FLAGELLATE GRAZING IN LAKES HOARE & FRYXELL


Acceptance and utilization of LTER data requires that:


FLAGELLATE GRAZING IN LAKES HOARE & FRYXELL

FILE NAME: flgltgrz.datData File (Comma Delimited Ascii Format)
flgltgrz.txtData File (MS-DOS Text - Table Layout).

PRINCIPAL INVESTIGATOR: Johanna Laybourn-Parry
Address:Institute of Environmental Sciences
University of Nottingham - Sutton Bonington Campus
Loughborough, LE12 5RD, United Kingdom
Phone:+44 115 951 6262
E-Mail:J.Laybourn-Parry@nottingham.ac.uk

OTHERS: Emily Roberts
Address:The Elms
Department of Physical & Environmental Science
University of Nottingham - Sutton Bonnington Campus
Leics., LE12 5RD, United Kingdom

KEYWORDS: lake, flagellate, mixotrophic, heterotrophic, cyanobacteria, grazing, bacteria, Antarctica, limnology, microzooplankton

ABSTRACT: In conjunction with the Long Term Ecological Research (LTER) project in the McMurdo Dry Valleys of Antarctica, lakes were monitored for microzooplankton by a team based out of the University of Nottingham (led by Johanna Laybourn-Parry). This dataset shows grazing rates of heterotrophic and mixotrophic flagellates found in Lakes Hoare and Fryxell at various depths and dates.

VARIABLES: location, date, depth (m), type of organism, bacteria grazing rate/h/indiv, %bacterial biomass grazed daily

RESEARCH LOCATION: Two perennial ice-covered lakes, Lake Fryxell and Lake Hoare, in the Taylor Valley, Southern Victoria Land, Antarctica (77°S, 162°E) were sampled. Lake Fryxell has a maximum depth of 20m and is a permanently stratified meromictic lake with a conductivity of 1.2 to 2.0 mS/cm in the upper mixomolimnion and 4.1 to 8.4 mS/cm in the lower anoxic monomolimnion. Water temperatures during the summer range from 0.01°C to 2.7°C, with temperature increasing with depth. The chemocline is situated at 9.5m. In contrast, Lake Hoare is unstratified during the summer and is freshwater. It has a maximum depth of 34m. Summer temperatures in the water column ranged between 0.01°C and 1.0°C.

METHODS: The water column was sampled at the deepest point in each lake with a 2.21 Niskin bottle, through a hole drilled in thick ice cover (approximately 4m thick). Duplicate 60ml samples from each depth were fixed in buffered glutaraldehyde to a final concentration of 2% and stored in the dark at 4°C prior to being analyzed for bacteria. For bacteria counts, 1-2ml samples were stained with DAPI (4', 6-diamindino-2-phenylindole), filtered onto 0.2 µm black polycarbonate membrane filters and then viewed under UV epifluorescence microscopy. Ten Whipple grids were counted on each filter and the mean value determined. For cryptophyte counts, 30-50ml of sample was stained with DAPI, filtered onto a 2.0 µm polycarbonate membrane filter and viewed under epifluorescence. Twenty Whipple grids were counted on each filter to determine mean abundance.

Biomass values for bacteria were derived by measuring 100 cells on each preparation using a Patterson graticule at a magnification of x1600. Mean cell volumes were converted to carbon values by applying a conversion factor of 220fg C/µm3. Cryptophyte biomass was calculated by measuring 50 cells on each preparation. Biovolume was derived by applying an ellipsoid geometric shape and converted to carbon using a conversion figure of 220fg C/µm3.

Flagellate ingestion rates were determined using fluorescently labelled bacteria (FLB). FLBs were prepared by labelling bacteria cultured from Lake Fryxell with DTAF [5-(4,6-dichlorotriazin-2-yl) aminofluorscein]. Ingestion rates were measured in flagellates collected from 6m and 12m in Lake Hoare and 6m, 8m, and 9m in Lake Fryxell. Incubations were conducted in situ at the appropriate depths using 60ml acid rinsed Nalgene bottles. Duplicate 50ml samples were fixed with ice-cold 2% phosphate buffered glutaraldehyde (final concentration) after 30 minutes, 1 hour, 2 hours and 3.5 hours. Samples were stained with DAPI filtered onto a 5 µm polycarbonate filter and viewed under epifluorescence microscopy. Four hundred cryptophyte cells were examined on each preparation, and the number of FLB in each cell recorded. Ingestion rates were calculated using the linear portion of the uptake curves.

TIMING: Samples were gathered on 19-Nov-1997 and 15-Dec-1997 at Lake Fryxell, and 7-Nov-1997 and 26-Jan-1998 at Lake Hoare.

CITATIONS: Roberts, Emily C. and Johanna Laybourn-Parry. 1998. Mixotrophic cryptophytes and their predators in the Dry Valley lakes of Antarctica. Freshwater Biology. In Press.

COMMENTS:

STATUS: Restricted Access (Type IV).

VARIABLE DESCRIPTION:

VARIABLE

TYPE

DESCRIPTION

UNITS

MISSING VALUE INDICATOR

MINIMUM

MAXIMUM

PRECISION

Location

Text

Name of lake where measurement was made

none

Required entry

n/a

n/a

n/a

Date

Date

Date on which sample was gathered

mm/dd/yy

Required entry

11/01/97

01/31/98

dd

Depth (m)

Number

Depth at which sample was drawn from lake

meters

Required entry

6

12

1

Type of Organism

Text

Category describing species

none

Required entry

n/a

n/a

n/a

Bacteria grazing rate/h/indiv

Number

Rate at which bacteria was consumed

# of bacteria/hour/individual

Required Entry

0

n/a

0.1

%Bacterial biomass grazed daily

Number

Proportion of bacterial biomass consumed in 24 hours

Percent

Null

0

100

0.1

LOG: Data for this file was submitted by Johanna Laybourn-Parry to the data manager at INSTAAR on October 21, 1998. Files were sent via e-mail as well as a hard copy. The original version of the file is stored on the Unix system in "/data1/data/lakes/plankton/laybourn-parry/DV". Upon arrival at INSTAAR, the data manager reformatted the file using Microsoft Access to present it in a relational mode. It was then exported in comma delimited ascii and MS-DOS text format to present on the web. Links to these files are provided above.

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.