Table of Contents:
Cruise Narrative
Figure 1. Cruise
Track
Individual Reports
Zooplankton
Preliminary
Zooplankton Results
Carbon
Production
Optics/Primary
Production
Table 2. Sampling operations and
samples collected
Appendix A. Personnel
List
Appendix B. Event
Log
Appendix C. Hydrographic Data
Acknowledgements
We appreciate and acknowledge the efforts and professionalism of the officers
and crew of the ALBATROSS IV. Their assistance and cooperation made the success
of this cruise possible.
This report was prepared by Jim Gibson, with inputs from
all Principal Investigators. The
contributions of Pilar Heredia, who maintained the event log during the cruise
and Maureen Taylor, who prepared the hydrographic data, were greatly
appreciated.
The US-GLOBEC Georges Bank research project is sponsored by
the National Science Foundation and the National Oceanic and Atmospheric
Administration. All data in this report
are to be considered preliminary.
Individual
Reports
Zooplankton Abundance, Physiological Condition, and Growth
Rates
( J.
Gibson, P. Heredia, A. Jacquet, D. Schreiber)
Objectives
(1) To collect
zooplankton samples at pre-selected priority 1 Broadscale standard stations during the long interim between
Broadscale survey seasons.
(2) To determine the
size (length, carbon, nitrogen) and condition (condition factor, RNA/DNA ratio) of Calanus finmarchicus at selected sites on the
Bank.
Methods
Zooplankton tows were made with the 1-m2 MOCNESS
equipped with five 150 _m mesh nets and cod ends. Tows were single oblique from the surface to a maximum depth of 10
m. off the bottom or 500 m. The depth
stratum sampled were: 0-bottom; bottom-100m; 100-40m; 40-15m; and 15m-0. The net #0 was used as the down net, and nets
#1, 2, 3 and 4 for the up-cast.. Winch rates were 15-20m/min. to control
volumes filtered and maintain a frame angle near 45 degrees. Once back on board, the nets were gently
rinsed with seawater into corresponding 5 gal. buckets and transported into the
wet lab. Samples with a large biomass
were split prior to preservation, using a 2-L plankton splitter. Samples were then preserved in 10% formalin.
At stations 38 (night), 29 (day) and WB, the bottom and
surface nets (#1 and #4) were not immediately preserved. 50 Calanus finmarchicus stage 5 copepodites were sorted from the
bottom net only, using dissecting microscopes.
Calanus abundance's in the surface net were to low to collect enough
animals. The animals were recorded using
a video system for length measurements, and were either placed in a tin boat and
dried over desiccant for carbon analysis or put into cryotubes and frozen in
liquid nitrogen for RNA/DNA determinations.
Prior to every MOC-1 tow, a vertical cast with a Seabird Electronics Seacat
model 19 profiling instrument (SBE19 Profiler) was done to measure temperature
and salinity, with depth. The Seabird
CTD was clamped to the boom wire and a 45-kilogram (kg) ball was attached to
depress the sampler.
Productivity
Organic and Inorganic Carbon Production in the Gulf of
Maine.
(L.
Graziano, D, Drapeau, S, Dunford, B, Vallincourt)
Two main types of measurements were made: productivity/calcification rates
of phytoplankton, and optical backscattering.
1.
Productivity: Calcification and
organic production rates were measured in profiles at 12 stations, and in 8
additional surface samples. One bottle
per depth was incubated with 14C-HCO3 for 24
hours, at simulated in situ temperature and light quantity and quality. Surface samples were taken from the ships
seawater system while underway. For
profiles 6 depths were used, and an additional bottle was incubated in the
dark. Water was collected from Niskin
bottles after determining appropriate depths, based on percentage light. A Biospherical PNF (Profiling natural
fluorescence) meter was lowered at daytime stations to collect light, depth
temperature, and fluorescence data. A
Secchi disk was also used to measure to 1% light depth. Water was collected from depths at 90%, 50%,
20%, 10%, 5%, and 1% of surface irradiance.
Depths were estimated at night-time stations.
100 mL water/bottle was spiked with 50 _Ci 14C. Subsamples were immediately taken for total 14C (100
_L) and for time-zero radioactivity in particulates (2 x 50 mL, filtered). After incubation for 24 hours 2 x 50 mL from
each bottle was filtered to collect particulate material. Each filter represented organic and inorganic
carbon production over 24 hours. Filters
were processed on board to separate organic and inorganic carbon into two
different vials. Radioactivity in each
vial was measured on a scintillation counter at Bigelow. Total number of bottles incubated: 92. Total number of vials:
472.
For each bottle incubated, samples were collected for particulate calcite
(100 mL filtered) and cell and Coccolith counts (60 mL preserved in buffered
formalin). A total of 81 calcite samples
and 76 preserved sampled were collected.
2. Underway
backscattering measurements: A
flow-through system continuously measured fluorescence, temperature, salinity,
pH, and optical backscattering before and after dissolution of calcite, at all
times while the ship was underway.
Backscattering was also measured on discrete samples at six depths at
each station.
Optics/Primary
Production
Complete Optical Datasets Throughout the Gulf of
Maine
(Dave
Phinney, J Hopkins, Doug Phinney, J Brown)
Our cruise activities aboard the Albatross IV were performed in support of a
NOAA grant entitled 'Development and Validation of Regional Time-Varying Coastal
Marine Algorithms: Gulf of Maine - A
Case Study'. This grant is primarily
devoted to the development and validation of regional ocean color remote sensing
algorithms for the Japanese Ocean Color and Temperature Scanner (OCTS) launched
in September, 1996, and the forthcoming NASA Sea Wide Field-of-view Sensor
(SeaWiFS). Ocean color algorithms are
the mathematical equations which derive ecological and oceanographic parameters
such as phytoplankton chlorophyll or ocean transparency from the spectral water
leaving radiance (light) measured by the satellite sensor from space. In order to build such algorithms, precise
measurements of the optical properties of ocean waters, the concentrations of
optically active substances found in these waters and the quantity of spectral
light exiting the ocean must be made in a variety of oceanographic regimes. Of particular importance to this project is
the goal of building regionally specific algorithms for the Gulf of Maine,
hence, the opportunity to collect measurements in the highly variable region
around Georges Bank in November was deemed valuable. This work is conducted in cooperation with Dr. W.M. Balch at
Bigelow Laboratory, Dr. J. Zaitzeff at NOAA/NESDIS and Dr. J. Brock at NOAA
Coastal Services Center in Charleston, SC.
Objectives
The objective of this work is to collect complete optical datasets in diverse
water mass types throughout the Gulf of Maine in support of ocean color
algorithm develop-ment. This includes
measurements of 1) the inherent optical properties of absorption and scattering,
2) concentrations and distributions of optically active substances such as
chlorophyll, colored dissolved organic matter (CDOM), total suspended solids,
phyto-plankton identification/enumeration, and cell size spectra, 3) optical
reflectance spectra at the sea surface and 4) calibrated spectral water leaving
radiance. Dr. Balch's group also
collects total and calcite specific backscattering data as well as particulate
calcite and particulate organic carbon concentrations. All of these optical measurements are made within the context of
traditional physical oceanographic measurements of salinity, temperature and
density. We participated in twelve
stations during the cruise, one on top of
the bank, one in Wilkinson Basin and ten around the periphery of Georges
Bank.
Instrumentation and Methods
A profiling package was used to continuously measure the physical and optical
properties of the water column as a function of depth to 75m. The package consisted of a SeaBird SeaCAT 19
CTD, WetLABS miniature in situ fluorometer configured for
chloro-phyll fluorescence, and a WetLABS AC9 nine channel spectral
absorption/attenuation. meter. The
package was deployed at a nominal rate of 20 meters/min. The SeaCAT 19 measures temperature,
conductivity and pressure at 2Hz as well as logging companion data from up to
two external sensors. The CTD operates
in autonomous mode logging the data internally as well as powering a sample pump
and external sensors. The external
sensor was a WetLABS miniature chlorophyll fluorometer used to measure the
distribution of phytoplankton biomass as a function of depth. All the data were downloaded to a laptop
computer after the cast, with salinity and density calculated by standard
subroutines as Practical Salinity Units (PSU) and sigma-t, respectively. The fluorometer was calibrated by discrete
determinations of chlorophyll from Niskin bottle samples. The WetLABS AC9 measured the inherent optical
properties of absorption (a) and attenuation (c) at nine wavelengths which
closely match the satellite sensor bands: 412, 440, 488, 510, 560, 630, 650,
676 and 715nm. Attenuation is the sum of
absorption and scattering (b), such that by measuring a and c, b may be obtained
by difference. The meter uses two
enclosed cuvettes to measure optical properties of pumped sample water over a
25cm path length: 1) the attenuation side is similar to a beam transmissometer
utilizing a blackened cuvette and a well defined beam of light to measure the
total loss of light from the beam over the path length and 2) the absorption
side uses the 'shiny tube' approach and a diffuse light source which accounts
for all internal reflections in a diffuse light field where absorption dominates
scattering. Data were transmitted via
hard wire in real-time and collected to a laptop computer and converted to
standard coefficient units of m-1. These
total absorption and attenuation coefficients reflect the influence of all
optically active materials present in the water column.
Discrete water samples were collected at six depths throughout the water
column using 5L Niskin bottles hung on the hydrographic wire immediately
following the optics cast. Salinity
samples for calibration of the CTD were collected from surface and deep bottles
only. Sample volumes were collected for
particulate and CDOM absorption, and chlorophyll determinations on-board, with
additional volumes collected for total suspended solids, phytoplankton
enumeration/identification and cell size spectra to be analyzed after the
cruise. Total absorption can be further partitioned as the sum of the
absorption due to water (which is a constant) plus optically active particulate
matter plus dissolved colored organic matter (CDOM). We measured particulate and CDOM spectral absorption independently
using a Baush and Lomb dual beam spectrophotometer between 350 and 750nm (1.6nm
resolution), which also served as a check on the performance of the profiling
instrument. Particulates from 100-1000ml
were harvested on pre-weighed Whatman GFF glass fiber filters and placed upright
in the dual beam spec with a blank wetted filter as a reference. Spectral absorption was scanned and stored in
a computer as log base 10 measurements of optical density. Absorption coefficients (m-1) were calculated
by converting optical density at each wavelength to natural log, multiplying by
a beta factor which corrects for the increased path length due to scattering
within the glass fiber filter and dividing by a factor relating the volume of
sample filtered to the geometric path length.
CDOM absorption was measured on 0.2 micron filtered seawater placed in
10cm cuvettes in the spectrophotometer.
Similarly filtered Nanopure water
was used in the reference cuvette.
Optical density values as a function of wavelength were converted to
natural log and multiplied by 10 to arrive at units of m-1. Chlorophyll a and phaeo-pigment concentrations were
measured fluorometrically: replicate
100ml samples were filtered through Millipore HA 0.45micron filters and cold
extracted for 24 hours prior to analysis.
The Turner Model 111 fluorometer was calibrated using chlorophyll a from spinach (Sigma Chemical
Co.).
Samples for total suspended solids were stored by placing the unfolded
particulate absorption filters into plastic Petri slides (Millipore Corp.) in
the freezer. At the lab, filters were
dried and reweighed to determine total suspended solids concentration in
mg/L. Samples for phytoplankton analyses
were collected at selected depths (3 per station) and stored in two ways: 1)
small raw sample volumes (3ml) under liquid nitrogen to preserve fluorescence
for analysis by flow cytometry and 2) 100ml volumes with the addition of Lugol's
iodine for microscopic analyses of settled samples. Flow cytometric analysis will be performed using a Becton-Dickinson
FACScan cytometer which measures light scatter and fluorescence simultaneously
from individual particles at rates to 1000 per second. Total particle counts are gated on chlorophyll fluorescence in
order to obtain counts of phytoplankton, by knowing the volume of sample
analyzed, concentrations per ml can be calculated. A size distribution curve is generated from the light scatter
measurements for both total and chlorophyll containing groups. However, this data is ataxonomic, and cell
populations must be identified by microscopic examination and counted by flow
cytometry. Cell identification of larger
cells will be performed on settled samples using a Zeiss inverted microscope,
smaller cell sizes will be identified to the lowest taxon possible using a Zeiss
Axiomat microscope. M. Keller of
Bigelow Laboratory is responsible for the phytoplankton identification and
enumeration work, flow cytometry will be performed in cooperation with the Jane
J. MacIsaac Flow Cytometry Facility at Bigelow.
Spectral reflectance and water leaving radiance at the sea surface were
measured in seven bands matched to the satellite sensors by a Satlantic TSRB II
tethered surface reflectance buoy. The
buoy was deployed for 15 minutes at each daytime station and measured
downwelling incident surface irradiance above the sea surface and upwelling
radiance just below the surface at 406, 412, 443, 490, 510, 555 and 670nm six
times per second. Upwelling radiance in
engineering units of mW nm-1 s-1 sr-1 were calculated from raw detector counts
compared to a calibration file. Surface
spectral reflectance was calculated by correcting the downwelling irradiance for
immersion effects (reflection as a function of solar angle and refraction at the
air/water interface) and propagating each waveband through the water to the
depth of the upwelling sensor (0.7m).
Reflectance was calculated as the ratio of upwelling to downwelling light
at each wavelength.
Samples Collected
Stations 12
CTD/fluorometer casts
12
Wet salinities 24
AC-9 casts 12
TSRB II deployments 4
Chlorophylls
136
Particulate absorptions
68
CDOM absorptions
68
Total suspended solids
68
Phytoplankton ident/enum.
36
Preliminary Results
We were only able to reach the bottom of the seasonal thermocline at deep
water (>150m) stations north of the bank and in Wilkinson Basin (stations 38
day and night, 34, 29 day, FB1, FB2 and WB1) with our 75m casts. Various mixed layer depths were found with
evidence of the onset of autumnal erosion of the surface warmed layer. Shallow (<100m) stations south of the bank
(3 and 9) displayed stepped physical structure indicative of convective
cooling. Shallow stations at the eastern
end and on top of Georges Bank (18, 20 and GB) were vertically homogeneous due
to tidal mixing. TSRB buoy casts were
obtained in each of these provinces.
Water column optical properties were strongly dependent on particle
distributions, the distribution of CDOM was nearly constant at low levels
representative of oceanic conditions with little influence from freshwater
sources. Particulate absorption curves
were dominated by phytoplankton with little effects of suspended sediments, even
on top of the bank. Chlorophyll
concentrations varied by a factor of 10-12, with 60m samples at deep stations on
the order of 0.5mg/m3 and sub-surface chlorophyll maximum samples
>6.0mg/m3. Average surface
concentrations were 3-4mg/m3. We are
pleased with the variety of water masses sampled and the excellent assistance of
the officers and crew of the R/V Albatross IV and Chief Scientist Jim
Gibson.
 
CRUISE NARRATIVE
The cruise aboard ALBATROSS IV (ALB-9612) departed Woods Hole at 1600 on Monday, November 4,
1996. It was determined that there would
not be a watch schedule for the scientific party. On station operations would begin with the AC-9, Niskin bottle
cast, PNF light meter, Secchi disk, TSRB light buoy, followed by the CTD and
MOCNESS. The light meters were only
deployed when we arrived on station during the day light hours. The vessel arrived on station 38 at 0016 on
Nov. 5. After the first few stations,
an efficient routine of sampling operations was established for the duration of
the cruise. Excellent weather
conditions, minimal technical problems and help from the crew of the ALBATROSS
IV throughout the entire cruise, allowed the scientific party to complete the
survey ahead of schedule.
The MOC-1 stations occupied were Broadscale standard
stations 38, 3, 9, 18, 20, 29, and 34 .
Stations 29 and 38 were sampled twice for a night/day comparison. In order to obtain a night and day sample at
Sta. 29, stations GB, FB1, and FB3 were added to allow a 12 hr interval between
sampling. Station GB was selected inside
the 60 m isobath to obtain productivity measurements on the Crest of Georges
Bank. Stations FB1 and FB3 were selected
to provide spatial information on zooplankton species composition and abundance
in Franklin Basin. The second arrival at
Station 38 occurred at 1220 on Nov. 7 which was ideal for the day-time sample.
At the completion of the station at Murray Basin (MB),
sampling operations were terminated and the vessel steamed to Woods Hole,
arriving at 0810 on Friday, Nov. 8.
Preliminary
zooplankton results
In all stations observed, Centropages hamatus and typicus. were the dominant
copepods. Centropages spp were found in all depth
strata sampled, concentrations were greatest at the surface. Pseudocalanus spp. appeared in low abundance at stations 3, 9, 18
and 20. Calanus finmarchicus was abundant at station 34, 38 (Great South
Channel), 29, Wilkinson Basin, and Murray Basin (Gulf of Maine).
Table 1:
Net# | Station | Local Time | Comments |
---|---|---|---|
4 | 38 | 0156 (night) | A mixed sample, mostly Centropages spp. Very low amount of biomass. No predators. |
1 | 38 | night | Some C. finmarchicus (C5, C6F
and C6M), C. hyperborous, and Metridia lucens but mostly Centropages spp. Some Euphausids and shrimps. |
4 | 38 | 1237 (day) | All Centropages spp. |
1 | 38 | day | C. finmarchicus and a few Euphausids. |
4 | 29 | 0806 (day) | Centropages spp. and Ctenophores. |
1 | 29 | day | C. finmarchicus plus predators (Shrimps, Euphausids). |
4 | 29 | 2307 (night) | Centropages spp. and large predators (Shrimps, Euphausids, and Amphipods) |
1 | 29 | night | C. finmarchicus, No large predators |
This table shows our observations on the
day/night samples collected at standard stations 38 and
29.
Net 1 = collected samples from bottom to
100m.
Net 4 = collected samples from the 15m to
surface.
At Standard
Stations 29, 34, 38, and WB, animals near the bottom were mostly C. finmarchicus C5's and C6 adult females. Within these
concentrations, the C5 stage comprised 90% of the biomass. These animals had very large oil sacs, which
indicates that they are in, or beginning diapause. Very few C.
finmarchicus were found in the surface samples. Diurnal and nocturnal (or Vertical) migration of zooplankton was
observed at stations 38 and 29 (see Table 1).
Large predatory zooplankton (Shrimps, Euphausids, Amphipods, Ctenophores,
Salps, and Siphonophores) were found in the depth strata from bottom to 100m, in
the samples collected during the day.
While in the samples collected at night, these predators were found in
the top 15m. On the bank, Chaetognaths
and Amphipods were the dominant predators.
At Franklin Basin, Salps and other gelatinous plankton comprised most of
the biomass. More accurate enumerations
will be completed in the lab.
Table 2: Sampling operations and samples collected during cruise AL96-12
Gear | Tows/Cast | Number of Samples |
---|---|---|
Seabird CTD | 13 casts | |
MOCNESS, 1-m2 | 14 tows | 61 preserved, 10% formalin |
Niskin bottles | 12 casts | 69 samples collected. |
AC-9 | 12 casts | |
Flow-through sampler | 8 stations | |
Secchi disk | 4 casts | |
PNF light meter | 2 casts | |
TSRB light buoy | 4 casts |
 
APPENDIX A
Scientific
Party
Name Title
Organization
James Gibson Chief
Scientist URI/GSO, Narragansett,
RI
Pilar Heredia
Scientist URI/GSO, Narragansett,
RI
Alyce Jacquet
Scientist URI/GSO, Narragansett,
RI
Dorothee Shreiber
Scientist URI/GSO, Narragansett,
RI
Lisa Graziano
Scientist Bigelow Lab Oce.
Sci. ME
David Drapeau
Scientist Bigelow Lab Oce.
Sci. ME
Suzanne Dunford
Scientist Bigelow Lab Oce.
Sci. ME
Bob Vallincourt
Scientist Bigelow Lab Oce.
Sci. ME
David Phinney
Scientist Bigelow Lab Oce.
Sci. ME
Jim Hopkins
Scientist Bigelow Lab Oce.
Sci. ME
Douglas Phinney
Scientist Bigelow Lab Oce.
Sci. ME
Jeff Brown
Scientist Bigelow Lab Oce.
Sci. ME
ALBATROSS
IV NOAA Officers and Crew
Derek Sutton
CO
Jason Maddox
XO
Joel Michalski
NAV
Kevin Cruse
CME
John Hurder
1AE
Charles Hersey
2AE
Orlando Thompson
EU
Royce Folks
GVA
Kenny Rondeau
CB
Willy Amaro
SF
Tony Romao
SF
Anthime Brunette
F
Tony Alvernaz
LF
Doug Roberts
GVA
Richard Whitehead
CS
Ernest Foster
GVA
O.C. Hill
GVA
Henry Jenkins
RET
Neal Lynch
NAV
APPENDIX B
Key to Instruments Used:
SG Shotgun surface sample
AC-9 9 channel spectral absorption/attenuation
meter
Nskn-bottles Water collection with Niskin
bottles
SeabirdCTD SBE Seabird profiler
MOC1 1 m2 MOCNESS
PNF Biospherical Profiler for natural
fluorescence
TSRB Tethered surface reflectance
buoy
Secchi Secchi disk
The event log for AL96-12.
APPENDIX C
Hydrographic data from the SBE Seabird CTD cast prior to
each MOC 1 tow.