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
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Data Tables, Images, and Other Entities: |
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 |
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Physical Structure Description:
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Object Name: | LOLA_Locations_Jul9.csv |
Text Format: |
Attribute Orientation: | column |
Simple Delimited: |
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Attribute(s) Info: |
Attribute Description (label and definition)
| | Measurement Type and Domain | | | | | |
Station - Station number in LOLA program |
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Site Depth (m) - water depth of site in meters |
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Unit | meter |
Precision | 0.1 |
Type | natural |
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Latitude - Latitude N in decimal degrees |
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Unit | degree |
Precision | 0.0001 |
Type | natural |
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Longitude - Longitude E in decimal degrees |
| ratio
Unit | degree |
Precision | 0.0001 |
Type | natural |
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Data Table: |
Name: | merged for KNB_July20.csv |
Online Distribution Info: |
Download File: | ecogrid://knb/jimont.130.6 |
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Physical Structure Description:
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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: |
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Number Of Records: | 154 |
Attribute(s) Info: |
Attribute Description (label and definition)
| | Measurement Type and Domain | | | | | |
Date date - date of sampling |
| dateTime
Format | YYYYMMDD |
Precision | 1 day |
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Ship - sampling platform |
| nominal
Enumerated Domain |
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Code Definition |
Order
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Code
| Limnos |
Definition
| CCGS Limnos |
Source
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Code Definition |
Order
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Code
| Guardian |
Definition
| R/V Lake Guardian |
Source
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Attribute Definition Reference | |
Attribute Definition Order | |
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Station - LOLA site sampled |
| nominal
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Time - Eastern Daylight Time (EDT) of sampling |
| dateTime
Format | hh:mm |
Precision | 1 minute |
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integration depth - integrated sample depth from surface |
| ratio
Unit | meter |
Precision | 0.1 |
Type | real |
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Silicate - Soluble Reactive Silicate (SiO2) in ug/L |
| ratio
Unit | microgram per liter |
Precision | 1 |
Type | real |
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SRP - Soluble Reactive Phosphorus in ug/L |
| ratio
Unit | microgram per L |
Precision | 0.1 |
Type | real |
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TP - total phosphorus in ug/L |
| ratio
Unit | microgram per L |
Precision | 0.1 |
Type | real |
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NO3+NO2 - nitrate plus nitrite |
| ratio
Unit | microgram per L |
Precision | 1 |
Type | real |
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Chl a - chlorophyll a in ug/L |
| ratio
Unit | microgram per L |
Precision | 0.01 |
Type | real |
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Secchi - water clarity as Secchi depth in meters |
| ratio
Unit | meter |
Precision | 0.1 |
Type | real |
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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 |
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Phone:
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Phone:
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Email Address:
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Individual: | Fred Luckey |
Organization: | US Environmental Protection Agency, Region 2 |
Position: | Environmental Scientist |
Address: |
290 Broadway, 24th Floor, |
New York, NY 1007-1866 USA |
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Phone:
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Email Address:
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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 |
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Phone:
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Phone:
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Email Address:
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Marten.Koops@dfo-mpo.gc.ca |
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Abstract: |
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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). |
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Keywords: |
Thesaurus: | Global Change Master Directory |
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- lakes
- Secchi depth
- phosphorus
- chlorophyll
- Lake Ontario
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License and Usage Rights: |
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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. |
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Geographic Coverage: |
Geographic Description: | Lake Ontario |
Bounding Coordinates:
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West: | -79.345 degrees
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East: | -76.391 degrees
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North: | 44.102 degrees
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South: | 43.568 degrees
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Temporal Coverage: |
Begin:
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End:
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Contact: |
Individual: | Kristen Holeck |
Organization: | Cornell Biological Field Station |
Position: | Research Support Specialist |
Address: |
900 Shackleton Pt Rd, |
Bridgeport, NY 13030 USA |
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Phone:
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Phone:
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Email Address:
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Methods Info: |
Step 1: |
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Description:
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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.
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Step 2: |
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Description:
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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
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Step 3: |
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Description:
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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.
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Step 4: |
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Description:
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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.
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Project Info: |
Title:
| Lake Ontario Lower Trophic Level Foodweb Assessment (2003, 2008) |
Personnel:
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Individual: | Dr. Lars Rudstam |
Organization: | Cornell Biological Field Station |
Position: | Director and Professor |
Address: |
900 Shackleton Pt Rd, |
Bridgeport, NY 13030 USA |
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Phone:
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Phone:
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Email Address:
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Role:
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Individual: | Dr. Ed Mills |
Organization: | Cornell Biological Field Station |
Position: | Professor and Former Director |
Address: |
900 Shackelton Pt Rd, |
Bridgeport, NY 13030 USA |
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Phone:
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Email Address:
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Role:
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Funding:
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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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Additional Metadata
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Access Control: |
Auth System: | knb |
Order: | allowFirst |
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