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Investigation and water management aspects of a Hungarian-Ukrainian transboundary aquifer

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Abstract

In the framework of an EEA Norway and EU grants project involving industrial and scientific partners, complex hydrogeological investigation and groundwater modeling of a regional transboundary aquifer between Hungary and Ukraine were carried out in 2010. To find a common groundwater management strategy, this challenging cooperation work was completed by an EU country and a non-EU country. This pilot project demonstrated how the EU Water Framework Directive and some other legal aspects can be applied for a regional scale transboundary aquifer between Hungary and Ukraine. The transboundary aquifers play significant role in Hungary because the country land is mainly located in a deep and closed basin called Carpathian. After finalizing the watershed management plans in 2009, it turned out that 40 from the total 185 groundwater bodies are classified as transboundary in Hungary. The authors were involved to participate in an earlier NATO Science for Peace Project, which investigated a transboundary aquifer between Hungary and Romania some years ago. The special experience gained that time was utilized in the current project.

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... National Water Strategy 2017.18 Szűcs et al. 2013.19 . ...
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The objective of the present paper is to show that groundwater is a general geologic agent. This perception could not, and did not, evolve until the system nature of basinal groundwater flow and its properties , geometries, and controlling factors became recognized and understood through the 1960s and 1970s. The two fundamental causes for groundwater's active role in nature are its ability to interact with the ambient environment and the systematized spatial distribution of its flow. Interaction and flow occur simultaneously at all scales of space and time, although at correspondingly varying rates and intensities. Thus, effects of groundwater flow are created from the land surface to the greatest depths of the porous parts of the Earth's crust, and from a day's length through geologic times. Three main types of interaction between groundwater and environment are identified in this paper, with several special processes for each one, namely: (1) Chemical interaction, with processes of dissolution, hydration, hydrolysis, oxidation-reduction, attack by acids, chemical precipitation, base exchange, sulfate reduction, concentration, and ultrafiltration or osmosis; (2) Physical interaction, with processes of lubrication and pore-pressure modification; and (3) Kinetic interaction , with the transport processes of water, aqueous and nonaqueous matter, and heat. Owing to the transporting ability and spatial patterns of basinal flow, the effects of interaction are cumulative and distributed according to the geometries of the flow systems. The number and diversity of natural phenomena that are generated by groundwater flow are almost unlimited, due to the fact that the relatively few basic types are modified by some or all of the three components of the hydrogeologic environment: topography, geology, and climate. The six basic groups into which manifestations of groundwater flow have been divided are: (1) Hydrology and hydraulics; (2) Chemistry and mineralogy; (3) Vegetation; (4) Soil and rock mechanics; (5) Geomorphology; and (6) Transport and accumulation. Based on such a diversity of effects and manifestations, it is concluded that groundwater is a general geologic agent. Résumé L'objectif de ce papier est de montrer que les eaux souterraines sont un agent géologique général. On n'a pas pu avoir conscience de ce rôle avant que la nature en tant que système de l'écoulement souterrain dans les bassins et ses propriétés, ses géométries et ses facteurs de contrôle aient été reconnus et compris au cours des années 60 et 70. Les deux causes fondamentales du rôle actif des eaux souterraines dans la nature sont leur capacité à interagir avec l'environnement et la distribution spatiale généralisée de leur écoulement. L'interaction et l'écoulement se produisent en même temps à toutes les échelles de temps et d'espace, mais à des taux et à des intensités variables selon les échelles. Ainsi, les écoulements souterrains produisent leurs effets depuis la surface du sol jusqu'aux profondeurs les plus grandes dans les parties poreuses de l'écorce terrestre, et pour des durées qui s'étendent d'une journée jusqu'aux temps géologiques. Trois types principaux d'interaction entre les eaux souterraines et l'environnement sont identifiés dans ce papier, avec plusieurs processus par-ticuliers pour chacun ; ce sont: 1) les interactions chimi-ques, avec les processus de dissolution, d'hydratation, d'hydrolyse, d'oxydo-réduction, d'attaque acide, de précipitation chimique, d'échange de bases, de réduc-tion des sulfates, de concentration et d'ultrafiltration ou d'osmose, 2) les interactions physiques, avec les processus de lubrification et de modification de pres-sion de pores, et 3) les interactions cinétiques, avec les processus de transport de l'eau, de substances aqueuses et non aqueuses et de chaleur. Grâce à la capacité de transport et à l'organisation spatiale des écoulements dans les bassins, les effets de ces interactions sont cumulatifs et se distribuent en fonction des géométries des systèmes d'écoulement. Le nombre et la diversité des phénomènes naturels générés par les écoulements souterrains sont presque 2 Hydrogeology Journal (1999) 7 : 1-14 Q Springer-Verlag illimités, du fait que les quelques types de base sont modifiés par certaines ou par l'ensemble des trois composantes de l'environnement hydrogéologique: la topographie, la géologie et le climat. Voici les six groupes de base dans lesquels les eaux souterraines se manifestent: 1) l'hydrologie et l'hydraulique, 2) la chimie et la minéralogie, 3) la végétation, 4) le sol et la mécanique des roches, 5) la géomorphologie, et 6) le transport et l'accumulation. En se basant sur une telle variété des effets et des manifestations, on en conclut que les eaux souterraines sont un agent géologique général. Resumen El objetivo del artículo es mostrar que el agua subterránea es un agente geológico habitual. Esta percepción no se pudo desarrollar hasta que la natu-raleza de la hidrogeología de cuenca, sus propiedades, geometría y factores de control no fueron reconocidos y entendidos en las décadas de los 60-70. Las dos causas fundamentales para el papel activo de las aguas subterráneas en la naturaleza son su capa-cidad para interactuar con el medio ambiente y la distribución espacial del flujo. Ambas tienen lugar simultáneamente a todas las escalas de espacio y tiempo, aunque con distintas intensidades. Así, el flujo subterráneo tiene lugar desde la superficie hasta a grandes profundidades, y desde escalas de un día hasta tiempos geológicos. En este artículo se identifican tres tipos principales de interacciones entre aguas subterrá-neas y medio ambiente, con ciertos procesos particu-lares para cada tipo de interacción: (1) Interacción química, con los procesos de disolución, hidratación, hidrólisis, oxidación-reducción, ataque químico, preci-pitación, intercambio iónico, reducción de sulfatos, concentración, ultrafiltración y ósmosis; (2) Interacción física, con los procesos de lubrificación y modificación de presiones y (3) Interacción cinética, con los procesos de transporte de agua, materia acuosa y no acuosa y calor. Dadas la capacidad de transporte y las caracterís-ticas especiales del flujo en cuencas sedimentarias, los efectos de interacción son acumulativos y se distri-buyen de acuerdo con la geometría de los sistemas de flujo. El número y la diversidad de los fenómenos natu-rales que se generan mediante flujo subterráneo son prácticamente ilimitados, ya que los tipos básicos se pueden modificar por una o varias de las componentes del medio hidrogeológico: topografía, geología y clima. Los seis grupos básicos en los que se han dividido las manifestaciones de flujo subterráneo son: (1) Hidro-logía e hidráulica, (2) Química y mineralogía, (3) Vege-tación, (4) Mecánica del suelo y de las rocas, (5) Geomorfología y (6) Transporte. Basándose en tan gran diversidad de efectos y manifestaciones se concluye que las aguas subterráneas son un agente geológico habitual.
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The alluvial aquifer of Somes-Szamos River is a transboundary hydrogeological basin, shared between Romania and Hungary. The research was carried out by a group of scientific teams formed by Belgium, Romanian and Hungarian partners, in the frame of the NATO Science for Peace programme. Difficult problems had to be overcome due to the specific hydrogeological structure of the aquifer. Before this project, every country had its own understanding of the geological structure. A scientific concertation allowed the establishment of a coherent geological interpretative model in agreement with all available data. Hydrogeologically, based on this conceptual model, a simplified structure of the regional groundwater flow model with 3 layers was considered as a reasonable compromise between the actual complexity of the aquifer and the relatively scarce volume of reliable data concerning hydrogeological parameters and variables. A spatially distributed and "process-based" numerical model has been established making optimal use of various data concerning geology, hydrology, hydrogeology, geomorphology, topography were required. Some of these data were collected from various archives; others were measured during successive field campaigns, undertaken in October 2001, April 2002, April 2003 and October 2003. All collected data were introduced and organised into a common database, whose concept was developed previously by the Hydrogeology Group of the University of Liège. This GIS-linked database was used first for providing and processing, input information for the regional groundwater modelling, but it will be usable for many purposes linked to the groundwater management of this transboundary aquifer.
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The Most Frequent Value Method (MFV) is applied to groundwater modeling as a robust and effective geostatistical method. The Most Frequent Value method is theoretically derived from the minimization of the information loss called the I-divergence. The MFV algorithm is then coupled with global optimization (Very Fast Simulated Annealing) to provide a powerful method for solving the inverse problems in groundwater modeling. The advantages and applicability of this new approach are illustrated by means of theoretical investigations and case studies. It is demonstrated that the MFV method has certain advantages over the conventional statistical methods derived from the maximum likelihood principle.
Simply-structured groundwater model analysis for informing management of transboundary aquifers: Examples from Bengal Aquifer System (Bangladesh, Insdia) and Nubian Sandstone Aquifer System
  • C I Voss
  • H A Michael
  • P Aggarwal
  • CI Voss
Voss, C.I., Michael, H.A., and Aggarwal, P., Simply structured groundwater model analysis for informing management of transboundary aquifers: Examples from Bengal Aquifer System (Bangladesh, Insdia) and Nubian Sandstone Aquifer System (Chad, Egypt, Libya, Sudan), Intern. Conf. "Transboundary Aquifers: Challenges and New Directions", ISARM2010, Paris, UNESCO, 6-8 December, 2010, pp. 1-2.
4.8 Hydrogeological Study of Somes-Szamos Transboundary Alluvial Aquifer, Transboundary Water Resources Management, A Multi-disciplinary Approach, Ganulis
  • R Drobot
  • P Szucs
  • S Brouyere
  • M Minciuna
  • L Lenart
  • A Dassargues
Drobot, R., Szucs P., Brouyere, S., Minciuna, M., Lenart, L., and Dassargues, A., 4.8 Hydrogeological Study of Somes Szamos Transboundary Alluvial Aquifer, Transboundary Water Resources Management, A Multi disciplinary Approach, Ganulis, J., Aureli, A., and Fried, J., Eds., 2011, ISBN 978 3 527 33014 0, Wiley VCH, Weinheim, 2011, pp. 136-142.
Transboundary aquifers: Managing a vital resource
  • R M Stephan
  • RM Stephan
Stephan, R.M., Transboundary aquifers: Managing a vital resource, UNESCO, Intern. Hydrological Program, France, 2009, pp. 1-24.
Common char acterization of the transboundary aquifer of Some Sza mos river
  • A Dassargues
  • S Brouyere
  • I Popescu
  • L Lenart
  • P Szucs
  • T Madarasz
  • A Szabo
  • M Bretotean
  • M Minciuna
  • A Filip
  • F Nistea
  • A Szendrei
  • S Curtean
  • M Virag
  • L Miko
Dassargues, A., Brouyere, S., Popescu, I., Lenart, L., Szucs, P., Madarasz, T., Szabo, A., Bretotean, M., Minciuna, M., Filip, A., Nistea, F., Szendrei, A., Curtean, S., Virag, M., and Miko, L., Common char acterization of the transboundary aquifer of Some Sza mos river (Romania Hungary), BALWOIS, Conference on Water Observation and Information Sytems for Deci sion Support, 25-29 May, 2004, Ohrid, Republic of Macedonia, pp. 1-11.