The 'Voordelta', the Contiguous Ebb-Tidal Deltas in the SW
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Study of Downstream Migrating Salmon Smolt in the River Rhine Using the NEDAP Trail System: 2006 and Preliminary Results 2007
Not to be cited without permission of the author International Council for North Atlantic Salmon the Exploration of the Sea Working Group Working Paper 2007/26 Study of downstream migrating salmon smolt in the River Rhine using the NEDAP Trail System: 2006 and preliminary results 2007 by Detlev Ingendahl *, Gerhard Feldhaus *, Gerard de Laak, Tim Vriese and André Breukelaar. *Bezirksregierung Arnsberg, Fishery and Freshwater ecology, Heinsbergerstr. 53, 57399 Kirchhundem, Germany Sportvisserij Nederland, Visadvies, RIZA Running headline: Downstream migrating salmon smolt in the River Rhine Key words: Salmon smolt, downstream migration, River Rhine, Nedap Trail system, Delta Abstract Downstream migration of Atlantic salmon smolt was studied in the River Rhine in 2006 and 2007 using the NEDAP Trail system. In 2006 10 fish and in 2007 78 fish were released into two tributaries of the River Rhine (R. Sieg in 2006 and R. Wupper in 2007). The smolts (> 150 g) were tagged with a transponder (length 3.5 cm, weight 11.5 g) by surgery and introduction into the body cavity. After a recovery period of three days (2006) and ten days (2007), respectively in the hatchery the fish were released into the river. The transponder equipped fish can be detected by fixed antenna stations when leaving the tributary and during their migration through the Rhine delta to the sea. The NEDAP trail system is based on inductive coupling between an antenna loop at the river bottom and the ferrite rod antenna within the transponders. Each transponder gives its unique ID- number when the fish is passing a detection station. Until now 64 fish left the river of release (5 in 2006 and 59 in 2007, respectively). -
Wild Bees in the Hoeksche Waard
Wild bees in the Hoeksche Waard Wilson Westdijk C.S.G. Willem van Oranje Text: Wilson Westdijk Applicant: C.S.G. Willem van Oranje Contact person applicant: Bart Lubbers Photos front page Upper: Typical landscape of the Hoeksche Waard - Rotary Hoeksche Waard Down left: Andrena rosae - Gert Huijzers Down right: Bombus muscorum - Gert Huijzers Table of contents Summary 3 Preface 3 Introduction 4 Research question 4 Hypothesis 4 Method 5 Field study 5 Literature study 5 Bee studies in the Hoeksche Waard 9 Habitats in the Hoeksche Waard 11 Origin of the Hoeksche Waard 11 Landscape and bees 12 Bees in the Hoeksche Waard 17 Recorded bee species in the Hoeksche Waard 17 Possible species in the Hoeksche Waard 22 Comparison 99 Compared to Land van Wijk en Wouden 100 Species of priority 101 Species of priority in the Hoeksche Waard 102 Threats 106 Recommendations 108 Conclusion 109 Discussion 109 Literature 111 Sources photos 112 Attachment 1: Logbook 112 2 Summary At this moment 98 bee species have been recorded in the Hoeksche Waard. 14 of these species are on the red list. 39 species, that have not been recorded yet, are likely to occur in the Hoeksche Waard. This results in 137 species, which is 41% of all species that occur in the Netherlands. The species of priority are: Andrena rosae, A. labialis, A. wilkella, Bombus jonellus, B. muscorum and B. veteranus. Potential species of priority are: Andrena pilipes, A. gravida Bombus ruderarius B. rupestris and Nomada bifasciata. Threats to bees are: scaling up in agriculture, eutrophication, reduction of flowers, pesticides and competition with honey bees. -
Dredging and Dumping in Laboratory Scale Experiments of Estuaries
Student number: 5821797 Effects of dredging and dumping in laboratory scale experiments of estuaries Cox, J.R. (Jana) Student number: 5821797 Utrecht University, Department of Physical Geography Faculty of Geosciences March 2018 – final version Master: Earth Surface and Water Track: Coastal and fluvial morphodynamics Supervisors: J.R.F.W Leuven & Prof. 0 M.G. Kleinhans Contents Table of figures ............................................................................................................................................. 3 Abstract ........................................................................................................................................................ 8 1. Introduction ......................................................................................................................................... 9 1.1 Review of the effects of dredging and dumping on estuaries & suggested mechanisms ................... 9 1.2 Description of the Western Scheldt estuary ..................................................................................... 11 1.2.1 Geological history of the estuary ............................................................................................... 11 1.2.2 Morphological development of the Western Scheldt estuary ................................................... 12 1.3 Current morphology of the Western Scheldt ................................................................................... 13 1.4 Sediment balance of the Western Scheldt estuary.......................................................................... -
Food for the Future
Food for the Future Rotterdam, September 2018 Innovative capacity of the Rotterdam Food Cluster Activities and innovation in the past, the present and the Next Economy Authors Dr N.P. van der Weerdt Prof. dr. F.G. van Oort J. van Haaren Dr E. Braun Dr W. Hulsink Dr E.F.M. Wubben Prof. O. van Kooten Table of contents 3 Foreword 6 Introduction 9 The unique starting position of the Rotterdam Food Cluster 10 A study of innovative capacity 10 Resilience and the importance of the connection to Rotterdam 12 Part 1 Dynamics in the Rotterdam Food Cluster 17 1 The Rotterdam Food Cluster as the regional entrepreneurial ecosystem 18 1.1 The importance of the agribusiness sector to the Netherlands 18 1.2 Innovation in agribusiness and the regional ecosystem 20 1.3 The agribusiness sector in Rotterdam and the surrounding area: the Rotterdam Food Cluster 21 2 Business dynamics in the Rotterdam Food Cluster 22 2.1 Food production 24 2.2 Food processing 26 2.3 Food retailing 27 2.4 A regional comparison 28 3 Conclusions 35 3.1 Follow-up questions 37 Part 2 Food Cluster icons 41 4 The Westland as a dynamic and resilient horticulture cluster: an evolutionary study of the Glass City (Glazen Stad) 42 4.1 Westland’s spatial and geological development 44 4.2 Activities in Westland 53 4.3 Funding for enterprise 75 4.4 Looking back to look ahead 88 5 From Schiedam Jeneverstad to Schiedam Gin City: historic developments in the market, products and business population 93 5.1 The production of (Dutch) jenever 94 5.2 The origin and development of the Dutch jenever -
Kaart Natura 2000-Gebied Grevelingen
Natura 2000-gebied #115 kaartblad 4 Grevelingen 67000 68000 69000 70000 71000 72000 73000 74000 75000 76000 g Weg Sint terin Dijk Krammerzicht We Oude Weg Polder Slikweg de Tille dijk Bouwlust Nieuwe-Tonge La nd sedijk Polder he Klinkerland 25 Polder Klinkerlandse Weg 't Anker rlandsc Eben-Haëzer Lage e Dijk Zeedijk noordse Tilse Klinkerlandse Klink Battenoordse Dijk Sl Batte 414000 Pl 51 414000 Tonisseweg Battenoord Katendrecht Oostendesche Dijk Korte Tilse Weg Tilse Pl 50 Bou Lust De Bouwstee Straalenburg Schenkelweg Lange dse Watering Jachthaven 2 Polder het Oudeland Polder Biermansweg Polder Battenoord Oudelan -1 Pannenweg Lage 26 -1 Pl 49 Weg Gemeente Huize Grietje Oostflakkee Havenweg (Gemeentehuis te Oude-Tonge) Weg Zeldenrust Oudelandsche Zonne-Hoeve De Pannenstee Oostende Oudelandsche van Oude-Tonge Blauwe Pl 48 Maranatha 27 Wilhelmina hoeve 413000 Weg 413000 2 Groene 36 Battenoord Kreek Stationsweg De Tille Tilseweg -2 -1 Sl -1 37 N59 Tweede Polder Terlon 35 38 Magdalenapolder Pl 47 Blaakweg Sl Bouwlust 39 Polder het -2 -2 Sl Weg -1 Polder Magdalenapolder OudelandseOudeland van Oude-Tonge Mag IJsbaan Km kreek Gemeente Middelharnis Batten 34 oord dalena weg Polder 412000 412000 -2 N59 -2 Eerste Groene 2 Dijk Sl Magdalenadijk Le Frans 29 Dijk Sl Magdalena Sl Spuikom N498 Pl 46 Molenpolder Sl -10 landse 30 -16 Helledijk -15 -5 Zuider Oude-Tonge Polder ZuiderlandseWeg Zuiderland Sl Mijn Eiland -13 33 Sl -12 Zuiveringsinst Polder Zuiderlandse Kreek Zeedijk Jacob -3 Sl St Pl 45 Heeren polder Pl 44 Bungalowpark Schinkelweg -6 De Eendracht -
The Ecology O F the Estuaries of Rhine, Meuse and Scheldt in The
TOPICS IN MARINE BIOLOGY. ROS. J. D. (ED.). SCIENT. MAR . 53(2-3): 457-463 1989 The ecology of the estuaries of Rhine, Meuse and Scheldt in the Netherlands* CARLO HEIP Delta Institute for Hydrobiological Research. Yerseke. The Netherlands SUMMARY: Three rivers, the Rhine, the Meuse and the Scheldt enter the North Sea close to each other in the Netherlands, where they form the so-called delta region. This area has been under constant human influence since the Middle Ages, but especially after a catastrophic flood in 1953, when very important coastal engineering projects changed the estuarine character of the area drastically. Freshwater, brackish water and marine lakes were formed and in one of the sea arms, the Eastern Scheldt, a storm surge barrier was constructed. Only the Western Scheldt remained a true estuary. The consecutive changes in this area have been extensively monitored and an important research effort was devoted to evaluate their ecological consequences. A summary and synthesis of some of these results are presented. In particular, the stagnant marine lake Grevelingen and the consequences of the storm surge barrier in the Eastern Scheldt have received much attention. In lake Grevelingen the principal aim of the study was to develop a nitrogen model. After the lake was formed the residence time of the water increased from a few days to several years. Primary production increased and the sediments were redistributed but the primary consumers suchs as the blue mussel and cockles survived. A remarkable increase ofZostera marina beds and the snail Nassarius reticulatus was observed. The storm surge barrier in the Eastern Scheldt was just finished in 1987. -
Half a Century of Morphological Change in the Haringvliet and Grevelingen Ebb-Tidal Deltas (SW Netherlands) - Impacts of Large-Scale Engineering 1964-2015
Half a century of morphological change in the Haringvliet and Grevelingen ebb-tidal deltas (SW Netherlands) - Impacts of large-scale engineering 1964-2015 Ad J.F. van der Spek1,2; Edwin P.L. Elias3 1Deltares, P.O. Box 177, 2600 MH Delft, The Netherlands; [email protected] 2Faculty of Geosciences, Utrecht University, P.O. Box 80115, 3508 TC Utrecht 3Deltares USA, 8070 Georgia Ave, Silver Spring, MD 20910, U.S.A.; [email protected] Abstract The estuaries in the SW Netherlands, a series of distributaries of the rivers Rhine, Meuse and Scheldt known as the Dutch Delta, have been engineered to a large extent. The complete or partial damming of these estuaries in the nineteensixties had an enormous impact on their ebb-tidal deltas. The strong reduction of the cross-shore tidal flow triggered a series of morphological changes that includes erosion of the ebb delta front, the building of a coast-parallel, linear intertidal sand bar at the seaward edge of the delta platform and infilling of the tidal channels. The continuous extension of the port of Rotterdam in the northern part of the Haringvliet ebb-tidal delta increasingly sheltered the latter from the impact of waves from the northwest and north. This led to breaching and erosion of the shore-parallel bar. Moreover, large-scale sedimentation diminished the average depth in this area. The Grevelingen ebb-tidal delta has a more exposed position and has not reached this stage of bar breaching yet. The observed development of the ebb-tidal deltas caused by restriction or even blocking of the tidal flow in the associated estuary or tidal inlet is summarized in a conceptual model. -
Investigating the Regional Employment Effects of Solo Self- Employed Formation Master Thesis
INVESTIGATING THE REGIONAL EMPLOYMENT EFFECTS OF SOLO SELF- EMPLOYED FORMATION MASTER THESIS ECONOMIC GEOGRAPHY FACULTY OF SPATIAL SCIENCES UNIVERSITY OF GRONINGEN M.D. Cornelissen SUPERVISOR: S. KOSTER Abstract The solo self-employed pool has increased amongst various European countries during the last two decades and became a considerable large source of income. Although recent empirical research suggests that solo self-employed entries may bring flexible services to incumbent firms, the exact economic impact of the solo self-employed group remains rather unclear. In this study, the overall contribution of the solo self-employed is followed over a period of ten years in which immediate and indirect effects are separated through an Almon polynomial distributed lag model. The results imply that solo self-employed stimulate the competition among incumbent firms rather than offer flexibility to the market. Furthermore, it was found that regional dissimilarities of the employment change induced by solo self-employed entrants could for a large part be clarified by respective differences of the indirect effects. Hence, the way solo self-employed interact with their regional environment plays a crucial role for explaining their influence on regional development. The results indicate that the indirect effects of solo self-employed entrants are more pronounced in agglomerations and the knowledge intensive sector. Keywords: Solo self-employed, regional development, regional employment, immediate and indirect effects, flexibility. 1. Introduction One of the most persistent economic trends in Europe is the increase of the solo self-employed group at the national workforce. This growth is seen in Greece, Romania, the United Kingdom, the Netherlands and among many other European nations (Van Stel et al., 2014; CBS, 2020). -
Veilig Veerkrachtig Vitaal Uitvoeringsprogramma Zuidwestelijke Delta 2010-2015+
Veilig Veerkrachtig Vitaal Uitvoeringsprogramma Zuidwestelijke Delta 2010-2015+ Versie voor behandeling in provinciale staten en besturen waterschappen December 2010 Ontwerp-Uitvoeringsprogramma Zuidwestelijke Delta 2010-2015+ Maart 2010 Veilig Veerkrachtig Vitaal Uitvoeringsprogramma Zuidwestelijke Delta 2010-2015+ Versie voor behandeling in provinciale staten en besturen waterschappen Stuurgroep Zuidwestelijke Delta in samenwerking met de Adviesgroep Zuidwestelijke Delta December 2010 g - levin iden en tit m ei Economisch sa t Ecologisch vitaal veerkrachtig r g u e u Nationale b t i l e u wateropgave d c re g gi in on el ale ikk gebiedsontw Klimaatbestendig en veilig Samenvatting: balans veilig, veerkrachtig en vitaal herstellen Een veilige, veerkrachtige en vitale zuidwestelijke delta. In de stilstaande, zoete of zoute wateren die zo ontston- Voor een betere balans tussen veilig, veerkrachtig en Dat is wat de provincies, waterschappen en ministeries, den ging de kwaliteit van het water echter sterk achter- vitaal, bevat het programma twee typen acties: verenigd in de Stuurgroep Zuidwestelijke Delta, als ideaal uit, met negatieve gevolgen voor recreatie, visserij en • Gebiedsprogramma’s voor herstel van het watermilieu, voor ogen staat. landbouw. Het Volkerak-Zoommeer heeft problemen met waarborgen van de veiligheid en verbeteren van leef- blauwalgen, stankoverlast, vissterfte en momenten van omgeving en economie. Dat betekent: onvoldoende geschikt water voor beregening. In de • Deltathema’s waar de stuurgroep zich op richt om vol- • Veilig: voldoende beschermd tegen overstromingen, Oosterschelde, die zijn getijdenritme behield, verdwij- gende stappen richting het ideaal van een veilige, ook wanneer de verwachte klimaatverandering meer nen intergetijdengebieden door erosie van de zand- veerkrachtige en vitale delta voor te bereiden. -
The 'Voordelta', the Contiguous Ebb-Tidal Deltas in the SW
Netherlands Journal of Geosciences — Geologie en Mijnbouw |96 – 3 | 233–259 | 2017 doi:10.1017/njg.2016.37 The ‘Voordelta’, the contiguous ebb-tidal deltas in the SW Netherlands: large-scale morphological changes and sediment budget 1965–2013; impacts of large-scale engineering Edwin P.L. Elias1,∗, Ad J.F. van der Spek2 & Marian Lazar3 1 Deltares USA, 8601 Georgia Ave., Suite 508, Silver Spring, MD 20910, USA 2 Deltares, AMO, P.O. Box 177, 2600 MH Delft, The Netherlands 3 Rijkswaterstaat, Sea and Delta, P.O. Box 556, 3000 AN Rotterdam, The Netherlands ∗ Corresponding author. Email: [email protected] Manuscript received: 20 December 2015, accepted: 9 September 2016 Abstract The estuaries in the SW Netherlands, a series of distributaries of the rivers Rhine, Meuse and Scheldt known as the Dutch Delta, have been engineered to a large extent as part of the Delta Project. The Voordelta, a coalescing system of the ebb-tidal deltas of these estuaries, extends c.10 km offshore and covers c.90 km of the coast. The complete or partial damming of the estuaries had an enormous impact on the ebb-tidal deltas. The strong reduction of the cross-shore directed tidal flow triggered a series of morphological changes that continue until today. This paper aims to give a concise overview of half a century of morphological changes and a sediment budget, both for the individual ebb-tidal deltas and the Voordelta as a whole, based on the analysis of a unique series of frequent bathymetric surveys. The well-monitored changes in the Voordelta, showing the differences in responses of the ebb-tidal deltas, provide clear insight into the underlying processes. -
Summary Report Plastic Litter in Rhine, Meuse and Scheldt, Contribution to Plastic Litter in the North Sea
Summary report Plastic litter in Rhine, Meuse and Scheldt, contribution to plastic litter in the North Sea 1206088-000-ZKS-0004, 27 May 2013, final Contents 1 Introduction 1 1.1 Definitions, sources and pathways 1 1.2 Effects of plastic litter in the aquatic environment 2 2 Transport processes of plastic litter 5 2.1 Processes in rivers 5 2.2 Methodology and data availability 6 3 Quantification of transported plastic litter 9 3.1 Contribution to litter in the North Sea 9 3.2 River Rhine 12 3.3 River Meuse– coarse and fine fraction 13 3.4 River Scheldt – coarse and fine fraction 13 4 Governance 15 5 Monitoring 17 6 General conclusions 19 7 Recommendations 21 Summary report Plastic litter in Rhine, Meuse and Scheldt, contribution to plastic litter in the North i Sea 1206088-000-ZKS-0004, 27 May 2013, final 1 Introduction The Marine Strategy Framework Directive (MSFD) establishes a framework within which Member States shall take the necessary measures to achieve or maintain good environmental status in the marine environment by the year 2020 at the latest. The MSFD.installed to ensure Good Environmental Status (GES) by 2020 includes the qualitative descriptor ‘Marine Litter’ (MSFD, Annex I, descriptor 10). For freshwater, one of the main policy instruments is the Water Framework Directive (WFD), which does not include litter in determining ecological status for freshwater bodies. National authorities in the Netherlands are currently implementing the MSFD and need to provide the European Commission with data on the amounts of litter in the Dutch part of the North Sea. -
Viaje Aep 2010
VIAJE AEP_2010 PAÍSES BAJOS AMSTERDAM ROTTERDAM ZEELAND VENLO ALEMANIA DUISBURG INSEL HOMBROICH CASTLE DYCK Asociación Española de Paisajistas índice 1.- Datos de contacto 2.- Programa 3.- Descripción de los proyectos 1 Asociación Española de Paisajistas datos de contacto Juan José Galán Tel: (0034) 627 43 44 93 Antonio Fresneda Tel: (0034) 625 41 22 22 Hotel Casa 400 Eerste Ringdijkstraat 4 1097 BC Amsterdam Nederland Tel:+31 (0)20 665 11 71 Fax:+31 (0)20 663 03 79 Nh Duesseldorf City Kölner Strasse, 186-188. D-40227 Düsseldorf Alemania Tel. +49.211.78110 Fax: +49.211.7811800 redacción del documento Juan José Galán Coordinación Antonio Fresneda Recopilación de documentación y maquetación David Sanz Recopilación de documentación agradecimientos Niek Hazendonk arquitecto de paisaje Ministerio de Agricultura, Naturaleza y Calidad Alimentaria 0031 (0)616762878 , 0031 (0) 345531156 [email protected] West 8 urban design & landscape architecture Schiehaven 13M 3024 EC Rotterdam The Netherlands H+N+S Landschapsarchitecten Bosch Slabbers [email protected] 2 Asociación Española de Paisajistas programa 10 JULIO (mañana): AMSTERDAM - Vuelo Madrid-Amsterdam (10:20-12:55) - Desplazamiento y check-in en Hotel (12:55-14:30) Comida (14:30-15:30) - Desplazamiento y visita BOS PARK (15:00-18:00) - Desplazamiento y visita: BORNEO ISLAND y IJBURG (urbanización/arquitectura contemporánea) (18:30-20:00) (noche en Amsterdam) 11 JULIO: ZONA CENTRO PAÍSES BAJOS Desplazamiento en autobús (9:00-10:00) - ZANDERIJ CRAILOO - KATTENBROEK y VATHORST. (Ejemplos de nuevos desarrollos urbanos sostenibles vinculados al agua) (10:00-13:00) Desplazamiento en autobús (13:00 a 13:30) Comida en KASTEL GROENEVELD (13:30-14:30) Desplazamiento en autobús (14:30 a 15:00) -DE HOGE VELUWE NATIONAL PARK.