Helgoland Marine Research

, Volume 67, Issue 3, pp 445–459

Benthos and demersal fish habitats in the German Exclusive Economic Zone (EEZ) of the North Sea

  • Hermann Neumann
  • Henning Reiss
  • Siegfried Ehrich
  • Anne Sell
  • Kay Panten
  • Matthias Kloppmann
  • Ingo Wilhelms
  • Ingrid Kröncke
Original Article

DOI: 10.1007/s10152-012-0334-z

Cite this article as:
Neumann, H., Reiss, H., Ehrich, S. et al. Helgol Mar Res (2013) 67: 445. doi:10.1007/s10152-012-0334-z

Abstract

We compiled data from different monitoring surveys to analyse and compare community and diversity patterns of fish, epi- and infauna in the German Exclusive Economic Zone (EEZ) of the North Sea in order to identify benthic habitats common to all faunal components. We found congruent community patterns of fish, epi- and infauna for the coastal waters, the Oysterground and the area called “Duck’s Bill”, which coincided with specific abiotic characteristics of these regions. The three regions were defined as special habitats for fish, epi- and infauna species in the German EEZ. The differences in the seasonal variability of abiotic factors seem to be the most important discriminating abiotic characteristic for the three habitats. The spatial distribution of fish, epifauna and infauna communities remained stable over time although habitat characteristics such as sea surface temperature increased due to climate change. However, it is expected that the coastal habitat will be more sensitive to future climate change effects in contrast to the Oysterground and Duck’s Bill habitat.

Keywords

Epifauna Infauna Demersal fish Spatial distribution Community structure Habitat stability Climate change 

Introduction

Analysing spatial patterns of species communities has a long tradition in North Sea research. First spatial investigations of benthic infauna communities were carried out by Petersen (1914) in Danish waters, while first studies on spatial patterns of benthic epifauna were conducted by Dyer et al. (1982, 1983) resulting from the analysis of fisheries’ bycatch. Daan et al. (1990) highlighted the importance to analyse fish communities instead of single commercial species to understand how the North Sea ecosystem functions. Since the beginning of such investigations, effort increased to analyse spatial community structure of fish (Greenstreet and Hall 1996; Ehrich et al. 2009), benthic infauna (Duineveld et al. 1991; Heip et al. 1992; Künitzer et al. 1992; Kröncke et al. 2011) and benthic epifauna (Frauenheim et al. 1989; Jennings et al. 1999; Zühlke et al. 2001) on a North Sea wide scale. However, similarities and the interrelationships in community structure between these faunal components were only recently studied, for example by Callaway et al. (2002) and Reiss et al. (2010). Most of these studies have identified the 50-m depth contour in the North Sea as a conspicuous boundary separating fish, epifauna and infauna communities since it closely matches the boundary between mixed and stratified waters and is, thus, related to abrupt changes in the abiotic environment. Additionally, epifauna and infauna diversity was found to be lower in the southern North Sea than in central and northern parts, while conversely fish diversity was highest near the major inflows of Atlantic water masses in the North Sea (Fair Isle, East Shetland and English Channel) (Callaway et al. 2002; Reiss et al. 2010).

Spatial boundaries for ecosystem management, nature conservation and spatial planning are in most cases represented by the Exclusive Economic Zones (EEZ) of the different North Sea neighbouring states. Within the German EEZ, limited attention has been paid to the interrelationships in community structure and diversity of different faunal components. Additionally, the spatial resolution of large-scale studies was often not sufficient to meet national management requirements. Callaway et al. (2002), for instance, only defined two epifauna communities and one fish community by analysing approximately 10 stations in the area of the German EEZ. Reiss et al. (2010) found three epifauna and two fish communities based on 25 stations. Epifauna community structure in and around the German EEZ was analysed by Neumann et al. (2009), but also on limited sampling resolution. The most detailed studies dealing with community structure of benthic infauna in the German EEZ were carried out by Salzwedel et al. (1985) and Rachor and Nehmer (2003). Rachor and Nehmer (2003) defined eight benthic regions in the German EEZ of the North Sea based on infauna community structure, which they also related to the presence and absence of epifauna species.

However, a comprehensive analysis of the interrelationships in community structure between fish, epifauna and infauna as well as underlying environmental drivers in the German EEZ is missing and, thus, a detailed description of habitats in the EEZ, which were defined here as “a particular environment which can be distinguished by its abiotic characteristics and associated biological communities at particular but dynamic scales of space and time in a specific geographic area” (sensu ICES 2006; Kearney 2006). Additionally, a single sampling gear as used in most studies is insufficient to sample the whole species inventory of habitats in the EEZ since catchability greatly differs between gears (Reiss et al. 2006a; Ehrich et al. 2007). International directives and policies such as the Habitat Directive (HD) and the Marine Strategy Framework Directive (MSFD) require the development of a favourable condition of habitats and species (Commission 1992, 2008). However, the lack of knowledge and data especially with regard to the benthos is often recognized in the implementation of such directives (BMU 2012). To provide some more baseline information in this context, data taken during surveys of the “International Bottom Trawl Survey (IBTS)”, the “German Autumn Survey in the Exclusive Economic Zone (GASEEZ)” and the German data of the “ICES North Sea Benthos Project 2000” were compiled and analysed (1) to describe community structures and diversity of fish, benthic epifauna and infauna in the German EEZ and (2) to identify congruent patterns between faunal components. Finally, we relate common community and diversity patterns to abiotic characteristics (3) to classify habitats in the German EEZ for all faunal components.

Materials and methods

Area of investigation

Samples were taken in the German Exclusive Economic Zone (EEZ) of the North Sea, which stretches from the seaward edge of the German territorial coastal waters (12 mile zone) out to approximately 170 nautical miles away from it covering an area of approximately 28,600 km2. The study area includes the German Bight in the south as well as parts of the eastern Dogger Bank and the central North Sea in the north (Duck’s Bill). The depth generally increase from the coast (approx. 15 m) towards the central North Sea (approx. 60 m) with exception of the Dogger Bank, where station depths is about 30 m and the post-glacial valley of the river Elbe in the south, where station depth exceed 40 m. Sediments in the German EEZ generally consists of fine sand. Mud content is highest in the inner German Bight (up to 40 %) and lowest at the Dogger Bank and along the North Frisian coast (Fig. 6b). Coarser sediments occur only locally in areas such as the “Borkum Riffgrund”, “Amrum Bank” or the “Helgoländer Steingrund”.

Data and data processing

Species abundance of three datasets for fish, two for benthic epifauna and one for benthic infauna dataset were used to analyse community structure of the three faunal components in the German EEZ.

Fish was sampled with a 7-m beam trawl (B7) at 75 stations in late autumn 2009 as well as at 66 stations in late autumn 2010 by using a cod trawl (CT) both during the “German Autumn Survey in the Exclusive Economic Zone (GASEEZ)” with the RV Solea. Both gears were equipped with a codend liner of 20-mm mesh opening. The standard towing time was 30 min for the cod trawl and 15 min for the 7-m beam trawl at a target speed of 3.5–4 knots over ground. Abundance data of 32 species (B7) and 34 species (CT) were used for the analyses standardized to the allocated tow duration. In addition, abundance data of fish caught by a 2-m beam trawl (B2) at 52 stations during the third quarter “International Bottom Trawl Survey (IBTS)” in summer 1999 and 2000 were analysed. The 2-m beam trawl was fitted with a 20-mm net and a codend liner of 4-mm mesh size and towed at 1–2 knots for 5 min. A depth probe was attached to the beam trawl to determine the time and position of contact with the seabed. 2-m beam trawl data were standardized to a sampled area of 500 m2. Twenty-four fish species were included in the analysis. Pelagic fishes were excluded from all datasets.

Benthic epifauna data were taken from 2- and 7-m beam trawl hauls within the IBTS in 1999 and 2000 (57 species) and the GASEEZ in 2009 (62 species) (see fish data for gear description). The 2-m beam trawl samples were sieved over 5-mm mesh size, and the epifauna were separated from the remains. Most species were identified on board, while unidentified species were preserved in 4 % buffered formalin for identification in the laboratory. Epifauna from the 7-m beam trawl were directly identified and counted from the fisheries hauls on board of the RV Solea. Data were standardized to 500 m2 towed area (2-m beam trawl) and 15 min (7-m beam trawl), respectively. Generally, colonial species as well as infauna species were omitted from analyses, but the bivalves Euspira pulchella and Nucula nitidosa as well as the snail Corbula gibba were included in the 2-m beam trawl dataset since they were caught regularly due to the small codend liner of the trawl.

Benthic infauna data were taken from the “ICES North Sea Benthos Project 2000” dataset (Rees et al. 2007) consisting of 321 infauna species from 190 stations in the German EEZ sampled in 2000 and based on Rachor and Nehmer (2003). Sampling was carried out by collecting infauna with a 0.1-m2 van Veen grab, sieving over 1-mm mesh size and preserving the material in 4 % buffered formalin for identification in the home laboratories. All data were standardized to 1 m2. For a detailed description of sampling methods, see Rees et al. (2007).

Sediment (mud; <63 μm sieve fraction) as well as winter (December–February) and summer (June–August) bottom temperature data of the German EEZ were taken from the Senckenberg sediment database and the temperature database of the vTI-Institute of Sea Fisheries covering a period from 1998 to 2008.

Data analyses

Hierarchical cluster analysis and non-metric multidimensional scaling (MDS) in the PRIMER version 6 package (Plymouth Marine Laboratory) were used to separate groups of stations with similar community structure based on square-root- (fish) and fourth-root (benthic epi- and infauna)-transformed abundance data. Fourth-root transformation for benthic fauna was used to minimize the influence of dominant species, which was not necessary for fish data. SIMPROF test and an average similarity of at least 40 % were used as criteria for defining groups with similar community structure. SIMPROF is a permutation test looking for statistical significance of clusters in samples which are not a priori divided into groups (contrary to ANOSIM; see below). The PRIMER program SIMPER was used to identify species predominantly responsible for the similarity within groups. Similarities were calculated using the Bray–Curtis coefficient. ANOSIM randomization tests were performed to test the differences in community structure between the areas in the German EEZ (H0 = no differences in community structure). RELATE analyses within the PRIMER package were used to test similarity between the community structures of different faunal components and gears, respectively, based on the corresponding similarity matrices. Diversity was assessed by calculating species number and Shannon–Wiener Index (H′) which both were given as mean values of the corresponding community. Inverse distance weighted interpolation in ArcGIS 10 was used for mapping species number, sediments as well as late autumn/winter and summer bottom temperature in the German EEZ.

Results

In total, 53 demersal fish species (cod trawl, 7- and 2-m beam trawl), 93 epifauna species (7- and 2-m beam trawl) and 321 infauna species (0.1-m2 van Veen grab) were recorded and analysed.

Community structure

Fish was sampled with a 2- and 7-m beam trawl as well as a cod trawl, and corresponding communities in the EEZ are shown in Fig. 1a, c, e. ANOSIM randomization test revealed significant differences between all five communities identified (R = 0.59–0.83; p < 0.001). Similarity within clusters varied from 40 to 71 %. Two clear coastal communities were obvious for fish caught with the 7-m beam trawl but not for the other gears. Characteristic species predominantly found at the coast with the 7-m beam trawl were the goby Pomatoschistus spp. (Fig. 2a; Table 1), the hooknose Agonus cataphractus (Fig. 2b) or the sea snail Liparis liparis (Appendix 2, ESM), but also widespread species such as the dab Limanda limanda were counted among the dominant coastal species (Table 1). Similar species but in different abundances were characteristic for the transitional communities between the coast and the Oysterground, which were generally found for all gears. In contrast, the solenette Buglossidium luteum was frequently caught with the 2- and 7-m beam trawl only (Fig. 3a; Appendix 2, ESM). An Oysterground community resulted from the cod trawl and 7-m beam trawl hauls. The grey gurnard Eutrigla gurnardus was characteristic for the Duck’s Bill region and was predominantly caught with the cod trawl and the 7-m beam trawl (Fig. 4b). A Dogger Bank community was obvious in the cod trawl for the dab L. limanda, the whiting Merlangius merlangus and the gurnard E. gurnardus as characteristic species. These species occurred also in the adjacent Duck’s Bill community, but in lower abundances (Table 1; Appendix 2–4, ESM).
Fig. 1

Fish (a, c, e), epifauna (b, d) and infauna (f) communities in the German EEZ sampled with 7-m beam trawl (a, b), 2-m beam trawl (c, d), cod trawl (e) and 0.1-m2 van Veen grab (f). (Co coast, Oy Oysterground, Du Duck’s Bill, CoOy transitional community coast/Oysterground, Do Dogger Bank, El post-glacial valley of the river Elbe, CeDo central North Sea/Dogger Bank)

Fig. 2

Distribution and abundance of characteristic fish (a, b), epifauna (c, d) and infauna species (e, f) in coastal communities of the German EEZ. (ad sampled with 7-m beam trawl; e and f with 0.1-m2 van Veen grab)

Table 1

Mean abundance of characteristic species in the identified communities (SIMPER)

 

Coast

Oysterground

Duck’s Bill

Co

Co2

CoOy

CoOy2

Oy

Oy2

Du

Species

Mean abund.

Species

Mean abund.

Species

Mean abund.

Species

Mean abund.

Species

Mean abund.

Species

Mean abund.

Species

Mean abund.

Fish CT

 

 

 

 

L. limanda

43

L. limanda

8

L. limanda

97

 

 

L. limanda

278

 

 

 

 

 

A. cataphractus

14

M. merlangus

8

M. merlangus

33

 

 

M. merlangus

60

 

 

 

 

 

Pomatoschistus spp.

5

S. rostellatus

2

P. platessa

37

 

 

E. gurnardus

22

Fish B7

Pomatoschistus spp.

337

L. limanda

36

L. limanda

183

 

 

B. luteum

95

 

 

L. limanda

161

 

A. cataphractus

87

M. merlangus

7

B. luteum

102

 

 

P. platessa

54

 

 

A. laterna

25

 

L. limanda

40

P. platessa

11

A. cataphractus

51

 

 

A. laterna

30

 

 

E. gurnardus

8

Fish B2

 

 

 

 

Pomatoschistus spp.

95

B. luteum

16

 

  

 

L. limanda

5

 

 

 

 

 

B. luteum

50

L. limanda

4

 

  

 

Pomatoschistus spp.

3

 

 

 

 

 

L. limanda

17

A. laterna

2

 

 

 

 

A. cataphractus

1

Epi B7

L. holsatus

4,872

 

 

A. rubens

975

 

 

L. holsatus

160

N. norvegicus

112

L. holsatus

55

 

A. rubens

3,631

 

 

L. holsatus

649

 

 

A. rubens

298

L. holsatus

72

A. rubens

81

 

C. crangon

929

 

 

C. crangon

230

 

 

A. irregularis

75

B. lyrifera

69

Pagurus bernhardus

22

Epi B2

C. crangon

2,210

O. albida

2,582

A. rubens

87

 

 

A. irregularis

38

 

 

O. albida

167

 

O. ophiura

1,808

A. rubens

203

L. holsatus

6

 

 

A. rubens

27

 

 

P. bernhardus

30

 

A. rubens

200

P. bernhardus

9

P. bernhardus

13

 

 

P. bernhardus

21

 

 

A. rubens

11

Infauna

O. borealis

20

 

 

T. fabula

207

A. paucibranchiata

213

S. bombyx

96

A. filiformis

618

A. filiformis

843

 

N. longosetosa

7

 

 

M. johnstoni

324

Branchiostoma lanceolatum

137

M. johnstoni

103

C. gibba

273

Mysella bidentata

525

 

Nephtys cirrosa

14

 

 

S. bombyx

117

O. borealis

14

C. gibba

129

Pholoe baltica

18

S. bombyx

330

The communities at the Dogger Bank and the post-glacial valley of the river Elbe were excluded and given in the Appendix 1, ESM. Mean abundance is given per 15 min for cod trawl (CT) and 7-m beam trawl (B7), 500 m2 for 2-m beam trawl (B2) and 1 m2 for van Veen grab (VV)

Fig. 3

Distribution and abundance of characteristic fish (a, b), epifauna (c, d) and infauna species (e, f) in Oysterground communities of the German EEZ. (a and c sampled with 2-m beam trawl; b with cod trawl; d with 7-m beam trawl; e and f with 0.1-m2 van Veen grab)

Fig. 4

Distribution and abundance of characteristic fish (a, b), epifauna (c, d) and infauna species (e, f) in Duck’s Bill communities of the German EEZ. (a, b sampled with cod trawl; c with 7-m beam trawl; d with 2-m beam trawl; e, f with 0.1-m2 van Veen grab)

Epifauna analyses were carried out with 7- and 2-m beam trawl data (Fig. 1b, d). All clusters found were significantly different (ANOSIM; R = 0.70 and 0.87; p < 0.001) with an average similarity within clusters between 50 and 71 %. Analyses revealed clearly separated communities at the coast dominated by very high abundances of common German Bight species such as the seastar Asterias rubens (Fig. 2d), the swimming crab Liocarcinus holsatus (Fig. 2c), the shrimp Crangon crangon or the brittle star Ophiura albida (Table 1; Appendix 2 + 3, ESM). High abundances and a widespread distribution in the EEZ made these species characteristic for almost all communities in the EEZ as revealed by the SIMPER analyses. However, the distribution of other species was more locally restricted. For example, the auger shell Turritella communis (Fig. 3c) or the angular crab (Fig. 3d) were predominantly found in Oysterground communities with the 2- and 7-m beam trawl, respectively. High mean abundances of the Norway lobster Nephrops norvegicus or the sea urchin Brissopsis lyrifera caught with 7-m beam trawl were responsible for the separation of the Oysterground 2 cluster (Table 1; Appendix 2, ESM). The seastar Luidia sarsi (Fig. 4c) and the whelk Buccinum undatum on the other hand were predominantly found in Duck’s Bill or Dogger Bank communities.

Benthic infauna was sampled with a 0.1-m2 van Veen grab on a dense station grid resulting in eight well-separated communities (Fig. 1f). ANOSIM test shows a significant separation between communities (R = 0.70; p < 0.001). Similarity within communities generally exceeded 40 % (up to 52 %) with exception of the two transitional communities between coast and Oysterground (29 and 36 %). The coastal community was characterized, for example, by the polychaetes Ophelia borealis (Fig. 2f) and Nephtys spp., while the two transitional communities between coast and Oysterground were characterized, for example, by the bean-like tellin Tellina fabula (Fig. 2e) or the polychaetes Aonides paucibranchiata (Table 1; Appendix 4, ESM). A distinguished community in the inner German Bight was only found for benthic infauna dominated by the small bivalve N. nitidosa (Appendix 1 + 4, ESM). Boundaries between the two Oysterground communities were not clearly defined, while distinct differences in community structure were evident. The basket shell C. gibba (Fig. 3e) was a common species in both Oysterground communities, while the polychaetes Spiophanes bombyx (Fig. 4e) and Magelona johnstoni (Appendix 4, ESM) were characterizing the Oysterground 1 community. Exceptional high abundance of the brittle star Amphiura filiformis (Fig. 3f) was characteristic for the Oysterground 2 community (Table 1), which was even higher in the Duck’s Bill. High abundances of the polychaetes S. bombyx were found in the Duck’s Bill area especially in the Central North Sea/Dogger Bank region.

Analyses revealed that identified community structure largely depends on the catchability of the gears, which is an important issue for sampling design. For example, larger fishes such as the grey gurnard E. gurnardus or the whiting M. merlangus were insufficiently sampled with the 2-m beam trawl, while in contrast, the solenette B. luteum was under-represented in cod trawls. In comparison with the 2-m beam trawl, catchability of the 7-m beam trawl was higher for larger, burrowing epifauna such as the Norway lobster N. norvegicus or the angular crab Goneplax rhomboides. In contrast, catchability of the 2-m beam trawl was higher for small benthic species such as O. albida and T. communis. Most of these species largely influence community structure, and, for example, the epifauna community “Oysterground 2” as identified for 7-m beam trawl was not found for the 2-m beam trawl due the low catchability of this gear for species such as N. norvegicus.

Diversity patterns

Diversity patterns were different between faunal components, but were coinciding well between gears. Highest fish diversity (species number and H′) was generally found in southern regions of the EEZ, while contrary highest benthic diversity was found in the northern parts (Fig. 5; Table 2). However, differences in mean and total species number were low for fish and epifauna compared to benthic infauna. For example, thirteen fish species were caught in the coast/Oysterground region by using the 7-m beam trawl, while nine species were caught in the Duck’s Bill region with the same gear. In contrast, infauna species number was more than threefold lower at the coast compared to the Central North Sea/Dogger Bank region (Fig. 5; Table 2).
Fig. 5

Interpolated species number (inverse distance weighting) per sample/haul of fish (a, c, e), epifauna (b, d) and infauna (f) sampled with 7-m beam trawl (a, b), 2-m beam trawl (c, d), cod trawl (e) and 0.1-m2 van Veen grab (f)

Table 2

Mean diversity and abundance of fish, epifauna and infauna within the habitats identified with cluster analysis and MDS

 

Coast

Oysterground

Duck’s Bill

 

Co

Co2

CoOy

CoOy2

El

Oy

Oy2

Du

Do

CeDo

Fish CT

H′

 

 

1.8

1.7

 

1.6

 

1.4

0.9

 

sp. nr.

 

 

10

6

 

9

 

8

6

 

abun.

 

 

78

22

 

182

 

407

107

 

Fish B7

H′

2.0

2.5

2.3

  

2.2

 

1.7

  

sp. nr.

12

11

13

  

10

 

9

  

abun.

541

119

459

 

 

224

 

236

 

 

Fish B2

H′

 

 

1.7

1.4

 

 

 

1.0

  

sp. nr.

 

 

6

4

 

 

 

3

  

abun.

 

 

191

26

 

 

 

10

 

 

Epi B7

H′

1.9

 

1.8

  

2.0

1.6

2.5

  

sp. nr.

10

 

9

  

11

10

12

  

abun.

12,126

 

2,185

 

 

596

296

331

 

 

Epi B2

H′

1.7

1.0

1.8

  

2.2

 

1.8

1.7

 

sp. nr.

8

8

10

  

15

 

9

12

 

abun.

4,407

2,929

158

 

 

565

 

254

257

 

Infauna VV

H′

2.9

 

2.9

3.0

3.5

3.7

2.6

3.0

 

2.9

sp. nr.

14

 

27

18

31

28

24

35

 

46

abun.

230

 

1,865

1,046

1,933

874

1,262

2,992

 

2,781

H′ mean Shannon–Wiener index; sp. nr. mean species number; abun. mean abundance per region; highest values indicated in bold

Comparisons of community structures and habitat classification

The RELATE analyses were used to test the similarities between community patterns and to identify interrelationships between them. It was found that the spatial community structures of all faunal components were in most cases significantly correlated (Table 3). Exceptions were the community patterns of fish caught with the cod trawl and the 2-m beam trawl, as well as fish (CT) and epifauna (B2), which is largely due to the low spatial fit of stations in these datasets. Highest correlations were found between epifauna and fish caught with the 7-m beam trawl (ρ = 0.67; p < 0.001) as well as epifauna (B7) and fish (B2) (ρ = 0.55; p < 0.001). Correlations between benthic infauna patterns and the other faunal components were generally low, which might be due to the very high sampling resolution of the benthic infauna dataset. However, despite of the different sampling resolution of datasets, it became obvious that number of identified communities generally increased from fish to benthic infauna (at the same level of similarity within clusters) which corresponds to an increasing species number from fish to benthic infauna (Fig. 5). Additionally, the importance of small-scale sediment characteristics as well as mobility decreases from fish to benthic infauna which also influences community structure largely (see discussion).
Table 3

Correlation coefficients (Rho) relating the similarity matrices of the different communities (RELATE)

 

Fish B2

Fish CT

Fish B7

Epi B2

Endo

Epi B7

0.55*

0.33*

0.67*

0.30*

0.46*

Endo

0.31*

0.25*

0.27*

0.44*

 

Epi B2

0.22*

0.24

0.35*

  

Fish B7

0.52*

0.50*

   

Fish CT

0.29

    

Significance level p < 0.001 is indicated by *

Although small-scale differences in community structure were found especially for benthic infauna, a general separation into a coastal, an Oysterground and a Duck’s Bill community was evident for all three faunal components (Fig. 1; roughly sketched in Fig. 6), which is largely based on the distribution and abundance of characteristic species. Dominant species in these communities were, for example, the goby Pomatoschistus spp., the grey gurnard E. gurnardus, the swimming crab L. holsatus, the seastar A. rubens or the polychaetes S. bombyx and O. borealis (Figs. 2, 3, 4). The spatial patterns of community structure largely correspond to abiotic habitat characteristics as reviewed in Table 4 and shown in Fig. 6. Especially bottom temperature variation between summer and late autumn/winter largely differed between the coast, the Oysterground and the Duck’s Bill with highest variation at the coast (12 °C) and lowest variation in the Duck’s Bill (3–4 °C) from 1998 to 2008. Lowest late autumn/winter bottom temperatures (1.98 °C) and highest summer bottom temperatures (18.48 °C) were recorded at the coast in 2003 and 1999, respectively. In general, the regions follow an increasing gradient of bottom temperature in late autumn/winter and a decreasing one in summer, from the coast to the Duck’s Bill (Fig. 6; Table 4). Salinity, length of thermal stratification and strength of residual currents also increased from the coast to the Duck’s Bill, while tidal stress, sedimentation rate and sediments parameter such as total organic carbon and chlorophyll a decreased with distance from shore (Table 4).
Fig. 6

Location and depth of the German (EEZ) in the North Sea (bold lines are suggested habitat boundaries; grey areas are Natura 2000 sites) (a). Percentage mud (<63 μm sieve fraction) of sediments in the German EEZ (b). Summer (c) and late autumn/winter (d) bottom temperature in the German EEZ (bd were interpolated by using “inverse distance weighting”)

Table 4

Habitat characteristics at the coast, the Oysterground and the Duck’s Bill

 

Coast

Oysterground

Duck’s Bill

 

TOC (sediment)

High

Moderate

Low

Kröncke et al. (2004), Reiss and Kröncke (2005), Stöck and Kröncke (2001)

Chl a (sediment)

High

Moderate

Moderate to high

Kröncke et al. (2004), Reiss and Kröncke (2005), Boon and Duineveld (1998), Stöck et al. (2002)

Mud content

High

Low to moderate

Low

Kröncke et al. (2004), Reiss and Kröncke (2005), Stöck et al. (2002)

Sedimentation rate

High

Moderate

Low

Kröncke et al. (2004), Stöck et al. (2002)

Tidal stress

High

Moderate

Low

Becker et al. (1992), Dippner (1993)

Summer bottom temperature

High

Moderate

Low

Neumann et al. (2009), Ehrich et al. (2007)

Winter bottom temperature

Low

Moderate

High

Neumann et al. (2009), Ehrich et al. (2007)

Salinity

Low

Moderate

High

Becker et al. (1992), Ehrich et al. (2007)

Length of thermal stratification

Low

Moderate

High

Neumann et al. (2009), Becker et al. (1992);

Residual currents

Low

Moderate to high

Moderate to high

Becker et al. (1992)

Discussion

This study revealed a general separation of fish, epifauna and infauna communities in the German EEZ into a coast, an Oysterground and a Duck’s Bill community, which coincided well with large-scale abiotic characteristics of the German EEZ. Gradients of temperature, salinity, stratification, tidal stress as well as total organic carbon (TOC) and chlorophyll a were found in the German EEZ, which correspond to these three communities and seem to have a higher influence on community structure than, for example, biotic interactions on that spatial scale. Thus, we conclude that the coast, the Oysterground and the Duck’s Bill were common habitats, which were distinguishable by their abiotic characteristics and associated biological communities (Fig. 2).

The coastal habitat is characterized by water masses, which are largely influenced by fresh water run-off from rivers resulting in low salinity and high nutrient input (Continental Coastal Water; according to Laevastu 1963). Additionally, water in the coastal habitat is well mixed throughout the year beneath the 20–30-m depth contour (Becker et al. 1992) resulting in high seasonal temperature variations (Fig. 6). As a consequence, species in coastal habitats were more strongly affected by extreme climatic events such as cold winters, but were also better adapted to strong seasonal temperature variations (Reiss et al. 2006b; Neumann et al. 2009). Species commonly found in the coastal habitat such as gobies, the pipefish Syngnathus rostellatus or the brittle star O. albida are known to have a high tolerance towards temperature and salinity variation (Ursin 1960; Knijn et al. 1993). High nutrient input, together with a relatively long residence time of the water masses in the coastal habitat, could also result in intense algal blooms and, therefore, in increased food supply for benthic fauna (Dauwe et al. 1998; Stöck and Kröncke 2001). Generally, most abiotic habitat characteristics changed gradually from the coast towards the Duck’s Bill area (Table 4). For example, length of summer stratification increased towards the Duck’s Bill, where a stable thermal stratification occurs from May to September. Water masses (central North Sea water) in the Duck’s Bill habitat were characterized by lower seasonal temperature variation as well as medium salinity and nutrient concentration (Laevastu 1963; Becker et al. 1992). Furthermore, stratification processes inhibited sedimentation of organic matter to the bottom and vice versa input of nutrients from bottom waters into upper layers, which resulted in a decreasing trend of TOC and chlorophyll a (Table 4), and hence food supply especially for benthic infauna species, from the coast to the Duck’s Bill (Kröncke et al. 2004). Most abiotic habitat characteristics and especially temperature (Fig. 6) exhibit strong seasonal variability, which largely differ between the habitats. Thus, it is assumed that the differences in the seasonal variability with respect to many abiotic habitat characteristics are the most important factor discriminating the habitats coast, Oysterground and Duck’s Bill.

The three habitats coast, Oysterground and Duck’s Bill are the major habitats common for demersal fish, epifauna and infauna in the German EEZ. However, it should be noted that these habitats were rather confined by gradual transitions than by conspicuous boundaries, which is supported by transitional communities found in this study. Additionally, small-scale habitats were obvious for single faunal components (or even species) since the importance of habitat characteristics depends on the spatial scale (Menge and Olson 1990) and on the faunal component (or species) under consideration (e.g. due to different mobility). Spatial variability of benthic infauna, for example, was often linked to sediment characteristics, which were related to food supply (Künitzer et al. 1992; Kröncke 2006). Sediments in the German EEZ are heterogeneous distributed consisting mainly of terrigenous sand, mud or a mixture of both (“Sublittoral sand” and “Sublittoral mud” after EUNIS classification 5.2 and 5.3). Locally, areas of morainic origin such as the “Borkum Riffgrund” or the “Helgoländer Steingrund” occur in the German EEZ, where also pebbles and boulders were found (EUNIS 5.1 “Sublittoral coarse sediment” and 4.7 “circalittoral rock”). This small-scale habitat heterogeneity within our three habitats provided also the basis of the selection of the Natura 2000 sites “Borkum Reef Ground”, “Dogger Bank” and “Sylter Outer Reef” in the North Sea (Fig. 6), where a total of 2,322 km2 of the habitat type “sandbanks” and 176 km2 of the habitat type “reefs” were located (Pedersen et al. 2009). Small-scale habitat heterogeneity resulted in particular community structures in this study, for example, the Dogger Bank, where the largest area of “sandbanks” in the EEZ is located (Fig. 1; Appendix 1, ESM) or the inner German Bight, where high abundances of the benthic infauna species N. nitidosa were found, which is a typical indicator for muddy sediments (Rachor 1980). Mud content of sediment also influenced the distribution of the Norway lobster N. norvegicus and the angular crab G. rhomboides (unpublished data), which both were tube-building species characteristic for specific areas in the Oysterground habitat. Additionally, the basket shell C. gibba, which revealed a similar distribution as the Norway lobster in the Oysterground, were often related to muddy, organically enriched sediments (Holmes and Miller 2006). However, with exception of the infauna dataset, the sampling resolution of this study was too coarse to analyse community structure of small-scale habitat types such as “reefs”. On the other hand, the importance of small-scale habitat types for the geographical limits of communities is decreasing with increasing mobility of species (generally increasing from benthic infauna to fish).

Habitat stability

A central question, for example, for management approaches is whether habitats are stable over time.

Kröncke et al. (2011) found no fundamental shifts for benthic infauna communities in the last decades on North Sea wide scale even if single species such as N. nitidosa slightly shifted their core distribution. This seems to be true also for the German EEZ, because Rachor and Nehmer (2003) found similar patterns to those described by Salzwedel et al. (1985) in the 1980s and Hagmeier (1925) in 1920s, indicating that no considerable and permanent changes of infauna community structure occurred over a period of almost 80 years. This might be partly explained by the comparatively stable sediment distribution in the EEZ, which is a more important habitat characteristic for benthic infauna than for other faunal components (Callaway et al. 2002; Schratzberger et al. 2006). Otherwise, it is reasonable that the general community structure of fish, epifauna and infauna characterizing the habitats coast, Oysterground and Ducks Bill remained rather stable over time since abiotic habitat characteristics such as different strength in seasonality of, for example, temperature have a larger influence on the general community structure than, for example, gradual warming of the water column due to climate change. However, contrary to communities distribution of single species was not stable but dynamic on seasonal and annual timescales. Many species revealed seasonal migration to avoid unfavourable temperatures in winter, while the spatial extend of this migration largely depends on the mobility of species (decreasing from fish to benthic infauna). For example, abundance of the grey gurnard E. gurnardus changed considerably between seasons with high abundances in the western part of the central North Sea in winter and high densities in the southern Bight in summer (Knijn et al. 1993). Seasonal migration between spawning and feeding grounds is also well known for the plaice Pleuronectes platessa (Knijn et al. 1993; van Keeken et al. 2007) and might partly explain the different distribution patterns of the plaice found in this study. Shrimps such as C. crangon are known to migrate seasonally between shallow coastal water (summer) and deeper offshore water (winter) to avoid unfavourable winter conditions (Boddeke 1976; Temming and Damm 2002). Not only temperature, but also other abiotic habitat characteristics were changing seasonally such as onshore wave stress, which increases in winter and is suggested to trigger the seasonal migration of the seastar Astropecten irregularis into deeper water (Freeman et al. 2001).

Habitat characteristics are changing also on long-term temporal scales. Beare et al. (2002) found an increase in late winter temperature (January, February) of ca. 1.1 °C in the German Bight between the early 1950s and the late 1990s. Additionally, salinity rose and stratification intensity decreased east of ca. 5°E. Increasing temperature in the German Bight resulted in small-scale distribution shifts of demersal fish species such as P. platessa, B. luteum and Arnoglossus laterna (van Keeken et al. 2007; van Hal et al. 2010), which dominated several communities found in this study. As a consequence, management tools such as the “Plaice Box” (a coastal area closed for fishing to protect young plaice) lose effectiveness since juvenile plaice shifted its distribution towards more offshore waters (van Keeken et al. 2007). Ehrich et al. (2007) found that demersal fish communities in the German Bight shifted from a gadoid-dominated community to a flatfish-dominated community in a period from 1987 to 2005. Distribution shifts in a sense of natural range expansion of, for example, southern species into the German EEZ were also found in the last decades. Recently, the angular crab G. rhomboides extended its distribution from the eastern Atlantic to the southern North Sea (Neumann et al. 2010) and also southern fish species such as the tub gurnard Trigla lucerna, the red mullet Mullus surmuletus and the pilchard Sardina pilchardus were now regularly found in the German Bight (Ehrich and Stransky 2001; Beare et al. 2004; Ehrich et al. 2007). In contrast, Kröncke et al. (2011) found no indications for range expansions of non-native benthic infauna species by a comparison of infauna communities between 1986 and 2000 on a North Sea wide scale. So far, these climate-related effects influenced only single species rather than communities as a whole. Additionally, climate change effects were rather expressed as changes in abundance of species in the EEZ habitats, which were, for example, related to temperature-mediated increase in primary production and, thus, food supply for benthos (Kröncke et al. 1998; Neumann et al. 2009; Kröncke et al. 2011). However, the coastal habitat was more sensitive to climate-related temperature changes compared to the more stable and stratified habitats Oysterground and Duck’s Bill. On the one hand, the effects of extreme climatic events such as cold winters were more pronounced in the well-mixed coastal habitat than in more stable offshore habitats (Reiss et al. 2006b; Neumann et al. 2009). Cold winters influence benthic fauna through enhanced mortality and reduced reproduction and production. These effects were observed as a reduced number of species as well as decreased diversity, biomass and secondary production (Ziegelmeier 1970; Buchanan and Moore 1986; Beukema 1992; Kröncke et al. 1998). Additionally, mass occurrences of r-selective species such as epibenthic brittle star O. albida were related to cold winter temperatures (Neumann et al. 2009). The effects of such extreme events influenced habitats for several years, and recovery time of communities in disturbed habitats was found to be 2–5 years for benthic infauna and 7–8 years for benthic epifauna (Schröder 2003; Neumann and Kröncke 2011). On the other hand, cold winters only rarely occurred in the last decade and increasing sea surface temperature has more direct effects on bottom living species in the coastal habitat due to the mixed water column. Consequently, it can be assumed that the coastal habitat will be more affected by climate change effects in future compared to the Oysterground and Duck’s Bill habitat.

Acknowledgments

We thank the captains and crews of RV “Walther Herwig III” and “Solea” for their assistance during sampling. The present study was conducted at the Biodiversity and Climate Research Centre (BiK-F), Frankfurt a.M. and financially supported by the research funding programme “LOEWE –Landes-Offensive zur Entwicklung Wissenschaftlich-ökonomischer Exzellenz” of Hesse’s Ministry of Higher Education, Research and the Arts.

Supplementary material

10152_2012_334_MOESM1_ESM.pdf (9 kb)
Supplementary material 1 (PDF 9 kb)
10152_2012_334_MOESM2_ESM.pdf (703 kb)
Supplementary material 2 (PDF 702 kb)
10152_2012_334_MOESM3_ESM.pdf (233 kb)
Supplementary material 3 (PDF 233 kb)
10152_2012_334_MOESM4_ESM.pdf (339 kb)
Supplementary material 4 (PDF 339 kb)

Copyright information

© Springer-Verlag Berlin Heidelberg and AWI 2012

Authors and Affiliations

  • Hermann Neumann
    • 1
  • Henning Reiss
    • 1
    • 3
  • Siegfried Ehrich
    • 2
  • Anne Sell
    • 2
  • Kay Panten
    • 2
  • Matthias Kloppmann
    • 2
  • Ingo Wilhelms
    • 2
  • Ingrid Kröncke
    • 1
  1. 1.Marine Research DepartmentSenckenberg am MeerWilhelmshavenGermany
  2. 2.Johann Heinrich von Thünen InstituteInstitute of Sea FisheriesHamburgGermany
  3. 3.Faculty of Biosciences and AquacultureUniversity of NordlandBodøNorway