Horns Rev II Offshore Wind Farm Food Basis for Common Scoter
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1 Horns Rev II Offshore Wind Farm Food Basis for Common Scoter Baseline Studies
2 Client DONG Energy A/S Teglholmen A.C. Meyers Vænge 9 DK 2450 København SV Tel: Representative Lars Bie Jensen labie@dongenergy.dk Consultant Orbicon A/S Jens Juuls Vej 18 DK 8260 Viby J Tel: DHI Water Environment Health A/S Agern Allé 5 DK-2970 Hørsholm Tel: In association with: Marine observers Svankkjærvej 6 DK-7752 Snedsted Authors Henrik Skov Jan Durinck Anders Erichsen Rikke Margrethe Kloster Flemming Møhlenberg Simon B. Leonhard Project Project manager Simon B. Leonhard Quality assurance Simon B. Leonhard Revision 3 Approved Lars Sloth Published September 2008 Photos: Jens Christensen Dong /Horns Rev 2 Food Basis for Common Scoter i Orbicon/DHI/Marine Observers
3 Contents 1 SUMMARY DANSK RESUME INTRODUCTION Background The Horns Rev II Project Location Free zone Monitoring requirements for Common Scoter and the need for modelling available food supply METHODS Study period Study area and dynamics of benthic prey organisms Hydrodynamic model software Bio-geochemical software Model set-up Boundaries and forcings Runoff Filter-feeder model Calibration Sediment and benthos samples Dietary studies Data analyses Development of habitat suitability model for Ensis americanus and Spisula subtruncata25 5 QUALITY CONTROL RESULTS Small-scale patterns of filter-feeder indices Habitat suitability models for Ensis americanus og Spisula subtruncata at Horns Rev Diet of Common Scoter DISCUSSION AND CONCLUSIONS Evaluation of model results Hydrodynamic and water quality model data Evaluation of calibration data Sediment and benthos samples Dietary data Conclusions REFERENCES APPENDICES Dong /Horns Rev 2 Food Basis for Common Scoter ii Orbicon/DHI/Marine Observers
4 1 SUMMARY DONG Energy has commissioned a consortium of Orbicon and DHI in association with Marine Observers to model the distribution of prey to Common Scoter Melanitta nigra by means of a habitat model as part of the monitoring program for the planned Horns Rev 2 offshore wind farm. The establishment of the Horns Rev 2 offshore wind farm (HR2 OWF) was granted by the Department of Energy on the 19 th March 2007 on the basis of DONG Energy s application of 13 th October The location of the HR2 OWF is planned for the outer part of Horns Rev, and it consists of a total of 91 turbines, each 2.3 MW which are placed with 13 east-west oriented rows of 7 turbines. Common Scoters feed almost exclusively on filter-feeding bivalves, and in the Danish part of the North Sea they are known to feed on both cut trough shells Spisula subtruncata and American razor clams Ensis americanus. The preference for razor clams seems to be of recent origin, and this preference has been suggested as a possible reason for the dispersal of scoters in the Horns Rev area experienced during the PSO-related monitoring programme. This dispersal pattern of razor clams possibly may affect the presence of scoters near the Horns Rev 2 site. As both primary prey species to Common scoter in the North Sea occur commonly in the region knowledge of the available supply of both razor clams and trough shells in the site and on Horns Rev in general is critical to the application of a BACI design for monitoring the impact of the wind farm on scoters. Lack of detailed hydrodynamic and geo-biochemical model to construct physiology-based growth models for standard knowledge about the distribution of prey can lead to ambiguous interpretations of monitoring results, and even bias conclusions on possible impacts. The modelling work integrated dynamic model data on the potential carrying capacity of the two potential prey species in the area and field data on benthos and surface sediments and the relief of the sea floor. The carrying capacity models were developed using the output from a local combined hydrodynamic and geo-biochemical model to construct physiology-based growth models for standard individuals with an advection term that replenish the food ingested by filter-feeders. Existing knowledge of food selection and prey dynamics by Common Scoter in the Horns Rev area could not be corroborated. Both additional dietary investigations in the main feeding area of the scoters, the linked benthos sampling programme and the model results unambiguously point at two rather well-defined prey communities of razor clams and trough shells, which are both utilised by the scoters. The community of through shells is related to the area of fine sediments and very high food supply in terms of nearseabed chlorophyll concentrations found in the Esperance Bugt and at the ground Cancer. Most of the areas over the reef are unsuitable to the trough shells, due to the sediment structure and the frequent turn-over of sediments as a result of periodic strong currents over the reef. The community of Razor clams, on the other hand, prefer the medium-sized sediments over the reef and to the northwest of the reef, including the planned wind farm site, and are due to their deep penetration into the sediment able to survive the frequent sediment re-bedding in these areas. Although this community is also found in the eastern part of the area the fine sediments seem to be unsuitable to the Dong /Horns Rev 2 Food Basis for Common Scoter 3 Orbicon/DHI/Marine Observers
5 species, and prevent the razor clams to utilise the higher concentrations of food found just off the Danish coast. Rather than an ecosystem dominated by one prey species, American razor clams, our results indicate that both prey species are important at Horns Rev, and that most birds now and historically have been feeding on trough shells in the area. The change in the historic distribution of Common Scoter recorded after 1999 showed a relocation of a proportion of % of the birds along the reef into the offshore areas shallower than 15 m on the reef as well as on the plains northwest of the reef. These areas can now be identified as suitable habitat for razor clams and as mainly unsuitable for trough shells. Thus, it is highly likely that Common Scoters mainly feed on razor clams in the new area of their distribution. As the birds collected in the area in 2006 and in 2008 all were in excellent condition the most probable function of this dual prey system is that razor clams provide a supplementary source of food for scoters which are generally experiencing a rich supply of food in terms of trough shells. This is supported by the fact that scoters seem to use the razor clam habitats more during the later part of the season, when food availability in their primary feeding area may become scarce as a result of their own predation. The distribution model for razor clam for the period 2000 to 2008 clearly shows that most of the footprint area of the HR2 OWF is prime habitat for this species, and hence that concentrations of Common Scoters may occur regularly in the wind farm site, as found during the surveys from 2005 to present. Based on the model results it is questionable whether scoters will use the existing HR1 wind farm site frequently, as the area does not seem to be highly suitable to razor clams. Data on surface sediments and benthos are lacking in the areas to the west of Fanø and the whole area northeast of Horns Rev, - areas which are important to describe in terms of potential food supply to Common Scoter. Equally important, the available data on the Spisula and Ensis do only allow for a break-down of habitat suitability based on presence/absence. Quantitative data are needed to base suitability estimations on biomass levels rather than presence/absence patterns, as such estimations most likely will result in better spatial information on gradients and patchiness in the distribution of the two species on Horns Rev. Dong /Horns Rev 2 Food Basis for Common Scoter 4 Orbicon/DHI/Marine Observers
6 2 DANSK RESUME Et konsortium bestående af Orbicon og DHI i samarbejde med Marine Observers har på vegne af DONG Energy gennemført modellering af udbredelsen af føden for sortænder Melanitta nigra som en del af overvågningsprogrammet for den planlagte Horns Rev 2 havvindmøllepark. Tilladelsen til at bygge Horns Rev 2 havvindmølleparken blev givet af Energistyrelsen den 19. marts 2007 på basis af DONG Energy s ansøgning af 13. oktober Placeringen af vindmølleparken er planlagt til at være på den ydre del af Horns Rev, og mølleparken består af 91 møller på hver 2.3 MW, som er placeret i 13 øst-vestgående rrækker med hver 7 møller. Sortænder spiser næsten udelukkende filtrerende muslinger, og i den danske del af Nordsøen er de kendte for at fouragere på både Hvælvet trugmusling Spisula subtruncata og Amerikansk knivmusling Ensis americanus. Præferencen for knivmuslinger synes at være af nyere dato, og den har været foreslået som en mulig årsag til udbredelsesmønstret af sortænder på Horns Rev, som blev fundet i forbindelse med det PSOrelaterede moniteringsprogram. Dette udbredelsesmønster af knivmuslinger kan påvirke forekomsten af sortænder ved Horns Rev 2 mølleparken. Da begge byttearter forekommer almindeligt i regionen vil kendskab til den tilgængelige fødemængde af både trugmuslinger og knivmuslinger i mølleparken og på Horns Rev generelt være kritisk for anvendelse af et BACI design i moniteringsprogrammet. Manglen på detaljeret viden om udbredelsen af bytte kan føre til tvivlsomme fortolkninger af overvågningsresultater, og kan tilmed føre til forkerte konklusioner omkring mulige påvirkninger. Modelarbejdet integrerede dynamiske modeldata på den potentielle bærevne for de to byttedyr i området sammen med feltdata på muslinger, overfladesediment og havbundsrelief. Modellerne for bærevnen blev udviklet ved brug af output fra en lokal kombineret hydrodynamisk og geo-biokemisk model. Fysiologisk-baserede vækstmodeller blev etableret for standardindivider med en beskrivelse af advektion til fornyelse af føden. Resultaterne af undersøgelserne støtter ikke den eksisterende viden om fødevalg og byttedyrsdynamik hos Sortand ved Horns Rev, idet såvel supplerende fødeundersøgelser fra sortændernes vigtigste fourageringsområde, det koblede indsamlingsprogram for muslinger og modelresultaterne alle entydigt pegede på forekomsten af to relativt veldefinerede byttedyrssamfund af knivmuslinger og trugmuslinger, som begge udnyttes af sortænder. Samfundet af trugmuslinger er knyttet til området med finere sediment og høje fødekoncentrationer i form af bundnært klorofyl i Esperance Bugt og ved grunden Cancer. De fleste områder på revet er uegnede for trugmuslinger p.g.a. sedimentstrukturen og den hyppige sedimentomlejring som et resultat af perioder med kraftig strøm. Samfundet med knivmuslinger er på den anden side knyttet til det lidt grovere sediment over revet og nordvest for revet, inklusiv mølleområdet, og er på grund af deres dybe forankring i sedimentet i stand til at overleve den hyppige omlejring af sedimentet i disse områder. Selvom knivmuslingesamfundet også findes i den østlige del af området synes det finere sediment at udgøre et uegnet substrat for knivmuslinger, og som forhindrer arten i at udnytte de højere fødekoncentrationer tættere på den danske kyst. Snarere end et økosystem domineret af én bytteart for sortænder tyder disse resultater således Dong /Horns Rev 2 Food Basis for Common Scoter 5 Orbicon/DHI/Marine Observers
7 på, at begge arter er vigtige for sortænder på Horns Rev, og at den største del af fuglene nu som tidligere fouragerer på trugmuslinger. Ændringen i den historiske udbredelse af sortænder observeret efter 1999 viste en omgruppering af omkring % af fuglene langs revet til offshore-områderne på dybder mindre end 15 m på og nordvest for revet. Disse områder kan nu identificeres som egnet habitat for knivmuslinger og som generelt uegnet habitat for trugmuslinger. Det er derfor sandsynligt, at sortænder især spiser knivmuslinger i de nye områder offshore. Eftersom fuglene indsamlet i 2006 og 2008 alle var i fin kondition er den mest sandsynlige funktion af det dobbelte byttedyrssystem, at knivmuslingerne udgør en supplementær fødekilde for sortænderne, som generelt finder en rigelig fødekilde i form af trugmuslinger i det kystnære område. Dette støttes af det faktum, at sortænderne især anvender knivmuslingehabitaten offshore sidst på vinteren, når fødetilgængeligheden antageligt mindskes i deres primære fourageringsområde som følge af deres egen prædation. Udbredelsesmodellen for knivmuslinger for perioden 2000 til 2002 viser tydeligt, at hovedparten af Horns Rev 2 mølleparken er velegnet habitat for arten, og at det derfor må anses for sandsynligt, at koncentrationer af sortænder vil forekomme regelmæssigt i vindmølleområdet, som dokumenteret i perioden fra 2005 til i dag. På basis af modelresultaterne er det tvivlsomt om sortænderne anvender den eksisterende HR1 vindmøllepark i særlig høj grad, eftersom området synes at være mindre egnet som habitat for knivmuslinger. Fremtidige kørsler af habitatmodellerne vil vise hvorvidt udbredelsesmønstrene for trugmuslinger og knivmuslinger har været stabile over hele perioden for overvågningsprogrammet for Horns Rev 1, og hvorvidt konsekvensvurderinger for denne møllepark i relation til habitattab hos sortænder bør revurderes. Data på overfladesediment og benthos mangler generelt for områderne vest for Fanø og fra hele området nordøst for Horns Rev, - områder som er væsentlige at beskrive i relation til potentiel fødemængde for sortænder. Et andet vigtigt problem er, at de tilgængelige data på knivmuslinger og trugmuslinger kun tillader estimering af habitatkvalitet ud fra om arten er tilstede eller ikke tilstede. Kvantitative data behøves for at estimere habitatkvalitet ud fra data på biomasse, idet disse formodentlig vil resultere i mere detaljeret information om gradienter og fordelingsmønstre af de to arter på Horns Rev. Dong /Horns Rev 2 Food Basis for Common Scoter 6 Orbicon/DHI/Marine Observers
8 3 INTRODUCTION 3.1 Background DONG Energy has commissioned a consortium of Orbicon and DHI in association with Marine Observers to establish a model of the distribution of potentially available food supply to non-breeding Common Scoter Melanitta nigra on Horns Rev in terms of cut trough shells Spisula subtruncata and American razor clams Ensis americanus. The food supply model should be used as a basis for modelling the dynamic habitat selection of Common Scoter in the area, and thus gain important insight in relation to the potential impacts envisaged on scoters from the planned Horns Rev 2 offshore wind farm. The establishment of the Horns Rev 2 offshore wind farm (HR2 OWF) was granted by the Department of Energy on the 19 th March 2007 on the basis of DONG Energy s application of 13 th October This report contains the results of the development of the food supply model and the habitat model for Common Scoter on Horns Rev. The implementation of the habitat model is covered by a report dealing with the distribution and abundance of Common Scoter during the baseline monitoring of waterbirds related to the HR2 OWF (Skov et al. 2008). 3.2 The Horns Rev II Project Location The location of the HR2 OWF is planned for the outer part of Horns Rev, a sand bank which stretches from the coast of Denmark (Blåvands Huk) and 40 km westwards, Figure 3-1. The distance from the HR2 OWF to Blåvands Huk is 30 km. The minimum distance between the existing OWF on Horns Rev and the planned HR2 OWF is 14 km. The water depth at the site of the HR2 OWF varies between 6 and 18 m. The HR2 OWF has been designed as an arc north of the shallow ground VovVov on the western Horn Rev. The HR2 OWF consists of a total of 91 turbines, each 2.3 MW which are placed with 13 east-west oriented rows of 7 turbines. Due to the design of the OWF the distance between the rows will vary from 700 m in the eastern part to 900 m in the western part, Figure 3-2. The distance between individual turbines is 550 m. Figure 3-1 and Figure 3-2 also show the proposed placement of three 15 MW test mills. The transformer station will be located 1 km east of the wind farm m northeast of the transformer station an accommodation platform will be installed with a gangway connecting the two platforms. Dong /Horns Rev 2 Food Basis for Common Scoter 7 Orbicon/DHI/Marine Observers
9 A P P E N D I X A Benthos samples Dong /Horns Rev 2 Food Basis for Common Scoter 40 Orbicon/DHI/Marine Observers
10 Table Size classes of mussels recorded from Van Veen grab samples in the Horns Rev area Horns Rev 2, bundfauna april 2008 Muslinger Længde i mm Nucula sulcata Mysella bidentata Mactra stultorum Spisula subtruncata Angulus tenuis Fabulina fabula Chamelea gallina Ensis americanus Phaxas pellucidus 1,00 2,00 3,00 11,00 12,00 11,00 12,00 1,00 3,00 4,00 5,00 6,00 7,00 10,00 12,00 3,00 4,00 6,00 11,00 1,00 2,00 3,00 4,00 5,00 6,00 7,00 9,00 11,00 12,00 2,00 1,00 2,00 4,00 9,00 3,00 Gennemsnit St.dv. N Min Max 7,91 2,06 N=2 6,45 9,37 6,03,85 N=2 5,43 6,63 6,30. N=1 6,30 6,30 6,84 1,49 N=5 5,43 9,37 2,50,62 N=3 2,12 3,22 2,51,45 N=17 2,20 3,48 2,51,46 N=20 2,12 3,48 46,00,00 N=2 46,00 46,00 55,00. N=1 55,00 55,00 49,00 5,20 N=3 46,00 55,00 10,49. N=1 10,49 10,49 13,12,96 N=6 11,75 14,16 7,70 1,40 N=2 6,71 8,69 8,55. N=1 8,55 8,55 7,78. N=1 7,78 7,78 14,41. N=1 14,41 14,41 7,57. N=1 7,57 7,57 12,89 2,43 N=9 8,63 15,17 11,77 2,78 N=22 6,71 15,17 8,72. N=1 8,72 8,72 9,79. N=1 9,79 9,79 7,50. N=1 7,50 7,50 9,13,03 N=2 9,11 9,15 8,85,85 N=5 7,50 9,79 9,45 2,80 N=9 6,62 14,39 12,75 3,78 N=3 9,78 17,01 6,64 1,66 N=6 4,45 8,83 12,97 2,91 N=4 8,83 15,55 8,25 1,60 N=5 6,43 10,15 8,24 1,71 N=7 5,31 10,32 12,13,11 N=2 12,05 12,21 6,98 2,04 N=7 4,66 10,01 17,54. N=1 17,54 17,54 10,70 4,60 N=6 3,73 17,38 9,38 3,40 N=50 3,73 17,54 9,94. N=1 9,94 9,94 9,94. N=1 9,94 9,94 124,71. N=1 124,71 124,71 150,00. N=1 150,00 150,00 80,00. N=1 80,00 80,00 130,00. N=1 130,00 130,00 121,18 29,53 N=4 80,00 150,00 24,22. N=1 24,22 24,22 24,22. N=1 24,22 24,22 Dong /Horns Rev 2 Food Basis for Common Scoter 41 Orbicon/DHI/Marine Observers
11 Table Benthos abundance and biomass sampled by Van Veen grab Horns Rev 2 April, 2008 Abundans, antal/prøve KORALDYR HAVBØRSTEORME KREBSDYR MUSLINGER PIGHUDER Actiniaria indet. Polychaeta indet. Crustacea indet. Nucula sulcata Mysella bidentata Mactra stultorum Spisula subtruncata Angulus tenuis Fabulina fabula Chamelea gallina Ensis americanus Phaxas pellucidus Ophiura sp. Echinocardium sp. 1,00 2,00 3,00 4,00 5,00 6,00 7,00 8,00 9,00 10,00 11,00 12, Horns Rev 2 April, 2008 Biomasse Tørvægt mg/prøve KORALDYR HAVBØRSTEORME KREBSDYR MUSLINGER PIGHUDER Actiniaria indet. Polychaeta indet. Crustacea indet. Nucula sulcata Mysella bidentata Mactra stultorum Spisula subtruncata Angulus tenuis Fabulina fabula Chamelea gallina Ensis americanus Phaxas pellucidus Ophiura sp. Echinocardium sp. 1,00 2,00 3,00 4,00 5,00 6,00 7,00 8,00 9,00 10,00 11,00 12, ,8 78,7 60, ,6 23, ,2 6488,9 150, ,5 158,3 106,3 73,0 283,5.. 35, ,1.. 21,6 30,5. 16, ,6. 304,8 245,0 52,9 307,5 91,6 128,8 135,4. 94,1. 189,5 335,4. 204, , , , , , Table Sampling transects and number of key species of mussels and benthic species in the triangular dredge samples. Triangular dredge sampler "WGS84_ MIN_Y" Start WGS84_MI N_X" "WGS84_ MIN_Y" End WGS84_MI N_X" Spisula subtruncata Species Spisula solida Ensis americanus Ophiura texturata Location Esperance Bugt , , , , Esperance Bugt , , , , VovVov 1 * 7 58, , , , VovVov , , , , VovVov3 * 7 57, , , , VovVov 4 * 7 56, , , , VovVov , , , , VovVov , , , , VovVov , , , , VovVov , , , , * Empty samples Dong /Horns Rev 2 Food Basis for Common Scoter 42 Orbicon/DHI/Marine Observers
12 Dong /Horns Rev 2 Food Basis for Common Scoter 43 Orbicon/DHI/Marine Observers
13 A P P E N D I X B Sediment characteristics Dong /Horns Rev 2 Food Basis for Common Scoter 44 Orbicon/DHI/Marine Observers
14 Horns Rev April 08 Vandindhold DS Station. Dybde meter Possition Vandinfdh. % Tørstof % 1 13, , ,301 17,7 82,3 2 15, , ,771 16,8 83,2 3 14, , ,032 14,1 85,9 4 14, , ,990 13,9 86,1 5 13, , ,542 14,6 85,4 6 12, , ,179 17,4 82,6 7 12, , ,035 18,4 81,6 8 11,0-8, , ,468 15,7 84,3 9 12, , ,078 9,4 90,6 10 7, , ,119 17,9 82,1 11 6, , ,410 18,2 81,8 12 6, , ,778 17,4 82,6 April DONG/Horns Rev 2 Baseline Birds Orbicon/DHI/BIOLA
15 46 DONG/Horns Rev 2 Baseline Birds Orbicon/DHI/BIOLA
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