{"pageNumber":"360","pageRowStart":"8975","pageSize":"25","recordCount":16506,"records":[{"id":70023115,"text":"70023115 - 2000 - Influence of net freshwater supply on salinity in Florida Bay","interactions":[],"lastModifiedDate":"2018-03-27T16:37:06","indexId":"70023115","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":3722,"text":"Water Resources Research","onlineIssn":"1944-7973","printIssn":"0043-1397","active":true,"publicationSubtype":{"id":10}},"title":"Influence of net freshwater supply on salinity in Florida Bay","docAbstract":"<div class=\"article-section__content n/a main\"><p>An annual water budget for Florida Bay, the large, seasonally hypersaline estuary in the Everglades National Park, was constructed using physically based models and long‐term (31 years) data on salinity, hydrology, and climate. Effects of seasonal and interannual variations of the net freshwater supply (runoff plus rainfall minus evaporation) on salinity variation within the bay were also examined. Particular attention was paid to the effects of runoff, which are the focus of ambitious plans to restore and conserve the Florida Bay ecosystem. From 1965 to 1995 the annual runoff from the Everglades into the bay was less than one tenth of the annual direct rainfall onto the bay, while estimated annual evaporation slightly exceeded annual rainfall. The average net freshwater supply to the bay over a year was thus approximately zero, and interannual variations in salinity appeared to be affected primarily by interannual fluctuations in rainfall. At the annual scale, runoff apparently had little effect on the bay as a whole during this period. On a seasonal basis, variations in rainfall, evaporation, and runoff were not in phase, and the net freshwater supply to the bay varied between positive and negative values, contributing to a strong seasonal pattern in salinity, especially in regions of the bay relatively isolated from exchanges with the Gulf of Mexico and Atlantic Ocean. Changes in runoff could have a greater effect on salinity in the bay if the seasonal patterns of rainfall and evaporation and the timing of the runoff are considered. One model was also used to simulate spatial and temporal patterns of salinity responses expected to result from changes in net freshwater supply. Simulations in which runoff was increased by a factor of 2 (but with no change in spatial pattern) indicated that increased runoff will lower salinity values in eastern Florida Bay, increase the variability of salinity in the South Region, but have little effect on salinity in the Central and West Regions.</p></div>","language":"English","publisher":"American Geophysical Union","doi":"10.1029/1999WR900352","usgsCitation":"Nuttle, W.K., Fourqurean, J.W., Cosby, B.J., Zieman, J.C., and Robblee, M.B., 2000, Influence of net freshwater supply on salinity in Florida Bay: Water Resources Research, v. 36, no. 7, p. 1805-1822, https://doi.org/10.1029/1999WR900352.","productDescription":"18 p.","startPage":"1805","endPage":"1822","costCenters":[],"links":[{"id":487447,"rank":1,"type":{"id":40,"text":"Open Access Publisher Index Page"},"url":"https://doi.org/10.1029/1999wr900352","text":"Publisher Index Page"},{"id":233809,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"Florida","otherGeospatial":"Florida Bay","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"type\": \"Polygon\",\n        \"coordinates\": [\n          [\n            [\n              -82.232666015625,\n              24.206889622398023\n            ],\n            [\n              -80.04089355468749,\n              24.206889622398023\n            ],\n            [\n              -80.04089355468749,\n              26.13571361317392\n            ],\n            [\n              -82.232666015625,\n              26.13571361317392\n            ],\n            [\n              -82.232666015625,\n              24.206889622398023\n            ]\n          ]\n        ]\n      }\n    }\n  ]\n}","volume":"36","issue":"7","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505a3b5ee4b0c8380cd6247d","contributors":{"authors":[{"text":"Nuttle, William K.","contributorId":189603,"corporation":false,"usgs":false,"family":"Nuttle","given":"William","email":"","middleInitial":"K.","affiliations":[],"preferred":false,"id":396218,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Fourqurean, James W.","contributorId":84491,"corporation":false,"usgs":true,"family":"Fourqurean","given":"James","email":"","middleInitial":"W.","affiliations":[],"preferred":false,"id":396217,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Cosby, Bernard J.","contributorId":107578,"corporation":false,"usgs":true,"family":"Cosby","given":"Bernard","email":"","middleInitial":"J.","affiliations":[],"preferred":false,"id":396219,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Zieman, Joseph C.","contributorId":20806,"corporation":false,"usgs":true,"family":"Zieman","given":"Joseph","email":"","middleInitial":"C.","affiliations":[],"preferred":false,"id":396215,"contributorType":{"id":1,"text":"Authors"},"rank":4},{"text":"Robblee, Michael B. mike_robblee@usgs.gov","contributorId":3865,"corporation":false,"usgs":true,"family":"Robblee","given":"Michael","email":"mike_robblee@usgs.gov","middleInitial":"B.","affiliations":[],"preferred":true,"id":396216,"contributorType":{"id":1,"text":"Authors"},"rank":5}]}}
,{"id":70023114,"text":"70023114 - 2000 - Attenuation-difference radar tomography: Results of a multiple-plane experiment at the U.S. Geological Survey Fractured-Rock Research Site, Mirror Lake, New Hampshire","interactions":[],"lastModifiedDate":"2019-10-16T06:32:28","indexId":"70023114","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":24,"text":"Conference Paper"},"publicationSubtype":{"id":19,"text":"Conference Paper"},"title":"Attenuation-difference radar tomography: Results of a multiple-plane experiment at the U.S. Geological Survey Fractured-Rock Research Site, Mirror Lake, New Hampshire","docAbstract":"Attenuation-difference, borehole-radar tomography was used to monitor a series of sodium chloride tracer injection tests conducted within the FSE, wellfield at the U.S. Geological Survey Fractured-Rock Hydrology Research Site in Grafton County, New Hampshire, USA. Borehole-radar tomography surveys were conducted using the sequential-scanning and injection method in three boreholes that form a triangular prism of adjoining tomographic image planes. Results indicate that time-lapse tomography methods provide high-resolution images of tracer distribution in permeable zones.","largerWorkTitle":"Proceedings of SPIE - The International Society for Optical Engineering","conferenceTitle":"GPR 2000: The 8th International Conference on Ground Penetrating Radar","conferenceDate":"May 23-26, 2000","conferenceLocation":"Goldcoast, Aust","language":"English","publisher":"Society of Photo-Optical Instrumentation Engineers","publisherLocation":"Bellingham, WA","issn":"0277786X","usgsCitation":"Lane, J., Day-Lewis, F., Harris, J., Haeni, F., and Gorelick, S., 2000, Attenuation-difference radar tomography: Results of a multiple-plane experiment at the U.S. Geological Survey Fractured-Rock Research Site, Mirror Lake, New Hampshire, <i>in</i> Proceedings of SPIE - The International Society for Optical Engineering, v. 4084, Goldcoast, Aust, May 23-26, 2000, p. 666-675.","productDescription":"10 p.","startPage":"666","endPage":"675","numberOfPages":"10","costCenters":[{"id":493,"text":"Office of Ground Water","active":true,"usgs":true}],"links":[{"id":233771,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"New Hampshire","county":"Carroll County","otherGeospatial":"Fractured Rock Research Site, Mirror Lake","geographicExtents":"{\"type\":\"FeatureCollection\",\"features\":[{\"type\":\"Feature\",\"geometry\":{\"type\":\"Polygon\",\"coordinates\":[[[-71.0103,44.2845],[-71.0095,44.2683],[-71.0086,44.2553],[-71.0079,44.2451],[-71.0071,44.2226],[-71.0065,44.2074],[-71.0027,44.1122],[-71.0027,44.1103],[-70.9978,44.0251],[-70.9944,43.9723],[-70.988,43.828],[-70.9862,43.793],[-70.9862,43.7924],[-70.9809,43.6903],[-70.9757,43.592],[-70.9743,43.5724],[-70.9689,43.5683],[-70.9633,43.5642],[-70.9588,43.5598],[-70.9557,43.556],[-70.9541,43.5521],[-70.9533,43.5496],[-70.9533,43.5482],[-70.9533,43.5459],[-70.9533,43.5441],[-70.954,43.5432],[-70.9559,43.5428],[-70.959,43.5419],[-70.9614,43.5402],[-70.9617,43.5397],[-70.9629,43.5386],[-71.0245,43.4825],[-71.0374,43.5294],[-71.0437,43.5244],[-71.0462,43.5294],[-71.052,43.5245],[-71.0557,43.5276],[-71.0627,43.524],[-71.0671,43.5268],[-71.0849,43.5064],[-71.0893,43.5123],[-71.0931,43.5068],[-71.0969,43.5114],[-71.1019,43.5073],[-71.1063,43.5123],[-71.112,43.5069],[-71.1281,43.5725],[-71.1636,43.5389],[-71.197,43.5576],[-71.1976,43.5581],[-71.2001,43.559],[-71.204,43.5526],[-71.209,43.5508],[-71.2279,43.565],[-71.2614,43.5719],[-71.3314,43.6193],[-71.3339,43.6193],[-71.3408,43.6266],[-71.4603,43.7096],[-71.4641,43.7118],[-71.4824,43.726],[-71.4856,43.7278],[-71.5318,43.7606],[-71.5375,43.7947],[-71.5382,43.7961],[-71.5439,43.7961],[-71.5521,43.8352],[-71.556,43.8516],[-71.5572,43.8571],[-71.5649,43.8926],[-71.5408,43.8949],[-71.4627,43.9031],[-71.4583,43.9035],[-71.4519,43.9045],[-71.4176,43.9085],[-71.37,43.9144],[-71.3624,43.9153],[-71.3662,43.9358],[-71.3693,43.95],[-71.3832,44.0219],[-71.3468,44.0688],[-71.3665,44.0688],[-71.3818,44.0976],[-71.3767,44.1035],[-71.376,44.119],[-71.3849,44.145],[-71.388,44.155],[-71.4129,44.1659],[-71.4256,44.2106],[-71.4154,44.212],[-71.3949,44.2151],[-71.3867,44.1878],[-71.3842,44.1796],[-71.3561,44.1673],[-71.3511,44.1499],[-71.3435,44.1217],[-71.348,44.0948],[-71.3372,44.0848],[-71.3345,44.086],[-71.3238,44.0911],[-71.3124,44.0911],[-71.3117,44.0943],[-71.3046,44.1248],[-71.3033,44.1357],[-71.3033,44.1367],[-71.3065,44.1367],[-71.2963,44.1567],[-71.2834,44.1831],[-71.2642,44.2218],[-71.2526,44.2441],[-71.0977,44.2346],[-71.0715,44.2373],[-71.0428,44.2372],[-71.0425,44.2746],[-71.0444,44.2832],[-71.0103,44.2845]]]},\"properties\":{\"name\":\"Carroll\",\"state\":\"NH\"}}]}","volume":"4084","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"5059eed3e4b0c8380cd49fbf","contributors":{"authors":[{"text":"Lane, J.W. Jr.","contributorId":66723,"corporation":false,"usgs":true,"family":"Lane","given":"J.W.","suffix":"Jr.","email":"","affiliations":[],"preferred":false,"id":396213,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Day-Lewis, F. D. 0000-0003-3526-886X","orcid":"https://orcid.org/0000-0003-3526-886X","contributorId":35773,"corporation":false,"usgs":true,"family":"Day-Lewis","given":"F. D.","affiliations":[],"preferred":false,"id":396211,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Harris, J.M.","contributorId":42751,"corporation":false,"usgs":true,"family":"Harris","given":"J.M.","email":"","affiliations":[],"preferred":false,"id":396212,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Haeni, F.P.","contributorId":87105,"corporation":false,"usgs":true,"family":"Haeni","given":"F.P.","affiliations":[],"preferred":false,"id":396214,"contributorType":{"id":1,"text":"Authors"},"rank":4},{"text":"Gorelick, S.M.","contributorId":21589,"corporation":false,"usgs":true,"family":"Gorelick","given":"S.M.","email":"","affiliations":[],"preferred":false,"id":396210,"contributorType":{"id":1,"text":"Authors"},"rank":5}]}}
,{"id":70023111,"text":"70023111 - 2000 - Characterizing multiple timescales of stream and storage zone interaction that affect solute fate and transport in streams","interactions":[],"lastModifiedDate":"2018-12-10T08:53:37","indexId":"70023111","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":3722,"text":"Water Resources Research","onlineIssn":"1944-7973","printIssn":"0043-1397","active":true,"publicationSubtype":{"id":10}},"title":"Characterizing multiple timescales of stream and storage zone interaction that affect solute fate and transport in streams","docAbstract":"<p><span>The fate of contaminants in streams and rivers is affected by exchange and biogeochemical transformation in slowly moving or stagnant flow zones that interact with rapid flow in the main channel. In a typical stream, there are multiple types of slowly moving flow zones in which exchange and transformation occur, such as stagnant or recirculating surface water as well as subsurface hyporheic zones. However, most investigators use transport models with just a single storage zone in their modeling studies, which assumes that the effects of multiple storage zones can be lumped together. Our study addressed the following question: Can a single‐storage zone model reliably characterize the effects of physical retention and biogeochemical reactions in multiple storage zones? We extended an existing stream transport model with a single storage zone to include a second storage zone. With the extended model we generated 500 data sets representing transport of nonreactive and reactive solutes in stream systems that have two different types of storage zones with variable hydrologic conditions. The one storage zone model was tested by optimizing the lumped storage parameters to achieve a best fit for each of the generated data sets. Multiple storage processes were categorized as possessing I, additive; II, competitive; or III, dominant storage zone characteristics. The classification was based on the goodness of fit of generated data sets, the degree of similarity in mean retention time of the two storage zones, and the relative distributions of exchange flux and storage capacity between the two storage zones. For most cases (&gt;90%) the one storage zone model described either the effect of the sum of multiple storage processes (category I) or the dominant storage process (category III). Failure of the one storage zone model occurred mainly for category II, that is, when one of the storage zones had a much longer mean retention time (</span><i>t<sub>s</sub></i><span><span>&nbsp;</span>ratio &gt; 5.0) and when the dominance of storage capacity and exchange flux occurred in different storage zones. We also used the one storage zone model to estimate a “single” lumped rate constant representing the net removal of a solute by biogeochemical reactions in multiple storage zones. For most cases the lumped rate constant that was optimized by one storage zone modeling estimated the flux‐weighted rate constant for multiple storage zones. Our results explain how the relative hydrologic properties of multiple storage zones (retention time, storage capacity, exchange flux, and biogeochemical reaction rate constant) affect the reliability of lumped parameters determined by a one storage zone transport model. We conclude that stream transport models with a single storage compartment will in most cases reliably characterize the dominant physical processes of solute retention and biogeochemical reactions in streams with multiple storage zones.</span></p>","language":"English","publisher":"American Geophysical Union","doi":"10.1029/2000WR900051","usgsCitation":"Choi, J., Harvey, J.W., and Conklin, M.H., 2000, Characterizing multiple timescales of stream and storage zone interaction that affect solute fate and transport in streams: Water Resources Research, v. 36, no. 6, p. 1511-1518, https://doi.org/10.1029/2000WR900051.","productDescription":"8 p.","startPage":"1511","endPage":"1518","costCenters":[{"id":589,"text":"Toxic Substances Hydrology Program","active":true,"usgs":true}],"links":[{"id":479285,"rank":1,"type":{"id":40,"text":"Open Access Publisher Index Page"},"url":"https://doi.org/10.1029/2000wr900051","text":"Publisher Index Page"},{"id":233735,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"36","issue":"6","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"5059f500e4b0c8380cd4c02a","contributors":{"authors":[{"text":"Choi, Jungyill","contributorId":70792,"corporation":false,"usgs":true,"family":"Choi","given":"Jungyill","email":"","affiliations":[],"preferred":false,"id":396203,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Harvey, Judson W. 0000-0002-2654-9873 jwharvey@usgs.gov","orcid":"https://orcid.org/0000-0002-2654-9873","contributorId":1796,"corporation":false,"usgs":true,"family":"Harvey","given":"Judson","email":"jwharvey@usgs.gov","middleInitial":"W.","affiliations":[{"id":436,"text":"National Research Program - Eastern Branch","active":true,"usgs":true}],"preferred":true,"id":396202,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Conklin, Martha H.","contributorId":189395,"corporation":false,"usgs":false,"family":"Conklin","given":"Martha","email":"","middleInitial":"H.","affiliations":[],"preferred":false,"id":396204,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
,{"id":70023103,"text":"70023103 - 2000 - Metal exposure in a benthic macroinvertebrate, Hydropsyche californica, related to mine drainage in the Sacramento River","interactions":[],"lastModifiedDate":"2018-12-07T05:51:27","indexId":"70023103","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":1169,"text":"Canadian Journal of Fisheries and Aquatic Sciences","active":true,"publicationSubtype":{"id":10}},"displayTitle":"Metal exposure in a benthic macroinvertebrate, <i>Hydropsyche californica</i>, related to mine drainage in the Sacramento River","title":"Metal exposure in a benthic macroinvertebrate, Hydropsyche californica, related to mine drainage in the Sacramento River","docAbstract":"<p><span>A biomonitoring technique was employed to complement studies of metal transport in the upper Sacramento River affected by acid mine drainage. Metals (Al, Cd, Cu, Fe, Hg, Pb, and Zn) were determined in a resident invertebrate,&nbsp;</span><i>Hydropsyche californica</i><span><span>&nbsp;</span>(Insecta: Trichoptera), and streambed sediments (&lt;62 µm) to assess metal contamination within a 111-km section of the river downstream of the mining area. Metals in<span>&nbsp;</span></span><i>H. californica</i><span><span>&nbsp;</span>also were interpreted to be broadly indicative of metal exposure in fish. Total Hg was determined in the whole body of the insect, whereas Al, Cd, Cu, Fe, Pb, and Zn were additionally separated into operationally defined cytosolic (used as an indicator of exposure to bioavailable metal) and particulate fractions. Total concentrations of Cd, Cu, Hg, Pb, and Zn in sediments were consistent with documented upstream sources of acid mine drainage. Metal distribution patterns in<span>&nbsp;</span></span><i>H. californica</i><span><span>&nbsp;</span>and sediments were generally consistent for Cd, Cu, and Pb but inconsistent for Hg and Zn. Concentrations in<span>&nbsp;</span></span><i>H. californica</i><span><span>&nbsp;</span>indicated that bioavailable Cd, Cu, Pb, and Zn was transported at least 120 km downstream of the mine sources. Zinc in<span>&nbsp;</span></span><i>H. californica</i><span><span>&nbsp;</span>was elevated, but unlike sediments, did not decrease downstream. Mercury in<span>&nbsp;</span></span><i>H. californica</i><span><span>&nbsp;</span>was not elevated.</span></p>","language":"English","publisher":"NRC Research Press","doi":"10.1139/f99-260","usgsCitation":"Cain, D.J., Carter, J.L., Fend, S.V., Luoma, S.N., Alpers, C.N., and Taylor, H.E., 2000, Metal exposure in a benthic macroinvertebrate, Hydropsyche californica, related to mine drainage in the Sacramento River: Canadian Journal of Fisheries and Aquatic Sciences, v. 57, no. 2, p. 380-390, https://doi.org/10.1139/f99-260.","productDescription":"11 p.","startPage":"380","endPage":"390","costCenters":[{"id":154,"text":"California Water Science Center","active":true,"usgs":true},{"id":438,"text":"National Research Program - Western Branch","active":true,"usgs":true},{"id":589,"text":"Toxic Substances Hydrology Program","active":true,"usgs":true},{"id":5044,"text":"National Research Program - Central Branch","active":true,"usgs":true}],"links":[{"id":233625,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"California","otherGeospatial":"Sacramento River","volume":"57","issue":"2","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505a547de4b0c8380cd6cfbf","contributors":{"authors":[{"text":"Cain, Daniel J. 0000-0002-3443-0493 djcain@usgs.gov","orcid":"https://orcid.org/0000-0002-3443-0493","contributorId":1784,"corporation":false,"usgs":true,"family":"Cain","given":"Daniel","email":"djcain@usgs.gov","middleInitial":"J.","affiliations":[{"id":438,"text":"National Research Program - Western Branch","active":true,"usgs":true},{"id":37277,"text":"WMA - Earth System Processes Division","active":true,"usgs":true}],"preferred":true,"id":396177,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Carter, James L. 0000-0002-0104-9776 jlcarter@usgs.gov","orcid":"https://orcid.org/0000-0002-0104-9776","contributorId":3278,"corporation":false,"usgs":true,"family":"Carter","given":"James","email":"jlcarter@usgs.gov","middleInitial":"L.","affiliations":[{"id":438,"text":"National Research Program - Western Branch","active":true,"usgs":true}],"preferred":true,"id":396175,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Fend, Steven V. 0000-0002-4638-6602 svfend@usgs.gov","orcid":"https://orcid.org/0000-0002-4638-6602","contributorId":3591,"corporation":false,"usgs":true,"family":"Fend","given":"Steven","email":"svfend@usgs.gov","middleInitial":"V.","affiliations":[{"id":438,"text":"National Research Program - Western Branch","active":true,"usgs":true}],"preferred":true,"id":396179,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Luoma, Samuel N. 0000-0001-5443-5091 snluoma@usgs.gov","orcid":"https://orcid.org/0000-0001-5443-5091","contributorId":2287,"corporation":false,"usgs":true,"family":"Luoma","given":"Samuel","email":"snluoma@usgs.gov","middleInitial":"N.","affiliations":[{"id":438,"text":"National Research Program - Western Branch","active":true,"usgs":true}],"preferred":true,"id":396178,"contributorType":{"id":1,"text":"Authors"},"rank":4},{"text":"Alpers, Charles N. 0000-0001-6945-7365 cnalpers@usgs.gov","orcid":"https://orcid.org/0000-0001-6945-7365","contributorId":411,"corporation":false,"usgs":true,"family":"Alpers","given":"Charles","email":"cnalpers@usgs.gov","middleInitial":"N.","affiliations":[{"id":154,"text":"California Water Science Center","active":true,"usgs":true}],"preferred":true,"id":396180,"contributorType":{"id":1,"text":"Authors"},"rank":5},{"text":"Taylor, Howard E. hetaylor@usgs.gov","contributorId":1551,"corporation":false,"usgs":true,"family":"Taylor","given":"Howard","email":"hetaylor@usgs.gov","middleInitial":"E.","affiliations":[{"id":5044,"text":"National Research Program - Central Branch","active":true,"usgs":true}],"preferred":true,"id":396176,"contributorType":{"id":1,"text":"Authors"},"rank":6}]}}
,{"id":70022930,"text":"70022930 - 2000 - Late-Quaternary recharge determined from chloride in shallow groundwater in the central Great Plains","interactions":[],"lastModifiedDate":"2012-03-12T17:20:39","indexId":"70022930","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":3218,"text":"Quaternary Research","active":true,"publicationSubtype":{"id":10}},"title":"Late-Quaternary recharge determined from chloride in shallow groundwater in the central Great Plains","docAbstract":"An extensive suite of isotopic and geochemical tracers in groundwater has been used to provide hydrologic assessments of the hierarchy of flow systems in aquifers underlying the central Great Plains (southeastern Colorado and western Kansas) of the United States and to determine the late Pleistocene and Holocene paleotemperature and paleorecharge record. Hydrogeologic and geochemical tracer data permit classification of the samples into late Holocene, late Pleistocene-early Holocene, and much older Pleistocene groups. Paleorecharge rates calculated from the Cl concentration in the samples show that recharge rates were at least twice the late Holocene rate during late Pleistocene-early Holocene time, which is consistent with their relative depletion in 16O and D. Noble gas (Ne, Ar, Kr, Xe) temperature calculations confirm that these older samples represent a recharge environment approximately 5??C cooler than late Holocene values. These results are consistent with the global climate models that show a trend toward a warmer, more arid climate during the Holocene. (C) 2000 University of Washington.","largerWorkType":{"id":2,"text":"Article"},"largerWorkTitle":"Quaternary Research","largerWorkSubtype":{"id":10,"text":"Journal Article"},"language":"English","doi":"10.1006/qres.1999.2113","issn":"00335894","usgsCitation":"Macfarlane, P.A., Clark, J., Davisson, M., Hudson, G., and Whittemore, D.O., 2000, Late-Quaternary recharge determined from chloride in shallow groundwater in the central Great Plains: Quaternary Research, v. 53, no. 2, p. 167-174, https://doi.org/10.1006/qres.1999.2113.","startPage":"167","endPage":"174","numberOfPages":"8","costCenters":[],"links":[{"id":479190,"rank":10000,"type":{"id":41,"text":"Open Access External Repository Page"},"url":"https://escholarship.org/uc/item/7b48q3wf","text":"External Repository"},{"id":208267,"rank":9999,"type":{"id":10,"text":"Digital Object Identifier"},"url":"https://dx.doi.org/10.1006/qres.1999.2113"},{"id":233898,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"53","issue":"2","noUsgsAuthors":false,"publicationDate":"2017-01-20","publicationStatus":"PW","scienceBaseUri":"505a4566e4b0c8380cd672ae","contributors":{"authors":[{"text":"Macfarlane, P. A.","contributorId":14597,"corporation":false,"usgs":true,"family":"Macfarlane","given":"P.","email":"","middleInitial":"A.","affiliations":[],"preferred":false,"id":395501,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Clark, J.F.","contributorId":24124,"corporation":false,"usgs":true,"family":"Clark","given":"J.F.","email":"","affiliations":[],"preferred":false,"id":395502,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Davisson, M.L.","contributorId":62277,"corporation":false,"usgs":true,"family":"Davisson","given":"M.L.","email":"","affiliations":[],"preferred":false,"id":395505,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Hudson, G.B.","contributorId":28768,"corporation":false,"usgs":true,"family":"Hudson","given":"G.B.","email":"","affiliations":[],"preferred":false,"id":395504,"contributorType":{"id":1,"text":"Authors"},"rank":4},{"text":"Whittemore, Donald O.","contributorId":28748,"corporation":false,"usgs":false,"family":"Whittemore","given":"Donald","email":"","middleInitial":"O.","affiliations":[],"preferred":false,"id":395503,"contributorType":{"id":1,"text":"Authors"},"rank":5}]}}
,{"id":70022922,"text":"70022922 - 2000 - Atmospheric nitrogen in the Mississippi River Basin:  Amissions, deposition and transport","interactions":[],"lastModifiedDate":"2018-12-10T07:44:04","indexId":"70022922","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":5331,"text":"Science of Total Environment","active":true,"publicationSubtype":{"id":10}},"title":"Atmospheric nitrogen in the Mississippi River Basin:  Amissions, deposition and transport","docAbstract":"<p>Atmospheric deposition of nitrogen has been cited as a major factor in the nitrogen saturation of forests in the north-eastern United States and as a contributor to the eutrophication of coastal waters, including the Gulf of Mexico near the mouth of the Mississippi River. Sources of nitrogen emissions and the resulting spatial patterns of nitrogen deposition within the Mississippi River Basin, however, have not been fully documented. An assessment of atmospheric nitrogen in the Mississippi River Basin was therefore conducted in 1998-1999 to: (1) evaluate the forms in which nitrogen is deposited from the atmosphere; (2) quantify the spatial distribution of atmospheric nitrogen deposition throughout the basin; and (3) relate locations of emission sources to spatial deposition patterns to evaluate atmospheric transport. Deposition data collected through the NADP/NTN (National Atmospheric Deposition Program/National Trends Network) and CASTNet (Clean Air Status and Trends Network) were used for this analysis. NO(x) Tier 1 emission data by county was obtained for 1992 from the US Environmental Protection Agency (Emissions Trends Viewer CD, 1985-1995, version 1.0, September 1996) and NH3 emissions data was derived from the 1992 Census of Agriculture (US Department of Commerce. Census of Agriculture, US Summary and County Level Data, US Department of Commerce, Bureau of the Census. Geographic Area series, 1995:1b) or the National Agricultural Statistics Service (US Department of Agriculture. National Agricultural Statistics Service Historical Data. Accessed 7/98 at URL, 1998. http://www.usda.gov/nass/pubs/hisdata.htm). The highest rates of wet deposition of NO3- were in the north-eastern part of the basin, downwind of electric utility plants and urban areas, whereas the highest rates of wet deposition of NH4+ were in Iowa, near the center of intensive agricultural activities in the Midwest. The lowest rates of atmospheric nitrogen deposition were on the western (windward) side of the basin, which suggests that most of the nitrogen deposited within the basin is derived from internal sources. Atmospheric transport eastward across the basin boundary is greater for NO3- than NH4+, but a significant amount of NH4+ is likely to be transported out of the basin through the formation of (NH4)2SO4 and NH4NO3 particles - a process that greatly increases the atmospheric residence time of NH4+. This process is also a likely factor in the atmospheric transport of nitrogen from the Midwest to upland forest regions in the North-East, such as the western Adirondack region of New York, where NH4+ constitutes 38% of the total wet deposition of N.&nbsp;</p>","language":"English","publisher":"Elsevier","doi":"10.1016/S0048-9697(99)00533-1","issn":"00489697","usgsCitation":"Lawrence, G., Goolsby, D.A., Battaglin, W., and Stensland, G., 2000, Atmospheric nitrogen in the Mississippi River Basin:  Amissions, deposition and transport: Science of Total Environment, v. 248, no. 2-3, p. 87-100, https://doi.org/10.1016/S0048-9697(99)00533-1.","productDescription":"14 p.","startPage":"87","endPage":"100","costCenters":[{"id":589,"text":"Toxic Substances Hydrology Program","active":true,"usgs":true}],"links":[{"id":233721,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"},{"id":208185,"rank":9999,"type":{"id":10,"text":"Digital Object Identifier"},"url":"https://dx.doi.org/10.1016/S0048-9697(99)00533-1"}],"volume":"248","issue":"2-3","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"5059eec4e4b0c8380cd49f3f","contributors":{"authors":[{"text":"Lawrence, G.B. 0000-0002-8035-2350","orcid":"https://orcid.org/0000-0002-8035-2350","contributorId":76347,"corporation":false,"usgs":true,"family":"Lawrence","given":"G.B.","affiliations":[],"preferred":false,"id":395423,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Goolsby, D. A.","contributorId":50508,"corporation":false,"usgs":true,"family":"Goolsby","given":"D.","email":"","middleInitial":"A.","affiliations":[],"preferred":false,"id":395421,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Battaglin, W.A.","contributorId":16376,"corporation":false,"usgs":true,"family":"Battaglin","given":"W.A.","email":"","affiliations":[],"preferred":false,"id":395420,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Stensland, G.J.","contributorId":62096,"corporation":false,"usgs":true,"family":"Stensland","given":"G.J.","email":"","affiliations":[],"preferred":false,"id":395422,"contributorType":{"id":1,"text":"Authors"},"rank":4}]}}
,{"id":70022921,"text":"70022921 - 2000 - A new method for collection of nitrate from fresh water and the analysis of nitrogen and oxygen isotope ratios","interactions":[],"lastModifiedDate":"2018-12-14T06:14:08","indexId":"70022921","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":2342,"text":"Journal of Hydrology","active":true,"publicationSubtype":{"id":10}},"title":"A new method for collection of nitrate from fresh water and the analysis of nitrogen and oxygen isotope ratios","docAbstract":"<p><span>A new method for concentrating&nbsp;nitrate&nbsp;from fresh waters for&nbsp;</span><i>δ</i><sup>15</sup>N and<span>&nbsp;</span><i>δ</i><sup>18</sup><span>O analysis has been developed and field-tested for four years. The benefits of the method are: (1) elimination of the need to transport large volumes of water to the laboratory for processing; (2) elimination of the need for hazardous&nbsp;preservatives; and (3) the ability to concentrate nitrate from fresh waters. Nitrate is collected by, passing the water-sample through pre-filled, disposable,&nbsp;anion&nbsp;exchanging&nbsp;resin&nbsp;columns in the field. The columns are subsequently transported to the laboratory where the nitrate is extracted, converted to AgNO</span><sub>3</sub><span>&nbsp;</span>and analyzed for its isotope composition. Nitrate is eluted from the anion exchange columns with 15&nbsp;ml of 3&nbsp;M HCl. The nitrate-bearing acid eluant is neutralized with Ag<sub>2</sub>O, filtered to remove the AgCl precipitate, then freeze-dried to obtain solid AgNO<sub>3</sub>, which is then combusted to N<sub>2</sub><span>&nbsp;in sealed&nbsp;quartz&nbsp;tubes for&nbsp;</span><i>δ</i><sup>15</sup>N analysis. For<span>&nbsp;</span><i>δ</i><sup>18</sup><span>O analysis, aliquots of the neutralized eluant are processed further to remove non-nitrate oxygen-bearing anions and dissolved organic matter.&nbsp;Barium&nbsp;chloride is added to precipitate&nbsp;sulfate&nbsp;and phosphate; the solution is then filtered, passed through a cation exchange column to remove excess Ba</span><sup>2+</sup>, re-neutralized with Ag<sub>2</sub><span>O, filtered, agitated with&nbsp;activated carbon&nbsp;to remove dissolved organic matter and freeze-dried. The resulting AgNO</span><sub>3</sub><span>&nbsp;is combusted with&nbsp;graphite&nbsp;in a closed tube to produce CO</span><sub>2</sub><span>, which is cryogenically purified and analyzed for its&nbsp;oxygen isotope&nbsp;composition. The 1</span><i>σ</i>analytical precisions for<span>&nbsp;</span><i>δ</i><sup>15</sup>N and<span>&nbsp;</span><i>δ</i><sup>18</sup>O are ±0.05‰ and ±0.5‰, respectively, for solutions of KNO<sub>3</sub><span>&nbsp;</span>standard processed through the entire column procedure.</p>","language":"English","publisher":"Elsevier","doi":"10.1016/S0022-1694(99)00205-X","issn":"00221694","usgsCitation":"Silva, S.R., Kendall, C., Wilkison, D., Ziegler, A., Chang, C.C., and Avanzino, R., 2000, A new method for collection of nitrate from fresh water and the analysis of nitrogen and oxygen isotope ratios: Journal of Hydrology, v. 228, no. 1-2, p. 22-36, https://doi.org/10.1016/S0022-1694(99)00205-X.","productDescription":"15 p.","startPage":"22","endPage":"36","costCenters":[{"id":589,"text":"Toxic Substances Hydrology Program","active":true,"usgs":true}],"links":[{"id":233686,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"},{"id":208169,"rank":9999,"type":{"id":10,"text":"Digital Object Identifier"},"url":"https://dx.doi.org/10.1016/S0022-1694(99)00205-X"}],"volume":"228","issue":"1-2","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"5059e4a7e4b0c8380cd467ed","contributors":{"authors":[{"text":"Silva, S. R.","contributorId":27474,"corporation":false,"usgs":true,"family":"Silva","given":"S.","email":"","middleInitial":"R.","affiliations":[],"preferred":false,"id":395414,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Kendall, C. 0000-0002-0247-3405","orcid":"https://orcid.org/0000-0002-0247-3405","contributorId":35050,"corporation":false,"usgs":true,"family":"Kendall","given":"C.","affiliations":[],"preferred":false,"id":395415,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Wilkison, D.H.","contributorId":39800,"corporation":false,"usgs":true,"family":"Wilkison","given":"D.H.","email":"","affiliations":[],"preferred":false,"id":395417,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Ziegler, A.C.","contributorId":74398,"corporation":false,"usgs":true,"family":"Ziegler","given":"A.C.","email":"","affiliations":[],"preferred":false,"id":395419,"contributorType":{"id":1,"text":"Authors"},"rank":4},{"text":"Chang, Cecily C.Y.","contributorId":68032,"corporation":false,"usgs":true,"family":"Chang","given":"Cecily","email":"","middleInitial":"C.Y.","affiliations":[],"preferred":false,"id":395418,"contributorType":{"id":1,"text":"Authors"},"rank":5},{"text":"Avanzino, R.J.","contributorId":37336,"corporation":false,"usgs":true,"family":"Avanzino","given":"R.J.","affiliations":[],"preferred":false,"id":395416,"contributorType":{"id":1,"text":"Authors"},"rank":6}]}}
,{"id":70022917,"text":"70022917 - 2000 - Occurrence of pesticides in rain and air in urban and agricultural areas of Mississippi, April-September 1995","interactions":[],"lastModifiedDate":"2021-05-28T16:35:47.437414","indexId":"70022917","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":5331,"text":"Science of Total Environment","active":true,"publicationSubtype":{"id":10}},"title":"Occurrence of pesticides in rain and air in urban and agricultural areas of Mississippi, April-September 1995","docAbstract":"<p>In April 1995, the US Geological Survey began a study to determine the occurrence and temporal distribution of 49 pesticides and pesticide metabolites in air and rain samples from an urban and an agricultural sampling site in Mississippi. The study was a joint effort between the National Water-Quality Assessment and the Toxic Substances Programs and was part of a larger study examining the occurrence and temporal distribution of pesticides in air and rain in the Mississippi River basin. Concurrent high-volume air and wet-only deposition samples were collected weekly. The air samplers consisted of a glass-fiber filter to collect particles and tandem polyurethane foam plugs to collect gas-phase pesticides. Every rain and air sample collected from the urban and agricultural sites had detectable levels of multiple pesticides. The magnitude of the total concentration was 5-10 times higher at the agricultural site as compared to the urban site. The pesticide with the highest concentration in rain at both sites was methyl parathion. The pesticide with the highest concentration in the air samples from the agricultural site was also methyl parathion, but from the urban site the highest concentration was diazinon followed closely by chlorpyrifos. More than two decades since p,p'-DDT was banned from use in the United States, p,p'-DDE, a metabolite of p,p'-DDT, was detected in every air sample collected from the agricultural site and in more than half of the air samples from the urban site.&nbsp;</p>","language":"English","publisher":"Elsevier","doi":"10.1016/S0048-9697(99)00545-8","usgsCitation":"Coupe, R., Manning, M., Foreman, W., Goolsby, D.A., and Majewski, M., 2000, Occurrence of pesticides in rain and air in urban and agricultural areas of Mississippi, April-September 1995: Science of Total Environment, v. 248, no. 2-3, p. 227-240, https://doi.org/10.1016/S0048-9697(99)00545-8.","productDescription":"14 p.","startPage":"227","endPage":"240","costCenters":[{"id":452,"text":"National Water Quality Laboratory","active":true,"usgs":true},{"id":589,"text":"Toxic Substances Hydrology 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A.","contributorId":50508,"corporation":false,"usgs":true,"family":"Goolsby","given":"D.","email":"","middleInitial":"A.","affiliations":[],"preferred":false,"id":395396,"contributorType":{"id":1,"text":"Authors"},"rank":4},{"text":"Majewski, M.S.","contributorId":88501,"corporation":false,"usgs":true,"family":"Majewski","given":"M.S.","email":"","affiliations":[],"preferred":false,"id":395398,"contributorType":{"id":1,"text":"Authors"},"rank":5}]}}
,{"id":70022914,"text":"70022914 - 2000 - Occurrence and distribution of microbiological indicators in groundwater and stream water","interactions":[],"lastModifiedDate":"2022-06-28T16:10:53.838458","indexId":"70022914","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":3711,"text":"Water Environment Research","active":true,"publicationSubtype":{"id":10}},"title":"Occurrence and distribution of microbiological indicators in groundwater and stream water","docAbstract":"<p>A total of 136 stream water and 143 groundwater samples collected in five important hydrologic systems of the United States were analyzed for microbiological indicators to test monitoring concepts in a nationally consistent program. Total coliforms were found in 99%,<span>&nbsp;</span><i>Escherichia coli</i><span>&nbsp;</span>in 97%, and<span>&nbsp;</span><i>Clostridium perfringens</i><span>&nbsp;</span>in 73% of stream water samples analyzed for each bacterium. Total coliforms were found in 20%, E. coli in less than 1%, and<span>&nbsp;</span><i>C. perfringens</i><span>&nbsp;</span>in none of the groundwater samples analyzed for each bacterium. Although coliphage analyses were performed on many of the samples, contamination in the laboratory and problems discerning discrete plaques precluded quantification. Land use was found to have the most significant effect on concentrations of bacterial indicators in stream water. Presence of septic systems on the property near the sampling site and well depth were found to be related to detection of coliforms in groundwater, although these relationships were not statistically significant. A greater diversity of sites, more detailed information about some factors, and a larger dataset may provide further insight to factors that affect microbiological indicators.</p>","language":"English","publisher":"Water Environment Federation","publisherLocation":"Alexandria, VA, United States","doi":"10.2175/106143000X137220","issn":"10614303","usgsCitation":"Francy, D.S., Helsel, D., and Nally, R.A., 2000, Occurrence and distribution of microbiological indicators in groundwater and stream water: Water Environment Research, v. 72, no. 2, p. 152-161, https://doi.org/10.2175/106143000X137220.","productDescription":"10 p.","startPage":"152","endPage":"161","costCenters":[{"id":629,"text":"Water Resources Division","active":false,"usgs":true}],"links":[{"id":233542,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      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             -118.51989,\n                34.02778\n              ],\n              [\n                -119.081,\n                34.078\n              ],\n              [\n                -119.43884,\n                34.34848\n              ],\n              [\n                -120.36778,\n                34.44711\n              ],\n              [\n                -120.62286,\n                34.60855\n              ],\n              [\n                -120.74433,\n                35.15686\n              ],\n              [\n                -121.71457,\n                36.16153\n              ],\n              [\n                -122.54747,\n                37.55176\n              ],\n              [\n                -122.51201,\n                37.78339\n              ],\n              [\n                -122.95319,\n                38.11371\n              ],\n              [\n                -123.7272,\n                38.95166\n              ],\n              [\n                -123.86517,\n                39.76699\n              ],\n              [\n                -124.39807,\n                40.3132\n              ],\n              [\n                -124.17886,\n                41.14202\n              ],\n              [\n                -124.2137,\n                41.99964\n              ],\n              [\n                -124.53284,\n                42.76599\n              ],\n              [\n                -124.14214,\n                43.70838\n              ],\n              [\n                -124.02053,\n                44.6159\n              ],\n              [\n                -123.89893,\n                45.52341\n              ],\n              [\n                -124.07963,\n                46.86475\n              ],\n              [\n                -124.39567,\n                47.72017\n              ],\n              [\n                -124.68721,\n                48.18443\n              ],\n              [\n                -124.5661,\n                48.37971\n              ],\n              [\n                -123.12,\n                48.04\n              ],\n              [\n                -122.58736,\n                47.096\n              ],\n              [\n                -122.34,\n                47.36\n              ],\n              [\n                -122.5,\n                48.18\n              ],\n              [\n                -122.84,\n                49\n              ],\n              [\n                -120,\n                49\n              ],\n              [\n                -117.03121,\n                49\n              ],\n              [\n                -116.04818,\n                49\n              ],\n              [\n                -113,\n                49\n              ],\n              [\n                -110.05,\n                49\n              ],\n              [\n                -107.05,\n                49\n              ],\n              [\n                -104.04826,\n                48.99986\n              ],\n              [\n                -100.65,\n                49\n              ],\n              [\n                -97.22872,\n                49.0007\n              ],\n              [\n                -95.15907,\n                49\n              ],\n              [\n                -95.15609,\n                49.38425\n              ],\n              [\n                -94.81758,\n                49.38905\n              ]\n            ]\n          ]\n        ]\n      },\n      \"properties\": {\n        \"name\": \"United States\"\n      }\n    }\n  ]\n}","volume":"72","issue":"2","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505a6b3ae4b0c8380cd745a8","contributors":{"authors":[{"text":"Francy, Donna S. 0000-0001-9229-3557 dsfrancy@usgs.gov","orcid":"https://orcid.org/0000-0001-9229-3557","contributorId":1853,"corporation":false,"usgs":true,"family":"Francy","given":"Donna","email":"dsfrancy@usgs.gov","middleInitial":"S.","affiliations":[{"id":513,"text":"Ohio Water Science Center","active":true,"usgs":true},{"id":35860,"text":"Ohio-Kentucky-Indiana Water Science Center","active":true,"usgs":true}],"preferred":true,"id":395385,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Helsel, Dennis R.","contributorId":85569,"corporation":false,"usgs":true,"family":"Helsel","given":"Dennis R.","affiliations":[],"preferred":false,"id":395384,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Nally, Rebecca A.","contributorId":94068,"corporation":false,"usgs":true,"family":"Nally","given":"Rebecca","email":"","middleInitial":"A.","affiliations":[],"preferred":false,"id":395386,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
,{"id":70022911,"text":"70022911 - 2000 - Nitrogen flux and sources in the Mississippi River Basin","interactions":[],"lastModifiedDate":"2018-12-07T05:38:14","indexId":"70022911","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":5331,"text":"Science of Total Environment","active":true,"publicationSubtype":{"id":10}},"title":"Nitrogen flux and sources in the Mississippi River Basin","docAbstract":"<div id=\"abstracts\" class=\"Abstracts\"><div id=\"aep-abstract-id10\" class=\"abstract author\"><div id=\"aep-abstract-sec-id11\"><p>Nitrogen from the Mississippi River Basin is believed to be at least partly responsible for the large zone of oxygen-depleted water that develops in the Gulf of Mexico each summer. Historical data show that concentrations of nitrate in the Mississippi River and some of its tributaries have increased by factors of 2 to more than 5 since the early 1900s. We have used the historical streamflow and concentration data in regression models to estimate the annual flux of nitrogen (N) to the Gulf of Mexico and to determine where the nitrogen originates within the Mississippi Basin. Results show that for 1980–1996 the mean annual total N flux to the Gulf of Mexico was 1&nbsp;568&nbsp;000 t/year. The flux was approximately 61% nitrate as N, 37% organic N, and 2% ammonium as N. The flux of nitrate to the Gulf has approximately tripled in the last 30 years with most of the increase occurring between 1970 and 1983. The mean annual N flux has changed little since the early 1980s, but large year-to-year variations in N flux occur because of variations in precipitation. During wet years the N flux can increase by 50% or more due to flushing of nitrate that has accumulated in the soils and unsaturated zones in the basin. The principal source areas of N are basins in southern Minnesota, Iowa, Illinois, Indiana, and Ohio that drain agricultural land. Basins in this region yield 800 to more than 3100 kg total N/km<sup>2</sup><span>&nbsp;</span>per year to streams, several times the N yield of basins outside this region. Assuming conservative transport of N in the Mississippi River, streams draining Iowa and Illinois contribute on average approximately 35% of the total N discharged by the Mississippi River to the Gulf of Mexico. In years with high precipitation they can contribute a larger percentage.</p></div></div></div>","language":"English","publisher":"Elsevier","doi":"10.1016/S0048-9697(99)00532-X","issn":"00489697","usgsCitation":"Goolsby, D.A., Battaglin, W., Aulenbach, B., and Hooper, R.P., 2000, Nitrogen flux and sources in the Mississippi River Basin: Science of Total Environment, v. 248, no. 2-3, p. 75-86, https://doi.org/10.1016/S0048-9697(99)00532-X.","productDescription":"12 p.","startPage":"75","endPage":"86","costCenters":[{"id":589,"text":"Toxic Substances Hydrology Program","active":true,"usgs":true}],"links":[{"id":208084,"rank":9999,"type":{"id":10,"text":"Digital Object Identifier"},"url":"https://dx.doi.org/10.1016/S0048-9697(99)00532-X"},{"id":233501,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"248","issue":"2-3","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505a66d8e4b0c8380cd7300b","contributors":{"authors":[{"text":"Goolsby, D. A.","contributorId":50508,"corporation":false,"usgs":true,"family":"Goolsby","given":"D.","email":"","middleInitial":"A.","affiliations":[],"preferred":false,"id":395377,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Battaglin, W.A.","contributorId":16376,"corporation":false,"usgs":true,"family":"Battaglin","given":"W.A.","email":"","affiliations":[],"preferred":false,"id":395375,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Aulenbach, Brent T.","contributorId":62766,"corporation":false,"usgs":true,"family":"Aulenbach","given":"Brent T.","affiliations":[],"preferred":false,"id":395378,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Hooper, R. P.","contributorId":26321,"corporation":false,"usgs":true,"family":"Hooper","given":"R.","email":"","middleInitial":"P.","affiliations":[],"preferred":false,"id":395376,"contributorType":{"id":1,"text":"Authors"},"rank":4}]}}
,{"id":70022871,"text":"70022871 - 2000 - Fractured-aquifer hydrogeology from geophysical logs: Brunswick group and Lockatong Formation, Pennsylvania","interactions":[],"lastModifiedDate":"2018-12-12T10:13:53","indexId":"70022871","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":1861,"text":"Ground Water","active":true,"publicationSubtype":{"id":10}},"title":"Fractured-aquifer hydrogeology from geophysical logs: Brunswick group and Lockatong Formation, Pennsylvania","docAbstract":"<p>The Brunswick Group and the underlying Lockatong Formation are composed of lithified Mesozoic sediments that constitute part of the Newark Basin in southeastern Pennsylvania. These fractured rocks form an important regional aquifer that consists of gradational sequences of shale, siltstone, and sandstone, with fluid transport occurring primarily in fractures. An extensive suite of geophysical logs was obtained in seven wells located at the borough of Lansdale, Pennsylvania, in order to better characterize the areal hydrogeologic system and provide guidelines for the refinement of numerical ground water models. Six of the seven wells are approximately 120 m deep and the seventh extends to a depth of 335 m. Temperature, fluid conductivity, and flowmeter logs are used to locate zones of fluid exchange and to quantify transmissivities. Electrical resistivity and natural gamma logs together yield detailed stratigraphic information, and digital acoustic televiewer data provide magnetically oriented images of the borehole wall from which almost 900 fractures are identified.</p><p>Analyses of the geophysical data indicate that the aquifer penetrated by the deep well can be separated into two distinct structural domains, which may, in turn, reflect different mechanical responses to basin extension by different sedimentary units:</p><p>1. In the shallow zone (above 125 m), the dominant fracture population consists of gently dipping bedding plane partings that strike N46°E and dip to the northwest at about 11 degrees. Fluid flow is concentrated in the upper 80 m along these subhorizontal fractures, with transmissivities rapidly diminishing in magnitude with depth.</p><p>2. The zone below 125 m marks the appearance of numerous high-angle fractures that are orthogonal to the bedding planes, striking parallel but dipping steeply southeast at 77 degrees.</p><p>This secondary set of fractures is associated with a fairly thick (approximately 60 m) high-resistivity, low-transmissivity sandstone unit that is abruptly terminated by a thin shale bed at a depth of 190 m. This lower contact effectively delineates the aquifer's vertical extent at this location because no detectable evidence of ground water movement is found below it. Thus, fluid flow is controlled by fractures, but fracture type and orientation are related to lithology. Finally, a transient thermal-conduction model is successfully applied to simulate observed temperature logs, thereby confirming the effects of ground-surface warming that occurred in the area as a result of urbanization at the turn of the century. The systematic warming of the upper 120 m has increased the transmissivity of this aquifer by almost 10%, simply due to changes in fluid viscosity and density.</p>","language":"English","publisher":"Wiley","doi":"10.1111/j.1745-6584.2000.tb00329.x","issn":"0017467X","usgsCitation":"Morin, R.H., Senior, L.A., and Decker, E.R., 2000, Fractured-aquifer hydrogeology from geophysical logs: Brunswick group and Lockatong Formation, Pennsylvania: Ground Water, v. 38, no. 2, p. 182-192, https://doi.org/10.1111/j.1745-6584.2000.tb00329.x.","productDescription":"11 p.","startPage":"182","endPage":"192","costCenters":[{"id":532,"text":"Pennsylvania Water Science Center","active":true,"usgs":true},{"id":589,"text":"Toxic Substances Hydrology Program","active":true,"usgs":true}],"links":[{"id":233460,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"Pennsylvania","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"type\": \"Polygon\",\n        \"coordinates\": [\n          [\n            [\n              -75.31667,\n              40.25833\n            ],\n            [\n              -75.25,\n              40.25833\n            ],\n            [\n              -75.25,\n              40.20833\n            ],\n            [\n              -75.31667,\n              40.20833\n            ],\n            [\n              -75.31667,\n              40.25833\n            ]\n          ]\n        ]\n      }\n    }\n  ]\n}","volume":"38","issue":"2","noUsgsAuthors":false,"publicationDate":"2005-08-04","publicationStatus":"PW","scienceBaseUri":"505a13b6e4b0c8380cd54758","contributors":{"authors":[{"text":"Morin, Roger H. rhmorin@usgs.gov","contributorId":2432,"corporation":false,"usgs":true,"family":"Morin","given":"Roger","email":"rhmorin@usgs.gov","middleInitial":"H.","affiliations":[],"preferred":true,"id":395221,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Senior, Lisa A. 0000-0003-2629-1996 lasenior@usgs.gov","orcid":"https://orcid.org/0000-0003-2629-1996","contributorId":2150,"corporation":false,"usgs":true,"family":"Senior","given":"Lisa","email":"lasenior@usgs.gov","middleInitial":"A.","affiliations":[{"id":532,"text":"Pennsylvania Water Science Center","active":true,"usgs":true}],"preferred":true,"id":395222,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Decker, Edward R.","contributorId":23975,"corporation":false,"usgs":true,"family":"Decker","given":"Edward","email":"","middleInitial":"R.","affiliations":[],"preferred":false,"id":395223,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
,{"id":70022058,"text":"70022058 - 2000 - Water quality degradation effects on freshwater availability: Impacts of human activities","interactions":[],"lastModifiedDate":"2022-06-28T15:37:25.188589","indexId":"70022058","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":3713,"text":"Water International","active":true,"publicationSubtype":{"id":10}},"displayTitle":"Water quality degradation effects on freshwater availability: <i>Impacts of human activities</i>","title":"Water quality degradation effects on freshwater availability: Impacts of human activities","docAbstract":"The quality of freshwater at any point on the landscape reflects the combined effects of many processes along water pathways. Human activities on all spatial scales affect both water quality and quantity. Alteration of the landscape and associated vegetation has not only changed the water balance, but typically has altered processes that control water quality. Effects of human activities on a small scale are relevant to an entire drainage basin. Furthermore, local, regional, and global differences in climate and water flow are considerable, causing varying effects of human activities on land and water quality and quantity, depending on location within a watershed, geology, biology, physiographic characteristics, and climate. These natural characteristics also greatly control human activities, which will, in turn, modify (or affect) the natural composition of water. One of the most important issues for effective resource management is recognition of cyclical and cascading effects of human activities on the water quality and quantity along hydrologic pathways. The degradation of water quality in one part of a watershed can have negative effects on users downstream. Everyone lives downstream of the effects of some human activity. An extremely important factor is that substances added to the atmosphere, land, and water generally have relatively long time scales for removal or clean up. The nature of the substance, including its affinity for adhering to soil and its ability to be transformed, affects the mobility and the time scale for removal of the substance. Policy alone will not solve many of the degradation issues, but a combination of policy, education, scientific knowledge, planning, and enforcement of applicable laws can provide mechanisms for slowing the rate of degradation and provide human and environmental protection. Such an integrated approach is needed to effectively manage land and water resources.","language":"English","publisher":"Taylor & Francis","doi":"10.1080/02508060008686817","issn":"02508060","usgsCitation":"Peters, N.E., and Meybeck, M., 2000, Water quality degradation effects on freshwater availability: Impacts of human activities: Water International, v. 25, no. 2, p. 185-193, https://doi.org/10.1080/02508060008686817.","productDescription":"9 p.","startPage":"185","endPage":"193","costCenters":[],"links":[{"id":230775,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"25","issue":"2","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505bc893e4b08c986b32c9d3","contributors":{"authors":[{"text":"Peters, Norman E. nepeters@usgs.gov","contributorId":1324,"corporation":false,"usgs":true,"family":"Peters","given":"Norman","email":"nepeters@usgs.gov","middleInitial":"E.","affiliations":[{"id":316,"text":"Georgia Water Science Center","active":true,"usgs":true}],"preferred":true,"id":392201,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Meybeck, Michel","contributorId":43521,"corporation":false,"usgs":true,"family":"Meybeck","given":"Michel","email":"","affiliations":[],"preferred":false,"id":392202,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":70022639,"text":"70022639 - 2000 - A Community Hydrometeorology Laboratory for Fostering Collaborative Research by the Atmospheric and Hydrologic Sciences","interactions":[],"lastModifiedDate":"2012-03-12T17:20:38","indexId":"70022639","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":1112,"text":"Bulletin of the American Meteorological Society","onlineIssn":"1520-0477","printIssn":"0003-0007","active":true,"publicationSubtype":{"id":10}},"title":"A Community Hydrometeorology Laboratory for Fostering Collaborative Research by the Atmospheric and Hydrologic Sciences","docAbstract":"A new community laboratory for fostering collaborative research between the atmospheric and hydrologie sciences communities is described. This facility, located at the National Center for Atmospheric Research (NCAR) in Boulder, Colorado, allows scientists from both communities to more easily focus resources and attention on interdisciplinary problems in atmospheric, hydrologic, and other related sciences. Researchers can remotely access the computing tools to use them or to download them to their own facility, or they can visit NCAR and use the laboratory with other scientists in joint research projects. An application of this facility is described, where scientists from NCAR, the University of Colorado, and the United States Geological Survey used quantitative precipitation estimates from weather radar to simulate a flash flood in the Buffalo Creek watershed in the mountainous Front Range near Denver, Colorado.","largerWorkType":{"id":2,"text":"Article"},"largerWorkTitle":"Bulletin of the American Meteorological Society","largerWorkSubtype":{"id":10,"text":"Journal Article"},"language":"English","issn":"00030007","usgsCitation":"Warner, T., Yates, D., and Leavesley, G., 2000, A Community Hydrometeorology Laboratory for Fostering Collaborative Research by the Atmospheric and Hydrologic Sciences: Bulletin of the American Meteorological Society, v. 81, no. 7, p. 1499-1505.","startPage":"1499","endPage":"1505","numberOfPages":"7","costCenters":[],"links":[{"id":233779,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"81","issue":"7","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"5059e2cee4b0c8380cd45c75","contributors":{"authors":[{"text":"Warner, T.T.","contributorId":7459,"corporation":false,"usgs":true,"family":"Warner","given":"T.T.","email":"","affiliations":[],"preferred":false,"id":394350,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Yates, D.N.","contributorId":55300,"corporation":false,"usgs":true,"family":"Yates","given":"D.N.","email":"","affiliations":[],"preferred":false,"id":394351,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Leavesley, G.H.","contributorId":93895,"corporation":false,"usgs":true,"family":"Leavesley","given":"G.H.","email":"","affiliations":[],"preferred":false,"id":394352,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
,{"id":70022613,"text":"70022613 - 2000 - Precipitation areal-reduction factor estimation using an annual-maxima centered approach","interactions":[],"lastModifiedDate":"2012-03-12T17:19:43","indexId":"70022613","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":2342,"text":"Journal of Hydrology","active":true,"publicationSubtype":{"id":10}},"title":"Precipitation areal-reduction factor estimation using an annual-maxima centered approach","docAbstract":"The adjustment of precipitation depth of a point storm to an effective (mean) depth over a watershed is important for characterizing rainfall-runoff relations and for cost-effective designs of hydraulic structures when design storms are considered. A design storm is the precipitation point depth having a specified duration and frequency (recurrence interval). Effective depths are often computed by multiplying point depths by areal-reduction factors (ARF). ARF range from 0 to 1, vary according to storm characteristics, such as recurrence interval; and are a function of watershed characteristics, such as watershed size, shape, and geographic location. This paper presents a new approach for estimating ARF and includes applications for the 1-day design storm in Austin, Dallas, and Houston, Texas. The approach, termed 'annual-maxima centered,' specifically considers the distribution of concurrent precipitation surrounding an annual-precipitation maxima, which is a feature not seen in other approaches. The approach does not require the prior spatial averaging of precipitation, explicit determination of spatial correlation coefficients, nor explicit definition of a representative area of a particular storm in the analysis. The annual-maxima centered approach was designed to exploit the wide availability of dense precipitation gauge data in many regions of the world. The approach produces ARF that decrease more rapidly than those from TP-29. Furthermore, the ARF from the approach decay rapidly with increasing recurrence interval of the annual-precipitation maxima. (C) 2000 Elsevier Science B.V.The adjustment of precipitation depth of a point storm to an effective (mean) depth over a watershed is important for characterizing rainfall-runoff relations and for cost-effective designs of hydraulic structures when design storms are considered. A design storm is the precipitation point depth having a specified duration and frequency (recurrence interval). Effective depths are often computed by multiplying point depths by areal-reduction factors (ARF). ARF range from 0 to 1, vary according to storm characteristics, such as recurrence interval; and are a function of watershed characteristics, such as watershed size, shape, and geographic location. This paper presents a new approach for estimating ARF and includes applications for the 1-day design storm in Austin, Dallas, and Houston, Texas. The approach, termed 'annual-maxima centered,' specifically considers the distribution of concurrent precipitation surrounding an annual-precipitation maxima, which is a feature not seen in other approaches. The approach does not require the prior spatial averaging of precipitation, explicit determination of spatial correlation coefficients, nor explicit definition of a representative area of a particular storm in the analysis. The annual-maxima centered approach was designed to exploit the wide availability of dense precipitation gauge data in many regions of the world. The approach produces ARF that decrease more rapidly than those from TP-29. Furthermore, the ARF from the approach decay rapidly with increasing recurrence interval of the annual-precipitation maxima.","largerWorkType":{"id":2,"text":"Article"},"largerWorkTitle":"Journal of Hydrology","largerWorkSubtype":{"id":10,"text":"Journal Article"},"language":"English","publisher":"Elsevier Science B.V.","publisherLocation":"Amsterdam, Netherlands","doi":"10.1016/S0022-1694(00)00170-0","issn":"00221694","usgsCitation":"Asquith, W., and Famiglietti, J., 2000, Precipitation areal-reduction factor estimation using an annual-maxima centered approach: Journal of Hydrology, v. 230, no. 1-2, p. 55-69, https://doi.org/10.1016/S0022-1694(00)00170-0.","startPage":"55","endPage":"69","numberOfPages":"15","costCenters":[],"links":[{"id":487332,"rank":10000,"type":{"id":41,"text":"Open Access External Repository Page"},"url":"https://escholarship.org/uc/item/30p9x5wd","text":"External Repository"},{"id":206829,"rank":9999,"type":{"id":10,"text":"Digital Object Identifier"},"url":"https://dx.doi.org/10.1016/S0022-1694(00)00170-0"},{"id":230884,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"230","issue":"1-2","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505a8112e4b0c8380cd7b35b","contributors":{"authors":[{"text":"Asquith, W.H.","contributorId":87980,"corporation":false,"usgs":true,"family":"Asquith","given":"W.H.","email":"","affiliations":[],"preferred":false,"id":394255,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Famiglietti, J.S.","contributorId":55994,"corporation":false,"usgs":true,"family":"Famiglietti","given":"J.S.","email":"","affiliations":[],"preferred":false,"id":394254,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":70022603,"text":"70022603 - 2000 - Snow crystal imaging using scanning electron microscopy: III. Glacier ice, snow and biota","interactions":[],"lastModifiedDate":"2022-09-20T15:31:44.279778","indexId":"70022603","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":1927,"text":"Hydrological Sciences Journal","active":true,"publicationSubtype":{"id":10}},"title":"Snow crystal imaging using scanning electron microscopy: III. Glacier ice, snow and biota","docAbstract":"<p><span>Low-temperature scanning electron microscopy (SEM) was used to observe metamorphosed snow, glacial firn, and glacial ice obtained from South Cascade Glacier in Washington State, USA. Biotic samples consisting of algae (</span><i>Chlamydomonas nivalis</i><span>) and ice worms (a species of oligochaetes) were also collected and imaged. In the field, the snow and biological samples were mounted on copper plates, cooled in liquid nitrogen, and stored in dry shipping containers which maintain a temperature of-196°C. The firn and glacier ice samples were obtained by extracting horizontal ice cores, 8 mm in diameter, at different levels from larger standard glaciological (vertical) ice cores 7.5 cm in diameter. These samples were cooled in liquid nitrogen and placed in cryotubes, were stored in the same dry shipping container, and sent to the SEM facility. In the laboratory, the samples were sputter coated with platinum and imaged by a low-temperature SEM. To image the firn and glacier ice samples, the cores were fractured in liquid nitrogen, attached to a specimen holder, and then imaged. While light microscope images of snow and ice are difficult to interpret because of internal reflection and refraction, the SEM images provide a clear and unique view of the surface of the samples because they are generated from electrons emitted or reflected only from the surface of the sample. In addition, the SEM has a great depth of field with a wide range of magnifying capabilities. The resulting images clearly show the individual grains of the seasonal snowpack and the bonding between the snow grains. Images of firn show individual ice crystals, the bonding between the crystals, and connected air spaces. Images of glacier ice show a crystal structure on a scale of 1–2 mm which is considerably smaller than the expected crystal size. Microscopic air bubbles, less than 15 μm in diameter, clearly marked the boundaries between these crystal-like features. The life forms associated with the glacier were easily imaged and studied. The low-temperature SEM sample collecting and handling methods proved to be operable in the field; the SEM analysis is applicable to glaciological studies and reveals details unattainable by conventional light microscopic methods.</span></p>","language":"English","publisher":"IAHS","publisherLocation":"Wallingford, United Kingdom","doi":"10.1080/02626660009492335","issn":"02626667","usgsCitation":"Rango, A., Wergin, W., Erbe, E., and Josberger, E., 2000, Snow crystal imaging using scanning electron microscopy: III. Glacier ice, snow and biota: Hydrological Sciences Journal, v. 45, no. 3, p. 357-375, https://doi.org/10.1080/02626660009492335.","productDescription":"19 p.","startPage":"357","endPage":"375","costCenters":[],"links":[{"id":487882,"rank":1,"type":{"id":40,"text":"Open Access Publisher Index Page"},"url":"https://doi.org/10.1080/02626660009492335","text":"Publisher Index Page"},{"id":230732,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"Washington","otherGeospatial":"North Cascades, South Cascade Glacier","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"type\": \"Polygon\",\n        \"coordinates\": [\n          [\n            [\n              -121.05135440826416,\n              48.358587379640454\n            ],\n            [\n              -121.05281352996825,\n     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     48.355507579049814\n            ],\n            [\n              -121.04620456695555,\n              48.356249029540734\n            ],\n            [\n              -121.0489511489868,\n              48.358102608560635\n            ],\n            [\n              -121.05135440826416,\n              48.358587379640454\n            ]\n          ]\n        ]\n      }\n    }\n  ]\n}","volume":"45","issue":"3","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505b91b4e4b08c986b319a4d","contributors":{"authors":[{"text":"Rango, A.","contributorId":94449,"corporation":false,"usgs":true,"family":"Rango","given":"A.","affiliations":[],"preferred":false,"id":394217,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Wergin, W.P.","contributorId":106280,"corporation":false,"usgs":true,"family":"Wergin","given":"W.P.","email":"","affiliations":[],"preferred":false,"id":394218,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Erbe, E.F.","contributorId":33877,"corporation":false,"usgs":true,"family":"Erbe","given":"E.F.","email":"","affiliations":[],"preferred":false,"id":394215,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Josberger, E.G.","contributorId":61161,"corporation":false,"usgs":true,"family":"Josberger","given":"E.G.","email":"","affiliations":[],"preferred":false,"id":394216,"contributorType":{"id":1,"text":"Authors"},"rank":4}]}}
,{"id":70022591,"text":"70022591 - 2000 - REE speciation in low-temperature acidic waters and the competitive effects of aluminum","interactions":[],"lastModifiedDate":"2018-12-12T08:45:04","indexId":"70022591","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":1213,"text":"Chemical Geology","active":true,"publicationSubtype":{"id":10}},"title":"REE speciation in low-temperature acidic waters and the competitive effects of aluminum","docAbstract":"<p>The effect of simultaneous competitive speciation of dissolved rare earth elements (REEs) in acidic waters (pH 3.3 to 5.2) has been evaluated by applying the PHREEQE code to the speciation of water analyses from Spain, Brazil, USA, and Canada. The main ions that might affect REE are Al3+, F-, SO42-, and PO43-. Fluoride, normally a significant complexer of REEs, is strongly associated with Al3+ in acid waters and consequently has little influence on REEs. The inclusion of aluminum concentrations in speciation calculations for acidic waters is essential for reliable speciation of REEs. Phosphate concentrations are too low (10-4 to 10-7 m) to affect REE speciation. Consequently, SO42- is the only important complexing ligand for REEs under these conditions. According to Millero [Millero, F.J., 1992. Stability constants for the formation of rare earth inorganic complexes as a function of ionic strength. Geochim. Cosmochim. Acta, 56, 3123-3132], the lanthanide sulfate stability constants are nearly constant with increasing atomic number so that no REE fractionation would be anticipated from aqueous complexation in acidic waters. Hence, REE enrichments or depletions must arise from mass transfer reactions.&nbsp;</p>","language":"English","publisher":"Elsevier","doi":"10.1016/S0009-2541(99)00166-7","issn":"00092541","usgsCitation":"Gimeno, S.M., Auque, S.L., and Nordstrom, D.K., 2000, REE speciation in low-temperature acidic waters and the competitive effects of aluminum: Chemical Geology, v. 165, no. 3-4, p. 167-180, https://doi.org/10.1016/S0009-2541(99)00166-7.","productDescription":"14 p.","startPage":"167","endPage":"180","costCenters":[{"id":589,"text":"Toxic Substances Hydrology Program","active":true,"usgs":true}],"links":[{"id":230547,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"},{"id":206683,"rank":9999,"type":{"id":10,"text":"Digital Object Identifier"},"url":"https://dx.doi.org/10.1016/S0009-2541(99)00166-7"}],"volume":"165","issue":"3-4","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505a9339e4b0c8380cd80cb1","contributors":{"authors":[{"text":"Gimeno, Serrano M.J.","contributorId":82182,"corporation":false,"usgs":true,"family":"Gimeno","given":"Serrano","email":"","middleInitial":"M.J.","affiliations":[],"preferred":false,"id":394178,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Auque, Sanz L.F.","contributorId":47245,"corporation":false,"usgs":true,"family":"Auque","given":"Sanz","email":"","middleInitial":"L.F.","affiliations":[],"preferred":false,"id":394177,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Nordstrom, D. Kirk 0000-0003-3283-5136 dkn@usgs.gov","orcid":"https://orcid.org/0000-0003-3283-5136","contributorId":749,"corporation":false,"usgs":true,"family":"Nordstrom","given":"D.","email":"dkn@usgs.gov","middleInitial":"Kirk","affiliations":[{"id":5044,"text":"National Research Program - Central Branch","active":true,"usgs":true},{"id":37277,"text":"WMA - Earth System Processes Division","active":true,"usgs":true}],"preferred":false,"id":394179,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
,{"id":70022588,"text":"70022588 - 2000 - Dating young groundwater with sulfur hexafluoride: Natural and anthropogenic sources of sulfur hexafluoride","interactions":[],"lastModifiedDate":"2018-12-07T06:25:39","indexId":"70022588","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":3722,"text":"Water Resources Research","onlineIssn":"1944-7973","printIssn":"0043-1397","active":true,"publicationSubtype":{"id":10}},"title":"Dating young groundwater with sulfur hexafluoride: Natural and anthropogenic sources of sulfur hexafluoride","docAbstract":"<p><span>Sulfur hexafluoride (SF</span><sub>6</sub><span>) is primarily of anthropogenic origin but also occurs naturally. The troposphere concentration of SF</span><sub>6</sub><span><span>&nbsp;</span>has increased from a steady state value of 0.054±0.009 to more than 4 parts per trillion volume during the past 40 years. An analytical procedure was developed for measuring concentrations of SF</span><sub>6</sub><span><span>&nbsp;</span>to less than 0.01 fmol/L in water. Groundwater can be dated with SF</span><sub>6</sub><span><span>&nbsp;</span>if it is in equilibrium with atmospheric SF</span><sub>6</sub><span><span>&nbsp;</span>at the time of recharge and does not contain significant SF</span><sub>6</sub><span><span>&nbsp;</span>from other sources. The dating range of SF</span><sub>6</sub><span><span>&nbsp;</span>is currently 0 to 30 years. The tracer was successfully used to date shallow groundwater of the Atlantic Coastal Plain sand aquifers of the United States and springs issuing near the top of the Blue Ridge Mountains of Virginia. Significant concentrations of naturally occurring SF</span><sub>6</sub><span><span>&nbsp;</span>were found in some igneous, volcanic, and sedimentary rocks and in some hydrothermal fluids.</span></p>","language":"English","publisher":"American Geophysical Union","doi":"10.1029/2000WR900151","usgsCitation":"Busenberg, E., and Plummer, N., 2000, Dating young groundwater with sulfur hexafluoride: Natural and anthropogenic sources of sulfur hexafluoride: Water Resources Research, v. 36, no. 10, p. 3011-3030, https://doi.org/10.1029/2000WR900151.","productDescription":"20 p.","startPage":"3011","endPage":"3030","costCenters":[{"id":589,"text":"Toxic Substances Hydrology Program","active":true,"usgs":true}],"links":[{"id":487378,"rank":1,"type":{"id":40,"text":"Open Access Publisher Index Page"},"url":"https://doi.org/10.1029/2000wr900151","text":"Publisher Index Page"},{"id":230471,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"36","issue":"10","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"5059fde4e4b0c8380cd4e9d5","contributors":{"authors":[{"text":"Busenberg, Eurybiades ebusenbe@usgs.gov","contributorId":2271,"corporation":false,"usgs":true,"family":"Busenberg","given":"Eurybiades","email":"ebusenbe@usgs.gov","affiliations":[{"id":436,"text":"National Research Program - Eastern Branch","active":true,"usgs":true}],"preferred":true,"id":394167,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Plummer, Niel 0000-0002-4020-1013 nplummer@usgs.gov","orcid":"https://orcid.org/0000-0002-4020-1013","contributorId":190100,"corporation":false,"usgs":true,"family":"Plummer","given":"Niel","email":"nplummer@usgs.gov","affiliations":[{"id":436,"text":"National Research Program - Eastern Branch","active":true,"usgs":true}],"preferred":true,"id":394168,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":70022580,"text":"70022580 - 2000 - Biodegradation of disinfection byproducts as a potential removal process during aquifer storage recovery","interactions":[],"lastModifiedDate":"2018-12-10T09:10:10","indexId":"70022580","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":2529,"text":"Journal of the American Water Resources Association","active":true,"publicationSubtype":{"id":10}},"title":"Biodegradation of disinfection byproducts as a potential removal process during aquifer storage recovery","docAbstract":"The biodegradation potential of two drinking water disinfection byproducts was investigated using aquifer materials obtained from approximately 100 and 200 meters below land surface in an aerobic aquifer system undergoing aquifer storage recovery of treated surface water. No significant biodegradation of a model trihalomethane compound, chloroform, was observed in aquifer microcosms under aerobic or anaerobic conditions. In contrast, between 16 and 27 percent mineralization of a radiolabeled model haloacetic acid compound, chloroacetic acid, was observed. These results indicate that although the potential for biodegradation of chloroacetic acid exists in deep aquifer systems, chloroform entrained within these aquifers or formed in situ will tend to persist. These results have important implications for water managers planning to meet anticipated lowered permissible levels of tri-halomethanes in drinking water.The biodegradation potential of two drinking water disinfection byproducts was investigated using aquifer materials obtained from approximately 100 and 200 meters below land surface in an aerobic aquifer system undergoing aquifer storage recovery of treated surface water. No significant biodegradation of a model trihalomethane compound, chloroform, was observed in aquifer microcosms under aerobic or anaerobic conditions. In contrast, between 16 and 27 percent mineralization of a radiolabeled model haloacetic acid compound, chloroacetic acid, was observed. These results indicate that although the potential for biodegradation of chloroacetic acid exists in deep aquifer systems, chloroform entrained within these aquifers or formed in situ will tend to persist. These results have important implications for water managers planning to meet anticipated lowered permissible levels of trihalomethanes in drinking water.Aquifer-storage-recovery injection water often contains disinfection byproducts. Results are presented from a study in which two model disinfection byproducts, chloroform and chloroacetic acid, were used to examine biodegradation by indigenous microorganisms. The recharge system studied was near Las Vegas, NV, where the aquifers are recharged artificially during the winter months. Microcosms were constructed using aquifer material recovered from two layers. Results showed that no significant biodegradation of chloroform occurred under aerobic or anaerobic conditions, but chloroacetic acid was biodegraded under both aerobic and anaerobic conditions.","language":"English","publisher":"Wiley","doi":"10.1111/j.1752-1688.2000.tb04312.x","issn":"1093474X","usgsCitation":"Landmeyer, J., Bradley, P., and Thomas, J.M., 2000, Biodegradation of disinfection byproducts as a potential removal process during aquifer storage recovery: Journal of the American Water Resources Association, v. 36, no. 4, p. 861-867, https://doi.org/10.1111/j.1752-1688.2000.tb04312.x.","productDescription":"7 p.","startPage":"861","endPage":"867","costCenters":[{"id":589,"text":"Toxic Substances Hydrology Program","active":true,"usgs":true}],"links":[{"id":230354,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"36","issue":"4","noUsgsAuthors":false,"publicationDate":"2007-06-08","publicationStatus":"PW","scienceBaseUri":"5059f147e4b0c8380cd4ab58","contributors":{"authors":[{"text":"Landmeyer, J. E.","contributorId":91140,"corporation":false,"usgs":true,"family":"Landmeyer","given":"J. E.","affiliations":[],"preferred":false,"id":394141,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Bradley, P. M. 0000-0001-7522-8606","orcid":"https://orcid.org/0000-0001-7522-8606","contributorId":29465,"corporation":false,"usgs":true,"family":"Bradley","given":"P. M.","affiliations":[],"preferred":false,"id":394139,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Thomas, J. M.","contributorId":62217,"corporation":false,"usgs":true,"family":"Thomas","given":"J.","email":"","middleInitial":"M.","affiliations":[],"preferred":false,"id":394140,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
,{"id":70022570,"text":"70022570 - 2000 - From safe yield to sustainable development of water resources - The Kansas experience","interactions":[],"lastModifiedDate":"2012-03-12T17:19:43","indexId":"70022570","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":2342,"text":"Journal of Hydrology","active":true,"publicationSubtype":{"id":10}},"title":"From safe yield to sustainable development of water resources - The Kansas experience","docAbstract":"This paper presents a synthesis of water sustainability issues from the hydrologic perspective. It shows that safe yield is a flawed concept and that sustainability is an idea that is broadly used but perhaps not well understood. In general, the sustainable yield of an aquifer must be considerably less than recharge if adequate amounts of water are to be available to sustain both the quantity and quality of streams, springs, wetlands, and ground-water-dependent ecosystems. To ensure sustainability, it is imperative that water limits be established based on hydrologic principles of mass balance. To establish water-use policies and planning horizons, the transition curves of aquifer systems from ground-water storage depletion to induced recharge of surface water need to be developed. Present-day numerical models are capable of generating such transition curves. Several idealized examples of aquifer systems show how this could be done. Because of the complexity of natural systems and the uncertainties in characterizing them, the current philosophy underlying sustainable management of water resources is based on the interconnected systems approach and on adaptive management. Examples of water-resources management from Kansas illustrate some of these concepts in a real-world setting. Some of the hallmarks of Kansas water management are the formation of local ground-water management districts, the adoption of minimum streamflow standards, the use of modified safe-yield policies in some districts, the implementation of integrated resource planning by the City of Wichita, and the subbasin water-resources management program in potential problem areas. These are all appropriate steps toward sustainable development. The Kansas examples show that local decision-making is the best way to fully account for local variability in water management. However, it is imperative that public education and involvement be encouraged, so that system complexities and constraints are better understood and overly simplistic solutions avoided. (C) 2000 Elsevier Science B.V.This paper presents a synthesis of water sustainability issues from the hydrologic perspective. It shows that safe yield is a flawed concept and that sustainability is an idea that is broadly used but perhaps not well understood. In general, the sustainable yield of an aquifer must be considerably less than recharge if adequate amounts of water are to be available to sustain both the quantity and quality of streams, springs, wetlands, and ground-water-dependent ecosystems. To ensure sustainability, it is imperative that water limits be established based on hydrologic principles of mass balance. To establish water-use policies and planning horizons, the transition curves of aquifer systems from ground-water storage depletion to induced recharge of surface water need to be developed. Present-day numerical models are capable of generating such transition curves. Several idealized examples of aquifer systems show how this could be done. Because of the complexity of natural systems and the uncertainties in characterizing them, the current philosophy underlying sustainable management of water resources is based on the interconnected systems approach and on adaptive management. Examples of water-resources management from Kansas illustrate some of these concepts in a real-world setting. Some of the hallmarks of Kansas water management are the formation of local ground-water management districts, the adoption of minimum streamflow standards, the use of modified safe-yield policies in some districts, the implementation of integrated resource planning by the City of Wichita, and the subbasin water-resources management program in potential problem areas. These are all appropriate steps toward sustainable development. The Kansas examples show that local decision-making is the best way to fully account for local variability in water management. However, it is imperative that public education and involv","largerWorkType":{"id":2,"text":"Article"},"largerWorkTitle":"Journal of Hydrology","largerWorkSubtype":{"id":10,"text":"Journal Article"},"language":"English","publisher":"Elsevier Science B.V.","publisherLocation":"Amsterdam, Netherlands","doi":"10.1016/S0022-1694(00)00263-8","issn":"00221694","usgsCitation":"Sophocleous, M., 2000, From safe yield to sustainable development of water resources - The Kansas experience: Journal of Hydrology, v. 235, no. 1-2, p. 27-43, https://doi.org/10.1016/S0022-1694(00)00263-8.","startPage":"27","endPage":"43","numberOfPages":"17","costCenters":[],"links":[{"id":206796,"rank":9999,"type":{"id":10,"text":"Digital Object Identifier"},"url":"https://dx.doi.org/10.1016/S0022-1694(00)00263-8"},{"id":230806,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"235","issue":"1-2","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505a13fbe4b0c8380cd54861","contributors":{"authors":[{"text":"Sophocleous, M.","contributorId":13373,"corporation":false,"usgs":true,"family":"Sophocleous","given":"M.","email":"","affiliations":[],"preferred":false,"id":394109,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":70022563,"text":"70022563 - 2000 - Colloid formation and metal transport through two mixing zones affected by acid mine drainage near Silverton, Colorado","interactions":[],"lastModifiedDate":"2018-12-12T08:19:48","indexId":"70022563","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":835,"text":"Applied Geochemistry","active":true,"publicationSubtype":{"id":10}},"title":"Colloid formation and metal transport through two mixing zones affected by acid mine drainage near Silverton, Colorado","docAbstract":"Stream discharges and concentrations of dissolved and colloidal metals (Al, Ca, Cu, Fe, Mg, Mn, Pb, and Zn), SO4, and dissolved silica were measured to identify chemical transformations and determine mass transports through two mixing zones in the Animas River that receive the inflows from Cement and Mineral Creeks. The creeks were the dominant sources of Al, Cu, Fe, and Pb, whereas the upstream Animas River supplied about half of the Zn. With the exception of Fe, which was present in dissolved and colloidal forms, the metals were dissolved in the acidic, high-SO4 waters of Cement Creek (pH 3.8). Mixing of Cement Creek with the Animas River increased pH to near-neutral values and transformed Al and some additional Fe into colloids which also contained Cu and Pb. Aluminium and Fe colloids had already formed in the mildly acidic conditions in Mineral Creek (pH 6.6) upstream of the confluence with the Animas River. Colloidal Fe continued to form downstream of both mixing zones. The Fe- and Al-rich colloids were important for transport of Cu, Pb, and Zn, which appeared to have sorbed to them. Partitioning of Zn between dissolved and colloidal phases was dependent on pH and colloid concentration. Mass balances showed conservative transports for Ca, Mg, Mn, SO4, and dissolved silica through the two mixing zones and small losses (< 10%) of colloidal Al, Fe and Zn from the water column.","language":"English","publisher":"Elsevier","doi":"10.1016/S0883-2927(99)00104-3","issn":"08832927","usgsCitation":"Schemel, L., Kimball, B.A., and Bencala, K., 2000, Colloid formation and metal transport through two mixing zones affected by acid mine drainage near Silverton, Colorado: Applied Geochemistry, v. 15, no. 7, p. 1003-1018, https://doi.org/10.1016/S0883-2927(99)00104-3.","productDescription":"16 p.","startPage":"1003","endPage":"1018","costCenters":[{"id":589,"text":"Toxic Substances Hydrology Program","active":true,"usgs":true}],"links":[{"id":230729,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"},{"id":206760,"rank":9999,"type":{"id":10,"text":"Digital Object Identifier"},"url":"https://dx.doi.org/10.1016/S0883-2927(99)00104-3"}],"country":"United States","state":"Colorado","city":"Silverton","volume":"15","issue":"7","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"5059f7b5e4b0c8380cd4cc7a","contributors":{"authors":[{"text":"Schemel, L. E.","contributorId":89529,"corporation":false,"usgs":true,"family":"Schemel","given":"L. E.","affiliations":[],"preferred":false,"id":394089,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Kimball, B. A.","contributorId":87583,"corporation":false,"usgs":false,"family":"Kimball","given":"B.","email":"","middleInitial":"A.","affiliations":[],"preferred":false,"id":394088,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Bencala, K.E.","contributorId":105312,"corporation":false,"usgs":true,"family":"Bencala","given":"K.E.","email":"","affiliations":[],"preferred":false,"id":394090,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
,{"id":70022558,"text":"70022558 - 2000 - Composition of fish communities in relation to stream acidification and habitat in the Neversink River, New York","interactions":[],"lastModifiedDate":"2022-07-05T13:32:10.035826","indexId":"70022558","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":3624,"text":"Transactions of the American Fisheries Society","active":true,"publicationSubtype":{"id":10}},"title":"Composition of fish communities in relation to stream acidification and habitat in the Neversink River, New York","docAbstract":"<p>The effects of acidification in lotic systems are not well documented. Spatial and temporal variability of habitat and water quality complicate the evaluation of acidification effects in streams and rivers. The Neversink River in the Catskill Mountains of southeastern New York, the tributaries of which vary from well buffered to severely acidified, provided an opportunity to investigate the extent and magnitude of acidification effects on fish communities of headwater systems. Composition of fish communities, water quality, stream hydrology, stream habitat, and physiographic factors were characterized from 1991 to 1995 at 16 first- to fourth-order sites in the basin. Correlation and regression analyses were used to develop empirical models and to assess the relations among fish species richness, total fish density, and total fish biomass and environmental variables. Chronic and episodic acidification and elevated concentrations of inorganic monomeric aluminum were common, and fish populations were rare or absent from several sites in the upper reaches of the basin; as many as six fish species were collected from sites in the lower reaches of the basin. Species distributions and species richness were most highly related to stream pH, acid-neutralizing capacity (ANC), inorganic monomeric aluminum (Al<sub>im</sub>), calcium (Ca)<sup>2+</sup>, and potassium (K)<sup>+</sup><span>&nbsp;</span>concentrations, site elevation, watershed drainage area, and water temperature. Fish density was most highly related to stream pH, Al<sub>im</sub>, ANC, K<sup>+</sup>, Ca<sup>2+</sup>, and magnesium (Mg)<sup>2+</sup><span>&nbsp;</span>concentrations. Fish biomass, unlike species richness and fish density, was most highly related to physical habitat characteristics, water temperature, and concentrations of Mg<sup>2+</sup><span>&nbsp;</span>and silicon. Acidity characteristics were of secondary importance to fish biomass at all but the most severely acidified sites. Our results indicate that (1) the total biomass of fish communities was not seriously affected at moderately to strongly acidified sites; (2) species richness and total density of fish were adversely affected at strongly to severely acidified sites; and (3) possible changes in competitive interactions may mitigate negative effects of acidification on fish communities in parts of the Neversink River Basin.</p>","language":"English","publisher":"American Fisheries Society","doi":"10.1577/1548-8659(2000)129<0060:COFCIR>2.0.CO;2","issn":"00028487","usgsCitation":"Baldigo, B., and Lawrence, G., 2000, Composition of fish communities in relation to stream acidification and habitat in the Neversink River, New York: Transactions of the American Fisheries Society, v. 129, no. 1, p. 60-76, https://doi.org/10.1577/1548-8659(2000)129<0060:COFCIR>2.0.CO;2.","productDescription":"17 p.","startPage":"60","endPage":"76","costCenters":[],"links":[{"id":230655,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"New York","otherGeospatial":"Catskill Mountains, Neversink River","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"type\": \"Polygon\",\n        \"coordinates\": [\n          [\n            [\n              -74.63424682617188,\n              41.87416255688654\n            ],\n            [\n              -74.61708068847656,\n              41.870583462266836\n            ],\n            [\n              -74.5803451538086,\n              41.88617662305848\n            ],\n            [\n              -74.56146240234375,\n              41.914796782203275\n            ],\n            [\n              -74.5037841796875,\n              41.930379151500844\n            ],\n            [\n              -74.47460174560545,\n              41.94953258640636\n            ],\n            [\n              -74.41932678222656,\n              41.95029860413908\n            ],\n            [\n              -74.38362121582031,\n              41.95949009892467\n            ],\n            [\n              -74.41761016845703,\n              42.018947439899584\n            ],\n            [\n              -74.50241088867188,\n              41.99879430655651\n            ],\n            [\n              -74.58549499511719,\n              41.955149836015146\n            ],\n            [\n              -74.59579467773438,\n              41.90304362629451\n            ],\n            [\n              -74.63768005371094,\n              41.88745458227552\n            ],\n            [\n              -74.63424682617188,\n              41.87416255688654\n            ]\n          ]\n        ]\n      }\n    }\n  ]\n}","volume":"129","issue":"1","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"5059f928e4b0c8380cd4d481","contributors":{"authors":[{"text":"Baldigo, Barry P. 0000-0002-9862-9119","orcid":"https://orcid.org/0000-0002-9862-9119","contributorId":25174,"corporation":false,"usgs":true,"family":"Baldigo","given":"Barry P.","affiliations":[{"id":474,"text":"New York Water Science Center","active":true,"usgs":true}],"preferred":true,"id":394073,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Lawrence, G.B. 0000-0002-8035-2350","orcid":"https://orcid.org/0000-0002-8035-2350","contributorId":76347,"corporation":false,"usgs":true,"family":"Lawrence","given":"G.B.","affiliations":[],"preferred":false,"id":394074,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":70022523,"text":"70022523 - 2000 - Negative pH and extremely acidic mine waters from Iron Mountain, California","interactions":[],"lastModifiedDate":"2018-12-07T05:58:04","indexId":"70022523","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":1565,"text":"Environmental Science & Technology","onlineIssn":"1520-5851","printIssn":"0013-936X","active":true,"publicationSubtype":{"id":10}},"title":"Negative pH and extremely acidic mine waters from Iron Mountain, California","docAbstract":"Extremely acidic mine waters with pH values as low as -3.6, total dissolved metal concentrations as high as 200 g/L, and sulfate concentrations as high as 760 g/L, have been encountered underground in the Richmond Mine at Iron Mountain, CA. These are the most acidic waters known. The pH measurements were obtained by using the Pitzer method to define pH for calibration of glass membrane electrodes. The calibration of pH below 0.5 with glass membrane electrodes becomes strongly nonlinear but is reproducible to a pH as low as -4. Numerous efflorescent minerals were found forming from these acid waters. These extreme acid waters were formed primarily by pyrite oxidation and concentration by evaporation with minor effects from aqueous ferrous iron oxidation and efflorescent mineral formation.","language":"English","publisher":"ACS","doi":"10.1021/es990646v","issn":"0013936X","usgsCitation":"Nordstrom, D.K., Alpers, C.N., Ptacek, C., and Blowes, D., 2000, Negative pH and extremely acidic mine waters from Iron Mountain, California: Environmental Science & Technology, v. 34, no. 2, p. 254-258, https://doi.org/10.1021/es990646v.","productDescription":"5 p.","startPage":"254","endPage":"258","costCenters":[{"id":154,"text":"California Water Science Center","active":true,"usgs":true},{"id":589,"text":"Toxic Substances Hydrology Program","active":true,"usgs":true}],"links":[{"id":230727,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"},{"id":206759,"rank":9999,"type":{"id":10,"text":"Digital Object Identifier"},"url":"https://dx.doi.org/10.1021/es990646v"}],"volume":"34","issue":"2","noUsgsAuthors":false,"publicationDate":"1999-12-10","publicationStatus":"PW","scienceBaseUri":"505a643ae4b0c8380cd72942","contributors":{"authors":[{"text":"Nordstrom, D. Kirk 0000-0003-3283-5136 dkn@usgs.gov","orcid":"https://orcid.org/0000-0003-3283-5136","contributorId":749,"corporation":false,"usgs":true,"family":"Nordstrom","given":"D.","email":"dkn@usgs.gov","middleInitial":"Kirk","affiliations":[{"id":37277,"text":"WMA - Earth System Processes Division","active":true,"usgs":true},{"id":5044,"text":"National Research Program - Central Branch","active":true,"usgs":true}],"preferred":false,"id":393939,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Alpers, Charles N. 0000-0001-6945-7365 cnalpers@usgs.gov","orcid":"https://orcid.org/0000-0001-6945-7365","contributorId":411,"corporation":false,"usgs":true,"family":"Alpers","given":"Charles","email":"cnalpers@usgs.gov","middleInitial":"N.","affiliations":[{"id":154,"text":"California Water Science Center","active":true,"usgs":true}],"preferred":true,"id":393940,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Ptacek, C.J.","contributorId":88616,"corporation":false,"usgs":true,"family":"Ptacek","given":"C.J.","affiliations":[],"preferred":false,"id":393938,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Blowes, D.W.","contributorId":21392,"corporation":false,"usgs":true,"family":"Blowes","given":"D.W.","email":"","affiliations":[],"preferred":false,"id":393937,"contributorType":{"id":1,"text":"Authors"},"rank":4}]}}
,{"id":70022522,"text":"70022522 - 2000 - Debris flow monitoring in the Acquabona watershed on the Dolomites (Italian Alps)","interactions":[],"lastModifiedDate":"2022-08-16T18:05:08.732868","indexId":"70022522","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":3068,"text":"Physics and Chemistry of the Earth, Part B: Hydrology, Oceans and Atmosphere","active":true,"publicationSubtype":{"id":10}},"title":"Debris flow monitoring in the Acquabona watershed on the Dolomites (Italian Alps)","docAbstract":"<p id=\"SP0005\">In 1997 a field monitoring system was installed in Acquabona Creek in the Dolomites (Eastern Italian Alps) to observe the hydrologic conditions for debris flow occurrence and some dynamic properties of debris flow. The monitoring system consists of three remote stations: an upper one located at the head of a deeply-incised channel and two others located downstream. The system is equipped with sensors for measuring rainfall, pore pressures in the mobile channel bottom, ground vibrations, debris flow depth, total normal stress and fluid pore-pressure at the base of the flow. Two video cameras record events at the upper channel station and one video is installed at the lowermost station. During summer 1998, three debris flows (volumes from less than 1000 m<sup>3</sup><span>&nbsp;</span>up to 9000 m<sup>3</sup>) occurred at Acquabona. The following results were obtained from a preliminary analysis of the data: 1) All of the flows were triggered by rainfalls of less than 1 hour duration, with peak rainfall intensities ranging from 4.8 to 14.7 mm / 10 minute. 2) Debris flows initiated in several reaches of the channel, including the head of the talus slope. 3) The initial surges of the mature flows had a higher solid concentration and a lower velocity (up to 4 m/s) than succeeding, more dilute surges (more than 7 m/s). 4) Total normal stress and pore fluid pressures measured at the base of the flow. (mean depth about 1.1 m) were similar (about 15 kPa), indicating a completely liquefied flow. 5) Peak flows entrained debris at a rate of about 6 m 3/m of channel length and channel bed scouring was proportional to the local slope gradient and was still evident in the lower channel where the slope was 7°.</p>","language":"English","publisher":"Elsevier","doi":"10.1016/S1464-1909(00)00090-3","issn":"14641909","usgsCitation":"Berti, M., Genevois, R., LaHusen, R., Simoni, A., and Tecca, P., 2000, Debris flow monitoring in the Acquabona watershed on the Dolomites (Italian Alps): Physics and Chemistry of the Earth, Part B: Hydrology, Oceans and Atmosphere, v. 25, no. 9, p. 707-715, https://doi.org/10.1016/S1464-1909(00)00090-3.","productDescription":"9 p.","startPage":"707","endPage":"715","costCenters":[],"links":[{"id":230726,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"Italy","otherGeospatial":"Acquabona Creek, Alps, Boite River, Dolomites","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"type\": \"Polygon\",\n        \"coordinates\": [\n          [\n            [\n              12.126502990722656,\n              46.48231911886259\n            ],\n            [\n              12.214393615722654,\n              46.48231911886259\n            ],\n            [\n              12.214393615722654,\n              46.521784367720734\n            ],\n            [\n              12.126502990722656,\n              46.521784367720734\n            ],\n            [\n              12.126502990722656,\n              46.48231911886259\n            ]\n          ]\n        ]\n      }\n    }\n  ]\n}","volume":"25","issue":"9","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"5059fdf0e4b0c8380cd4ea0e","contributors":{"authors":[{"text":"Berti, M.","contributorId":22935,"corporation":false,"usgs":true,"family":"Berti","given":"M.","email":"","affiliations":[],"preferred":false,"id":393933,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Genevois, R.","contributorId":48728,"corporation":false,"usgs":true,"family":"Genevois","given":"R.","email":"","affiliations":[],"preferred":false,"id":393936,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"LaHusen, R.","contributorId":7446,"corporation":false,"usgs":true,"family":"LaHusen","given":"R.","email":"","affiliations":[],"preferred":false,"id":393932,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Simoni, A.","contributorId":25319,"corporation":false,"usgs":true,"family":"Simoni","given":"A.","email":"","affiliations":[],"preferred":false,"id":393935,"contributorType":{"id":1,"text":"Authors"},"rank":4},{"text":"Tecca, P.R.","contributorId":24123,"corporation":false,"usgs":true,"family":"Tecca","given":"P.R.","email":"","affiliations":[],"preferred":false,"id":393934,"contributorType":{"id":1,"text":"Authors"},"rank":5}]}}
,{"id":70022504,"text":"70022504 - 2000 - Calcite crystal growth inhibition by humic substances with emphasis on hydrophobic acids from the Florida Everglades","interactions":[],"lastModifiedDate":"2018-12-03T10:26:41","indexId":"70022504","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":1759,"text":"Geochimica et Cosmochimica Acta","active":true,"publicationSubtype":{"id":10}},"title":"Calcite crystal growth inhibition by humic substances with emphasis on hydrophobic acids from the Florida Everglades","docAbstract":"<div id=\"abstracts\" class=\"Abstracts\"><div id=\"aep-abstract-id9\" class=\"abstract author\"><div id=\"aep-abstract-sec-id10\"><p>The crystallization of calcium carbonate minerals plays an integral role in the water chemistry of terrestrial ecosystems. Humic substances, which are ubiquitous in natural waters, have been shown to reduce or inhibit calcite crystal growth in experiments. The purpose of this study is to quantify and understand the kinetic effects of hydrophobic organic acids isolated from the Florida Everglades and a fulvic acid from Lake Fryxell, Antarctica, on the crystal growth of calcite (CaCO<sub>3</sub>). Highly reproducible calcite growth experiments were performed in a sealed reactor at constant pH, temperature, supersaturation (Ω = 4.5), P<sub>CO</sub><sub>2</sub>(10<sup>−3.5</sup>atm), and ionic strength (0.1 M) with various concentrations of organic acids. Higher plant-derived aquatic hydrophobic acids from the Everglades were more effective growth inhibitors than microbially derived fulvic acid from Lake Fryxell. Organic acid aromaticity correlated strongly with growth inhibition. Molecular weight and heteroatom content correlated well with growth inhibition, whereas carboxyl content and aliphatic nature did not.</p></div></div></div>","language":"English","publisher":"Elsevier","doi":"10.1016/S0016-7037(99)00179-9","issn":"00167037","usgsCitation":"Hoch, A., Reddy, M., and Aiken, G., 2000, Calcite crystal growth inhibition by humic substances with emphasis on hydrophobic acids from the Florida Everglades: Geochimica et Cosmochimica Acta, v. 64, no. 1, p. 61-72, https://doi.org/10.1016/S0016-7037(99)00179-9.","productDescription":"12 p.","startPage":"61","endPage":"72","costCenters":[{"id":589,"text":"Toxic Substances Hydrology Program","active":true,"usgs":true}],"links":[{"id":206617,"rank":9999,"type":{"id":10,"text":"Digital Object Identifier"},"url":"https://dx.doi.org/10.1016/S0016-7037(99)00179-9"},{"id":230389,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"Florida","otherGeospatial":"Everglades ","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"type\": \"Polygon\",\n        \"coordinates\": [\n          [\n            [\n              -81.97448730468749,\n              24.943728712051445\n            ],\n            [\n              -79.99969482421875,\n              24.943728712051445\n            ],\n            [\n              -79.99969482421875,\n              26.45090222367262\n            ],\n            [\n              -81.97448730468749,\n              26.45090222367262\n            ],\n            [\n              -81.97448730468749,\n              24.943728712051445\n            ]\n          ]\n        ]\n      }\n    }\n  ]\n}","volume":"64","issue":"1","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"5059f2f3e4b0c8380cd4b4dd","contributors":{"authors":[{"text":"Hoch, A.R.","contributorId":71711,"corporation":false,"usgs":true,"family":"Hoch","given":"A.R.","email":"","affiliations":[],"preferred":false,"id":393859,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Reddy, M.M.","contributorId":24363,"corporation":false,"usgs":true,"family":"Reddy","given":"M.M.","email":"","affiliations":[],"preferred":false,"id":393858,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Aiken, G. R. 0000-0001-8454-0984","orcid":"https://orcid.org/0000-0001-8454-0984","contributorId":14452,"corporation":false,"usgs":true,"family":"Aiken","given":"G. R.","affiliations":[],"preferred":false,"id":393857,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
,{"id":70022660,"text":"70022660 - 2000 - Sediment loads and accumulation in a small riparian wetland system in northern Missouri","interactions":[],"lastModifiedDate":"2022-06-28T14:13:57.336079","indexId":"70022660","displayToPublicDate":"2000-01-01T00:00:00","publicationYear":"2000","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":3750,"text":"Wetlands","onlineIssn":"1943-6246","printIssn":"0277-5212","active":true,"publicationSubtype":{"id":10}},"title":"Sediment loads and accumulation in a small riparian wetland system in northern Missouri","docAbstract":"<p>Sediment transport and deposition along a stream in an agricultural basin (65 km<sup>2</sup>) in northern Missouri, USA were quantified as part of a long-term study to evaluate effects of silvicultural practices on the hydrology, sediment, vegetation, and wildlife characteristics of remaining forested riparian systems. Median cumulative sediment deposition, measured using feldspar clay pads, increased from August 1995 to August 1998 at a rate of about 1 cm/yr. Median deposition amounts from single floods ranged from 0.03 cm to 0.64 cm. Floodplain and riparian maintenance flows corresponded to monitored floods with calculated recurrence intervals as low as &lt;2 years. Simple linear regression models, using flood event suspendedsediment load or streamflow characteristics, explained up to 82 percent of variability in median event sediment deposition on the floodplain clay pads. There was little apparent correlation between cumulative shortterm deposition and site elevation, distance from channel, longitudinal distance, or fluvial landform type. This may be due to upstream channelization, floodplain complexity, short duration of events, or sedimentload characteristics of low-recurrence interval floods (&lt;2 to 5 years) sampled in this study. Dendrogeomorphic measurements indicated a substantial increase in the mean rate of deposition on the Long Branch Creek floodplain from about 1950 through 1980. Eighty-nine percent of the clay pad monitoring sites and all dendrogeomorphic monitoring sites experienced net positive deposition emphasizing the role of this riparian area as a net sediment storage site.</p>","language":"English","publisher":"Springer","doi":"10.1672/0277-5212(2000)020[0219:SLAAIA]2.0.CO;2","issn":"02775212","usgsCitation":"Heimann, D.C., and Roell, M.J., 2000, Sediment loads and accumulation in a small riparian wetland system in northern Missouri: Wetlands, v. 20, no. 2, p. 219-231, https://doi.org/10.1672/0277-5212(2000)020[0219:SLAAIA]2.0.CO;2.","productDescription":"13 p.","startPage":"219","endPage":"231","costCenters":[],"links":[{"id":233561,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"Missouri","county":"Macon County","otherGeospatial":"Atlanta Conservation Area","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"type\": \"Polygon\",\n        \"coordinates\": [\n          [\n            [\n              -92.50428199768066,\n              39.85500387809296\n            ],\n            [\n              -92.48042106628418,\n              39.85500387809296\n            ],\n            [\n              -92.48042106628418,\n              39.88787487783849\n            ],\n            [\n              -92.50428199768066,\n              39.88787487783849\n            ],\n            [\n              -92.50428199768066,\n              39.85500387809296\n            ]\n          ]\n        ]\n      }\n    }\n  ]\n}","volume":"20","issue":"2","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505b898fe4b08c986b316e22","contributors":{"authors":[{"text":"Heimann, David C. 0000-0003-0450-2545 dheimann@usgs.gov","orcid":"https://orcid.org/0000-0003-0450-2545","contributorId":3822,"corporation":false,"usgs":true,"family":"Heimann","given":"David","email":"dheimann@usgs.gov","middleInitial":"C.","affiliations":[{"id":36532,"text":"Central Midwest Water Science Center","active":true,"usgs":true},{"id":396,"text":"Missouri Water Science Center","active":true,"usgs":true}],"preferred":true,"id":394414,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Roell, Michael J.","contributorId":82897,"corporation":false,"usgs":true,"family":"Roell","given":"Michael","email":"","middleInitial":"J.","affiliations":[],"preferred":false,"id":394415,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
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