© 2004 by ICES/CIEM International Council for the Exploration of the Sea/Conseil International pour l'Exploration de la Mer
Comparative ecology of over-wintering Calanus finmarchicus in the northern North Atlantic, and implications for life-cycle patterns
a Marine Laboratory PO Box 101, Victoria Road, Aberdeen, AB11 9DB, Scotland, UK
b University of Aberdeen, Department of Zoology Tillydrone Avenue, Aberdeen AB9 2TN, Scotland, UK
c Marine Research Institute Skulagata 4, PO Box 1390 Reykjavik, Iceland
d University of Strathclyde, Department of Statistics and Modelling Science Glasgow G1 1XH, Scotland, UK
e Department of Fisheries and Oceans, Ocean Science Division, Bedford Institute of Oceanography PO Box 1006, Dartmouth, Nova Scotia B2Y 4A2, Canada
f Danish Institute for Fisheries Research Kavalergaarden 6, Charlottenlund, DK-2920 Denmark
g Plymouth Marine Laboratory Prospect Place, West Hoe, Plymouth PL1 3DH, England, UK
h Southampton Oceanography Centre, George Deacon Division Waterfront Campus, Empress Dock, Southampton SO14 3ZH, England, UK
i IPRC/SOEST, University of Hawaii POST Bldg. 409, 1680 East West Road, Honolulu, HI 96822, USA
j Department of Marine Ecology, University of Aarhus Finlandsgade 14, DK 8200 Aarhus, Denmark
*Correspondence to M. R. Heath: tel: +44 1224 876544; fax: +44 1224 295511. e-mail: heathmr{at}marlab.ac.uk.
Data from plankton net and Optical Plankton Counter sampling during 12 winter cruises between 1994 and 2002 have been used to derive a multi-annual composite 3-D distribution of the abundance of over-wintering Calanus finmarchicus in a swath across the North Atlantic from Labrador to Norway. Dense concentrations occurred in the Labrador Sea, northern Irminger Basin, northern Iceland Basin, eastern Norwegian Sea, FaroeShetland Channel, and in the Norwegian Trench of the North Sea. A model of buoyancy regulation in C. finmarchicus was used to derive the lipid content implied by the in situ temperature and salinity at over-wintering depths, assuming neutral buoyancy. The FaroeShetland Channel and eastern Norwegian Sea emerged as having the highest water column-integrated abundances of copepodites, the lowest over-wintering temperature, and the highest implied lipid content. The results are discussed in the context of spatial persistence of populations, seasonal patterns of abundance, and relationships between over-wintering and lipid accumulation in the surface waters.
Keywords: Iceland Basin, Irminger Sea, Labrador Sea, lipid, net sampling, Norwegian Sea, Optical Plankton Counter, vertical distribution, zooplankton
| Introduction |
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Ocean-basin-scale information on the spatial distribution of Calanus finmarchicus has largely been derived from the Continuous Plankton Recorder (CPR) surveys (Matthews, 1969; Planque et al., 1997). However, these data reflect only the distribution in the surface waters, while the winter distribution, when the copepodites are far below the depth of the CPR, may more effectively delineate the persistent population structures (Bryant et al., 1998).
The winter dormancy phase of C. finmarchicus, which may involve a diapause state, has been well documented (see review by Hirche, 1996). Development is arrested during copepodite moult stages IV and V in the late summer and autumn and the animals then descend out of the surface waters to, it is assumed, some neutral buoyancy depth that, in the open ocean, is typically between 500 and 1500 m. Arousal from diapause and the moult transition to copepodite stage VI does not take place until late winterearly spring of the following year. Stage VI copepodites migrate to the surface to begin spawning (Heath, 1999; Gislason and Astthorsson, 2000). Low temperature, avoidance of predators, and limited parasite infection have been suggested as factors conferring high survival probability on dormant animals over-wintering at depth (Kaartvedt, 1996).
Less well documented are the ocean-basin-scale patterns of distribution and properties of over-wintering stages. Regional studies have identified accumulations in pits and trenches in continental shelf regions (e.g. Durbin et al., 1995), in fjords with relatively limited exchange between the bottom waters and the open sea (e.g. Hirche, 1983), and at depths of 5002000 m at various locations in the ocean (e.g. Hirche, 1996). Heath et al. (2000a) collated data from depth-resolved plankton samples collected during a number of regional surveys in the mid to late 1990s to map the large-scale 3-D distribution of over-wintering C. finmarchicus in the shelf and ocean waters of the Northeastern Atlantic. Here, we extend this synthesis by including material collected since 1999 from previously unsurveyed areas to map a swath across the northern North Atlantic, from Labrador in the southwest to northern Norway in the northeast. At these scales, the data begin to complement the CPR in spatial coverage, although they are still a multi-annual composite. Nevertheless, we can begin to discern basin-scale structure in the over-wintering population that may help to account for seasonal and spatial dynamics elucidated from the surface water CPR data.
| Materials and methods |
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The survey area and sampling locations are shown in Figure 1. Sampling was carried out from the RV "Dana" (Danish Fisheries Research Institute), RV "Bjarni Sæmundsson" (Marine Research Institute, Iceland), RV "Scotia" (Fisheries Research Services, Scotland), RV "Hudson" (Department of Fisheries and Oceans, Canada), and RV "Discovery" (Natural Environment Research Council, UK) between 1994 and 2002 (Table 1). A few additional data were available from the database of the EU-funded Trans-Atlantic Study of Calanus (TASC) (http://calanus.nfh.uit.no/TASC.HTML) arising from time-series sampling in 1997 at Ocean Weather Station (OWS) "Mike" (Institute of Marine Research, Bergen), an oil rig in the northern North Sea and a coastal site off eastern Scotland (Fisheries Research Services, Scotland), the Westmann Islands off southern Iceland (Marine Research Institute, Iceland), and off the Faroe Islands (Faroese Fisheries Laboratory). The data used for the project were all collected in November or December, with the exception of one survey in the FaroeShetland Channel in January 1995.
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Plankton were sampled with various versions of the ARIES system (Dunn et al., 1993) towed from "Dana", "Scotia", and "Discovery", and with a vertically hauled multi-net from "Bjarni Sæmundsson" (Gislason and Astthorsson, 2000), "Hudson", and at OWS Mike. At the coastal TASC time-series sites, samples were collected with vertically hauled bongo nets (Heath et al., 2000b). All net systems collected plankton with a 200-µm mesh. ARIES and multi-net systems collected plankton from discrete depth layers (4060-m depth intervals with ARIES, 100200-m intervals with the multi-net) between a maximum of 3000 m and the surface. In addition, the ARIES system also carried an Optical Plankton Counter (OPC; Focal Technologies Inc, Canada; Herman, 1992), a CTD (Sea-Bird Electronics 911+), and a water-sampling rosette. CTD data were collected by separate lowered casts from "Bjarni Sæmunsson" and "Hudson". The OPC data were logged as integrated particle counts over 30- or 60-s time intervals (approximately equivalent to 1020-m depth intervals) and 40-µm intervals of Equivalent Spherical Diameter (ESD) during each deployment. Further details concerning the operation of the ARIES and OPC systems were given by Heath and Jónasdóttir (1999).
Most plankton were preserved in buffered 4% seawaterformaldehyde solution and subsequently sorted under microscopes to enumerate Calanus species and moult stages. During surveys by "Discovery", subsets of samples were also preserved in alcohol for molecular taxonomy analysis. From the microscope analysis of samples, the total numbers of specimens per sample were converted to concentration per m3 of water using flowmeter data.
The same core team of microscopists was responsible for the analysis of formaldehyde preserved samples from the "Dana", "Scotia", and "Discovery" surveys. Different teams analysed the "Bjarni Sæmunsson" and "Hudson" samples. Given the stage composition of the populations, C. hyperboreus was readily distinguishable from other Calanus species on a range of criteria. Stage CIV, CV, and female CVI of C. finmarchicus were distinguished from C. helgolandicus by examination of the head shape and the curvature of the inner edge of the basal segment of the fifth leg. Male CVI of the two species was discriminated on the basis of the relative lengths of the endopod and exopod of the fifth leg. C. glacialis could be microscopically distinguished from C. finmarchicus only on the basis of carapace length measurements, as described by Hirche (1991).
Alcohol-preserved samples collected aboard "Discovery" were sorted into developmental stages and visually distinguishable species. Specimens of these categories from each sample were then analysed using an MWG Roboseq 4204 robotic workstation and a modification of the method of Lindeque et al. (1999) to provide a molecular identification to species. The system involves amplification of a region of the 16S rRNA gene using the Polymerase Chain Reaction (PCR) followed by Restriction Fragment Length Polymorphism (RFLP) analysis of the amplified product (Lindeque et al., in press).
To date, not all of the net samples collected on the cruises included in the study have been analysed (Table 1). In the cases where no net analyses were available, OPC data were used to provide estimates of the concentration of C. finmarchicus. The OPC does not discriminate between plankton and detrital particles of equivalent size, but Heath et al. (1999b, 2000a) developed a procedure for calibrating OPC data to estimate numbers of stage CIVCV C. finmarchicus. For this project, the calibration coefficients given by Heath et al. (2000a) were applied to the OPC data:
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| Spatial synthesis of stage abundance data |
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Combined data on C. finmarchicus stage CIV plus CV from net catches and calibrated OPC data, where appropriate from all 12 surveys and TASC time-series sites, were averaged over 200-m depth intervals at each sampling station. The concentrations (m3) in each 200-m-thick layer were then gridded horizontally to 15' longitude x 7.5' latitude resolution using an inverse distance algorithm in SURFER. The 15 gridded layers in the range 03000 m were then vertically integrated at each horizontal node, taking account of the seabed depth. Seabed topographic data were assembled from 5' resolution values from the US National Geophysical Data Centre (http://www.ngdc.noaa.gov/mgg/global/seltopo.html). The resulting 2-D data represented the abundance (m2) of C. finmarchicus at each grid node.
| Vertical structure and linkage to hydrographic data |
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Centile depth horizons were used to parameterize the vertical structure of C. finmarchicus abundance. For example, 17% of the water column-integrated population was to be found between the sea surface and the 17th-centile depth. The 50th-centile depth was referred to as the median depth; 66% of the population were to be found between the 17th and 83rd centile depths.
Centile depths were derived for each developmental stage in each individual profile of C. finmarchicus concentration obtained with ARIES, multi-net, or OPC systems. This was performed by digitizing the stage profiles to 2-m-depth resolution, assuming that concentrations were uniformly distributed over the depth integration interval of each net or OPC sample. Given centile depths were then estimated by integration from the sea surface. For plankton profiles with associated CTD data (which was almost all profiles), the in situ pressures, temperatures, and salinities at centile depths were estimated by averaging the CTD data over ±2 m of each centile.
Estimating the lipid content implied by the hydrographic conditions at centile depths
The very low levels of swimming activity observed in freshly sampled diapause specimens of C. finmarchicus (Hirche, 1983; Ingvarsdottir, 1998) suggest that these stages have little active control over their vertical location, and their vertical distribution is a product of their buoyancy and rates of vertical mixing. Visser and Jónasdóttir (1999) presented a model of buoyancy control in diapausing copepods, which depended on the fact that the thermal expansivity and compressibility of wax ester, which constitutes most of the storage lipid in C. finmarchicus, is higher than that of seawater. As a result, copepodites that are positively buoyant in warm shallow water can become neutrally buoyant in cold deep water, but have to actively swim down to their neutral buoyancy depth rather than sink passively. Visser and Jónasdóttir used the model to derive neutral buoyancy depths and spring ascent rates of copepods given temperature and salinity profiles and lipid contents. Here, we use the model inversely to estimate the lipid content of copepods implied by given pressure, temperature, and salinity, assuming neutral buoyancy.
Visser and Jónasdóttir assumed that the copepod body is composed of lipid of density
L, water of density
W, and other material of density
O. The density of water within the copepod
W is assumed to be the same as that outside and, hence, a function of ambient pressure, temperature, and salinity, while
L is a function of ambient temperature and pressure only (equation 2 in Visser and Jónasdóttir, 1999). The mass ratio of lipid to lipid-free dry weight is then:
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O is problematic. Some of this material will be protein which has a relatively high density, such that small variations in protein content can significantly affect the lipid-free dry density. Visser and Jónasdóttir (1999) estimated
O to be 1080 kg m3 from settling experiments on previously frozen specimens, but assumed a value of 1240 kg m3 to be representative of deep over-wintering animals based on a typical protein content of 45% of dry weight. However, Ingvarsdottir (1998) found that for C. finmarchicus in the FaroeShetland Channel the seasonal minimum of protein content (20% of dry weight) occurred in winter diapause stages, and that values of >35% were restricted to the summer period. Hence, an appropriate value of
O for winter copepodites is probably towards the lower end of the range offered by Visser and Jónasdóttir (1999). | Direct measurements of lipid content and body weight |
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Jónasdóttir (1999) described the procedures for measuring lipid composition and content and dry mass of C. finmarchicus specimens collected during "Dana" surveys in December 1994 and January 1995. Equivalent measurements were performed on material collected during the survey in November and December 1996. Very briefly, as soon as possible after recovery of the sampling nets, groups of up to 10 stage CV specimens were sorted from the catch in depth layers selected on the basis of the OPC data, and preserved in liquid nitrogen. Later, lipids were extracted in chloroform/methanol, and analysed by Thin layer Chromatography/Flame Ionization detection using an Iatroscan MK-5. Lipid composition was estimated chromatographically to distinguish in particular wax ester (WE) and tracylglycerol (TAG). Carapace length was measured on specimens from each sample and subsequently transformed to an estimate of total dry mass using calibration relationships established for each survey by freeze drying and weighing batches of 310 measured specimens.
| Results |
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Species identification
The molecular analysis of samples from the "Discovery" survey in 2001 showed that the microscopists' identification of C. finmarchicus was 100% correct, except at two stations on the East Greenland slope. In this area, 4.5% of specimens identified by microscopists as C. finmarchicus were in fact C. glacialis. The molecular methodology did not reveal any misidentification of C. helgolandicus, although the areas covered by "Discovery" were not those where we would have expected this species to form a significant component of the community.
Composite distribution of C. finmarchicus
The population of C. finmarchicus was aggregated into five main centres each with depth-integrated abundance >15 000 m2. These were located in the Labrador Sea, northern Irminger Basin, northern Iceland Basin, FaroeShetland Channel/eastern Norwegian Sea, and a small patch in the Norwegian Trench of the eastern North Sea. The highest abundances (>40 000 m2) were located in the FaroeShetland Channel and Norwegian Sea (Figure 2). The Rockall Basin contained very low abundances. A plume of locally high abundance was present to the southwest of the Faroe Islands, coinciding with the area where deep overflow water from the FaroeShetland Channel enters the Atlantic through the Faroe Bank Channel and flows westwards along the southern face of the IcelandScotland Ridge (Hansen, 1985; Heath and Jónasdóttir, 1999).
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The stage composition of the depth-integrated populations in the different basins was investigated by aggregating data from deployments falling within a set of nine rectangular compartments located in the major basins and/or over-wintering centres (Figure 2). The populations in the different regions were all similar in that stages CIV, CV, and CVI female copepodites accounted for >99% of the copepodite population. However, the contributions of these three stages varied between regions (Figure 3). The proportion of stage CV decreased, and that of CIV increased, from west to east. Thus, the population in the Labrador Sea comprised >90% CV, while in the Rockall Basin the population was made up of 40% CIV and almost 60% CV. Stage CVI females occurred at >4% only in the Labrador Sea and Norwegian Sea. No net sample analyses from the Norwegian Trench were available for comparison.
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Regional variations in depth below the sea surface and altitude above the seabed of CIV, CV, and CVI female stages were further resolved from the compartmentalized station data. These results (Figure 4) showed clearly the differences between basins of the North Atlantic. The vertical distribution tended to be broad and deep in the Atlantic basins south of the GreenlandScotland Ridge, and narrow and shallow in the Subarctic areas (Norwegian Sea and FaroeShetland Channel) and in the Labrador Sea. In general, stage CVI females tended to be deeper than CV, which in turn were deeper than CIV, though this was not the case in all areas. The altitude of copepodites above the seabed also varied greatly. The 83rd centile depth was >2000 m above the seabed in the Labrador Sea (water depth 3400 m), but only 100 m in the FaroeShetland Channel (water depth 1180 m).
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Despite the large differences in depth distribution, copepodites in the Iceland Basin and west of the Mid-Atlantic Ridge all occupied a temperature range of 36°C and a salinity of approximately 34.9. The population in the Norwegian Trench and the small numbers of C. finmarchicus in the Rockall Basin experienced the warmest and most saline conditions of all (79°C and 35.235.3 salinity). In contrast, copepodites north of the IcelandScotland Ridge and in the FaroeShetland Channel were located in much colder water of between +0.5 and 0.5°C.
The lipid contents implied by the pressure, temperature, and salinity at centile depths, assuming a lipid-free dry density of 1080 kg m3 and that over-wintering copepodite stages were neutrally buoyant, are shown in Figure 4. The Norwegian Sea, FaroeShetland Channel and Labrador Sea emerged as supporting copepodites with the highest implied lipid content per unit body weight. The Rockall Basin contained copepodites with smallest implied reserves of lipid. Absolute values of the implied lipid content were dependent on the assumed value of lipid-free dry density, but the relative distribution in space was largely unaffected. Taking the data from all of the sampling locations into account rather than just those within the nine compartments showed the extent of the lipid-rich region in the Norwegian Sea and FaroeShetland Channel (Figure 5). Copepodites in the slope and shelf waters of the Eastern Atlantic were implied to have the lowest lipid content.
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Measurements of WE, TAG content, and body mass for stage CV C. finmarchicus collected from a range of depths at 109 sampling locations during three cruises in the Northeastern Atlantic ("Dana" December 1994, January 1995, November/December 1996) were available for comparison with the implied lipid content. Samples from depths falling between the 17th and 83rd centiles of the vertical distribution of the CV population at each sampling site were selected from the data set. Of these, samples in which the TAG content as a proportion of WE + TAG exceeded 1% were rejected on the grounds that these could represent specimens in which gonad development and emergence from diapause had commenced and, hence, the neutral buoyancy assumption might not be applicable. Most of the samples rejected on the basis of TAG content came from late in the January 1995 survey. The remaining data comprised specimens from 46 sampling depths at 34 stations in an area centred on the IcelandScotland Ridge and including the maximum contrast in the implied lipid content (Figure 5). The means and ranges of measured WE/total weight were then related to the implied lipid/total weights at the median depths and the ranges over the 17th to 83rd centiles (Figure 6). There was a significant relationship between measured and implied lipid content (r2=0.24, p<0.005) when assuming a low value for the lipid-free dry density (
= 1080 kg m3), although the values conformed to 1:1 proportionality only at low levels of measured lipid content. If a higher value of lipid-free dry density was assumed (
= 1240 kg m3), then the relationship was weaker (r2=0.11, p<0.05) and the values conformed to 1:1 proportionality only at higher levels of measured lipid content. The implication is that while lipid content explains a significant part of the variation in observed depth distributions, variations in the lipid-free dry density, most likely related to protein content, may also be involved. The expectation would be that lipid and protein contents should be directly related.
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| Discussion |
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In this study, we have assembled data collected mainly between mid-November and late December, but from eight different years, and generally different regions in each year, in order to produce a composite interpretation of the large-scale distribution and properties of over-wintering C. finmarchicus. The high costs and technical difficulties associated with sampling in the North Atlantic at this time of year are such that piecing together data in this way is currently the only means of interpreting basin-scale patterns of abundance. The CPR surveys, which have provided so much large-scale information for the spring and summer months, are unable to address the issue in winter. However, this composite use of data is potentially problematic if there is significant within-year and interannual variability in the distribution and abundance.
Considering first the potential for bias due to within-year variation, the major concerns are the effects of mortality on the perception of spatial distribution from data collected over a period of 68 weeks, and the effects of lipid utilization on the perceived patterns of vertical distribution. Regarding mortality, there are no direct estimates of mortality rates for diapause stages at ocean depths, but Heath et al. (2000b) estimated a value of 0.003 d1 by model fitting to data from Weatherstation M in the Norwegian Sea. The same approach yielded estimates of up to 0.007 d1 for shelf waters. So, for the ocean areas, we might expect up to a 20% loss of abundance over a 2-month period. Even if systematically applied, this could not negate the large-scale horizontal gradients observed in the composite data set.
Regarding interannual variability, the FaroeShetland Channel is the only oceanic location in the geographic range covered by data where sampling has been carried out in every year. An assessment of the interannual variability up to 1999 was presented by Heath et al. (1999a). The updated series to winter 2002/2003 shows a maximum deviation of ±20% from the 19942002 average abundance in the 6001000-m depth layer. Hence, the occurrence of over-winter aggregations in the FaroeShetland Channel can be regarded as a persistent feature, and the interannual variability is small compared to the large-scale gradients. So, although there is only one location in the North Atlantic where such an assessment can be performed, the indications are that the multi-annual composite approach probably provides a meaningful overall view.
Backhaus et al. (1994) proposed that the seasonal ontogenetic vertical migration of C. finmarchicus in the Northeastern Atlantic interacts with the basin-scale circulation to create the potential for spatial closure of life-cycle lineages, i.e. generation lines, thus maintaining spatial persistence in the face of a strongly advective system. In this hypothesis, the over-winter stock is effectively the epicentre of the regional population, and its location should be tied to large-scale circulation features. New generations produced in spring and summer are broadcast over a large area of the surface waters by advection and diffusion. Many lineages will be terminal, especially those which are carried into shelf waters where the mortality may be high and the scope for return to an over-wintering epicentre is low. However, the very existence of a consistent over-wintering epicentre implies that there is sufficient spatial closure of lineages to overcome mortality losses through the winter. The Backhaus et al. hypothesis was developed in the Northeast Atlantic, but Greene and Pershing (2000) have discussed a comparable scheme to explain the patterns of C. finmarchicus in the Western Atlantic.
Bryant et al. (1998) investigated the likely epicentres of spatially persistent populations of C. finmarchicus in the Northeast Atlantic and Norwegian Sea using a particle-tracking model with seasonal vertical migration coupled to results from a large-scale 3-D hydrodynamic model. Particles were released uniformly over the whole model domain and most were flushed out of the system within 12 years. Particles that persisted in the model for five or more annual cycles followed trajectories which took them through the southern and eastern basins of the Norwegian Sea and the FaroeShetland Channel. During the over-wintering phase of the simulations, these particles were concentrated in three main areas: around the southern and eastern fringe of the Norwegian Sea, and to the south and southwest of Iceland. All of these areas emerge from our synthesis of field data as supporting accumulations of over-wintering stages. However, Bryant et al. (1998) imposed a deterministic time-varying depth scheme on the tracked particles in which the over-winter depth was held constant at 600 m. Harms et al. (2000) subsequently showed that the spatial dynamics of particles in a similar tracking model were highly sensitive to the assumed over-wintering depth. Now, we can add a new dimension to the basic hypothesis of Backhaus et al. (1994), involving a coupling between the magnitude of lipid accumulation during the summer feeding and reproductive phase in the surface waters, and the advection route during and following the autumn descent phase. For a given 3-D temperature, salinity, and flow regime, we can expect different outcomes for copepodites descending at the same time and location with different lipid contents and hence different neutral buoyancy depths. The range of lipid contents permitting spatial closure of life-history lineages will be spatially variable and could be quite narrow in some regions. Presumably, copepodites with lipid content representative of the Labrador Sea would not be capable of contributing to spatial closure of life-history lineages in the Norwegian Sea, and vice versa.
The spatial persistence modelling approach of Bryant et al. (1998) has yet to be applied to the Western Atlantic. However, it has always been clear from surface CPR data that the Labrador Sea must also contain an epicentre of over-wintering stock. Until the cruise by RV "Hudson" in December 2002, there were no deep, depth-resolved plankton samples to confirm this. Here, we show that C. finmarchicus are concentrated at depths between 300 and 1000 m across the full width of the Labrador Sea. The area concentrations (m2) are lower than in the FaroeShetland Channel or Norwegian Sea, but the spatially integrated abundance across the basin must be very high.
Our synthesis of stage abundance data shows a systematic westeast gradient in the contribution of copepodite stages CIV, CV, and CVI females to the over-wintering population. This pattern is probably not an artifact of differences in the collection date of samples, because most measurements were carried out within the month of December and the patterns are not consistent with the spatial pattern of collection dates. Variation in the proportions of stages could result from several factors, including the timing and degree of synchrony of descent from the summer surface population, the contribution of first and, where occurring, second generations to the over-winter stock, and the rate of any development during over-wintering. However, whatever the cause, CVI production was more imminent in the populations of the Northwestern Atlantic, which had a low proportion of CIV, than those in the east. In fact, the low temperatures experienced by the copepodites in the Norwegian Sea and FaroeShetland Channel should enhance rather than reduce this contrast. However, estimates of the timing of appearance of CVI in the surface waters across the North Atlantic, which might corroborate this inference, are inconclusive. Surface water measurements in the southern Labrador Sea show a high proportion of females from the over-winter stock (G0) in May/June (Head et al., 2000). However, it is not easy to estimate the temporal distribution of G0 appearance from these data. Time-series data from sites in the Eastern Atlantic have shown peak abundance of G0 females in the surface waters at the end of March at Weatherstation India in the Iceland Basin (Irigoien, 1999), early to mid-April at Weatherstation M in the Norwegian Sea (Heath, 1999; Hirche et al., 2001), and between mid-April and early May around Iceland and in the FaroeShetland Channel (Heath, 1999; Gaard and Hansen, 2000; Gislason and Astthorsson, 2000). Possibly, any relationship between the arousal date of G0 at depth and their arrival at the surface is complicated by the vertical ascent distance, which our synthesis shows to vary considerably across the Atlantic.
One point to note from the various time-series studies in the Eastern Atlantic is that peak abundance of G0 in the surface waters pre-dates by 12 months the seasonal maximum in CV and CVI abundance, which is composed mainly of G1 copepodites, i.e. the offspring of G0. While CPR data provide the only basin-wide seasonal information on the abundance and distribution of C. finmarchicus in the surface waters, their stage and temporal resolutions are too low to effectively resolve the arrival of G0 at the surface. Thus, the principal components analysis of spatial patterns in seasonality of CV and CVI abundance by Planque et al. (1997) reflects more the timing of maturation of G1 than the arrival of G0 at the surface. Their analysis showed that most of the central and eastern North Atlantic shared a common seasonal pattern of abundance with a peak in May, while the area south of Grand Banks was characterized by an earlier "bloom" with a peak in February, and the Labrador/southern Irminger Seas, by a broader and later peak in abundance.
In summary, we have synthesized data on the winter abundance and habitat of C. finmarchicus from a swath across the North Atlantic, and exposed some fundamental regional differences in the condition of the populations. The basin-scale population is shown to be composed of several regional epicentres of over-wintering abundance, rather than a broad-scale diffuse distribution. As an extension to the hypothesis of Backhaus et al. (1994), we propose a connection between lipid accumulation during the summer productive season and the spacetime dynamics of the population mediated through buoyancy control and the over-wintering depth in relation to the circulation regime. Next, stages should be to investigate how the over-wintering epicentres are interrelated and linked to the basin-scale circulation features by analysis of population genetic data (e.g. Bucklin et al., 2000). In addition, interannual variability in hydrographic conditions, vertical distribution, and lipid content should be investigated at key sites such as the Labrador Sea and FaroeShetland Channel to determine whether the relationships established in this article are robust over time.
| Acknowledgements |
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The EU ICOS and TASC projects (MAS2-CT94-0085 and MAS3-CT95-0039) and UK Natural Environment Research Council Marine Productivity Programme, together with Canadian, Danish, Icelandic, and Scottish Fisheries Department funding supported the field sampling described here. Collection of time-series data from Weatherstation M and the Faroe Islands downloaded from the TASC website, are attributable to Webjørn Melle and Bjørnar Ellertsen (Institute of Marine Research Bergen) and Eilif Gaard (Faroese Fisheries Laboratory).
| References |
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Backhaus J.O., Harms I., Krause M., Heath M.R. (1994) An hypothesis concerning the spacetime succession of Calanus finmarchicus in the northern North Sea. ICES Journal of Marine Science 51:169180.
Bryant A.D., Hainbucher D., Heath M.R. (1998) Basin-scale advection and population persistence of Calanus finmarchicus. Fisheries Oceanography 7:235244.[CrossRef][Web of Science]
Bucklin A., Astthorsson O.S., Gislason A., Allen L.D., Smolenack S.B., Wiebe P.H. (2000) Population genetic variation of Calanus finmarchicus in Icelandic waters: preliminary evidence of genetic differences between Atlantic and Arctic populations. ICES Journal of Marine Science 57:15921604.
Dunn J., Hall C.D., Heath M.R., Mitchell R.B., Ritchie B.J. (1993) ARIES: a system for concurrent physical, biological and chemical sampling at sea. Deep-Sea Research 40:867878.
Durbin E.G., Gilman S.L., Campbell R.G., Durbin A.G. (1995) Abundance, biomass, vertical migration and estimated development rate of the copepod Calanus finmarchicus in the southern Gulf of Maine during late spring. Continental Shelf Research 15:571591.[CrossRef][Web of Science]
Gaard E. and Hansen B. (2000) Variations in the advection of Calanus finmarchicus onto the Faroe Shelf. ICES Journal of Marine Science 57:16121618.
Gislason A. and Astthorsson O.S. (2000) Winter distribution, ontogenetic migration, and rates of egg production of Calanus finmarchicus southwest of Iceland. ICES Journal of Marine Science 57:17271739.
Greene C.H. and Pershing A.J. (2000) The response of Calanus finmarchicus populations to climate variability in the Northwest Atlantic: basin-scale forcing associated with the North Atlantic Oscillation. ICES Journal of Marine Science 57:15361544.
Hansen B. (1985) The circulation of the northern part of the Northeast Atlantic. Rit Fiskideildar 9:110126.
Harms I.H., Heath M.R., Bryant A.D., Backhaus J.O., Hainbucher D. (2000) Modelling the Northeast Atlantic circulation: implications for the spring invasion of shelf regions by Calanus finmarchicus. ICES Journal of Marine Science 57:16941707.
Head E.J.H., Harris L.R., Campbell R.W. (2000) Investigations on the ecology of Calanus spp. in the Labrador Sea. I. Relationship between the phytoplankton bloom and reproduction and development of Calanus finmarchicus in spring. Marine Ecology Progress Series 193:5373.[Web of Science]
Heath M.R. (1999) The ascent migration of the copepod Calanus finmarchicus from overwintering depths in the FaroeShetland Channel. Fisheries Oceanography 8:Suppl 1, 8499.[CrossRef]
Heath M.R., Astthorsson O.S., Dunn J., Ellertsen B., Gislason A., Gaard E., Gurney W.S.C., Hind A.T., Irigoien X., Melle W., Niehoff B., Olsen K., Skreslet S., Tande K.S. (2000) Comparative analysis of Calanus finmarchicus demography at locations around the Northeast Atlantic. ICES Journal of Marine Science 57:15621580.
Heath M. R., Beare D. J., Dunn J., Fraser J. G., Hay S. J., Turrell W. R. (1999a) Monitoring the effects of climate change: overwintering abundance of Calanus finmarchicus in the FaroeShetland Channel. Fisheries Research Services Report 14/99. 24 pp. (http://www.frs-scotland.gov.uk/FRS.Web/Uploads/Documents/frsr1499.pdf).
Heath M.R., Dunn J., Fraser J.G., Hay S.J., Madden H. (1999) Field calibration of the Optical Plankton Counter with respect to Calanus finmarchicus. Fisheries Oceanography 8:Suppl 1, 1324.[CrossRef]
Heath M.R., Fraser J.G., Gislason A., Hay S.J., Jónasdóttir S.H., Richardson K. (2000) Winter distribution of Calanus finmarchicus in the Northeast Atlantic. ICES Journal of Marine Science 57:16281635.
Heath M.R. and Jónasdóttir S.H. (1999) Distribution and abundance of overwintering Calanus finmarchicus in the FaroeShetland Channel. Fisheries Oceanography 8:Suppl 1, 4060.[CrossRef]
Herman A.W. (1992) Design and calibration of a new Optical Plankton Counter capable of sizing small zooplankton. Deep-Sea Research 39:395415.
Hirche H.-J. (1983) Overwintering of Calanus finmarchicus and Calanus helgolandicus. Marine Ecology Progress Series 11:281292.[Web of Science]
Hirche H.-J. (1991) Distribution of dominant calanoid copepod species in the Greenland Sea during late fall. Polar Biology 11:351362.
Hirche H.-J. (1996) Diapause in the marine copepod, Calanus finmarchicus: a review. Ophelia 44:129143.[Web of Science]
Hirche H.-J., Brey T., Niehoff B. (2001) A high-frequency time series at Ocean Weather Ship Station M (Norwegian Sea): population dynamics of Calanus finmarchicus. Marine Ecology Progress Series 219:205219.[Web of Science]
Ingvarsdottir A. (1998) Seasonal changes in physiology and chemical composition of Calanus finmarchicus copepodite stages. PhD thesis, University of Aberdeen. 152 pp.
Irigoien X. (1999) Vertical distribution and population dynamics of Calanus finmarchicus at station India (59°N, 19°W) during the passage of the great salinity anomaly, 19711975. Deep-Sea Research I 47:126.
Jónasdóttir S.H. (1999) Lipid content of Calanus finmarchicus during overwintering in the FaroeShetland Channel. Fisheries Oceanography 8:Suppl 1, 6172.[CrossRef]
Kaartvedt S. (1996) Habitat preference during overwintering and timing of seasonal vertical migration of Calanus finmarchicus. Ophelia 44:145156.[Web of Science]
Lindeque P., Harris R., Jones M., Smerdon G. (1999) Calanus: a simple molecular method to distinguish the species identity of any developmental stage. Marine Biology 133:9196.[CrossRef][Web of Science]
Lindeque P. K., Harris R. P., Jones M., Smerdon G. R. Distribution of Calanus spp. as determined using a genetic identification system. Scientia Marina (in press).
Matthews J.B.L. (1969) Continuous plankton records: the geographical and seasonal distribution of Calanus finmarchicus L. in the North Atlantic. Bulletin of Marine Ecology 6:251273.
Planque B., Hays G.C., Ibanez F., Gamble J.C. (1997) Large-scale spatial variations in the seasonal abundance of Calanus finmarchicus. Deep-Sea Research 44:315326.
Visser A.W. and Jónasdóttir S.H. (1999) Lipids, buoyancy and the seasonal vertical migration of Calanus finmarchicus. Fisheries Oceanography 8:Suppl 1, 100106.[CrossRef]
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