Data from 10-day sediment toxicity tests of bed sediments from the Eighteenmile Creek Area of Concern and Oak Orchard Creek (nearby reference stream), Niagara and Orleans County, New York, respectively. Specifically, the data was used to compare the survival and growth of two macroinvertebrate species in sediments from study sites and laboratory controls. Results are from 10-day sediment exposures of two test species, Chironomus dilutus and Hyalella azteca. Sediment samples were collected from five sites on each stream. Bed-sediments were collected from depositional areas using a petite Ponar (0.03 square meter) dredge. At each site, approximately five grabs were composited into a bucket, mixed, and a 4-liter (L) subsample was stored in a polyethylene container. Sediment toxicity testing were then conducted by a contract laboratory to quantify toxicity with the dipteran, Chironomus dilutus, and the amphipod, Hyalella azteca, during 10-day survival and growth bioassays following USEPA test methods 100.2 and 100.1, respectively. U.S. Environmental Protection Agency, 2000, Methods for measuring the toxicity and bioaccumulation of sediment associated contaminants with freshwater invertebrates. Second edition: U.S. Environmental Protection Agency, Office of Research and Development EPA 600/R-99/064. This spreadsheet contains 13 columns. The first 7 columns describe the sample collection information, the remaining 6 columns provide the survival and growth results of two test species used in sediment toxicity tests. The data include the stream name, site ID, latitude and longitude, replicate number, and site type. Six columns of results from 10-day sediment exposures of two test species, Chironomus dilutus and Hyalella azteca. The following endpoints were measured for each species following the 10-day exposure: number of surviving organisms, percentage of organisms surviving (hereafter survival), and average ash-free dry weight of the surviving organisms (hereafter growth).

Data from 10-day sediment toxicity tests of bed sediments from the Eighteenmile Creek Area of Concern and Oak Orchard Creek (nearby reference stream), Niagara and Orleans County, New York, respectively. Specifically, the data was used to compare the survival and growth of two macroinvertebrate species in sediments from study sites and laboratory controls. Results are from 10-day sediment exposures of two test species, Chironomus dilutus and Hyalella azteca. Sediment samples were collected from five sites on each stream. Bed-sediments were collected from depositional areas using a petite Ponar (0.03 square meter) dredge. At each site, approximately five grabs were composited into a bucket, mixed, and a 4-liter (L) subsample was stored in a polyethylene container. Sediment toxicity testing were then conducted by a contract laboratory to quantify toxicity with the dipteran, Chironomus dilutus, and the amphipod, Hyalella azteca, during 10-day survival and growth bioassays following USEPA test methods 100.2 and 100.1, respectively. U.S. Environmental Protection Agency, 2000, Methods for measuring the toxicity and bioaccumulation of sediment associated contaminants with freshwater invertebrates. Second edition: U.S. Environmental Protection Agency, Office of Research and Development EPA 600/R-99/064. This spreadsheet contains 13 columns. The first 7 columns describe the sample collection information, the remaining 6 columns provide the survival and growth results of two test species used in sediment toxicity tests. The data include the stream name, site ID, latitude and longitude, replicate number, and site type. Six columns of results from 10-day sediment exposures of two test species, Chironomus dilutus and Hyalella azteca. The following endpoints were measured for each species following the 10-day exposure: number of surviving organisms, percentage of organisms surviving (hereafter survival), and average ash-free dry weight of the surviving organisms (hereafter growth).

This data release provides contaminant data from bed sediment collected from small streams between 2021 and 2024 in the Chesapeake Bay Watershed. These data are part of a larger study designed to determine how conservation practices are affecting local stream ecosystem health, which stressors are negatively impacting streams, and which landscape characteristics are associated with better or worse conditions in local streams. Samples were analyzed at RTI Laboratories Incorporated, Livonia, Michigan and The U.S. Geological Survey, Florence Bascom Geoscience Center, Wetland Ecosystem Ecology and Biogeochemistry Lab, Reston, Virginia. Exact site location information for these sites is not available as a result of privacy concerns.

A data release containing information on macroinvertebrate communities and sediment toxicity in the Niagara River and adjacent areas collected during a sampling effort conducted between 2019 and 2020, and a sampling effort conducted in 2022. During the first sampling effort, bed sediments were collected at 60 sites in the Niagara River, 5 sites on lower Smoke Creek, and 6 sites on Hoyt Lake for use in sediment toxicity testing and determination of grain size distribution and total organic carbon concentration. Additionally, macroinvertebrate samples were collected from the 60 sites on the Niagara River. During the second sampling effort, bed sediments were collected at 10 sites on lower Smoke Creek (5 of which were repeated from the first sampling effort), 5 reference sites on upper Smoke Creek, and 6 sites on Hoyt Lake (all of which were repeated from the first sampling effort) for toxicity testing, macroinvertebrate community assessment, and and determination of grain size distribution and total organic carbon concentration. Additionally, sediments were collected at 10 sites in the Black Rock Canal, 5 reference sites in the upper Black Rock Canal, and 5 sites in Erie Basin Marina for macroinvertebrate community assessment. The selection of site locations and analyses was done by the U.S. Army Corps of Engineers and the New York State Department of Environmental Conservation based on existing data gaps and prior sediment chemistry data. For both sampling efforts, in situ habitat measurements were taken at the time of sample collection at all sites. All sediment samples were collected using a petite Ponar dredge. Ten-day sediment toxicity tests were performed using two test species, Chironomus dilutus and Hyalella azteca, following standard USEPA test methods. Macroinvertebrates were identified to the lowest practical taxonomic resolution and used to calculate metrics of biological integrity following standard New York State Department of Environmental Conservation procedures. A morphological deformity analysis was also conducted on the mentum mouthpart of midge larvae in the genus Chironomus as an additional measure of toxicity following standard New York State Department of Environmental Conservation procedures. The data release has five separate tables: one containing site locations and habitat information, one containing the results of sediment toxicity tests, one containing macroinvertebrate identifications, one containing standard New York State Department of Environmental Conservation metrics of macroinvertebrate community integrity calculated from the macroinvertebrate identifications, and one containing the results of the morphological deformity analysis.

A data release containing information on macroinvertebrate communities and sediment toxicity in the Niagara River and adjacent areas collected during a sampling effort conducted between 2019 and 2020, and a sampling effort conducted in 2022. During the first sampling effort, bed sediments were collected at 60 sites in the Niagara River, 5 sites on lower Smoke Creek, and 6 sites on Hoyt Lake for use in sediment toxicity testing and determination of grain size distribution and total organic carbon concentration. Additionally, macroinvertebrate samples were collected from the 60 sites on the Niagara River. During the second sampling effort, bed sediments were collected at 10 sites on lower Smoke Creek (5 of which were repeated from the first sampling effort), 5 reference sites on upper Smoke Creek, and 6 sites on Hoyt Lake (all of which were repeated from the first sampling effort) for toxicity testing, macroinvertebrate community assessment, and and determination of grain size distribution and total organic carbon concentration. Additionally, sediments were collected at 10 sites in the Black Rock Canal, 5 reference sites in the upper Black Rock Canal, and 5 sites in Erie Basin Marina for macroinvertebrate community assessment. The selection of site locations and analyses was done by the U.S. Army Corps of Engineers and the New York State Department of Environmental Conservation based on existing data gaps and prior sediment chemistry data. For both sampling efforts, in situ habitat measurements were taken at the time of sample collection at all sites. All sediment samples were collected using a petite Ponar dredge. Ten-day sediment toxicity tests were performed using two test species, Chironomus dilutus and Hyalella azteca, following standard USEPA test methods. Macroinvertebrates were identified to the lowest practical taxonomic resolution and used to calculate metrics of biological integrity following standard New York State Department of Environmental Conservation procedures. A morphological deformity analysis was also conducted on the mentum mouthpart of midge larvae in the genus Chironomus as an additional measure of toxicity following standard New York State Department of Environmental Conservation procedures. The data release has five separate tables: one containing site locations and habitat information, one containing the results of sediment toxicity tests, one containing macroinvertebrate identifications, one containing standard New York State Department of Environmental Conservation metrics of macroinvertebrate community integrity calculated from the macroinvertebrate identifications, and one containing the results of the morphological deformity analysis.

These data present the results of sediment toxicity tests conducted by the US Geological Survey's Columbia Environmental Research Center (CERC) in Columbia, MO, in 2014. The sediments were collected as one part of a larger study on stream quality in Southeastern USA streams during the summer of 2014. For more information on the larger study see- https://webapps.usgs.gov/rsqa. The data include results from two test species, the amphipod Hyalella azteca and the midge Chironomus dilutus (formerly known as C. tentans). Three endpoints per species tested are listed as survival, growth and biomass from 76 freshwater stream sediments collected in the study. Values listed are the average response across four test replicates per species, per sediment tested, and are listed as both absolute values per test endpoint and as values normalized to organism performance in reference sediments included within the study. Laboratory testing methods followed standard sediment toxicity test methods for these species from American Society for Testing and Materials (E1706-05(2010)) and US EPA method EPA/600/R-99/064 (2000). For more information about the study and analysis of these results, see associated journal article; 'Moran, P.W., Kemble, N.E., Waite, I.R., Mahler, B.J., Nowell, L.H., Van Metre, P.C. 2020. Legacy and current-use contaminants in sediments limit macroinvertebrate communities in Southeastern USA streams. Environmental Toxicology and Chemistry, in press.

These data present the results of sediment toxicity tests conducted by the US Geological Survey's Columbia Environmental Research Center (CERC) in Columbia, MO, in 2014. The sediments were collected as one part of a larger study on stream quality in Southeastern USA streams during the summer of 2014. For more information on the larger study see- https://webapps.usgs.gov/rsqa. The data include results from two test species, the amphipod Hyalella azteca and the midge Chironomus dilutus (formerly known as C. tentans). Three endpoints per species tested are listed as survival, growth and biomass from 76 freshwater stream sediments collected in the study. Values listed are the average response across four test replicates per species, per sediment tested, and are listed as both absolute values per test endpoint and as values normalized to organism performance in reference sediments included within the study. Laboratory testing methods followed standard sediment toxicity test methods for these species from American Society for Testing and Materials (E1706-05(2010)) and US EPA method EPA/600/R-99/064 (2000). For more information about the study and analysis of these results, see associated journal article; 'Moran, P.W., Kemble, N.E., Waite, I.R., Mahler, B.J., Nowell, L.H., Van Metre, P.C. 2020. Legacy and current-use contaminants in sediments limit macroinvertebrate communities in Southeastern USA streams. Environmental Toxicology and Chemistry, in press.

Data from 10-day sediment toxicity tests of bed sediments from the Buffalo River Area of Concern (AOC) and reference reaches on the Buffalo River upstream of the AOC, Erie County, New York, respectively. Specifically, the data was used to compare the survival and growth of two macroinvertebrate species in sediments from study sites and laboratory controls. Results are from 10-day sediment exposures of two test species, Chironomus dilutus and Hyalella azteca. Sediment samples were collected from 8 sites within the AOC and from 6 reference sites upstream of the AOC. Bed-sediments were collected from depositional areas using a petite Ponar (0.03 square meter) dredge. At each site, approximately five grabs were composited into a bucket, mixed, and a 4-liter (L) subsample was stored in a polyethylene container. Sediment toxicity testing were then conducted by a contract laboratory to quantify toxicity with the dipteran, Chironomus dilutus, and the amphipod, Hyalella azteca, during 10-day survival and growth bioassays following USEPA test methods 100.2 and 100.1, respectively. (U.S. Environmental Protection Agency, 2000, Methods for measuring the toxicity and bioaccumulation of sediment associated contaminants with freshwater invertebrates. Second edition: U.S. Environmental Protection Agency, Office of Research and Development EPA 600/R-99/064.) This spreadsheet contains 16 columns. The first 8 columns describe the sample collection information, the remaining 8 columns provide the survival and growth results of two test species used in sediment toxicity tests. The data include the stream name, site ID, National Water Information System (NWIS) ID, latitude and longitude, replicate number, and site type. The following eight columns present results from 10-day sediment exposures of two test species, Chironomus dilutus and Hyalella azteca. The following endpoints were measured for each species following the 10-day exposure: number of surviving organisms, percentage of organisms surviving (hereafter survival), average ash-free dry weight of the surviving organisms (hereafter growth), and ash-free dry weight of the surviving organisms divided by the initial number of organisms (hereafter biomass).

Data from 10-day sediment toxicity tests of bed sediments from the Buffalo River Area of Concern (AOC) and reference reaches on the Buffalo River upstream of the AOC, Erie County, New York, respectively. Specifically, the data was used to compare the survival and growth of two macroinvertebrate species in sediments from study sites and laboratory controls. Results are from 10-day sediment exposures of two test species, Chironomus dilutus and Hyalella azteca. Sediment samples were collected from 8 sites within the AOC and from 6 reference sites upstream of the AOC. Bed-sediments were collected from depositional areas using a petite Ponar (0.03 square meter) dredge. At each site, approximately five grabs were composited into a bucket, mixed, and a 4-liter (L) subsample was stored in a polyethylene container. Sediment toxicity testing were then conducted by a contract laboratory to quantify toxicity with the dipteran, Chironomus dilutus, and the amphipod, Hyalella azteca, during 10-day survival and growth bioassays following USEPA test methods 100.2 and 100.1, respectively. (U.S. Environmental Protection Agency, 2000, Methods for measuring the toxicity and bioaccumulation of sediment associated contaminants with freshwater invertebrates. Second edition: U.S. Environmental Protection Agency, Office of Research and Development EPA 600/R-99/064.) This spreadsheet contains 16 columns. The first 8 columns describe the sample collection information, the remaining 8 columns provide the survival and growth results of two test species used in sediment toxicity tests. The data include the stream name, site ID, National Water Information System (NWIS) ID, latitude and longitude, replicate number, and site type. The following eight columns present results from 10-day sediment exposures of two test species, Chironomus dilutus and Hyalella azteca. The following endpoints were measured for each species following the 10-day exposure: number of surviving organisms, percentage of organisms surviving (hereafter survival), average ash-free dry weight of the surviving organisms (hereafter growth), and ash-free dry weight of the surviving organisms divided by the initial number of organisms (hereafter biomass).

These data represent water and bed sediment samples analyzed for a variety of organic compounds. The samples were collected in streams and rivers in the Chesapeake Bay watershed from 2006-2014. Water samples were collected from 61 sites and analyzed for hormones (SH2434 method; Tables 1A and 1B), pharmaceuticals (SH2080 method; Tables 2A and 2B), wastewater indicators (SH1433 method; Tables 3A and 3B), and antibiotics (LCAB method; Tables 4A and 4B). Select water samples were analyzed at the U.S. Geological Survey National Water Quality Laboratory for pesticides (SH2001 method and SH2003 method; Tables 5A/5B and 6A/6B, respectively), wastewater indicators (SH4433 method; Tables 7A and 7B), pharmaceuticals (SH8244 method; Tables 8A and 8B), and hormones (SH4434 method; Tables 9A and 9B). Bed sediment samples were collected from 56 sites and analyzed for wastewater compounds (SH5433 method; Tables 10A and 10B), hormones (SH6434 method; tables 11A and 11B), and organohalogen compounds (LC8093 method; Tables 12A and 12B). Water samples were analyzed for antibiotics at the U.S. Geological Survey Kansas Organic Geochemistry Laboratory. For each of the 12 laboratory methods there are two files, an analyte file (A; analytical method details) and data file (B; site information and analyte concentration if detected). The information can be downloaded in three formats: CSV (comma delimited; alldata-csv.zip), ASCII TXT (tab delimited; alldata-tab-delim-txt.zip), and XLSX (two Excel 2013 files; each dataset is a workbook tab; alldata.for.scibase.part-01.020317.xlsx [Tables 1-4, 10-12], alldata.for.scibase.part-02.020317.xlsx [Tables 5-9]). The Dataset XML file includes an complete list of Analyte Compounds, Compound Groups, CAS Numbers, and USGS NWIS Parameter codes found in each analyte file and associated data file. The analyte file for each method includes analyte compound names, compound group, CAS Number(s), USGS National Water Information System (NWIS) Parameter code, method detection limit, and reporting limit. Compound groups (in alphabetic order) include Androgen, Antibiotics Human and Veterinary, Antidepressant, Antihistamine, Antiviral, Beta-Blocker/Heart, Caffeine/Nicotine, Estrogen, Flame Retardant, Fungicide, Herbicide, Insecticide, Opiate, Persistent Organic Pollutant, Personal Care/Domestic Use (PCDU), Pesticide, Pharmaceutical, Plant/Animal Biochemical (PAB), Plasticizer, Polychlorinated Biphenyl, Polycyclic Aromatic Hydrocarbon, Progesterone, Progestin, and Stimulant/Abuse. The data file for each laboratory method includes State, Network, Sample Number, Station ID, Sample Date, Sample Time, Compound Group, Compound concentration. Network: CHEDC, data collected between 2012-2013 by the Chesapeake Endocrine Disruption project; PAREC, data available from Pennsylvania (other than Chesapeake Endocrine Disruption project samples)(various years listed in headnote); PA012, data available from Pennsylvania collected before 2013; C2007, data collected in Maryland, Virginia, and West Virginia between 2006-2007; CTEM, data collected at sites in West Virginia (various years listed in headnote). Station ID: When available, U.S. Geological Survey National Water Information (NWIS) site number. Sample time is standard time. Table head notes list sample media: filtered or unfiltered water, or bed sediment. Analyte Concentrations Units are listed in the table headnote (micrograms per kilogram OR nanograms per liter); nd denotes non-detect; dnq denotes detected, but not quantified; concentrations in italics denote replicate of previous sample. Site locations (including latitude/longitude) are provided in interactive map viewer, downloadable ESRI ArcGIS Shape file (Chesapeake_Bay_Watershed_water_and_sediment_sampling_sites_for_ScienceBase4.zip), and ArcGIS Mapping Service (REST Service).