No abstract available.
","largerWorkType":{"id":4,"text":"Book"},"largerWorkTitle":"Atlas of the Breeding Birds of Wisconsin","largerWorkSubtype":{"id":15,"text":"Monograph"},"language":"English","publisher":"Wisconsin Society for Ornithology, Inc.","publisherLocation":"Waukesha. WI","usgsCitation":"Robbins, C., 2006, Foreword, chap. of Atlas of the Breeding Birds of Wisconsin.","productDescription":"xxii, 602 p.","startPage":"xi","costCenters":[{"id":531,"text":"Patuxent Wildlife Research Center","active":true,"usgs":true}],"links":[{"id":195893,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e49d6e4b07f02db5de157","contributors":{"editors":[{"text":"Cutright, Noel J.","contributorId":113039,"corporation":false,"usgs":true,"family":"Cutright","given":"Noel","email":"","middleInitial":"J.","affiliations":[],"preferred":false,"id":508001,"contributorType":{"id":2,"text":"Editors"},"rank":1},{"text":"Harriman, Bettie R.","contributorId":111548,"corporation":false,"usgs":true,"family":"Harriman","given":"Bettie","email":"","middleInitial":"R.","affiliations":[],"preferred":false,"id":507999,"contributorType":{"id":2,"text":"Editors"},"rank":2},{"text":"Howe, Robert W.","contributorId":112208,"corporation":false,"usgs":true,"family":"Howe","given":"Robert W.","affiliations":[],"preferred":false,"id":508000,"contributorType":{"id":2,"text":"Editors"},"rank":3}],"authors":[{"text":"Robbins, C.S.","contributorId":53907,"corporation":false,"usgs":true,"family":"Robbins","given":"C.S.","email":"","affiliations":[],"preferred":false,"id":330777,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}} ,{"id":5200303,"text":"5200303 - 2006 - Avian comparisons between Kingman and Kenilworth Marshes: Final report 2001-2004","interactions":[],"lastModifiedDate":"2012-02-02T00:15:13","indexId":"5200303","displayToPublicDate":"2009-06-08T16:49:39","publicationYear":"2006","noYear":false,"publicationType":{"id":4,"text":"Book"},"title":"Avian comparisons between Kingman and Kenilworth Marshes: Final report 2001-2004","docAbstract":"In 2001 avi-fauna was added as a parameter to be monitored as an indicator of the status and relative success of the two reconstructed freshwater tidal wetlands residing in the Anacostia River estuary in Washington, D.C. at that time. They were Kenilworth Marsh which was reconstructed in 1993 and Kingman Marsh seven years later in 2000. Other studies were already underway looking at vegetation, seeds, soils and contaminants. Even though these new wetlands were relatively small, together about 70 acres, it was felt this might be sufficient area to sustain and attract birds to the habitat. Birds have been used elsewhere as wetland indicators and we hoped they could prove useful here especially in terms of numbers and species richness. The study was conducted for almost four years (2001-2004) and was designed to ascertain if the recently reconstructed Kingman Marsh evolved similarly with respect to the avi fauna as Kenilworth which had the seven year head start. Twelve observation points were established, six at each marsh, which were to be used weekly so as to alternate the high and low tidal regimes and the observation start times. Additional notations were recorded for species while walking between observation points. The course of the study became interrupted with the incursion of resident Canada geese particularly upon the Kingman Marsh site. Goose herbivory coupled with lowered sediment elevations reduced vegetation cover at Kingman Marsh to less than one-third its intended scope while Kenilworth was barely affected. The result was actually much less impact on the bird populations than on the vegetation. In fact the additional mudflat area at Kingman may have actually helped attract some birds. Together 177 species were identified at the marshes comprising 14 taxonomic orders and 16 families, 137 species at Kingman and 164 at Kenilworth. However, Kingman actually attracted more birds than Kenilworth, whether or not Canada Geese were included. At both wetlands winter usage was significantly greater than at other seasons; however, there were more species in the spring and summer. Three functional guilds were looked at in particular: wetland users, freshwater marsh users and mudflat/shore users. Mudflat users were greatest during the winter while marsh users were greater in the fall. Additional useful data was collected relative to the Canada Goose impacts. The interruption in marsh evolution at Kingman driven by the goose herbivory precluded the opportunity to use the avifauna as an indicator of marsh restoration success.","language":"English","publisher":"[USGS Patuxent Wildlife Research Center]","publisherLocation":"[Laurel, Maryland]","collaboration":" PDF on file: 6589_Paul.pdf","usgsCitation":"Paul, M., Krafft, C., and Hammerschlag, D., 2006, Avian comparisons between Kingman and Kenilworth Marshes: Final report 2001-2004, 79.","productDescription":"79","numberOfPages":"79","costCenters":[{"id":531,"text":"Patuxent Wildlife Research Center","active":true,"usgs":true}],"links":[{"id":195890,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"},{"id":91975,"rank":300,"type":{"id":11,"text":"Document"},"url":"https://www.pwrc.usgs.gov/resshow/hammerschlag/FINAL%20VERSION_Avian%20Study.pdf","linkFileType":{"id":1,"text":"pdf"}}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4a82e4b07f02db64af7b","contributors":{"authors":[{"text":"Paul, M.","contributorId":100096,"corporation":false,"usgs":true,"family":"Paul","given":"M.","email":"","affiliations":[],"preferred":false,"id":327469,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Krafft, C.","contributorId":32263,"corporation":false,"usgs":true,"family":"Krafft","given":"C.","email":"","affiliations":[],"preferred":false,"id":327468,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Hammerschlag, D.","contributorId":17335,"corporation":false,"usgs":true,"family":"Hammerschlag","given":"D.","email":"","affiliations":[],"preferred":false,"id":327467,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}} ,{"id":5200305,"text":"5200305 - 2006 - Final report (2002-2004): Benthic macroinvertebrate communities of reconstructed freshwater tidal wetlands in the Anacostia River, Washington, D.C","interactions":[],"lastModifiedDate":"2012-02-02T00:15:15","indexId":"5200305","displayToPublicDate":"2009-06-08T16:49:39","publicationYear":"2006","noYear":false,"publicationType":{"id":4,"text":"Book"},"title":"Final report (2002-2004): Benthic macroinvertebrate communities of reconstructed freshwater tidal wetlands in the Anacostia River, Washington, D.C","docAbstract":"Considerable work has been conducted on the benthic communities of inland aquatic systems, but there remains a paucity of effort on freshwater tidal wetlands. This study characterized the benthic macroinvertebrate communities of recently reconstructed urban freshwater tidal wetlands along the Anacostia River in Washington, D.C. The focus of the study was on the two main areas of Kingman Marsh, which were reconstructed by the U.S. Army Corps of Engineers in 2000 using Anacostia dredge material. Populations from this 'new' marsh were compared to those of similarly reconstructed Kenilworth Marsh (1993) just one half mile upstream, the relic reference Dueling Creek Marsh in the upper Anacostia estuary and the outside reference Patuxent freshwater tidal marsh in an adjacent watershed. Benthic macro invertebrate organisms were collected using selected techniques for evaluation including the Ekman bottom grab sampler, sediment corer, D-net and Hester-Dendy sampler. Samples were collected at least seasonally from tidal channels, tidal mudflats, three vegetation/sediment zones (low, middle and high marsh), and pools over a 3-year period (late 2001-2004). The macroinvertebrate communities present at the marsh sites proved to be good indicators of disturbance and stress (Kingman Marsh), pollution, urban vs. rural location (Kenilworth and Patuxent), and similarities between reconstructed and remnant wetlands (Kenilworth and Dueling Creek). Macroinvertebrate density was significantly greater at Kingman Marsh than Kenilworth Marsh due to more numerous chironomids and oligochaetes. This may reflect an increase in unvegetated sediments at Kingman (even at elevations above natural mudflat) due to grazing pressure from over-abundant resident Canada geese. Unvegetated sediments yielded greater macroinvertebrate abundance but lower richness than vegetated marsh sites. Data collected from this study provides information on the extent that benthic macroinvertebrate communities can serve as indicators of the relative success of freshwater tidal marsh reconstruction.","language":"English","publisher":"[USGS Patuxent Wildlife Research Center]","publisherLocation":"[Laurel, Maryland]","collaboration":" PDF on file: 6591_Brittingham.pdf","usgsCitation":"Brittingham, K., and Hammerschlag, R., 2006, Final report (2002-2004): Benthic macroinvertebrate communities of reconstructed freshwater tidal wetlands in the Anacostia River, Washington, D.C, 50.","productDescription":"50","numberOfPages":"50","costCenters":[{"id":531,"text":"Patuxent Wildlife Research Center","active":true,"usgs":true}],"links":[{"id":91976,"rank":300,"type":{"id":11,"text":"Document"},"url":"https://www.pwrc.usgs.gov/resshow/hammerschlag/Final%20Benthic%20Report_0706.pdf","linkFileType":{"id":1,"text":"pdf"}},{"id":201426,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4ae0e4b07f02db6883d9","contributors":{"authors":[{"text":"Brittingham, K.D.","contributorId":75663,"corporation":false,"usgs":true,"family":"Brittingham","given":"K.D.","email":"","affiliations":[],"preferred":false,"id":327478,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Hammerschlag, R.S.","contributorId":78050,"corporation":false,"usgs":true,"family":"Hammerschlag","given":"R.S.","email":"","affiliations":[],"preferred":false,"id":327479,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}} ,{"id":5200304,"text":"5200304 - 2006 - Final Report: Five years of monitoring reconstructed freshwater tidal wetlands in the urban Anacostia River (2000-2004)","interactions":[],"lastModifiedDate":"2012-02-02T00:15:16","indexId":"5200304","displayToPublicDate":"2009-06-08T16:49:39","publicationYear":"2006","noYear":false,"publicationType":{"id":4,"text":"Book"},"title":"Final Report: Five years of monitoring reconstructed freshwater tidal wetlands in the urban Anacostia River (2000-2004)","docAbstract":"The Anacostia River in Washington, D.C. USA consisted of over 809 hectares (2000 acres) of freshwater tidal wetlands before mandatory dredging removed most of them in the first half of the 20th century. Much of this13 kilometer (8 mile) reach was transferred to the National Park Service (NPS). Planning processes in the 1980?s envisioned a restoration (rejuvenation) of some wetlands for habitat, aesthetics, water quality and interpretative purposes. Subsequently, the U.S. Army Corps of Engineers in a cost share agreement with the District of Columbia reconstructed wetlands on NPS lands at Kenilworth - 12.5 hectares (1993), Kingman - 27 hectares (2000), a Fringe Marsh - 6.5 hectares (2003) and is currently constructing Heritage Marsh - 2.5 hectares (2005/2006). The USGS Patuxent Wildlife Research Center in conjunction with the University of Maryland Biological Engineering Department was contracted to conduct post-reconstruction monitoring (2000-2004) to document the relative success and progress of the Kingman Marsh reconstruction primarily based on vegetative response but also in conjunction with seed bank and soil characteristics. Results from Kingman were compared to Kenilworth Marsh (reconstructed 7 years prior), Dueling Creek Marsh (last best remaining freshwater tidal wetland bench in the urbanized Anacostia watershed) and Patuxent River Marsh (in a more natural adjacent watershed). Vegetation establishment was initially strong at Kingman, but declined rapidly as measured by cover, richness, diversity , etc. under grazing pressure from resident Canada geese and associated reduction in sediment levels. This decline did not occur at the other wetlands. The decline occurred despite a substantial seed bank that was sustained primarily be water born propagules. Soil development, as true for most juvenile wetlands, was slow with almost no organic matter accumulation. By 2004 only two of 7 planted species remained (mostly Peltandra virginica) at Kingman which did provide almost 50% of the approximately 1/3 total vegetation cover remaining.","language":"English","publisher":"[USGS Patuxent Wildlife Research Center]","publisherLocation":"[Laurel, Maryland]","collaboration":" PDF on file: 6590_Hammerschlag.pdf 6.2 MB","usgsCitation":"Hammerschlag, R., Baldwin, A., Krafft, C., Neff, K.P., Paul, M., Brittingham, K., Rusello, K., and Hatfield, J., 2006, Final Report: Five years of monitoring reconstructed freshwater tidal wetlands in the urban Anacostia River (2000-2004), 101.","productDescription":"101","numberOfPages":"101","costCenters":[{"id":531,"text":"Patuxent Wildlife Research Center","active":true,"usgs":true}],"links":[{"id":201430,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e49fbe4b07f02db5f484d","contributors":{"authors":[{"text":"Hammerschlag, R.S.","contributorId":78050,"corporation":false,"usgs":true,"family":"Hammerschlag","given":"R.S.","email":"","affiliations":[],"preferred":false,"id":327473,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Baldwin, A.H.","contributorId":24064,"corporation":false,"usgs":true,"family":"Baldwin","given":"A.H.","email":"","affiliations":[],"preferred":false,"id":327470,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Krafft, C.C.","contributorId":82425,"corporation":false,"usgs":true,"family":"Krafft","given":"C.C.","email":"","affiliations":[],"preferred":false,"id":327475,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Neff, K. P.","contributorId":91969,"corporation":false,"usgs":true,"family":"Neff","given":"K.","email":"","middleInitial":"P.","affiliations":[],"preferred":false,"id":327477,"contributorType":{"id":1,"text":"Authors"},"rank":4},{"text":"Paul, M.M.","contributorId":89262,"corporation":false,"usgs":true,"family":"Paul","given":"M.M.","email":"","affiliations":[],"preferred":false,"id":327476,"contributorType":{"id":1,"text":"Authors"},"rank":5},{"text":"Brittingham, K.D.","contributorId":75663,"corporation":false,"usgs":true,"family":"Brittingham","given":"K.D.","email":"","affiliations":[],"preferred":false,"id":327472,"contributorType":{"id":1,"text":"Authors"},"rank":6},{"text":"Rusello, K.","contributorId":79595,"corporation":false,"usgs":true,"family":"Rusello","given":"K.","email":"","affiliations":[],"preferred":false,"id":327474,"contributorType":{"id":1,"text":"Authors"},"rank":7},{"text":"Hatfield, Jeff S.","contributorId":41372,"corporation":false,"usgs":true,"family":"Hatfield","given":"Jeff S.","affiliations":[],"preferred":false,"id":327471,"contributorType":{"id":1,"text":"Authors"},"rank":8}]}} ,{"id":5200313,"text":"5200313 - 2006 - Migration, home range, and important use areas of Florida sub-adult bald eagles","interactions":[],"lastModifiedDate":"2012-02-02T00:15:18","indexId":"5200313","displayToPublicDate":"2009-06-08T16:49:39","publicationYear":"2006","noYear":false,"publicationType":{"id":4,"text":"Book"},"title":"Migration, home range, and important use areas of Florida sub-adult bald eagles","docAbstract":"Long distance movements of Bald Eagles (Haliaeetus leucocephalus) have prevented a thorough documentation of their migration when monitored with traditional methods of banding and radio telemetry. I used satellite telemetry to determine diurnal and nocturnal important use areas (IUAs), migration routes, stopover sites, and home ranges of 69 migratory and non-migratory Florida sub-adult Bald Eagles. I located 151 daytime IUAs in 20 states and provinces, and 50 nocturnal roosts in 8 states and provinces. There was no difference in coarse home range size of migratory eagles between sexes in winter or summer (2-way ANOVA sex x season). Coarse home ranges were larger in winter ( x = 25,218 km2, 95% CI: 13,015 ? 37,421) than summer ( x = 6,166 km2, 95% CI: 2,696 ? 9,637; F1,64 = 4.03, P = 0.01). Eagles made equal use of Coastal Plain (n = 24) and Appalachian Mountain (n = 26) migratory routes during the first migration north. I recommend conserving nocturnal roosts and undeveloped shoreline forest within IUAs for sustained recruitment of Florida Bald Eagles.","language":"English","publisher":"M.S. thesis, University of Georgia","publisherLocation":"Athens, Georgia","collaboration":"Partically funded by Patuxent. PDF on file: 6652_Mojica.pdf","usgsCitation":"Mojica, E., 2006, Migration, home range, and important use areas of Florida sub-adult bald eagles, ix, 87.","productDescription":"ix, 87","costCenters":[{"id":531,"text":"Patuxent Wildlife Research Center","active":true,"usgs":true}],"links":[{"id":201318,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4a60e4b07f02db635581","contributors":{"authors":[{"text":"Mojica, E.K.","contributorId":10513,"corporation":false,"usgs":true,"family":"Mojica","given":"E.K.","affiliations":[],"preferred":false,"id":327514,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}} ,{"id":5200306,"text":"5200306 - 2006 - Contaminant exposure and potential effects on terrestrial vertebrates residing in the National Capital Region network and Mid-Atlantic network","interactions":[],"lastModifiedDate":"2016-05-04T08:59:19","indexId":"5200306","displayToPublicDate":"2009-06-08T16:49:39","publicationYear":"2006","noYear":false,"publicationType":{"id":18,"text":"Report"},"title":"Contaminant exposure and potential effects on terrestrial vertebrates residing in the National Capital Region network and Mid-Atlantic network","docAbstract":"On September 17 and 18, 2001, samples of settled dust and airfall debris were collected from 34 sites within a 1-km radius of the WTC collapse site, including a sample from an indoor location unaffected by rainfall, and samples of insulation from two steel beams at Ground Zero. Laboratory spectral and x-ray diffraction analyses of the field samples detected trace levels of serpentine minerals, including chrysotile asbestos, in about two-thirds of the dust samples at concentrations at or below ~1 wt%. One sample of a beam coating material contained up to 20 wt% chrysotile asbestos. Analyses indicate that trace levels of chrysotile were distributed with the dust radially to distances greater than 0.75 km from Ground Zero. The chrysotile content of the dust is variable and may indicate that chrysotile asbestos was not distributed uniformly during the three collapse events.
","largerWorkType":{"id":4,"text":"Book"},"largerWorkTitle":"Urban Aerosols and Their Impacts","largerWorkSubtype":{"id":15,"text":"Monograph"},"language":"English","publisher":"American Chemical Society","publisherLocation":"Washington, D.C.","doi":"10.1021/bk-2006-0919.ch003","usgsCitation":"Swayze, G.A., Clark, R.N., Sutley, S.J., Hoefen, T.M., Plumlee, G.S., Meeker, G.P., Brownfield, I., Livo, K.E., and Morath, L.C., 2006, Spectroscopic and x-ray diffraction analyses of asbestos in the World Trade Center dust: Asbestos content of the settled dust, chap. 3 of Urban Aerosols and Their Impacts, p. 40-65, https://doi.org/10.1021/bk-2006-0919.ch003.","productDescription":"26 p.","startPage":"40","endPage":"65","numberOfPages":"26","onlineOnly":"N","additionalOnlineFiles":"N","costCenters":[{"id":211,"text":"Crustal Geophysics and Geochemistry Science Center","active":true,"usgs":true}],"links":[{"id":297849,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"New York","otherGeospatial":"World Trade Center site","geographicExtents":"{\n \"type\": \"FeatureCollection\",\n \"features\": [\n {\n \"type\": \"Feature\",\n \"properties\": {},\n \"geometry\": {\n \"type\": \"Polygon\",\n \"coordinates\": [\n [\n [\n -74.02055740356445,\n 40.699901911003046\n ],\n [\n -73.99703979492188,\n 40.699901911003046\n ],\n [\n -73.99703979492188,\n 40.72202247464282\n ],\n [\n -74.02055740356445,\n 40.72202247464282\n ],\n [\n -74.02055740356445,\n 40.699901911003046\n ]\n ]\n ]\n }\n }\n ]\n}","noUsgsAuthors":false,"publicationDate":"2009-07-23","publicationStatus":"PW","scienceBaseUri":"54dd2c5fe4b08de9379b3763","contributors":{"authors":[{"text":"Swayze, Gregg A. 0000-0002-1814-7823 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J.","contributorId":60296,"corporation":false,"usgs":true,"family":"Sutley","given":"Stephen","email":"","middleInitial":"J.","affiliations":[],"preferred":false,"id":540127,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Hoefen, Todd M. 0000-0002-3083-5987 thoefen@usgs.gov","orcid":"https://orcid.org/0000-0002-3083-5987","contributorId":403,"corporation":false,"usgs":true,"family":"Hoefen","given":"Todd","email":"thoefen@usgs.gov","middleInitial":"M.","affiliations":[{"id":171,"text":"Central Mineral and Environmental Resources Science Center","active":true,"usgs":true},{"id":211,"text":"Crustal Geophysics and Geochemistry Science Center","active":true,"usgs":true}],"preferred":true,"id":540128,"contributorType":{"id":1,"text":"Authors"},"rank":4},{"text":"Plumlee, Geoffrey S. 0000-0002-9607-5626 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