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Core OL-92 from Owens Lake, southeast California

Diatoms present in sediments

J. Platt Bradbury
U.S. Geological Survey, Denver, Colorado

Contents:

Introduction

A total of 294 samples (154 samples from core 1; 129 samples from core 2 and 11 samples from core 3) from Owens Lake, Inyo County, California were examined for diatoms to document Quaternary paleolimnological changes of this record.

Methods

Approximately 0.5 cc of dry sample was placed in a 15 ml graduated test tube and covered with about 5 ml concentrated HNO3. After cessation of CaCO3 reaction, the test tubes were placed in 100o C hot water bath for 30 minutes to dissolve remaining carbonates and related minerals and to oxidize organic matter. When cool, the acid was diluted with distilled water and dissolved substances in the supernatent liquid were removed by decantation following centrifugation. Rinsing, centrifugation and decantation were repeated until all dissolved materials were removed from the processed material. The processed sediment was then allowed to settle in the tubes overnight, and the volume of water-saturated sediment was determined in the graduated tube. The water-saturated sediment was then suspended in 10x its water-saturated volume. Three drops of the diluted suspension were placed in a 50 ml settling dish that contained an 18 mm diameter coverslip. Water was added to the settling dish to resuspend the sediment-laden drops so the sediment and diatoms could settle evenly over the coverslip and floor of the settling dish (e.g. Battarbee, 1974).

After 3 hours, the water was removed from the settling dish by micro- capillary wicking and the coverslips were allowed to dry. Coverslips were mounted in hyrax, a refractive mounting medium (n = 1.65). Diatoms were enumerated at 1000x magnification along transects measured by stage micrometer until at least 30 mm of transect were examined or until at least 300 diatoms were counted. Because the water-saturated sediment volumes were all proportionally diluted (10x) and because the same volume (3 drops) of suspended sediment was placed in each settling dish, the diatoms encountered per mm of transect in each sample gives an approximation of diatom concentration in the sample.

The technique can only be approximate for the following reasons: (1) The original samples contain variable amounts of soluble minerals (mostly carbonates) and digestion therefore variably concentrates diatoms. (2) Samples rich in glacial flour, silt, clay, or diatoms behave differently during suspension and delivery to the settling dish so that different amounts of residue may be deposited onto the coverslip. (3) Measured volumes in graduated 15 ml test tubes and by drops from disposable pipettes have inherent inaccuracies. (4) Diatoms are variably fragmented and enumeration techniques discriminate against small fragments. Nevertheless, the variation in numbers of diatoms in the samples is greater than the variability in lithologies and quantification techniques. The results can be considered consistently semi-quantitative and provide a useful measure of diatom concentration.

Diatoms were identified as closely as possible to descriptions of taxa in standard texts or placed in an open nomenclature. However, the diatom flora of the western United States is poorly known, and some taxa from Quaternary deposits of distinctive paleolimnological environments are probably new to science. In some cases such taxa are recorded by "cf." or "aff." on the original worksheets; in other cases they are lumped together with the nearest taxon of similar morphological appearance. Typically diatom preservation is variable and often quite poor in Owens Lake sediment because of breakage and corrosion. The raw counts presented in Appendices 1 and 2 represent whole valves and (or) large (> 40%) fragments of valves. Table 1 provides the provisional species names represented by the coded abbreviations on the spreadsheets.


Table 1. Column headings in data tables
ach
Achnanthes (total)
amp-cof
Amphora coffaeiformis
amp-oval
Amphora ovalis
amp-per
Amphora perpusilla
ano-cos
Anomoeoneis costata
ast-form
Asterionella formosa
au-amb
Aulacoseira ambigua
au-gr
Aulacoseira granulata
au-isl?
Aulacoseira islandica?
au-sarc
Aulacoseira subarctica
au-sol
Aulacoseira solida
cal
Caloneis (total)
cam-cly
Campylodiscus clypeus
cam-smo
Campylodiscus sp? a smooth morphotype perhaps related to Surirella hoffleri.
chaet
Chaetoceros muelleri (usually spores)
coc
Cocconeis spp. (total)
coc-neot
Cocconeis neothumensis
coc-plac
Cocconeis placentula
cyc-bod
Cyclotella bodanica
cyc-casp
Cyclotella caspia
cyc-men
Cyclotella meneghiniana
cyc-oce
Cyclotella ocellata
cyc-quil
Cyclotella quillensis
cymb
Cymbella spp. (total)
cyst-opn
Cyclostephanos sp. (open center, with loosely packed areolae)
epi
Epithemia spp. (total)
fr-brev
Fragilaria (Pseudostaurosira) brevistriata
fr-cap
Fragilaria caupucina
fr-con
Fragilaria (Staurosira) construens
fr-crot
Fragilaria crotonensis
fr-lepto
Fragilaria (Staurosirella) leptostauron
fr-pin
Fragilaria (Staurosirella) pinnata
fr-vau
Fragilaria vaucheriae
gom
Gomphonema spp. (total)
gyro
Gyrosigma spp (total)
hz-am
Hantzschia amphioxys
mel-hudt
Melosira hustedti
mel-var
Melosira varians
nav
Navicula spp. (total)
nitz
Nitzschia spp. (total)
nz-frust
Nitzschia frustulum
nz-mono
Nitzschia monoensis
nz-pus
Nitzschia pusilla
pin
Pinnularia spp. (total)
rho-con
Rhopalodia constricta
rho-gbr
Rhopalodia gibberula
rho-gib
Rhopalodia gibba
rhoi
Rhoicosphenia curvata
st-ast
Stephanodiscus asteroides
st-carc
Stephanodiscus sp. cf. St. carconensis
st-fn/ecc
Stephanodiscus sp. a finely-structured eccentric species
st-min
Stephanodiscus minutulus type
st-nia
Stephanodiscus niagarae
st-ore
Stephanodiscus oregonicus
st-ovecc
Stephanodiscus sp. (oval and eccentric form)
st-parv
Stephanodiscus parvus
st-10
Stephanodiscus sp. (similar to #10 of Stoermer e.p.). Maybe a Cyclostephanos species.
sur-str
Surirella striatula
sur-ova
Surirella ovalis type
syn-acus
Synedra acus
syn-maz
Synedra mazamaensis
syn-rum
Synedra rumpens types
syn-uln
Synedra ulna
d/mm
diatom valves per mm of transect
count
total diatom valve count
trav
traverse length in mm

Results

The graphic representation of diatom counts (Figs. 1-18) are plotted against composite stratigraphic sequence based on Owens Lake cores 1, 2, and 3. A minor stratigraphic overlap may exist between the base of the uppermost core (7.122m, Core 3) and the top of underlying Core 1 (7.02m). The distribution of Cyclotella ocellata across the boundary also suggests a potential overlap (Appendix 1). For the stratigraphic plots (Figs. 1-20) the overlapping depths between Cores 1 and 3 have been adjusted to eliminate possible stratigraphic overlap. There appears to be no stratigraphic overlap between the basal sample of Core 1 (61.12m) and the top sample of Core 2 (61.31m).

Overall, Figures 1-18 document rapid fluctuations of numbers of individual diatom taxa counted, even over short stratigraphic intervals. Diatom concentration, calculated as the number of all diatom valves encountered per mm of microscope transect (Fig. 19) also varies widely between adjacent samples, particularly in zones where saline diatoms are abundant. Throughout its history, Owens Lake was extraordinarily sensitive to hydrologic and climatic change, sometimes oscillating between a large, through-flowing, freshwater lake and a saline playa over short periods of time. Stratigraphic and paleolimnologic continuity is better developed during periods when the lake was fresh and overflowing than when it was shallow and saline. For example, the most closely spaced samples (e.g. Core 1; 9.5 - 19.0 m) are about 20 cm (~250 yr) apart (Fig. 20). Within this interval, the concentration of Asterionella formosa, a freshwater planktonic diatom documents cycles of limnological change during the full glacial (15.9 - 25.3 ka) at millennial to sub-millennial scales. The greater stratigraphic continuity during fresh, high-water stages probably reflects more stable limnologic environments that favor deposition rather than short cycles of deposition and erosion characteristic of low and saline lake stages.

It is clear that at least parts of the Owens Lake cores have the potential for high resolution studies of climate change if detailed chronologies can be established.

The diatoms of the Owens Lake core can be organized into ecological groups that have more or less coherent stratigraphic distributions. Five groups have been established (Figs. 21-22).

  1. Freshwater planktonic diatoms: all species of Stephanodiscus, Asterionella formosa, Fragilaria crotonensis, Cyclotella ocellata, C. bodanica, Cyclostephanos species, and all Aulacoseira species.

  2. Saline planktonic diatoms: Chaetoceros muelleri spores, Cyclotella caspia, C. quillensis, C. meneghiniana.

  3. Saline benthic diatoms: Amphora coffaeiformis, Anomoeoneis costata, Campylodiscus clypeus, Nitzschia frustulum, N. monoensis, N. pusilla, Rhopalodia constricta, R. gibberula, Surirella hoffleri, S. ovalis, S. striatula.

  4. Benthic freshwater "Fragilaria" species: Fragilaria brevistriata, F. construens, F. leptostauron, and F. pinnata.

  5. Other Freshwater (mostly benthic) taxa: Achnanthes, Amphora ovalis, A. perpusilla, Caloneis, Cocconeis, Cymbella, Epithemia, Fragilaria vaucheriae, Fragilaria capucina, Gomphonema, Gyrosigma, Hantzschia, Melosira, Pinnularia, Rhoicosphenia curvata, Rhopalodia gibba, Synedra acus, S. mazamaensis, S. rumpens, S. ulna.

The general concentration of freshwater planktonic diatoms is an order of magnitude greater than concentrations of saline diatoms (Fig. 21), probably reflecting poor diatom preservation in saline systems. Alkaline corrosion of biogenic silica, slow deposition rates, sub aerial exposure of lake sediments probably account for much of the diatom destruction in such habitats. Episodes of high concentrations of saline planktonic diatoms, implying large and possibly deep saline lakes are rare in the Owens Lake record and contrast with the paleolimnology of terminal Great Basin lakes such as Walker Lake (Bradbury et al., 1989). Throughout most of its history, Owens Lake apparently drained and freshened when there was sufficient flow in the Owens River.

Peaks of freshwater planktonic diatoms logically correlate with increased flow of the Owens River and probably reflect moister, glacial climates during which Sierran glaciers would expand. Saline planktonic and benthic diatoms most likely correlate with arid, interglacial climates and reduced flow of the Owens River.

Species of Fragilaria and other freshwater benthic diatoms have a similar stratigraphic distribution, although benthic Fragilaria species dominate below 200 m (Fig. 22). Large concentrations of Fragilaria species indicate periods of time when Owens Lake was shallow, but fresh; probably a through-flowing marsh system. It is reasonable to suppose that tectonic rejuvenation of the basin was required to reestablish a lake morphometry suitable for planktonic diatoms, although geomorphic alteration of the Owens sill could also be involved. Perhaps the stratigraphic distribution of Fragilaria species documents periods of tectonic quiescence that allowed the Owens basin to fill with sediment and develop persistent shallow but fresh marsh environments.

The full paleolimnological interpretation of the diatom stratigraphy of the Owens Lake cores will require integration of ancillary stratigraphic data from pollen, ostracodes, geochemistry and mineralogy coupled with a detailed absolute chronology.

Figures

  1. Figures 1-18 Raw diatom counts versus depth in the composite Owens Lake core, based on analyses of cores 1, 2, and 3. Abscissa represents numbers of valves.
  2. Figure 19. Diatom concentration (diatom valves encountered per mm of microscope transect) versus depth in the composite Owens Lake core.
  3. Figure 20. Concentration of Asterionella formosa between ~15 and ~25 ka (9.5 - 19.0 m) showing sub-millennial cycles of abundance.
  4. Figure 21-22. Concentration of ecological groups of diatoms in the Owens Lake composite core.

References


U.S. Department of Interior, U.S. Geological Survey
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