Woods
Hole Field Center
Geochemical
Sediment Analysis Procedures
U.S. Geological Survey Open-File Report 02-371
by S.A.
Jablonski, E.L. Mecray,
J.M. Munson, and D.S. Blackwood
Carbon:
The Woods Hole Field Center (WHFC) has the capability to measure organic,
inorganic, and total carbon contact using Coulometer and CHN Analyzers.
Total and organic carbon percentages are determined using the Perkin
Elmer 2400 Series II CHN Analyzer (Figure 1). From these analyses, one
can determine the percent inorganic carbon of a sediment sample by subtracting
the percent organic carbon from the percent total carbon:
%total carbon = %inorganic carbon + %organic carbon. Another instrument
available for the determination of inorganic carbon content in sediment,
is the UIC Coulometrics, Inc. Carbon Dioxide Coulometer with an acidification
unit
(Figure 2).
The organic carbon fraction in sediments is important because it serves
as a binding site for contaminant metals. The abundance of organic carbon
controls many diagenic processes. Normalizing contaminant data by the
% organic carbon allows for the distinction of specific anthropogenic
sources.
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Figure 1. Perkin Elmer
Series II CHN Analyzer.
Figure 2. Coulometer with Acidification Unit |
CHN
Analyzer procedures - The CHN Analyzer uses a combustion method to convert
the sample elements to simple gases (CO2, H2O,
and N2). The dried and ground sediment sample is first
oxidized using classical reagents like Silver Vanadate, Silver Tungstate,
and EA-1000, which is mixture of chrome and nickel oxides. Products produced
in the combustion zone include CO2, H2O,
and N2. Elements such as halogens and sulfur are removed
by scrubbing agents in the combustion zone. The resulting gases are homogenized
and controlled to exact conditions of pressure, temperature, and volume. The
homogenized gases are allowed to de-pressurize through a column where they
are separated in a stepwise steady-state manner and quantified as a function
of their thermal conductivities (Perkin Elmer Instruction Manual).
In order to measure %organic
carbon in sediment samples, one must first acidify the samples to remove all
inorganic matter. The inorganic material is removed by adding sulfurous acid
to the sediment so the inorganics will turn to gas and leave the sample. Using
this method, only the organic material is analyzed by the CHN Analyzer (Verardo,
David J. et. al).
Coulometer procedures - The Coulometer provides an
accurate and absolute determination of the concentration of carbon dioxide (CO2)
evolved from an acidification process. The coulometer cell is filled with a
cathode and an anode solution (proprietary through UIC) with a colorimetric
indicator. A platinum cathode and a silver anode are positioned in the cell
and the assembly is positioned between a light source and a photodetector in
the coulometer. When a gas stream passes through the solution, CO2
is quantitatively absorbed, reacting with the elements in the cathode/anode
solutions to form a titratable acid. This acid causes the color indicator to
fade. Photodetection monitors the change in the solution's color as percent
transmittance (%T). As the %T increases, the titration current is automatically
activated to stoichiometrically generate a base at a rate proportional to the
%T. When the solution returns to its original color (original %T), the current
stops (UIC Coulometrics Instruction Manual).
Equipment used for these procedures includes the instruments described above
(Perkin Elmer 2400 Series II CHN Analyzer and a UIC Coulometrics Coulometer
with an Acidification Unit), as well as a ball-mill grinder used to grind
the dried sediment sample to a fine powder, ovens used to insure the sample
is dry, desiccators used to cool and store samples in a moisture-free environment,
and the chemicals involved in the analysis process.
Geochemistry:
This laboratory is equipped to handle wet sediment samples (cores and
grabs) as they are returned from field collection. Samples are collected
from marine and coastal areas and returned to the laboratory for analysis.
Cores are sectioned and sub-sampled using titanium tools to minimize
contamination (Figure 3). Samples from cores and grabs are freeze-dried
(Figure 4) and sent to contract laboratories for various analyses including
toxicity tests, mercury concentrations, foraminifera identification,
pollen counting, nitrogen isotope analysis, and organic and inorganic
contaminant concentrations.
Core sectioning procedures - A fully illustrated
tutorial on the methods used at the Woods Hole Field Center is presented
in this publication.
Freeze Drying procedures
- A fully illustrated tutorial on the methods used at the Woods Hole
Field Center is presented in this publication.
Freeze drying is a process whereby water is removed from frozen materials
by converting the frozen water directly into its vapor without the intermediate
formation of liquid water. The basis for this sublimation process involves:
the use of a vacuum pump to enhance the removal of water vapor from
the surface of the sample; the transfer and deposition of water vapor
onto the condenser; the removal of heat, due to ice formation, from
the condenser by means of a refrigeration system. In essence, the freeze
dry process is a balance between the heat absorbed by the sample to
vaporize the water and the heat removed from the condenser to convert
the water vapor into ice (LABCONCO Instruction Manual).
The vacuum environment is important as it speeds the sublimation process
by removing atmospheric pressure which would act to contain the molecules
in liquid form.
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Figure 3. Sampling
a core using a hydraulic extruder.
Figure 4. Freeze Dryer unit
|
Equipment used for the procedures in this laboratory includes the instrumentation
mentioned above (hydraulic core extruder and freeze dryer), as well as acid-washing
baths to clean the titanium spatulas, and a sample splitter to get a non-biased
sub-sample.
Radiochemistry:
This laboratory is equipped to determine gamma decay emissions from
dried sediment samples. This method allows for the determination of
the sample's age and the sedimentation rates in sediment cores. Two
types of gamma detectors are used: well-type (Figure 5) and planar-type
(Figure 6). These high purity germanium (HPGe) detectors are in constant
use and are located in a shared laboratory on the Woods Hole Oceanographic
campus.
Radioisotopes, such as Pb-210 and Cs-137, can be measured by gamma
emission and used in conjunction with a numerical model to estimate
sedimentation rates. These measurements are important in modeling chronological
changes such as heavy metal pollution. The WHFC conducts studies in
the New York Bight (NYB) and in Long Island Sound (LIS) because they
are in close proximity to high-density population centers and sewage
dumping. Anthropogenic sources have added metals, carbon, bacteria,
and organic contaminants to the sea floor. Although these pollutants
have been dispersed over time, they are still present in the sedimentary
record and can be measured. Cs-137 is a fallout isotope produced from
bomb tests in the 1950's and 1960's and since it is not a naturally
occurring isotope, it is known that the onset date for this isotope
is 1954 and this information can be used to date the sediment cores
collected from those areas (Santschi et al, 1999).
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Figure 5. Well-type
Gamma Detector.
Figure 6. Planar-type Gamma Detector
|
Well and Planar-type detector procedures - A fully
illustrated tutorial on the methods used at the Woods Hole Field Center is provided
in this publication. These detectors produce output pulses directly proportional
to the energy of the gamma ray. The HPGe detectors are semiconductor diodes
and require liquid nitrogen to cool the system reducing the leakage current
and therefore reducing the noise and increasing the resolution.
Freeze Dryer procedures - A fully
illustrated tutorial on the methods used at the Woods Hole Field Center is provided
in this publication.
Instrumentation for these procedures requires both a well-type and a planar-type
HPGe detector and a freeze dryer unit.
Biogenic
Silica:
The WHFC has the capability to digest sediment samples to be further
analyzed by Inductively Coupled Plasma - Emission Spectrometry (ICP-ES)
for biogenic silica. Biogenic silica fluxes indicate ecosystem productivity
over time. The WHFC does not, at this time, have the instrumentation
to analyze the biogenic silica extracts, so contract laboratories are
used.
Biogenic silica digestion procedures - A
fully illustrated tutorial on the methods used at the Woods Hole Field
Center is provided in this publication. The method used is adapted from
Mortlock, R.A. et. al (1989).
Equipment for this procedure includes a heated shaker bath (Figure 7)
to resuspend the sediment and a centrifuge
(Figure 8) to help remove the supernatent, as well as ovens to dry sediment
samples, a mortar and pestle to grind the sediment samples, a balance
to weigh samples, a vortexer to swirl the samples, a sonicator to break
up sample particles, and the chemicals used in the preparation of the
sediment samples.
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Figure 7. Heated Shaker
Bath.
Figure 8. Centrifuge. |
This report is preliminary and has not been reviewed for conformity with U.S. Geological Survey editorial standards (or with the North American Stratigraphic Code). Any use of trade, product, or firm names is for descriptive purposes only and does not imply endorsement by the U.S. government.
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