Analysis of Effects of Pollution Due to Flooding

Total Page:16

File Type:pdf, Size:1020Kb

Analysis of Effects of Pollution Due to Flooding Integrated Flood Risk Analysis and Management Methodologies Analysis of effects of pollution due to flooding Date March 2007 Report Number T22-07-02 Revision Number 1_1_P01 Deliverable Number: D22.1 Actual submission date: March 2007 Task Leader UFZ FLOODsite is co-funded by the European Community Sixth Framework Programme for European Research and Technological Development (2002-2006) FLOODsite is an Integrated Project in the Global Change and Eco-systems Sub-Priority Start date March 2004, duration 5 Years Document Dissemination Level PU Public PU PP Restricted to other programme participants (including the Commission Services) RE Restricted to a group specified by the consortium (including the Commission Services) CO Confidential, only for members of the consortium (including the Commission Services) Co-ordinator: HR Wallingford, UK Project Contract No: GOCE-CT-2004-505420 Project website: www.floodsite.net Analysis pollution D22.1 Contract No:GOCE-CT-2004-505420 DOCUMENT INFORMATION Title Analysis of effects of pollution due to flooding Lead Author UFZ Contributors Distribution Public Document Reference T22-07-02 DOCUMENT HISTORY Date Revision Prepared by Organisation Approved by Notes 20/03/07 1_0 UFZ UFZ 22/05/09 1_1_P01 J Rance HR Wallingford ACKNOWLEDGEMENT The work described in this publication was supported by the European Community’s Sixth Framework Programme through the grant to the budget of the Integrated Project FLOODsite, Contract GOCE-CT- 2004-505420. DISCLAIMER This document reflects only the authors’ views and not those of the European Community. This work may rely on data from sources external to members of the FLOODsite project Consortium. Members of the Consortium do not accept liability for loss or damage suffered by any third party as a result of errors or inaccuracies in such data. The information in this document is provided “as is” and no guarantee or warranty is given that the information is fit for any particular purpose. The user thereof uses the information at its sole risk and neither the European Community nor any member of the FLOODsite Consortium is liable for any use that may be made of the information. © Members of the FLOODsite Consortium T22_07_02_Analysis_pollution_D22_1_V1_1_P01 22 May 2009 ii Analysis pollution D22.1 Contract No:GOCE-CT-2004-505420 SUMMARY In early 2000, two major mining-related accidents occurred in the Maramureş County in Romania which caused the release of large amounts of cyanide and heavy metals into the rivers Szamos and Tisza (a major tributary of the Danube). The high concentrations of cyanides killed almost immediately more than 1,000 t of fish on the Hungarian side. Cyanides pose a short-term threat to the environment due to their degradability. In contrast, heavy metals deposit in the river catchment area and can accumulate in the food web due to their lack of degradability, which results in a long-term threat to the ecosystem and to humans. To assess the contamination, sediments were sampled along Szamos and Tisza in Hungary from 2000 to 2005. The aqua-regia soluble element contents and the bonding forms of selected elements were analyzed in the grain size fraction < 20 µm. Heavy metal concentrations in sediments were initially high at the Szamos (≤ 3,000 mg/kg Zn) and decreased with increasing distance from the mining accident (ca. 500 µg/g Zn in the middle section of the Tisza). In 2005, the trace element concentrations in the Szamos have decreased to a level slightly higher than in the Tisza. The concentration decline is probably caused by dilution with “uncontaminated” sediment, transport of contaminated substrate further downriver as well as transport out off the river onto the floodplains. Most of the sediment profiles do not reflect the mining accidents of the year 2000, which indicates a long history of heavy metal contamination in the Tisza catchment. Cluster analysis discriminates three sections of the research area: (1) Szamos, (2) middle Tisza and (3) lower Tisza. This pattern is based on the contamination level ranking from high to low. Over the observed years the element pattern changed only marginally: (1) Cd–Pb–Zn, (2) As–Cu, (3) Cr and (4) Co–Ni. Although the decrease of the sedimentary heavy metal concentration gives a positive impression regarding the sediment quality, potential sinks of the contaminants should be determined. Therefore further research is needed to assess the effect on floodplains, because they are due to their agricultural use integrated in the human food web. T22_07_02_Analysis_pollution_D22_1_V1_1_P01 22 May 2009 iii Analysis pollution D22.1 Contract No:GOCE-CT-2004-505420 T22_07_02_Analysis_pollution_D22_1_V1_1_P01 22 May 2009 iv Analysis pollution D22.1 Contract No:GOCE-CT-2004-505420 CONTENTS Document Information ii Document History ii Acknowledgement ii Disclaimer ii Summary iii Contents v 1. Introduction ...................................................................................................................... 1 1.1 Motivation ........................................................................................................... 1 1.2 The accidents ....................................................................................................... 1 1.3 (Potential) Sources of pollution........................................................................... 1 2. Investigation area ............................................................................................................. 5 2.1 Tisza River........................................................................................................... 5 2.2 Overview of selected studies on the spills in 2000 in the investigation area....... 5 2.3 Szamos................................................................................................................. 6 2.4 Körös and Maros ................................................................................................. 6 3. Methods............................................................................................................................ 6 3.1 Sampling.............................................................................................................. 6 3.1.1 Sampling locations and conditions......................................................... 6 3.1.2 Sampling techniques (methods and depth)............................................. 8 3.2 Sample preparation and grain size fractionation.................................................. 9 3.3 Chemical analysis.............................................................................................. 10 3.3.1 Carbon analysis .................................................................................... 10 3.3.2 Aqua regia soluble element contents.................................................... 10 3.3.3 Sequential extraction............................................................................ 11 3.4 Data evaluation.................................................................................................. 12 4. Results ............................................................................................................................ 12 4.1 Sediment composition ....................................................................................... 12 4.2 Aqua regia soluble element content................................................................... 13 4.2.1 Comparison of aqua regia soluble element contents of the grain size fractions < 20 µm and < 1 mm............................................................. 13 4.2.2 Geogenic vs. anthropogenic proportions of the heavy metal load ....... 14 4.2.3 Temporal changes of the concentration of selected elements .............. 15 4.2.4 Comparison with legal values and guidelines for sediments and soils 30 4.3 Bonding form distributions of selected elements .............................................. 31 4.3.1 General remarks ................................................................................... 31 4.3.2 Major elements..................................................................................... 32 4.3.3 Trace elements ..................................................................................... 34 5. Discussion ......................................................................................................................41 5.1 t-Test.................................................................................................................. 41 5.2 Correlation analysis ........................................................................................... 41 5.3 Cluster analysis.................................................................................................. 45 5.3.1 Grouping of sampling locations based on As and selected heavy metals (Cd, Co, Cr, Cu, Ni, Pb, Zn) for each sampling campaign (< 20 µm; Z-score) ............................................................................... 45 5.3.2 Grouping of heavy metals (Cd, Co, Cr, Cu, Ni, Pb, Zn) and As for each year (< 20 µm; Z-score)............................................................... 46 5.4 Changes in heavy metal concentration .............................................................. 49 T22_07_02_Analysis_pollution_D22_1_V1_1_P01 22 May 2009 v Analysis pollution D22.1 Contract No:GOCE-CT-2004-505420 5.5 Changes in heavy metal bonding forms............................................................. 50 6. Conclusions ...................................................................................................................
Recommended publications
  • Mtntng ACTTVTTIES Tn the APUSENT MOUNTATNS, ROMANTA
    Geosciences in the 27't century. ENVIRONMENTAL PROBLEMS ASSOCIATED WITH THE MtNtNG ACTTVTTIES tN THE APUSENT MOUNTATNS, ROMANTA Elena-Luisa IATAN lnstitute of Geodynamics ,,Sabba S. $tefdnescu" of Romanian Academy, D-21 Jeon-Louis Calderon St, o2oo32 Buchorest, e-mail: [email protected] Mining is one of the oldest industries, and abandoned mines with the potential to release harmful substances into soil, water and air are found throughout Romanian territory. Due to the mining activity of ore deposits for more than 2000 years, in Romania there are over 550 tailings dumps, covering an area of approximately 800 ha and storing over 200 million cubic meters of tailings and 54 tailings ponds, which covers an area of almost 1350 ha and stores over 350 million m3 of waste. Mining activities create a potential impact on the environment, both during exploitation and in the years after mine closure. Underground exploitation presents the risk of collapsing galleries and surface overflowing and involves the dislocation of a large amount of rocks. Quarrying is one of the most common forms of mineral extraction, being particularly harmful to the environment, as strategic minerals are often available in low concentrations, which increases the amount of ore extracted. Althou8h mininB activities are currently stopped in most areas, the potential risk of environmental contamination exists due to the huge quantities of tailings in the tailings ponds and the tailinBs dumps very close to the watercourses. These are permanent sources of pollution for surface and groundwater, soil and air in the area (Fig. 1). The oxidation of sulphide minerals led to the removal of soluble metal ions from the mineralization found in mining related wastes under the effect of water.
    [Show full text]
  • International Conference of Territorial Intelligence, Alba Iulia 2006. Vol.1
    International Conference of Territorial Intelligence, Alba Iulia 2006. Vol.1, Papers on region, identity and sustainable development (deliverable 12 of caENTI, project funded under FP6 research program of the European Union), Aeternitas, Alba Iulia, 2007 Jean-Jacques Girardot, M. Pascaru, Ioan Ileana To cite this version: Jean-Jacques Girardot, M. Pascaru, Ioan Ileana. International Conference of Territorial Intelligence, Alba Iulia 2006. Vol.1, Papers on region, identity and sustainable development (deliverable 12 of caENTI, project funded under FP6 research program of the European Union), Aeternitas, Alba Iulia, 2007. 2007, 280 p. halshs-00531457 HAL Id: halshs-00531457 https://halshs.archives-ouvertes.fr/halshs-00531457 Submitted on 26 Jun 2014 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. International Conference of Territorial Intelligence of Alba Iulia 2006 (CAENTI) | http://www.territorial-intelligence.eu Jean-Jacques GIRARDOT Mihai PASCARU Ioan ILEANĂ Editors International Conference of Territorial Intelligence ALBA IULIA 2006 Volume 1
    [Show full text]
  • Zero Alternative” Will Be Conducted on a Pre-Feasibility Level
    Description of the "Zero" (No Project) Alternative for Roşia Montană Prepared for: S.C. ROŞIA MONTANĂ GOLD CORPORATION S.A. 321, Pietei Street 3385, Roşia Montană, Alba County, Romania Prepared by: WISUTEC Wismut Umwelttechnik GmbH Jagdschänkenstr. 33 D-09117 Chemnitz Germany in collaboration with WISMUT GmbH Jagdschänkenstr. 29 D-09117 Chemnitz www.wismut.de SC Rosia Motana Gold CorporationEnvironmental Impact Study Description of the "Zero" (No Project) Alternative for Roşia Montană Table of Contents 1 Introduction .................................................................................................................. 5 1.1 Background and Objective.................................................................................... 5 1.2 Applicable Romanian and International Regulations and Guidelines ................... 6 1.3 Sources of Information.......................................................................................... 6 2 Site Conditions ............................................................................................................. 7 2.1 Site History............................................................................................................ 7 2.2 Facilities Considered in this Study ........................................................................ 8 2.3 Local Conditions ................................................................................................. 13 General .........................................................................................................................
    [Show full text]
  • Strategic Action Plan for the Danube River Basin 1995 - 2005 Revision 1999
    DANUBE POLLUTION REDUCTION PROGRAMME STRATEGIC ACTION PLAN FOR THE DANUBE RIVER BASIN 1995 - 2005 REVISION 1999 Programme Coordination Unit UNDP/GEF Assistance DANUBE POLLUTION REDUCTION PROGRAMME STRATEGIC ACTION PLAN FOR THE DANUBE RIVER BASIN 1995 – 2005 REVISION 1999 Programme Coordination Unit UNDP/GEF Assistance Preface The present Report of the SAP has been prepared on the basis of existing analytical documents, in particular the National Review Reports and the results of the National Planning Workshops. A genuine bottom-top approach has associated in the elaboration of this SAP about 300 professionals and experts from all Danube countries, from central and local Governments, from Non Governmental Organizations (NGOs), from universities and research institutions and from the private sector. This planning process has allowed to reflect national considerations concerning the analysis of problems, the formulation of objectives and targets and the identification of appropriate measures for pollution reduction. Transboundary effects of pollution have been identified and the need for regional cooperation has been defined. The first draft of the SAP has been reviewed in the frame of Hernstein II Workshop, Austria, from 12 to 16 May 1999. Experts from all Danube Countries and invited specialists from international and financing institutions have thus contributed to produce a coherent document reflecting genuinely policies and strategies of the Danube River Protection Convention. The ICPDR Steering Group, at the Meeting in Vienna on 10 and
    [Show full text]
  • Rapid Environmental Assessment of the Tisza River Basin
    RAPID ENVIRONMENTAL ASSESSMENT OF THE TISZA RIVER BASIN 2004 United Nations Environment Programme Prepared by Karin Burnod-Requia This is a joint publication of UNEP/ROE and UNEP/DEWA/GRID~Europe, in collaboration with UNEP/Vienna-ISCC. Disclaimers The contents and views express in this publication do not necessarily reflect the views or policies of the contributory organizations or the United Nations Environment Programme (UNEP). The opinions, figures and estimates set forth in this publication do not imply the expression of any opinion whatsoever on the part of UNEP concerning the legal status of any country, territory, city or its authorities, or concerning the delimitation of its frontiers and boundaries. Mention of a commercial company or product in this publication does not imply the endorsement of UNEP. Reproduction This publication may be reproduced in whole or in part and in any form for educational or non-profit purposes without special permission from the copyright holder, provided acknowledgement of the source is made. UNEP would appreciate receiving a copy of any publication that uses this publication as a source. No use of this publication may be made for resale or any other commercial purpose whatsoever without prior permission in writing from UNEP. The use of information from this publication concerning proprietary products for publicity or advertising is not permitted. UNEP/Regional Office for Europe International Environment House 11, Chemin des Anémones CH-1219 Châtelaine, Geneva, Switzerland http://www.unep.org UNEP/DEWA/GRID~Europe International Environment House 11, Chemin des Anémones CH-1219 Châtelaine, Geneva, Switzerland http://www.grid.unep.ch ii CONTENTS INTRODUCTION 1 1.
    [Show full text]
  • Analele Ştiinţifice
    View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Scientific Annals of "Alexandru Ioan Cuza" University of Iasi ANALELE ŞTIINTIFICE ALE UNIVERSITĂŢII SCIENTIFIC ANNALS OF „ALEXANDRU IOAN CUZA” din IAŞI „ALEXANDRU IOAN CUZA” UNIVERSITY OF IAŞI Tom LIX, nr.2, s. IIc, Geografie 2013 Volume LIX, no.2, s. II c, Geography series 2013 ISSN 1223-5334 (printed version) (online version) 2284-6379 eISSN © Author(s) 2013. CC Attribution 3.0 License THE POTENTIAL FOR WATER DIFFUSE POLLUTION WITH HEAVY METALS IN ARIEȘ RIVER BASIN 1*Iulia FONTANINE, 2Romulus COSTACHE Faculty of Geography, University of Bucharest [email protected], [email protected] Abstract: The potential for water diffuse pollution with heavy metals in Arieș river basin. Arieș river basin is found mostly in the area of mining extractions from Apuseni Mountains. Its position causes a high vulnerability of water courses to pollution with heavy metals derived from mine waters. In this sutdy, in order to determine the potential for water diffuse pollution in Arieș river basin, two main factors were integrated in GIS software, respectively: the potential for surface runoff and the localization of the sources of water pollution with heavy metals (from quarries, mines, blank depositions, decantation ponds). The highlighting of the potential for water diffuse pollution was achieved by computing the DPPI index for each river sub-basin. The index was computed by multiplying the average values of the Flash-Flood Susceptibility Index for each river sub-basin by the number of difuse pollution sources (from quarries, mines, blank depositions, decantation ponds) within the sub-basin units.
    [Show full text]
  • Initial Sediment Transport Model of the Mining- Affected Aries River Basin, Romania
    In Cooperation with the World Bank, the Romanian National Agency for Mineral Resources, and Futures Group Initial Sediment Transport Model of the Mining- Affected Aries River Basin, Romania By Michael J. Friedel and Joshua I. Linard Open-File Report 2008–1171 U.S. Department of the Interior U.S. Geological Survey U.S. Department of the Interior DIRK KEMPTHORNE, Secretary U.S. Geological Survey Mark D. Myers, Director U.S. Geological Survey, Reston, Virginia: 2008 For product and ordering information: World Wide Web: http://www.usgs.gov/pubprod Telephone: 1-888-ASK-USGS For more information on the USGS—the Federal source for science about the Earth, its natural and living resources, natural hazards, and the environment: World Wide Web: http://www.usgs.gov Telephone: 1-888-ASK-USGS Suggested citation: Friedel, M.J., and Linard, J., 2008, Initial Sediment Transport Model of the mining-affected Aries River basin, Romania: U.S. Geological Survey, Open-File Report 2008-1171, 23 p. Any use of trade, product, or firm names is for descriptive purposes only and does not imply endorsement by the U.S. Government. Although this report is in the public domain, permission must be secured from the individual copyright owners to reproduce any copyrighted material contained within this report. ii Abstract.........................................................................................................................................1 Introduction ...................................................................................................................................1
    [Show full text]
  • Respondent's Post Hearing Brief
    INTERNATIONAL CENTRE FOR THE SETTLEMENT OF INVESTMENT DISPUTES GABRIEL RESOURCES LTD. AND GABRIEL RESOURCES (JERSEY) LTD. Claimants VS. ROMANIA Respondent ICSID CASE NO. ARB/15/31 RESPONDENT’S POST HEARING BRIEF 18 FEBRUARY 2021 LALIVE Gabriel Resources et al. v. Romania Respondent’s Post Hearing Brief 18 February 2021 TABLE OF CONTENTS 1 INTRODUCTION .................................................................. 1 2 ROMANIA HAS AT ALL TIMES ACCORDED FAIR AND EQUITABLE TREATMENT TO THE CLAIMANTS’ INVESTMENTS .................................................................... 8 2.1 The Ministry of Environment’s Non-Issuance of the Environmental Permit Does Not Amount to Failure to Provide Fair and Equitable Treatment ......................................... 9 2.1.1 The TAC and the Ministry of Environment Had Discretion in Deciding Whether to Issue the Permit and in Deciding the Conditions to Be Attached to the Permit ............................................................................................... 9 2.1.2 By November 2011, the Ministry of Environment Was Nowhere Near Deciding on the Environmental Permit ....... 14 2.1.3 The November 2011 TAC Meeting Did Not Mark the End of the EIA Review Process ........................................... 17 2.1.4 RMGC Failed to Meet (or Delayed in Meeting) Environmental Permit Requirements .................................. 22 2.1.4.1 RMGC Did Not Secure the Ministry of Culture Endorsement until 2013 ................................................. 22 2.1.4.2 RMGC Did Not Secure the Approval of the Waste Management Plan until May 2013 ................................ 25 2.1.4.3 RMGC Did Not Have (Approved) Urban Plans ............ 26 2.1.4.4 RMGC Did Not Have a Valid Urban Certificate ........... 29 2.1.4.5 RMGC Did Not Comply with the Water Framework Directive ........................................................................ 31 2.1.4.6 RMGC Failed to Secure the Surface Rights .................
    [Show full text]
  • Respondent's Rejoinder
    INTERNATIONAL CENTRE FOR THE SETTLEMENT OF INVESTMENT DISPUTES GABRIEL RESOURCES LTD. AND GABRIEL RESOURCES (JERSEY) LTD. Claimants VS. ROMANIA Respondent ICSID CASE NO. ARB/15/31 RESPONDENT’S REJOINDER 24 MAY 2019 Gabriel Resources et al. v. Romania Respondent’s Rejoinder 24 May 2019 TABLE OF CONTENTS 1 INTRODUCTION ..................................................................1 2 THE CLAIMS FALL OUTSIDE THE TRIBUNAL’S JURISDICTION................................................................... 11 2.1 Gabriel Canada’s Claims Fall Outside the Tribunal’s Jurisdiction ................................................................................11 2.1.1 Gabriel Canada Cannot Claim Both on Its Own Behalf and on Behalf of RMGC......................................................11 2.1.2 Gabriel Canada’s Claims Fall Outside the Tribunal’s Jurisdiction to the Extent They Fail to Comply with Articles XIII(2) and (3)(b) of the Canada-Romania BIT .............................................................................................12 2.1.3 Gabriel Canada’s Claims Fall Outside the Tribunal’s Jurisdiction Since They Arise Out of Measures Taken Prior to 30 July 2012 ...........................................................17 2.1.4 Gabriel Canada’s Umbrella Clause Claim Falls Outside the Tribunal’s Jurisdiction ...................................................21 2.1.5 Gabriel Canada’s Claims Are Limited by the Substantive Provisions of the BIT .......................................22 2.1.5.1 Claims Relating to Environmental Measures
    [Show full text]
  • Map 21 Dacia-Moesia Compiled by JJ Wilkes, 1996
    Map 21 Dacia-Moesia Compiled by J.J. Wilkes, 1996 Introduction The map is centered on the Carpathian basin, traversed by the middle course of the Danube, Europe’s greatest river. The sandy wastes of the great Hungarian plain (Alföld), once an inland sea and still marshy in the south, are bounded on the west by the river and on the east by the mountains and high plains of Romanian Transylvania (Dacia). Further south, the rolling hills and wooded valleys of Serbia lie between the mountains of Bosnia and Montenegro to the west and the Bulgarian Stara Planina (Balkan Mts.) and Rhodope range (Map 51 C1) to the east. The plain has a continental climate of cold winters and short hot summers. South of the Danube the climate is milder, though snow and seasonal floods regularly impede movement. The Serbian plain and tributary valleys support cereal cultivation, but the region also has rich mineral deposits, gold, iron ore, silver and lead. Gold and iron ore are also present in western Transylvania. In the Vács (Waitzen) gorge (B2, north of Aquincum) the Danube bends from an eastward to a southward course and flows 230 miles to a confluence with the Dravus (modern Drava). It then continues south-east for 220 miles, during which it receives the Pathissus (Tisza), which drains the Hungarian plain and–through its major tributaries–Transylvania. After confluences first with the Savus at Singidunum (Belgrade), and then with the Margus, the Danube next enters a succession of gorges (Djerdap), where the stream is in places narrowed to barely 500 ft.
    [Show full text]
  • The Mineral Industry of Romania in 2017-2018
    2017–2018 Minerals Yearbook ROMANIA [ADVANCE RELEASE] U.S. Department of the Interior April 2021 U.S. Geological Survey The Mineral Industry of Romania By Lindsey Abdale and Ji Won Moon Note: In this chapter, information for 2017 is followed by information for 2018. Romania had identified mineral resources of ferrous and Europe (87% of total imports received), followed by countries nonferrous metals, industrial minerals, and mineral fuels, in Asia (10%) and the Americas (including North America, including coal, natural gas, and crude petroleum. In 2017, Central America and the Caribbean, and South America) (2.4%). Romania produced alumina, aluminum, cement, coal, copper, Romania’s main import trading partners were Germany (which iron and steel, refined lead, natural gas, nitrogen, petroleum, and supplied 20% of Romania’s total imports), Italy (10%), Hungary salt. Although Romania was not a significant mineral producer (7.5%), Poland (5.4%), and France (5.3%) (National Institute of on a global scale, it was one of the leading vertically integrated Statistics, 2018, p. 74, 75, 78). aluminum producers in Europe that use imported bauxite (table 1; Alro S.A., 2019). Production Minerals in the National Economy In 2017, the production of manganese (ore, Mn content) increased by 200%; primary and secondary zinc, by 167%; In 2017, Romania’s real gross domestic product (GDP) feldspar, by 67%; secondary lead, by 38%; nitrogen (N content increased by 6.9% from that of 2016, and the nominal GDP of ammonia), by 18%; copper (Cu content of concentrates), by in 2017 was $212 billion. The GDP in current prices for the 16%; salt (other), by 15%; and bentonite, lignite coal, and steel industrial sector was $53.2 billion, which was an increase of pipes and tubes, by 12% each.
    [Show full text]
  • Updated Integrated Tisza River Basin Management Plan
    Updated Integrated Tisza River Basin Management Plan Annex 1. List of surface water bodies List of surface water bodies in the Tisza River Basin RIVER WATER TRANS- LENGTH OF RIVER COUNTRY RIVER NAME RIVER WATER BODY NAME EUCD RWB BODY BOUNDARY WATER BODY CHARACTER WATER BODY [km] Hungary Berettyó Berettyó HUAEP322 HMWB 74.382 Hungary Bodrog Bodrog HUAEP334 NATURAL 51.172 Hungary Bódva Bódva felső HUAEP335 NATURAL 15.597 Hungary Bódva Bódva alsó HUAEP336 NATURAL 39.88 Hungary Dongéri-főcsatorna Dong-éri-főcsatorna felső HUAEP431 HMWB 65.653 Hungary Dongéri-főcsatorna Dong-éri-főcsatorna alsó HUAEP432 HMWB 15.277 Hungary Ér-főcsatorna Ér-főcsatorna HUAEP462 HMWB 8.486 Hungary Fehér-Körös Fehér-Körös HUAEP471 AWB 9.741 Hungary Fekete-Körös Fekete-Körös HUAEP475 HMWB 20.511 Hungary Hernád Hernád alsó HUAEP579 NATURAL 53.699 Hungary Hernád Hernád felső HUAEP580 HMWB 68.225 Hungary Hortobágy-Berettyó Hortobágy-Berettyó HUAEP594 HMWB 79.058 Hungary Kálló-ér Kálló-ér HUAEP625 HMWB 29.392 Hungary Keleti-főcsatorna Keleti-főcsatorna dél HUAEP650 AWB 93.692 Hungary Keleti-főcsatorna Keleti-főcsatorna észak HUAEP651 AWB 4.885 Hungary Kettős-Körös Kettős-Körös HUAEP668 HMWB 37.292 Hungary Kraszna Kraszna HUAEP729 HMWB 46.238 Hungary Lónyay-főcsatorna Lónyai-főcsatorna HUAEP766 AWB 45.190 Hungary Maros Maros torkolat HUAEP783 HMWB 28.612 Hungary Maros Maros kelet HUAEP784 HMWB 22.215 Hungary Sajó Sajó felső HUAEP931 NATURAL 52.904 Hungary Sajó Sajó alsó HUAEP932 NATURAL 70.970 Hungary Sebes-Körös Sebes-Körös felső HUAEP953 NATURAL 44.141 Updated Integrated
    [Show full text]