SUMMER PHYTOPLANKTON DENSITIES 1992-2001


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SUMMER PHYTOPLANKTON DENSITIES 1992-2001

FILE NAME: phytplkt.datData File (Comma Delimited Ascii Format).

PRINCIPAL INVESTIGATOR: Diane McKnight
Address:INSTAAR, 1560 30th Street, Campus Box 450, Boulder CO, 80309-0450
Phone:(303)492-4687
E-Mail:mcknight@snobear.colorado.edu

OTHERS:

KEYWORDS: lake, limnology, phytoplankton, density, phylum

ABSTRACT: Phytoplankton were collected over four austral summers (1991-92 through 1994-95) to examine seasonal and annual fluctuation in species composition and biovolume in Lakes Fryxell, Hoare, West Lake Bonney, and East Lake Bonney. All of these lakes are perennially ice-covered lakes located in the Dry Valleys of South Victoria Land, Antarctica. The phytoplankton consisted primarily of cryptophyte and chlorophyte flagellates, and filamentous cyanobacteria. Some common taxa were vertically stratified (Oscillatoria limnetica, Phormidium angustissimum, Pyramimonas sp., Oscillatoria sp.), while others showed no distinct vertical stratification (Chlamydomonas subcaudata, Cryptomonas sp.). The stratification of the phytoplankton reflects the gradients of nutrients and light, and the stability of the water column.

VARIABLES: limno run, location name, location code, date, depth (m), phylum, species, density (cells/mL), file name

RESEARCH LOCATION: Lake Fryxell, Lake Bonney and Lake Hoare are all located in Taylor Valley, South Victoria Land, Antarctica. Lake Fryxell (77 37'S, 163 07'E) is at an elevation of 16 m above sea level. It has an area of 7 km2 and a maximum depth of 19 m. The perennial ice cover has a thickness of ~4.5 m. Sampling was conducted at a center station, where the depth was 18.5 m. Lake Bonney is roughly 6.0 kilometers in length and up tp 900 meters wide. It is comprised of a larger east basin and a smaller west basin. Samples were gathered from both basins. The east lobe has a perennial ice cover thickness of ~3.8 m; the west lobe has a perennial ice cover thickness of ~3.7 m. Lake Hoare occupies a narrower portion of the valley, is dammed by the Canada Glacier, and would drain almost completely without this dam. It is roughly 4.2 kilometers long and up to 1100 meters wide. There are a number of islands which may be related to an old terminal moraine of Canada Glacier. The perennial ice cover thickness is ~4.0 m.

METHODS: Discrete samples for phytoplankton enumeration were collected from the oxygenated portion of the water column (below the bottom of the ice to a depth of 10 m) at 0.5 m intervals. Sampling was done primarily between the hours of 14:00 and 20:00 (during the austral summer, the illuminated period is 24 h/day) by either peristaltic pump or Kemmerer bottle. Samples were collected in 1 l bottles and preserved immediately with Lugon's solution (American Public Health Association, 1985). Identification and counts were made with an inverted microscope by the method of Utermohl (1958). At least 100 individuals of the most numerous algae were counted per sample at 100x magnification. The total number of individuals counted was dependent on the number of taxa, but ranged between 200 and 500. Counting error ranged between 13 and 26%, depending on species. Algal species identifications were made using Geitler (1932), Seaburg et al. (1979) and Prescott (1962). Cell volumes were estimated for dominant taxa by measuring cell dimensions of 50-100 individuals and using closest geometric formulas of additional dates and depths to determine changes in cell volume over time. For rare taxa, volume estimates were made from fewer cell measurements.

Primary productivity was measured using the method of Strickland and Parsons (1972). In situ 24 h incubations were made in triplicate 300 ml light and duplicate 300 ml dark bottles with Na14CO3 (3 uCi per 300 ml, New England Nuclear). Following 24 h incubation, samples were well shaken and filtered through Whatman GF/F filters in the dark. The filters were placed in scintillation vials and acidified with 1 ml of 5% acetic acid in methanol to remove [C14] carbonates. The [C14] fixed by biological activity was determined in Aquasol (New England Nuclear) by liquid scintillation.

Samples for nitrate and orthophosphate were frozen within several hours of collection, later filtered through 0.45 um Nucleopore filters and analyzed by air-segmented continuous-flow absorption spectrophotometry (Alpkem RFA-300) (Antweiler et al., 1993). Chlorophyll extractions were made in 95% ethanol (Jesperson and Christoffersen, 1987) and measured in a Turner Designs Model 10 Fluorometer.

TIMING: Samples were gathered from the following locations and dates:
LocationDate(s)
Lake Fryxell:1/10/92, 11/16/93, 1/7/94, 1/18/94, 11/14/94, 12/4/94, 1/17/95, 9/14/95, 11/26/95, 12/27/95, 10/26/96, 11/19/96, 1/9/97, 11/18/97, 12/29/97, 10/28/98, 11/23/98, 12/20/98, 10/30/99, 11/27/99, 12/23/99, 11/7/00, 12/3/00, 12/30/00, 1/17/01
East Lake Bonney:10/27/93, 11/24/93, 12/21/93, 11/2/94, 12/17/94
West Lake Bonney:10/29/93, 11/26/93, 12/23/93, 11/4/94, 12/19/94
Lake Hoare:11/5/93, 12/1/93, 12/30/93, 1/19/94, 11/10/94, 12/24/94, 1/20/95, 10/10/95, 11/21/95, 12/23/95, 11/8/96, 12/2/96, 11/14/97, 12/1/97, 12/26/97, 11/3/98, 12/1/98, 12/26/98, 11/17/99, 12/12/99, 1/4/00, 11/11/00, 1/2/01

CITATIONS: Spaulding, Sarah A, Diane M. McKnight, Richard L. Smith and Richard Dufford. 1994. Phytoplankton population dynamics in perennially ice-covered Lake Fryxell, Antarctica. Journal of Plankton Research. Vol.16 no.5 pp.527-541.

COMMENTS:

STATUS: Public Access (Type 1).

VARIABLE DESCRIPTION:

 
VARIABLE	TYPE	UNITS		MISSING VALUE INDICATOR   MINIMUM	MAXIMUM	    PRECISION

Location	String	None		  Required entry	   n/a		  n/a	       n/a
Latitude	String	DD-MM-SS South	  Required entry	   n/a		  n/a	       n/a
Longitude	String	DDD-MM-SS East	  Required entry	   n/a		  n/a	       n/a
Description	String	None			Null		   n/a		  n/a	       n/a

LOG:

NOTE: Data contained in these files has been subjected to quality control standards imposed by the investigator. The user of this data should be aware that, while efforts have been taken to ensure that these data are of the highest quality, there is no guarantee of perfection for the data contained herein and the possibility of errors exists. If you encounter questionable data, please contact the MCM LTER data manager (; (303)492-4639) so that the data can be corrected or qualified. Thus, these data may be modified and future data will be appended.