- 0.0 EXECUTIVE SUMMARY
- 0.1 Program Objectives and Participants
- 0.1.1 The Pan-Arctic Region: Highlights of the Literature Review
- 0.1.1.1 Behavior and Fate of Oil in the Arctic
- 0.1.1.2 VECs and Ecotoxicity
- 0.1.2 Role of Ecosystem Consequence Analyses in NEBA Applications for the Arctic
- 0.1.2.1 Arctic Population Resiliency and Potential for Recovery
- 0.2 Priority Recommendations to Enhance NEBA Applications in the Arctic
- 0.2.1 Development of ARCAT Matrices
- 0.2.2 Influence of Oil on Unique Arctic Communities
- 0.2.3 Biodegradation in Unique Communities
- 0.2.4 Modeling of Acute and Chronic Population Effects of Exposure to OSRs
- 0.3 Further Information
- 1.0 THE PHYSICAL ENVIRONMENT
- 1.1 Introduction
- 1.1.1 The Arctic Ocean, Marginal Seas, and Basins
- 1.2 Knowledge Status
- 1.2.1 The Circumpolar Margins
- 1.2.2 Arctic Hydrography
- 1.2.3 Ice And Ice-Edges
- 1.2.4 Seasonality: Productivity and the Carbon Cycle in the Arctic
- 1.3 Future Research Considerations
- 1.3.1 Priority Recommendations to Enhance NEBA Applications in the Arctic
- 1.4 Further Information
- 2.0 ARCTIC ECOSYSTEMS AND VALUABLE RESOURCES
- 2.1 Introduction
- 2.2 Knowledge Status
- 2.2.1 Habitats of the Arctic
- 2.2.2 Arctic Food Webs
- 2.2.2.1 Pelagic Communities
- 2.2.2.2 Benthic and Demersal Communities
- 2.2.2.2 Sea-ice Communities
- 2.2.2.4 Mammals and Birds
- 2.2.2.5 Communities of Special Significance
- 2.2.3 Pelagic Realm
- 2.2.3.1 Phytoplankton
- 2.2.3.2 Zooplankton
- 2.2.3.3 Neuston
- 2.2.3.4 Other Pelagic Invertebrates
- 2.2.3.4.1 Krill
- 2.2.3.4.2 Amphipods
- 2.2.3.4.3 Cephalopods
- 2.2.3.4.4 Jellyfish
- 2.2.3.5 Fish
- 2.2.3.5.1 Pelagic Fish
- 2.2.3.5.2 Anadromous Fish
- 2.2.3.5.3 Demersal Fish
- 2.2.3.5.4 Deep-Sea Fish
- 2.2.3.6 Marine Mammals
- 2.2.3.6.1 Bowhead Whale (Balaena mysticetus)
- 2.2.3.6.2 White Whale (Delphinapterus Leucas)
- 2.2.3.6.3 Narwhal (Monodon monoceros)
- 2.2.3.6.4 Ice Seals
- 2.2.3.6.5 Walrus (Odobenus rosmarus)
- 2.2.3.6.6 Orca Whales (Orcinus orca)
- 2.2.3.6.7 Polar Bear (Ursus maritimus)
- 2.2.3.7 Birds
- 2.2.3.7.1 Black-legged kittiwakes (Rissa tridactyla)
- 2.2.3.7.2 Black Guillemots (Cepphus grille)
- 2.2.3.7.3 Thick billed Murres (Uria lomvia)
- 2.2.3.7.4 Northern Fulmar (Fulmarus glacialis)
- 2.2.3.7.5 Common Eider (Somateria mollissima)
- 2.2.3.7.6 Little Auk/Dovekie (Alle alle)
- 2.2.3.7.7 Glaucous gull (Larus glaucescens)
- 2.2.3.7.8 Arctic jaeger (Stercorarius parasiticus)
- 2.2.4 Benthic Realm
- 2.2.4.1 Intertidal Communities
- 2.2.4.2 Shelf and Deepwater Communities
- 2.2.4.3 Mollusca
- 2.2.4.4 Polychaetes
- 2.2.4.5 Amphipods
- 2.2.4.6 Decapod Crustaceans
- 2.2.4.7 Echinoderms
- 2.2.5 Sea-Ice Realm
- 2.2.5.1 Ice Algae
- 2.2.5.2 Sympagic Copepods
- 2.2.5.3 Ice Amphipods
- 2.2.5.4 Pelagic Copepods
- 2.2.5.5 Sympagic Fish
- 2.2.5.6 Mammals
- 2.2.5.7 Birds
- 2.2.6 VECs of Arctic Marine Environments
- 2.2.6.1 Seasonal Distribution Patterns of Arctic Marine Populations
- 2.3 Future Research Considerations
- 2.3.1 Priority Recommendations to Enhance NEBA Applications in the Arctic
- 2.4 Further Information
- 3.0 THE TRANSPORT AND FATE OF OIL IN THE ARCTIC
- 3.1 Introduction
- 3.2 Knowledge Status
- 3.2.1 Weathering of Oil Spilled in Ice
- 3.2.2 Oil in Ice Interactions
- 3.2.3 Oil on Arctic Shorelines
- 3.2.4 Oil-Sediment Interactions
- 3.3 Future Research Considerations
- 3.3.1 Priority Recommendations for Enhanced NEBA Applications in the Arctic
- 3.4 Further Information
- 4.0 OIL SPILL RESPONSE STRATEGIES
- 4.1 Introduction
- 4.1.1 Environmental Uniqueness of the Arctic Region in Relation to OSR
- 4.2 Knowledge Status - Impact of OSRs
- 4.2.1 Natural Attentuation
- 4.2.1.1 Potential Environmental Impact of Untreated Oil
- 4.2.1.2 Conclusions on Natural Attenuation
- 4.2.2 Mechanical Recovery and Containment
- 4.2.2.1 Environmental impacts from Mechanical Recovery and Containment
- 4.2.2.2 Conclusions
- 4.2.3 In-Situ Burning and Chemical Herders
- 4.2.3.1 Potential environmental and human health effects of ISB residues and unburnt oil
- 4.2.3.2 Environmental Impact of Herders
- 4.2.3.3 Conclusions on ISB and Herders
- 4.2.4 Improving Dispersion of Oil
- 4.2.4.1 Impact of Chemically Dispersed Oil
- 4.2.4.2 Conclusions on Chemical Dispersion
- 4.2.4.3 Dispersing Oil using Oil Mineral Aggregates (OMA)
- 4.2.4.4 Environmental Impact of OMA formation
- 4.2.4.5 Conclusions on OMA
- 4.3 Future Research Considerations
- 4.3.1 Priority Recommendations for Enhanced NEBA Applications in the Arctic
- 4.4 Further Information
- 5.0 BIODEGRADATION
- 5.1 Introduction
- 5.1.1 The Microbiology of the Arctic Oceans
- 5.1.1.1 Transport routes
- 5.1.1.2 Microbial populations in the Arctic Ocean
- 5.1.2 Microbial Adaptation to Arctic Conditions
- 5.1.2.1 Low temperature and microbial adaptions
- 5.1.2.2 Light and microbial phototrophs
- 5.1.2.3 Marine ice and microbial survival and metabolism
- 5.2 Knowledge Status
- 5.2.1 Biodegradation of Oil in Cold Marine Environments
- 5.2.1.1 Types of Crude Oils
- 5.2.1.2 Surface oil spills
- 5.2.1.2.1 Evaporation
- 5.2.1.2.2 Water solubility
- 5.2.1.2.3 Photooxidation
- 5.2.1.2.4 Sedimentation
- 5.2.1.2.5 Water-in-oil emulsification
- 5.2.1.2.6 Natural dispersion
- 5.2.1.2.7 Oil films
- 5.2.1.3 Microbial Oil-Degrading Populations in Cold Water Environments
- 5.2.1.3.1 Indigenous Microorganism Populations
- 5.2.1.3.2 Population Effects on Oil Degradation
- 5.2.1.4 Hydrocarbon biodegradation in cold marine environments
- 5.2.1.4.1 Seawater
- 5.2.1.4.2 Sediments and soils
- 5.2.1.4.3 Sea ice
- 5.2.1.5 Modeling of biodegradation
- 5.2.1.5.1 Biodegradation in oil spill models
- 5.2.1.5.2 Biodegradation modeling and temperature
- 5.2.1.6 Determination of Biodegradation
- 5.2.1.6.1 Analytical methods for oil compound analyses
- 5.2.1.6.2 Experimental apparatus
- 5.2.1.6.3 Biodegradation data processing
- 5.2.1.7 Persistent Oil Compounds
- 5.2.2 Accelerated Biodegradation
- 5.2.2.1 Biostimulation
- 5.2.2.1.1 Shoreline sediments
- 5.2.2.1.2 Seawater
- 5.2.2.1.3 Marine ice
- 5.2.2.2 Bioaugmentation
- 5.2.2.3 Understanding Processes in Accelerated Biodegradation
- 5.3 Future Research Considerations
- 5.3.1 Priority Recommendations for Enhanced NEBA Applications in the Arctic
- 5.4 Further Information
- 6.0 ECOTOXICOLOGY OF OIL AND TREATED OIL IN THE ARCTIC
- 6.1 Introduction
- 6.1.1 General Methods and Relevant Endpoints in Laboratory Testing
- 6.1.1.1 Test Exposure
- 6.1.1.2 Test Media Preparation
- 6.1.1.2.1 Water Soluble Fractions (WSF)
- 6.1.1.2.2 Water Accommodated Fractions (WAF, CEWAF)
- 6.1.1.2.3 Oil-in-Water Dispersions (Oil Droplets)
- 6.1.1.2.4 Oil Type/Weathering
- 6.1.1.2.5 Exposure Concentrations
- 6.1.1.2.6 Test Organisms
- 6.1.1.2.7 Test Endpoints and Exposures
- 6.1.1.2.8 Data Extrapolation and Population Models
- 6.2 Knowledge Status
- 6.2.1 Species represented in the data set
- 6.2.2 Arctic ecosystem compartments in the dataset
- 6.2.2.1 Pack ice
- 6.2.2.2 Pelagic
- 6.2.2.3 Benthic
- 6.2.3 Review by Taxa
- 6.2.3.1 Phytoplankton and seaweed
- 6.2.3.2 Mysids
- 6.2.3.3 Copepods
- 6.2.3.4 Amphipods
- 6.2.3.5 Benthic organisms
- 6.2.3.6 Fish
- 6.3 Discussion
- 6.3.1 Petroleum related components
- 6.3.1.1 Crude oil
- 6.3.1.2 Single PAH
- 6.3.2 Chemically dispersed oil versus physically dispersed oil
- 6.3.3 Are Arctic species more sensitive than temperate species?
- 6.4 Future Research Considerations
- 6.4.1 Priority Recommendations to Enhance NEBA Applications in the Arctic
- 6.5 Further Information
- 7.0 POPULATION EFFECTS MODELING
- 7.1 Introduction
- 7.2 Knowledge Status
- 7.2.1 Parameters Needed to Assess Potential Responses of VECs to Environmental Stressors
- 7.2.1.1 Transport and fate / exposure potential
- 7.2.1.2 Oil toxicity evaluations / sensitivity
- 7.2.1.3 Population distributions, stressors, and mortality rates
- 7.2.2 Copepod Population Ecology
- 7.2.2.1 Copepod Growth and Development
- 7.2.2.2 Summary of Arctic and Sub-Arctic Copepod Species
- 7.2.3 Copepod Populations
- 7.2.4 Arctic Fish Population Ecology
- 7.2.4.1 Arctic Fish Species Diversity
- 7.2.4.2 Representative Fish Species
- 7.2.5 Application of Population Models
- 7.3 Future Research Considerations
- 7.3.1 Priority Recommendations to Enhance NEBA Applications in the Arctic
- 7.4 Further Information
- 8.0 ECOSYSTEM RECOVERY
- 8.1 Introduction
- 8.2 Knowledge Status
- 8.2.1 Resilience and Potential for Recovery
- 8.3 Future Research Considerations
- 8.3.1 Priority Recommendations for Enhanced NEBA Applications in the Arctic
- 8.4 Further Information
- 9.0 NET ENVIRONMENTAL BENEFIT ANALYSES FOR OIL SPILL
- 9.1 Introduction
- 9.2 Knowledge Status
- 9.2.1 Importance of NEBA Development for Arctic Regions
- 9.2.2 Scope and Applicability
- 9.2.3 Information Required to Utilize the NEBA Process
- 9.2.3.1 Potential oil spill scenarios
- 9.2.3.2 Response resources available
- 9.2.4 Ecological Resources at Risk
- 9.2.5 Social and Economic Relevance
- 9.2.6 Historical uses of NEBA and Case Studies
- 9.2.6.1 Assessing response strategy effectiveness and estimating oil fate and transport
- 9.2.6.2 Assessing the potential impacts and resource recovery rates
- 9.2.7 Historical Spills that Used or Informed NEBA Processes
- 9.2.7.1 A. Experimental: Baffin Island tests in northern Canada
- 9.2.7.2 B. Experimental: TROPICS study
- 9.2.7.3 C. Tanker: Braer Spill
- 9.2.7.4 D. Tanker: Sea Empress spill
- 9.2.7.5 E. Well Blowout: Montara spill (also known as the West Atlas Spill)
- 9.2.8 Potential Challenges to Applying NEBA Processes in the Arctic Environment
- 9.3 Future Research Considerations
- 9.3.1 Priority Recommendations for Enhanced NEBA Applications in the Arctic
- 9.4 Further Information
- APPENDIX: USE OF NEDRA IN CONNECTION TO OIL SPILL CONTINGENCY PLANNING IN NORWAY
- 10.0 SUPPORTING REPORTS
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1.2 Knowledge Status
1.2.1 The Circumpolar Margins
Most oil and gas development activities, shipping routes, as well as major fishing grounds occur along the margins of the Arctic Ocean at the interface of land and sea edges. Figure 1-4 highlights the main shipping routes transiting Arctic waters and areas of active oil and gas exploration. Increased periods of ice-free conditions along shipping routes will result in increased vessel and fishing activities. It should be noted that increased commercial fishery pressure itself may lead to changes in fishery stocks and biodiversity in the Arctic.
Continental runoff is a major source of freshwater, terrigenous materials and nutrient loads to the Arctic Ocean. Information gathered from the Regional Arctic Hydrographic Network data set (R-ArcticNET) indicates that the overall annual discharge is ~3,300 km3 y-1. This buoyant freshwater contributes to a low saline layer (upper 200 m) of the Arctic Ocean which is isolated from the warmer, saltier Atlantic layer by a strong halocline (Fichot et al. 2013). Rivers account for 2% of the influx of water to the Arctic region resulting in highly productive areas, particularly during the peak flow occurring from April to July (~60%). The rivers in Siberia (Ob, Yenisey, Lena, and Kolyma) and in North America (Yukon, and Mackenzie) provide the majority of continental fresh water to the Arctic Ocean. The Arctic Great Rivers Observatory (Arctic-GRO) monitors the discharge of these six river systems.
River systems generally increase productivity due to the availability of increased organic nutrients in the areas of riverine discharges. Figure 1-5 shows the locations of the major rivers in the Arctic. The regions along the continental shelf may be the most likely to encounter oil spill incidents, either due to oil and gas production activities or vessel mishaps. In determining environmental impacts of released oil, areas of special importance are the interfaces where oil components may re-concentrate (e.g. current convergence zones, pycnoclines, upwelling or downwelling of water masses, shoreline stranding or concentration at air-water, ice-water, or sediment-water interfaces).
1.2.2 Arctic Hydrography
Ocean temperatures vary widely depending on latitude and proximity to warm Atlantic or Pacific Ocean waters. For the Arctic Ocean, temperature variation between winter and summer is small (remains close to freezing year round) and salinities vary between 30 and 33. In the coastal shelf areas, surface water temperatures range from -1 °C to 4-5 °C, winter to summer, respectively while salinities may be <30, especially in areas receiving freshwater from rivers and ice melt. In areas where oceanic mixing occurs, the temperature remains higher than 0 °C throughout the year. In the Kara Sea and Siberian shelf, salinity is <20 throughout the year, and may drop to 10 during the summer (Figure 1-5; AMAP 1998). Arctic seas are primarily ‘beta oceans’, i.e. a salinity profile is the most important permanent stratification feature (Carmack and Wassmann 2006).
Figure 1-6. Temperature, salinity, and density profiles (AMAP 1998)
Warm ocean currents flow northward from the Atlantic and Pacific Oceans and cold Arctic countercurrents flow southward (Figure 1-6). Arctic Ocean water mainly flows from the Atlantic Ocean (79%), while inflow from the Bering Strait accounts for only 19%. Concern with thinning of Arctic ice cover over recent decades has generated numerous investigations of the ocean-ice heat flux and changes in the Arctic Ocean surface layer (ASL). The ASL is generally insulated from the warmer and higher salinity bottom water (Atlantic water layer; AWL) by a well-developed halocline (cold halocline layer, CHL). The halocline establishes as a strong barrier to upward mixing by turbulence, and consequently most of the ocean heat flux in the central basins of the Arctic is generated by solar heating through open leads and thin ice during the summer months.
Figure 1-7. Arctic currents (AMAP 1998)
Researchers have found that although changes in surface velocity and surface stress in the open ocean reflects large scale atmospheric pressure fields (the Arctic oscillation, AO), the properties of sea-ice concentrate energy into relatively narrow zones of intense shear which can raise the pycnocline. Such events may greatly enhance ocean-to-ice heat transfer (McPhee et al. 2005). Examination of hydrographic records indicated that the CHL dissipated during a low pressure system from 1988 to 1997 in the Nansen and Amundsen Basins, resulting in an increased rate of melting sea-ice (15-25 cm/y). The lateral Ekman currents moved in a counter-clockwise direction, resulting in upwelling of warmer, saltier water from the AWL and raising a weakened halocline layer about 50 m. Average seasonal changes in sea-ice conditions (concentration and movement), sea level pressure, Ekman transport vectors, and upwelling patterns are presented in Figure 1-7 (Yang 2008).
Figure 1-8. Seasonal sea-ice and ocean movement averaged over a 28 year period (Yang 2008)
Closer to shore, the seasonal cycle of Ekman transport is highly influenced by high sea level pressure in fall and winter. For example, strong offshore transport along the Beaufort, Chukchi and East Siberian coasts intensifies coastal upwelling and downwelling in the interior Canadian Basin. The offshore transport also pushes low-salinity warm shelf water toward the deeper basins, reducing salinity and increasing temperature.
The continental shelf zones comprise about 50% of the Arctic Ocean surface and there are marked regional differences. Narrow shelves are characteristic of the North American continent, and wide shelves with very steep slopes are typical of Eurasian continents (Table 1-1). Carmack and Wassmann (2006) group shelf areas according to function: 1) Inflow shelves (Bering Strait/Chukchi Sea, Barents Sea); 2) 2) Interior shelves (Beaufort and Kara/Laptev/East Siberian Seas); and 3) Outflow shelves (Canadian Archipelago and East-Greenland shelf). The pan-Arctic shelves are estuarine in nature in that waters originating from the Atlantic and/or the Pacific Oceans mix with inflowing river waters. Although there are regional differences in source water characteristics, all shelf areas are generally associated with the nutrient enrichment, productivity, and biodiversity. Figure 1-8 is an excellent illustration of the dynamic physical, chemical, and biological interactions occurring in the Arctic shelf regions in the vicinity of receiving waters of major river systems. In general, the nearshore ecosystems are characterized by relatively few trophic links and low biodiversity, and would be more sensitive to increased climatic warming than temperate regions (Carmack and Wassmann 2006).
Arctic Sea | Function | Mean depth (m) | Area (103 km2) | % Total shelf area |
---|---|---|---|---|
Barents Sea |
Inflow |
200 |
1597 |
27 |
Kara Sea |
Interior |
56 |
926 |
15 |
Laptev Sea |
Interior |
131 |
498 |
8 |
East Siberian Sea |
Interior |
48 |
987 |
16 |
Chukchi Sea |
Inflow |
58 |
620 |
10 |
Beaufort Sea |
Interior |
80 |
178 |
3 |
Canadian Arctic Archipelago (CAA) |
Outflow |
124 |
1032 |
18 |
Northern CAA |
Outflow |
310 |
210 |
3 |
Total |
140 |
6048 |
100% |
Table 1-3. Characteristics of Arctic shelves (after Carmack and Wassmann 2006)
1.2.3 Ice And Ice-Edges
Sea ice forms when the temperature of the ocean falls below the freezing point, effectively converting the seawater to ice (-1.8 °C at 33 ‰ salinity). Ice is characterized by where it is located: landfast ice lines the shoreline and first year ice is intermediate between the multi-year ice and open water. The annual changes in pack ice are determined by temperature, winds, and ocean currents (such as the Alaska, Labrador, East Greenland currents and the warm West Spitsbergen and North Cape currents). Multi-year ice averages 2.5 to 4 m in thickness and may be intersected by leads such as shown in the photo above (~1% open in winter to 10-20% open in summer; Gow and Tucker 1990). The two main ice circulation systems in the Arctic are the clockwise Beaufort Gyre in the Amerasian Arctic and the Transpolar Drift in the Eurasian Arctic (migrating east to west, exiting via the Fram Strait). The North Cap current keeps the southern Barents Sea ice-free during the winter.
Photo 1-2. Ice lead (Lionel Camus)
Ice leads and open-water lenses (polynyas) form in nearshore or ocean areas and are characterized by cold, highly saline water (Photos 1-2 and 1-3). The processes of ice production, salt flux, and heat transfer from leads and polynyas are important contributors to the larger scale climate events in the Arctic. Polynyas occur for the most part during winter and harsh weather conditions and may be formed by two processes: 1) Mechanically forced (wind-driven; strong winds force ice cover away from the coast; 2) Convectively forced (ice subsidence; subsurface heat is transferred to the surface water by the upwelling of warmer, deeper water); refer to Figure 1-10. Improved satellite technologies (e.g. synthetic aperture radar, SAR) and mathematical algorithms (e.g. polynya signature simulation method, PSSM) have made it possible to define the size and shape of polynyas as well as differentiate open water, new ice, and young ice (Dokken et al. 2002). The heat exchange from the ocean to the atmosphere can be orders of magnitude larger in polynyas compared to the surrounding ice pack, and polynyas can contribute ~50% of the seasonal mean of annual ice production in some areas (Winsor and Bork 2000). Winsor and Bjork (2000) estimated the mean ice production and corresponding salt flux from Arctic polynyas and found that the salt flux represents about 30% of that necessary to maintain the CHL. The marginal seas contributing the most to the CHL are the Barents, Kara, Chukchi, and Bering; the Chukchi Sea is the only sea contributing actively to deep water formation. The North Water Polynya is located between Greenland and Canada in northern Baffin Bay. It is 85,000 sq. km in area and creates a warm microclimate that is one of the most biologically productive marine areas in the Arctic Ocean. Polynyas are of critical importance to significant populations of marine birds, mammals, and fish.
The term seasonal ice zone (SIZ) describes the presence of transitional ice (i.e. freezes and melts annually) whereas marginal ice zone (MIZ) is used to describe the areas where open water meets ice cover during any season. About half of the Arctic sea-ice freezes and melts annually. During summer months, narrow MIZ and wide SIZ bands circumscribe the polar region. It is along this band of expanding and shrinking open water linkages that most of the Arctic Ocean productivity takes place and where climatic changes would be most evident (Carmack and Wassmann 2006). In recent years, the ice-free season in the Arctic increased at a steady rate of 1.1 days/year. A record low in sea ice was recorded in 2007, with 168 ice-free days (Rodrigues 2009). Increasing seasonal open water periods is coincident with anticipated increases in shipping traffic via the polar routes (Northwest Passage and Northern Sea Route).
1.2.4 Seasonality: Productivity and the Carbon Cycle in the Arctic
Biological productivity hinges upon solar irradiance and nutrient availability. These two resources are regulated by salinity stratification of the Arctic waters. In general stratification is expressed as buoyancy frequency relating vertical temperature and salinity gradients with consideration of gravity, thermal expansion, and haline contraction coefficients (Carmack and Wassmann 2006).
The annual productivity/carbon cycle in the Arctic is illustrated in Figure 1-10. The sun appears over the horizon in April, supplying light to support the growth of ice algae and phytoplankton. Production peaks in June when the sun is at its highest; zooplankton thrive on this superabundance of food. The production gradually declines during the season as the phytoplankton use up the nutrients in the water and as the sun sinks below the horizon, the plankton hibernate until the next growing season (http://www.arcticsystem.no). For areas in the Canadian high Arctic, Welch et al. (1992) estimated the relative importance of contributors to primary productivity as: phytoplankton (90%) > ice algae (10%) > benthic algae (1%). This relationship likely varies in different locations.
Physical processes inherent in ice field characteristics, water column stratification, vertical mixing, light and nutrients in combination with phytoplankton determine the balance of productivity and biomass build-up in the euphotic zone and its transfer to the aphotic zone. The fate of suspended and sinking biogenic matter is based on the magnitude of export production and biological activities such as grazing in the upper water column. The transfer of carbon from the surface layer to the deep ocean is accomplished via the passive sinking (exported) or the active transport of organic material (harvested, fecal production). The greatest congregation of zooplankton often occurs just below the euphotic zone (Olli et al. 2006); excess detrital matter ultimately sinks into the aphotic zone. In some regions such as the Barents Sea, the pelagic food web is positively correlated with benthic standing stocks (Carmack and Wassmann 2008). There is considerable variability in sediment community structures and biomass, depending on carbon development in the upper layers. Ice cover and other physical factors have been observed to limit primary production and benthic biomass (Grebmeier et al. 1995).
The highly seasonal attributes of the Arctic influence species abundance and distribution patterns. The lack of sunlight during the Arctic winter in combination with ice-covered waters limits primary and secondary production when solar irradiance is unavailable. The periods of low production are punctuated by extremely high production during breakup and seasonal open water. The combination of open water, long days, and high nutrient concentrations during break up and early summer creates intense periods of primary production, grazing by primary consumers, and predation by the higher trophic levels. Whereas the aquatic communities are limited during the winter, the diversity and abundance of species increases dramatically in the summer. Key Arctic species have adapted their life cycles to take advantage of this period of high production, and larval or juvenile life stages are adapted to capitalize on the short period of enriched food resources.
The initiation and duration of summer production follows a latitudinal gradient from the southern Barents Sea in March – April to August – September in the Fram Strait and Arctic Ocean (Figure 2-5; Falk-Peterson et al. 2007) with substantially shorter periods of high production in the higher latitudes. This suggests not only a strong temporal component, but a strong regional component. The largest seasonal effects are seen in the surface and nearshore waters, however there are seasonal patterns in the deeper waters as well, with Arctic cod (adults, YOY and larval cod) and copepods moving to deeper waters during the winter months.
Seasonal migrations and changes in abundance, particularly of the younger life stages are an important consideration for environmental consequence analysis (ECA) and the relative vulnerability of different VECs. Based on information provided in this review, there are some general pan-Arctic patterns of seasonal sensitivity. However, for the purposes of assessing the spill response options, a regional approach is recommended. Surface waters along ice-edges and in leads, particularly during the breakup and early ice-free period are important concentration points for copepods and juvenile cod, as well as migratory birds and mammals. During the ice-free period, the ice edge continues to be an important feeding ground for large marine mammals as well as ice-seal pups. Nearshore waters, are also a concentration point for water column resources, particularly juvenile forms and migratory species (e.g. toothed whales, sea birds). As in more temperate waters, estuarine lagoons and rocky intertidal habitat during the ice-free season are important nursery grounds and act as a convergence point for aquatic, avian, and terrestrial species (Dunton et al. 2006). During the open water season, nearshore waters and shallow shelf waters are also important feeding and breeding grounds for walrus. Portions of the nearshore and shallow shelf are staging and feeding grounds for nesting sea birds and their chicks (Robertson 2013). The midwater pelagic region is a concentration point for shoals of arctic cod and feeding migratory whales. In the winter months, Arctic cod and Calanoid copepods move to deeper waters. Leads and polynyas are concentration points for VEC species during the winter, in particular toothed whales.
For further detailed information on Arctic species, communities, and trophic linkages, please refer to Section 2.