Data Set Citation
Rudstam L of Cornell Biological Field Station, Luckey F of US Environmental Protection Agency, Region 2, and Koops M of Great Lakes Laboratory for Fisheries and Aquatic Sciences, Fisheries and Oceans Canada.Water Quality in Offshore Lake Ontario during Intensive Sampling Years 2003 and 2008: Results from the LOLA (Lake Ontario Lower foodweb Assessment) program..
jimont.133.5
Data Tables, Images, and Other Entities:
Metadata download:Ecological Metadata Language (EML) File
Data Table:
Name:LOLA_Locations_Jul9.csv
Description:Locations of stations for LOLA sampling program in 2003 and 2008
Online Distribution Info:
Download File: ecogrid://knb/jimont.123.9
Physical Structure Description:
Object Name:LOLA_Locations_Jul9.csv
Text Format:
Attribute Orientation:column
Simple Delimited:
Field Delimeter:,
Attribute(s) Info:
Attribute Description
(label and definition)
Measurement Type and Domain
Station - Station number in LOLA program   ratio
Unitnumber
Typenatural
         
Site Depth (m) - water depth of site in meters   ratio
Unitmeter
Precision0.1
Typenatural
         
Latitude - Latitude N in decimal degrees   ratio
Unitdegree
Precision0.0001
Typenatural
         
Longitude - Longitude E in decimal degrees   ratio
Unitdegree
Precision0.0001
Typenatural
         
Data Table:
Name:merged for KNB_July20.csv
Online Distribution Info:
Download File: ecogrid://knb/jimont.130.6
Physical Structure Description:
Object Name:merged for KNB_July20.csv
Size:8483 byte
Text Format:
Number of Header Lines:1
Record Delimiter:#x0A
Attribute Orientation:column
Simple Delimited:
Field Delimeter:,
Number Of Records:154
Attribute(s) Info:
Attribute Description
(label and definition)
Measurement Type and Domain
Date date - date of sampling   dateTime
FormatYYYYMMDD
Precision1 day
         
Ship - sampling platform   nominal
Enumerated Domain 
Code Definition
Order
Code Limnos
Definition CCGS Limnos
Source
Code Definition
Order
Code Guardian
Definition R/V Lake Guardian
Source
Attribute Definition Reference
Attribute Definition Order
         
Station - LOLA site sampled   nominal
DefLOLA sites
         
Time - Eastern Daylight Time (EDT) of sampling   dateTime
Formathh:mm
Precision1 minute
         
integration depth - integrated sample depth from surface   ratio
Unitmeter
Precision0.1
Typereal
         
Silicate - Soluble Reactive Silicate (SiO2) in ug/L   ratio
Unitmicrogram per liter
Precision1
Typereal
         
SRP - Soluble Reactive Phosphorus in ug/L   ratio
Unitmicrogram per L
Precision0.1
Typereal
         
TP - total phosphorus in ug/L   ratio
Unitmicrogram per L
Precision0.1
Typereal
         
NO3+NO2 - nitrate plus nitrite   ratio
Unitmicrogram per L
Precision1
Typereal
         
Chl a - chlorophyll a in ug/L   ratio
Unitmicrogram per L
Precision0.01
Typereal
         
Secchi - water clarity as Secchi depth in meters   ratio
Unitmeter
Precision0.1
Typereal
         
Data Set Owner(s):
Individual:Dr. Lars Rudstam
Organization:Cornell Biological Field Station
Position:Director and Professor
Address:
900 Shackleton Pt Rd,
Bridgeport, NY 13030 USA
Phone:
315-633-9243 (voice)
Phone:
315-633-2358 (fax)
Email Address:
lgr1@cornell.edu
Individual: Fred Luckey
Organization:US Environmental Protection Agency, Region 2
Position:Environmental Scientist
Address:
290 Broadway, 24th Floor,
New York, NY 1007-1866 USA
Phone:
212-637-3853 (voice)
Email Address:
luckey.frederick@epa.gov
Individual:Dr. Marten Koops
Organization:Great Lakes Laboratory for Fisheries and Aquatic Sciences, Fisheries and Oceans Canada
Position:Research Scientist
Address:
867 Lakeshore Road,
Burlington, Ontario L7R 4A6 Canada
Phone:
905-336-4559 (voice)
Phone:
905-336-6437 (fax)
Email Address:
Marten.Koops@dfo-mpo.gc.ca
Abstract:
 
Intensive sampling of the offshore waters of Lake Ontario occurs on a five-year cycle. The 2003 and 2008 binational sampling program is known as the Lake Ontario Lower foodweb Assessment (LOLA). Research cruises were conducted in spring (April), summer (July or August) and fall (September) along several north-south transects. Trophic indicators in this data package include nutrients (total phosphorus (TP), soluble reactive phosphorus (SRP), dissolved silicate(Si02), and total dissolved inorganic nitrogen(nitrate and nitrite), water clarity (Secchi depth), and chlorophyll a. Other measurements measured include density and biomass of zooplankton, assessment of phytoplankton and the microbial food web, benthic community assessment, and water column profiles (temperature, fluorescence, turbidity, and oxygen).
Keywords:
Thesaurus:Global Change Master Directory
 
  • lakes
  • Secchi depth
  • phosphorus
  • chlorophyll
  • Lake Ontario
License and Usage Rights:
 
This data set is made available under the Open Data Commons Attribution License: http://www.opendatacommons.org/licenses/by/1.0/. Users of this data set are very strongly encouraged to check with the data set Owner or the individual listed as the Contact for this data set to verify that they have the most current and correct version of the data. Users are also encouraged to notify the data set Owner/Contact to describe their intended use of the data set, including planned publications, and to supply the Owner/Contact with a copy of any publication or derivative work using or citing the data set.
Geographic Coverage:
Geographic Description:Lake Ontario
Bounding Coordinates:
West:  -79.345  degrees
East:  -76.391  degrees
North:  44.102  degrees
South:  43.568  degrees
Temporal Coverage:
Begin:
2003
End:
2008
Contact:
Individual: Kristen Holeck
Organization:Cornell Biological Field Station
Position:Research Support Specialist
Address:
900 Shackleton Pt Rd,
Bridgeport, NY 13030 USA
Phone:
315-633-9243 (voice)
Phone:
315-633-2358 (fax)
Email Address:
kth1@cornell.edu
Methods Info:
Step 1:  
Description:
LOLA 2003 and 2008 – Background
Extensive surveys for each Great Lake occur generally on a rotating five-year schedule. The binational lakewide sampling effort of Lake Ontario for 2003 and 2008 is known as LOLA (Lake Ontario Lower foodweb Assessment). Standard sites on several north-south transects were sampled once during isothermal (April) and twice during stratified (July-September) conditions. Ecosystem indicators included water chemistry, microbial food web, phytoplankton, zooplankton, and benthos. Two ships were used- the EPA’s R/V Lake Guardian and Environment Canada’s R/V Limnos. The project was similar in scope and design to the LOTT (Lake Ontario Trophic Transfer) program of 1990 and 1996. This data package documents several water quality indicators including water clarity (secchi depth), chlorophyll a, and nutrients.
Step 2:  
Description:
Water Sample Collection
During spring isothermal conditions, integrated water samples were collected from 20-m depth or two meters above the bottom (for shallow stations) to the surface. In summer and fall, integrated water samples were collected from one meter
above the thermocline to the surface. An electronic bathythermograph (EBT, Limnos) or conductivity-temperature-depth (Seabird SBE25 CTD, Lake Guardian) profiler was used to determine thermocline depth. Aboard the Limnos, water samples were collected using an integrated tube sampler (1.9-cm inside diameter Nalgene tube) lowered to the appropriate depth. Aboard the Lake Guardian, three discrete (1.5 m, intermediate and 1 m above the thermocline) Niskin bottles were combined. Time of sampling was recorded as Eastern Daylight Time. Secchi depth measurements were only taken at stations visited during daylight hours. Water column profiles that include sensors for temperature, dissolved oxygen, fluorescence (chl a), turbidity, and light attenuation are also available.
Duplicate samples of total phosphorus (TP), soluble reactive phosphorus (SRP), soluble reactive silicate (SiO2), and Nitrate+Nitrite (NO3+NO2, 2008 only) were collected. Total phosphorus samples were unfiltered and placed in acid rinsed 500 ml HDPE bottles with 1 ml of sulfuric acid added. For SRS, SRP, and NO3+NO2, 30 ml of water was filtered in the field (0.45 micron membrane filter) and stored in separate 30 ml HDPE bottles. Sample volume was reduced if filter clogging occurred. SRS and SRP were not acidified but 1-2 drops of sulfuric acid were added to the NO3+NO2 samples. All nutrient samples were frozen.
Triplicate samples of chlorophyll a (chl a) were taken. At least 800 ml was filtered using a Whatman GF/C (nominal pore size of 1.2 um) glass fiber filter at a pressure not exceeding 300 mm Hg, and the filter was wrapped in foil and frozen for later analysis.
I
Step 3:  
Description:
Sample Analysis
In 2003, nutrient and chl a samples were analyzed at Environment Canada in Burlington, Ontario. The National Lab for Environmental Testing (George Braedon) ran the chemistry samples. Michele Burley analyzed the chl a samples. For 2008, an EPA-certified laboratory at SUNY-Brockport (Ted Lewis and Joe Makarewicz, 585-395-5747) processed the nutrient and chl a samples.
Nutrients were analyzed with an autoanalyzer using the following methods-
TP concentration was determined using the ammonium molybdate – stannous chloride method after persulfate digestion. SRP was analyzed using the ammonium molybdate-stannous chloride method without digestion (APHA 1999, SM 4500-P F).
Dissolved Silicate (SiO2) was analyzed using the heteropoly blue method (APHA 1999, SM 4500-Si F).
Nitrate+Nitrite was analyzed in 2008 using the cadmium reduction method (APHA 1999, SM 4500-NO3 F).
Chl a filters were ground and extracted in 90% acetone. In 2003, filter extracts were analyzed for chl a using the spectrophotometric technique. Values reported here are for uncorrected chl a (before acid addition). In 2008, a calibrated Turner 10-AU fluorometer was used yielding chl a (Wetzel and Likens 2000).
Detection limits for each analyte were below levels given by the standard work order (SWO) to the two laboratories. Average values presented here are calculated assuming that values below the detection limit or given as not detected are at the detection limit. Many summer SRP values are therefore given as the detection limit (0.2 for 2003 and 0.5 for 2008). Two samples with TP not detected (20030429, station 64 and 20030820, station 40) and one sample with NOx not detected (20080726, station 33) were assumed to be in error and not included. -999 entries indicate these culled data as well as no data present.
Detection Limits
TP 0.2 ug/L (2003) and 1.2 ug/L (2008) [2.0 ug/L in SWO]
SRP 0.2 ug/L(2003) and 0.6 ug/L (2008) [2.0 ug/L in SWO]
Dissolved Silicate 20 ug/L (2003) and 50 ug/L (2008) [100 ug/L in SWO]
Nitrate + Nitrite 40 ug/L (2008 only) [100 ug/L in SWO]
Chlorophyll a 0.5 ug/L (2003) and 0.5 ug/L (2008) [0.5 ug/L in SWO]
References
APHA. 1999 Standard Methods for the Examination of Waste and Wastewater, New York: American Public Health Association.
Wetzel, R.G. and Likens, G.E. 2000. Limnological Analysis, 3rd Edition. New York: Springer-Verlag.
Step 4:  
Description:
Published research that used previous versions of this dataset
Holeck, K., Watkins, J.M., Mills, E.L., Johannsson, O. Millard, S., Richardson, V., Bowen
K. 2008. Spatial and long-term temporal assessment of Lake Ontario water
clarity, nutrients, chlorophyll a, and zooplankton. Aquatic Ecosystem Health
and Management. 11:377-391.
Project Info:
Title: Lake Ontario Lower Trophic Level Foodweb Assessment (2003, 2008)
Personnel:
Individual:Dr. Lars Rudstam
Organization:Cornell Biological Field Station
Position:Director and Professor
Address:
900 Shackleton Pt Rd,
Bridgeport, NY 13030 USA
Phone:
315-633-9243 (voice)
Phone:
315-633-2358 (fax)
Email Address:
lgr1@cornell.edu
Role:
PI for 2008 Project
Individual:Dr. Ed Mills
Organization:Cornell Biological Field Station
Position:Professor and Former Director
Address:
900 Shackelton Pt Rd,
Bridgeport, NY 13030 USA
Phone:
315-633-9243 (voice)
Email Address:
elm5@cornell.edu
Role:
PI for 2003 Project
Funding:
For LOLA 2003, EPA grant CR-83209001 to Cornell University and a Canada Ontario Agreement (COA) from Ontario Ministry of Natural Resources (OMNR). For LOLA 2008, EPA funded project under Great Lakes Restoration Initiative (GLRI) “Evaluation of the current status of the Lake Ontario ecosystem.”

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