MUMM Winmon Report 2012

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MUMM Winmon Report 2012 Offshore wind farms in the Belgian part of the North Sea Heading for an understanding of environmental impacts Edited by Steven Degraer Robin Brabant Bob Rumes 2012 Royal Belgian Institute of Natural Sciences Management Unit of the North Sea Mathematical Models Marine Ecosystem Management Section in collaboration with I Commissioned and produced in 2012 by: Royal Belgian Institute of Natural Sciences (RBINS) Management Unit of the North Sea Mathematical Models (MUMM) www.mumm.ac.be Edited by: Steven Degraer ([email protected]) Robin Brabant ([email protected]) Bob Rumes ([email protected]) Cover photo: The first phase of the C-Power wind farm on the Thorntonbank (photo J. Haelters / MUMM / RBINS) Status draft final version revised version of document confidential Available in English Dutch French This report should be cited as: Degraer, S., Brabant, R. & Rumes, B., (Eds.) (2012). Offshore wind farms in the Belgian part of the North Sea: Heading for an understanding of environmental impacts. Royal Belgian Institute of Natural Sciences, Management Unit of the North Sea Mathematical Models, Marine ecosystem management unit. 155 pp. + annexes. If a separate chapter is cited, the authors and the title of that chapter need to be mentioned. If you have any questions or wish to receive a digital version of this document, please send an e-mail to [email protected], quoting the reference, or write to: MUMM 100 Gulledelle B–1200 Brussels Belgium Phone: +32 2 773 2111 Fax: +32 2 770 6972 http://www.mumm.ac.be/ Acknowledgements This research is financed by C-Power nv, Belwind nv and Northwind nv, in fulfillment of the environmental monitoring programme of their environmental permits. The authors want to thank C- Power, Belwind and Northwind for their willing cooperation. This monitoring exercise benefited from the use of the research vessel Belgica (operated by the Belgian Navy under charter of the RBINS), the research vessel Zeeleeuw (operated by the Flanders Institute of the Sea) and the observation aircraft of RBINS for collecting the necessary data at sea. II Table of contents Chapter 1 Degraer, S., Brabant, R., Coates, D., Courtens, W., Derweduwen, J., Haelters, J., Hostens, K., Houziaux, J.-S., Kerckhof, F., Norro, A., Onkelinx, T., Rumes, B., Stienen, E.W.M., Vanaverbeke, J., Vandendriessche, S., Van de walle, M., Vanermen, N., Van Roy, W., Verschelde, P.,Verstraete, H., Vigin, L., Vincx, M. & Willems, T., (2012). Executive Summary. pp. 1-8. Chapter 2 Brabant, R., Degraer, S. & Rumes, B., (2012). Offshore wind energy development in the Belgian part of the North Sea & anticipated impacts: an update. pp. 9-16. Chapter 3 Kerckhof, F., Rumes, B., Norro, A., Houziaux, J.-S. & Degraer, S., (2012). A comparison of the first stages of biofouling in two offshore wind farms in the Belgian part of the North Sea. pp. 17-39. Chapter 4 Coates, D., Vanaverbeke, J. & Vincx, M., (2012). Enrichment of the soft sediment macrobenthos around a gravity based foundation on the Thorntonbank pp. 41-54. Chapter 5 Vandendriessche, S., Derweduwen, J. & Hostens, K., (2012). Monitoring the effects of offshore wind farms on the epifauna and demersal fish fauna of soft-bottom sediments. pp. 55-71. Chapter 6 Derweduwen, J., Vandendriessche, S., Willems, T. & Hostens, K., (2012). The diet of demersal and semi-pelagic fish in the Thorntonbank wind farm: tracing changes using stomach analyses data. pp. 73-84. Chapter 7 Vanermen, N., Stienen, E.W.M., Onkelinx, T., Courtens, W., Van de walle, M., Verschelde, P. & Verstraete, H. (2012). Seabirds & Offshore Wind Farms: Monitoring Results 2011. pp. 85-109. Chapter 8 Brabant, R., Vigin, L., Stienen, E.W.M., Vanermen, N. & Degraer, S., (2012). Radar research on the impact of offshore wind farms on birds: Preparing to go offshore. pp. 111-126. Chapter 9 Haelters, J., Van Roy, W., Vigin, L. & Degraer, S., (2012). The effect of pile driving on harbour porpoises in Belgian waters. pp. 127-143. Chapter 10 Norro, A., Rumes, B. & Degraer, S., (2012). Differentiating between underwater construction noise of monopile and jacket foundation wind turbines: A case study from the Belgian part of the North Sea. pp. 145-155. Annexes Annex 1. Systematic species list of soft substratum macrobenthos. pp. 159-161. Annex 2. Results Two-way SIMPER analysis. pp. 163-164 Chapter 1. Executive summary S. Degraer1*, R. Brabant1, D. Coates2, W. Courtens3, J. Derweduwen4, J. Haelters1, K. Hostens4, J.-S. Houziaux1, F. Kerckhof1, A. Norro1, T. Onkelinx3, B. Rumes1, E.W.M. Stienen3, J. Vanaverbeke2, S. Vandendriessche4, M. Van de walle3, N. Vanermen3, W. Van Roy1, P. Verschelde3, H. Verstraete3, L. Vigin1 , M. Vincx2 & T. Willems4 1Royal Belgian Institute of Natural Sciences, Management Unit of the North Sea Mathematical Models (MUMM), Gulledelle 100, 1200 Brussels and 3e en 23e Linieregimentsplein, 8400 Ostend 2Ghent University, Biology Department, Marine Biology Research Group, Krijgslaan 281 (S8), 9000 Ghent 3Research Institute for Nature and Forest, Ministry of the Flemish Government, Kliniekstraat 25, 1070 Brussels 4Institute for Agricultural and Fisheries Research (ILVO-Fisheries), Bio-Environmental Research Group, Ankerstraat 1, 8400 Ostend *Corresponding author: [email protected] Hard substrate epifauna on the C-Power D5 turbine Photo A. Norro / RBINS / MUMM 2 S. Degraer et al. 1.1. Introduction With the launching of its new Climate Plan in 2008, the European Union committed itself to produce 20% of its electricity from renewable energy sources by 2020. Targets vary between member states and for Belgium the goal was set at 13%, to achieve by 2020. Offshore wind energy production is expected to be a major contributor in reaching this goal. The Royal Decree of 17 May 2004 delineated a zone for the production of electricity from water, current and wind in the Belgian part of the North Sea (BPNS). Since 2004, four companies, C-Power (Thorntonbank: 54 turbines, 325 MW), Belwind (Bligh Bank: 110 turbines, 330 MW), Northwind (formerly Eldepasco, Lodewijkbank: 72 turbines, 216 MW) and Norther (south of the Thorntonbank: 47-86 turbines, 258-470 MW), were granted a domain concession and an environmental permit to build and exploit an offshore wind farm. By July 2012 three other companies, Rentel, Seastar and Mermaid, obtained a concession, but still have to obtain an environmental permit. Both C-Power and Belwind already started the installation of an offshore wind farm. C-Power has built six gravity based foundation (GBF) wind turbines on the Thorntonbank in 2008, which were the first wind turbines in Belgian waters. Another 49 jacket foundations were installed in 2011 and the first half of 2012, which are now being equipped with the turbines. At the Belwind concession area, construction activities started in autumn 2009: in a first phase, 56 monopiles were driven into the seabed after which the foundations were equipped with turbines. The 55 wind turbines and one offshore high voltage station are operational since early 2011. Construction activities at Northwind will commence in early 2013. Belwind’s second phase is foreseen to start in 2014. To allow for a proper evaluation and auditing of the environmental impacts of offshore wind farms, the environmental permit includes a monitoring program to ensure (1) the ability to mitigate or even halt the activities in case of extreme damage to the marine ecosystem and (2) an understanding of the environmental impact of offshore wind farms to support policy, management and design of future offshore wind farms. The former objective is basically tackled through the baseline monitoring, focusing on the a posteriori, resultant impact quantification, while the latter monitoring objective is covered by the targeted or process monitoring, focusing on the cause-effect relationships of a priori selected impacts1. As such, the baseline monitoring deals with observing rather than understanding impacts and hence leads to area-specific results, which might form a basis for halting activities. Targeted monitoring on the other hand deals with the understanding of the processes behind the impacts and hence leads to more generic results, which might form a sound basis for impact mitigation. For more details on baseline and targeted monitoring we refer to Degraer & Brabant (2009). The monitoring program targets physical (i.e. hydro-geomorphology and underwater noise), biological (i.e. hard substrate epifouling and fish communities, soft substrate macrobenthos, epibenthos and fish, seabirds and marine mammals), as well as socio-economical (i.e. seascape perception and offshore renewables appreciation) aspects of the marine environment. The Management Unit of the North Sea Mathematical Models (MUMM) of the Royal Belgian Institute of Natural Sciences coordinates the monitoring and specifically covers hydro-geomorphology, underwater noise, hard substrate epifauna, radar detection of seabirds, marine mammals and socio- economic aspects. In 2011, MUMM further collaborated with different institutes to complete the necessary expertise in the following domains: noise (INTEC, Ghent University), seabirds (Research Institute for Nature and Forest, INBO), soft substrate epibenthos and fish (Institute for Agricultural and Fisheries Research, ILVO-Fisheries), and soft substrate macrobenthos (Marine Biology Section, Ghent University). For details on the specific research strategies followed and methodologies used, one is referred to the individual chapters. 1 While the first two integrated reports (Degraer & Brabant, 2009; Degraer et al., 2010) mainly dealt with the results of the baseline monitoring aspect, last year’s report (Degraer et al., 2011) as well as this report rather focus on selected findings from the targeted or process monitoring in search for a proper understanding of the environmental impacts. Chapter 1. Executive summary 3 1.2. This report’s focus The first phase of the monitoring program (2005-2012) started the year before the (anticipated) construction of the first wind turbines at the Thorntonbank (i.e. 2005). At the end of this first phase, an overview and discussion of the monitoring activities and outcomes between MUMM, its monitoring partners and the wind farm industry is planned.
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