Wetland Soils, Hydrology and Geomorphology
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Peat and Peatland Resources of Southeastern Ontario
THESE TERMS GOVERN YOUR USE OF THIS DOCUMENT Your use of this Ontario Geological Survey document (the “Content”) is governed by the terms set out on this page (“Terms of Use”). By downloading this Content, you (the “User”) have accepted, and have agreed to be bound by, the Terms of Use. Content: This Content is offered by the Province of Ontario’s Ministry of Northern Development and Mines (MNDM) as a public service, on an “as-is” basis. Recommendations and statements of opinion expressed in the Content are those of the author or authors and are not to be construed as statement of government policy. You are solely responsible for your use of the Content. You should not rely on the Content for legal advice nor as authoritative in your particular circumstances. Users should verify the accuracy and applicability of any Content before acting on it. MNDM does not guarantee, or make any warranty express or implied, that the Content is current, accurate, complete or reliable. MNDM is not responsible for any damage however caused, which results, directly or indirectly, from your use of the Content. MNDM assumes no legal liability or responsibility for the Content whatsoever. Links to Other Web Sites: This Content may contain links, to Web sites that are not operated by MNDM. Linked Web sites may not be available in French. MNDM neither endorses nor assumes any responsibility for the safety, accuracy or availability of linked Web sites or the information contained on them. The linked Web sites, their operation and content are the responsibility of the person or entity for which they were created or maintained (the “Owner”). -
Northern Fen Communitynorthern Abstract Fen, Page 1
Northern Fen CommunityNorthern Abstract Fen, Page 1 Community Range Prevalent or likely prevalent Infrequent or likely infrequent Absent or likely absent Photo by Joshua G. Cohen Overview: Northern fen is a sedge- and rush-dominated 8,000 years. Expansion of peatlands likely occurred wetland occurring on neutral to moderately alkaline following climatic cooling, approximately 5,000 years saturated peat and/or marl influenced by groundwater ago (Heinselman 1970, Boelter and Verry 1977, Riley rich in calcium and magnesium carbonates. The 1989). community occurs north of the climatic tension zone and is found primarily where calcareous bedrock Several other natural peatland communities also underlies a thin mantle of glacial drift on flat areas or occur in Michigan and can be distinguished from shallow depressions of glacial outwash and glacial minerotrophic (nutrient-rich) northern fens, based on lakeplains and also in kettle depressions on pitted comparisons of nutrient levels, flora, canopy closure, outwash and moraines. distribution, landscape context, and groundwater influence (Kost et al. 2007). Northern fen is dominated Global and State Rank: G3G5/S3 by sedges, rushes, and grasses (Mitsch and Gosselink 2000). Additional open wetlands occurring on organic Range: Northern fen is a peatland type of glaciated soils include coastal fen, poor fen, prairie fen, bog, landscapes of the northern Great Lakes region, ranging intermittent wetland, and northern wet meadow. Bogs, from Michigan west to Minnesota and northward peat-covered wetlands raised above the surrounding into central Canada (Ontario, Manitoba, and Quebec) groundwater by an accumulation of peat, receive inputs (Gignac et al. 2000, Faber-Langendoen 2001, Amon of nutrients and water primarily from precipitation et al. -
Parametric Terracing As Optimization of Controlled Slope Intervention
water Article Parametric Terracing as Optimization of Controlled Slope Intervention Tomaž Berˇciˇc and Lucija Ažman-Momirski * Faculty of Architecture, University of Ljubljana, Zoisova 12, 1000 Ljubljana, Slovenia; [email protected] * Correspondence: [email protected] Received: 31 December 2019; Accepted: 21 February 2020; Published: 26 February 2020 Abstract: With the introduction of mechanization in agriculture, the area of terraced slopes has increased. However, in most cases, the planning of terracing in practice remains experience-based, which is no longer effective from an agricultural, geological, and hydrological point of view. The usual method of building terraces, especially terraces with earth risers, is therefore outdated, and a new method must be found for planning and building terraced areas. In addition to geographical information system (GIS) tools, parametric design tools for planning terraced landscapes are now available. Based on the design approaches for a selected plot in the Gorizia Hills in Slovenia, where we used a trial-and-error method, we improved previous results by defining a model using a computer algorithm that generates a terraced landscape on a selected slope depending on various input parameters such as the height of the terrace slope, the inclination of the terrace slope, the width of the terrace platform, and the number of terraces. For the definition of the algorithm we used the visual program tool Grasshopper. By changing the values of the input data parameters, the algorithm was able to present combinatorial simulations through a variety of different solutions with all the corresponding statistics. With such results it is much easier to make a conscious decision on which combination of parameters is optimal to prevent landslides, plan adequate drainage, and control soil movements when building terraces. -
Pocket Guide to Hydric Soils for Wetland Delineations In
The Buzzards Bay National Estuary Program Buzzards Bay National Estuary Program 2870 Cranberry Highway East Wareham, MA 02538 Pocket Guide to Hydric Soils #508-291-3625 x 14 www.buzzardsbay.org for Wetland Delineations in Massachusetts Version 2.1 The Buzzards Bay National Estuary Program November, 2014 This document is a compilation of material taken from Delineating Bordering Vegetated Appendix G – Observing and Recording Hue, Value and Chroma Wetlands under the Wetlands Protection Act, published by the Massachusetts Department of Environmental Protection, Division of Wetlands, and Waterways and the Regional All colors noted in this Booklet refer to moist Munsell® colors (Gretag/Macbeth 2000). Do not attempt to determine colors while wearing sunglasses or tinted lenses. Colors must be determined Supplement to the Corps of Engineers Wetland Delineation Manual: Northcentral and under natural light and not under artificial light. Northeast Region (Version 2.0), published by the U.S. Army Engineer Research and Development Center. Chroma Soil colors specified in the ACOE indicators do not have decimal points (except for indicator A12); This document also includes excerpts from the Field Indicators of Hydric Soils in the however, intermediate colors do occur between Munsell chips. Soil color should not be rounded to United States, A Guide for Identifying and Delineation Hydric Soils, Version 7.0, qualify as meeting an indicator. For example, a soil matrix with a chroma between 2 and 3 should including the 2013 Errata, as well as Field Indicators for Identifying Hydric Soils in New be recorded as having a chroma of 2+. This soil material does not have a chroma of 2 and would England, 3rd ed. -
Field Indicators of Hydric Soils in the United States Natural Resources a Guide for Identifying and Delineating Conservation Service Hydric Soils, Version 7.0, 2010
United States In cooperation with Department of the National Technical Agriculture Committee for Hydric Soils Field Indicators of Hydric Soils in the United States Natural Resources A Guide for Identifying and Delineating Conservation Service Hydric Soils, Version 7.0, 2010 Field Indicators of Hydric Soils in the United States A Guide for Identifying and Delineating Hydric Soils, Version 7.0, 2010 United States Department of Agriculture, Natural Resources Conservation Service, in cooperation with the National Technical Committee for Hydric Soils Edited by L.M. Vasilas, Soil Scientist, NRCS, Washington, DC; G.W. Hurt, Soil Scientist, University of Florida, Gainesville, FL; and C.V. Noble, Soil Scientist, USACE, Vicksburg, MS ii The U.S. Department of Agriculture (USDA) prohibits discrimination in all its programs and activities on the basis of race, color, national origin, age, disability, and where applicable, sex, marital status, familial status, parental status, religion, sexual orientation, genetic information, political beliefs, reprisal, or because all or a part of an individual’s income is derived from any public assistance program. (Not all prohibited bases apply to all programs.) Persons with disabilities who require alternative means for communication of program information (Braille, large print, audiotape, etc.) should contact USDA’s TARGET Center at (202) 720-2600 (voice and TDD). To file a complaint of discrimination, write to USDA, Director, Office of Civil Rights, 1400 Independence Avenue, S.W., Washington, D.C. 20250-9410 or call (800) 795-3272 (voice) or (202) 720-6382 (TDD). USDA is an equal opportunity provider and employer. Copies of this publication can be obtained from: NRCS National Publications and Forms Distribution Center LANDCARE 1-888-LANDCARE (888-526-3227) [email protected] Information contained in this publication and additional information concerning hydric soils are maintained on the Web site at http://soils.usda.gov/use/hydric/. -
5.15 Water Pollution and Hydrologic Impacts 5.15.1 Chapter Index 5.15
Transportation Cost and Benefit Analysis II – Water Pollution Victoria Transport Policy Institute (www.vtpi.org) 5.15 Water Pollution and Hydrologic Impacts This chapter describes water pollution and hydrologic impacts caused by transport facilities and vehicle use. 5.15.1 Chapter Index 5.15 Water Pollution and Hydrologic Impacts ........................................................... 1 5.15.2 Definitions .............................................................................................. 1 5.15.3 Discussion ............................................................................................. 1 5.15.4 Estimates: .............................................................................................. 3 Summary Table ..................................................................................... 3 Water Pollution & Combined Estimates ................................................. 4 Storm Water, Hydrology and Wetlands ................................................. 6 5.15.5 Variability ............................................................................................... 7 5.15.6 Equity and Efficiency Issues .................................................................. 7 5.15.7 Conclusion ............................................................................................. 7 5.15.8 Information Resources .......................................................................... 9 5.15.2 Definitions Water pollution refers to harmful substances released into surface or ground water, -
Field Indicators of Hydric Soils
United States Department of Field Indicators of Agriculture Natural Resources Hydric Soils in the Conservation Service United States In cooperation with A Guide for Identifying and Delineating the National Technical Committee for Hydric Soils Hydric Soils, Version 8.2, 2018 Field Indicators of Hydric Soils in the United States A Guide for Identifying and Delineating Hydric Soils Version 8.2, 2018 (Including revisions to versions 8.0 and 8.1) United States Department of Agriculture, Natural Resources Conservation Service, in cooperation with the National Technical Committee for Hydric Soils Edited by L.M. Vasilas, Soil Scientist, NRCS, Washington, DC; G.W. Hurt, Soil Scientist, University of Florida, Gainesville, FL; and J.F. Berkowitz, Soil Scientist, USACE, Vicksburg, MS ii In accordance with Federal civil rights law and U.S. Department of Agriculture (USDA) civil rights regulations and policies, the USDA, its Agencies, offices, and employees, and institutions participating in or administering USDA programs are prohibited from discriminating based on race, color, national origin, religion, sex, gender identity (including gender expression), sexual orientation, disability, age, marital status, family/parental status, income derived from a public assistance program, political beliefs, or reprisal or retaliation for prior civil rights activity, in any program or activity conducted or funded by USDA (not all bases apply to all programs). Remedies and complaint filing deadlines vary by program or incident. Persons with disabilities who require alternative means of communication for program information (e.g., Braille, large print, audiotape, American Sign Language, etc.) should contact the responsible Agency or USDA’s TARGET Center at (202) 720-2600 (voice and TTY) or contact USDA through the Federal Relay Service at (800) 877-8339. -
Modeling Groundwater Rise Caused by Sea-Level Rise in Coastal New Hampshire Jayne F
Journal of Coastal Research 35 1 143–157 Coconut Creek, Florida January 2019 Modeling Groundwater Rise Caused by Sea-Level Rise in Coastal New Hampshire Jayne F. Knott†*, Jennifer M. Jacobs†, Jo S. Daniel†, and Paul Kirshen‡ †Department of Civil and Environmental Engineering ‡School for the Environment University of New Hampshire University of Massachusetts Boston Durham, NH 03824, U.S.A. Boston, MA 02125, U.S.A. ABSTRACT Knott, J.F.; Jacobs, J.M.; Daniel, J.S., and Kirshen, P., 2019. Modeling groundwater rise caused by sea-level rise in coastal New Hampshire. Journal of Coastal Research, 35(1), 143–157. Coconut Creek (Florida), ISSN 0749-0208. Coastal communities with low topography are vulnerable from sea-level rise (SLR) caused by climate change and glacial isostasy. Coastal groundwater will rise with sea level, affecting water quality, the structural integrity of infrastructure, and natural ecosystem health. SLR-induced groundwater rise has been studied in coastal areas of high aquifer transmissivity. In this regional study, SLR-induced groundwater rise is investigated in a coastal area characterized by shallow unconsolidated deposits overlying fractured bedrock, typical of the glaciated NE. A numerical groundwater-flow model is used with groundwater observations and withdrawals, LIDAR topography, and surface-water hydrology to investigate SLR-induced changes in groundwater levels in New Hampshire’s coastal region. The SLR groundwater signal is detected more than three times farther inland than projected tidal flooding from SLR. The projected mean groundwater rise relative to SLR is 66% between 0 and 1 km, 34% between 1 and 2 km, 18% between 2 and 3 km, 7% between 3 and 4 km, and 3% between 4 and 5 km of the coastline, with large variability around the mean. -
Soil Characterization, Classification, and Biomass Accumulation in the Otter Creek Wilderness
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by The Research Repository @ WVU (West Virginia University) Graduate Theses, Dissertations, and Problem Reports 2003 Soil characterization, classification, and biomass accumulation in the Otter Creek Wilderness Jamie Schnably West Virginia University Follow this and additional works at: https://researchrepository.wvu.edu/etd Recommended Citation Schnably, Jamie, "Soil characterization, classification, and biomass accumulation in the Otter Creek Wilderness" (2003). Graduate Theses, Dissertations, and Problem Reports. 1800. https://researchrepository.wvu.edu/etd/1800 This Thesis is protected by copyright and/or related rights. It has been brought to you by the The Research Repository @ WVU with permission from the rights-holder(s). You are free to use this Thesis in any way that is permitted by the copyright and related rights legislation that applies to your use. For other uses you must obtain permission from the rights-holder(s) directly, unless additional rights are indicated by a Creative Commons license in the record and/ or on the work itself. This Thesis has been accepted for inclusion in WVU Graduate Theses, Dissertations, and Problem Reports collection by an authorized administrator of The Research Repository @ WVU. For more information, please contact [email protected]. Soil Characterization, Classification, and Biomass Accumulation in the Otter Creek Wilderness Jamie Schnably Thesis submitted to The Davis College of Agriculture, Forestry, and Consumer Sciences at West Virginia University In partial fulfillment of the requirements for the degree of Master of Science In Plant and Soil Sciences John C. Sencindiver, Ph. D., Chair Louis McDonald, Ph. -
NRSM 385 Syllabus for Watershed Hydrology V200114 Spring 2020
NRSM 385 Syllabus for Watershed Hydrology v200114 Spring 2020 NRSM (385) Watershed Hydrology Instructor: Teaching Assistant: Kevin Hyde Shea Coons CHCB 404 CHCB 404 [email protected] [email protected] Course Time & Location: Office Hours: (or by appointment) Tue/Thu 0800 – 0920h Kevin: Tue & Thu, 1500 – 1600h Natural Science 307 Shea: Wed & Fri, 1200 – 1300h Recommended course text: Physical Hydrology by SL Dingman, 2002 (2nd edition). Other readings as assigned. Additional course information and materials will be posted on Moodle: umonline.umt.edu Science of water resource management in the 21st Century: Sustainability of all life requires fundamental changes in hydrologic science and water resource management. Forty percent of the Earth’s ever-increasing population lives in areas of water scarcity, where the available supply cannot meet basic needs. Water pollution from human activities and increasing water withdrawals for human use impair and threaten entire ecosystems upon which human survival depends. Climate change increases environmental variability, exacerbating drought in some regions while leading to greater hydrologic hazards in others. Higher intensity and more frequent storms generate flooding that is especially destructive in densely developed areas of and where ecosystems are already compromised. Sustainable water resource management starts with scientifically sound management of forested landscapes. Eighty percent of fresh water supplies in the US originate on forested lands, providing over 60% of municipal drinking water. Forests also account for significant portions of biologically complex and vital ecosystems. Multiple land use activities including logging, agriculture, industry, mining, and urban development compromise forest ecosystems and threaten aquatic ecosystems and freshwater supplies. -
Town of Seneca
TOWN OF BRISTOL Inventory of Land Use and Land Cover Prepared for: Ontario County Water Resources Council 20 Ontario Street, 3rd Floor Canandaigua, New York 14424 and Town of Bristol 6740 County Road 32 Canandaigua, New York 14424 Prepared by: Dr. Bruce Gilman Department of Environmental Conservation and Horticulture Finger Lakes Community College 3325 Marvin Sands Drive Canandaigua, New York 14424-8395 2020 Cover image: Ground level view of a perched swamp white oak forest community (S1S2) surrounding a shrub swamp that was discovered and documented on Johnson Hill north of Dugway Road. This forest community type is rare statewide and extremely rare locally, and harbors a unique assemblage of uncommon plant species. (Image by the Bruce Gilman). Acknowledgments: For over a decade, the Ontario County Planning Department has supported a working partnership between local towns and the Department of Environmental Conservation and Horticulture at Finger Lakes Community College that involves field research, ground truthing and digital mapping of natural land cover and cultural land use patterns. Previous studies have been completed for the Canandaigua Lake watershed, the southern Honeoye Valley, the Honeoye Lake watershed, the complete Towns of Canandaigua, Gorham, Richmond and Victor, and the woodlots, wetlands and riparian corridors in the Towns of Seneca, Phelps and Geneva. This report summarizes the latest land use/land cover study conducted in the Town of Bristol. The final report would not have been completed without the vital assistance of Terry Saxby of the Ontario County Planning Department. He is gratefully thanked for his assistance with landowner information, his patience as the fieldwork was slowly completed, and his noteworthy help transcribing the field maps to geographic information system (GIS) shape files. -
Properties of Soils of the Outwash Terraces of Wisconsin Age in Iowa
Proceedings of the Iowa Academy of Science Volume 59 Annual Issue Article 30 1952 Properties of Soils of the Outwash Terraces of Wisconsin Age in Iowa C. Lynn Coultas Iowa State College Ralph J. McCracken U.S. Department of Agriculture Let us know how access to this document benefits ouy Copyright ©1952 Iowa Academy of Science, Inc. Follow this and additional works at: https://scholarworks.uni.edu/pias Recommended Citation Coultas, C. Lynn and McCracken, Ralph J. (1952) "Properties of Soils of the Outwash Terraces of Wisconsin Age in Iowa," Proceedings of the Iowa Academy of Science, 59(1), 233-247. Available at: https://scholarworks.uni.edu/pias/vol59/iss1/30 This Research is brought to you for free and open access by the Iowa Academy of Science at UNI ScholarWorks. It has been accepted for inclusion in Proceedings of the Iowa Academy of Science by an authorized editor of UNI ScholarWorks. For more information, please contact [email protected]. Coultas and McCracken: Properties of Soils of the Outwash Terraces of Wisconsin Age in I Properties of Soils of the Outwash Terraces of Wisconsin Age in Iowa By C. LYNN CouLTAS1 AND RALPH J. McCRACKEN2 Joint contribution from the Iowa Agricultural Experiment Station and the U. S. Department of Agriculture. Journal paper No. J-2092, Project 1152 of the Iowa Agricultural Experiment Station, Ames, Iowa. INTRODUCTION For adequate classification and mapping of soils it is necessary to learn as much as possible about their chemical and physical properties, their age, and the parent materials or geological materials from which they have formed.