes Across the United States." (2020). Dissertations and Theses. 190. https://digitalcommons.esf.edu/etds/190 This Open Access Dissertation is brought to you for free and open access by Digital Commons @ ESF. It has been accepted for inclusion in Dissertations and Theses by an authorized administrator of Digital Commons @ ESF. For more information, please contact [email protected], [email protected]. THE EFFECTS OF RIPRIAN MANAGEMENT ZONE DELINEATION ON TIMBER VALUE AND ECOSYSTEM SERVICES IN DIVERSE FOREST BIOMES ACROSS THE UNITED STATES by Maneesha Thirasara Jayasuriya A thesis submitted in partial fulfillment of the requirements for the Doctor of Philosophy Degree State University of New York College of Environmental Science and Forestry Syracuse, New York August 2020 Department of Sustainable Resources Management Approved by: René Germain, Major Professor Neil Ringler, Chair, Examining Committee Christopher Nowak, Department Chair S. Scott Shannon, Dean, The Graduate School Acknowledgements I wish to express my sincere gratitude to Dr. René Germain for being a great mentor and good friend. I truly value his expert knowledge, support, encouragement, and guidance given to me throughout the past years.
    [Show full text]
  • Towards Ecologically Functional Riparian Zones a Meta
    http://www.diva-portal.org This is the published version of a paper published in Journal of Environmental Management. Citation for the original published paper (version of record): Lind, L., Hasselquist, E M., Laudon, H. (2019) Towards ecologically functional riparian zones: A meta-analysis to develop guidelines for protecting ecosystem functions and biodiversity in agricultural landscapes Journal of Environmental Management, 249: 1-8 https://doi.org/10.1016/j.jenvman.2019.109391 Access to the published version may require subscription. N.B. When citing this work, cite the original published paper. Permanent link to this version: http://urn.kb.se/resolve?urn=urn:nbn:se:kau:diva-75700 Journal of Environmental Management 249 (2019) 109391 Contents lists available at ScienceDirect Journal of Environmental Management journal homepage: www.elsevier.com/locate/jenvman Review Towards ecologically functional riparian zones: A meta-analysis to develop guidelines for protecting ecosystem functions and biodiversity in T agricultural landscapes ⁎ Lovisa Linda,b, , Eliza Maher Hasselquista, Hjalmar Laudona a Department of Forest Ecology and Management, Swedish University of Agricultural Sciences, 901 83, Umeå, Sweden b Department of Environmental and Life Sciences, Karlstad University, 656 37, Karlstad, Sweden ARTICLE INFO ABSTRACT Keywords: Riparian zones contribute with biodiversity and ecosystem functions of fundamental importance for regulating Agricultural flow and nutrient transport in waterways. However, agricultural land-use and physical changes made to improve Buffer zone crop productivity and yield have resulted in modified hydrology and displaced natural vegetation. The mod- Ecological functional riparian zones ification to the hydrology and natural vegetation have affected the biodiversity and many ecosystem functions Riparian zone provided by riparian zones.
    [Show full text]
  • Malaysia's Policies and Plans Contain Emphasis and Provisions for Holistic
    Malaysia’s policies and plans contain emphasis and provisions for holistic and integrated planning and management of natural resource and biodiversity assets as a precursor for environmentally sustainable development. For planners, decision-makers and practitioners to meet these aspirations, resources must be viewed in a broader context. Not only must it go beyond sectors to include all stakeholders in the decision process, but it must also use the best science available to define suitable management actions. The overall purpose of this Guideline is to support this important endeavour. MANAGING BIODIVERSITY IN THE RIPARIAN ZONE i Table of Contents Tables, Figures and Text Boxes .....................................................................ii Abbreviations..................................................................................................iii 1 Introduction .................................................................................................1 1.1 Who is this Guide for?.......................................................................1 1.2 Purpose of this Guide.........................................................................1 1.3 Using this Guide ................................................................................1 2 The Riparian Zone ......................................................................................2 2.1 What is a riparian zone?.....................................................................3 2.2 Why is the riparian zone important?..................................................3
    [Show full text]
  • Hydrology and Water Quality of a Field and Riparian Buffer Adjacent to A
    G Model ECOENG-2313; No. of Pages 9 ARTICLE IN PRESS Ecological Engineering xxx (2012) xxx–xxx Contents lists available at SciVerse ScienceDirect Ecological Engineering j ournal homepage: www.elsevier.com/locate/ecoleng Hydrology and water quality of a field and riparian buffer adjacent to a mangrove wetland in Jobos Bay watershed, Puerto Rico c a,∗ a b c d a C.O. Williams , R. Lowrance , D.D. Bosch , J.R. Williams , E. Benham , A. Dieppa , R. Hubbard , e a f b a a E. Mas , T. Potter , D. Sotomayor , E.M. Steglich , T. Strickland , R.G. Williams a Southeast Watershed Research Laboratory, 2379 Rainwater Road, Tifton, GA 31794, United States b Blackland Research Center, Texas A&M University, Temple, TX 76502, United States c Charles E. Kellogg National Soil Survey Laboratory & Research, 100 Centennial Mall North, Lincoln, NE 68508, United States d National Estuarine Research Reserve, Call Box B, Aguirre, PR 00704, United States e Natural Resource Conservation Service-Caribbean, 2200 Pedro Albizu Campos Ave 23, Mayaguez, PR 00680, United States f University of Puerto Rico-Mayagüez, P.O. Box 9000, Mayagüez, PR 00681, United States a r t i c l e i n f o a b s t r a c t Article history: Agriculture in coastal areas of Puerto Rico is often adjacent to or near mangrove wetlands. Riparian buffers, Received 24 January 2012 while they may also be wetlands, can be used to protect mangrove wetlands from agricultural inputs of Received in revised form sediment, nutrients, and pesticides. We used simulation models and field data to estimate the water, 25 September 2012 nitrogen, and phosphorus inputs from an agricultural field and riparian buffer to a mangrove wetland Accepted 28 September 2012 in Jobos Bay watershed, Puerto Rico.
    [Show full text]
  • Characterization of Riparian Tree Communities Along a River Basin in the Pacific Slope of Guatemala
    Article Characterization of Riparian Tree Communities along a River Basin in the Pacific Slope of Guatemala Alejandra Alfaro Pinto 1,2,* , Juan J. Castillo Mont 2, David E. Mendieta Jiménez 2, Alex Guerra Noriega 3, Jorge Jiménez Barrios 4 and Andrea Clavijo McCormick 1,* 1 School of Agriculture & Environment, Massey University, Palmerston North 4474, New Zealand 2 Herbarium AGUAT ‘Professor José Ernesto Carrillo’, Agronomy Faculty, University of San Carlos of Guatemala, Guatemala City 1012, Guatemala; [email protected] (J.J.C.M.); [email protected] (D.E.M.J.) 3 Private Institute for Climate Change Research (ICC), Santa Lucía Cotzumalguapa, Escuintla 5002, Guatemala; [email protected] 4 School of Biology, University of San Carlos of Guatemala, Guatemala City 1012, Guatemala; [email protected] * Correspondence: [email protected] (A.A.P.); [email protected] (A.C.M.) Abstract: Ecosystem conservation in Mesoamerica, one of the world’s biodiversity hotspots, is a top priority because of the rapid loss of native vegetation due to anthropogenic activities. Riparian forests are often the only remaining preserved areas among expansive agricultural matrices. These forest remnants are essential to maintaining water quality, providing habitats for a variety of wildlife Citation: Alfaro Pinto, A.; Castillo and acting as biological corridors that enable the movement and dispersal of local species. The Mont, J.J.; Mendieta Jiménez, D.E.; Acomé river is located on the Pacific slope of Guatemala. This region is heavily impacted by intensive Guerra Noriega, A.; Jiménez Barrios, agriculture (mostly sugarcane plantations), fires and grazing. Most of this region’s original forest J.; Clavijo McCormick, A.
    [Show full text]
  • Guidelines for Riparian and Wetland Buffers
    Guidelines for Riparian and Wetland Buffers Prepared for: City of Carlsbad Planning Department 1635 Faraday Avenue Carlsbad, CA 92008 Prepared by: Technology Associates (TAIC) 9089 Clairemont Mesa Blvd. Suite 200 San Diego, CA 92123 April 9, 2010 This page intentionally left blank Table of Contents Contents Page 1.0 INTRODUCTION ....................................................................................................................... 1 1.1 BENEFITS OF RIPARIAN AND WETLAND BUFFERS....................................................................... 2 1.2 GOALS & OBJECTIVES.............................................................................................................. 3 1.3 DEFINITIONS............................................................................................................................ 3 2.0 BUFFER DESIGN GUIDELINES .............................................................................................. 6 2.1 HMP AREA-WIDE .................................................................................................................... 6 2.2 COASTAL ZONE ....................................................................................................................... 7 2.3 STANDARDS AREAS ................................................................................................................. 8 2.4 THREE-ZONE BUFFER DESIGN ................................................................................................. 9 2.5 ALTERNATIVE BUFFER CONFIGURATIONS ...............................................................................
    [Show full text]