Appendix C: Paleolimnological Sampling
(Sedimented Diatoms)
Diatoms and chrysophytes preserved in lake sediments are integrators
of lake history and make it possible to infer changes in other biotic
assemblages (Charles et al. 1994, Dixit et al. 1992). Environmental variables,
such as alkalinity, aluminum, dissolved organic carbon (DOC), salinity,
nickel, conductivity, calcium, total nitrogen, total phosphorus, Secchi
transparency, and "trophic state," have been inferred using diatom-based
predictive models (Charles et al. 1994, Dixit et al. 1992, Fritz 1990).
Sedimented diatoms samples are not subject to short-term temporal variability
as are other assemblages such as phytoplankton. A sediment surface sample
contains an integrated record of 1 to 3 years, and sediment cores can
be calibrated with other information (e.g., varves, known contamination
events, radioisotopes, pollen) to obtain time series with resolution of
up to 1 to 10 years.
The diatom fossil record can aid in establishing reference conditions.
Surface sediments represent contemporary lake conditions and usually integrate
the assemblage over 1 or more years (Dixit et al. 1992), whereas presettlement
conditions can be characterized by sediment cores of 0.5m to 1.0m depths
(Charles et al. 1994). Dating sediment cores is possible using pollen
or 210Pb (radon decay product).
Paleolimnological analysis, part of the EMAP protocol (USEPA 1994b),
requires development of a data set that associates current environmental
conditions with current surficial diatom assemblages. Present-day associations
are used to infer past conditions based on fossil diatom assemblages in
deeper sediment layers. The calibration process is usually done in two
steps. First is an evaluation of species-environment relationships and
statistical determination of which environmental characteristics can be
inferred using predictive models. Currently, this is done using Canonical
Correspondence Analysis (CCA) (Dixit et al. 1992, Jongman et al. 1987,
ter Braak 1986) frequently using the computer program CANOCO (ter Braak
1986). The second step is to develop the predictive models and calculate
error estimates (Birks et al. 1990, Charles and Smol l994). The computer
program WACALIB (Line et al. 1994) is an efficient way to perform these
calculations. Further documentation of these methods is in Charles and
Smol (1994), Charles et al. (l994), Birks et al. (1990), and ter Braak
and Juggins (1993).
Level of Effort
Analysis of an individual paleolimnological subsample (section of a core)
generally requires 1 to 4 hours,which is similar to other diatom and phytoplankton
analyses. In order to infer ancient conditions, a calibration data set
is necessary, consisting of surface sediment samples from 50 or more impaired
and unimpaired lakes. Standard diatom metrics, as well as similarity indices,
can be calculated (Table C-1).
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Table C-1.
Potential paleolimnological metrics.

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Methods
Field sampling - For sedimented diatoms can be relatively
fast. Field methods outlined below are the same as those used in EMAP
(USEPA 1994b)
Sample location - Sediment samples are obtained from or near
the deepest area of the lake. A single core is sufficient.
Sample collection - The procedure from the EMAP manual (USEPA
1994b) is followed for diatom analysis and is quoted here: Sediment cores
are collected from the deep, central area of a lake (at or near the index
site) using a modified K-B gravity corer (Glew 1989). Core samples are
extruded from the corer and subsectioned immediately after collection.
A core of at least 45 cm length is desired. The top and bottom lcm intervals
are collected from each core and placed in separate sealable plastic bags
along with wet paper towels to prevent desiccation. These intervals are
sectioned and removed from the core using an apparatus described by Glew
(1988). The sample bags are labeled with either standardized adhesive
labels or identification information is written on each bag using a permanent
ink marking pen. The bags prepared from a single core sample are placed
in a sealed container for storage and transport. Samples are kept at 4°C
until shipment. Detailed procedures for collecting and preparing core
samples are presented in the field operations manual.
Sample analysis - Analytical methods are the same as for sedimented
diatoms (Section 6.3) summarized in Table C-2.
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Table C-2.
EMAP analytical methods: sedimented diatoms indicator (from USEPA
1994b).

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Chapter 3 ~ Chapter 4 ~ Chapter 5 ~ Chapter 6
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Appendix A ~ Appendix B ~ Appendix C ~ Appendix D
Appendix E ~ Appendix F ~ Appendix G
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