Status of benthic macroinvertebrate communities and toxicity of sediments in the Niagara River Area of Concern, New York Active
Approach:
The general approach for the USGS sediment-toxicity study in the Niagara River AOC is outlined below as six sequential tasks; (1) planning/reconnaissance, (2) establishing subcontracts, (3) field surveys, (4) toxicity testing, (5) data analysis and interpretation, and (6) preparation of an interpretive sediment-toxicity report.
Task 1 – Project planning and reconnaissance will occur during winter/spring of year 1 and consist of finalizing a draft work plan, obtaining RAP committee and other stakeholder input, selecting target study sites, and reconnaissance visits. Prospective study sites will be visited to evaluate accessibility and bed sediments. The sampling plan and field logistics will be finalized following the reconnaissance visits.
Task 2 - Subcontracts for testing acute and chronic toxicity of sediments (using USEPA-approved methods for two invertebrate species - Chironomus dilutus and Hyallela azteca) will be established during spring of year 1. This will entail identifying subcontractors, inviting bids for toxicity tests, assessing bids, selecting the final contract laboratory, and assembling a purchase (or services) agreement.
Task 3 - The field surveys will be done during the summer of year 1, and will consist of collecting benthic-community and sediment samples once from as many as 55 sites in the Niagara River. The Niagara survey does not involve a direct BUI assessment; therefore, a probabilistic sampling design is planned to establish baseline toxicity and community information across the entire AOC prior to active remediation. This design will enable us to define the current conditions in depositional areas with statistically defensible metrics; i.e., with known levels of variability (Diaz-Ramos et al., 1996; Stevens and Olsen, 1999). Ten percent of sediment samples will be collected in duplicate to evaluate the reproducibility and precision of endpoints for the toxicity tests. At each site, a Petite Ponar sampler will be used to collect 5 replicate macroinvertebrate-community samples, and to collect a single composite sediment sample for toxicity testing. Bed-sediment size and organic content will be quantified by a NYSDEC subcontract laboratory using a split from the composite sediment-toxicity sample.
Task 4 - The sediment toxicity tests or bioassays will be conducted by a subcontract laboratory during summer/fall of year 1 to define the current levels of toxicity in sediments from study sites in the AOC. Acute (survival) and chronic (growth) toxicity tests will be conducted using C. dilutus and H. azteca and follow standard USEPA-approved methods (ASTM, 2010; USEPA, 1994, 2000).
Task 5 - Data analysis and interpretation will be conducted during the winter/spring of year 2. Graphical and statistical analyses, including multivariate ordination methods, will be used to summarize current (baseline) sediment toxicity levels and potential contaminant and toxicity strata across the Niagara River AOC. Results will also be used to quantify variability and to evaluate the suitability of the current benthos-BUI designation.
Task 6 - One USGS report or peer-reviewed journal manuscript (paper) will be prepared during the spring/summer/fall of year 2 in collaboration with NYSDEC and NOAA staff. This report will summarize baseline sediment-toxicity levels and identify potential toxicity strata across the Niagara AOC. The report/paper will undergo USGS technical and editorial reviews and revision prior to submission for publication internally or via a peer-reviewed journal.
References:
Report
George, S.D., Baldigo, B.P., and Duffy, B.T., 2016, Toxicity of bed sediments from the Niagara River Area of Concern and tributaries, New York, to Chironomus dilutus and Hyalella azteca, 2014–15: U.S. Geological Survey Data Series 1016, 8 p., https://pubs.er.usgs.gov/publication/ds1016
Project
Location by County
Niagara County, NY, Erie County, NY
- Source: USGS Sciencebase (id: 55e043fae4b0f42e3d040e54)
- Overview
Background:The USGS propose a collaborative investigation with the NYSDEC and NOAA to evaluate the current condition of benthic macroinvertebrate communities and toxicity of bed sediments in the Niagara River Area of Concern (AOC). Using a probabilistic study design, sediment-toxicity data compiled by the USGS, invertebrate community data collected by NYSDEC, and sediment-chemistry data collected by NOAA will be assimilated using a Sediment Quality Triad approach (Chapman et al., 1992; USEPA, 1992) to provide a sediment-quality baseline needed to gauge changes expected to follow remediation of contaminated sediments in parts of the AOC. These data will also be used directly to confirm that the macroinvertebrate communities are presently impaired and support the current listing of the benthos Beneficial Use Impairment (BUI). Although concurrent surveys at comparable control sites are not planned at this time, sediment-toxicity data and benthic-community data from inside the Niagara River AOC can also be compared to available data from non-AOC sites in the region (e.g., St. Lawrence River at Massena) to further assess the benthos-BUI designation. Benthic invertebrate community and sediment toxicity data will be compared to benthos-BUI removal criteria to determine if the classification for the entire river remains impaired or if strata (reaches) of unimpaired status exist. This remainder of this summary addresses only the direct USGS (sediment toxicity assessment) contribution to the overall program.
Approach:
The general approach for the USGS sediment-toxicity study in the Niagara River AOC is outlined below as six sequential tasks; (1) planning/reconnaissance, (2) establishing subcontracts, (3) field surveys, (4) toxicity testing, (5) data analysis and interpretation, and (6) preparation of an interpretive sediment-toxicity report.
Task 1 – Project planning and reconnaissance will occur during winter/spring of year 1 and consist of finalizing a draft work plan, obtaining RAP committee and other stakeholder input, selecting target study sites, and reconnaissance visits. Prospective study sites will be visited to evaluate accessibility and bed sediments. The sampling plan and field logistics will be finalized following the reconnaissance visits.
Task 2 - Subcontracts for testing acute and chronic toxicity of sediments (using USEPA-approved methods for two invertebrate species - Chironomus dilutus and Hyallela azteca) will be established during spring of year 1. This will entail identifying subcontractors, inviting bids for toxicity tests, assessing bids, selecting the final contract laboratory, and assembling a purchase (or services) agreement.
Task 3 - The field surveys will be done during the summer of year 1, and will consist of collecting benthic-community and sediment samples once from as many as 55 sites in the Niagara River. The Niagara survey does not involve a direct BUI assessment; therefore, a probabilistic sampling design is planned to establish baseline toxicity and community information across the entire AOC prior to active remediation. This design will enable us to define the current conditions in depositional areas with statistically defensible metrics; i.e., with known levels of variability (Diaz-Ramos et al., 1996; Stevens and Olsen, 1999). Ten percent of sediment samples will be collected in duplicate to evaluate the reproducibility and precision of endpoints for the toxicity tests. At each site, a Petite Ponar sampler will be used to collect 5 replicate macroinvertebrate-community samples, and to collect a single composite sediment sample for toxicity testing. Bed-sediment size and organic content will be quantified by a NYSDEC subcontract laboratory using a split from the composite sediment-toxicity sample.
Task 4 - The sediment toxicity tests or bioassays will be conducted by a subcontract laboratory during summer/fall of year 1 to define the current levels of toxicity in sediments from study sites in the AOC. Acute (survival) and chronic (growth) toxicity tests will be conducted using C. dilutus and H. azteca and follow standard USEPA-approved methods (ASTM, 2010; USEPA, 1994, 2000).
Task 5 - Data analysis and interpretation will be conducted during the winter/spring of year 2. Graphical and statistical analyses, including multivariate ordination methods, will be used to summarize current (baseline) sediment toxicity levels and potential contaminant and toxicity strata across the Niagara River AOC. Results will also be used to quantify variability and to evaluate the suitability of the current benthos-BUI designation.
Task 6 - One USGS report or peer-reviewed journal manuscript (paper) will be prepared during the spring/summer/fall of year 2 in collaboration with NYSDEC and NOAA staff. This report will summarize baseline sediment-toxicity levels and identify potential toxicity strata across the Niagara AOC. The report/paper will undergo USGS technical and editorial reviews and revision prior to submission for publication internally or via a peer-reviewed journal.
References:
Report
George, S.D., Baldigo, B.P., and Duffy, B.T., 2016, Toxicity of bed sediments from the Niagara River Area of Concern and tributaries, New York, to Chironomus dilutus and Hyalella azteca, 2014–15: U.S. Geological Survey Data Series 1016, 8 p., https://pubs.er.usgs.gov/publication/ds1016
Project
Location by CountyNiagara County, NY, Erie County, NY
- Source: USGS Sciencebase (id: 55e043fae4b0f42e3d040e54)
- Connect