{"pageNumber":"133","pageRowStart":"3300","pageSize":"25","recordCount":6233,"records":[{"id":53354,"text":"wdrKS021 - 2003 - Water Resources Data, Kansas, Water Year 2002","interactions":[],"lastModifiedDate":"2012-02-02T00:11:25","indexId":"wdrKS021","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":340,"text":"Water Data Report","code":"WDR","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"KS-02-1","title":"Water Resources Data, Kansas, Water Year 2002","docAbstract":"Water-resources data for the 2002 water year for Kansas consist of records of stage, discharge, and water quality of streams; elevation and contents of lakes and reservoirs; and water levels of ground-water wells. This report contains records for water discharge at 149 complete-record gaging stations; elevation and contents at 20 lakes and reservoirs; waterquality records at 2 precipitation stations, water-level data at 18 observation wells; and records of specific conductance, pH, water temperature, dissolved oxygen, and turbidity at 11 gaging stations. Also included are discharge data for 26 high-flow partial-record stations, miscellaneous onsite water-quality data collected at 142 stations, and suspended-sediment concentration for 12 stations. These data represent that part of the National Water Information System collected by the U.S. Geological Survey in cooperation with local, State, and Federal agencies in Kansas.","language":"ENGLISH","doi":"10.3133/wdrKS021","usgsCitation":"Putnam, J., and Schneider, D., 2003, Water Resources Data, Kansas, Water Year 2002: U.S. Geological Survey Water Data Report KS-02-1, 539 p., https://doi.org/10.3133/wdrKS021.","productDescription":"539 p.","costCenters":[],"links":[{"id":179124,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"},{"id":5076,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.water.usgs.gov/wdr-ks-02-1/","linkFileType":{"id":5,"text":"html"}}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4a0ae4b07f02db5fb7f8","contributors":{"authors":[{"text":"Putnam, J.E.","contributorId":54634,"corporation":false,"usgs":true,"family":"Putnam","given":"J.E.","email":"","affiliations":[],"preferred":false,"id":247353,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Schneider, D.R.","contributorId":67579,"corporation":false,"usgs":true,"family":"Schneider","given":"D.R.","email":"","affiliations":[],"preferred":false,"id":247354,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":47515,"text":"wri024204 - 2003 - Simulation of the shallow aquifer in the vicinity of Silver Lake, Washington County, Wisconsin, using analytic elements","interactions":[],"lastModifiedDate":"2022-09-28T18:58:04.096795","indexId":"wri024204","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":342,"text":"Water-Resources Investigations Report","code":"WRI","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"2002-4204","title":"Simulation of the shallow aquifer in the vicinity of Silver Lake, Washington County, Wisconsin, using analytic elements","docAbstract":"<p>Shallow ground-water flow in the vicinity of Silver Lake, Washington County, Wisconsin, was investigated to develop an understanding of the hydrology of the shallow aquifer, define a water balance for the lake, delineate ground-water recharge areas for the lake, and to estimate solute flux toward the lake. A single-layer, steady-state, analytic-element model was used to simulate shallow ground-water flow. Regional model parameters include a recharge rate of 4 inches per year, hydraulic conductivity of 50 feet per day and a model base of 800 feet above sea level. A model inhomogeneity was added to represent deviations from these regional values for an area roughly coincident with the Kettle Moraine Area that trends through the study area. Model calibration was accomplished by varying the regional parameter values and those of the inhomogeneity through trial-and-error to determine a best-fit match between simulated and measured values for head and streamflow targets. There was no change to the regional parameter values as a result of calibration, however, the calibrated values for the inhomogeneity are: recharge rate of 12 inches per year, hydraulic conductivity of 20 feet per day, and a model base of 900 feet. These changes represent a four- to five-fold reduction in transmissivity within the inhomogeneity as compared to the regional model.</p>\n<p>A Silver Lake water budget was defined using both published hydrologic data and simulations using the calibrated model. Model simulations show that 1.08 cubic feet per second of ground water enters Silver Lake on the upgradient (primarily western) side and 0.08 cubic feet per second recharges to ground water on the downgradient (primarily eastern) side. Net precipitation (precipitation minus evaporation) on the lake is 0.04 cubic feet per second. Collectively, these water-budget terms provide a residual value of 1.04 cubic feet per second flow to Silver Creek at the north end of Silver Lake, which is a very good match to the range of measured flow (0.7 to 5.2 cubic feet per second). Ground-water recharge areas for Silver Lake are largely on the western side of the lake. The recharge area for the northern two-thirds of Silver Lake is west toward Big Cedar Lake. Assuming a porosity of 20 percent, model results indicate that the 50-year time-of-travel for recharge to Silver Lake does not extend to Big Cedar Lake. The recharge area for the southern one-third of Silver Lake is west toward Little Cedar Lake. Model results indicate that time of travel for recharge to Silver Lake from Little Cedar Lake is about 15 to 20 years. For travel times greater than 15 or 20 years, the ground-water recharge area for Little Cedar Lake and inflow from Big Cedar Lake also should be considered recharge affecting Silver Lake. Solute flux toward Silver Lake was calculated based on simulated ground-water flux and measured concentrations in the upgradient piezometers and observation wells.</p>","language":"English","publisher":"U.S. Geological Survey","doi":"10.3133/wri024204","collaboration":"Prepared in cooperation with the Silver Lake Protection and Rehabilitation District","usgsCitation":"Dunning, C.P., Thomas, J.C., and Lin, Y., 2003, Simulation of the shallow aquifer in the vicinity of Silver Lake, Washington County, Wisconsin, using analytic elements: U.S. Geological Survey Water-Resources Investigations Report 2002-4204, v, 29 p., https://doi.org/10.3133/wri024204.","productDescription":"v, 29 p.","numberOfPages":"35","onlineOnly":"N","additionalOnlineFiles":"N","costCenters":[{"id":677,"text":"Wisconsin Water Science Center","active":true,"usgs":true}],"links":[{"id":407533,"rank":4,"type":{"id":36,"text":"NGMDB Index Page"},"url":"https://ngmdb.usgs.gov/Prodesc/proddesc_54501.htm","linkFileType":{"id":5,"text":"html"}},{"id":168727,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/wri/2002/4204/report-thumb.jpg"},{"id":84454,"rank":299,"type":{"id":11,"text":"Document"},"url":"https://pubs.usgs.gov/wri/2002/4204/report.pdf","linkFileType":{"id":1,"text":"pdf"}}],"country":"United States","state":"Wisconsin","county":"Washington County","otherGeospatial":"Silver Lake","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"type\": \"Polygon\",\n        \"coordinates\": [\n          [\n            [\n              -88.29299926757812,\n              43.34540466524301\n            ],\n            [\n              -88.29299926757812,\n              43.42699324866588\n            ],\n            [\n              -88.18107604980469,\n              43.42699324866588\n            ],\n            [\n              -88.18107604980469,\n              43.34540466524301\n            ],\n            [\n              -88.29299926757812,\n              43.34540466524301\n            ]\n          ]\n        ]\n      }\n    }\n  ]\n}","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4b06e4b07f02db69a0eb","contributors":{"authors":[{"text":"Dunning, C. P.","contributorId":35792,"corporation":false,"usgs":true,"family":"Dunning","given":"C.","email":"","middleInitial":"P.","affiliations":[],"preferred":false,"id":235603,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Thomas, Judith Coffman","contributorId":73261,"corporation":false,"usgs":true,"family":"Thomas","given":"Judith","email":"","middleInitial":"Coffman","affiliations":[],"preferred":false,"id":235604,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Lin, Yu-Feng","contributorId":108167,"corporation":false,"usgs":true,"family":"Lin","given":"Yu-Feng","affiliations":[],"preferred":false,"id":235605,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
,{"id":56148,"text":"wdrNY022 - 2003 - Water resources data, New York, water year 2002, volume 2, Long Islan","interactions":[],"lastModifiedDate":"2017-03-28T10:33:39","indexId":"wdrNY022","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":340,"text":"Water Data Report","code":"WDR","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"NY-02-2","title":"Water resources data, New York, water year 2002, volume 2, Long Islan","docAbstract":"<p>Water resources data for the 2002 water year for New York consist of records of stage, discharge, and water quality of streams; stage, contents, and water quality of lakes and ponds; stage and water quality of estuaries; and water levels and water quality of ground-water wells. This volume contains records for water discharge at 15 gaging stations; lake stage at 6 gaging stations; tide stage at 5 gaging stations; and water levels at 464 observation wells. Also included are data for 10 low-flow partial record stations. Additional water data were collected at various sites not involved in the systematic data collection program, and are published as miscellaneous measurements and analyses. These data, together with the data in Volume 1 and 3 represent that part of the National Water Data system operated by the U.S. Geological Survey in cooperation with State, Federal, and other agencies in New York.</p>","language":"English","publisher":"U.S. Geological Survey","publisherLocation":"Reston, VA","doi":"10.3133/wdrNY022","collaboration":"Prepared in cooperation with the local agencies","usgsCitation":"Spinello, A.G., Busciolano, R., Pena-Cruz, G., and Winowitch, R., 2003, Water resources data, New York, water year 2002, volume 2, Long Islan: U.S. Geological Survey Water Data Report NY-02-2, 262 p., https://doi.org/10.3133/wdrNY022.","productDescription":"262 p.","onlineOnly":"Y","additionalOnlineFiles":"N","costCenters":[{"id":474,"text":"New York Water Science Center","active":true,"usgs":true}],"links":[{"id":184534,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/wdr/2002/ny-02-2/coverthb.jpg"},{"id":5636,"rank":300,"type":{"id":11,"text":"Document"},"url":"https://pubs.usgs.gov/wdr/2002/ny-02-2/wdr_ny022.pdf","text":"Report","size":"4.28 MB","linkFileType":{"id":1,"text":"pdf"},"description":"WDR 022"}],"contact":"<p>Director, New York Water Science Center<br /> U.S. Geological Survey<br /> 425 Jordan Rd<br /> Troy, NY 12180-8349<br /> (518) 285-5695<br /> <a href=\"http://ny.water.usgs.gov/\">http://ny.water.usgs.gov/</a></p>","tableOfContents":"<ul>\n<li>New York district office locations and addresses</li>\n<li>Preface</li>\n<li>List of surface-water stations, in downstream order, for which records are published in this volume</li>\n<li>List of discontinued surface-water discharge stations</li>\n<li>Introduction</li>\n<li>Cooperation</li>\n<li>Summary of hydrologic conditions</li>\n<li>Special networks and programs</li>\n<li>Explanation of the records</li>\n<li>Selected recent U.S. Geological Survey reports relevant to Long Island, New York</li>\n<li>Access to USGS water data</li>\n<li>Definition of terms</li>\n<li>Publications on Techniques of Water-Resources Investigations</li>\n<li>Station records, surface water</li>\n<li>Station records, ground water</li>\n<li>Analysis of samples collected at water-quality miscellaneous sites</li>\n<li>Index</li>\n</ul>","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e49f5e4b07f02db5f0d91","contributors":{"authors":[{"text":"Spinello, A. G.","contributorId":19983,"corporation":false,"usgs":true,"family":"Spinello","given":"A.","email":"","middleInitial":"G.","affiliations":[],"preferred":false,"id":254830,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Busciolano, R.","contributorId":24017,"corporation":false,"usgs":true,"family":"Busciolano","given":"R.","email":"","affiliations":[],"preferred":false,"id":254831,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Pena-Cruz, G.P.","contributorId":39868,"corporation":false,"usgs":true,"family":"Pena-Cruz","given":"G.P.","email":"","affiliations":[],"preferred":false,"id":254832,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Winowitch, R.B.","contributorId":67148,"corporation":false,"usgs":true,"family":"Winowitch","given":"R.B.","email":"","affiliations":[],"preferred":false,"id":254833,"contributorType":{"id":1,"text":"Authors"},"rank":4}]}}
,{"id":53285,"text":"wdrPA022 - 2003 - Water Resources Data, Pennsylvania, Water Year 2002, Volume 2. Susquehanna and Potomac River Basins","interactions":[],"lastModifiedDate":"2018-05-29T12:57:49","indexId":"wdrPA022","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":340,"text":"Water Data Report","code":"WDR","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"PA-02-2","title":"Water Resources Data, Pennsylvania, Water Year 2002, Volume 2. Susquehanna and Potomac River Basins","docAbstract":"Water-resources data for the 2002 water year for Pennsylvania consists of records of discharge and water quality of streams; contents and elevations of lakes and reservoirs; and water levels and water quality of ground-water wells. This report, Volume 2 contains (1) discharge records for 82 continuous-record streamflow-gaging stations, 13 partial-record stations, 24 special study and miscellaneous streamflow sites, and 33 low-flow miscellaneous streamflow sites; (2) elevation and contents records for 12 lake and reservoirs; (3) water-quality records for 33 gaging stations and 104 ungaged streamsites; (4) water-level records for 38 network observation wells; (5) water-quality analyses at 32 special study ground-water wells; and (6) miscellaneous water-level measurements at 31 special study ground-water wells. Site locations are shown in figures throughout the report. Additional water data collected at various sites not involved in the systematic data-collection program are also presented. These data together with the data in Volumes 1 and 3, represent that part of the National Water Data System operated by the U.S. Geological Survey and cooperating State, local, and Federal agencies in Pennsylvania.","language":"English","publisher":"U.S. Geological Survey","publisherLocation":"Reston, VA","doi":"10.3133/wdrPA022","collaboration":"Prepared in cooperation with the Pennsylvania Department of Environmental Protection, the Baltimore District of the U.S. Army Corps of Engineers, and with the other State, municipal, and Federal agencies","usgsCitation":"Durlin, R.R., and Schaffstall, W.P., 2003, Water Resources Data, Pennsylvania, Water Year 2002, Volume 2. Susquehanna and Potomac River Basins: U.S. Geological Survey Water Data Report PA-02-2, 536 p., https://doi.org/10.3133/wdrPA022.","productDescription":"536 p.","costCenters":[{"id":532,"text":"Pennsylvania Water Science Center","active":true,"usgs":true}],"links":[{"id":177386,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/wdr/2002/pa-02-2/coverthb.jpg"},{"id":4988,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.usgs.gov/wdr/2002/pa-02-2/wdr-susq2002-2.html","linkFileType":{"id":5,"text":"html"},"description":"WDR PA-02-2"}],"contact":"<p><a href=\"mailto:dc_pa@usgs.gov\" data-mce-href=\"mailto:dc_pa@usgs.gov\">Director</a>, <a href=\"https://pa.water.usgs.gov\" data-mce-href=\"https://pa.water.usgs.gov\">Pennsylvania Water Science Center</a><br> U.S. Geological Survey <br> 215 Limekiln Road <br> New Cumberland, PA 17070</p>","tableOfContents":"<ul><li>Preface</li><li>List of surface-water stations, in downstream order, for which records are published in this volume</li><li>List of ground-water wells, by county, for which records are published in this volume</li><li>List of discontinued continuous-record surface-water discharge stations</li><li>List of discontinued continuous-record surface-water-quality stations</li><li>Pennsylvania District office locations and addresses</li><li>Introduction</li><li>Cooperation</li><li>Summary of hydrologic conditions</li><li>Special networks and programs</li><li>Explanation of the records</li><li>Access to USGS Water Data</li><li>Definition of terms</li><li>Techniques of Water-Resources Investigations of the U.S. Geological Survey</li><li>Special Notes, Remark Codes, and Selected Constituent Definitions</li><li>Station records, surface water</li><li>Special Notes, Remark Codes, and Selected Constituent Definitions</li><li>Station records, ground water</li><li>Index</li></ul>","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4a09e4b07f02db5fac2a","contributors":{"authors":[{"text":"Durlin, Randall R.","contributorId":64719,"corporation":false,"usgs":true,"family":"Durlin","given":"Randall","email":"","middleInitial":"R.","affiliations":[],"preferred":false,"id":247179,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Schaffstall, William P.","contributorId":29054,"corporation":false,"usgs":true,"family":"Schaffstall","given":"William","email":"","middleInitial":"P.","affiliations":[],"preferred":false,"id":247178,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":47785,"text":"wri034026 - 2003 - Concentrations and loads of suspended sediment and nutrients in surface water of the Yakima River basin, Washington, 1999-2000 [electronic resource] : with an analysis of trends in concentrations","interactions":[],"lastModifiedDate":"2012-02-02T00:10:43","indexId":"wri034026","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":342,"text":"Water-Resources Investigations Report","code":"WRI","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"2003-4026","title":"Concentrations and loads of suspended sediment and nutrients in surface water of the Yakima River basin, Washington, 1999-2000 [electronic resource] : with an analysis of trends in concentrations","docAbstract":"Spatial and temporal variations in concentrations and loads of suspended sediment and nutrients in surface water of the Yakima River Basin were assessed using data collected during 1999?2000 as part of the U.S. Geological Survey (USGS) National Water-Quality Assessment (NAWQA) Program. Samples were collected at 34 sites located throughout the Basin in August 1999 using a Lagrangian sampling design, and also were collected weekly and monthly from May 1999 through January 2000 at three of the sites. Nutrient and sediment data collected at various time intervals from 1973 through 2001 by the USGS, Bureau of Reclamation, Washington State Department of Ecology, and Roza-Sunnyside Board of Joint Control were used to assess trends in concentrations.\r\n\r\nDuring irrigation season (mid-March to mid-October), concentrations of suspended sediment and nutrients in the Yakima River increase as relatively pristine water from the forested headwaters moves downstream and mixes with discharges from streams, agricultural drains, and wastewater treatment plants. Concentrations of nutrients also depend partly on the proportions of mixing between river water and discharges: in years of ample water supply in headwater reservoirs, more water is released during irrigation season and there is more dilution of nutrients discharged to the river downstream. For example, streamflow from river mile (RM) 103.7 to RM 72 in August 1999 exceeded streamflow in July 1988 by a factor of almost 2.5, but loads of total nitrogen and phosphorus discharged to the reach from streams, drains, and wastewater treatment plants were only 1.2 and 1.1 times larger.\r\n\r\nIn years of ample water supply, canal water, which is diverted from either the Yakima or Naches River, makes up more of the flow in drains and streams carrying agricultural return flows. The canal water dilutes nutrients (especially nitrate) transported to the drains and streams in runoff from fields and in discharges from subsurface field drains and the shallow ground-water system. The average concentration of total nitrogen in drains and streams discharging to the Yakima River from RM 103.7 to RM 72 in August 1999 was 2.63 mg/L, and in July 1988 was 3.16 mg/L; average concentrations of total phosphorus were 0.20 and 0.26 mg/L.\r\n\r\nAfter irrigation season, streamflow in agricultural drains decreases because irrigation water is no longer diverted from the Yakima and Naches Rivers. As a result, concentrations of total nitrogen in drains increase because nitrate, which constitutes much of total nitrogen, continues to enter the drains from subsurface drains and shallow ground water. Concentrations of total phosphorus and suspended sediment often decrease, because they are transported to the drains in runoff of irrigation water from fields. In Granger Drain, concentrations of total nitrogen ranged from 2-4 mg/L during irrigation season and increased to about 6 mg/L after irrigation season, and concentrations of total phosphorus, as high as 1 mg/L, decreased to about 0.2 mg/L.\r\n\r\nIn calendar year 1999, Moxee Drain transported an average of 28,000 lb/d (pounds per day) of suspended sediment, 380 lb/d of total nitrogen, and 46 lb/d of total phosphorus to the Yakima River. These loads were about half the average loads transported by Granger Drain during the same period. Average streamflows were similar for the two drains, so the difference in loads was due to differences in constituent concentrations: those in Moxee Drain were about 40-60 percent less than those in Granger Drain.\r\n\r\nLoads of suspended sediment and total phosphorus in Moxee and Granger Drains were nearly four times higher during irrigation season than during the non-irrigation season because with increased flow during irrigation season, concentrations of suspended sediment and total phosphorus are usually higher. Loads of nitrate in the drains were about the same in both seasons because nitrate concentrations are higher during the non-irrigation season. \r\n\r","language":"ENGLISH","doi":"10.3133/wri034026","usgsCitation":"Ebbert, J.C., Embrey, S.S., and Kelley, J.A., 2003, Concentrations and loads of suspended sediment and nutrients in surface water of the Yakima River basin, Washington, 1999-2000 [electronic resource] : with an analysis of trends in concentrations: U.S. Geological Survey Water-Resources Investigations Report 2003-4026, 111 p., https://doi.org/10.3133/wri034026.","productDescription":"111 p.","costCenters":[],"links":[{"id":170849,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"},{"id":3997,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.water.usgs.gov/wri034026/","linkFileType":{"id":5,"text":"html"}}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4b17e4b07f02db6a5d8f","contributors":{"authors":[{"text":"Ebbert, James C.","contributorId":73990,"corporation":false,"usgs":true,"family":"Ebbert","given":"James","email":"","middleInitial":"C.","affiliations":[],"preferred":false,"id":236235,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Embrey, Sandra S.","contributorId":48170,"corporation":false,"usgs":true,"family":"Embrey","given":"Sandra","email":"","middleInitial":"S.","affiliations":[],"preferred":false,"id":236233,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Kelley, Janet A.","contributorId":57926,"corporation":false,"usgs":true,"family":"Kelley","given":"Janet","email":"","middleInitial":"A.","affiliations":[],"preferred":false,"id":236234,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
,{"id":53284,"text":"wdrPA021 - 2003 - Water Resources Data, Pennsylvania, Water Year 2002, Volume 1. Delaware River Basin","interactions":[],"lastModifiedDate":"2018-05-29T12:57:11","indexId":"wdrPA021","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":340,"text":"Water Data Report","code":"WDR","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"PA-02-1","title":"Water Resources Data, Pennsylvania, Water Year 2002, Volume 1. Delaware River Basin","docAbstract":"Water-resources data for the 2002 water year for Pennsylvania consists of records of discharge and water quality of streams; contents and elevations of lakes and reservoirs; and water levels and water quality of ground-water wells. This report, Volume 1 contains (1) discharge records for 80 continuous-record streamflow-gaging stations, 8 partial-record stations, 19 special study and miscellaneous streamflow sites, and 39 low-flow miscellaneous streamflow sites; (2) elevation and contents records for 13 lake and reservoirs; (3) water-quality records for 38 gaging stations and 14 ungaged streamsites; (4) water-quality records for 47 special-study station; (5) water-level records for 63 network observation wells; (6) water-quality analyses of ground water from 55 ground-water wells. Site locations are shown in figures throughout the report. Additional water data collected at various sites not involved in the systematic data-collection program are also presented. These data together with the data in Volumes 2 and 3, represent that part of the National Water Data System operated by the U.S. Geological Survey and cooperating State, local, and Federal agencies in Pennsylvania.","language":"English","publisher":"U.S. Geological Survey","publisherLocation":"Reston, VA","doi":"10.3133/wdrPA021","collaboration":"Prepared in cooperation with the Pennsylvania Department of Environmental Protection, the Philadelphia District of the U.S. Army Corps of Engineers, the Chester County Water Resources Authority, and with other State, municipal, and Federal agencies","usgsCitation":"Durlin, R.R., and Schaffstall, W.P., 2003, Water Resources Data, Pennsylvania, Water Year 2002, Volume 1. Delaware River Basin: U.S. Geological Survey Water Data Report PA-02-1, 527 p., https://doi.org/10.3133/wdrPA021.","productDescription":"527 p.","costCenters":[{"id":532,"text":"Pennsylvania Water Science Center","active":true,"usgs":true}],"links":[{"id":4987,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.usgs.gov/wdr/2002/pa-02-1/wdr-del-2002-1.html","linkFileType":{"id":5,"text":"html"}},{"id":177300,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/wdr/2002/pa-02-1/coverthb.jpg"}],"contact":"<p><a href=\"mailto:dc_pa@usgs.gov\" data-mce-href=\"mailto:dc_pa@usgs.gov\">Director</a>, <a href=\"https://pa.water.usgs.gov/\" data-mce-href=\"https://pa.water.usgs.gov/\">Pennsylvania Water Science Center</a><br> U.S. Geological Survey <br> 215 Limekiln Road <br> New Cumberland, PA 17070</p>","tableOfContents":"<ul><li>Preface</li><li>List of surface-water stations, in downstream order, for which records are published in this volume</li><li>List of ground-water wells, by county, for which records are published in this volume</li><li>List of discontinued continuous-record surface-water discharge stations</li><li>List of discontinued continuous-record surface-water-quality stations</li><li>Pennsylvania District office locations and addresses</li><li>Introduction</li><li>Cooperation</li><li>Summary of hydrologic conditions</li><li>Special networks and programs</li><li>Explanation of the record</li><li>Access to USGS Water Data</li><li>Definition of terms</li><li>Techniques of Waer-Resources Investigations of the U.S. Geological Survey</li><li>Special Notes, Remark Codes, and Selected Constituent Definition</li><li>Station records, surface water</li><li>Special Notes, Remark Codes, and Selected Constituent Definitions</li><li>Station records, ground water</li><li>Index</li></ul>","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4a09e4b07f02db5fac28","contributors":{"authors":[{"text":"Durlin, Randall R.","contributorId":64719,"corporation":false,"usgs":true,"family":"Durlin","given":"Randall","email":"","middleInitial":"R.","affiliations":[],"preferred":false,"id":247177,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Schaffstall, William P.","contributorId":29054,"corporation":false,"usgs":true,"family":"Schaffstall","given":"William","email":"","middleInitial":"P.","affiliations":[],"preferred":false,"id":247176,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":51327,"text":"ofr2003331 - 2003 - Rainfall, Streamflow, and Water-Quality Data During Stormwater Monitoring, Halawa Stream Drainage Basin, Oahu, Hawaii, July 1, 2002 to June 30, 2003","interactions":[],"lastModifiedDate":"2012-03-08T17:16:16","indexId":"ofr2003331","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":330,"text":"Open-File Report","code":"OFR","onlineIssn":"2331-1258","printIssn":"0196-1497","active":true,"publicationSubtype":{"id":5}},"seriesNumber":"2003-331","title":"Rainfall, Streamflow, and Water-Quality Data During Stormwater Monitoring, Halawa Stream Drainage Basin, Oahu, Hawaii, July 1, 2002 to June 30, 2003","docAbstract":"Storm runoff water-quality samples were collected as part of the State of Hawaii Department of Transportation Stormwater Monitoring Program. This program is designed to assess the effects of highway runoff and urban runoff on Halawa Stream. For this program, rainfall data was collected at two sites, continuous streamflow data at three sites, and water-quality data at five sites, which include the three streamflow sites. This report summarizes rainfall, streamflow, and water-quality data collected between July 1, 2002 to June 30, 2003. \r\n\r\n \r\n\r\nA total of 28 samples were collected over five storms during July 1, 2002 to June 30, 2003. For two of the five storms, five grab samples and three flow-weighted timecomposite samples were collected. Grab samples were collected nearly simultaneously at all five sites, and flow-weighted timecomposite samples were collected at the three sites equipped with automatic samplers. The other three storms were partially sampled, where only flow-weighted time-composite samples were collected and/or not all stations were sampled. Samples were analyzed for total suspended solids, total dissolved solids, nutrients, chemical oxygen demand, and selected trace metals (cadmium, copper, lead, and zinc). Grab samples were additionally analyzed for oil and grease, total petroleum hydrocarbons, fecal coliform, and biological oxygen demand. Quality-assurance/qualitycontrol samples, collected during storms and during routine maintenance, were also collected to verify analytical procedures and insure proper cleaning of equipment.","language":"ENGLISH","publisher":"Geological Survey (U.S.)","doi":"10.3133/ofr2003331","collaboration":"Prepared in cooperation with the State of Hawaii Department of Transportation","usgsCitation":"Young, S.T., and Ball, M.T., 2003, Rainfall, Streamflow, and Water-Quality Data During Stormwater Monitoring, Halawa Stream Drainage Basin, Oahu, Hawaii, July 1, 2002 to June 30, 2003: U.S. Geological Survey Open-File Report 2003-331, v, 30 p., https://doi.org/10.3133/ofr2003331.","productDescription":"v, 30 p.","additionalOnlineFiles":"Y","temporalStart":"2002-07-01","temporalEnd":"2003-06-30","costCenters":[{"id":525,"text":"Pacific Islands Water Science Center","active":true,"usgs":true}],"links":[{"id":176238,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"},{"id":4658,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.usgs.gov/of/2003/ofr03-331/","linkFileType":{"id":5,"text":"html"}}],"geographicExtents":"{ \"type\": \"FeatureCollection\", \"features\": [ { \"type\": \"Feature\", \"properties\": {}, \"geometry\": { \"type\": \"Polygon\", \"coordinates\": [ [ [ -157.96666666666667,21.333333333333332 ], [ -157.96666666666667,21.466666666666665 ], [ -157.8,21.466666666666665 ], [ -157.8,21.333333333333332 ], [ -157.96666666666667,21.333333333333332 ] ] ] } } ] }","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4a80e4b07f02db6496ec","contributors":{"authors":[{"text":"Young, Stacie T. M.","contributorId":63432,"corporation":false,"usgs":true,"family":"Young","given":"Stacie","email":"","middleInitial":"T. M.","affiliations":[],"preferred":false,"id":243332,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Ball, Marcael T.J.","contributorId":16904,"corporation":false,"usgs":true,"family":"Ball","given":"Marcael","email":"","middleInitial":"T.J.","affiliations":[],"preferred":false,"id":243331,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":50432,"text":"ofr01328 - 2003 - User's Manual for the New England Water-Use Data System (NEWUDS)","interactions":[],"lastModifiedDate":"2012-02-02T00:11:19","indexId":"ofr01328","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":330,"text":"Open-File Report","code":"OFR","onlineIssn":"2331-1258","printIssn":"0196-1497","active":true,"publicationSubtype":{"id":5}},"seriesNumber":"2001-328","title":"User's Manual for the New England Water-Use Data System (NEWUDS)","docAbstract":"Water is used in a variety of ways that need to be understood for effective management of water resources. Water-use activities need to be categorized and included in a database management system to understand current water uses and to provide information to water-resource management policy decisionmakers.\r\n\r\nThe New England Water-Use Data System (NEWUDS) is a complex database developed to store water-use information that allows water to be tracked from a point of water-use activity (called a 'Site'), such as withdrawal from a resource (reservoir or aquifer), to a second Site, such as distribution to a user (business or irrigator). NEWUDS conceptual model consists of 10 core entities: system, owner, address, location, site, data source, resource, conveyance, transaction/rate, and alias, with tables available to store user-defined details. Three components--site (with both a From Site and a To Site), a conveyance that connects them, and a transaction/rate associated with the movement of water over a specific time interval form the core of the basic NEWUDS network model. \r\n\r\nThe most important step in correctly translating real-world water-use activities into a storable format in NEWUDS depends on choosing the appropriate sites and linking them correctly in a network to model the flow of water from the initial From Site to the final To Site. Ten water-use networks representing real-world activities are described--three withdrawal networks, three return networks, two user networks, two complex community-system networks. Ten case studies of water use, one for each network, also are included in this manual to illustrate how to compile, store, and retrieve the appropriate data.\r\n\r\nThe sequence of data entry into tables is critical because there are many foreign keys. The recommended core entity sequence is (1) system, (2) owner, (3) address, (4) location, (5) site, (6) data source, (7) resource, (8) conveyance, (9) transaction, and (10) rate; with (11) alias and (12) user-defined detail subject areas populated as needed. After each step in data entry, quality-assurance queries should be run to ensure the data are correctly entered so that it can be retrieved accurately. The point of data storage is retrieval. Several retrieval queries that focus on retrieving only relevant data to specific questions are presented in this manual as examples for the NEWUDS user.","language":"ENGLISH","doi":"10.3133/ofr01328","usgsCitation":"Horn, M.A., 2003, User's Manual for the New England Water-Use Data System (NEWUDS): U.S. Geological Survey Open-File Report 2001-328, 392 p., https://doi.org/10.3133/ofr01328.","productDescription":"392 p.","costCenters":[],"links":[{"id":175626,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"},{"id":4241,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.usgs.gov/of/2001/ofr01-328/","linkFileType":{"id":5,"text":"html"}}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4a17e4b07f02db603fc7","contributors":{"authors":[{"text":"Horn, Marilee A. mhorn@usgs.gov","contributorId":2792,"corporation":false,"usgs":true,"family":"Horn","given":"Marilee","email":"mhorn@usgs.gov","middleInitial":"A.","affiliations":[{"id":405,"text":"NH/VT office of New England Water Science Center","active":true,"usgs":true}],"preferred":true,"id":241447,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":53433,"text":"wri024258 - 2003 - Simulations of Flooding on Pea River and Whitewater Creek in the Vicinity of the Proposed Elba Bypass at Elba, Alabama","interactions":[],"lastModifiedDate":"2012-02-02T00:11:58","indexId":"wri024258","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":342,"text":"Water-Resources Investigations Report","code":"WRI","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"2002-4258","title":"Simulations of Flooding on Pea River and Whitewater Creek in the Vicinity of the Proposed Elba Bypass at Elba, Alabama","docAbstract":"A two-dimensional finite-element surface-water model was used to study the effects of proposed modifications to the State Highway 203 corridor (proposed Elba Bypass/relocated U.S. Highway 84) on water-surface elevations and flow distributions during flooding in the Pea River and Whitewater Creek Basins at Elba, Coffee County, Alabama. Flooding was first simulated for the March 17, 1990, flood, using the 1990 flood-plain conditions to calibrate the model to match measured data collected by the U.S. Geological Survey and the U.S. Army Corps of Engineers after the flood. After model calibration, the effects of flooding were simulated for four scenarios: (1) floods having the 50- and 100-year recurrence intervals for the existing flood-plain, bridge, highway, and levee conditions; (2) floods having the 50- and 100-year recurrence intervals for the existing flood-plain and levee conditions with the State Highway 203 embankment and bridge removed; (3) floods having the 50- and 100-year recurrence intervals for the existing flood-plain, bridge, and highway conditions with proposed modifications (elevating) to the levee; and (4) floods having the 50- and 100-year recurrence intervals for the proposed conditions reflecting the Elba Bypass and modified levee.\r\nThe simulation of floodflow for the Pea River and Whitewater Creek flood of March 17, 1990, in the study reach compared closely to flood profile data obtained after the flood. The flood of March 17, 1990, had an estimated peak discharge of 58,000 cubic feet per second at the gage (just below the confluence) and was estimated to be between a 50-year and 100-year flood event. The estimated peak discharge for Pea River and Whitewater Creek was 40,000 and 42,000 cubic feet per second, respectively.\r\nSimulation of floodflows for the 50-year flood (51,400 cubic feet per second) at the gage for existing flood-plain, bridge, highway, and levee conditions indicated that about 31 percent of the peak flow was conveyed by the State Highway 203 bridge over Whitewater Creek, approximately 12 percent overtopped the State Highway 203 embankment, and about 57 percent was conveyed by the Pea River flood plain east of State Highway 125. For this simulation, flow from Pea River (2,380 cubic feet per second) overtopped State Highway 125 and crossed over into the Whitewater Creek flood plain north of State Highway 203, creating one common flood plain. The water-surface elevation estimated at the downstream side of the State Highway 203 bridge crossing Whitewater Creek was 202.82 feet. The girders for both the State Highway 203 and U.S. Highway 84 bridges were partially submerged, but U.S. Highway 84 was not overtopped.\r\nFor the 100-year flood (63,500 cubic feet per second) at the gage, the simulation indicated that about 25 percent of the peak flow was conveyed by the State Highway 203 bridge over Whitewater Creek, approximately 24 percent overtopped the State Highway 203 embankment, and about 51 percent was conveyed by the Pea River flood plain east of State Highway 125. The existing levee adjacent to Whitewater Creek was overtopped by a flow of 3,200 cubic feet per second during the 100-year flood. For this simulation, flow from Pea River (6,710 cubic feet per second) overtopped State Highway 125 and crossed over into the Whitewater Creek flood plain north of State Highway 203. The water-surface elevation estimated at the downstream side of the State Highway 203 bridge crossing Whitewater Creek was 205.60 feet. The girders for both the State Highway 203 and U.S. Highway 84 bridges were partially submerged, and the west end of the U.S. Highway 84 bridge was overtopped.\r\nSimulation of floodflows for the 50-year flood at the gage for existing flood-plain and levee conditions, but with the State Highway 203 embankment and bridge removed, yielded a lower water-surface elevation (202.90 feet) upstream of this bridge than that computed for the existing conditions. For the 100-year flood, the simulation indi","language":"ENGLISH","doi":"10.3133/wri024258","usgsCitation":"Hedgecock, T.S., 2003, Simulations of Flooding on Pea River and Whitewater Creek in the Vicinity of the Proposed Elba Bypass at Elba, Alabama: U.S. Geological Survey Water-Resources Investigations Report 2002-4258, 35 p., https://doi.org/10.3133/wri024258.","productDescription":"35 p.","costCenters":[],"links":[{"id":100364,"rank":300,"type":{"id":11,"text":"Document"},"url":"https://pubs.usgs.gov/wri/2002/4258/report.pdf","size":"11964","linkFileType":{"id":1,"text":"pdf"}},{"id":180807,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/wri/2002/4258/report-thumb.jpg"}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e48d3e4b07f02db548e12","contributors":{"authors":[{"text":"Hedgecock, T. Scott","contributorId":20783,"corporation":false,"usgs":true,"family":"Hedgecock","given":"T.","email":"","middleInitial":"Scott","affiliations":[],"preferred":false,"id":247577,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":53267,"text":"ofr03315 - 2003 - Database of historically documented springs and spring flow measurements in Texas","interactions":[],"lastModifiedDate":"2017-05-23T15:13:22","indexId":"ofr03315","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":330,"text":"Open-File Report","code":"OFR","onlineIssn":"2331-1258","printIssn":"0196-1497","active":true,"publicationSubtype":{"id":5}},"seriesNumber":"2003-315","title":"Database of historically documented springs and spring flow measurements in Texas","docAbstract":"Springs are naturally occurring features that convey excess ground water to the land surface; they represent a transition from ground water to surface water. Water issues\r\nthrough one opening, multiple openings, or numerous seeps in the rock or soil.\r\n\r\nThe database of this report provides information about springs and spring flow in Texas including spring names, identification numbers, location, and, if available, water\r\nsource and use. This database does not include every spring in Texas, but is limited to an aggregation of selected digital and hard-copy data of the U.S. Geological Survey\r\n(USGS), the Texas Water Development Board (TWDB), and Capitol Environmental Services.","language":"English","publisher":"U.S. Geological Survey","doi":"10.3133/ofr03315","usgsCitation":"Heitmuller, F.T., and Reece, B.D., 2003, Database of historically documented springs and spring flow measurements in Texas: U.S. Geological Survey Open-File Report 2003-315, Report: 4 p.; Database, https://doi.org/10.3133/ofr03315.","productDescription":"Report: 4 p.; Database","costCenters":[{"id":583,"text":"Texas Water Science Center","active":true,"usgs":true}],"links":[{"id":177926,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"},{"id":4975,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.water.usgs.gov/ofr03-315/","linkFileType":{"id":5,"text":"html"}}],"country":"United States","state":"Texas","geographicExtents":"{\"type\":\"FeatureCollection\",\"features\":[{\"type\":\"Feature\",\"geometry\":{\"type\":\"MultiPolygon\",\"coordinates\":[[[[-97.240849,26.411504],[-97.276425,26.521729],[-97.31073,26.556558],[-97.345822,26.700589],[-97.370438,26.723896],[-97.368343,26.795649],[-97.387459,26.820789],[-97.390078,27.156512],[-97.359963,27.304732],[-97.361796,27.359988],[-97.317277,27.46369],[-97.236882,27.598293],[-97.231383,27.632336],[-97.214099,27.631551],[-97.200743,27.650144],[-97.203474,27.684533],[-97.103326,27.789068],[-97.098874,27.82285],[-97.134489,27.825206],[-97.056713,27.842294],[-96.985745,27.954048],[-96.967807,28.020041],[-96.952618,28.01644],[-96.906004,28.076147],[-96.886233,28.084396],[-96.879424,28.131402],[-96.84538,28.108881],[-96.83003,28.111842],[-96.81042,28.126034],[-96.816443,28.174808],[-96.791958,28.188687],[-96.703838,28.198246],[-96.702659,28.211208],[-96.662462,28.227314],[-96.651856,28.251275],[-96.592934,28.296972],[-96.450998,28.337039],[-96.403206,28.371475],[-96.397846,28.343513],[-96.4137,28.327343],[-96.547774,28.270798],[-96.694666,28.18212],[-96.849624,28.064939],[-96.966996,27.950531],[-97.166682,27.676583],[-97.30447,27.407734],[-97.350398,27.268105],[-97.370941,27.161166],[-97.37913,27.047996],[-97.370731,26.909706],[-97.333028,26.736479],[-97.194644,26.306513],[-97.154271,26.066841],[-97.169842,26.077853],[-97.194458,26.27164],[-97.240849,26.411504]]],[[[-94.886539,29.510724],[-94.894747,29.52697],[-94.87675,29.507922],[-94.886539,29.510724]]],[[[-97.868235,26.056656],[-97.88653,26.066339],[-97.967358,26.051718],[-97.981335,26.067182],[-98.028759,26.06647],[-98.039239,26.041275],[-98.070021,26.047992],[-98.084755,26.070808],[-98.091038,26.059169],[-98.105505,26.067537],[-98.146622,26.049412],[-98.177897,26.074672],[-98.197046,26.056153],[-98.220673,26.076467],[-98.248806,26.073101],[-98.264514,26.085507],[-98.277218,26.098802],[-98.265698,26.12037],[-98.296195,26.120321],[-98.302979,26.11005],[-98.323828,26.121249],[-98.336837,26.166432],[-98.354645,26.15304],[-98.386694,26.157872],[-98.404433,26.182564],[-98.442536,26.199151],[-98.450976,26.219904],[-98.496684,26.212853],[-98.543852,26.234492],[-98.576188,26.235221],[-98.599154,26.257612],[-98.669397,26.23632],[-98.681167,26.26271],[-98.745272,26.303096],[-98.755242,26.3251],[-98.789822,26.331575],[-98.807348,26.369421],[-98.890965,26.357569],[-98.921277,26.381426],[-98.950186,26.380303],[-98.967587,26.398266],[-99.008003,26.395459],[-99.032316,26.412082],[-99.082002,26.39651],[-99.110855,26.426278],[-99.091635,26.476977],[-99.127782,26.525199],[-99.166742,26.536079],[-99.178064,26.620547],[-99.209948,26.693938],[-99.208907,26.724761],[-99.240023,26.745851],[-99.242444,26.788262],[-99.268613,26.843213],[-99.295146,26.86544],[-99.316753,26.865831],[-99.3289,26.879761],[-99.324684,26.915973],[-99.379149,26.93449],[-99.393748,26.96073],[-99.377312,26.973819],[-99.415476,27.01724],[-99.42938,27.010833],[-99.446524,27.023008],[-99.452316,27.062669],[-99.429209,27.090982],[-99.442123,27.106839],[-99.426348,27.176262],[-99.441549,27.24992],[-99.463309,27.268437],[-99.492407,27.264118],[-99.494604,27.303542],[-99.536443,27.312538],[-99.504837,27.338289],[-99.487521,27.412396],[-99.495104,27.451518],[-99.480419,27.481596],[-99.497519,27.500496],[-99.52582,27.496696],[-99.515978,27.572131],[-99.55495,27.614454],[-99.580006,27.602251],[-99.578099,27.619196],[-99.594038,27.638573],[-99.638929,27.626758],[-99.665948,27.635968],[-99.668942,27.659974],[-99.711511,27.658365],[-99.77074,27.732134],[-99.796342,27.735586],[-99.813086,27.773952],[-99.835127,27.762881],[-99.850877,27.793974],[-99.877677,27.799427],[-99.876003,27.837968],[-99.904385,27.875284],[-99.895828,27.904178],[-99.937142,27.940537],[-99.931812,27.980967],[-99.991447,27.99456],[-100.017914,28.064787],[-100.053123,28.08473],[-100.083393,28.144035],[-100.208059,28.190383],[-100.22363,28.235224],[-100.2462,28.234092],[-100.289384,28.273491],[-100.286471,28.312296],[-100.341869,28.384953],[-100.349586,28.402604],[-100.337797,28.44296],[-100.368288,28.477196],[-100.333814,28.499252],[-100.38886,28.515748],[-100.411414,28.551899],[-100.398385,28.584884],[-100.44732,28.609325],[-100.445529,28.637144],[-100.495863,28.658569],[-100.510055,28.690723],[-100.507613,28.740599],[-100.533017,28.76328],[-100.53583,28.805888],[-100.547324,28.825817],[-100.57051,28.826317],[-100.602054,28.901944],[-100.640568,28.914212],[-100.651512,28.943432],[-100.645894,28.986421],[-100.674656,29.099777],[-100.772649,29.168492],[-100.767059,29.195287],[-100.785521,29.228137],[-100.795681,29.22773],[-100.797671,29.246943],[-100.876049,29.279585],[-100.886842,29.307848],[-100.948972,29.347246],[-101.004207,29.364772],[-101.060151,29.458661],[-101.151877,29.477005],[-101.173821,29.514566],[-101.254895,29.520342],[-101.242023,29.592512],[-101.259127,29.607284],[-101.307332,29.587847],[-101.311219,29.648491],[-101.361756,29.657821],[-101.415402,29.756561],[-101.441059,29.753451],[-101.475269,29.780663],[-101.522695,29.759671],[-101.546797,29.796991],[-101.582562,29.771334],[-101.625958,29.771063],[-101.646418,29.754304],[-101.662453,29.77128],[-101.706636,29.762737],[-101.852604,29.801895],[-101.922585,29.790161],[-101.974548,29.810276],[-101.987539,29.801057],[-102.034759,29.804028],[-102.050044,29.78507],[-102.115682,29.79239],[-102.159601,29.814356],[-102.181894,29.846034],[-102.227553,29.843534],[-102.315389,29.87992],[-102.364542,29.845387],[-102.386678,29.76688],[-102.508313,29.783219],[-102.513381,29.76576],[-102.539417,29.751629],[-102.559343,29.760377],[-102.630151,29.734315],[-102.670971,29.741954],[-102.698347,29.695591],[-102.693466,29.676507],[-102.742031,29.632142],[-102.739991,29.599041],[-102.768341,29.594734],[-102.771429,29.548546],[-102.808692,29.522319],[-102.807327,29.494009],[-102.832539,29.433109],[-102.824564,29.399558],[-102.843021,29.357988],[-102.879534,29.353327],[-102.888328,29.291947],[-102.906296,29.260011],[-102.871347,29.241625],[-102.866846,29.225015],[-102.890064,29.208814],[-102.915866,29.215878],[-102.917805,29.190697],[-102.944911,29.18882],[-102.953475,29.176308],[-102.989432,29.183174],[-103.015028,29.12577],[-103.035683,29.103029],[-103.074407,29.088534],[-103.100266,29.0577],[-103.113922,28.988547],[-103.156646,28.972831],[-103.227801,28.991532],[-103.239109,28.981651],[-103.260308,28.989731],[-103.28119,28.982138],[-103.341463,29.041224],[-103.355428,29.021529],[-103.427754,29.042334],[-103.471265,29.073115],[-103.503236,29.11911],[-103.524613,29.120998],[-103.523384,29.133389],[-103.558679,29.154962],[-103.645635,29.159286],[-103.71377,29.185008],[-103.816642,29.270927],[-103.975235,29.296017],[-104.038282,29.320156],[-104.106467,29.373127],[-104.166563,29.399352],[-104.233487,29.492734],[-104.318074,29.527938],[-104.334811,29.519463],[-104.381041,29.543406],[-104.399591,29.572319],[-104.507568,29.639624],[-104.539761,29.676074],[-104.565688,29.770462],[-104.679772,29.924659],[-104.679661,29.975272],[-104.706874,30.050685],[-104.685003,30.085643],[-104.695366,30.13213],[-104.687296,30.179464],[-104.713166,30.237957],[-104.733822,30.261221],[-104.749664,30.26126],[-104.761634,30.301148],[-104.809794,30.334926],[-104.824314,30.370466],[-104.859521,30.390413],[-104.85242,30.418792],[-104.876787,30.511004],[-104.924796,30.604832],[-104.967167,30.608107],[-105.002057,30.680972],[-105.062334,30.686303],[-105.113816,30.746001],[-105.152362,30.751452],[-105.195144,30.792138],[-105.255416,30.797029],[-105.287238,30.822206],[-105.314863,30.816961],[-105.360672,30.847384],[-105.394242,30.852979],[-105.399609,30.888941],[-105.533088,30.984859],[-105.55743,30.990229],[-105.60333,31.082625],[-105.64189,31.098322],[-105.646731,31.113908],[-105.709491,31.136375],[-105.742678,31.164897],[-105.773257,31.166897],[-105.779725,31.191283],[-105.869353,31.288634],[-105.938452,31.318735],[-105.953943,31.364749],[-106.004926,31.392458],[-106.080258,31.398702],[-106.203969,31.465378],[-106.246203,31.541153],[-106.280811,31.562062],[-106.303536,31.620413],[-106.378039,31.72831],[-106.451541,31.764808],[-106.484642,31.747809],[-106.542097,31.802146],[-106.602727,31.825024],[-106.605845,31.846305],[-106.635926,31.866235],[-106.629197,31.883717],[-106.645296,31.894859],[-106.614346,31.918003],[-106.623933,31.925335],[-106.614702,31.956],[-106.622819,31.952891],[-106.618745,31.966955],[-106.638186,31.97682],[-106.618486,32.000495],[-103.064423,32.000518],[-103.064625,32.999899],[-103.043531,34.018014],[-103.041924,36.500439],[-100.003762,36.499699],[-100.000381,34.560509],[-99.929334,34.576714],[-99.825325,34.497596],[-99.754248,34.421289],[-99.696462,34.381036],[-99.665992,34.374185],[-99.600026,34.374688],[-99.569696,34.418418],[-99.499875,34.409608],[-99.430995,34.373414],[-99.399603,34.375079],[-99.394956,34.442099],[-99.381011,34.456936],[-99.358795,34.455863],[-99.318363,34.408296],[-99.289922,34.414731],[-99.264167,34.405149],[-99.25898,34.391243],[-99.273958,34.38756],[-99.242945,34.372668],[-99.233274,34.344101],[-99.210716,34.336304],[-99.211648,34.292232],[-99.19457,34.272424],[-99.189511,34.214312],[-99.159016,34.20888],[-99.130609,34.219408],[-99.126567,34.203004],[-99.079535,34.211518],[-99.048792,34.198209],[-99.013075,34.203222],[-98.990852,34.221633],[-98.974132,34.203566],[-98.952513,34.21265],[-98.909349,34.177499],[-98.872922,34.166584],[-98.868116,34.149635],[-98.8579,34.159627],[-98.812954,34.158444],[-98.749291,34.124238],[-98.735471,34.135208],[-98.696518,34.133521],[-98.648073,34.164441],[-98.603978,34.160249],[-98.577136,34.148962],[-98.486328,34.062598],[-98.414426,34.085074],[-98.384381,34.146317],[-98.367494,34.156191],[-98.16912,34.114171],[-98.114506,34.154727],[-98.09066,34.12198],[-98.120208,34.072127],[-98.099096,34.048639],[-98.104022,34.036233],[-98.088203,34.005481],[-98.027672,33.993357],[-97.978243,34.005387],[-97.947572,33.991053],[-97.974173,33.942832],[-97.955511,33.938186],[-97.957155,33.914454],[-97.983552,33.904002],[-97.967777,33.88243],[-97.877387,33.850236],[-97.834333,33.857671],[-97.784657,33.890632],[-97.783717,33.91056],[-97.76377,33.914241],[-97.762768,33.934396],[-97.725289,33.941045],[-97.69311,33.983699],[-97.671772,33.99137],[-97.589598,33.953554],[-97.589254,33.903922],[-97.551541,33.897947],[-97.50096,33.919643],[-97.460376,33.903948],[-97.451469,33.87093],[-97.462857,33.841772],[-97.426493,33.819398],[-97.365507,33.823763],[-97.33294,33.87444],[-97.315913,33.865838],[-97.299245,33.880175],[-97.256625,33.863286],[-97.24618,33.900344],[-97.210921,33.916064],[-97.179609,33.89225],[-97.166629,33.847311],[-97.203514,33.821825],[-97.205431,33.801488],[-97.172192,33.737545],[-97.126102,33.716941],[-97.086195,33.743933],[-97.087999,33.808747],[-97.058623,33.818752],[-97.052209,33.841737],[-97.023899,33.844213],[-96.985567,33.886522],[-96.996183,33.941728],[-96.979415,33.956178],[-96.973807,33.935697],[-96.9163,33.957798],[-96.875281,33.860505],[-96.85609,33.84749],[-96.837413,33.871349],[-96.794276,33.868886],[-96.761588,33.824406],[-96.704457,33.835021],[-96.667187,33.91694],[-96.630117,33.895422],[-96.592948,33.895616],[-96.590112,33.880665],[-96.625399,33.856542],[-96.623155,33.841483],[-96.572937,33.819098],[-96.523863,33.818114],[-96.502286,33.77346],[-96.422643,33.776041],[-96.348306,33.686379],[-96.309964,33.710489],[-96.294867,33.764771],[-96.277269,33.769735],[-96.220521,33.74739],[-96.178059,33.760518],[-96.162757,33.788769],[-96.178964,33.810553],[-96.150765,33.816987],[-96.15163,33.831946],[-96.138905,33.839159],[-96.09936,33.83047],[-96.101349,33.845721],[-96.005296,33.845505],[-95.991487,33.866869],[-95.951609,33.857017],[-95.936132,33.886826],[-95.831948,33.835161],[-95.821666,33.856633],[-95.805149,33.861304],[-95.776255,33.845145],[-95.75431,33.853992],[-95.761916,33.883402],[-95.747335,33.895756],[-95.696962,33.885218],[-95.669978,33.905844],[-95.636978,33.906613],[-95.599678,33.934247],[-95.556915,33.92702],[-95.545197,33.880294],[-95.515302,33.891142],[-95.492028,33.874822],[-95.461499,33.883686],[-95.464211,33.873372],[-95.44737,33.86885],[-95.339122,33.868873],[-95.334523,33.885788],[-95.283445,33.877746],[-95.280351,33.896751],[-95.255747,33.902939],[-95.252906,33.933648],[-95.219358,33.961567],[-95.121184,33.931307],[-95.093929,33.895963],[-95.061065,33.895292],[-95.049025,33.86409],[-95.008376,33.866089],[-94.983303,33.851354],[-94.976208,33.859847],[-94.948716,33.818023],[-94.91945,33.810176],[-94.919614,33.786305],[-94.879218,33.764912],[-94.8693,33.745871],[-94.830804,33.740068],[-94.817427,33.752172],[-94.798634,33.744527],[-94.775064,33.755038],[-94.762961,33.731787],[-94.742576,33.727009],[-94.732384,33.700254],[-94.714865,33.707261],[-94.710725,33.691654],[-94.684792,33.684353],[-94.659167,33.692138],[-94.646113,33.6693],[-94.57962,33.677623],[-94.520725,33.616567],[-94.491503,33.625115],[-94.485875,33.637867],[-94.448637,33.642766],[-94.468086,33.599436],[-94.430039,33.591124],[-94.413155,33.569368],[-94.378076,33.577019],[-94.397398,33.562314],[-94.389515,33.546778],[-94.355945,33.54318],[-94.345513,33.567313],[-94.309582,33.551673],[-94.289129,33.582144],[-94.280849,33.577187],[-94.290901,33.558872],[-94.27909,33.557026],[-94.245932,33.589114],[-94.237975,33.577757],[-94.250197,33.556765],[-94.226392,33.552912],[-94.205634,33.567229],[-94.193248,33.556154],[-94.192483,33.570425],[-94.217408,33.57926],[-94.183913,33.594682],[-94.152626,33.575923],[-94.146048,33.581975],[-94.14852,33.565678],[-94.136864,33.571],[-94.128658,33.550952],[-94.088943,33.575322],[-94.061283,33.568805],[-94.055663,33.561887],[-94.073744,33.558285],[-94.06548,33.550909],[-94.04604,33.551321],[-94.04272,31.999265],[-94.018664,31.990843],[-93.971712,31.920384],[-93.923929,31.88985],[-93.904766,31.890599],[-93.874761,31.821661],[-93.827451,31.777741],[-93.830647,31.745811],[-93.802694,31.697783],[-93.826462,31.666919],[-93.816838,31.622509],[-93.838057,31.606795],[-93.834924,31.586211],[-93.798087,31.534044],[-93.743376,31.525196],[-93.725925,31.504092],[-93.74987,31.475276],[-93.70093,31.437784],[-93.704879,31.410881],[-93.674117,31.397681],[-93.665052,31.363886],[-93.687851,31.309835],[-93.642516,31.269508],[-93.620343,31.271025],[-93.598828,31.174679],[-93.588503,31.165581],[-93.535097,31.185614],[-93.551693,31.097258],[-93.52301,31.065241],[-93.516943,31.032584],[-93.539526,31.008498],[-93.566017,31.004567],[-93.571906,30.987614],[-93.526245,30.939411],[-93.567788,30.888302],[-93.554057,30.824941],[-93.561666,30.807739],[-93.584265,30.796663],[-93.592828,30.763986],[-93.619129,30.742002],[-93.611192,30.718053],[-93.629904,30.67994],[-93.6831,30.640763],[-93.684329,30.592586],[-93.727844,30.57407],[-93.729195,30.544842],[-93.740253,30.539569],[-93.714322,30.518562],[-93.697828,30.443838],[-93.757654,30.390423],[-93.765822,30.333318],[-93.708645,30.288317],[-93.705083,30.242752],[-93.720946,30.209852],[-93.688212,30.141376],[-93.701252,30.137376],[-93.702436,30.112721],[-93.732485,30.088914],[-93.70082,30.056274],[-93.720805,30.053043],[-93.739734,30.023987],[-93.786935,29.99058],[-93.838374,29.882855],[-93.927992,29.80964],[-93.926504,29.78956],[-93.89847,29.771577],[-93.891637,29.744618],[-93.873941,29.73777],[-93.837971,29.690619],[-93.866981,29.673085],[-94.001406,29.681486],[-94.132577,29.646217],[-94.594853,29.467903],[-94.694158,29.415632],[-94.731047,29.369141],[-94.778691,29.361483],[-94.783131,29.375642],[-94.766848,29.393489],[-94.6724,29.476843],[-94.608557,29.483345],[-94.566674,29.531988],[-94.532348,29.5178],[-94.495025,29.525031],[-94.503429,29.54325],[-94.522421,29.545672],[-94.553988,29.573882],[-94.740699,29.525858],[-94.783296,29.535314],[-94.78954,29.546494],[-94.755237,29.562782],[-94.708741,29.625226],[-94.693154,29.694453],[-94.695317,29.723052],[-94.735271,29.785433],[-94.816085,29.75671],[-94.851108,29.721373],[-94.872551,29.67125],[-94.893107,29.661336],[-94.915413,29.656614],[-94.936089,29.692704],[-94.965963,29.70033],[-95.015636,29.639457],[-94.982936,29.60167],[-95.016889,29.548303],[-94.981916,29.511141],[-94.909898,29.49691],[-94.930861,29.450504],[-94.8908,29.433432],[-94.893994,29.30817],[-94.921593,29.281556],[-94.952526,29.290122],[-95.099101,29.173529],[-95.151925,29.151162],[-95.16525,29.113566],[-95.136221,29.084537],[-94.879239,29.285839],[-94.824953,29.306005],[-94.822307,29.344254],[-94.810696,29.353435],[-94.784895,29.335535],[-94.72253,29.331446],[-95.081773,29.111222],[-95.38239,28.866348],[-95.439594,28.859022],[-95.812504,28.664942],[-96.220376,28.491966],[-96.378616,28.383909],[-96.37596,28.401682],[-96.335119,28.437795],[-96.223825,28.495067],[-96.21505,28.509679],[-95.98616,28.606319],[-95.978526,28.650594],[-95.996338,28.658736],[-96.006516,28.648049],[-96.047737,28.649067],[-96.221784,28.580364],[-96.233998,28.596649],[-96.212624,28.622604],[-96.230944,28.641433],[-96.192267,28.687744],[-96.19583,28.69894],[-96.222802,28.698431],[-96.287942,28.683164],[-96.304227,28.671459],[-96.303718,28.644996],[-96.373439,28.626675],[-96.487943,28.569677],[-96.485907,28.607845],[-96.510844,28.61497],[-96.499648,28.635835],[-96.563262,28.644487],[-96.572931,28.667897],[-96.561226,28.696395],[-96.584091,28.722798],[-96.664534,28.696904],[-96.61059,28.638889],[-96.61975,28.627693],[-96.611099,28.585962],[-96.565297,28.5824],[-96.561226,28.570695],[-96.526111,28.557972],[-96.505755,28.525911],[-96.402446,28.449066],[-96.59176,28.357462],[-96.672677,28.335579],[-96.705247,28.348811],[-96.710336,28.406827],[-96.772209,28.408074],[-96.794554,28.365688],[-96.791761,28.31217],[-96.809573,28.290287],[-96.787181,28.255681],[-96.800413,28.224128],[-96.934765,28.123873],[-96.962755,28.123365],[-97.027014,28.148408],[-97.021303,28.1841],[-97.037008,28.185528],[-97.153601,28.13318],[-97.214039,28.087494],[-97.21535,28.076575],[-97.176444,28.059892],[-97.137421,28.057037],[-97.025693,28.11216],[-97.035528,28.084688],[-97.025859,28.041939],[-97.129168,27.919801],[-97.186709,27.825453],[-97.219738,27.823939],[-97.250797,27.876035],[-97.272253,27.881427],[-97.379042,27.837867],[-97.393291,27.782905],[-97.368355,27.741683],[-97.316446,27.712676],[-97.253955,27.696696],[-97.296598,27.613947],[-97.294054,27.5941],[-97.321535,27.571199],[-97.401942,27.335574],[-97.508304,27.275014],[-97.532223,27.278577],[-97.544437,27.284175],[-97.498126,27.308602],[-97.502706,27.322343],[-97.483877,27.338628],[-97.48693,27.358984],[-97.501688,27.366618],[-97.609068,27.285193],[-97.63146,27.28621],[-97.640111,27.270943],[-97.628916,27.242953],[-97.54291,27.229213],[-97.42408,27.264073],[-97.443673,27.116235],[-97.45665,27.099695],[-97.495836,27.094098],[-97.477515,27.066108],[-97.48693,27.057711],[-97.486676,27.03481],[-97.473444,27.02285],[-97.478533,26.999186],[-97.555378,26.99028],[-97.555378,26.93888],[-97.540874,26.90631],[-97.563266,26.842188],[-97.509831,26.803511],[-97.468609,26.740915],[-97.445708,26.609362],[-97.416955,26.553637],[-97.441383,26.455418],[-97.41721,26.44982],[-97.42179,26.417249],[-97.382485,26.411326],[-97.369627,26.394603],[-97.388965,26.36585],[-97.387947,26.330481],[-97.358176,26.356435],[-97.335275,26.355672],[-97.336802,26.331753],[-97.352833,26.318521],[-97.343927,26.267376],[-97.311866,26.273737],[-97.307031,26.253126],[-97.32128,26.236078],[-97.296598,26.200709],[-97.306776,26.159487],[-97.282094,26.120301],[-97.294054,26.11394],[-97.270898,26.086459],[-97.199651,26.077044],[-97.195071,26.04193],[-97.224842,26.027426],[-97.219244,25.996128],[-97.208557,25.991802],[-97.167208,26.007069],[-97.162628,26.023482],[-97.18273,26.053126],[-97.152009,26.062108],[-97.146294,25.955606],[-97.276707,25.952147],[-97.277163,25.935438],[-97.350398,25.925241],[-97.37443,25.907444],[-97.360082,25.868874],[-97.372864,25.840117],[-97.422636,25.840378],[-97.445113,25.850026],[-97.454727,25.879337],[-97.521762,25.886458],[-97.546421,25.934077],[-97.582565,25.937857],[-97.583044,25.955443],[-97.598043,25.957556],[-97.643708,26.016943],[-97.758838,26.032131],[-97.789823,26.04246],[-97.801344,26.060017],[-97.868235,26.056656]]]]},\"properties\":{\"name\":\"Texas\",\"nation\":\"USA  \"}}]}","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4abbe4b07f02db672b4c","contributors":{"authors":[{"text":"Heitmuller, Franklin T.","contributorId":67476,"corporation":false,"usgs":true,"family":"Heitmuller","given":"Franklin","email":"","middleInitial":"T.","affiliations":[],"preferred":false,"id":247127,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Reece, Brian D. bdreece@usgs.gov","contributorId":2129,"corporation":false,"usgs":true,"family":"Reece","given":"Brian","email":"bdreece@usgs.gov","middleInitial":"D.","affiliations":[],"preferred":true,"id":247126,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":53255,"text":"ofr03406 - 2003 - Pallid sturgeon in the Lower Mississippi Region: Hematology and genome information","interactions":[],"lastModifiedDate":"2018-06-13T09:10:03","indexId":"ofr03406","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":330,"text":"Open-File Report","code":"OFR","onlineIssn":"2331-1258","printIssn":"0196-1497","active":true,"publicationSubtype":{"id":5}},"seriesNumber":"03-406","title":"Pallid sturgeon in the Lower Mississippi Region: Hematology and genome information","docAbstract":"<p>This project (Project 1448-43270-2M-002) has been coordinated through the Natchitoches National Fish Hatchery (NNFH) and the U.S. Geological Survey’s National Wetlands Research Center (NWRC). From November 2001 to April 2002, over 280 sturgeon of the genus Scaphirhynchus (including pallid sturgeon, shovelnose, and their hybrids) were sampled from the outflow channel of the Old River Control Structure Complex (ORCC) in Concordia Parish, La. In the overall project, several datasets were collected (see Appendix), including species identification by using microsatellites and morphometric characters, food habits, physical anomalies, information on blood cells, and pathologic evidence of iridovirus – the first indication in the lower Mississippi population of pallid sturgeon. In this study, data on blood cells were obtained from the sturgeon collected monthly from approximately 20 different animals at each sampling time. </p><p>This report presents preliminary information on differential blood cell identifications in sturgeon, data on comparative genomic DNA content and DNA degradation, and summaries and interpretations of data collected in light of available scientific literature addressing blood parameters of fish and sturgeon, in particular. Results obtained from collection and examination of blood and body fluids are often essential in establishing the health of fish (Blaxhall, 1972; Fange, 1992). Blood cells and sperm cells can be obtained nondestructively from fishes, even from small specimens that weigh less than 100 g (Stoskopf, 1992a). For flow cytometry assays, whereby cells are analyzed individually in a fluid stream, less than 1 :L of blood is needed. Examinations of blood by microscopy and flow cytometry were performed at NWRC in assisting in the efforts directed at recovery of the pallid sturgeon population in the Lower Mississippi River Basin. </p>","language":"English","publisher":"U.S. Geological Survey","publisherLocation":"Reston, VA","doi":"10.3133/ofr03406","collaboration":"Prepared in cooperation with U.S. Fish and Wildlife Service, Southeast Region, Natchitoches National Fish Hatchery, Natchitoches, Louisiana","usgsCitation":"Jenkins, J.A., 2003, Pallid sturgeon in the Lower Mississippi Region: Hematology and genome information: U.S. Geological Survey Open-File Report 03-406, iv, 32 p., https://doi.org/10.3133/ofr03406.","productDescription":"iv, 32 p.","numberOfPages":"37","onlineOnly":"Y","costCenters":[{"id":455,"text":"National Wetlands Research Center","active":true,"usgs":true},{"id":17705,"text":"Wetland and Aquatic Research Center","active":true,"usgs":true}],"links":[{"id":354893,"rank":2,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/of/2003/0406/coverthb.jpg"},{"id":354894,"rank":3,"type":{"id":11,"text":"Document"},"url":"https://pubs.usgs.gov/of/2003/0406/ofr2003406.pdf","text":"Report","size":"1.46 MB","linkFileType":{"id":1,"text":"pdf"},"description":"ofr 2003–406"}],"contact":"<p>Director,&nbsp;<a href=\"https://www.usgs.gov/centers/wetland-and-aquatic-research-center-warc/\" data-mce-href=\"https://www.usgs.gov/centers/wetland-and-aquatic-research-center-warc/\">Wetland and Aquatic Research Center</a><br>U.S. Geological Survey<br>700 Cajundome Blvd.<br>Lafayette, LA 70506</p>","tableOfContents":"<ul><li>Preface<br></li><li>Introduction<br></li><li>Materials and Methods<br></li><li>Results<br></li><li>Discussion<br></li><li>Acknowledgments<br></li><li>References Cited<br></li><li>Appendix<br></li></ul>","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4ae4e4b07f02db689ad3","contributors":{"authors":[{"text":"Jenkins, Jill A. 0000-0002-5087-0894 jenkinsj@usgs.gov","orcid":"https://orcid.org/0000-0002-5087-0894","contributorId":2710,"corporation":false,"usgs":true,"family":"Jenkins","given":"Jill","email":"jenkinsj@usgs.gov","middleInitial":"A.","affiliations":[{"id":17705,"text":"Wetland and Aquatic Research Center","active":true,"usgs":true},{"id":455,"text":"National Wetlands Research Center","active":true,"usgs":true}],"preferred":true,"id":247080,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":51528,"text":"ofr03264 - 2003 - Saturation overland flow estimated from TOPMODEL for the conterminous United States","interactions":[],"lastModifiedDate":"2012-02-02T00:11:13","indexId":"ofr03264","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":330,"text":"Open-File Report","code":"OFR","onlineIssn":"2331-1258","printIssn":"0196-1497","active":true,"publicationSubtype":{"id":5}},"seriesNumber":"2003-264","title":"Saturation overland flow estimated from TOPMODEL for the conterminous United States","docAbstract":"This 5-kilometer resolution raster (grid) dataset for the conterminous United States represents the average percentage of saturation overland flow in total streamflow estimated by the watershed model TOPMODEL. Saturation overland flow is simulated in TOPMODEL as precipitation that falls on saturated land-surface areas and enters the stream channel.\r\n\r\nTOPMODEL was applied to 5- by 5-kilometer areas across the conterminous United States using national climate, soils, and terrain GIS datasets. The model was run for 1,000 days for each 5- by 5-kilometer area. The average percentage of saturation overland flow in total streamflow was computed for the 1,000-day simulation in each grid cell.","language":"ENGLISH","doi":"10.3133/ofr03264","usgsCitation":"Wolock, D.M., 2003, Saturation overland flow estimated from TOPMODEL for the conterminous United States: U.S. Geological Survey Open-File Report 2003-264, raster digital data, https://doi.org/10.3133/ofr03264.","productDescription":"raster digital data","costCenters":[],"links":[{"id":4548,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://water.usgs.gov/lookup/getspatial?satof48","linkFileType":{"id":5,"text":"html"}},{"id":176328,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4a0ee4b07f02db5fdba9","contributors":{"authors":[{"text":"Wolock, David M. 0000-0002-6209-938X dwolock@usgs.gov","orcid":"https://orcid.org/0000-0002-6209-938X","contributorId":540,"corporation":false,"usgs":true,"family":"Wolock","given":"David","email":"dwolock@usgs.gov","middleInitial":"M.","affiliations":[{"id":451,"text":"National Water Quality Assessment Program","active":true,"usgs":true},{"id":503,"text":"Office of Water Quality","active":true,"usgs":true},{"id":353,"text":"Kansas Water Science Center","active":false,"usgs":true},{"id":27111,"text":"National Water Quality Program","active":true,"usgs":true},{"id":37778,"text":"WMA - Integrated Modeling and Prediction Division","active":true,"usgs":true}],"preferred":true,"id":243853,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":51536,"text":"ofr03201 - 2003 - Sequence-Stratigraphic Analysis of the Regional Observation Monitoring Program (ROMP) 29A Test Corehole and Its Relation to Carbonate Porosity and Regional Transmissivity in the Floridan Aquifer System, Highlands County, Florida","interactions":[],"lastModifiedDate":"2012-02-02T00:11:13","indexId":"ofr03201","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":330,"text":"Open-File Report","code":"OFR","onlineIssn":"2331-1258","printIssn":"0196-1497","active":true,"publicationSubtype":{"id":5}},"seriesNumber":"2003-201","title":"Sequence-Stratigraphic Analysis of the Regional Observation Monitoring Program (ROMP) 29A Test Corehole and Its Relation to Carbonate Porosity and Regional Transmissivity in the Floridan Aquifer System, Highlands County, Florida","docAbstract":"An analysis was made to describe and interpret the lithology of a part of the Upper Floridan aquifer penetrated by the Regional Observation Monitoring Program (ROMP) 29A test corehole in Highlands County, Florida. This information was integrated into a one-dimensional hydrostratigraphic model that delineates candidate flow zones and confining units in the context of sequence stratigraphy. Results from this test corehole will serve as a starting point to build a robust three-dimensional sequence-stratigraphic framework of the Floridan aquifer system. \r\n\r\nThe ROMP 29A test corehole penetrated the Avon Park Formation, Ocala Limestone, Suwannee Limestone, and Hawthorn Group of middle Eocene to Pliocene age. The part of the Avon Park Formation penetrated in the ROMP 29A test corehole contains two composite depositional sequences. A transgressive systems tract and a highstand systems tract were interpreted for the upper composite sequence; however, only a highstand systems tract was interpreted for the lower composite sequence of the deeper Avon Park stratigraphic section. The composite depositional sequences are composed of at least five high-frequency depositional sequences. These sequences contain high-frequency cycle sets that are an amalgamation of vertically stacked high-frequency cycles. Three types of high-frequency cycles have been identified in the Avon Park Formation: peritidal, shallow subtidal, and deeper subtidal high-frequency cycles. \r\n\r\nThe vertical distribution of carbonate-rock diffuse flow zones within the Avon Park Formation is heterogeneous. Porous vuggy intervals are less than 10 feet, and most are much thinner. The volumetric arrangement of the diffuse flow zones shows that most occur in the highstand systems tract of the lower composite sequence of the Avon Park Formation as compared to the upper composite sequence, which contains both a backstepping transgressive systems tract and a prograding highstand systems tract. Although the porous and permeable layers are not thick, some intervals may exhibit lateral continuity because of their deposition on a broad low-relief ramp. A thick interval of thin vuggy zones and open faults forms thin conduit flow zones mixed with relatively thicker carbonate-rock diffuse flow zones between a depth of 1,070 and 1,244 feet below land surface (bottom of the test corehole). This interval is the most transmissive part of the Avon Park Formation penetrated in the ROMP 29A test corehole and is included in the highstand systems tract of the lower composite sequence. \r\n\r\nThe Ocala Limestone is considered to be a semiconfining unit and contains three depositional sequences penetrated by the ROMP 29A test corehole. Deposited within deeper subtidal depositional cycles, no zones of enhanced porosity and permeability are expected in the Ocala Limestone. A thin erosional remnant of the shallow marine Suwannee Limestone overlies the Ocala Limestone, and permeability seems to be comparatively low because moldic porosity is poorly connected. Rocks that comprise the lower Hawthorn Group, Suwannee Limestone, and Ocala Limestone form a permeable upper zone of the Upper Floridan aquifer, and rocks of the lower Ocala Limestone and Avon Park Formation form a permeable lower zone of the Upper Floridan aquifer. On the basis of a preliminary analysis of transmissivity estimates for wells located north of Lake Okeechobee, spatial relations among groups of relatively high and low transmissivity values within the upper zone are evident. Upper zone transmissivity is generally less than 10,000 feet squared per day in areas located south of a line that extends through Charlotte, Sarasota, DeSoto, Highlands, Polk, Osceola, Okeechobee, and St. Lucie Counties. Transmissivity patterns within the lower zone of the Avon Park Formation cannot be regionally assessed because insufficient data over a wide areal extent have not been compiled.","language":"ENGLISH","doi":"10.3133/ofr03201","usgsCitation":"Ward, W.C., Cunningham, K., Renken, R., Wacker, M., and Carlson, J., 2003, Sequence-Stratigraphic Analysis of the Regional Observation Monitoring Program (ROMP) 29A Test Corehole and Its Relation to Carbonate Porosity and Regional Transmissivity in the Floridan Aquifer System, Highlands County, Florida: U.S. Geological Survey Open-File Report 2003-201, 34 p., plus appendixes, https://doi.org/10.3133/ofr03201.","productDescription":"34 p., plus appendixes","costCenters":[],"links":[{"id":4553,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.water.usgs.gov/ofr03-201/","linkFileType":{"id":5,"text":"html"}},{"id":176526,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4b07e4b07f02db69ad80","contributors":{"authors":[{"text":"Ward, W. C.","contributorId":8925,"corporation":false,"usgs":false,"family":"Ward","given":"W.","email":"","middleInitial":"C.","affiliations":[],"preferred":false,"id":243874,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Cunningham, K.J.","contributorId":39852,"corporation":false,"usgs":true,"family":"Cunningham","given":"K.J.","email":"","affiliations":[],"preferred":false,"id":243875,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Renken, R.A.","contributorId":99161,"corporation":false,"usgs":true,"family":"Renken","given":"R.A.","email":"","affiliations":[],"preferred":false,"id":243878,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Wacker, M.A.","contributorId":91168,"corporation":false,"usgs":true,"family":"Wacker","given":"M.A.","email":"","affiliations":[],"preferred":false,"id":243876,"contributorType":{"id":1,"text":"Authors"},"rank":4},{"text":"Carlson, J.I.","contributorId":96344,"corporation":false,"usgs":true,"family":"Carlson","given":"J.I.","email":"","affiliations":[],"preferred":false,"id":243877,"contributorType":{"id":1,"text":"Authors"},"rank":5}]}}
,{"id":51553,"text":"ofr03146 - 2003 - Flow characteristics at U.S. Geological Survey streamgages in the conterminous United States","interactions":[],"lastModifiedDate":"2012-02-02T00:11:31","indexId":"ofr03146","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":330,"text":"Open-File Report","code":"OFR","onlineIssn":"2331-1258","printIssn":"0196-1497","active":true,"publicationSubtype":{"id":5}},"seriesNumber":"2003-146","title":"Flow characteristics at U.S. Geological Survey streamgages in the conterminous United States","docAbstract":"This dataset represents point locations and flow characteristics for current (as of November 20, 2001) and historical U.S. Geological Survey (USGS) streamgages in the conterminous United States. The flow characteristics were computed from the daily streamflow data recorded at each streamgage for the period of record.\r\n\r\nThe attributes associated with each streamgage include:\r\n\r\nStation number\r\nStation name\r\nStation latitude (decimal degrees in North American Datum of 1983, NAD 83)\r\nStation longitude (decimal degrees in NAD 83)\r\nFirst date (year, month, day) of streamflow data\r\nLast date (year, month, day) of streamflow data\r\nNumber of days of streamflow data\r\nMinimum and maximum daily flow for the period of record (cubic feet per second)\r\nPercentiles (1, 5, 10, 20, 25, 50, 75, 80, 90, 95, 99) of daily flow for the period of record (cubic feet per second)\r\nAverage and standard deviation of daily flow for the period of record (cubic feet per second)\r\nMean annual base-flow index (BFI: see supplemental information) computed for the period of record (fraction, ranging from 0 to 1)\r\nYear-to-year standard deviation of the annual base-flow index computed for the period of record (fraction)\r\nNumber of years of data used to compute the base-flow index (years)\r\nReported drainage area (square miles)\r\nReported contributing drainage area (square miles)\r\nNational Water Information System (NWIS)-Web page URL for streamgage\r\nHydrologic Unit Code (HUC, 8 digit)\r\nHydrologic landscape region (HLR)\r\nRiver Reach File 1 (RF1) segment identification number (E2RF1##)\r\n\r\nStation numbers, names, locations, and drainage areas were acquired through the National Water Information System (NWIS)-Web (http://water.usgs.gov/nwis) on November 20, 2001. The streamflow data used to compute flow characteristics were copied from the Water server (water.usgs.gov:/www/htdocs/nwisweb/data1/discharge/) on November 2, 2001.\r\n\r\nThe missing value indicator for all attributes is -99. Some streamflow characteristics are missing for: (1) streamgages measuring flow subject to tidal effects, which cause flow to reverse directions, (2) streamgages with site information but no streamflow data at the time the data were retrieved, and (3) streamgages with record length too short to compute the base-flow index.","language":"ENGLISH","doi":"10.3133/ofr03146","usgsCitation":"Wolock, D., 2003, Flow characteristics at U.S. Geological Survey streamgages in the conterminous United States: U.S. Geological Survey Open-File Report 2003-146, vector digital data, https://doi.org/10.3133/ofr03146.","productDescription":"vector digital data","costCenters":[],"links":[{"id":4587,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://water.usgs.gov/lookup/getspatial?qsitesdd","linkFileType":{"id":5,"text":"html"}},{"id":179481,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4a1ae4b07f02db606794","contributors":{"authors":[{"text":"Wolock, David","contributorId":61528,"corporation":false,"usgs":true,"family":"Wolock","given":"David","affiliations":[],"preferred":false,"id":243935,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":54020,"text":"ofr03454 - 2003 - Water temperature, streamflow, and ground-water elevation in and adjacent to the Russian river between Hopland and Guerneville, California from 1998-2002","interactions":[],"lastModifiedDate":"2020-02-11T07:19:47","indexId":"ofr03454","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":330,"text":"Open-File Report","code":"OFR","onlineIssn":"2331-1258","printIssn":"0196-1497","active":true,"publicationSubtype":{"id":5}},"seriesNumber":"2003-454","title":"Water temperature, streamflow, and ground-water elevation in and adjacent to the Russian river between Hopland and Guerneville, California from 1998-2002","docAbstract":"Temperature, water level elevation, stage height, and river discharge data for this report were collected in and adjacent to the Russian River from Hopland to Guerneville, CA over a four-year period from 1998 to 2002 to establish baselines for long-term water quality, water supply and habitat. Data files presented in this report were collected by the USGS and the Sonoma County Water Agency's Engineering Resource and Planning, and Natural Resource Divisions.  Temperature data were collected in single-channel submersible microloggers or temperature data were collected simultaneously with water-elevation data in dual-channel down-hole data loggers.  Stream stage and streamflow data were collected at USGS stream gaging stations located near Hopland, Healdsburg, and Guerneville over a 130 km reach of the Russian River.  During the period of record stream flow ranged from 3 to 1458 m3/s.  Stream temperature ranged from 8 to 29 oC while groundwater temperature ranged from 10 to 38 oC.  Stream stage varied 5 m seasonly, while ground-water level varied 19 m over the same time scale.","language":"English","publisher":"U.S. Geological Survey","doi":"10.3133/ofr03454","usgsCitation":"Cox, M.H., and Hatch, C., 2003, Water temperature, streamflow, and ground-water elevation in and adjacent to the Russian river between Hopland and Guerneville, California from 1998-2002: U.S. Geological Survey Open-File Report 2003-454, 39 p., https://doi.org/10.3133/ofr03454.","productDescription":"39 p.","costCenters":[{"id":589,"text":"Toxic Substances Hydrology Program","active":true,"usgs":true}],"links":[{"id":182038,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"},{"id":5460,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.water.usgs.gov/ofr03-454/","linkFileType":{"id":5,"text":"html"}}],"country":"United States","state":"California","county":"Mendocino County, Sonoma County","city":"Hopland, Guerneville","geographicExtents":"{\"type\":\"FeatureCollection\",\"features\":[{\"type\":\"Feature\",\"geometry\":{\"type\":\"MultiPolygon\",\"coordinates\":[[[[-123.544,40.0038],[-123.543,39.978],[-123.443,39.9784],[-123.368,39.978],[-123.343,39.9783],[-123.227,39.9786],[-123.171,39.9785],[-123.151,39.9781],[-123.088,39.9786],[-123.059,39.9785],[-123.025,39.979],[-122.934,39.9784],[-122.934,39.9829],[-122.924,39.9677],[-122.926,39.9486],[-122.915,39.9389],[-122.909,39.9355],[-122.909,39.9341],[-122.917,39.9312],[-122.92,39.9279],[-122.919,39.9189],[-122.922,39.9156],[-122.933,39.9122],[-122.94,39.9106],[-122.949,39.9076],[-122.948,39.9054],[-122.946,39.8977],[-122.947,39.8932],[-122.949,39.8872],[-122.95,39.8777],[-122.951,39.8754],[-122.95,39.8681],[-122.955,39.8608],[-122.955,39.8562],[-122.958,39.8484],[-122.956,39.8399],[-122.947,39.8356],[-122.947,39.8315],[-122.944,39.8225],[-122.944,39.8188],[-122.942,39.8103],[-122.944,39.8061],[-122.942,39.7989],[-122.937,39.7991],[-122.936,39.7501],[-122.912,39.7499],[-122.91,39.7118],[-122.891,39.7114],[-122.89,39.6257],[-122.888,39.6171],[-122.888,39.5827],[-122.889,39.5309],[-122.937,39.5319],[-122.937,39.5174],[-123.023,39.5191],[-123.023,39.5114],[-123.045,39.5107],[-123.045,39.503],[-123.062,39.5034],[-123.063,39.4522],[-123.072,39.4524],[-123.07,39.437],[-123.075,39.4373],[-123.075,39.4246],[-123.076,39.4083],[-123.057,39.4074],[-123.057,39.3793],[-123.047,39.3796],[-123.048,39.3737],[-123.049,39.3646],[-123.039,39.3639],[-123.038,39.3372],[-123.029,39.3366],[-123.03,39.322],[-123.02,39.3223],[-123.02,39.2779],[-123.005,39.2783],[-123.004,39.2574],[-122.996,39.2572],[-122.995,39.2368],[-123.013,39.2363],[-123.013,39.2223],[-123.021,39.2225],[-123.021,39.2143],[-123.025,39.2138],[-123.025,39.2083],[-123.03,39.2082],[-123.03,39.2005],[-123.035,39.2003],[-123.035,39.1931],[-123.042,39.1929],[-123.041,39.1811],[-123.046,39.1814],[-123.047,39.175],[-123.081,39.175],[-123.081,39.1391],[-123.088,39.1394],[-123.088,39.1108],[-123.085,39.1105],[-123.084,39.0955],[-123.094,39.0948],[-123.093,39.0807],[-123.093,39.073],[-123.084,39.0728],[-123.084,39.066],[-123.066,39.0661],[-123.066,39.0516],[-123.057,39.0509],[-123.057,39.0369],[-123.056,39.0219],[-123.045,39.0218],[-123.046,39.0145],[-123.037,39.0143],[-123.037,39.008],[-123.027,39.0082],[-123.027,38.9973],[-123.018,38.9972],[-123.018,38.994],[-123.011,38.9937],[-123.011,38.9983],[-122.987,38.9976],[-122.987,38.984],[-122.976,38.9838],[-122.977,38.9471],[-122.968,38.9469],[-122.969,38.9332],[-122.961,38.9325],[-122.961,38.9257],[-122.949,38.9252],[-122.948,38.9116],[-122.948,38.9007],[-122.91,38.9022],[-122.91,38.8963],[-122.894,38.8963],[-122.894,38.8823],[-122.876,38.8818],[-122.875,38.8746],[-122.858,38.8746],[-122.858,38.8674],[-122.84,38.8678],[-122.839,38.8583],[-122.82,38.858],[-122.818,38.8503],[-122.815,38.8449],[-122.811,38.8423],[-122.809,38.8378],[-122.805,38.838],[-122.799,38.8395],[-122.796,38.8386],[-122.775,38.8224],[-122.763,38.8118],[-122.758,38.8093],[-122.746,38.8018],[-122.749,38.7909],[-122.742,38.7843],[-122.739,38.7825],[-122.733,38.7745],[-122.728,38.7706],[-122.723,38.7607],[-122.718,38.7545],[-122.712,38.7533],[-122.708,38.7493],[-122.711,38.7434],[-122.71,38.7379],[-122.71,38.7343],[-122.703,38.7322],[-122.701,38.7296],[-122.699,38.7237],[-122.696,38.7184],[-122.693,38.7139],[-122.688,38.7104],[-122.677,38.7075],[-122.67,38.7091],[-122.659,38.7057],[-122.653,38.7067],[-122.649,38.7069],[-122.644,38.7038],[-122.632,38.681],[-122.625,38.6748],[-122.626,38.6675],[-122.623,38.6626],[-122.624,38.6535],[-122.633,38.6379],[-122.631,38.6298],[-122.627,38.6226],[-122.631,38.6203],[-122.647,38.5999],[-122.63,38.5772],[-122.632,38.5703],[-122.626,38.5696],[-122.622,38.5688],[-122.618,38.5612],[-122.599,38.5589],[-122.582,38.5476],[-122.574,38.5382],[-122.566,38.5253],[-122.547,38.5239],[-122.542,38.515],[-122.54,38.5092],[-122.542,38.5059],[-122.536,38.5006],[-122.543,38.4973],[-122.539,38.4892],[-122.534,38.4803],[-122.528,38.4714],[-122.522,38.4706],[-122.516,38.4712],[-122.507,38.4651],[-122.508,38.4587],[-122.503,38.4557],[-122.493,38.4559],[-122.486,38.4552],[-122.481,38.4521],[-122.482,38.443],[-122.486,38.4379],[-122.491,38.4337],[-122.495,38.4277],[-122.5,38.4231],[-122.487,38.4171],[-122.478,38.4109],[-122.471,38.4016],[-122.469,38.3948],[-122.465,38.3908],[-122.458,38.3865],[-122.453,38.3825],[-122.445,38.3773],[-122.448,38.3758],[-122.455,38.3734],[-122.456,38.3702],[-122.452,38.3639],[-122.444,38.3591],[-122.435,38.3553],[-122.429,38.3513],[-122.421,38.3424],[-122.415,38.3381],[-122.409,38.3237],[-122.406,38.3229],[-122.402,38.3143],[-122.396,38.3063],[-122.397,38.3045],[-122.403,38.3012],[-122.401,38.2935],[-122.401,38.2862],[-122.403,38.2826],[-122.401,38.2767],[-122.397,38.2732],[-122.389,38.2743],[-122.388,38.2734],[-122.391,38.2638],[-122.389,38.2607],[-122.387,38.2558],[-122.384,38.2518],[-122.376,38.2492],[-122.374,38.2465],[-122.373,38.2443],[-122.37,38.2448],[-122.368,38.2462],[-122.365,38.2463],[-122.362,38.2373],[-122.358,38.2229],[-122.357,38.212],[-122.354,38.2062],[-122.352,38.2035],[-122.351,38.1976],[-122.352,38.1963],[-122.353,38.194],[-122.36,38.1947],[-122.358,38.1861],[-122.361,38.1829],[-122.367,38.1841],[-122.37,38.18],[-122.366,38.1692],[-122.366,38.1633],[-122.369,38.1564],[-122.379,38.1607],[-122.392,38.1622],[-122.403,38.1615],[-122.407,38.1573],[-122.404,38.1511],[-122.403,38.1509],[-122.398,38.1448],[-122.399,38.1431],[-122.398,38.1403],[-122.399,38.1397],[-122.401,38.1375],[-122.407,38.1336],[-122.408,38.1336],[-122.416,38.1303],[-122.417,38.1303],[-122.42,38.1286],[-122.422,38.1283],[-122.435,38.1214],[-122.439,38.1178],[-122.465,38.1153],[-122.469,38.1153],[-122.469,38.115],[-122.475,38.1147],[-122.475,38.1144],[-122.48,38.1144],[-122.482,38.1136],[-122.491,38.1117],[-122.496,38.1122],[-122.496,38.1125],[-122.51,38.1272],[-122.511,38.1275],[-122.513,38.1316],[-122.521,38.1429],[-122.538,38.1515],[-122.539,38.1524],[-122.545,38.1547],[-122.549,38.1551],[-122.554,38.1564],[-122.56,38.1594],[-122.559,38.1641],[-122.556,38.167],[-122.556,38.1691],[-122.562,38.1702],[-122.565,38.1714],[-122.566,38.1724],[-122.568,38.178],[-122.569,38.1839],[-122.572,38.1859],[-122.581,38.1817],[-122.586,38.1833],[-122.586,38.1845],[-122.588,38.1859],[-122.594,38.1872],[-122.601,38.187],[-122.601,38.1843],[-122.603,38.184],[-122.608,38.1806],[-122.614,38.1823],[-122.617,38.1816],[-122.623,38.1819],[-122.626,38.1782],[-122.646,38.1823],[-122.656,38.1878],[-122.662,38.1901],[-122.675,38.192],[-122.682,38.1915],[-122.685,38.1925],[-122.687,38.1944],[-122.707,38.1966],[-122.711,38.196],[-122.715,38.1982],[-122.721,38.2057],[-122.74,38.2071],[-122.891,38.3104],[-122.903,38.3169],[-122.908,38.3145],[-122.911,38.3144],[-122.911,38.3176],[-122.912,38.3185],[-122.913,38.3189],[-122.916,38.3193],[-122.919,38.3178],[-122.92,38.3164],[-122.916,38.3129],[-122.922,38.3082],[-122.925,38.3127],[-122.935,38.3101],[-122.935,38.3142],[-122.938,38.315],[-122.94,38.3127],[-122.942,38.3117],[-122.95,38.3111],[-122.955,38.3146],[-122.962,38.3171],[-122.967,38.3169],[-122.971,38.3109],[-122.98,38.312],[-122.986,38.3087],[-122.994,38.3062],[-122.995,38.3003],[-123.003,38.2964],[-123.004,38.2966],[-123.01,38.3006],[-123.011,38.3007],[-123.014,38.3033],[-123.026,38.3103],[-123.037,38.3131],[-123.052,38.3081],[-123.052,38.3075],[-123.054,38.3058],[-123.055,38.3069],[-123.055,38.3086],[-123.053,38.3119],[-123.052,38.3147],[-123.043,38.3153],[-123.043,38.3156],[-123.041,38.3161],[-123.041,38.3192],[-123.04,38.3194],[-123.04,38.3208],[-123.039,38.3231],[-123.042,38.3261],[-123.043,38.3261],[-123.048,38.33],[-123.048,38.3306],[-123.049,38.3325],[-123.051,38.3328],[-123.052,38.3303],[-123.053,38.3297],[-123.054,38.3344],[-123.06,38.3347],[-123.06,38.3339],[-123.057,38.3308],[-123.055,38.3192],[-123.056,38.3147],[-123.061,38.3117],[-123.052,38.3015],[-123.052,38.3008],[-123.054,38.2986],[-123.056,38.2987],[-123.058,38.2975],[-123.058,38.2972],[-123.059,38.2981],[-123.06,38.2975],[-123.066,38.3039],[-123.066,38.3061],[-123.07,38.3106],[-123.077,38.32],[-123.078,38.32],[-123.079,38.3228],[-123.079,38.3231],[-123.07,38.3308],[-123.069,38.3325],[-123.069,38.3344],[-123.068,38.3372],[-123.068,38.3503],[-123.067,38.3511],[-123.066,38.3511],[-123.066,38.3517],[-123.072,38.3647],[-123.074,38.3675],[-123.076,38.3711],[-123.078,38.3725],[-123.079,38.3764],[-123.082,38.3781],[-123.084,38.3844],[-123.085,38.3853],[-123.086,38.3894],[-123.091,38.3928],[-123.096,38.3947],[-123.096,38.3953],[-123.095,38.3969],[-123.095,38.3989],[-123.096,38.3992],[-123.096,38.4011],[-123.1,38.4072],[-123.101,38.4106],[-123.103,38.4144],[-123.106,38.4158],[-123.109,38.4189],[-123.109,38.4194],[-123.111,38.42],[-123.116,38.4228],[-123.116,38.4253],[-123.117,38.4261],[-123.117,38.4269],[-123.119,38.4283],[-123.12,38.4283],[-123.122,38.4292],[-123.121,38.4317],[-123.121,38.4331],[-123.122,38.4336],[-123.124,38.4403],[-123.132,38.4528],[-123.133,38.4536],[-123.138,38.4542],[-123.139,38.455],[-123.144,38.4575],[-123.147,38.4583],[-123.15,38.4606],[-123.151,38.4625],[-123.153,38.4642],[-123.154,38.4642],[-123.154,38.4636],[-123.155,38.4636],[-123.159,38.4678],[-123.16,38.4678],[-123.161,38.4669],[-123.164,38.4689],[-123.164,38.4719],[-123.173,38.4764],[-123.173,38.4767],[-123.176,38.4792],[-123.179,38.4808],[-123.191,38.4886],[-123.203,38.4939],[-123.209,38.4956],[-123.209,38.4953],[-123.213,38.4972],[-123.217,38.4986],[-123.217,38.4983],[-123.219,38.4983],[-123.219,38.4981],[-123.224,38.4989],[-123.224,38.4992],[-123.227,38.5011],[-123.228,38.5011],[-123.231,38.5022],[-123.232,38.5022],[-123.233,38.5039],[-123.232,38.5044],[-123.234,38.5053],[-123.235,38.5061],[-123.236,38.5078],[-123.238,38.5089],[-123.239,38.5092],[-123.239,38.5089],[-123.243,38.5103],[-123.246,38.5125],[-123.247,38.5125],[-123.249,38.5113],[-123.251,38.5095],[-123.252,38.51],[-123.256,38.5158],[-123.257,38.5158],[-123.259,38.5169],[-123.259,38.5175],[-123.263,38.5203],[-123.265,38.5222],[-123.267,38.5233],[-123.269,38.5236],[-123.269,38.5261],[-123.27,38.5289],[-123.271,38.5289],[-123.272,38.5308],[-123.274,38.5317],[-123.279,38.5306],[-123.28,38.5331],[-123.28,38.5353],[-123.283,38.5356],[-123.283,38.5364],[-123.287,38.539],[-123.291,38.5403],[-123.299,38.5442],[-123.305,38.5481],[-123.306,38.55],[-123.305,38.5542],[-123.309,38.5556],[-123.309,38.5553],[-123.318,38.5581],[-123.318,38.5586],[-123.323,38.5597],[-123.325,38.5611],[-123.325,38.5619],[-123.324,38.5625],[-123.336,38.5672],[-123.34,38.5742],[-123.341,38.5777],[-123.34,38.5797],[-123.34,38.5818],[-123.342,38.5869],[-123.349,38.5942],[-123.351,38.5958],[-123.355,38.5978],[-123.356,38.5978],[-123.359,38.595],[-123.36,38.5958],[-123.36,38.5963],[-123.363,38.6006],[-123.369,38.6025],[-123.372,38.6058],[-123.371,38.6083],[-123.37,38.6139],[-123.372,38.6139],[-123.373,38.615],[-123.378,38.6181],[-123.38,38.6211],[-123.384,38.625],[-123.388,38.6283],[-123.391,38.6347],[-123.395,38.6364],[-123.394,38.6394],[-123.394,38.6404],[-123.396,38.6403],[-123.396,38.6406],[-123.398,38.6419],[-123.399,38.6419],[-123.399,38.6425],[-123.402,38.6469],[-123.4,38.6467],[-123.4,38.6472],[-123.401,38.6486],[-123.402,38.6489],[-123.403,38.6486],[-123.408,38.6522],[-123.409,38.6528],[-123.41,38.6528],[-123.409,38.656],[-123.406,38.6567],[-123.411,38.6592],[-123.41,38.66],[-123.41,38.6617],[-123.417,38.6669],[-123.419,38.6711],[-123.421,38.6736],[-123.422,38.6736],[-123.423,38.6744],[-123.424,38.6744],[-123.425,38.6756],[-123.427,38.6767],[-123.428,38.6767],[-123.43,38.6783],[-123.431,38.6783],[-123.434,38.6794],[-123.432,38.6839],[-123.432,38.6847],[-123.434,38.6892],[-123.437,38.6919],[-123.443,38.6994],[-123.447,38.7031],[-123.449,38.7025],[-123.451,38.7044],[-123.451,38.7036],[-123.454,38.7046],[-123.454,38.71],[-123.463,38.7172],[-123.488,38.7283],[-123.491,38.7344],[-123.493,38.7344],[-123.495,38.7367],[-123.498,38.7372],[-123.499,38.7381],[-123.501,38.7381],[-123.501,38.7378],[-123.513,38.74],[-123.516,38.7419],[-123.519,38.745],[-123.521,38.7481],[-123.526,38.7506],[-123.527,38.7514],[-123.532,38.76],[-123.531,38.7608],[-123.531,38.7617],[-123.524,38.7591],[-123.531,38.764],[-123.537,38.77],[-123.539,38.7714],[-123.548,38.7792],[-123.549,38.7792],[-123.559,38.7844],[-123.56,38.7838],[-123.564,38.7858],[-123.564,38.7886],[-123.568,38.7936],[-123.569,38.7936],[-123.573,38.7975],[-123.573,38.7972],[-123.581,38.8028],[-123.584,38.8022],[-123.59,38.8017],[-123.592,38.8039],[-123.592,38.8044],[-123.6,38.8069],[-123.6,38.8088],[-123.599,38.8117],[-123.601,38.8139],[-123.602,38.8186],[-123.609,38.8239],[-123.61,38.8253],[-123.613,38.8264],[-123.617,38.8264],[-123.621,38.8303],[-123.626,38.8306],[-123.627,38.8328],[-123.63,38.8353],[-123.63,38.8358],[-123.636,38.8397],[-123.636,38.8403],[-123.638,38.8425],[-123.641,38.8433],[-123.642,38.8425],[-123.644,38.8458],[-123.645,38.8453],[-123.649,38.8483],[-123.653,38.8561],[-123.654,38.86],[-123.654,38.8633],[-123.655,38.8661],[-123.657,38.8694],[-123.659,38.8714],[-123.665,38.8756],[-123.666,38.8756],[-123.672,38.8781],[-123.675,38.88],[-123.675,38.8806],[-123.679,38.8811],[-123.682,38.8839],[-123.684,38.8872],[-123.686,38.8886],[-123.687,38.8922],[-123.693,38.8956],[-123.706,38.9067],[-123.71,38.9092],[-123.71,38.9097],[-123.712,38.9125],[-123.715,38.9158],[-123.716,38.9156],[-123.718,38.9161],[-123.729,38.9258],[-123.729,38.9303],[-123.727,38.9358],[-123.732,38.9406],[-123.733,38.9419],[-123.734,38.9447],[-123.739,38.9506],[-123.741,38.9539],[-123.74,38.9556],[-123.737,38.9567],[-123.737,38.9575],[-123.733,38.9572],[-123.729,38.9561],[-123.725,38.9594],[-123.725,38.9597],[-123.72,38.9644],[-123.713,38.9744],[-123.711,38.9767],[-123.701,38.9953],[-123.701,38.9969],[-123.694,39.0108],[-123.692,39.0239],[-123.69,39.0339],[-123.691,39.0364],[-123.694,39.0397],[-123.695,39.0415],[-123.691,39.0444],[-123.693,39.0497],[-123.693,39.0525],[-123.694,39.0525],[-123.695,39.0542],[-123.694,39.0592],[-123.695,39.0591],[-123.696,39.0622],[-123.7,39.0681],[-123.703,39.0742],[-123.704,39.0792],[-123.705,39.0792],[-123.706,39.0872],[-123.709,39.0931],[-123.71,39.0967],[-123.71,39.1036],[-123.714,39.1086],[-123.714,39.1094],[-123.718,39.12],[-123.718,39.1211],[-123.719,39.1214],[-123.72,39.1231],[-123.719,39.1286],[-123.737,39.1408],[-123.736,39.1414],[-123.737,39.1489],[-123.739,39.1525],[-123.738,39.1536],[-123.736,39.1542],[-123.735,39.1572],[-123.739,39.163],[-123.743,39.165],[-123.744,39.1673],[-123.744,39.1688],[-123.745,39.1692],[-123.746,39.1702],[-123.746,39.1708],[-123.749,39.1735],[-123.751,39.1738],[-123.751,39.1744],[-123.753,39.1755],[-123.753,39.1763],[-123.752,39.1775],[-123.753,39.1784],[-123.76,39.1917],[-123.759,39.1933],[-123.76,39.1938],[-123.764,39.1915],[-123.765,39.1929],[-123.766,39.1933],[-123.768,39.1933],[-123.768,39.1936],[-123.771,39.1949],[-123.771,39.1956],[-123.772,39.1974],[-123.772,39.1989],[-123.776,39.2145],[-123.777,39.2233],[-123.771,39.2292],[-123.773,39.2289],[-123.779,39.2336],[-123.779,39.2428],[-123.782,39.2485],[-123.787,39.2552],[-123.786,39.2554],[-123.784,39.2572],[-123.785,39.259],[-123.788,39.2617],[-123.789,39.2657],[-123.795,39.2736],[-123.795,39.2728],[-123.796,39.2726],[-123.801,39.2744],[-123.802,39.2767],[-123.803,39.2781],[-123.802,39.2917],[-123.794,39.2924],[-123.796,39.2931],[-123.784,39.3033],[-123.784,39.3036],[-123.789,39.3018],[-123.794,39.303],[-123.799,39.3026],[-123.807,39.3029],[-123.808,39.3035],[-123.808,39.3031],[-123.81,39.304],[-123.81,39.3103],[-123.808,39.3109],[-123.807,39.3119],[-123.806,39.3122],[-123.801,39.3189],[-123.801,39.3194],[-123.807,39.3235],[-123.807,39.3253],[-123.806,39.3253],[-123.812,39.328],[-123.818,39.3361],[-123.817,39.3387],[-123.819,39.3389],[-123.819,39.3402],[-123.82,39.3418],[-123.823,39.3434],[-123.823,39.3443],[-123.824,39.3447],[-123.825,39.3456],[-123.827,39.3487],[-123.827,39.3499],[-123.825,39.3531],[-123.823,39.3541],[-123.824,39.3569],[-123.822,39.3618],[-123.822,39.3661],[-123.825,39.3695],[-123.822,39.3725],[-123.821,39.3725],[-123.821,39.3764],[-123.82,39.3783],[-123.821,39.3812],[-123.82,39.3844],[-123.82,39.3865],[-123.818,39.3881],[-123.82,39.3899],[-123.819,39.392],[-123.822,39.4025],[-123.821,39.4039],[-123.821,39.4044],[-123.822,39.4063],[-123.822,39.407],[-123.813,39.418],[-123.814,39.4181],[-123.816,39.4195],[-123.818,39.4227],[-123.813,39.4262],[-123.812,39.4264],[-123.81,39.4286],[-123.82,39.436],[-123.819,39.44],[-123.818,39.4397],[-123.814,39.4411],[-123.813,39.4428],[-123.814,39.4483],[-123.814,39.4531],[-123.813,39.4544],[-123.812,39.4551],[-123.809,39.4617],[-123.808,39.463],[-123.808,39.4711],[-123.805,39.4735],[-123.803,39.483],[-123.803,39.4875],[-123.804,39.488],[-123.804,39.4902],[-123.803,39.4902],[-123.795,39.4947],[-123.786,39.5064],[-123.784,39.5107],[-123.783,39.5122],[-123.783,39.5139],[-123.778,39.5217],[-123.774,39.5317],[-123.767,39.5517],[-123.762,39.549],[-123.768,39.5558],[-123.768,39.561],[-123.769,39.5614],[-123.769,39.5622],[-123.768,39.563],[-123.769,39.5653],[-123.772,39.5672],[-123.772,39.5697],[-123.773,39.5703],[-123.778,39.5778],[-123.778,39.5833],[-123.779,39.5848],[-123.781,39.5865],[-123.781,39.5879],[-123.782,39.589],[-123.785,39.591],[-123.785,39.5939],[-123.787,39.5964],[-123.789,39.6011],[-123.789,39.6036],[-123.787,39.6058],[-123.787,39.6081],[-123.786,39.6078],[-123.783,39.6133],[-123.783,39.6219],[-123.787,39.6389],[-123.785,39.6497],[-123.785,39.6523],[-123.787,39.6561],[-123.786,39.6607],[-123.789,39.6636],[-123.791,39.666],[-123.792,39.6775],[-123.795,39.6901],[-123.796,39.6908],[-123.8,39.6956],[-123.802,39.6972],[-123.802,39.6978],[-123.804,39.6992],[-123.804,39.7006],[-123.805,39.7059],[-123.806,39.7063],[-123.807,39.7085],[-123.808,39.7096],[-123.813,39.7122],[-123.815,39.7139],[-123.817,39.7143],[-123.82,39.7159],[-123.831,39.7292],[-123.831,39.7306],[-123.829,39.7338],[-123.829,39.7348],[-123.833,39.7378],[-123.832,39.7388],[-123.832,39.7398],[-123.835,39.7494],[-123.835,39.7504],[-123.836,39.7509],[-123.839,39.7566],[-123.839,39.7636],[-123.838,39.765],[-123.838,39.778],[-123.84,39.7964],[-123.842,39.7989],[-123.843,39.8031],[-123.844,39.8053],[-123.845,39.8063],[-123.846,39.8064],[-123.848,39.8222],[-123.851,39.8314],[-123.852,39.8323],[-123.867,39.8384],[-123.875,39.8422],[-123.876,39.8422],[-123.886,39.8475],[-123.889,39.8511],[-123.894,39.8538],[-123.894,39.8549],[-123.896,39.8552],[-123.897,39.855],[-123.898,39.8553],[-123.901,39.8575],[-123.91,39.8678],[-123.912,39.8696],[-123.916,39.8806],[-123.917,39.8817],[-123.926,39.9008],[-123.927,39.9016],[-123.928,39.9039],[-123.932,39.91],[-123.933,39.91],[-123.936,39.9122],[-123.952,39.9213],[-123.957,39.9258],[-123.959,39.9292],[-123.962,39.9364],[-123.974,39.9522],[-123.989,39.9686],[-124.024,40.0019],[-123.799,40.003],[-123.779,40.0028],[-123.611,40.0034],[-123.592,40.0031],[-123.544,40.0038]]],[[[-123.7296,38.9345],[-123.73,38.9342],[-123.7304,38.9343],[-123.7311,38.9358],[-123.7312,38.9371],[-123.7308,38.9374],[-123.729,38.9353],[-123.7292,38.9347],[-123.7296,38.9345]]],[[[-123.5922,38.7984],[-123.5925,38.798],[-123.5933,38.7981],[-123.5952,38.7992],[-123.595,38.8016],[-123.5941,38.8013],[-123.5929,38.7994],[-123.5922,38.7989],[-123.5922,38.7984]]]]},\"properties\":{\"name\":\"Mendocino\",\"state\":\"CA\"}}]}","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e48d1e4b07f02db547847","contributors":{"authors":[{"text":"Cox, Marisa H.","contributorId":52146,"corporation":false,"usgs":true,"family":"Cox","given":"Marisa","email":"","middleInitial":"H.","affiliations":[],"preferred":false,"id":248943,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Hatch, Christine","contributorId":43035,"corporation":false,"usgs":true,"family":"Hatch","given":"Christine","affiliations":[],"preferred":false,"id":248942,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":53445,"text":"ofr0240 - 2003 - ERF1_2 -- Enhanced River Reach File 2.0","interactions":[],"lastModifiedDate":"2013-06-04T13:54:08","indexId":"ofr0240","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":330,"text":"Open-File Report","code":"OFR","onlineIssn":"2331-1258","printIssn":"0196-1497","active":true,"publicationSubtype":{"id":5}},"seriesNumber":"2002-40","title":"ERF1_2 -- Enhanced River Reach File 2.0","docAbstract":"The digital segmented network based on watershed boundaries, ERF1_2, includes enhancements to the U.S. Environmental Protection Agency's River Reach File 1 (RF1) (USEPA, 1996; DeWald and others, 1985) to support national and regional-scale surface water-quality modeling.  Alexander and others (1999) developed ERF1, which assessed the hydrologic integrity of the digital reach traces and calculated the mean water time-of-travel in river reaches and reservoirs.  ERF1_2 serves as the foundation for SPARROW (Spatially Referenced Regressions (of nutrient transport) on Watershed) modeling.  Within the context of a Geographic Information System, SPARROW estimates the proportion of watersheds in the conterminous U.S. with outflow concentrations of several nutrients, including total nitrogen and total phosphorus, (Smith, R.A., Schwarz, G.E., and Alexander, R.B., 1997).  This version of the network expands on ERF1 (Version 1.2; Alexander, et al., 1999) and includes the incremental and total drainage area derived from 1-kilometer (km) elevation data for North America.  Previous estimates of the water time-of-travel were recomputed for reaches with water-quality monitoring sites that included two reaches.  The mean flow and velocity estimates for these split reaches are based on previous estimation methods (Alexander et al., 1999) and are unchanged in ERF1_2.  Drainage area calculations provide data used to estimate the contribution of a given nutrient to the outflow.  Data estimates depend on the accuracy of node connectivity.  Reaches split at water-quality or pesticide-monitoring sites indicate the source point for estimating the contribution and transport of nutrients and their loads throughout the watersheds.  The ERF1_2 coverage extends the earlier drainage area founded on the 1-kilometer data for North America (Verdin, 1996; Verdin and Jenson, 1996).  A 1-kilometer raster grid of ERF1_2 projected to Lambert Azimuthal Equal Area, NAD 27 Datum (Snyder, 1987), was merged with the HYDRO1K flow direction data set (Verdin and Jenson, 1996) to generate a DEM-based watershed grid, ERF1_2WS_LG.  The watershed boundaries are maintained in a raster (grid cell) format as well as a vector (polygon) format for subsequent model analysis.  Both the coverage, ERF1_2, and the grid, ERF1_2WS_LG, are available at:  URL:http://water.usgs.gov/lookup/getspatial?erf1_2","language":"English","publisher":"U.S. Geological Survey","publisherLocation":"Reston, VA","doi":"10.3133/ofr0240","usgsCitation":"Nolan, J.V., Brakebill, J.W., Alexander, R.B., and Schwarz, G., 2003, ERF1_2 -- Enhanced River Reach File 2.0 (Version 2.0, November 10, 2003): U.S. Geological Survey Open-File Report 2002-40, Dataset, https://doi.org/10.3133/ofr0240.","productDescription":"Dataset","costCenters":[],"links":[{"id":175238,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"},{"id":5267,"rank":800,"type":{"id":11,"text":"Document"},"url":"https://water.usgs.gov/GIS/metadata/usgswrd/XML/erf1_2.xml"}],"edition":"Version 2.0, November 10, 2003","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4a54e4b07f02db62c32a","contributors":{"authors":[{"text":"Nolan, Jacqueline V.","contributorId":97185,"corporation":false,"usgs":true,"family":"Nolan","given":"Jacqueline","email":"","middleInitial":"V.","affiliations":[],"preferred":false,"id":247614,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Brakebill, John W. 0000-0001-9235-6810 jwbrakeb@usgs.gov","orcid":"https://orcid.org/0000-0001-9235-6810","contributorId":1061,"corporation":false,"usgs":true,"family":"Brakebill","given":"John","email":"jwbrakeb@usgs.gov","middleInitial":"W.","affiliations":[{"id":374,"text":"Maryland Water Science Center","active":true,"usgs":true}],"preferred":true,"id":247613,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Alexander, Richard B. 0000-0001-9166-0626 ralex@usgs.gov","orcid":"https://orcid.org/0000-0001-9166-0626","contributorId":541,"corporation":false,"usgs":true,"family":"Alexander","given":"Richard","email":"ralex@usgs.gov","middleInitial":"B.","affiliations":[{"id":451,"text":"National Water Quality Assessment Program","active":true,"usgs":true},{"id":503,"text":"Office of Water Quality","active":true,"usgs":true}],"preferred":true,"id":247611,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Schwarz, Gregory E. 0000-0002-9239-4566 gschwarz@usgs.gov","orcid":"https://orcid.org/0000-0002-9239-4566","contributorId":543,"corporation":false,"usgs":true,"family":"Schwarz","given":"Gregory E.","email":"gschwarz@usgs.gov","affiliations":[{"id":451,"text":"National Water Quality Assessment Program","active":true,"usgs":true},{"id":5067,"text":"Northeast Regional Director's Office","active":true,"usgs":true}],"preferred":false,"id":247612,"contributorType":{"id":1,"text":"Authors"},"rank":4}]}}
,{"id":53965,"text":"wri034262 - 2003 - Potential for saltwater intrusion into the lower Tamiami aquifer near Bonita Springs, southwestern Florida","interactions":[],"lastModifiedDate":"2023-01-04T22:00:32.384385","indexId":"wri034262","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":342,"text":"Water-Resources Investigations Report","code":"WRI","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"2003-4262","title":"Potential for saltwater intrusion into the lower Tamiami aquifer near Bonita Springs, southwestern Florida","docAbstract":"A study was conducted to examine the potential for saltwater intrusion into the lower Tamiami aquifer beneath Bonita Springs in southwestern Florida. Field data were collected, and constant- and variable-density ground-water flow simulations were performed that: (1) spatially quantified modern and seasonal stresses, (2) identified potential mechanisms of saltwater intrusion, and (3) estimated the potential extent of saltwater intrusion for the area of concern. \r\n\r\nMODFLOW and the inverse modeling routine UCODE were used to spatially quantify modern and seasonal stresses by calibrating a constant-density ground-water flow model to field data collected in 1996. The model was calibrated by assuming hydraulic conductivity parameters were accurate and by estimating unmonitored ground-water pumpage and potential evapotranspiration with UCODE. Uncertainty in these estimated parameters was quantified with 95-percent confidence intervals. These confidence intervals indicate more uncertainty (or less reliability) in the estimates of unmonitored ground-water pumpage than estimates of pan-evaporation multipliers, because of the nature and distribution of observations used during calibration. Comparison of simulated water levels, streamflows, and net recharge with field data suggests the model is a good representation of field conditions. \r\n\r\nPotential mechanisms of saltwater intrusion into the lower Tamiami aquifer include: (1) lateral inland movement of the freshwater-saltwater interface from the southwestern coast of Florida; (2) upward leakage from deeper saline water-bearing zones through natural upwelling and upconing, both of which could occur as diffuse upward flow through semiconfining layers, conduit flow through karst features, or pipe flow through leaky artesian wells; (3) downward leakage of saltwater from surface-water channels; and (4) movement of unflushed pockets of relict seawater. Of the many potential mechanisms of saltwater intrusion, field data and variable-density ground-water flow simulations suggest that upconing is of utmost concern, and lateral encroachment is of second-most concern. This interpretation is uncertain, however, because the predominance of saltwater intrusion through leaky artesian wells with connection to deeper, more saline, and higher pressure aquifers was difficult to establish. \r\n\r\nEffective management of ground-water resources in southwestern Florida requires an understanding of the potential extent of saltwater intrusion in the lower Tamiami aquifer near Bonita Springs. Variable-density, ground-water flow simulations suggest that when saltwater is at dynamic equilibrium with 1996 seasonal stresses, the extent of saltwater intrusion is about 100 square kilometers areally and 70,000 hectare-meters volumetrically. The volumetric extent of saltwater intrusion was most sensitive to changes in recharge, ground-water pumpage, sea level, salinity of the Gulf of Mexico, and the potentiometric surface of the sandstone aquifer, respectively.","language":"English","publisher":"U.S. Geological Survey","doi":"10.3133/wri034262","usgsCitation":"Shoemaker, W., and Edwards, K.M., 2003, Potential for saltwater intrusion into the lower Tamiami aquifer near Bonita Springs, southwestern Florida: U.S. Geological Survey Water-Resources Investigations Report 2003-4262, Report: vi, 74 p.; 2 Plates: 34.00 x 36.00 inches, https://doi.org/10.3133/wri034262.","productDescription":"Report: vi, 74 p.; 2 Plates: 34.00 x 36.00 inches","costCenters":[],"links":[{"id":4908,"rank":2,"type":{"id":15,"text":"Index Page"},"url":"https://fl.water.usgs.gov/Abstracts/wri03_4262_shoemaker.html","linkFileType":{"id":5,"text":"html"}},{"id":177141,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"},{"id":411387,"rank":3,"type":{"id":36,"text":"NGMDB Index Page"},"url":"https://ngmdb.usgs.gov/Prodesc/proddesc_70817.htm","linkFileType":{"id":5,"text":"html"}}],"country":"United States","state":"Florida","city":"Bonita Springs","otherGeospatial":"Lower Tamiami aquifer","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"coordinates\": [\n          [\n            [\n              -82,\n              26.5917\n            ],\n            [\n              -82,\n              26\n            ],\n            [\n              -81.4,\n              26\n            ],\n            [\n              -81.4,\n              26.5917\n            ],\n            [\n              -82,\n              26.5917\n            ]\n          ]\n        ],\n        \"type\": \"Polygon\"\n      }\n    }\n  ]\n}","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4b1ae4b07f02db6a8792","contributors":{"authors":[{"text":"Shoemaker, W. Barclay bshoemak@usgs.gov","contributorId":1495,"corporation":false,"usgs":true,"family":"Shoemaker","given":"W. Barclay","email":"bshoemak@usgs.gov","affiliations":[{"id":156,"text":"Caribbean Water Science Center","active":true,"usgs":true},{"id":269,"text":"FLWSC-Ft. Lauderdale","active":true,"usgs":true}],"preferred":true,"id":248795,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Edwards, K. Michelle","contributorId":27927,"corporation":false,"usgs":true,"family":"Edwards","given":"K.","email":"","middleInitial":"Michelle","affiliations":[],"preferred":false,"id":248796,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":50979,"text":"wri034096 - 2003 - Geohydrologic Framework of Recharge and Seawater Intrusion in the Pajaro Valley, Santa Cruz and Monterey Counties, California","interactions":[],"lastModifiedDate":"2012-02-02T00:11:21","indexId":"wri034096","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":342,"text":"Water-Resources Investigations Report","code":"WRI","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"2003-4096","title":"Geohydrologic Framework of Recharge and Seawater Intrusion in the Pajaro Valley, Santa Cruz and Monterey Counties, California","docAbstract":"Pajaro Valley is a coastal watershed of 160 square miles located along Monterey Bay north of Elkhorn Slough and south of the city of Santa Cruz. The valley has been predominantly developed for agriculture since the late 1800s. In 1984 the Pajaro Valley Water Management Agency (PVWMA) was formed and was delegated with the responsibility of the management of the water resources within the Pajaro Valley by the State of California. About 84 percent of the water is used for agriculture and 16 percent is used for industrial and municipal water supply; almost all of the demand is supplied by ground water. Ground-water pumpage varies with seasonal and climatic periods.\r\n\r\nThe alluvial aquifers are composed of Quaternary- and Tertiary-aged sediments that are layered marine and terrestrial coarse-grained deposits separated by extensive fine-grained deposits that potentially restrict vertical movement of ground water and seawater intrusion in the coastal subareas. The coarse-grained deposits, which persist over large areas, control pumpage and related seawater intrusion. The Aromas Sand crops out throughout the north and central parts of the PVWMA area and offshore on the continental shelf and in Monterey submarine canyon. Because many of the wells in the coastal and inland subregions are screened at depths of 200 to 400 feet below land surface, a direct avenue is provided for seawater intrusion through the coarse-grained deposits of the shallower alluvium and Aromas Sand. Geophysical logs from monitoring wells indicate discrete zones of saline water that are related to pumpage and seawater intrusion in the aquifers of the shallower alluvium and upper Aromas Sand in the upper-aquifer system and to deeper saline waters in the lower Aromas Sand within the lower-aquifer system.\r\n\r\nThe precipitation data indicate that there were at least nine dry and nine wet periods that range from 2 to 19 years during the period of record, 1880?1997. The ground-water pumpage, runoff, streamflow and related water quality of streamflow also vary with seasonal and climatic periods.\r\n\r\nRecharge occurs from deep percolation of precipitation and from infiltration of streamflow. Streamflow originates from local runoff and from outside the valley as inflow from the Pajaro River. Although partly regulated, streamflow in the Pajaro River at Chittenden is less than 200 cubic feet per second 88 percent of the time and is less than 12 cubic feet per second 50 percent of the time. Streamflow water-quality data suggest that there may be several sources of poor-quality water that contribute to elevated chloride, sulfate, and nitrate concentrations in streamflow. The poor water quality occurring during lower streamflows indicates that low flows may be an additional source of salinity for ground-water recharge as streamflow infiltration along the Pajaro River.\r\n\r\nThe geochemical data from this study indicate that the two main sources of recharge are deep percolation of local runoff and streamflow infiltration of Pajaro River water. The geophysical and geochemical data suggest that only the shallow alluvial aquifer and parts of the upper Aromas Sand that constitute the upper-aquifer system are being replenished by recent recharge in the coastal areas of Pajaro Valley and represent the renewable ground-water resources. These data also suggest that there is very little vertical flow through the layered aquifer systems in the coastal regions. The confining aquitards are laterally extensive but may be missing in places owing to fluvial erosion or offsetting by fault movement. Geochemical and geophysical data indicate that the ground water from some parts of the upper and lower Aromas Sand in the coastal regions was recharged thousands of years ago and may, in part, represent nonrenewable ground-water resources. \r\n\r\nThe analysis of major-ion chemistry, in combination with isotope and trace-element/chloride ratios, indicates that the coastal ground-water and surface-water samples ","language":"ENGLISH","doi":"10.3133/wri034096","usgsCitation":"Hanson, R.T., 2003, Geohydrologic Framework of Recharge and Seawater Intrusion in the Pajaro Valley, Santa Cruz and Monterey Counties, California: U.S. Geological Survey Water-Resources Investigations Report 2003-4096, 88 p., https://doi.org/10.3133/wri034096.","productDescription":"88 p.","costCenters":[],"links":[{"id":4417,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.water.usgs.gov/wri034096/","linkFileType":{"id":5,"text":"html"}},{"id":178832,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4b1be4b07f02db6a8f84","contributors":{"authors":[{"text":"Hanson, Randall T. 0000-0002-9819-7141 rthanson@usgs.gov","orcid":"https://orcid.org/0000-0002-9819-7141","contributorId":801,"corporation":false,"usgs":true,"family":"Hanson","given":"Randall","email":"rthanson@usgs.gov","middleInitial":"T.","affiliations":[{"id":154,"text":"California Water Science Center","active":true,"usgs":true}],"preferred":true,"id":242707,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":53186,"text":"wri034130 - 2003 - Simulation of ground-water flow and rainfall runoff with emphasis on the effects of land cover, Whittlesey Creek, Bayfield County, Wisconsin, 1999-2001","interactions":[],"lastModifiedDate":"2015-11-13T13:44:48","indexId":"wri034130","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":342,"text":"Water-Resources Investigations Report","code":"WRI","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"2003-4130","title":"Simulation of ground-water flow and rainfall runoff with emphasis on the effects of land cover, Whittlesey Creek, Bayfield County, Wisconsin, 1999-2001","docAbstract":"<p>The effects of land cover on flooding and base-flow characteristics of Whittlesey Creek, Bayfield County, Wis., were examined in a study that involved ground-water-flow and rainfall-runoff modeling. Field data were collected during 1999-2001 for synoptic base flow, streambed head and temperature, precipitation, continuous streamflow and stream stage, and other physical characteristics. Well logs provided data for potentiometric-surface altitudes and stratigraphic descriptions. Geologic, soil, hydrography, altitude, and historical land-cover data were compiled into a geographic information system and used in two ground-water-flow models (GFLOW and MODFLOW) and a rainfall-runoff model (SWAT). A deep ground-water system intersects Whittlesey Creek near the confluence with the North Fork, producing a steady base flow of 17?18 cubic feet per second. Upstream from the confluence, the creek has little or no base flow; flow is from surface runoff and a small amount of perched ground water. Most of the base flow to Whittlesey Creek originates as recharge through the permeable sands in the center of the Bayfield Peninsula to the northwest of the surface-water-contributing basin. Based on simulations, model-wide changes in recharge caused a proportional change in simulated base flow for Whittlesey Creek. Changing the simulated amount of recharge by 25 to 50 percent in only the ground-water-contributing area results in relatively small changes in base flow to Whittlesey Creek (about 2?11 percent). Simulated changes in land cover within the Whittlesey Creek surface-water-contributing basin would have minimal effects on base flow and average annual runoff, but flood peaks (based on daily mean flows on peak-flow days) could be affected. Based on the simulations, changing the basin land cover to a reforested condition results in a reduction in flood peaks of about 12 to 14 percent for up to a 100-yr flood. Changing the basin land cover to 25 percent urban land or returning basin land cover to the intensive row-crop agriculture of the 1920s results in flood peaks increasing by as much as 18 percent. The SWAT model is limited to a daily time step, which is adequate for describing the surface-water/ground-water interaction and percentage changes. It may not, however, be adequate in describing peak flow because the instantaneous peak flow in Whittlesey Creek during a flood can be more than twice the magnitude of the daily mean flow during that same flood. In addition, the storage and infiltration capacities of wetlands in the basin are not fully understood and need further study.</p>","language":"English","publisher":"U.S. Geological Survey","doi":"10.3133/wri034130","collaboration":"In cooperation with the Bayfield County Land and Water Conservation Department and the U.S. Fish and Wildlife Service","usgsCitation":"Lenz, B.N., Saad, D.A., and Fitzpatrick, F.A., 2003, Simulation of ground-water flow and rainfall runoff with emphasis on the effects of land cover, Whittlesey Creek, Bayfield County, Wisconsin, 1999-2001: U.S. Geological Survey Water-Resources Investigations Report 2003-4130, viii, 47 p., https://doi.org/10.3133/wri034130.","productDescription":"viii, 47 p.","numberOfPages":"56","onlineOnly":"N","additionalOnlineFiles":"N","costCenters":[{"id":677,"text":"Wisconsin Water Science Center","active":true,"usgs":true}],"links":[{"id":173948,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"},{"id":311312,"rank":101,"type":{"id":11,"text":"Document"},"url":"https://pubs.usgs.gov/wri/wrir-03-4130/pdf/wrir03-4130.pdf"},{"id":4782,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.water.usgs.gov/wri034130/","linkFileType":{"id":5,"text":"html"}}],"country":"United States","state":"Wisconsin","county":"Bayfield County","otherGeospatial":"Whittlesey Creek","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"type\": \"Polygon\",\n        \"coordinates\": [\n          [\n            [\n              -88.58722686767578,\n              46.74244865234409\n            ],\n            [\n              -88.58722686767578,\n              46.790892872885806\n            ],\n            [\n              -88.48251342773438,\n              46.790892872885806\n            ],\n            [\n              -88.48251342773438,\n              46.74244865234409\n            ],\n            [\n              -88.58722686767578,\n              46.74244865234409\n            ]\n          ]\n        ]\n      }\n    }\n  ]\n}","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e49f8e4b07f02db5f2b12","contributors":{"authors":[{"text":"Lenz, Bernard N.","contributorId":85170,"corporation":false,"usgs":true,"family":"Lenz","given":"Bernard","email":"","middleInitial":"N.","affiliations":[{"id":595,"text":"U.S. Geological Survey","active":false,"usgs":true}],"preferred":false,"id":246857,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Saad, David A. dasaad@usgs.gov","contributorId":121,"corporation":false,"usgs":true,"family":"Saad","given":"David","email":"dasaad@usgs.gov","middleInitial":"A.","affiliations":[{"id":677,"text":"Wisconsin Water Science Center","active":true,"usgs":true}],"preferred":true,"id":246855,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Fitzpatrick, Faith A. fafitzpa@usgs.gov","contributorId":1182,"corporation":false,"usgs":true,"family":"Fitzpatrick","given":"Faith","email":"fafitzpa@usgs.gov","middleInitial":"A.","affiliations":[{"id":476,"text":"North Carolina Water Science Center","active":true,"usgs":true}],"preferred":false,"id":246856,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
,{"id":50882,"text":"ofr03219 - 2003 - An acoustic doppler current profiler survey of flow velocities in Detroit River, a connecting channel of the Great Lakes","interactions":[],"lastModifiedDate":"2016-10-06T15:19:30","indexId":"ofr03219","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":330,"text":"Open-File Report","code":"OFR","onlineIssn":"2331-1258","printIssn":"0196-1497","active":true,"publicationSubtype":{"id":5}},"seriesNumber":"2003-219","title":"An acoustic doppler current profiler survey of flow velocities in Detroit River, a connecting channel of the Great Lakes","docAbstract":"Acoustic Doppler current profilers (ADCP) were used to survey flow velocities in Detroit River from July 8-19, 2002, as part of a study to assess the susceptibility of public water intakes to contaminants on the St. Clair-Detroit River Waterway. More than 3.5 million point velocities were measured at 130 cross sections. Cross sections were generally spaced about 1,800 ft apart along the river from the head of Detroit River at the outlet of Lake St. Clair to the mouth of Detroit River on Lake Erie. Two transects were surveyed at each cross section, one in each direction across the river. Along each transect, velocity profiles were generally obtained 0.8-2.2 ft apart. At each velocity profile, average water velocity data were obtained at 1.64 ft intervals of depth. The raw position and velocity data from the ADCP field survey were adjusted for local magnetic anomalies using global positioning system (GPS) measurements at the end points of the transects. The adjusted velocity and ancillary data can be retrieved though the internet and extracted to column-oriented data files.","language":"English","publisher":"U.S. Geological Survey","publisherLocation":"Lansing, MI","doi":"10.3133/ofr03219","collaboration":"Prepared in cooperation with the Michigan Department of Environmental Quality, Detroit Water and Sewerage Department, and the American Water Works Association Research Foundation","usgsCitation":"Holtschlag, D.J., and Koschik, J.A., 2003, An acoustic doppler current profiler survey of flow velocities in Detroit River, a connecting channel of the Great Lakes: U.S. Geological Survey Open-File Report 2003-219, Online version, https://doi.org/10.3133/ofr03219.","productDescription":"Online version","costCenters":[{"id":382,"text":"Michigan Water Science Center","active":true,"usgs":true}],"links":[{"id":175364,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"},{"id":4647,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.water.usgs.gov/ofr03219/","linkFileType":{"id":5,"text":"html"}}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4adce4b07f02db68674e","contributors":{"authors":[{"text":"Holtschlag, David J. 0000-0001-5185-4928 dholtschlag@usgs.gov","orcid":"https://orcid.org/0000-0001-5185-4928","contributorId":5447,"corporation":false,"usgs":true,"family":"Holtschlag","given":"David","email":"dholtschlag@usgs.gov","middleInitial":"J.","affiliations":[{"id":382,"text":"Michigan Water Science Center","active":true,"usgs":true}],"preferred":true,"id":242543,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Koschik, John A.","contributorId":24020,"corporation":false,"usgs":true,"family":"Koschik","given":"John","email":"","middleInitial":"A.","affiliations":[],"preferred":false,"id":242544,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":53745,"text":"fs06103 - 2003 - Flooding Associated with Typhoon Chata'an, July 5, 2002, Guam","interactions":[],"lastModifiedDate":"2012-03-08T17:16:16","indexId":"fs06103","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":313,"text":"Fact Sheet","code":"FS","onlineIssn":"2327-6932","printIssn":"2327-6916","active":true,"publicationSubtype":{"id":5}},"seriesNumber":"061-03","title":"Flooding Associated with Typhoon Chata'an, July 5, 2002, Guam","docAbstract":"Introduction\r\n\r\nOn July 5, 2002, starting at about 8 a.m., the southern half of the eye of Typhoon Chata'an passed directly over the northern part of the island of Guam. Data collected on Guam indicate that the typhoon had sustained winds of 85 to 90 miles per hour (mi/hr) with gusts of up to 115 mi/hr (Charles Guard, National Weather Service, written commun., 2003). Storm rainfall totals exceeded 21 inches (in.) over the mountainous areas in south-central Guam. During the peak of the storm, rain fell at rates of up to 6.48 inches per hour (in/hr). Because of the damage caused by Typhoon Chata'an, the President signed a major disaster declaration on July 6, 2002.\r\n\r\nDamages associated with Typhoon Chata'an, while considered moderate relative to other storms that have affected Guam, amounted to several tens of millions of dollars. In excess of 1,000 single-family and multi-family homes were either extensively damaged or destroyed. Electrical power was out for several days over most of the island and no potable water was available through public distribution systems (Federal Emergency Management Agency, 2002). The extreme rainfall led to flooding in southern Guam and caused numerous landslides and severe erosion along water courses. The most significant evidence of these effects could be found in the Fena Valley Reservoir, where elevated sediment concentrations made the water unsuitable for use as a domestic water supply for several days. During normal operation, Fena Valley Reservoir supplies most of the drinking water for the military and some of the general public in southern Guam. All of the stream-gaging stations operated by the U.S. Geological Survey (USGS) on Guam were damaged to some extent during the flood and three of the stations were totally destroyed.\r\n\r\nPeak flows in many rivers in southern Guam reached record levels during Typhoon Chata'an. New record peak stages and/or flows of record occurred at 14 of 15 sites where the USGS has collected data. In some areas, the magnitude of flood peaks exceeded previous records significantly. Peak flows had recurrence intervals of 80 years or more at 9 of the 13 sites where sufficient data were available to make the computations. Four of the 9 sites had recurrence intervals that were determined to be greater than 100 years.\r\n\r\nIn this fact sheet, storm rainfall totals and maximum rainfall totals for durations of 1-, 3-, 6-, and 12-hours are summarized for 12 rain gages on Guam. Peak stages and/or flows were computed at 15 USGS streamflow-gaging stations and recurrence intervals for the peaks determined. Rainfall and streamflow-gaging stations operated by the USGS on Guam are supported by funding provided by numerous agencies including the U.S. Navy, the U.S. Army Corps of Engineers (USACE), and the University of Guam through the Water and Environmental Research Institute (WERI). The USGS Office of Surface Water, as part of a national program to document the effects of extreme floods in the United States, provided funding to support the preparation of this fact sheet.","language":"ENGLISH","publisher":"Geological Survey (U.S.)","doi":"10.3133/fs06103","usgsCitation":"Fontaine, R.A., 2003, Flooding Associated with Typhoon Chata'an, July 5, 2002, Guam: U.S. Geological Survey Fact Sheet 061-03, 4 p., https://doi.org/10.3133/fs06103.","productDescription":"4 p.","costCenters":[{"id":525,"text":"Pacific Islands Water Science Center","active":true,"usgs":true}],"links":[{"id":125767,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/fs_061_03.jpg"},{"id":5146,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.water.usgs.gov/fs-061-03/","linkFileType":{"id":5,"text":"html"}}],"geographicExtents":"{ \"type\": \"FeatureCollection\", \"features\": [ { \"type\": \"Feature\", \"properties\": {}, \"geometry\": { \"type\": \"Polygon\", \"coordinates\": [ [ [ 144.58333333333334,13.25 ], [ 144.58333333333334,13.75 ], [ 145,13.75 ], [ 145,13.25 ], [ 144.58333333333334,13.25 ] ] ] } } ] }","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e49e2e4b07f02db5e4ff8","contributors":{"authors":[{"text":"Fontaine, Richard A. rfontain@usgs.gov","contributorId":2379,"corporation":false,"usgs":true,"family":"Fontaine","given":"Richard","email":"rfontain@usgs.gov","middleInitial":"A.","affiliations":[],"preferred":true,"id":248286,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":44894,"text":"wri024196 - 2003 - Investigation of water quality in the Great Sand Dunes National Monument and Preserve, Saguache County, Colorado, February 1999 through September 2000: Qualifying for outstanding waters designation","interactions":[],"lastModifiedDate":"2012-02-02T00:10:13","indexId":"wri024196","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":342,"text":"Water-Resources Investigations Report","code":"WRI","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"2002-4196","title":"Investigation of water quality in the Great Sand Dunes National Monument and Preserve, Saguache County, Colorado, February 1999 through September 2000: Qualifying for outstanding waters designation","docAbstract":"Great Sand Dunes National Monument and Preserve is located on the eastern side of the San Luis Valley in south-central Colorado. The monument covers 60.4 square miles in Saguache and Alamosa Counties and lies at the base of the Sangre de Cristo Mountains, where a unique combination of climate, topography, and hydrology has created and maintained the Nation?s tallest inland sand dunes. The Sangre de Cristo Mountains, which rise to more than 14,000 feet to the north and east of the dunes, are the source of several streams that flow around the dunes and eventually recharge the aquifer beneath the valley. Sand Creek and Medano Creeks are the largest of the streams in the monument that originate in the Sangre de Cristo Mountains; several ephemeral streams flow into Sand Creek and Medano Creek. Maintaining the high surface-water quality in the Great Sand Dunes National Monument and Preserve is identified as a critical issue by the National Park Service. Additionally, the National Park Service has indicated a desire to pursue an Outstanding Waters Designation, which offers the highest level of water-quality protection available under the Clean Water Act and Colorado regulations. This designation is designed to prevent any degradation from existing conditions (Chatman and others, 1997). Assessment is needed to evaluate whether the water quality of the streams in the monument meets the requirements for an Outstanding Waters Designation. Historically, prospecting and mining activities have occurred in the watersheds of Sand and Medano Creeks; currently, however, there is no mining activity in those watersheds. In addition, the camping and recreation that occur upstream from the monument on national preserve lands and water activities that occur in Medano Creek during the summer are a potential source of human-waste contamination.  Figure 1. Location of study area, sampling sites, and indication of sites that meet or exceed instream standards. The U.S. Geological Survey (USGS), in cooperation with the National Park Service, investigated the water quality at 15 sites (fig. 1) from February 1999 through September 2000 to identify baseline water-quality conditions and to determine if the water met standards to qualify for the Outstanding Waters Designation. This report describes current water-quality conditions in streams in the monument and compares the water-quality data to Colorado instream standards to assist the State of Colorado Water Quality Control Commission in the determination of qualification for Outstanding Waters Designation.","language":"ENGLISH","doi":"10.3133/wri024196","usgsCitation":"Ferguson, S.A., 2003, Investigation of water quality in the Great Sand Dunes National Monument and Preserve, Saguache County, Colorado, February 1999 through September 2000: Qualifying for outstanding waters designation: U.S. Geological Survey Water-Resources Investigations Report 2002-4196, 8 p. : ill., map ; 28 cm., https://doi.org/10.3133/wri024196.","productDescription":"8 p. : ill., map ; 28 cm.","costCenters":[],"links":[{"id":169966,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"},{"id":3787,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.water.usgs.gov/wri024196","linkFileType":{"id":5,"text":"html"}}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4783e4b07f02db483888","contributors":{"authors":[{"text":"Ferguson, Sheryl A.","contributorId":78698,"corporation":false,"usgs":true,"family":"Ferguson","given":"Sheryl","email":"","middleInitial":"A.","affiliations":[],"preferred":false,"id":230631,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":51978,"text":"wri20034207 - 2003 - Evaluation of Streamflow, Water Quality, and Permitted and Nonpermitted Loads and Yields in the Raritan River Basin, New Jersey, Water Years 1991-98","interactions":[],"lastModifiedDate":"2012-03-08T17:16:17","indexId":"wri20034207","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":342,"text":"Water-Resources Investigations Report","code":"WRI","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"2003-4207","title":"Evaluation of Streamflow, Water Quality, and Permitted and Nonpermitted Loads and Yields in the Raritan River Basin, New Jersey, Water Years 1991-98","docAbstract":"Seventeen water-quality constituents were analyzed in samples collected from 21 surface-water sampling sites in the Raritan River Basin during water years 1991-97. Loads were computed for seven constituents. Thirteen constituents have associated instream water-quality standards that are used as reference levels when evaluating the data. Nine of the 13 constituents did not meet water-quality reference levels in all samples at all sites. The constituents that most commonly failed to meet the water-quality reference levels in the 801 samples analyzed were total phosphorus (greater than 0.1 mg/L (milligrams per liter) in 32 percent of samples), fecal coliform bacteria (greater than 400 counts/100 milliliters in 29 percent), hardness (less than 50 mg/L in 21 percent), pH (greater than 8.5 or less than 6.5 in 17 percent), and water temperature in designated trout waters (greater than 20 degrees Celsius in 12 percent of samples). Concentrations of chloride, total dissolved solids, nitrate plus nitrite, and sulfate did not exceed water-quality reference levels in any sample. Results from previous studies on pesticides and volatile organic compounds in streamwater during 1996-98, and organic compounds and trace elements in sediments during 1976-93, were summarized for this study. Concentrations of pesticides in some samples exceeded the relevant standards. \r\n\r\nWater-quality data varied significantly as season and streamflow changed. Concentrations or values of 12 constituents were significantly higher in the growing season than in the nongrowing season at 1 to 21 sites, and concentrations of 6 constituents were significantly higher in the nongrowing season at 1 to 21 sites. Concentrations or values of seven constituents decreased significantly with increased streamflow, indicating a more significant contribution from base flow or permitted sources than from runoff. Concentrations or values of four constituents increased with increased flow, indicating a more significant contribution from runoff than from base flow or permitted sources. Phosphorus concentrations increased with flow at two sites with no point sources and decreased with flow at five sites with four or more permitted point sources. Concentrations of five constituents did not vary significantly with changes in streamflow at any of the sites. \r\n\r\nConcentrations of constituents differed significantly between sites. The sites with the most desirable values for the most constituents were Mulhockaway Creek, Spruce Run, Millstone River at Manalapan, Manalapan Brook, and Lamington River at Pottersville. The sites with the least desirable values for the most constituents were Millstone River at Blackwells Mills, Matchaponix Brook, Raritan River at Bound Brook, Neshanic River, and Millstone River at Grovers Mill. \r\n\r\nThe total instream loads of seven constituents - total ammonia plus organic nitrogen (TKN), biochemical oxygen demand (BOD), total dissolved solids (TDS), nitrate plus nitrite (NO3+NO2), total organic carbon (TOC), total phosphorus, and total suspended solids (TSS) - were analyzed at low, median, and high flows. The quantities of total instream load that originated from facilities with permits issued by the New Jersey Department of Environmental Protection to discharge effluent to streams (permitted sources) and from other sources (nonpermitted sources) were estimated for each sampling site. TOC and TSS loads primarily were contributed by nonpermitted sources at all flows. BOD and TDS loads primarily were contributed by nonpermitted sources at median and high flows. At low flow, permitted sources contributed more than one-third of the TDS load at 10 sites and more than one-third of the BOD load at 3 sites. Permitted sources contributed more than one-third of the total phosphorus load at 15 and 14 sites at low and median flows, respectively. Permitted sources accounted for more than one-third of total instream load of NO3+NO2 at low- and median-flow conditions at nearly ","language":"ENGLISH","publisher":"U.S. Geological Survey","doi":"10.3133/wri20034207","collaboration":"Prepared in cooperation with the New Jersey Water Supply Authority","usgsCitation":"Reiser, R.G., 2003, Evaluation of Streamflow, Water Quality, and Permitted and Nonpermitted Loads and Yields in the Raritan River Basin, New Jersey, Water Years 1991-98: U.S. Geological Survey Water-Resources Investigations Report 2003-4207, xii, 210 p., https://doi.org/10.3133/wri20034207.","productDescription":"xii, 210 p.","additionalOnlineFiles":"Y","temporalStart":"1990-10-01","temporalEnd":"1997-09-30","costCenters":[{"id":470,"text":"New Jersey Water Science Center","active":true,"usgs":true}],"links":[{"id":178877,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"},{"id":12679,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.usgs.gov/wri/wri03-4207/","linkFileType":{"id":5,"text":"html"}}],"geographicExtents":"{ \"type\": \"FeatureCollection\", \"features\": [ { \"type\": \"Feature\", \"properties\": {}, \"geometry\": { \"type\": \"Polygon\", \"coordinates\": [ [ [ -75.16666666666667,40 ], [ -75.16666666666667,41 ], [ -74,41 ], [ -74,40 ], [ -75.16666666666667,40 ] ] ] } } ] }","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4a04e4b07f02db5f8626","contributors":{"authors":[{"text":"Reiser, Robert G. 0000-0001-5140-2745 rreiser@usgs.gov","orcid":"https://orcid.org/0000-0001-5140-2745","contributorId":4083,"corporation":false,"usgs":true,"family":"Reiser","given":"Robert","email":"rreiser@usgs.gov","middleInitial":"G.","affiliations":[{"id":470,"text":"New Jersey Water Science Center","active":true,"usgs":true}],"preferred":true,"id":244594,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":53165,"text":"fs07103 - 2003 - Shuttle Radar Topography Mission (SRTM)","interactions":[],"lastModifiedDate":"2012-03-16T17:16:06","indexId":"fs07103","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":313,"text":"Fact Sheet","code":"FS","onlineIssn":"2327-6932","printIssn":"2327-6916","active":true,"publicationSubtype":{"id":5}},"seriesNumber":"071-03","title":"Shuttle Radar Topography Mission (SRTM)","docAbstract":"Under an agreement with the National Aeronautics and Space Administration (NASA) and the Department of Defense's National Imagery and Mapping Agency (NIMA), the U.S. Geological Survey (USGS) is now distributing elevation data from the Shuttle Radar Topography Mission (SRTM). The SRTM is a joint project between NASA and NIMA to map the Earth's land surface in three dimensions at a level of detail unprecedented for such a large area. Flown aboard the NASA Space Shuttle Endeavour February 11-22, 2000, the SRTM successfully collected data over 80 percent of the Earth's land surface, for most of the area between 60? N. and 56? S. latitude. The SRTM hardware included the Spaceborne Imaging Radar-C (SIR-C) and X-band Synthetic Aperture Radar (X-SAR) systems that had flown twice previously on other space shuttle missions. The SRTM data were collected specifically with a technique known as interferometry that allows image data from dual radar antennas to be processed for the extraction of ground heights.","language":"ENGLISH","publisher":"U.S. Geological Survey","publisherLocation":"Reston, VA","doi":"10.3133/fs07103","usgsCitation":"Water Resources Division, U.S. Geological Survey, 2003, Shuttle Radar Topography Mission (SRTM): U.S. Geological Survey Fact Sheet 071-03, 2 p., https://doi.org/10.3133/fs07103.","productDescription":"2 p.","costCenters":[{"id":222,"text":"Earth Resources Observation and Science (EROS) Center","active":true,"usgs":true}],"links":[{"id":126430,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/fs/2003/0071/report-thumb.jpg"},{"id":87124,"rank":300,"type":{"id":11,"text":"Document"},"url":"https://pubs.usgs.gov/fs/2003/0071/report.pdf","linkFileType":{"id":1,"text":"pdf"}}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4b06e4b07f02db69a0fb","contributors":{"authors":[{"text":"Water Resources Division, U.S. Geological Survey","contributorId":128075,"corporation":true,"usgs":false,"organization":"Water Resources Division, U.S. Geological Survey","id":532170,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":53716,"text":"ofr03500 - 2003 - Using Logistic Regression To Predict the Probability of Debris Flows Occurring in Areas Recently Burned By Wildland Fires","interactions":[],"lastModifiedDate":"2012-02-02T00:11:35","indexId":"ofr03500","displayToPublicDate":"1994-01-01T00:00:00","publicationYear":"2003","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":330,"text":"Open-File Report","code":"OFR","onlineIssn":"2331-1258","printIssn":"0196-1497","active":true,"publicationSubtype":{"id":5}},"seriesNumber":"2003-500","title":"Using Logistic Regression To Predict the Probability of Debris Flows Occurring in Areas Recently Burned By Wildland Fires","docAbstract":"Logistic regression was used to predict the probability of debris flows occurring in areas recently burned by wildland fires. Multiple logistic regression is conceptually similar to multiple linear regression because statistical relations between one dependent variable and several independent variables are evaluated. In logistic regression, however, the dependent variable is transformed to a binary variable (debris flow did or did not occur), and the actual probability of the debris flow occurring is statistically modeled. Data from 399 basins located within 15 wildland fires that burned during 2000-2002 in Colorado, Idaho, Montana, and New Mexico were evaluated. More than 35 independent variables describing the burn severity, geology, land surface gradient, rainfall, and soil properties were evaluated. The models were developed as follows: (1) Basins that did and did not produce debris flows were delineated from National Elevation Data using a Geographic Information System (GIS). (2) Data describing the burn severity, geology, land surface gradient, rainfall, and soil properties were determined for each basin. These data were then downloaded to a statistics software package for analysis using logistic regression. (3) Relations between the occurrence/non-occurrence of debris flows and burn severity, geology, land surface gradient, rainfall, and soil properties were evaluated and several preliminary multivariate logistic regression models were constructed. All possible combinations of independent variables were evaluated to determine which combination produced the most effective model. The multivariate model that best predicted the occurrence of debris flows was selected. (4) The multivariate logistic regression model was entered into a GIS, and a map showing the probability of debris flows was constructed. The most effective model incorporates the percentage of each basin with slope greater than 30 percent, percentage of land burned at medium and high burn severity in each basin, particle size sorting, average storm intensity (millimeters per hour), soil organic matter content, soil permeability, and soil drainage. The results of this study demonstrate that logistic regression is a valuable tool for predicting the probability of debris flows occurring in recently-burned landscapes.","language":"ENGLISH","doi":"10.3133/ofr03500","usgsCitation":"Rupert, M.G., Cannon, S.H., and Gartner, J.E., 2003, Using Logistic Regression To Predict the Probability of Debris Flows Occurring in Areas Recently Burned By Wildland Fires: U.S. Geological Survey Open-File Report 2003-500, 1 over-sized sheet, 60 by 35 inches, https://doi.org/10.3133/ofr03500.","productDescription":"1 over-sized sheet, 60 by 35 inches","costCenters":[],"links":[{"id":177178,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"},{"id":5058,"rank":100,"type":{"id":15,"text":"Index Page"},"url":"https://pubs.usgs.gov/of/2003/ofr03500/","linkFileType":{"id":5,"text":"html"}}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4aaae4b07f02db669344","contributors":{"authors":[{"text":"Rupert, Michael G. mgrupert@usgs.gov","contributorId":1194,"corporation":false,"usgs":true,"family":"Rupert","given":"Michael","email":"mgrupert@usgs.gov","middleInitial":"G.","affiliations":[{"id":191,"text":"Colorado Water Science Center","active":true,"usgs":true}],"preferred":true,"id":248205,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Cannon, Susan H. cannon@usgs.gov","contributorId":1019,"corporation":false,"usgs":true,"family":"Cannon","given":"Susan","email":"cannon@usgs.gov","middleInitial":"H.","affiliations":[{"id":300,"text":"Geologic Hazards Science Center","active":true,"usgs":true}],"preferred":true,"id":248204,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Gartner, Joseph E. jegartner@usgs.gov","contributorId":1876,"corporation":false,"usgs":true,"family":"Gartner","given":"Joseph","email":"jegartner@usgs.gov","middleInitial":"E.","affiliations":[{"id":300,"text":"Geologic Hazards Science Center","active":true,"usgs":true}],"preferred":true,"id":248206,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
]}