US JGOFS Antarctic Environments Southern Ocean Process Study (AESOPS)

Palmer Leg 97-01; January-February 1997

Documentation for:  The Trace Metal Rosette Hydrographic bottle data

L.A. Codispoti (lou@ccpo.odu.edu)
Old Dominion University,  July 1998

General Comments:

This "readme" file pertains to the salinity, dissolved oxygen, and nutrient
data taken from the trace metal rosette that was equipped with 8 ~30-liter
"Go-Flo"  bottles during Palmer leg 97-01 (January-February, 1997). Dr. John
Marra of the Lamont Doherty Earth Observatory of Columbia University was the
chief scientist during this leg (jmarra@ldeo.columbia.edu).  This cruise was
the second process study leg of the U.S. JGOFS program in the Southern Ocean
(AESOPS).  The CTD system on the trace metal rosette was not capable of the
precision obtained from the system on the hydrographic rosette, and Go-Flo
bottles, while superior for obtaining trace metal clean samples, are not the
bottles of choice for obtaining hydrographic (salinity, oxygen, and nutrient)
data.  At times, bottle "firing" and data acquisition/processing problems also
complicated the interpretation of the data from the trace metal rosette, and
the trace metal rosette data from this leg underwent significant post-cruise
editing.  BECAUSE THESE DATA FROM THE TRACE METAL ROSETTE ARE NOT OF THE SAME
QUALITY AS THE DATA FROM THE HYDROGRAPHIC ROSETTE, THEY SHOULD BE MAINTAINED IN
A SEPARATE FILE.  IN ADDITION, IT SHOULD BE NOTED THAT SOME OF THE INITIAL
TRACE METAL DATA ROSETTE DATA PRODUCED DURING THE CRUISE CONTAINED SIGNIFICANT
DATA ACQUISITION AND PROCESSING ERRORS.


Some questionable data are not included in this report.  These data are
retained in files at Old Dominion University and are available upon request.

No units are given for salinity in this report because the most recent
definitions of salinity define it as a dimensionless number.  To accommodate
every preference, Winkler oxygen values are reported in ml/l, micromolar, and
micromoles per kg.  The latter values can only be calculated with a knowledge
of the oxygen sample temperatures when the samples were drawn. These "draw
temperatures" are not reported here, but can be obtained by contacting
lou@ccpo.odu.edu.  Nutrient values are reported in micromolar. They can be
converted to micromoles per kg, by combining laboratory temperature on the
Palmer (approx. 21 degrees C during this leg) and the salinity of the sample to
compute density and then dividing the value in micromolar by this number.


Methods:

In general, the methods employed for the bottle salinity, Winkler dissolved
oxygen, and nutrient analyses did not differ significantly from those described
in the JGOFS protocols that were distributed in 1994 (UNESCO, IOC Manual and
Guide #29). Minor differences included the following:  1) The weights of the
potassium iodate used for primary standards for dissolved oxygen were not
adjusted to an "in vacuo" basis as suggested in the protocols. It is unlikely
that this departure from procedure would cause significant errors. Our
calculations suggest that the maximum differences arising from our decision to
not correct to an "in vacuo" basis would be 0.02%.  2) The protocols give one a
choice of adjusting nutrient methods so that calibration curves are strictly
linear, or opting for more response and taking into account non-linearities. 
We choose the former method.  3) No corrections were made for "carryover"
between nutrient samples run on the Technicon Autoanalyzer.  Carryover effects
in our nutrient analyses are generally less than ~2% of the concentration
difference between adjacent samples, and were minimized by arranging samples in
depth order and by running duplicate samples in some cases.  4) Calibration and
re-calibration of volumetric ware were not exactly as described in the JGOFS
protocols.  5) Duplicate oxygen samples were not routinely drawn.  6) The JGOFS
protocols do not describe an automated technique for the determination of
ammonium concentrations.  We employed the Berthelot reaction using a method
somewhat similar to that described by Whitledge et al. (1981, Whitledge, T.E.,
Malloy, S.C., Patton, C.J. and Wirick, C.D. Automated Nutrient Analyses in
Seawater. Brookhaven National Laboratory Rept. BNL 51398, 216pp.).  Details on
this method can be obtained from Dr. Louis I. Gordon (lgordon@orst.oce.edu).


Temperature:

The temperature data associated with each bottle depth were taken by the CTD
system during the bottle tripping process.  


Sampling:

The samples in this report were taken from ~30 liter Go-Flo bottles. 

Bottles were generally held at the sampling depth for at least 30 seconds 
before tripping, BUT THE  RELATIVELY CALM CONDITIONS ON THIS CRUISE MAY HAVE
PREVENTED COMPLETE  FLUSING OF THE GO-FLO BOTTLES DESPITE THE 30 SECOND SOAK
TIME. NORMALLY,  INCOMPLETE FLUSHING WOULD MEAN THAT THE BOTTLE CONTAINED A
MIXTURE OF WATER FROM THE DESIRED SAMPLING DEPTHS AND FROM DEEPER  DEPTHS. 
EXAMINATION OF PAIRED BOTTLE AND CTD SALINITIES FROM THE HYDROGRAPHIC ROSETTE
SUGGESTED THAT INCOMPLETE FLUSHING OF THE  10 LITER BULLISTER BOTTLES USED ON
THAT ROSETTE OFTEN CREATED MIXTURES OF WATER WITH EFFECTIVE DEPTHS A FEW METERS
DEEPER THAN THE ACTUAL SAMPLING DEPTH.  IN THE CASE OF THE HYDROGRAPHIC ROSETTE
MOST OF THESE OFFSETS WERE LESS THAN 5 METERS,  BUT FLUSHING OF THE 30 LITER 
GO-FLO BOTTLES  ON THE TRACE METAL ROSETTE MAY HAVE BEEN POORER.   PAIRED CTD
AND BOTTLE  SALINITY DATA MAY BE OF SOME HELP IN ADDRESSING THIS FLUSHING
PROBLEM BUT THE CTD DATA FROM THE TRACE METAL ROSETTE HAVE NOT YET BEEN
CORRECTED FOR "SPIKING" THAT CAN OCCUR IN GRADIENTS AND FOR AN OFFSET OF  ABOUT
0.02 TO   (BOTTLE SALINITIES MINUS TRACE METAL CTD SALINITIES) IN THE TRACE
METAL CTD DATA.      


Salinity:

Salinities were determined with Guildline Autosal salinometers using JGOFS
protocols.  New vials of standard sea-water were used to standardize before and
at the end of every run.  These bottle salinities were, in general, about 0.02
higher than the  trace metal rosette's CTD salinities which are also reported
here in the absence of significant flushing or spiking problems (see above). 
Freezing in the Go-Flo bottles can also cause  bottle salinities to be higher
than the CTD values, but the cruise notes do not suggest that this was a
problem on this leg.  


Dissolved oxygen:

The Winkler dissolved oxygen apparatus was built and supplied by the SIO/ODF
group.  This system is computer controlled and detects the end-point
photometrically.  Temperature of the thiosulfate and standard solutions is
automatically monitored by this system.  

Nutrients:

Note that the terminology used to describe nutrients has become somewhat loose
over the years and that silicate=silicic acid or reactive silicate, and
phosphate=reactive phosphorus.  Nutrient analyses were performed on a 5-channel
Technicon II AA system that was modified and provided by Dr. Lou Gordon of
Oregon State University.

During an earlier Palmer Leg (96-04a) nutrient standards provided by Dr.
Gordon's group were compared with standards from the Ocean Data Facility (ODF) 
Group at Scripps and with standards purchased from Ocean Scientific
International (OSI) Leg 96-04a. The results of these comparisons were good.
Interested users may contact Dr. Louis I. Gordon (lgordon@oce.orst.edu) if they
are interested in the details of these intercomparisons.  The only notable
differences were a tendency for the OSI silicate values to be ~1% high relative
to the OSU standards, and 4% low relative to OSU nitrite standards.  We believe
that the OSI nitrite standards may be in error, but in any event, nitrite
values in the data reported from this leg were always less than 0.25
micromolar, so the error would be <0.01 micromolar even if the OSI nitrite
standards were correct. Because of the concentration of effort over the Ross
Sea shelf and the season, significant amounts on nitrite and ammonium could
occur throughout the water column.  Therefore, the usual method of looking at
deep-water values to assess nitrite and ammonium baselines could not be
employed.  Thus, there may be some baseline uncertainties in nitrite and
ammonium concentrations that would result in errors of less than ~0.1
micromolar for ammonium and less than ~0.02 micromolar for nitrite.  Tests of
the salt effect in the ammonium analysis during this cruise suggested that it
was unlikely to effect the results reported here by more than ~1%.  Because of
the low nitrite concentrations and Cd column efficiencies that appeared to be
always greater that 95%, the nitrate data from this cruise are not
significantly affected by changes in Cd column efficiency.


Queries:

Questions about these data may be addressed to:


Dr. L.A. Codispoti
CCPO
Old Dominion University
Norfolk, VA 23529
lou@ccpo.odu.edu