An Autoethnographic Investigation of Chernobyl As a Dark Heritage Site by Nicholas Hryhorczuk Dissertation
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GHOST GEAR: the ABANDONED FISHING NETS HAUNTING OUR OCEANS Sea Turtle Entangled in Fishing Gear in the Mediterranean Sea © Marco Care/Greenpeace CONTENTS
GHOST GEAR: THE ABANDONED FISHING NETS HAUNTING OUR OCEANS Sea turtle entangled in fishing gear in the Mediterranean Sea © Marco Care/Greenpeace CONTENTS 4 Zusammenfassung 5 Executive summary 6 Introduction 8 Main types of fishing – Nets – Lines – Traps & pots – FADs 11 Ghost gear impacts – Killing ocean creatures – Damaging habitats – Economic and other impacts 13 Current regulations – International agreements and recommendations – Other programmes and resolutions – A cross-sector approach – The need for a Global Ocean Treaty 16 References 2019 / 10 Published by Greenpeace Germany November 2019 Stand Greenpeace e. V., Hongkongstraße 10, 20457 Hamburg, Tel. 040/3 06 18 - 0, [email protected] , www . greenpeace . de Authors Karli Thomas, Dr. Cat Dorey and Farah Obaidullah Responsible for content Helena Spiritus Layout Klasse 3b, Hamburg S 0264 1 Contents 3 DEUTSCHE ZUSAMMENFASSUNG DER STUDIE GHOST GEAR: THE ABANDONED FISHING NETS HAUNTING OUR OCEANS → Rund 640.000 Tonnen altes Fischereigerät inklusive Geisternetzen, Bojen, Leinen, Fallen und Körbe landen jährlich als Fischereimüll in den Ozeanen. → Weltweit trägt altes Fischereigerät zu etwa zehn Prozent zum Plastikeintrag in die Meere bei. → 45 Prozent aller Arten auf der Roten IUCN-Liste hatten bereits Kontakt mit Plastik im Meer. → Sechs Prozent aller eingesetzten Netze, neun Prozent aller Fallen und 29 Prozent aller Langleinen gehen jährlich auf den Ozeanen verloren und enden als Meeresmüll. → Treibnetze, Fallen und Fischsammler (Fish Aggregating Devices, FADs) gehen weltweit am häufigsten als Müll auf den Ozeanen verloren und bergen die meisten Risiken für Meereslebewesen. → Durch FADs sterben 2,8 bis 6,7 Mal mehr Tiere - darunter bedrohte Arten wie Haie – als Beifang als die Zielarten, für die sie eingesetzt werden. -
Municipal Solid Waste Landfill Operation and Management Workbook
MUNICIPAL SOLID WASTE LANDFILL OPERATION AND MANAGEMENT WORKBOOK Revised April 2018 Preface In many ways, constructing, operating and maintaining a municipal solid waste landfill is similar to constructing, operating, and maintaining a highway, dam, canal, bridge, or other engineered structure. The most important similarity is that landfills, like other engineered structures, must be constructed and operated in a manner that will provide safe, long-term, and reliable service to the communities they serve. Proper design, construction, operation, monitoring, closure and post-closure care are critical because after disposal the waste can be a threat to human health and the environment for decades to centuries. This workbook is intended to provide municipal landfill operators and managers in Wyoming with the fundamental knowledge and technical background necessary to ensure that landfills are operated efficiently, effectively, and in a manner that is protective of human health and the environment. This workbook contains information regarding basic construction and operation activities that are encountered on a routine basis at most landfills. The basic procedures and fundamental elements of landfill permitting, construction management, monitoring, closure, post-closure care, and financial assurance are also addressed. The workbook includes informative tips and information that landfill operators and managers can use to conserve landfill space, minimize the potential for pollution, reduce operating costs, and comply with applicable rules and regulations. In addition to this workbook, operators and managers need to become familiar with the Wyoming Solid Waste Rules and Regulations applicable to municipal solid waste. The DEQ also provides numerous guidelines that may help understand regulatory requirements in more detail. -
Urbanization As a Threat to Biodiversity: Trophic Theory, Economic Geography, and Implications for Conservation Land Acquisition
Proceedings of a Symposium at the Society for Conservation Biology 2004 Annual Meeting URBANIZATION AS A THREAT TO BIODIVERSITY: TROPHIC THEORY, ECONOMIC GEOGRAPHY, AND IMPLICATIONS FOR CONSERVATION LAND ACQUISITION Brian Czech1 ABSTRACT—Habitat loss is often cited as the primary cause of species endangerment in the United States, followed by invasive species, pollution, and direct take. Urbanization, one type of habitat loss, is the leading cause of species endangerment in the contiguous United States and entails a relatively thorough transformation from the “economy of nature” to the human economy. Principles of economic geography indicate that urbanization will continue as a function of economic growth, while principles of conservation biology indicate that the most thorough competitive exclusion occurs in urban areas. These findings suggest the need for an ecologically macroeconomic approach to conservation land acquisition strategies. “Habitat loss” is often cited as the primary cause of species these types of habitat loss are considered separate causes of endangerment in the United States, followed by invasive species endangerment, invasive species are identified as the species, pollution, disease, and direct take. However, vari- leading cause of species endangerment in the United States, ous types of habitat loss are readily identified, such as log- including Hawaii and Puerto Rico (Czech et al. 2000). On ging, mining, agriculture, and urbanization (table 1). When the mainland United States, however, urbanization is the Table 1.— Causes of endangerment for the first 877 (of the current 1,262) species in the United States and Puerto Rico classified as threatened or endangered by the United States Fish and Wildlife Service (from Czech et al. -
Toxic Tide: the Threat of Marine Plastic Pollution in Australia
The Senate Environment and Communications References Committee Toxic tide: the threat of marine plastic pollution in Australia April 2016 © Commonwealth of Australia 2016 ISBN 978-1-76010-400-9 Committee contact details PO Box 6100 Parliament House Canberra ACT 2600 Tel: 02 6277 3526 Fax: 02 6277 5818 Email: [email protected] Internet: www.aph.gov.au/senate_ec This work is licensed under the Creative Commons Attribution-NonCommercial-NoDerivs 3.0 Australia License. The details of this licence are available on the Creative Commons website: http://creativecommons.org/licenses/by-nc-nd/3.0/au/. This document was printed by the Senate Printing Unit, Parliament House, Canberra Committee membership Committee members Senator Anne Urquhart, Chair ALP, TAS Senator Linda Reynolds CSC, Deputy Chair (from 12 October 2015) LP, WA Senator Anne McEwen (from 18 April 2016) ALP, WA Senator Chris Back (from 12 October 2015) LP, WA Senator the Hon Lisa Singh ALP, TAS Senator Larissa Waters AG, QLD Substitute member for this inquiry Senator Peter Whish-Wilson (AG, TAS) for Senator Larissa Waters (AG, QLD) Former members Senator the Hon Anne Ruston, Deputy Chair (to 12 October 2015) LP, SA Senator the Hon James McGrath (to 12 October 2015) LP, QLD Senator Joe Bullock (to 13 April 2016) ALP, WA Committee secretariat Ms Christine McDonald, Committee Secretary Mr Colby Hannan, Principal Research Officer Ms Fattimah Imtoual, Senior Research Officer Ms Kirsty Cattanach, Research Officer iii iv Table of Contents List of recommendations ..................................................................................vii List of abbreviations ....................................................................................... xiii Chapter 1: Introduction ..................................................................................... 1 Conduct of the inquiry ............................................................................................ 1 Acknowledgement ................................................................................................. -
Rates of Particulate Pollution Deposition Onto Leaf Surfaces: Temporal and Inter-Species Magnetic Analyses
ARTICLE IN PRESS Environmental Pollution xxx (2010) 1–7 Contents lists available at ScienceDirect Environmental Pollution journal homepage: www.elsevier.com/locate/envpol Rates of particulate pollution deposition onto leaf surfaces: Temporal and inter-species magnetic analyses R. Mitchell a,*, B.A. Maher a, R. Kinnersley b a Centre for Environmental Magnetism and Palaeomagnetism, Lancaster Environment Centre, University of Lancaster, Lancaster LA1 4YQ, UK b Evidence Directorate, Environment Agency, Olton Court, 10 Warwick Road, Olton, Solihull B92 7HX, UK This research uses biomagnetic techniques to enable quantitative mapping of particulate pollution distribution at uniquely high spatial resolution. article info abstract Article history: Evaluation of health impacts arising from inhalation of pollutant particles <10 mm (PM10) is an active Received 1 September 2009 research area. However, lack of exposure data at high spatial resolution impedes identification of Received in revised form causal associations between exposure and illness. Biomagnetic monitoring of PM10 deposited on tree 11 December 2009 leaves may provide a means of obtaining exposure data at high spatial resolution. To calculate ambient Accepted 16 December 2009 PM10 concentrations from leaf magnetic values, the relationship between the magnetic signal and total PM10 mass must be quantified, and the exposure time (via magnetic deposition velocity (MVd) Keywords: calculations) known. Birches display higher MV (w5cmÀ1) than lime trees (w2cmÀ1). Leaf saturation Magnetic biomonitoring d w Deposition velocity remanence values reached ‘equilibrium’ with ambient PM10 concentrations after 6 ‘dry’ days (<3 mm/day rainfall). Other co-located species displayed within-species consistency in MV ; robust PM10 monitoring d Tree leaves inter-calibration can thus be achieved, enabling magnetic PM10 biomonitoring at unprecedented spatial Inter-species calibration resolution. -
Standard Procedures for Establishing and Evaluating Air Pollution Biomonitoring Gardens in National Park Units
DRAFT STANDARD PROCEDURES FOR ESTABLISHING AND EVALUATING AIR POLLUTION BIOMONITORING GARDENS IN NATIONAL PARK UNITS National Park Service Air Quality Division P.O. Box 25287 Denver, CO 80225 Contacts: Kenneth W. Stolte James P. Bennett Tel: 303-236-8770 FTS: 776-8770 August, 1985 2 BIOMONITORING GARDENS Introduction The Air Quality Division of the National Park Service has been actively researching the extent and severity of air pollution injury in park units since 1979. Air quality studies conducted in 1984 revealed that plant species in many park units were injured by air pollution, primarily O3 and S02« The large area that many park units comprise makes it difficult and expensive to frequently evaluate biomonitoring plots scattered throughout the parks. Additionally, only a small percentage of each park flora has been experimen tally tested for air pollution sensitivity. Consequently the air pollution sensitivity of most of each park flora is relatively unknown. Bioindicator species of known or suspected pollutant sensitivity should be co-located with ambient air quality monitoring stations so that the pollutant response of the indicator species can be correlated with ambient pollution concentrations. A planting of air pollutant sensitive species in a common area, preferably near an ambient pollutant monitoring station, is termed a biomonitoring garden. Biomonitoring gardens can be established to: (1) relate ambient pollution levels with visible injury thresholds for species of known pollutant sensi tivity; (2) serve as a convenient, easily accessible grouping of native park species of known or suspected air pollution sensitivity; (3) provide a habitat where colonizing native species can be ranked for sensitivity to ambient air pollution. -
Crime Prevention That Works: Documentation C: the Care of Public Transport in ='----Centre the Netherlands
If you have issues viewing or accessing this file contact us at NCJRS.gov. ... Henk van Andel I~ research and I) Crime prevention that works: documentation c: the care of public transport in ='----centre the Netherlands . N ·1/88 / ((o/$. 2- Henk van Andel I~ research and [) Crime prevention that works: documentation (: the care of public transport in centre the N,etherlands 116152 U.S. Department of Justice National Institute 01 Justice This document has been reproduced exactly as received from the person or organizalion originating it. Points of view or opinions sta/Ad in Ihis documenl are those of the authors and do no! neces:;arily represent the official position or policies of the National ittsiitute of Justice. Permission to reproduce Ihis copyrighted malerial has been granted by ~inistry of Justice The NETHERLAND~S~ __________ Ministry of Justice to the National Criminal Justice Reference Service (NCJRS). Netherlands 1988 Further reproduction outside of the NCJRS system requires permis sion of the copyright owner. " 1/88 Contents Swnmary 1 Introduction 2 Description of the measures 2.1 SIC project 2.2 Change in boarding procedure on the bases 3 Design of the evaluation 4 Results 4.1 Fare-dodging tI f 4.2 Safety 4.3 Vandalism 4.4 Information 4.5 What the changes mean to passengers and staff 5 Evaluation 5.1 Deployment of SIC's 5.2 Financial costs and benefits of the SIC project 5.3 Financial costs and benefits of the new boarding procedure on the buses 5.4 Social benefits 6 Discussion ~ Notes \ References (, 1 Summary An experiment has been carried out in the Dutch public transport system to tackle fare-dodging, vandalism and aggression. -
Municipality
TheMunicipality Your Voice Your Wisconsin. December | 2020 GARBAGE Wisconsin Municipalities Wisconsin’s Solid Garbage Collection DNR Update on Can Provide High-Speed Trees Support Enforcing Seasonal Waste Management and Recycling Recycling Internet — Some Mental Health “This Is Not My Weight Limitation History – A Timeline FAQs in Wisconsin Already Have… During COVID-19 Beautiful House…” Ordinances 4 8 9The Municipality13 | December 202017 20 23 1 CYBER LIABILITY? DON’T WORRY, YOU’RE COVERED. Insured by LWMMI? You are automatically covered to Policy Limits with no deductible - including the investigation on how the breach occurred, notifi cation to people affected and defense of potential claims. If your municipality is not insured by the LWMMI you may be “phishing” for trouble and left to “phlounder” on your own. With LWMMI Insurance you have the peace of mind to run your City or Village the way you want to and Don’t Worry, You’re Covered! Protecting The Communities We Live In. 608.833.9595 | www.LWMMI.org A Mutual Company Owned by Member Cities and Villages. TheMunicipality The Municipality Official Monthly Publication of the League of Wisconsin Municipalities Volume 115, No 12, December 2020 December | 2020 Editorial Offices 131 W. Wilson St., Suite 505, Madison, WI 53703 Dial (608) 267-2380 Feature Fax: (608) 267-0645 e-mail: [email protected] Website: www.lwm-info.org Wisconsin’s Solid Waste DNR Update Voters Approve Your Turn Management History – on Recycling Municipal Levy Limit The Municipality serves as the medium of exchange of ideas and information on municipal A Timeline in Wisconsin Referendums affairs for the officials of Wisconsin cities and villages. -
Land Use Changes: Economic, Social, and Environmental Impacts Junjie Wu
Land Use Changes: Economic, Social, and Environmental Impacts JunJie Wu JEL Classifications.' Q24, Q28 Major land-use changes have occurred in the United Land use change, however, does not come without States during the past 25 years. The total area of cropland, costs (see Table 1).Conversion of farmland and forests to pastureland and rangeland decreased by 76 million acres urban development reduces the amount of lands available in the lower 48 states from 1982 to 2003, while the to- for food and timber production. Soil erosion, salinization, tal area of developed land increased by 36 million acres or desertification, and other soil degradations associated with 48%. What are the potential economic, social, and envi- intensive agriculture and deforestation reduce the qual- ronmental impacts ofland use changes? How does land use ity of land resources and future agricultural productivity change affect agriculture and rural communities? What are (Lubowski et al. 2006). the important economic and environmental implications Urbanization presents many challenges for farmers for commodity production and trade, water and soil con- on the urban fringe. Conflicts with nonfarm neighbors servation, open space preservation, and other policy issues? and vandalism, such as destruction of crops and damage This article addresses some of these issues and their policy to farm equipment, are major concerns of farmers at the implications. urban fringe (Lisansky, 1986). Neighboring farmers of- Socioeconomic Impacts ten cooperate in production activities, including equip- ment sharing, land renting, custom work, and irrigation Land is one of three major factors of production in classical system development. These benefits will disappear when economics (along with labor and capital) and an essential neighboring farms are converted to development. -
Modelling Radiocaesium Fluxes in Forest Ecosystems
BY0000223 Modelling Radiocaesium Fluxes in Forest Ecosystems Results from the ECP-5 project conducted under the Agreement for International Collaboration on the Consequences of the Chernobyl Accident between the European Commission and the Ministries for Chernobyl Affairs in Belarus, Russia and Ukraine G. Shaw: Centre for Analytical Research in the Environment, Imperial College at Silwood Park, Ascot, Berkshire, SL5 7TE, United Kingdom A Kliashtorin, S. Mamikhin, A Shcheglov: Radioecology Laboratory, Soil Science Faculty, Moscow State University, Moscow, 119899 Russian Federation B. Rafferty: Radiological Protection Institute of Ireland, 3 Clonskeagh Square, Clonskeagh Road, Dublin 14, Ireland A. Dvornik, T. Zhuchenko: Byelorussian Research Institute of Forestry, Gomel, Belarus N. Kuchma: 'Pripyat' Research and Industrial Association, 1-a B. Khmelnitsky Street, Chernobyl, 255620 Ukraine Abstract: Monitoring of radiocaesium inventories and fluxes has been carried out in forest ecosystems in Ukraine, Belarus and Ireland to determine distributions and rates of migration. This information has been used to construct and calibrate mathematical models which are being used to predict the likely longevity of contamination of forests and forest products such as timber following the Chernobyl accident. 1. Introduction Little information on radionuclide migration processes within forest ecosystems existed before the Chernobyl accident. Yet in countries such as Belarus, where approximately 20% of the national forest cover is contaminated to levels in excess of 15 Ci km"2 (555 kBq m"2), the post-contamination management of forests is a highly important economic and social problem [1]. During the period 1992 - 1995 forest sites contaminated by the Chernobyl accident in Ukraine, Belarus and Ireland have been monitored by ECP-5 to determine the magnitudes of radionuclide fluxes (principally radiocaesium) between the major components of the forest ecosystems concerned. -
Support to Radioactive Waste Management in Ukraine Project U4.01/10 D
EC- UkraineContract International No.: NSI/2014/341 Nuclear Safety-739 Cooperation (INSC) Program Support to radioactive waste management in Ukraine Project U4.01/10 D Project D: Investigation of radioactive waste burial and temporary storage sites in the Chernobyl Exclusion Zone Project D Leader: Dr. Norbert Molitor, Plejades Project Director: Dr. Zoran Drace, Plejades Presentation by: Dmitri Bugai, IGS, Ukraine (national project expert) Ukraine-Japan Collaboration Workshop , Kiev, 30 January 2015 Overview of clean-up waste burial sites (RWTSP) Support to radioactive waste management in Ukraine 09 July 2014 (U4.01/10 C+D+F project) RWTSP - Radioactive Waste Temporary Storage Places 9 RWTSP Sites: • Neftebaza Kopachi Clamp example • Peschanoe Plato • Old/Staraya Stroybaza • New/Novaya Stroybaza • Chistogalovka • Kopachi • Pripyat • Red Forest Red Forest Trench example • Yanov Station In total (currently characterized) 470 trenches and clamps 884,000 m³ radwaste (~ 70% investigated of the tot.area of ~12km2) RWDS - Radioactive Waste Disposal Sites Engineered facilities: Podlesny • Podlesny • ChNPP 3rd Stage 3rd turn ChNPP • RWDS contain (potentially) HLW – LLW originating from Sarcophagus site (1986-87) • Inventory is highly uncertain • Waste storage conditions do not comply with safety requirements Chernobyl 3rd stage Radwaste Inventory data for ChEZ Aims of Project D Investigation of radioactive waste burial and temporary storage sites in the ChEZ: – Characterization of waste disposal sites using airborne geophysical techniques (location, -
The Competition Commission
CHERNOBYL – A NUCLEAR C ATASTROPHE 20 YEARS ON A REVIEW OF THE PRESENT SITUATION IN THE UKRAINE O REF N Q3143-A2 Client: GREENPEACE INTERNATIONAL 1ST ISSUE REVISION NO APPROVED CURRENT ISSUE DATE 21 DECEMBER 2 005 Q3143-A1-11 22 APRIL 2006 2 - 29 CHERNOBYL – A NUCLEAR CATASTROPHE 20 YEARS ON SUMMARY Twenty years ago the No 4 reactor of the Chernobyl nuclear power and excused on the basis that they, those receiving the higher dose station underwent catastrophic failure, spewing radioactivity into and risk, can choose to leave whenever they themselves wish to do the environment for 10 or so days. The radiological consequences so. applied throughout most of Europe, extending as far afield as Britain and Scandinavia. Locally, in the regions of the Ukraine, It might not be a full understanding to put this deadlock entirely Russian and Belarus, the radiological situation was very severe, in down to the almost symbiotic relationship that has developed fact so bad necessitating the immediate evacuation of ninety between those in the contaminated territories, who receive financial thousand or more population from towns and villages nearby the compensation, and the politicians who look towards this stricken Chernobyl nuclear power plant and, as time passed, whole compensated group as a block vote. Correcting this overdosing via settlements were evacuated, demolished and ploughed into the the food uptake path requires a greater degree of intervention ground, and more and more stringent controls over foodstuffs and management of the agricultural cycle and critical group habit. Put agricultural were imposed. simply, it requires additional resources costing relatively small sums of money to finance, perhaps no more that €10M per year for Today the town of Pripyat, once home to 50,000, remains deserted a few successive years.