Hudson River (HUD) NERR Water Quality Metadata March - December 2004 Latest Update: May 2, 2005Entry ID: CDMO_hudwq03-12.04m
Abstract: Water quality monitoring is conducted at 26 National Estuarine Research Reserves (NERR) at four locations within or adjacent to the reserve. The following parameters are collected at least every 30 minutes: water temperature, specific conductivity, salinity, percent saturation, dissolved oxygen concentration, water depth, pH and turbidity. All water quality data loggers will be deployed from a known depth from the bottom at each site.
Purpose: Research objectives The objective of this study is to monitor surface water quality at the Tivoli Bays component of the Hudson River National Estuarine Research Reserve (NERR). Two tidal freshwater wetlands, Tivoli North Bay and Tivoli South Bay, and their primary upland tributaries, Stony Creek and Saw Kill Creek respectively, are monitored using four dataloggers (YSI 6600 sondes). In Tivoli ... North Bay and Tivoli South Bay the dataloggers monitor the ebbing and flooding Hudson River water. In Stony Creek and Saw Kill Creek, the dataloggers are deployed above the area of tidal influence and monitor the quality of water entering the Tivoli Bays via stream flow. Thus, the relative importance of stream flow and tidal exchange and the potential impacts of intertidal areas on the water quality of the Tivoli Bays can be determined. Monitoring the water quality of the tributaries is important because it has previously been determined that urban and residential land use practices are markedly influencing the water chemistry of the tributaries, especially Saw Kill Creek. Since residential coverage continues to increase, we hope that the intensive monitoring of the surface waters in these watersheds will identify trends associated with this rapid development. Examining the influence of tidal exchange allows identification of long-term trends in the water quality of the Hudson River Estuary at this location and the potential inputs to the Estuary from the Tivoli Bays. Finally, the influence of intertidal areas on water quality within the Tivoli Bays is interesting because of the potential impacts of both floating and emergent invasive plant species present in this system.
Associated researchers and projects As part of the Hudson River NERR water quality monitoring project, physical and chemical constituents of the tributary waters discharging into HUDNERR marshes and marsh waters are measured monthly during ebb tides. Measurements include dissolved oxygen, seston, alkalinity, pH, temperature, salinity, conductivity and concentrations of ammonium, nitrate, phosphate, sulfate and chloride. Associated researchers working at the Tivoli Bays component site include scientists from the Institute of Ecosystem Studies in Millbrook, NY, Yale School of Forestry and Environmental Studies in New Haven, CT, and Rensselaer Polytechnic Institute in Troy, NY. Other remarks/notes A reference to negative and/or zero depth or depth readings flagged as outliers indicates that depth was recorded as a negative value in the raw data file and as zero in the edited data file due to the formatting of Excel. The technician edited none of these data points by hand nor did the technician delete any of them. The range for the turbidity probe is 0-1000 NTU, with an accuracy of + 0.5% or 2 NTU, whichever is greater. Therefore, a reading of ?2 is acceptable. Saw Kill Creek is a low-turbidity site due to the presence of a dam allowing settling of a large amount of suspended matter. Turbidity readings of 0 to ?2 are frequently recorded, but are not outliers. Therefore, QA/QC of the turbidity data (all sites) involves flagging all data below ?2 NTU as outliers, data between 0 and ?2 are not considered outliers and are not documented in the metadata.. If the post-deployment dissolved oxygen readings were out of the specification range (98%-102%), the data were carefully examined for obvious shifts in dissolved oxygen readings during deployment and readings at the end of deployment were checked against readings from the newly calibrated replacement sonde. If there were no obvious discontinuities and the probe was functioning adequately, data are not considered suspect and the post-deployment readings were not mentioned in the Data Anomalies section (Section 11) of the metadata. The location of the sonde in Stony Creek (SC) was changed on 7/21/2004, due to variable stream flow resulting in frequent exposure of the instrument to air. The new location is approximately 50 m upstream, in a pool area. Daily precipitation totals for 2004: Date TotPrcp (mm) 1/2/2004 1.5 1/3/2004 3.3 1/4/2004 10.7 1/5/2004 11.2 1/12/2004 0.8 1/15/2004 0.3 1/18/2004 0.3 1/27/2004 0.5 1/29/2004 0.3 1/31/2004 0.3 2/1/2004 1 2/2/2004 0.5 2/3/2004 1.5 2/4/2004 6.9 2/5/2004 0.8 2/6/2004 8.4 2/7/2004 14 2/9/2004 1 2/10/2004 4.6 2/13/2004 0.3 2/21/2004 0.5 3/2/2004 1 3/4/2004 2.3 3/5/2004 3 3/6/2004 5.8 3/7/2004 0.3 3/8/2004 11.4 3/9/2004 1.3 3/17/2004 2.8 3/18/2004 7.1 3/19/2004 0.8 3/20/2004 1.5 3/26/2004 0.3 3/27/2004 3.3 3/31/2004 19.6 4/1/2004 18.8 4/2/2004 0.8 4/12/2004 8.6 4/13/2004 21.3 4/14/2004 0.5 4/22/2004 3 4/23/2004 18.3 4/24/2004 0.3 4/25/2004 0.3 4/26/2004 18 4/27/2004 1 5/2/2004 1.8 5/3/2004 11.2 5/4/2004 0.3 5/9/2004 0.8 5/10/2004 2.8 5/12/2004 0.5 5/13/2004 1.5 5/18/2004 4.8 5/21/2004 0.8 5/22/2004 0.3 5/23/2004 5.8 5/24/2004 17 5/25/2004 1 5/26/2004 35.1 5/27/2004 3.6 5/28/2004 4.8 5/31/2004 6.1 6/1/2004 10.9 6/2/2004 1.5 6/3/2004 0.8 6/5/2004 0.3 6/6/2004 0.8 6/9/2004 1.8 6/17/2004 5.1 6/22/2004 1.8 6/25/2004 1.5 6/26/2004 6.6 6/28/2004 1.5 6/29/2004 0.3 7/1/2004 3.6 7/2/2004 2.3 7/5/2004 11.7 7/8/2004 3.8 7/12/2004 1.8 7/13/2004 3 7/14/2004 1.8 7/15/2004 5.3 7/16/2004 0.3 7/18/2004 11.2 7/23/2004 27.7 7/27/2004 27.9 7/28/2004 2.8 7/30/2004 4.1 7/31/2004 0.3 8/1/2004 14 8/4/2004 5.1 8/5/2004 4.6 8/7/2004 1 8/8/2004 1 8/11/2004 8.4 8/12/2004 6.6 8/13/2004 15.5 8/16/2004 16.5 8/17/2004 0.3 8/20/2004 11.7 8/21/2004 23.9 8/30/2004 43.2 8/31/2004 0.3 9/8/2004 32.3 9/9/2004 16 9/17/2004 29.7 9/18/2004 52.1 9/28/2004 65.3 9/29/2004 4.6 9/30/2004 3 10/2/2004 5.8 10/14/2004 0.8 10/15/2004 9.7 10/16/2004 0.8 10/18/2004 2 10/19/2004 20.3 10/21/2004 2 11/3/2004 0.3 11/4/2004 15 11/12/2004 2 11/13/2004 3 11/14/2004 0.5 11/20/2004 2.3 11/21/2004 1 11/24/2004 12.7 11/25/2004 15 11/28/2004 27.2 12/1/2004 29.2 12/7/2004 19.1 12/9/2004 5.8 12/10/2004 14.7 12/11/2004 2.5 12/13/2004 0.3 12/19/2004 0.5 12/22/2004 2 12/23/2004 30.7 12/27/2004 0.8 12/30/2004 0.3
SPATIAL DATA ORGANIZATION INFORMATION:
Indirect Spatial Reference: Site location and character The Hudson River National Estuarine Research Reserve (HUDNERR) is a multi-component site totaling approximately 5,000 acres. Each component of the reserve is referenced by River Mile (RM) of the Hudson River in New York State proceeding north from the southern tip of Manhattan (RM 0). The reserve includes the following four component sites: Piermont Marsh, Rockland County (RM 24)(41o02'30"N 73o54'15"W), Iona Island, Rockland County (RM 45)(41o18'15"N 73o58'45"W), Tivoli Bays, Dutchess County (RM 98)(42o02'15"N 73o55'10"W), and Stockport Flats, Columbia County (RM 124)(42o02'30"N 73o46'00"W). The four component sites include open water, tidal wetland, and adjacent upland buffer habitats and are representative of the diverse plant and animal communities that occupy the salinity gradient within the Hudson River Estuary. Development within the watersheds of the four component sites ranges from predominantly urban/suburban to forested/agricultural. The highlighted component for this study is the Tivoli Bays in Annandale, NY. This component includes four monitored sites: Tivoli South Bay (TS), Tivoli North Bay (TN), Saw Kill Creek (SK) and Stony Creek (SC). All four monitored sites are freshwater (0.0 ppt salinity). Tivoli South Bay (latitude 42° 01' 37.336" N, longitude 73° 55' 33.445" W) is a tidal freshwater wetland with intertidal mudflats exposed at low tide. During the growing season (June ? September), the subtidal area of Tivoli South Bay is dominated by the invasive floating macrophyte Trapa natans. Tivoli South Bay has a tidal range of 1.19 meters and a soft, silt/clay bottom type. The depth at the sampling location ranges from 0.5 to 2.5 meters. The non-tidal freshwater input to Tivoli South Bay includes that of a large upland tributary and a few small perennial streams. Tivoli North Bay (latitude 42° 02' 11.56464" N, longitude 73° 55' 31.16645" W) is a freshwater tidal marsh with emergent marsh vegetation dominated by the cattail Typha angustifolia. Tivoli North Bay has a tidal range of 1.19 meters, a soft, silt/clay bottom type, and a depth range from 0.5 to 3.0 meters at the sampling location. The non-tidal freshwater input to Tivoli North Bay includes that of a large upland tributary and a few small perennial streams. Saw Kill Creek (latitude 42° 01' 01.543" N, longitude 73° 54' 53.589" W) is the main tributary flowing into Tivoli South Bay. The Saw Kill Creek watershed is 26.6 square miles and land use within the watershed includes forested (51.1%), agricultural (25.8%), and urban (16.5%) areas. Saw Kill Creek is non-tidal and freshwater input to this tributary consists of smaller creeks in the watershed. At the sampling location Saw Kill Creek has a depth range of 0.5 to 2.0 meters, a discharge range of 2x10-5 to 1.2 m3/sec, and a rocky bottom type. Stony Creek (latitude 42° 02' 46.881" N, longitude 73° 54' 38.984" W) is the main tributary flowing into Tivoli North Bay. The Stony Creek watershed is approximately 23 square miles and is dominated by agricultural land use. Characteristics of Stony Creek at the sampling location include a solid rock bottom and a depth range of 0.5 to 1.5 meters. Stony Creek discharge is currently being determined. Since both Stony Creek and Saw Kill Creek are non-tidal, freshwater input to these tributaries consists of smaller creeks in their watersheds. This site was moved permanently to latitude 42° 02' 46.8816" N, longitude 73° 54' 38.984" W on 07/21/04. The entire Hudson River system south of the Troy Dam is affected by polychlorinated biphenyls (PCBs), and Tivoli North and South Bays have low sedimentary concentrations of PCBs. Nutrient inputs to the Tivoli Bays via the non-tidal tributaries are the main concern in terms of pollutants. High concentrations of nitrate and phosphate have previously been documented in both Saw Kill Creek and Stony Creek. Saw Kill Creek appears to be strongly influenced by residential land use practices. Stony Creek appears to be strongly influenced by a municipal wastewater treatment plant upstream of the sampling site. This highlights the importance of continued monitoring and identification of both non-point and point sources of pollution at these sites.
Data Set Citation
Dataset Originator/Creator: William C. Nieder, Geofrey E. Eckerlin, Serena Ciparis
Dataset Title: Hudson River (HUD) NERR Water Quality Metadata March - December 2004 Latest Update: May 2, 2005
Dataset Release Date: 2006-02-10
Data Presentation Form: Unknown
Other Citation Details: NAOnline Resource: http://cdmo.baruch.sc.edu/
This description is a member of a collection. The collection is described in
Start Date: 2004-03-01Stop Date: 2004-12-31
TERRESTRIAL HYDROSPHERE > SURFACE WATER > SURFACE WATER PROCESSES/MEASUREMENTS > WATER DEPTH
TERRESTRIAL HYDROSPHERE > WATER QUALITY/WATER CHEMISTRY > CONDUCTIVITY
TERRESTRIAL HYDROSPHERE > WATER QUALITY/WATER CHEMISTRY > DISSOLVED GASES > DISSOLVED OXYGEN
TERRESTRIAL HYDROSPHERE > WATER QUALITY/WATER CHEMISTRY > PH
TERRESTRIAL HYDROSPHERE > WATER QUALITY/WATER CHEMISTRY > TURBIDITY
TERRESTRIAL HYDROSPHERE > WATER QUALITY/WATER CHEMISTRY > WATER TEMPERATURE
OCEANS > SALINITY/DENSITY > SALINITY
BIOSPHERE > ECOSYSTEMS > TERRESTRIAL ECOSYSTEMS > WETLANDS > ESTUARINE WETLANDS
BIOSPHERE > ECOSYSTEMS > AQUATIC ECOSYSTEMS > WETLANDS > ESTUARINE WETLANDS
Access Constraints Data collected in conjunction with the National Estuarine Research Reserve System's (NERRS) System-wide Monitoring Program (SWMP) is considered public information. Please see site for further information: http://cdmo.baruch.sc.edu/aboutdata.htm
Distribution NOAA Ocean and Coastal Resource Management Data Ownership and ... Dissemination Policy for the NERRS National Monitoring Program: Data collected in conjunction with the National Estuarine Research Reserve System's (NERRS) National Monitoring Program is considered public information. The principal investigators (PIs) responsible for collecting data at each NERRS site must process the data using Estuarine Reserve Division (ERD) approved quality assurance and quality control (QA/QC) protocols. The PI transmits the QA/QC processed data to ERD or an ERD approved Centralized Data Management Office (CDMO) in accordance with the standard rules for application to oceanographic data sets (NOAA Administrative Order 216-101). The submission schedule determined by the CDMO assumes an adequate and uninterrupted funding for the monitoring effort at each site, therefore the data processing and the transmission timetable may be adjusted accordingly. An awardee may own a copyright on the publication of the processed data developed or bought under a Federal assistance award. The Federal awarding agency reserves a royalty-free, nonexclusive, and irrevocable license to reproduce, publish, or otherwise use, and to authorize others to use, for Federal government purposes, the copyright in any work developed under an award, or any rights of copyright purchased by an awardee with Federal assistance support (15 C.F.R. 24.34). Any such publication will include a notice identifying the award and recognizing the license rights of the government under this clause. This paragraph will have no force and effect for the processed data not published by the recipient. The data set enclosed within this package/transmission is only as good as the quality assurance and quality control procedures outlined by the enclosed metadata reporting statement. The user bears all responsibility for its subsequent use/misuse in any further analyses or comparisons. The Federal government does not assume liability to the Recipient or third persons, nor will the Federal government reimburse or indemnify the Recipient for its liability due to any losses resulting in any way from the use of this data. NERR water quality data and metadata can be obtained from the Research Coordinator at the individual NERR site (please see Section 2.2-1 Principal investigators and contact persons), from the Data Manager at the Centralized Data Management Office (please see personnel directory under the general information link on the CDMO home page) and online at the CDMO home page http://cdmo.baruch.sc.edu/. Data are available in text tab-delimited format, Microsoft Excel spreadsheet format and comma-delimited format.
Use Constraints The principal investigator (PI) listed in the enclosed metadata retains the right to be fully credited for having collected and processed the data. Please see the site for further information: http://cdmo.baruch.sc.edu/aboutdata.htm
Data Set Progress
Distribution Format: Ascii File, Formatted For Text Attributes, Declared Format (ASCII)NA
Fees: Data is available at no charge.
Role: DIF AUTHOR
Role: TECHNICAL CONTACT
New York State Department of Environmental Conservation
Province or State: NY
Postal Code: 12504
Extended Metadata Properties
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Creation and Review Dates
DIF Creation Date: 2008-08-01
Last DIF Revision Date: 2017-11-23