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Quality Control and Soil Quality Data in support of Baseline Environmental Monitoring at the Ammonium Perchlorate Rocket Motor Destruction (ARMD) Facility at the Letterkenny Army Depot, Chambersburg, Pennsylvania, 2016
From September to December, 2016, herein referred to as the baseline characterization period, monthly samples were collected from four groundwater wells, one surface-water site, and nine soil samples near the ARMD Facility. The only surface-water site sampled monthly during the baseline characterization period was upgradient of the facility. There was no streamflow at surface-water sites downgradient from the facility during the baseline characterization period on days when surface-water samples were collected. This Data Release presents the quality control data from ALS laboratories for the groundwater, surface-water, and soil samples (ALS_QAQC.txt). Quality control replicate and blank water samples that are stored in the USGS water-quality database are presented (ARMD_QAQC.txt). Three volatile organic compounds (VOCs), bromomethane, acetone, and chloromethane, and total chloride were detected in blank water samples. No constituents in groundwater or surface-water samples exceeded any U.S. Environmental Protection Agency (EPA) Maximum Contaminant Level (MCL). Dissolved iron (Fe) was the only groundwater constituent that exceeded a Secondary Maximum Contaminant Level (SMCL) established by the EPA. The SMCL for Fe is 300 micrograms per liter (µg/L), and samples from 3 of 4 wells exceeded this value, with exceedance values ranging from 1,100 to 2,600 µg/L. The only VOCs detected in groundwater samples were bromomethane, acetone, and chloromethane. All VOC detections in groundwater samples were less than the Report Detection Levels (RDLs). Detections of bromomethane, acetone, and chloromethane in groundwater ranged from 0.41 - 0.67, 3.4 - 5.4, and 0.44 - 0.46 µg/L, respectively. Bromomethane, acetone, and chloromethane were also detected in blank samples with values ranging from 0.40 to 0.65 µg/L, 5.2 to 5.8 µg/L, and 0.43 to 0.55 µg/L, respectively. No EPA established MCLs or SMCLs were exceeded for any constituents in samples collected from the surface-water site. Similar to groundwater results, some VOCs were detected in surface water at less than the RDLs. The VOCs detected in surface water were generally the same VOCs detected at less than the RDLs for groundwater. Perchlorate was detected in each surface-water sample collected at SW-U, with a mean concentration of 0.07 µg/L. All perchlorate results were less than the RDL of 0.2 µg/L. In addition, the soils data collected at the nine soil sampling sites is presented (ARMD_soils.txt). During the baseline characterization period, monthly soil samples were collected from 9 sites near the ARMD Facility. Soil sites SO-5 and SO-6 were not sampled in December 2016 since the area was paved over with asphalt. The soil samples collected during the baseline characterization period did not show any concentrations that exceeded any medium-specific concentrations (MSC) or soil screening levels (SSL) established by either the state of Pennsylvania or the USEPA. The state of Pennsylvania calculates MSCs based on either a function of acceptable concentrations in groundwater or based on health concerns if the soil is directly contacted. The USEPA derives acceptable concentrations of constituents (SSLs) in soil based on standardized equations combining exposure information assumptions with EPA toxicity data. The USEPA calculates SSLs for residential and industrial sites. Soil sites at the ARMD Facility were considered “industrial” for comparative purposes. There was at least one order of magnitude difference between any inorganic soil concentration detected and the MSC and/or SSL for that constituent. Four VOCs were detected in soil samples collected during the baseline period. None of the VOCs detected in the soils were within three orders of magnitude of any MSCs or SSLs established. The VOCs detected in soil were dichloromethane, methyl tert-butyl ether (MTBE), tetrachloroethene, and acetone (only detected once). Dichloromethane was the only VOC detected above the RDLs, with all samples
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Quality Control and Soil Quality Data in support of Baseline Environmental Monitoring at the Ammonium Perchlorate Rocket Motor Destruction (ARMD) Facility at the Letterkenny Army Depot, Chambersburg, Pennsylvania, 2016
공공데이터포털
From September to December, 2016, herein referred to as the baseline characterization period, monthly samples were collected from four groundwater wells, one surface-water site, and nine soil samples near the ARMD Facility. The only surface-water site sampled monthly during the baseline characterization period was upgradient of the facility. There was no streamflow at surface-water sites downgradient from the facility during the baseline characterization period on days when surface-water samples were collected. This Data Release presents the quality control data from ALS laboratories for the groundwater, surface-water, and soil samples (ALS_QAQC.txt). Quality control replicate and blank water samples that are stored in the USGS water-quality database are presented (ARMD_QAQC.txt). Three volatile organic compounds (VOCs), bromomethane, acetone, and chloromethane, and total chloride were detected in blank water samples. No constituents in groundwater or surface-water samples exceeded any U.S. Environmental Protection Agency (EPA) Maximum Contaminant Level (MCL). Dissolved iron (Fe) was the only groundwater constituent that exceeded a Secondary Maximum Contaminant Level (SMCL) established by the EPA. The SMCL for Fe is 300 micrograms per liter (µg/L), and samples from 3 of 4 wells exceeded this value, with exceedance values ranging from 1,100 to 2,600 µg/L. The only VOCs detected in groundwater samples were bromomethane, acetone, and chloromethane. All VOC detections in groundwater samples were less than the Report Detection Levels (RDLs). Detections of bromomethane, acetone, and chloromethane in groundwater ranged from 0.41 - 0.67, 3.4 - 5.4, and 0.44 - 0.46 µg/L, respectively. Bromomethane, acetone, and chloromethane were also detected in blank samples with values ranging from 0.40 to 0.65 µg/L, 5.2 to 5.8 µg/L, and 0.43 to 0.55 µg/L, respectively. No EPA established MCLs or SMCLs were exceeded for any constituents in samples collected from the surface-water site. Similar to groundwater results, some VOCs were detected in surface water at less than the RDLs. The VOCs detected in surface water were generally the same VOCs detected at less than the RDLs for groundwater. Perchlorate was detected in each surface-water sample collected at SW-U, with a mean concentration of 0.07 µg/L. All perchlorate results were less than the RDL of 0.2 µg/L. In addition, the soils data collected at the nine soil sampling sites is presented (ARMD_soils.txt). During the baseline characterization period, monthly soil samples were collected from 9 sites near the ARMD Facility. Soil sites SO-5 and SO-6 were not sampled in December 2016 since the area was paved over with asphalt. The soil samples collected during the baseline characterization period did not show any concentrations that exceeded any medium-specific concentrations (MSC) or soil screening levels (SSL) established by either the state of Pennsylvania or the USEPA. The state of Pennsylvania calculates MSCs based on either a function of acceptable concentrations in groundwater or based on health concerns if the soil is directly contacted. The USEPA derives acceptable concentrations of constituents (SSLs) in soil based on standardized equations combining exposure information assumptions with EPA toxicity data. The USEPA calculates SSLs for residential and industrial sites. Soil sites at the ARMD Facility were considered “industrial” for comparative purposes. There was at least one order of magnitude difference between any inorganic soil concentration detected and the MSC and/or SSL for that constituent. Four VOCs were detected in soil samples collected during the baseline period. None of the VOCs detected in the soils were within three orders of magnitude of any MSCs or SSLs established. The VOCs detected in soil were dichloromethane, methyl tert-butyl ether (MTBE), tetrachloroethene, and acetone (only detected once). Dichloromethane was the only VOC detected above the RDLs, with all samples
Groundwater, surface water, and soil data collected near and at the Ammonium Perchlorate Rocket Motor Destruction (ARMD) facility at the Letterkenny Army Depot, Chambersburg, Pennsylvania
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Sampling was conducted by the U.S. Geological Survey (USGS) at four wells, one surface water site, and five soil sampling locations near and at the Ammonium Perchlorate Rocket Motor Destruction (ARMD) facility at the Letterkenny Army Depot. Analytical results for groundwater samples collected in 2021 are provided in “ARMD_wells_data_2021.xlsx”. Analytical results for surface-water samples collected in 2021 are provided in “ARMD_sw_data_2021.xlsx”. Analytical results for soil samples collected in 2021 are provided in “ARMD_soil_data_2021.xlsx”. The data files with analytical results also include quality assurance/quality control sample results.
Groundwater, surface water, and soil data collected near and at the Ammonium Perchlorate Rocket Motor Destruction (ARMD) facility at the Letterkenny Army Depot, Chambersburg, Pennsylvania
공공데이터포털
Sampling was conducted by the U.S. Geological Survey (USGS) at four wells, one surface water site, and five soil sampling locations near and at the Ammonium Perchlorate Rocket Motor Destruction (ARMD) facility at the Letterkenny Army Depot. Analytical results for groundwater samples collected in 2021 are provided in “ARMD_wells_data_2021.xlsx”. Analytical results for surface-water samples collected in 2021 are provided in “ARMD_sw_data_2021.xlsx”. Analytical results for soil samples collected in 2021 are provided in “ARMD_soil_data_2021.xlsx”. The data files with analytical results also include quality assurance/quality control sample results.
Soil Chemistry and Quality Control Data in support of Environmental Monitoring at the Open Burning/Open Detonation (OB/OD) areas in the Ammunition Area (AA) at Letterkenny Army Depot, Chambersburg, Pennsylvania, 2021 (version 1.1, February 2022)
공공데이터포털
Soil sampling was needed to provide analytical soil data for areas near the Open Burning/Open Detonation (OB/OD) areas in the Ammunition Area (AA) of Letterkenny Army Depot. The U.S. Geological Survey sampled 10 locations and prepared the samples for chemical analyses. Samples were collected from depths of zero to six inches with a stainless-steel trowel. Multiple subsamples (10-20) were homogenized at each location in a disposable plastic bowl, and the homogenized samples were used to fill two eight-ounce glass containers for each location. Seven soil sampling locations were in forested areas, two were in open-field areas, and one was at a forest-field interface. The results will be used to determine impacts of OB/OD activities on areas near the OB/OD area. This Data Release presents the analytical chemistry soil results (OBOD_soil_analytical.txt and OBOD_soil_MS.txt) for samples collected near the OB/OD area on April 21, 2021. Results for environmental samples and one replicate are provided in “OBOD_soil_analytical.txt“, and results for a matrix spike/matrix spike replicate are provided in “OBOD_soil_MS.txt”. Samples were analyzed for anions, metals, and selected explosive compounds. Metals that were detected at the highest concentrations were iron (range of 32,100 to 47,000 milligrams per kilogram (mg/kg)), aluminum (range of 22,200 to 26,800 mg/kg), and manganese (range of 1,040 to 2,460 mg/kg). Cadmium, chromium(VI), mercury, molybdenum, selenium, silver, and thallium were all detected at mean concentrations below one mg/kg. No chloride, sulfate, antimony, or tin were detected at any of the sampling locations. Explosive compounds analyzed as part of this study included perchlorate, 2-amino-4,6-dinitrotoluene, 4-amino-2,6-dinitrotoluene, 2,4-dinitrotoluene, 1,3,5-Trinitrobenzene, nitroglycerin, nitroguanidine, nitrocellulose, 2,4,6-trinitrotoluene (TNT), high melting explosive (HMX), royal demolition explosive (RDX), and tetryl. Results for explosive compounds were below the detection limit for all compounds analyzed. Matrix-spike data showed that percent recoveries for explosive compounds were within acceptable quality-control (QC) limits. For the 28 other constituents, twenty had acceptable recoveries within QC limits. The metals with the highest concentrations (iron, aluminum, manganese, barium, and zinc) had recoveries that were outside acceptable QC limits. Fluoride, antimony, and chromium(VI) had percent recoveries that were below acceptable QC limits. The analytical chemistry data reported for soil samples collected in April 2021 near the Open Burning/Open Detonation (OB/OD) areas in the Ammunition Area (AA) at Letterkenny Army Depot will be used to determine if there are any impacts to the nearby soil environment from current and past activities within the OB/OD areas. Version 1.1 revision of this data release includes a data validation report of the analytical data presented in the original data release (version 1.0). Version 1.1 provides an analysis of the quality assurance/quality control data provided by the analytical laboratories. This was conducted to determine if any additional data qualifiers were necessary for any constituents. NOTE: The previous version is available from the author; all of the data in the previous version can be found in version 1.1. First posted - September 16, 2021 (available from author) Revised - February 15, 2022 (version 1.1)
Soil Chemistry and Quality Control Data in support of Environmental Monitoring at the Open Burning/Open Detonation (OB/OD) areas in the Ammunition Area (AA) at Letterkenny Army Depot, Chambersburg, Pennsylvania, 2021 (version 1.1, February 2022)
공공데이터포털
Soil sampling was needed to provide analytical soil data for areas near the Open Burning/Open Detonation (OB/OD) areas in the Ammunition Area (AA) of Letterkenny Army Depot. The U.S. Geological Survey sampled 10 locations and prepared the samples for chemical analyses. Samples were collected from depths of zero to six inches with a stainless-steel trowel. Multiple subsamples (10-20) were homogenized at each location in a disposable plastic bowl, and the homogenized samples were used to fill two eight-ounce glass containers for each location. Seven soil sampling locations were in forested areas, two were in open-field areas, and one was at a forest-field interface. The results will be used to determine impacts of OB/OD activities on areas near the OB/OD area. This Data Release presents the analytical chemistry soil results (OBOD_soil_analytical.txt and OBOD_soil_MS.txt) for samples collected near the OB/OD area on April 21, 2021. Results for environmental samples and one replicate are provided in “OBOD_soil_analytical.txt“, and results for a matrix spike/matrix spike replicate are provided in “OBOD_soil_MS.txt”. Samples were analyzed for anions, metals, and selected explosive compounds. Metals that were detected at the highest concentrations were iron (range of 32,100 to 47,000 milligrams per kilogram (mg/kg)), aluminum (range of 22,200 to 26,800 mg/kg), and manganese (range of 1,040 to 2,460 mg/kg). Cadmium, chromium(VI), mercury, molybdenum, selenium, silver, and thallium were all detected at mean concentrations below one mg/kg. No chloride, sulfate, antimony, or tin were detected at any of the sampling locations. Explosive compounds analyzed as part of this study included perchlorate, 2-amino-4,6-dinitrotoluene, 4-amino-2,6-dinitrotoluene, 2,4-dinitrotoluene, 1,3,5-Trinitrobenzene, nitroglycerin, nitroguanidine, nitrocellulose, 2,4,6-trinitrotoluene (TNT), high melting explosive (HMX), royal demolition explosive (RDX), and tetryl. Results for explosive compounds were below the detection limit for all compounds analyzed. Matrix-spike data showed that percent recoveries for explosive compounds were within acceptable quality-control (QC) limits. For the 28 other constituents, twenty had acceptable recoveries within QC limits. The metals with the highest concentrations (iron, aluminum, manganese, barium, and zinc) had recoveries that were outside acceptable QC limits. Fluoride, antimony, and chromium(VI) had percent recoveries that were below acceptable QC limits. The analytical chemistry data reported for soil samples collected in April 2021 near the Open Burning/Open Detonation (OB/OD) areas in the Ammunition Area (AA) at Letterkenny Army Depot will be used to determine if there are any impacts to the nearby soil environment from current and past activities within the OB/OD areas. Version 1.1 revision of this data release includes a data validation report of the analytical data presented in the original data release (version 1.0). Version 1.1 provides an analysis of the quality assurance/quality control data provided by the analytical laboratories. This was conducted to determine if any additional data qualifiers were necessary for any constituents. NOTE: The previous version is available from the author; all of the data in the previous version can be found in version 1.1. First posted - September 16, 2021 (available from author) Revised - February 15, 2022 (version 1.1)
Groundwater, surface water, bed sediment, soil, benthic macroinvertebrate taxa, habitat, and biological indices data collected near and at the Open Burning/Open Detonation (OB/OD) Areas at the Letterkenny Army Depot, Chambersburg, Pennsylvania, (ver. 3.0, September 2025)
공공데이터포털
Groundwater, surface water, sediment and soil sampling was conducted by the U.S. Geological Survey (USGS) at nine groundwater wells, eight surface water sites, three bed sediment retention ponds, and two fields, respectively at areas near and within the Open Burning/Open Detonation (OB/OD) areas in the Ammunition Area (AA) of Letterkenny Army Depot. Analytical results for groundwater samples collected from 2018-2023 are provided in “OBOD_wells_data_2018-2023.xlsx”. Analytical results for surface-water samples from 2018-2023 are provided in “OBOD_sw_data_2018-2023.xlsx”. Benthic macroinvertebrate taxonomic data collected from 2018-2023 at three streams are also provided in “OBOD_benthic_taxa_2018-2023.xlsx”. The field and habitat data for benthic-macroinvertebrate sampling are provided in “OBOD_benthic_field_data_2018-2023.xlsx” and “OBOD_benthic_habitat_data_2018-2023.xlsx”, respectively. The form used to assess habitat is provided in “OBOD_benthic_habitat_assessment_form.xlsx”. The biological metrics for the benthic macroinvertebrate data are provided in “OBOD_benthic_metrics_2018-2023.xlsx”. Analytical results for soil samples collected from 2019-2023 are provided in “OBOD_soil_data_2019-2023.xlsx”. Analytical results for bed sediment samples collected from 2018-2023 are provided in “OBOD_bed_sediment_data_2018-2023.xlsx”. The data files with analytical results also include quality assurance/quality control sample results. NOTE: While previous versions are available from the author, all the records in the previous versions can be found in version 3.0. In this version, water-quality data from 2022 and 2023 were appended to the files. Additional columns with parameter, data qualifier, and remark code information were added to 5 of the data files. First Posted - September 23, 2022 (available from author) Revised - April 18, 2024 (version 2.0 - available from author) Revised - September 2, 2025 (version 3.0)
Groundwater, surface water, bed sediment, soil, benthic macroinvertebrate taxa, habitat, and biological indices data collected near and at the Open Burning/Open Detonation (OB/OD) Areas at the Letterkenny Army Depot, Chambersburg, Pennsylvania, (ver. 3.0, September 2025)
공공데이터포털
Groundwater, surface water, sediment and soil sampling was conducted by the U.S. Geological Survey (USGS) at nine groundwater wells, eight surface water sites, three bed sediment retention ponds, and two fields, respectively at areas near and within the Open Burning/Open Detonation (OB/OD) areas in the Ammunition Area (AA) of Letterkenny Army Depot. Analytical results for groundwater samples collected from 2018-2023 are provided in “OBOD_wells_data_2018-2023.xlsx”. Analytical results for surface-water samples from 2018-2023 are provided in “OBOD_sw_data_2018-2023.xlsx”. Benthic macroinvertebrate taxonomic data collected from 2018-2023 at three streams are also provided in “OBOD_benthic_taxa_2018-2023.xlsx”. The field and habitat data for benthic-macroinvertebrate sampling are provided in “OBOD_benthic_field_data_2018-2023.xlsx” and “OBOD_benthic_habitat_data_2018-2023.xlsx”, respectively. The form used to assess habitat is provided in “OBOD_benthic_habitat_assessment_form.xlsx”. The biological metrics for the benthic macroinvertebrate data are provided in “OBOD_benthic_metrics_2018-2023.xlsx”. Analytical results for soil samples collected from 2019-2023 are provided in “OBOD_soil_data_2019-2023.xlsx”. Analytical results for bed sediment samples collected from 2018-2023 are provided in “OBOD_bed_sediment_data_2018-2023.xlsx”. The data files with analytical results also include quality assurance/quality control sample results. NOTE: While previous versions are available from the author, all the records in the previous versions can be found in version 3.0. In this version, water-quality data from 2022 and 2023 were appended to the files. Additional columns with parameter, data qualifier, and remark code information were added to 5 of the data files. First Posted - September 23, 2022 (available from author) Revised - April 18, 2024 (version 2.0 - available from author) Revised - September 2, 2025 (version 3.0)
Groundwater, surface water, bed sediment, soil, benthic macroinvertebrate taxa, habitat, and biological indices data collected near and at the Open Burning/Open Detonation (OB/OD) Areas at the Letterkenny Army Depot, Chambersburg, Pennsylvania, (ver. 3.0, September 2025)
공공데이터포털
Sampling is conducted by the U.S. Geological Survey (USGS) at nine wells, eight surface water sites, three bed sediment retention ponds, and two fields for soil samples at areas near and within the Open Burning/Open Detonation (OB/OD) areas in the Ammunition Area (AA) of Letterkenny Army Depot. Analytical results for groundwater samples collected from 2018-2021 are provided in “OBOD_wells_data_2018-2021.xlsx”. Analytical results for surface-water samples from 2018-2021 are provided in “OBOD_sw_data_2018-2021.xlsx”. Benthic macroinvertebrate taxonomic data collected from 2018-2021 at three streams are provided in “OBOD_benthic_taxa_2018-2021.xlsx”. The biological metrics for the benthic macroinvertebrate data are provided in “OBOD_benthic_metrics_2018-2021.xlsx”. Analytical results for soil samples collected from 2019-2020 are provided in “OBOD_soil_data_2019-2020.xlsx”. Analytical results for bed sediment samples collected from 2018-2020 are provided in “OBOD_bed_sediment_data_2018-2020.xlsx”. The data files with analytical results also include quality assurance/quality control sample results.
Data for Characterization of Ambient Groundwater Quality within a State-wide, Fixed Station Monitoring Network in Pennsylvania, 2015-2019
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This dataset contains quality-assurance and quality-control data (QA/QC) not publicly available in the online National Water Information System (NWIS) for the Pennsylvania Groundwater Monitoring Network collected by the U.S. Geological Survey (USGS) in Pennsylvania, 2015-2019. The quality-control data (such as blanks and replicates) were collected at a subset of sites to ensure that the data meets specific data-quality objectives of this program. Also included in this data release are the supplemental tables for the accompanying USGS publication “Characterization of Ambient Groundwater Quality within a State-wide, Fixed Station Monitoring Network in Pennsylvania, 2015-2019.” The supplemental tables consist of: 1) a correlation matrix using results from principal components analysis (PCA) and 2) individual contributions of each sample to the PCA results are also included.
Biogeochemical analyses of water samples collected in the mudstone aquifer underlying the Naval Air Warfare Center, West Trenton, NJ (2008-2013)
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These data sets present results from the analyses of groundwater samples collected from monitoring wells and monitoring intervals in bedrock wells in the mudstone aquifer underlying the former Naval Air Warfare Center (NAWC), West Trenton, NJ. The water samples were collected between 2008 and 2013 and were analyzed for field parameters, inorganic and organic constituents, and the abundances of selected microbes of importance to the evaluation of biological degradation of organic contaminants in groundwater. The collection and analyses of the groundwater samples coincides with conducting a bioaugmentation experiment in a targeted region of the mudstone aquifer. The purpose of the bioaugmentation was to introduce and stimulate microbial species that are capable of degrading trichloroethene (TCE). The bioaugmentation experiment was initiated on October 15, 2008. Samples were collected in wells prior to the start of the experiment and for a period of 5 years after the experiment was initiated.