Beaver Conflicts in Vermont
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Chapter Ii Mine Tailings Facilities
14 TOWARDS ZERO HARM – A COMPENDIUM OF PAPERS PREPARED FOR THE GLOBAL TAILINGS REVIEW TOWARDS ZERO HARM – A COMPENDIUM OF PAPERS PREPARED FOR THE GLOBAL TAILINGS REVIEW 15 SETTING THE SCENE CHAPTER II Upstream MINE TAILINGS 4 3 FACILITIES: OVERVIEW 2 1 AND INDUSTRY TRENDS Starter dyke: 1 Downstream The embankment design terms, upstream, Elaine Baker*, Professor, The University of Sydney, Australia and GRID Arendal, Arendal, Norway downstream and centreline, indicate the 4 Michael Davies*, Senior Advisor – Tailings & Mine Waste, Teck Resources Limited, Vancouver, Canada direction in which the embankment crest 3 moves in relation to the starter dyke at the Andy Fourie, Professor, University of Western Australia, Australia 2 base of the embankment wall. Gavin Mudd, Associate Professor, RMIT University, Australia 1 Kristina Thygesen, Programme Group Leader, Geological Resources and Ocean Governance, GRID Arendal, Norway Centreline Dyke: 2 to 4 or more 4 Dykes are added to raise the embankment. This continues throughout the operation 3 of the mine. 1. INTRODUCTION The tailings are most commonly stored on site 2 in a tailings storage facility. Storage methods for 1 This chapter provides an overview of mine tailings conventional tailings include cross-valley and paddock and mine tailings facilities. It illustrates why and (ring-dyke) impoundments, where the tailings are how mine tailings are produced, and the complexity behind a raised embankment(s) that then, by many Source: Vick, 1983, 1990 involved in the long-term storage and management definitions, become a dam, or multiple dams. of this waste product. The call for a global standard However, a tailings facility can have an embankment Figure 1. -
Dam Effects on Low-Tide Channel Pools and Fish Use of Estuarine Habitat
Beaver in Tidal Marshes: Dam Effects on Low-Tide Channel Pools and Fish Use of Estuarine Habitat W. Gregory Hood Wetlands Official Scholarly Journal of the Society of Wetland Scientists ISSN 0277-5212 Wetlands DOI 10.1007/s13157-012-0294-8 1 23 Your article is protected by copyright and all rights are held exclusively by Society of Wetland Scientists. This e-offprint is for personal use only and shall not be self- archived in electronic repositories. If you wish to self-archive your work, please use the accepted author’s version for posting to your own website or your institution’s repository. You may further deposit the accepted author’s version on a funder’s repository at a funder’s request, provided it is not made publicly available until 12 months after publication. 1 23 Author's personal copy Wetlands DOI 10.1007/s13157-012-0294-8 ARTICLE Beaver in Tidal Marshes: Dam Effects on Low-Tide Channel Pools and Fish Use of Estuarine Habitat W. Gregory Hood Received: 31 August 2011 /Accepted: 16 February 2012 # Society of Wetland Scientists 2012 Abstract Beaver (Castor spp.) are considered a riverine or can have multi-decadal or longer effects on river channel form, lacustrine animal, but surveys of tidal channels in the Skagit riverine and floodplain wetlands, riparian vegetation, nutrient Delta (Washington, USA) found beaver dams and lodges in the spiraling, benthic community structure, and the abundance and tidal shrub zone at densities equal or greater than in non-tidal productivity of fish and wildlife (Jenkins and Busher 1979; rivers. Dams were typically flooded by a meter or more during Naiman et al. -
Inventory of Tidepool and Estuarine Fishes in Acadia National Park
INVENTORY OF TIDEPOOL AND ESTUARINE FISHES IN ACADIA NATIONAL PARK Edited by Linda J. Kling and Adrian Jordaan School of Marines Sciences University of Maine Orono, Maine 04469 Report to the National Park Service Acadia National Park February 2008 EXECUTIVE SUMMARY Acadia National Park (ANP) is part of the Northeast Temperate Network (NETN) of the National Park Service’s Inventory and Monitoring Program. Inventory and monitoring activities supported by the NETN are becoming increasingly important for setting and meeting long-term management goals. Detailed inventories of fishes of estuaries and intertidal areas of ANP are very limited, necessitating the collection of information within these habitats. The objectives of this project were to inventory fish species found in (1) tidepools and (2) estuaries at locations adjacent to park lands on Mount Desert Island and the Schoodic Peninsula over different seasons. The inventories were not intended to be part of a long-term monitoring effort. Rather, the objective was to sample as many diverse habitats as possible in the intertidal and estuarine zones to maximize the resultant species list. Beyond these original objectives, we evaluated the data for spatial and temporal patterns and trends as well as relationships with other biological and physical characteristics of the tidepools and estuaries. For the tidepool survey, eighteen intertidal sections with multiple pools were inventoried. The majority of the tidepool sampling took place in 2001 but a few tidepools were revisited during the spring/summer period of 2002 and 2003. Each tidepool was visited once during late spring (Period 1: June 6 – June 26), twice during the summer (Period 2: July 3 – August 2 and Period 3: August 3 – September 18) and once during early fall (Period 4: September 29 – October 21). -
Beaver Dam Mine Project Environmental Impact Statement
Plain Language Summary BEAVER DAM MINE PROJECT ENVIRONMENTAL IMPACT STATEMENT 1 Table Of Contents 3 About 4 Project Overview 5 Sustainable Development at Beaver Dam Mine Project 6 Current Condition of the Project Site 8 Project Description 10 The Life of the Mine 12 The Environmental Assessment Process 14 Engaging Communities of Nova Scotia • Meeting with the Mi’kmaq of Nova Scotia • Meeting with the General Public 16 Traditional Use by Mi’kmaq People • Nearest Mi’kmaq Communities 18 The Natural & Human Environment Today • Fish & Wildlife • Water • Current Use by Mi’kmaq Communities • Mi’kmaq Ecological Knowledge Study • Traditional Land and Resource Use Study (Millbrook First Nation) • Cultural and Heritage Resources • Recreational and Commercial Activities 22 Effects on the Natural & Human Environment • Air • Light • Noise • Groundwater • Surface Water • Land • Animals • Fish • Birds • Cultural and Heritage Resources • Effects to the Mi’kmaq People 34 Environmental Monitoring 36 Reclamation 38 Environmental Management Programs ꢀ 40ꢀ BenefitsꢀofꢀtheꢀProject 2 41 Conclusions 1 Increase font size for all body copy? About The purpose of this booklet is to describe, in plain language, theꢀproposed development of a gold mine at Beaver Dam (Marinette), inꢀHalifax County, Nova Scotia. Atlantic Mining NS Corp. (Atlantic Gold) isꢀtheꢀcompany that wants to develop this mine. This is a plain language summary of the Environmental Impact Statement that Atlantic Gold first gave to the federal government in 2017. It is important to Atlantic Gold that you understand how they will build the mine. Atlantic Gold wants you to know how they will protect the environment during building, operating and closure of the mine. -
Louvicourt Mine Tailings Storage Facility and Polishing Pond 2019 Dam Safety Inspection
REPORT Louvicourt Mine Tailings Storage Facility and Polishing Pond 2019 Dam Safety Inspection Submitted to: Morgan Lypka, P.Eng. Teck Resources Ltd. 601 Knighton Road, Kimberley, BC V1A 3E1 Submitted by: Golder Associates Ltd. 7250, rue du Mile End, 3e étage Montréal (Québec) H2R 3A4 Canada +1 514 383 0990 001-19118317-5000-RA-Rev0 25 March 2020 25 March 2020 001-19118317-5000-RA-Rev0 Distribution List 1 e-copy: Teck Resources Ltd., Kimberley, BC 1 e-copy: Golder Associates Ltd., Saskatoon, SK 1 e-copy: Golder Associates Ltd., Montreal, QC 1 e-copy: MELCC, Rouyn-Noranda, QC 1 copy: MELCC, Rouyn-Noranda, QC i 25 March 2020 001-19118317-5000-RA-Rev0 Executive Summary This report presents the 2019 annual dam safety inspection (DSI) for the tailings storage facility (TSF) and polishing pond at the closed Louvicourt mine site located near Val-d’Or, Quebec. This report was prepared based on a site visit carried out on September 24, 2019 by Laurent Gareau and Simon Chapuis of Golder Associates Ltd (Golder), Morgan Lypka and Jason McBain of Teck Resources Limited (Teck, Owner), Jonathan Charland of Glencore Canada (Glencore, Owner) and Rene Fontaine of WSP (who conducts routine inspections with Glencore personnel), as well as on a review of available data representative of conditions over the period since the previous annual DSI. Golder Associates are the original designer of the facility and have been the provider of the Engineer of Record (EOR) since 2017. Golder performed an inspection in 2009, and then has performed annual inspections of the facilities since 2014. -
Beavers Are Cleaning Stormwater, Cooling Streams, and Increasing Complexity in Gresham
Beavers are Cleaning Stormwater, Cooling Streams, and Increasing Complexity in Gresham Katie Holzer Watershed Scientist City of Gresham, Oregon 1 Overview 1) Stormwater facility study 2) Stream temperature study 3) Stream complexity observations 2 Gresham 3 Dozens of Beaver Dams in Gresham Streams • Seem to be increasing drastically in past 10 years • Most strongly associated with public land 4 Variety of Dams https://www.facebook.com/JohnsonCreekWC/videos/382315012475862/ 5 1) Stormwater Facility Study 6 Columbia Slough Regional Water Quality Facility • Constructed in 2007-08 • 13-acre site • Treats 965 acres of industrial and commercial land • Cost = $2.4M • Goals: clean stormwater, provide habitat, foster education 7 Columbia Slough Regional Water Quality Facility 8 Columbia Slough Regional Water Quality Facility + Beavers 9 Question: Do the beaver dams help or hinder the water quality treatment in this facility? 10 Methods – Dam Removal 11 Methods – Water Quality Sampling • Collected water quality samples during storms • Inlets and outlets of facility • Before and after dam removal and rebuilding • 7 storms without dams, 7 storms with dams • Metals, nutrients, sediment, pesticides 12 Results 100 No beaver dams 80 60 40 20 % Pollutant Removal Pollutant % 0 -20 -40 13 Results 100 No beaver dams With beaver dams 80 60 40 20 % Pollutant Removal Pollutant % 0 -20 -40 14 Beaver dams slow and filter stormwater 15 New Question: What if the beavers leave?! 16 Continually Remove One Dam 17 Suggestions for Designing Stormwater Facilities with -
Beaver Dam Lake Report 2012
Beaver Dam Lake Aquatic Macrophytic Survey Report 580 Rockport Rd. Hackettstown, NJ 07840 Phone: 908-850-8690 Fax: 908-850-4994 www.alliedbiological.com Table of Contents Introduction .................................................................................................................................................. 3 Procedures: ............................................................................................................................................... 3 Macrophyte Summary: ................................................................................................................................. 4 Macrophyte Abundance and Distribution Discussion .................................................................................. 9 Summary of Findings: ................................................................................................................................. 12 2 11/30/2012 Beaver Dam Lake Protection and Rehabilitation District 557 Shore Drive New Windsor, NY 12553 2012 Aquatic Macrophytic Survey Report Beaver Dam Lake Orange County, New York Introduction On September 7, 2012 Allied Biological, Inc. conducted a detailed aquatic macrophyte survey at Beaver Dam Lake located in Orange County, NY. During the survey, 102 GPS-referenced locations were sampled for the presence of aquatic macrophytes in the main basin of the lake. The primary goal of the survey was to map the diverse vegetation present in the lake for scientific determination of best management strategies. In the Appendix -
W234 N8676 Woodside Rd. Lisbon, WI 53089
TOWN OF LISBON W234 N8676 Woodside Rd. Lisbon, WI 53089 Join Zoom Meeting Online: https://zoom.us/j/97986382979?pwd=T3V0cURMY3dIRnU4eHhHNXgxOHBsQT09 Join Zoom by Phone: Dial 1-312-626-6799 Meeting ID: 979 8638 2979 Passcode: 060914 TOWN BOARD MEETING AGENDA Lisbon Town Hall Board Room Monday, June 14, 2021 6:30 P.M. 1. Roll Call. 2. Pledge of Allegiance. 3. Comments from citizens present. Citizens are invited to share their questions, comments, or concerns with the Town Board. When speaking, citizens should state their name and address for the record and limit their presentation to three minutes. Where possible, the Board will answer factual questions immediately. If a response would involve discussion of Board policy or decisions, which might be of interest to citizens, not present at the meeting, the Board may place the item on a future meeting agenda. 4. Meeting Minutes. • Discussion and necessary action regarding approval of May 24, 2021, Town Board minutes. 5. Accounts Payable. • Authorize the payment of bills in the amount of $242,407.54 • Monthly report of ACH & Autopays – May 2021 6. Announcements/Correspondence. • Sanitary Sewer District #1 Commission – Wednesday, 6/16/21 at 6:30p.m., Town Hall • Lisbon Community Festival – Saturday, 6/19/21, 11:00a.m. – 4:00p.m., Community Park • Parks Committee – Monday, 6/21/21 at 6:30p.m., Richard Jung Fire Station • Town Board Meeting – Monday, 6/28/21 at 6:30 p.m. Town Hall • Plan Commission – Thursday, 7/1/21 at 6:30p.m., Richard Jung Fire Station 7. Administrator’s Report. 8. -
Beaver Dam Management
BMP Factsheet #8 BEAVER DAM MANAGEMENT Introduction corn, other herbaceous plants, and a variety of woody Beavers are North America’s largest rodent and perhaps plants. Beaver dams create habitat for many animals and are second only to humans in their ability to alter the plants and provide essential habitat for juvenile salmon, environment. Beaver dams can cause drainage problems particulary Coho. In winter, deer and elk frequent beaver on managed watercourses and impounded water can ponds to forage on shrubby plants that grow where cause property damage. beavers cut down trees for food or to use in making their dams and lodges. Weasels, raccoons, and herons Pursuant to RCW 77.55 a permit must be issued for hunt frogs and other prey along the marshy edges of work that will use, obstruct, change, or divert the bed beaver ponds. Migratory waterbirds use beaver ponds as or flow of state waters. To remove or modify a beaver nesting areas and resting stops during migration. Ducks dam on a natural or modified watercourse, you must and geese often nest on top of beaver lodges, since they have a Hydraulic Project Approval (HPA) issued by the offer warmth and protection, especially when lodges are Washington Department of Fish & Wildlife (WDFW). formed in the middle of a pond. The trees that die as a In emergency situations (when an immediate threat to result of rising water levels attract insects, which in turn property or life exists), verbal approval from WDFW may feed woodpeckers, whose holes later provide homes for be obtained for work necessary to solve the problem. -
Effects of Beaver Dams on Subarctic Wetland Runoff
EFFECTS OF BEAVER DAMS ON SUBARCTIC WETLAND RUNOFF BY JAMES MICHAEL WADDINGTON A Research Paper Submi tted to the Department of Geography i n Fulfilment of the Requirements of Geography 4C6 McMaster University March 1989 URBAN DOCUMENT CENTRE RESEARCH UNir " URBAN STUDIES M STER UNiVERSill HAI~ILTON, ONTARIO ABSTRACT Beaver ams located on streams of a western James Bay marsh were stu ied to determine their effects on the runoff from subarctic wetlands. A survey of the location, type, class, and geometry of 50 dams on five different creeks were related to streamflow hydrographs from the 1987 field season. The hydrographs showed that although gapflow and overflow type dams stored more water upstream during low flow, little alteration to s tormflow occurred except for the shedding of water to the s rrounding wetland. Throughflow type dams altered streamfl ow only at the local scale, while underflow type beaver dams, despite having little affect at low flow, created a 12 hour time lag and a long hydrograph recession during high flows. A water balance comparison was performed for the period June 18th to July 28th, 1988 between a basin without a beaver dam and one dammed by the beaver to determine the effects of the beaver dams at the basin scale. The amount of water stored in the beaver dam basin (18mm) was 53mm greater than that stored in the basin without a dam (-35mm) indicating (ii) a distinct diffe rence in the basins' abilities to store water. In both basi ns, net subsurface flow was negligible. Precipitation wa s similar in magnitude between the two basins. -
Montana Department of Natural Resources and Conservation
Montana Department of Natural Resources and Conservation ∼ Guidance for Landowners and Practitioners Engaged in Stream and Wetland Restoration Activities ∼ This document offers guidance for the development and implementation of wetland and stream restoration projects as they pertain to Montana water rights. These guidelines are not intended to offer official departmental policy nor do they serve as a substitute for administrative rules established through the rulemaking process. DNRC’s intention in the development of these guidelines is to provide an educational resource to the public and restoration practitioners involved in the work of stream and wetland restoration efforts. This document discusses restoration techniques in terms of whether or not they constitute a diversion, impoundment or withdrawal of a quantity of water for beneficial use, which is how the Montana Water Use Act defines an appropriation of water that requires a water right. This document only pertains to State of Montana water right issues and does not contemplate other aspects of private property rights or civil law. This document also does not contemplate permitting requirements in addition to those directly relating to Montana water rights, but other permitting information can be found here: http://dnrc.mt.gov/licenses-and-permits/stream-permitting DNRC strongly encourages individuals engaged in restoration work to contact their local DNRC Regional Office staff to obtain assistance regarding water rights questions for specific restoration projects: Billings: (406) 247-4415 Bozeman: (406) 586-3136 Glasgow: (406) 228-2561 Havre: (406) 265-5516 Helena: (406) 444-6999 Kalispell: (406) 752-2288 Lewistown: (406) 538-7459 Missoula: (406) 721-4284 Background: There is concern that inappropriately assuming a water right is required for wetland and stream restoration projects, including beavery mimicry, might limit ongoing ecological restoration efforts. -
2015 Beaver Dam Lake Scorecard Citizens Statewide Lake Assessment Program
2015 Beaver Dam Lake Scorecard Citizens Statewide Lake Assessment Program Introduction The Citizens Statewide Lake Assessment Program (CSLAP) is a volunteer lake monitoring and education program managed by DEC and the New York State Federation of Lake Associations (NYSFOLA). Lake information from a variety of sources, including CSLAP volunteers, is combined to create a scorecard for each CSLAP lake. The purpose of the scorecard is to provide a quick and simple summary of sampling results for: • water quality conditions • biological health • lake perception • lake uses The condition of each lake characteristic is represented by a color scale: Blue Green Yellow Red Black Best Worst No color indicates the condition is not known due to insufficient data. How information is turned into scores CSLAP volunteers collect valuable lake water quality data using accepted scientific methods to evaluate nutrient enrichment, aquatic weed and algae growth, general lake conditions, and the recreational quality of a lake. Water quality data is grouped and assigned scores related to the “health” (good or poor) of the lake. The scoring system is based on water quality standards, scientific principles and statistical analysis. Tips for interpreting scorecard information Each section of the scorecard includes a table identifying and describing lake characteristics and generally explains what they tell us about the lake’s health. This table can be used to help interpret scorecard results. Limitations of the information Water quality assessments and summaries of lake perception provided in this scorecard are based on information collected by CSLAP, and could be different from assessments and summaries based on information collected by other sources.