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Chapter 11. Water Resources Element
Humboldt County General Plan Planning Commission Approved Draft Chapter 11. Water Resources Element 11.1 Purpose This Element addresses water planning issues including river and stream water quality, stormwater runoff, groundwater management, water needs of fish and wildlife, water consumption, conservation and re-use methods, and state and federal regulations. 11.2 Relationship to Other Elements These and other water-related topics can be found throughout the General Plan. Water availability for development is addressed in the Land Use Element. The Conservation and Open Space elements address riparian corridors, wetlands, wildlife protection, fishery resources, other biotic resources, water-oriented recreation, and soil erosion. The Community Infrastructure and Services Element addresses public water and wastewater systems. 11.3 Background Surface and Groundwater Abundant water resources Large rivers and biologically rich watersheds are defining characteristics of Humboldt County. These resources provide local water supply, spawning habitat for fisheries, recreation opportunities, and local wealth for the fishing and tourism industries. The Eel, Trinity, and Klamath rivers extend well beyond county borders linking Humboldt to the complex regional, state, and interstate water resource and habitat management issues affecting their respective watersheds. The average annual runoff of the rivers running through the county reflects almost 30% of the state’s total runoff. Significant sections of these rivers and the Van Duzen River have been designated by the California legislature as wild, scenic, or recreational under the California Wild and Scenic River System. North Coast watersheds retain some of the last viable salmon and steelhead populations in the state and are a focal point for regional, state, federal, and tribal habitat recovery efforts. -
Horseshoe Bend Trail Rails & Trails Made Upofdeepsandand Es
Code: GC3QN7Z Rails & Trails Written and Researched by Wayne Robinson Horseshoe Bend Trail Site Identification Nearest Community: Lillooet, B.C. Geocache Location: N 50°51.608' W 122°09.318' Ownership: Crown Land Accuracy: 4 meters Photo: Wayne Robinson Overall Difficulty: 2.5 Overall Terrain: 3 The Horseshoe Bend is located on Highway 40, along the Bridge River just south of the confluence of the Bridge Access Information and and Yalakom Rivers. This is an interesting feature marked Restrictions: by a dramatic bend within the river. The canyon walls From the Mile 0 Cairn go north 2 km and turn left on Hwy 40 and follow for are laced with hoodoos and made up of deep sand and 28 km approximately to Horseshoe Bend gravel deposits left behind by retreating glaciers. At pull off. Do not drive down old road. first glance the Horseshoe Bend looks to be a marvel of Beware of cliff edge. Watch for falling geological forces, but it is a human made feature. This rock. Caution if with children and pets. Do not walk on upper rim of Horseshoe feature is sometimes called Horseshoe Wash; this helps Bend. describe the way in which the feature was created, through hydraulic mining for gold. It is amazing that this is a mine. Parking Advice: Operations began here in the 1908 and continued off and Between trees off the road at a natural on until relatively recent times. Between 1908 and 1914 view point. over a million dollars’ worth of gold was extracted from this area (using the historic gold value of $32 per ounce). -
Water Situation in China – Crisis Or Business As Usual?
Water Situation In China – Crisis Or Business As Usual? Elaine Leong Master Thesis LIU-IEI-TEK-A--13/01600—SE Department of Management and Engineering Sub-department 1 Water Situation In China – Crisis Or Business As Usual? Elaine Leong Supervisor at LiU: Niclas Svensson Examiner at LiU: Niclas Svensson Supervisor at Shell Global Solutions: Gert-Jan Kramer Master Thesis LIU-IEI-TEK-A--13/01600—SE Department of Management and Engineering Sub-department 2 This page is left blank with purpose 3 Summary Several studies indicates China is experiencing a water crisis, were several regions are suffering of severe water scarcity and rivers are heavily polluted. On the other hand, water is used inefficiently and wastefully: water use efficiency in the agriculture sector is only 40% and within industry, only 40% of the industrial wastewater is recycled. However, based on statistical data, China’s total water resources is ranked sixth in the world, based on its water resources and yet, Yellow River and Hai River dries up in its estuary every year. In some regions, the water situation is exacerbated by the fact that rivers’ water is heavily polluted with a large amount of untreated wastewater, discharged into the rivers and deteriorating the water quality. Several regions’ groundwater is overexploited due to human activities demand, which is not met by local. Some provinces have over withdrawn groundwater, which has caused ground subsidence and increased soil salinity. So what is the situation in China? Is there a water crisis, and if so, what are the causes? This report is a review of several global water scarcity assessment methods and summarizes the findings of the results of China’s water resources to get a better understanding about the water situation. -
Water Resources Compared
Water Resources Overview The goals of the Water Resources Chapter are listed below: - Protect the water supply from pollution and encroachment of developments. - Provide an adequate and safe drinking water supply to serve the existing and future residents of the City of Frederick. - Provide an adequate capacity of wastewater treatment with effluent meeting all necessary regulatory requirements for existing and future residents of the City. - Restore and protect water quality and contribute toward meeting the water qualityby striving to meet or exceed regulatory requirements. for water quality. This will require addressinginclude current water quality impacts as well as future impacts from land development and population growth. - Develop adequate stormwater management. - Protect the habitat value of the local and regional rivers and streams. - Efficiently use public dollars for infrastructure that ensures sustainable, safe, and adequate supply of water for all residents. The City is committed to ensuring water and wastewater (sewer) capacity for both existing and new developments andwhile minimizing the negative impacts of stormwater runoff. In 2002, the City established the Water and Sewer Allocation System to make certain that adequate treatment capacity for potable water and wastewater is in place for new growth prior to approval. In 2012, Ordinance G-12-13 was adopted which updated the allocation process and combined it with it the Impact Fees payable for water and sewer service. The City adopted an Adequate Public Facilities Ordinance (APFO) in 2007 that allows development to proceed only after it has been demonstrated that sufficient infrastructure exists or will be created in the water and wastewater systems. -
BRGMON-1 | Lower Bridge River Aquatic Monitoring
Bridge River Project Water Use Plan Lower Bridge River Aquatic Monitoring Implementation Year 6 Reference: BRGMON-1 BRGMON-1 Lower Bridge River Aquatic Monitoring, Year 6 (2017) Results Study Period: April 1 2017 to March 31 2018 Jeff Sneep Chris Perrin, Shauna Bennett, and Jennifer Harding, Limnotek Josh Korman, Ecometric Research Field Studies and Data Collection Completed by: Alyson McHugh, Danny O’Farrell, and Elijah Michel, Coldstream Ecology Ltd. November 7, 2018 BRGMON-1 Lower Bridge River Aquatic Monitoring, Year 6 (2017) Results Report Prepared for: St’at’imc Eco-Resources Report Prepared by: Jeff Sneep Chris Perrin, Shauna Bennett & Jennifer Harding, Limnotek, and Josh Korman, Ecometric Research Field Studies and Data Collection Completed by: Alyson McHugh, Danny O’Farrell & Elijah Michel, Coldstream Ecology Ltd. File no. BRGMON-1 April 2018 Lower Bridge River Aquatic Monitoring Year 6 (2017) Executive Summary A second year of high flow monitoring was conducted in 2017. The peak flow release from Terzaghi Dam was 127 m3∙s-1 and average flows for the year were 19 m3∙s-1. The high flow period began in the third week of May, peaked across the month of June, and was ramped back down by the third week of July (high flow duration = 59 days). Outside of the high flow period, the flow releases conformed to the Trial 2 hydrograph from the Lower Bridge River (LBR) flow experiment. Increases in the maximum Terzaghi Dam discharge were expected to have impacts on the aquatic ecosystem in the LBR. In both the short- and long-term, high flows were anticipated to affect periphyton accrual and biomass, benthic invertebrate abundance and diversity, and juvenile salmonid growth and abundance, related to disturbance and changes in habitat suitability associated with the high flows. -
A Thesis Submitted to the Department of Environmental Sciences And
A thesis submitted to the Department of Environmental Sciences and Policy of Central European University in part fulfilment of the Degree of Master of Science AN ANALYSIS ON SYNERGIC EFFORTS ON ENVIRONMENTAL SUSTAINABILITY AND POVERTY ALLEVIATION TOWARDS ACHIEVING MILLENNIUM DEVELOPMENT GOALS IN NEPAL CEU eTD Collection arjun DHAKAL July, 2007 Budapest Notes on copyright and the ownership of intellectual property rights: (1) Copyright in text of this thesis rests with the Author. Copies (by any process) either in full, or of extracts, may be made only in accordance with instructions given by the Author and lodged in the Central European University Library. Details may be obtained from the Librarian. This page must form part of any such copies made. Further copies (by any process) of copies made in accordance with such instructions may not be made without the permission (in writing) of the Author. (2) The ownership of any intellectual property rights which may be described in this thesis is vested in the Central European University, subject to any prior agreement to the contrary, and may not be made available for use by third parties without the written permission of the University, which will prescribe the terms and conditions of any such agreement. (3) For bibliographic and reference purposes this thesis should be referred to as: Dhakal, A. 2007. An analysis on synergic efforts on environmental sustainability and poverty alleviation towards achieving Millennium Development Goals in Nepal. Master of Science thesis, Department of Environmental Sciences and Policy, Central European University, Budapest. Further information on the conditions under which disclosures and exploitation may take place is available from the Head of the Department of Environmental Sciences and Policy, Central European University. -
Community Risk Assessment
COMMUNITY RISK ASSESSMENT Squamish-Lillooet Regional District Abstract This Community Risk Assessment is a component of the SLRD Comprehensive Emergency Management Plan. A Community Risk Assessment is the foundation for any local authority emergency management program. It informs risk reduction strategies, emergency response and recovery plans, and other elements of the SLRD emergency program. Evaluating risks is a requirement mandated by the Local Authority Emergency Management Regulation. Section 2(1) of this regulation requires local authorities to prepare emergency plans that reflects their assessment of the relative risk of occurrence, and the potential impact, of emergencies or disasters on people and property. SLRD Emergency Program [email protected] Version: 1.0 Published: January, 2021 SLRD Community Risk Assessment SLRD Emergency Management Program Executive Summary This Community Risk Assessment (CRA) is a component of the Squamish-Lillooet Regional District (SLRD) Comprehensive Emergency Management Plan and presents a survey and analysis of known hazards, risks and related community vulnerabilities in the SLRD. The purpose of a CRA is to: • Consider all known hazards that may trigger a risk event and impact communities of the SLRD; • Identify what would trigger a risk event to occur; and • Determine what the potential impact would be if the risk event did occur. The results of the CRA inform risk reduction strategies, emergency response and recovery plans, and other elements of the SLRD emergency program. Evaluating risks is a requirement mandated by the Local Authority Emergency Management Regulation. Section 2(1) of this regulation requires local authorities to prepare emergency plans that reflect their assessment of the relative risk of occurrence, and the potential impact, of emergencies or disasters on people and property. -
Without Land, There Is No Life: Chinese State Suppression of Uyghur Environmental Activism
Without land, there is no life: Chinese state suppression of Uyghur environmental activism Table of Contents Summary ..............................................................................................................................2 Cultural Significance of the Environment and Environmentalism ......................................5 Nuclear Testing: Suppression of Uyghur Activism ...........................................................15 Pollution and Ecological Destruction in East Turkestan ...................................................30 Lack of Participation in Decision Making: Development and Displacement ....................45 Legal Instruments...............................................................................................................61 Recommendations ..............................................................................................................66 Acknowledgements ............................................................................................................69 Endnotes .............................................................................................................................70 Cover image: Dead toghrak (populus nigra) tree in Niya. Photo courtesy of Flickr 1 Summary The intimate connection between the Uyghur people and the land of East Turkestan is celebrated in songs and poetry written and performed in the Uyghur language. Proverbs in Uyghur convey how the Uyghur culture is tied to reverence of the land and that an individual’s identity is inseparable -
Ecosystem Service Assessment of the Ili Delta, Kazakhstan Niels Thevs
Ecosystem service assessment of the Ili Delta, Kazakhstan Niels Thevs, Volker Beckmann, Sabir Nurtazin, Ruslan Salmuzauli, Azim Baibaysov, Altyn Akimalieva, Elisabeth A. A. Baranoeski, Thea L. Schäpe, Helena Röttgers, Nikita Tychkov 1. Territorial and geographical location Ili Delta, Kazakhstan Almatinskaya Oblast (province), Bakanas Rayon (county) The Ili Delta is part of the Ramsar Site Ile River Delta and South Lake Balkhash Ramsar Site 2. Natural and geographic data Basic geographical data: location between 45° N and 46° N as well as 74° E and 75.5° E. Fig. 1: Map of the Ili-Balkhash Basin (Imentai et al., 2015). Natural areas: The Ramsar Site Ile River Delta and South Lake Balkhash Ramsar Site comprises wetlands and meadow vegetation (the modern delta), ancient river terraces that now harbour Saxaul and Tamarx shrub vegetation, and the southern coast line of the western part of Lake Balkhash. Most ecosystem services can be attributed to the wetlands and meadow vegetation. Therefore, this study focusses on the modern delta with its wetlands and meadows. During this study, a land cover map was created through classification of Rapid Eye Satellite images from the year 2014. The land cover classes relevant for this study were: water bodies in the delta, dense reed (total vegetation more than 70%), and open reed and shrub vegetation (vegetation cover of reed 20- 70% and vegetation cover of shrubs and trees more than 70%). The land cover class dense reed was further split into submerged dense reed and non-submerged dense reed by applying a threshold to the short wave infrared channel of a Landsat satellite image from 4 April 2015. -
Policy Brief POLICY BRIEF February 2018
TERI Policy Brief POLICY BRIEF FEBRUARY 2018 The Energy and Resources Institute Measures to Control Air Pollution in Urban Centres of India: Policy and Institutional framework Background and Objective Many Indian cities including New Delhi are included in the list of most polluted cities in the world (WHO 2014, Cheng et al. 2016). About 80 per cent of cities in India violate the prescribed standards of ambient air CONTENTS quality (CPCB 2014). Multiple sources contribute to the problem and, hence, sector-specific strategies are required for control of air quality. • Background and Objective 1 This policy brief aims to analyse the whole issue in terms of key drivers, • Drivers of Air Pollution 1 such as rapid urbanization, transportation, industrialization, power • Growth of Pollutant Emissions in generation, and agricultural activities, that subsequently lead to air India 2 pollution at different scales in India. These drivers lead to generation • Impacts of Air Pollution in India 2 of pressures on the air quality through release of pollutants. The brief • Urban Air Pollution Source assesses the contribution of different sources of emission and pollutant Apportionment Studies 4 concentrations at urban and national scales and the impact on human • Strategies for Control of Air health and other important receptors and discusses the key measures Pollution in Urban Centres 4 required for improvement of air quality in urban centres of India. • Conclusions 18 Drivers of Air Pollution Authors Urbanization, transportation, industrialization, power generation, and Sumit Sharma, Fellow agricultural activities are the key drivers that lead to air pollution through Jai Malik, Research Associate release of emissions. -
Pangani Basin: a Situation Analysis
Pangani Basin: A Situation Analysis IUCN Eastern Africa Programme 2003 i Published by: Copyright: © 2003 International Union for Conservation of Nature and Natural Resources This publication may be produced in whole or part and in any form for education or non-profit uses, without special permission from the copyright holder, provided acknowledgement of the source is made. IUCN would appreciate receiving a copy of any publication which uses this publication as a source. No use of this publication may be made for resale or other commercial purpose without the prior written permission of IUCN. Citation: IUCN Eastern Africa Programme, 2003. The Pangani River Basin: A Situation Analysis, xvi + 104pp. ISBN: 2-8317-0760-9 Design and layout: Gordon O. Arara Printed by: ScanHouse Press Ltd. Photo 1: The summit of Mount Kilimanjaro; Photo 2: Forest stand at 1 Shire Njoro; Photo 3: Gate controlling the release of water into irrigation furrows; Photo 4: Children swimming in an irrigation 3 4 reservoir; Photo 5: Sisal plantations; Photo 6: Irrigated rice scheme; 2 Photo 7: Water gauging station at Chemka Spring; Photo 8: Vandalized gate controlling the release of water into irrigation furrows; Photo 9: 5 Dam wall at Nyumba ya Mungu Reservoir (color changes mark the declining water levels); Photo 10: A vendor sells water from a borehole 6 9 10 Photos 1, 3, 5, 6, 8, 9 copyright 2003 Kelly West; Photos 2, 7 7 8 copyright 2002 Kim Geheb; Photos 4, 10 copyright 2003 Ger Bergkamp. Available from: IUCN- EARO Publications Service Unit, P. O. Box 68200 - 00200, Nairobi, Kenya; Telephone ++ 254 20 890605-12; Fax ++ 254 20 890615; E-mail: [email protected] The designations of geographical entities in this book, and the presentation of the material, do not imply the expression of any opinion whatsoever on the part of the participating organiza- tions concerning the legal status of any country, territory, or area, or of its authorities, or con- cerning the delimitation of its frontiers or boundaries. -
The Framework on Eco-Efficient Water Infrastructure Development in China
KICT-UNESCAP Eco-Efficient Water Infrastructure Project The Framework on Eco-efficient Water Infrastructure Development in China (Final-Report) General Institute of Water Resources and Hydropower Planning and Design, Ministry of Water Resources, China December 2009 Contents 1. WATER RESOURCES AND WATER INFRASTRUCTURE PRESENT SITUATION AND ITS DEVELOPMENT IN CHINA ............................................................................................................................. 1 1.1 CHARACTERISTICS OF WATER RESOURCES....................................................................................................... 6 1.2 WATER USE ISSUES IN CHINA .......................................................................................................................... 7 1.3 FOUR WATER RESOURCES ISSUES FACED BY CHINA .......................................................................................... 8 1.4 CHINA’S PRACTICE IN WATER RESOURCES MANAGEMENT................................................................................10 1.4.1 Philosophy change of water resources management...............................................................................10 1.4.2 Water resources management system .....................................................................................................12 1.4.3 Environmental management system for water infrastructure construction ..............................................13 1.4.4 System of water-draw and utilization assessment ...................................................................................13