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Problems and Challenges Working In an Observationally Poor Environment

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Presentation on theme: "Problems and Challenges Working In an Observationally Poor Environment"— Presentation transcript:

1 Problems and Challenges Working In an Observationally Poor Environment
Scott Glenn and Oscar Schofield Rutgers Coastal Ocean Observation Laboratory Special acknowledgements to my partners Bob Chant (RU COOL) Mark Moline (Cal-Poly), Paul Bissett (FERI), and Trisha Bergmann, Josh Kohut, & Matt Oliver

2 Our Long Term Goal: To Build a Nested Coastal
Observation Network l Why? l Monitoring Global Change and Phytoplankton Communities l Sediment Transport in Estuaries l THIS AFTERNOON: Integrated Systems and the Future Ocean Observatories

3 In Situ Research- ‘The Early Years’

4 The Problem for Aquatic Sciences
(Lots of processes interacting over many time/space scales) Horizontal Spatial Scales 1mm 1cm 1m 10m 100m 1km 10km 100km AUVs 1 sec molecular processes 1 min research vessels Turbulent mixing & physiological acclimation satellites 1 hour Individual Movement 1 day Temporal Scales Phytoplankton bloom Fisheries and aquaculture 1 week moorings 1 month seasonal 1 year fishermen 10 year

5 Case Example 1: Importance in Monitoring Phytoplankton
Community Composition Study Site The Antarctic Penisula 64 48’ S Hermit Island E B Janus Island Litchfield Island Torgersen Anvers Island Palmer 64 46’ S Bonaparte Point 64 04’ W

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7 Integrated Chlorophyll a vs. Upper Mixed Layer Depth
350 Station B 300 Mitchell & Holm Hansen (1991) 250 200 Integrated UML Chl a (mg m-3) 150 100 50 10 20 30 40 50 60 70 80 Upper Mixed Layer Depth (m)

8 Thalassiosira antarctica
100m Thalassiosira antarctica Cryptomonas cryophila Corethron criophilum Palmer Cryptophytes --> 8 ± 2m 10m SEM Micrographs fromMcMinn and Hodgson 1993

9 Cryptophytes in the Coastal Ocean (Antarctica) Palmer Station
1 Palmer Station (n=162) 0.8 0.6 Proportion of total chlorophyll a associated with diatoms Ocean warm low salinity 0.4 Ocean cold-salty 0.2 0.2 0.4 0.6 0.8 1 Proportion of total chlorophyll a associated with cryptophytes

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11 The Ice-melt Wall % Cryptophytes 100 80 60 40 20
20 40 60 80 100 -15 -10 -5 5 10 Mean Air Temperature (°C) % Cryptophytes

12 Antarctic Peninsula Salinity 33.3 33.6 33.8 Palmer Station 65°S
% Crypts 25 50 65°S 64°W

13 Where have all the good krill gone?
100 6 Krill:Salp 10 1 Ice Index 4 0.1 2 0.01 YEAR 0.001 80 82 84 86 88 90 92 94 96 100 10 1 Krill:Salp 0.1 0.01 Ice Index 0.001 2 4 6 100 10 Krill:Salp 1 0.1 0.01 0.001 -4 -2 Mean Air Temperature (°C) From Loeb et al., 1997

14 Phytoplankton Size (m)
McClatchie and Boyd 1983 Boyd et al. 1984 Quetin and Ross 1985 100 100 50 80 80 40 % Retention by Krill 60 60 30 40 40 20 20 20 10 5-10 >15 5-10 >15 5-10 >15 Phytoplankton Size (m)

15 Changes over the last 50 years
1.2 0.8 0.4 Mean Summer Air Temperatures (°C) Faraday Station R2 = 0.64 -0.4 Signy Station R2 = 0.73 -0.8 1945 1955 1965 1975 1985 Year From Smith (1994)

16 (fish, penguins, whales)
4% 62% 12% 22% 33.3 (Krill:Salp) 15% 33% 24% 28% 0.06 (Krill:Salp) Higher Trophic Levels Recycled carbon Respiration Autotrophic Losses Other Grazers (copepods) Diatoms & Other Phytoplankton Cryptophytes Autotrophic Carbon Production Krill Salps Sedimentation (Microbial Loop) Respiration (Other Losses) Higher Trophic Levels (fish, penguins, whales) Partitioning Model Autotrophic Losses (Not Grazing)

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18 Conclusions for Case 1: 1) Phytoplankton community composition is
impacted by glacial melt 2) Small cryptophytes dominate the meltwater. 3) Small cryptophytes cannot be grazed efficiently by krill, salps replace the krill 4) This impacts the food web 5) The traditional sampling without context is useless. 6) Long term monitoring is needed to provide context, 7) Real-time data is needed to allow for adaptive sampling

19 Case Example 2: Newark Bay Contaminant Assessment and
Reduction Program

20 NB1 KVK PA New York Bight Hudson River Manhattan Hackensack River
Passaic River Newark Bay Kill Van Kull Arthur Kill Raritan Bay Raritan River Manhattan Staten Island New Jersey Brooklyn Sandy Hook = Mooring NB1 PA KVK Bight New York

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22 Newark Bay Perth Amboy cm/s

23 Transect Distance (km) Transect Distance (km)
Transect Distance (km) Transect Distance (km)

24 NB1 KVK PA CTD ADP OBS Battery Pack LISST Hudson River Manhattan
Hackensack River Passaic River Newark Bay Kill Van Kull Arthur Kill Raritan Bay Raritan River Manhattan Staten Island New Jersey Brooklyn Sandy Hook = Mooring NB1 PA KVK ADP LISST Battery Pack OBS CTD

25 Perth Amboy (PA) Mooring
Flood Ebb 8th th th th th th th nd

26 OBS ABS Lisst

27 Ebb Flood PA

28 ebb flood Particle Sizes Sediment Transport flood ebb PSA Transport

29 Emptying/filling mode
Flow through mode Day 63 Emptying/filling mode Day 81.8 Staten Island Staten Island

30 Conclusions for Case 2: 1) Sediment transport is dominated by tides.
2) Greatest concentrations during spring tides. 3) At Perth Amboy, transport is greatest during floods indicating a net transport into the Bay 4) Long term records indicate 2 modes to the subtidal flow 5) The traditional sampling without context is useless. 6) Long term monitoring is needed to provide context, 7) Real-time data is needed to allow for adaptive sampling

31 So, lets build system to do this
We need to know: What is in the water. Where it is going. Where it will be tomorrow. So, lets build system to do this

32 New Jersey Shelf Observing System (NJ-SOS)


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