{"pageNumber":"2032","pageRowStart":"50775","pageSize":"25","recordCount":68919,"records":[{"id":5223355,"text":"5223355 - 1984 - Residues of organochlorine insecticides, polychlorinated biphenyls, and heavy metals in biota from Apalachicola River, Florida, 1978","interactions":[],"lastModifiedDate":"2024-05-14T15:39:24.933335","indexId":"5223355","displayToPublicDate":"2010-06-16T12:19:29","publicationYear":"1984","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":2533,"text":"Journal of the Association of Official Analytical Chemists","active":true,"publicationSubtype":{"id":10}},"title":"Residues of organochlorine insecticides, polychlorinated biphenyls, and heavy metals in biota from Apalachicola River, Florida, 1978","docAbstract":"<p><span>Seventy-seven composite samples composed of largemouth bass (</span><i>Micropterus salmoides</i><span>), channel catfish (</span><i>Ictaluras punctatus</i><span>), threadfin shad (</span><i>Dorosoma petenense</i><span>), Asiatic clam (</span><i>Corbicula fluminea</i><span>), burrowing mayfly (</span><i>Hexagenia</i><span>&nbsp;sp.), water snake (</span><i>Natrix</i><span>&nbsp;spp.), and little green heron (</span><i>Butorides virescens</i><span>) were collected from upper and lower reaches of the Apalachicola River, Florida, in 1978 for residue analysis of organochlorine insecticides, PCBs (polychlorinated biphenyls), and metals. Compared with data from the National Pesticide Monitoring Program and criteria recommended for the protection of aquatic life, residue concentrations were moderately high in the Apalachicola River. Biota from the upper river generally had higher organic and lower metal residues than those from the lower river. Highest residues in the biota were total DDT, total PCBs, and toxaphene. Although individual mean concentrations were below 2 μg/g and total organic contaminant residues never exceeded 5 μg/g, residue concentrations of DDT, PCBs, and toxaphene (particularly from the upper river) exceeded recommended permissible levels for the protection of aquatic life. Metal residues were generally below 1 μg/g. Exceptions were arsenic residues in threadfin shad (1.07 μg/g) and Asiatic clams (1.75 μg/g), and selenium in eggs of channel catfish (1.39 μg/g). The residues observed in the biota, particularly from the upper station, indicated moderate contamination of the Apalachicola River system at the time samples were collected.</span></p>","language":"English","publisher":"Association of Official Analytical Chemists","doi":"10.1093/jaoac/67.2.325","usgsCitation":"Winger, P.V., Sieckman, C., May, T., and Johnson, W., 1984, Residues of organochlorine insecticides, polychlorinated biphenyls, and heavy metals in biota from Apalachicola River, Florida, 1978: Journal of the Association of Official Analytical Chemists, v. 67, p. 325-333, https://doi.org/10.1093/jaoac/67.2.325.","productDescription":"9 p.","startPage":"325","endPage":"333","numberOfPages":"9","costCenters":[{"id":531,"text":"Patuxent Wildlife Research Center","active":true,"usgs":true}],"links":[{"id":486958,"rank":2,"type":{"id":40,"text":"Open Access Publisher Index Page"},"url":"https://doi.org/10.1093/jaoac/67.2.325","text":"Publisher Index Page"},{"id":199757,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"67","noUsgsAuthors":false,"publicationDate":"2020-02-15","publicationStatus":"PW","scienceBaseUri":"4f4e4a53e4b07f02db62b936","contributors":{"authors":[{"text":"Winger, P. V.","contributorId":43075,"corporation":false,"usgs":true,"family":"Winger","given":"P.","email":"","middleInitial":"V.","affiliations":[],"preferred":false,"id":338513,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Sieckman, C.","contributorId":16130,"corporation":false,"usgs":true,"family":"Sieckman","given":"C.","email":"","affiliations":[],"preferred":false,"id":338511,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"May, T.W.","contributorId":75878,"corporation":false,"usgs":true,"family":"May","given":"T.W.","email":"","affiliations":[],"preferred":false,"id":338514,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Johnson, W.W.","contributorId":20032,"corporation":false,"usgs":true,"family":"Johnson","given":"W.W.","email":"","affiliations":[],"preferred":false,"id":338512,"contributorType":{"id":1,"text":"Authors"},"rank":4}]}}
,{"id":5222485,"text":"5222485 - 1984 - Compensatory mortality in waterfowl populations:  A review of the evidence and implications for research and management","interactions":[],"lastModifiedDate":"2012-02-02T00:14:44","indexId":"5222485","displayToPublicDate":"2010-06-16T12:19:24","publicationYear":"1984","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":3638,"text":"Transactions of the North American Wildlife and Natural Resources Conference","active":true,"publicationSubtype":{"id":10}},"title":"Compensatory mortality in waterfowl populations:  A review of the evidence and implications for research and management","largerWorkType":{"id":2,"text":"Article"},"largerWorkTitle":"Transactions of the North American Wildlife and Natural Resources Conference","largerWorkSubtype":{"id":10,"text":"Journal Article"},"language":"English","usgsCitation":"Nichols, J., Conroy, M., Anderson, D., and Burnham, K., 1984, Compensatory mortality in waterfowl populations:  A review of the evidence and implications for research and management: Transactions of the North American Wildlife and Natural Resources Conference, v. 49, p. 535-554.","productDescription":"535-554","startPage":"535","endPage":"554","numberOfPages":"20","costCenters":[{"id":531,"text":"Patuxent Wildlife Research Center","active":true,"usgs":true}],"links":[{"id":197296,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"49","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4b1ee4b07f02db6aa2fd","contributors":{"authors":[{"text":"Nichols, J.D. 0000-0002-7631-2890","orcid":"https://orcid.org/0000-0002-7631-2890","contributorId":14332,"corporation":false,"usgs":true,"family":"Nichols","given":"J.D.","affiliations":[],"preferred":false,"id":336363,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Conroy, M.J.","contributorId":84690,"corporation":false,"usgs":true,"family":"Conroy","given":"M.J.","email":"","affiliations":[],"preferred":false,"id":336365,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Anderson, David R.","contributorId":8413,"corporation":false,"usgs":true,"family":"Anderson","given":"David R.","affiliations":[],"preferred":false,"id":336362,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Burnham, K.P.","contributorId":63760,"corporation":false,"usgs":true,"family":"Burnham","given":"K.P.","email":"","affiliations":[],"preferred":false,"id":336364,"contributorType":{"id":1,"text":"Authors"},"rank":4}]}}
,{"id":5221913,"text":"5221913 - 1984 - The use of auxiliary variables in capture-recapture and removal experiments","interactions":[],"lastModifiedDate":"2023-11-06T12:55:02.114418","indexId":"5221913","displayToPublicDate":"2010-06-16T12:19:24","publicationYear":"1984","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":1039,"text":"Biometrics","active":true,"publicationSubtype":{"id":10}},"title":"The use of auxiliary variables in capture-recapture and removal experiments","docAbstract":"The dependence of animal capture probabilities on auxiliary variables is an important practical problem which has not been considered in the development of estimation procedures for capture-recapture and removal experiments.  In this paper the linear logistic binary regression model is used to relate the probability of capture to continuous auxiliary variables.  The auxiliary variables could be environmental quantities such as air or water temperature, or characteristics of individual animals, such as body length or weight.  Maximum likelihood estimators of the population parameters are considered for a variety of models which all assume a closed population.  Testing between models is also considered.  The models can also be used when one auxiliary variable is a measure of the effort expended in obtaining the sample.","language":"English","publisher":"International Biometric Society","doi":"10.2307/2531386","usgsCitation":"Pollock, K.H., Hines, J., and Nichols, J., 1984, The use of auxiliary variables in capture-recapture and removal experiments: Biometrics, v. 40, no. 2, p. 329-340, https://doi.org/10.2307/2531386.","productDescription":"12 p.","startPage":"329","endPage":"340","numberOfPages":"12","costCenters":[{"id":531,"text":"Patuxent Wildlife Research Center","active":true,"usgs":true}],"links":[{"id":197421,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"40","issue":"2","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4a14e4b07f02db602ba2","contributors":{"authors":[{"text":"Pollock, K. H.","contributorId":65184,"corporation":false,"usgs":false,"family":"Pollock","given":"K.","email":"","middleInitial":"H.","affiliations":[],"preferred":false,"id":335006,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Hines, J.E. 0000-0001-5478-7230","orcid":"https://orcid.org/0000-0001-5478-7230","contributorId":36885,"corporation":false,"usgs":true,"family":"Hines","given":"J.E.","affiliations":[{"id":531,"text":"Patuxent Wildlife Research Center","active":true,"usgs":true}],"preferred":false,"id":335005,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Nichols, J.D. 0000-0002-7631-2890","orcid":"https://orcid.org/0000-0002-7631-2890","contributorId":14332,"corporation":false,"usgs":true,"family":"Nichols","given":"J.D.","affiliations":[],"preferred":false,"id":335004,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
,{"id":5221994,"text":"5221994 - 1984 - Monitoring colonial waterbird populations in the Northeast: Historical and future perspectives","interactions":[],"lastModifiedDate":"2012-02-02T00:14:49","indexId":"5221994","displayToPublicDate":"2010-06-16T12:19:19","publicationYear":"1984","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":3639,"text":"Transactions of the Northeast Fish and Wildlife Conference","active":true,"publicationSubtype":{"id":10}},"title":"Monitoring colonial waterbird populations in the Northeast: Historical and future perspectives","largerWorkType":{"id":2,"text":"Article"},"largerWorkTitle":"Transactions of the Northeast Fish and Wildlife Conference","largerWorkSubtype":{"id":10,"text":"Journal Article"},"language":"English","usgsCitation":"Erwin, R., 1984, Monitoring colonial waterbird populations in the Northeast: Historical and future perspectives: Transactions of the Northeast Fish and Wildlife Conference, v. 41, p. 97-109.","productDescription":"97-109","startPage":"97","endPage":"109","numberOfPages":"13","costCenters":[{"id":531,"text":"Patuxent Wildlife Research Center","active":true,"usgs":true}],"links":[{"id":197334,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"41","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4b04e4b07f02db699150","contributors":{"authors":[{"text":"Erwin, R.M.","contributorId":57396,"corporation":false,"usgs":true,"family":"Erwin","given":"R.M.","email":"","affiliations":[],"preferred":false,"id":335213,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":5221968,"text":"5221968 - 1984 - Population trends and environmental contaminants in herons in the Tennessee Valley, 1980-81","interactions":[],"lastModifiedDate":"2023-11-20T12:38:59.305317","indexId":"5221968","displayToPublicDate":"2010-06-16T12:19:19","publicationYear":"1984","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":1272,"text":"Colonial Waterbirds","printIssn":"07386028","active":false,"publicationSubtype":{"id":10}},"title":"Population trends and environmental contaminants in herons in the Tennessee Valley, 1980-81","docAbstract":"Great Blue Heron (Ardea herodias) eggs (N = 40) collected in 1980 from four of the largest colonies in the Tennessee Valley contained organochlorine pesticide, polychlorinated biphenyl (PCB), and chromium concentrations below those associated with reduced productivity.  Low concentrations of organochlorine pesticide and PCB residues also were found in eggs (N = 31) from three of the larger Black-crowned Night-Heron (Nycticorax nycticorax) colonies in the Tennessee Valley.  However, DDE concentrations in two of the Black-crowned Night-Heron eggs exceeded levels associated with reduced nesting success.  Mercury was found in all eggs of both species with residues ranging to a high of 2.0 ppm; residues  of this magnitude have not been identified as reducing nesting success of either of these two species.  Green-backed Heron (Butorides striatus) eggs collected in 1981 near a former DDT manufacturing site in the Tennessee Valley had the highest DDE concentrations ever reported for this species;  the effect of these high concentrations on productivity is not known. Eggshell thickness of Great Blue Heron, Green-backed Heron, and Black- crowned Night-Heron eggs averaged 7.5%, 7.6%, and 3% thinner, respectively, than shell thickness of eggs collected before 1947.  This amount of  thinning is not deleterious; intraclutch variation in shell thickness is often this high.  Shell thickness in all three species was correlated (P lt 0.1) with DDE concentrations.  The number of nesting pairs of Great Blue Herons and Black-crowned Night-Herons at each of the colonies studied has been stable or increasing during the previous decade. These population data, combined with the residue data, suggest that organochlorine pesticides, PCBs, mercury, and chromium are not adversely affecting these populations.  However, we did not assess nesting success which would be a  requisite for confirming this.","language":"English","publisher":"Waterbird Society","doi":"10.2307/1521083","usgsCitation":"Fleming, W.J., Pullin, B., and Swineford, D.M., 1984, Population trends and environmental contaminants in herons in the Tennessee Valley, 1980-81: Colonial Waterbirds, v. 7, no. 1, p. 63-73, https://doi.org/10.2307/1521083.","productDescription":"11 p.","startPage":"63","endPage":"73","numberOfPages":"11","costCenters":[{"id":531,"text":"Patuxent Wildlife Research Center","active":true,"usgs":true}],"links":[{"id":196246,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"7","issue":"1","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4acce4b07f02db67e615","contributors":{"authors":[{"text":"Fleming, W. James","contributorId":85279,"corporation":false,"usgs":true,"family":"Fleming","given":"W.","email":"","middleInitial":"James","affiliations":[],"preferred":false,"id":335152,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Pullin, B.P.","contributorId":106600,"corporation":false,"usgs":true,"family":"Pullin","given":"B.P.","email":"","affiliations":[],"preferred":false,"id":335153,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Swineford, D. M.","contributorId":106839,"corporation":false,"usgs":true,"family":"Swineford","given":"D.","email":"","middleInitial":"M.","affiliations":[],"preferred":false,"id":335154,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
,{"id":5221517,"text":"5221517 - 1984 - Conservation of colonial waterbirds in the Caribbean Basin: Summary of a panel discussion","interactions":[],"lastModifiedDate":"2023-11-20T12:40:21.973006","indexId":"5221517","displayToPublicDate":"2010-06-16T12:19:19","publicationYear":"1984","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":1272,"text":"Colonial Waterbirds","printIssn":"07386028","active":false,"publicationSubtype":{"id":10}},"title":"Conservation of colonial waterbirds in the Caribbean Basin: Summary of a panel discussion","docAbstract":"<p>No abstract available.</p>","language":"English","publisher":"Waterbird Society","doi":"10.2307/1521093","usgsCitation":"Erwin, R., Kushlan, J., Luthin, C., Price, I., and Sprunt, A., 1984, Conservation of colonial waterbirds in the Caribbean Basin: Summary of a panel discussion: Colonial Waterbirds, v. 7, no. 1, p. 139-142, https://doi.org/10.2307/1521093.","productDescription":"4 p.","startPage":"139","endPage":"142","numberOfPages":"4","costCenters":[{"id":531,"text":"Patuxent Wildlife Research Center","active":true,"usgs":true}],"links":[{"id":197605,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"7","issue":"1","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4b13e4b07f02db6a30c6","contributors":{"authors":[{"text":"Erwin, R.M.","contributorId":57396,"corporation":false,"usgs":true,"family":"Erwin","given":"R.M.","email":"","affiliations":[],"preferred":false,"id":334041,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Kushlan, J.A.","contributorId":18301,"corporation":false,"usgs":true,"family":"Kushlan","given":"J.A.","affiliations":[],"preferred":false,"id":334038,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Luthin, C.","contributorId":41546,"corporation":false,"usgs":true,"family":"Luthin","given":"C.","email":"","affiliations":[],"preferred":false,"id":334039,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Price, I.M.","contributorId":48278,"corporation":false,"usgs":true,"family":"Price","given":"I.M.","email":"","affiliations":[],"preferred":false,"id":334040,"contributorType":{"id":1,"text":"Authors"},"rank":4},{"text":"Sprunt, A. IV","contributorId":65561,"corporation":false,"usgs":true,"family":"Sprunt","given":"A.","suffix":"IV","email":"","affiliations":[],"preferred":false,"id":334042,"contributorType":{"id":1,"text":"Authors"},"rank":5}]}}
,{"id":5221516,"text":"5221516 - 1984 - Feeding flights of nesting wading birds at a Virginia colony","interactions":[],"lastModifiedDate":"2023-11-20T12:42:23.011669","indexId":"5221516","displayToPublicDate":"2010-06-16T12:19:19","publicationYear":"1984","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":1272,"text":"Colonial Waterbirds","printIssn":"07386028","active":false,"publicationSubtype":{"id":10}},"title":"Feeding flights of nesting wading birds at a Virginia colony","docAbstract":"Feeding flights of Snowy Egrets (Egretta thula), Tricolored Herons (E. tricolor), Little Blue Herons (E. caerulea), and Cattle Egrets (Bubulcus ibis) were monitored at a small nesting colony near Chincoteague, Virginia during late May and June 1979. All four species varied their flight directions over a series of days.  Cattle Egrets oriented in a different direction (toward uplands) from the other three wetland-feeding species, which oriented toward Spartina marsh areas.  None of the species showed a tendency to form groups while departing from or arriving at the colony.  Tide level had little influence on flight directions used.  Comparisons are made between these results and those from a similar study in coastal North  Carolina.","language":"English","publisher":"Waterbird Society","doi":"10.2307/1521084","usgsCitation":"Erwin, R., 1984, Feeding flights of nesting wading birds at a Virginia colony: Colonial Waterbirds, v. 7, no. 1, p. 74-79, https://doi.org/10.2307/1521084.","productDescription":"6 p.","startPage":"74","endPage":"79","numberOfPages":"6","costCenters":[{"id":531,"text":"Patuxent Wildlife Research Center","active":true,"usgs":true}],"links":[{"id":197604,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"Virginia","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"coordinates\": [\n          [\n            [\n              -76.66111223625715,\n              38.19295328072141\n            ],\n            [\n              -76.66111223625715,\n              36.88630319807231\n            ],\n            [\n              -75.0571083300075,\n              36.88630319807231\n            ],\n            [\n              -75.0571083300075,\n              38.19295328072141\n            ],\n            [\n              -76.66111223625715,\n              38.19295328072141\n            ]\n          ]\n        ],\n        \"type\": \"Polygon\"\n      }\n    }\n  ]\n}","volume":"7","issue":"1","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e49fde4b07f02db5f5d7e","contributors":{"authors":[{"text":"Erwin, R.M.","contributorId":57396,"corporation":false,"usgs":true,"family":"Erwin","given":"R.M.","email":"","affiliations":[],"preferred":false,"id":334037,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":5221925,"text":"5221925 - 1984 - Improving stability of annual state waterfowl harvest estimates in highly-skewed data","interactions":[],"lastModifiedDate":"2012-02-02T00:14:51","indexId":"5221925","displayToPublicDate":"2010-06-16T12:19:16","publicationYear":"1984","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":745,"text":"American Statistical Association, Proceedings of the Section on Survey Research Methods","active":true,"publicationSubtype":{"id":10}},"title":"Improving stability of annual state waterfowl harvest estimates in highly-skewed data","largerWorkType":{"id":2,"text":"Article"},"largerWorkTitle":"American Statistical Association, Proceedings of the Section on Survey Research Methods","largerWorkSubtype":{"id":10,"text":"Journal Article"},"language":"English","usgsCitation":"Moyer, L., and Geissler, P., 1984, Improving stability of annual state waterfowl harvest estimates in highly-skewed data: American Statistical Association, Proceedings of the Section on Survey Research Methods, v. 1984, p. 467-471.","productDescription":"467-471","startPage":"467","endPage":"471","numberOfPages":"5","costCenters":[{"id":531,"text":"Patuxent Wildlife Research Center","active":true,"usgs":true}],"links":[{"id":197351,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"volume":"1984","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e49fce4b07f02db5f5c5a","contributors":{"authors":[{"text":"Moyer, L.M.","contributorId":96787,"corporation":false,"usgs":true,"family":"Moyer","given":"L.M.","email":"","affiliations":[],"preferred":false,"id":335044,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Geissler, P.H.","contributorId":24038,"corporation":false,"usgs":true,"family":"Geissler","given":"P.H.","email":"","affiliations":[],"preferred":false,"id":335043,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":5210334,"text":"5210334 - 1984 - The Patuxent team","interactions":[],"lastModifiedDate":"2012-02-02T00:15:19","indexId":"5210334","displayToPublicDate":"2009-06-09T09:23:17","publicationYear":"1984","noYear":false,"publicationType":{"id":5,"text":"Book chapter"},"publicationSubtype":{"id":24,"text":"Book Chapter"},"title":"The Patuxent team","largerWorkType":{"id":4,"text":"Book"},"largerWorkTitle":"Flyways: Pioneering Waterfowl Management in North America ","largerWorkSubtype":{"id":4,"text":"Other Government Series"},"language":"English","publisher":"U.S. Fish and Wildlife Service","publisherLocation":"Washington, D.C.","usgsCitation":"Perry, M., 1984, The Patuxent team, chap. <i>of</i> Flyways: Pioneering Waterfowl Management in North America , p. 113-117.","productDescription":"xix, 517 ","startPage":"113","endPage":"117","costCenters":[{"id":531,"text":"Patuxent Wildlife Research Center","active":true,"usgs":true}],"links":[{"id":201260,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4ac7e4b07f02db67ae3b","contributors":{"editors":[{"text":"Hawkins, A.S.","contributorId":29085,"corporation":false,"usgs":true,"family":"Hawkins","given":"A.S.","email":"","affiliations":[],"preferred":false,"id":506298,"contributorType":{"id":2,"text":"Editors"},"rank":1},{"text":"Hanson, R.C.","contributorId":112565,"corporation":false,"usgs":true,"family":"Hanson","given":"R.C.","email":"","affiliations":[],"preferred":false,"id":506300,"contributorType":{"id":2,"text":"Editors"},"rank":2},{"text":"Nelson, H.K.","contributorId":21489,"corporation":false,"usgs":true,"family":"Nelson","given":"H.K.","email":"","affiliations":[],"preferred":false,"id":506297,"contributorType":{"id":2,"text":"Editors"},"rank":3},{"text":"Reeves, H.M.","contributorId":92634,"corporation":false,"usgs":true,"family":"Reeves","given":"H.M.","email":"","affiliations":[],"preferred":false,"id":506299,"contributorType":{"id":2,"text":"Editors"},"rank":4}],"authors":[{"text":"Perry, Matthew C. 0000-0001-6452-9534","orcid":"https://orcid.org/0000-0001-6452-9534","contributorId":16372,"corporation":false,"usgs":true,"family":"Perry","given":"Matthew C.","affiliations":[],"preferred":false,"id":328217,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":70039514,"text":"70039514 - 1984 - Geographic Names Information System","interactions":[],"lastModifiedDate":"2012-08-11T01:01:51","indexId":"70039514","displayToPublicDate":"2008-01-23T16:11:00","publicationYear":"1984","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":6,"text":"USGS Unnumbered Series"},"title":"Geographic Names Information System","docAbstract":"The Geographic Names Information System (GNIS) is an automated data system developed by the U.S. Geological Survey (USGS) to standardize and disseminate information on geographic names. GNIS provides primary information for all known places, features, and areas in the United States identified by a proper name. The information in the system can be manipulated to meet varied needs. You can incorporate information from GNIS into your own data base for special applications.","language":"English","publisher":"U.S. Geological Survey","publisherLocation":"Reston, VA","doi":"10.3133/70039514","usgsCitation":"Water Resources Division, U.S. Geological Survey, 1984, Geographic Names Information System, 2 p., https://doi.org/10.3133/70039514.","productDescription":"2 p.","numberOfPages":"2","costCenters":[{"id":409,"text":"National Cartographic Information Center","active":false,"usgs":true}],"links":[{"id":261642,"rank":800,"type":{"id":11,"text":"Document"},"url":"https://pubs.usgs.gov/unnumbered/70039514/report.pdf"},{"id":261643,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/unnumbered/70039514/report-thumb.jpg"}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505a1756e4b0c8380cd5548d","contributors":{"authors":[{"text":"Water Resources Division, U.S. Geological Survey","contributorId":128075,"corporation":true,"usgs":false,"organization":"Water Resources Division, U.S. Geological Survey","id":535337,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":80063,"text":"wri82508 - 1984 - Fluoride, Nitrate, and Dissolved-Solids Concentrations in Ground Waters of Washington","interactions":[],"lastModifiedDate":"2012-02-10T00:11:44","indexId":"wri82508","displayToPublicDate":"2007-06-28T00:00:00","publicationYear":"1984","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":342,"text":"Water-Resources Investigations Report","code":"WRI","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"82-508","title":"Fluoride, Nitrate, and Dissolved-Solids Concentrations in Ground Waters of Washington","docAbstract":"This study provides basic data on ground-water quality throughout the State. It is intended for uses in planning and management by agencies and individuals who have responsibility for or interest in, public health and welfare. It also provides a basis for directing future studies of ground-water quality toward areas where ground-water quality problems may already exist. The information presented is a compilation of existing data from numerous sources including: the Washington Departments of Ecology and Social and Health Services, the Environmental Protection Agency, as well as many other local, county, state and federal agencies and private corporations. Only data on fluoride, nitrate, and dissolved-solids concentrations in ground water are presented, as these constituents are among those commonly used to determine the suitability of water for drinking or other purposes. They also reflect both natural and man-imposed effects on water quality and are the most readily available water-quality data for the State of Washington. The percentage of wells with fluoride, nitrate, or dissolved-solids concentrations exceeding U.S. Environmental Protection Agency Primary and Secondary Drinking Water Regulations were about 1, about 3, and about 3, respectively. Most high concentrations occurred in widely separated wells. Two exceptions were: high concentrations of nitrate and dissolved solids in wells on the Hanford Department of Energy Facility and high concentrations of nitrate in the lower Yakima River basin. (USGS)","language":"ENGLISH","publisher":"Geological Survey (U.S.)","doi":"10.3133/wri82508","collaboration":"Prepared in cooperation with the State of Washington Department of Ecology","usgsCitation":"Lum, W.E., and Turney, G.L., 1984, Fluoride, Nitrate, and Dissolved-Solids Concentrations in Ground Waters of Washington (WRI/OFR 82-508): U.S. Geological Survey Water-Resources Investigations Report 82-508, 4 Sheets (3 maps and 1 data sheet; each sheet 21 x 27 inches), https://doi.org/10.3133/wri82508.","productDescription":"4 Sheets (3 maps and 1 data sheet; each sheet 21 x 27 inches)","costCenters":[{"id":595,"text":"U.S. Geological Survey","active":false,"usgs":true}],"links":[{"id":194716,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/usgs_thumb.jpg"},{"id":264344,"type":{"id":17,"text":"Plate"},"url":"https://pubs.usgs.gov/wri/1982/0508/plate-1.pdf","size":"3794","linkFileType":{"id":1,"text":"pdf"}},{"id":264345,"type":{"id":17,"text":"Plate"},"url":"https://pubs.usgs.gov/wri/1982/0508/plate-2.pdf","size":"3646","linkFileType":{"id":1,"text":"pdf"}},{"id":264346,"type":{"id":17,"text":"Plate"},"url":"https://pubs.usgs.gov/wri/1982/0508/plate-3.pdf","size":"3745","linkFileType":{"id":1,"text":"pdf"}},{"id":264347,"type":{"id":17,"text":"Plate"},"url":"https://pubs.usgs.gov/wri/1982/0508/plate-4.pdf","size":"3568","linkFileType":{"id":1,"text":"pdf"}}],"scale":"1000000","geographicExtents":"{ \"type\": \"FeatureCollection\", \"features\": [ { \"type\": \"Feature\", \"properties\": {}, \"geometry\": { \"type\": \"Polygon\", \"coordinates\": [ [ [ -125,45 ], [ -125,49 ], [ -116,49 ], [ -116,45 ], [ -125,45 ] ] ] } } ] }","edition":"WRI/OFR 82-508","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4b24e4b07f02db6aec01","contributors":{"authors":[{"text":"Lum, W. E. II","contributorId":81504,"corporation":false,"usgs":true,"family":"Lum","given":"W.","suffix":"II","email":"","middleInitial":"E.","affiliations":[],"preferred":false,"id":291610,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Turney, Gary L.","contributorId":72446,"corporation":false,"usgs":true,"family":"Turney","given":"Gary","email":"","middleInitial":"L.","affiliations":[],"preferred":false,"id":291609,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":80038,"text":"wri83698 - 1984 - Hydrology of Area 62, Northern Great Plains and Rocky Mountain Coal Provinces, New Mexico and Arizona","interactions":[],"lastModifiedDate":"2012-02-10T00:11:41","indexId":"wri83698","displayToPublicDate":"2007-06-20T00:00:00","publicationYear":"1984","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":342,"text":"Water-Resources Investigations Report","code":"WRI","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"83-698","title":"Hydrology of Area 62, Northern Great Plains and Rocky Mountain Coal Provinces, New Mexico and Arizona","docAbstract":"This report summarizes available hydrologic data for Area 62 and will aid leasing decisions, and the preparation and appraisal of environmental impact studies and mine-permit applications. Area 62 is located at the southern end of the Rocky Mountain Coal Province in parts of New Mexico and Arizona and includes approximately 9,500 square miles. Surface mining alters, at least temporarily, the environment; if the areas are unreclaimed, there can be long-term environmental consequences.\r\n\r\nThe land-ownership pattern in Area 62 is complicated. The checkerboard pattern created by several types of ownership makes effective management of these lands difficult.\r\n\r\nThe climate generally is semiarid with average annual precipitation ranging from 10 to 20 inches. Pinons, junipers, and grasslands cover most of the area, and much of it is used for grazing by livestock. Soils vary with landscape, differing from flood plains and hillslopes to mountain slopes.\r\n\r\nThe major structural features of this area were largely developed during middle Tertiary time. The main structural features are the southern San Juan Basin and the Mogollon slope. Coal-bearing rocks are present in four Cretaceous rock units of the Mesaverde Group: the Gallup Sandstone, the Dileo Coal Member, and the Gibson Coal Member of the Crevasse Canyon Formation, and the Cleary Coal Member of the Menefee Formation.\r\n\r\nArea 62 is drained by Black Creek, the Puerco River, the Zuni River, Carrizo Wash-Largo Creek, and the Rio San Jose. Only at the headwaters of the Zuni River is the flow perennial. The streamflow-gaging station network consists of 25 stations operated for a variety of needs. Streamflow changes throughout the year with variation related directly to rainfall and snowmelt. Base flow in Area 62 is zero indicating no significant ground-water discharge. Mountainous areas contribute the highest mean annual runoff of 1.0 inch. Very few water-quality data are available for the surface-water stations. Of the nine surface-water stations that have water-quality data, only one has chemical analyses from more than 10 samples. Therefore, sufficient data to characterize the area in detail are not available. Suspended sediment data are available only for a few surface-\r\nwater stations in the area. Erosion rates generally are less than 1 acre-foot per square mile per year. Greater erosion rates are found within the badland areas.\r\n\r\nWater levels are periodically measured at 21 selected wells in Area 62. These observation wells are located mostly along the Rio San Jose and northeast of Gallup, New Mexico. The recharge to ground-water aquifers generally coincide with areas of greater precipitation in the mountainous areas. Depth to water below land surface is generally less than 200 feet. Well yields of 100 gallons per minute are common in most of the area.\r\n\r\nGround-water quality is variable both within each aquifer and between aquifers. Water quality generally is best near recharge areas.\r\n\r\nHistorical and current data related to stream discharge, water quality, and suspended sediment are available from computer files in the U.S. Geological Survey's National Water Data Storage and Retrieval System (WATSTORE) and through the National Water Data Exchange (NAWDEX).","language":"ENGLISH","publisher":"Geological Survey (U.S.)","doi":"10.3133/wri83698","usgsCitation":"Roybal, F., Wells, J., Gold, R., and Flager, J., 1984, Hydrology of Area 62, Northern Great Plains and Rocky Mountain Coal Provinces, New Mexico and Arizona (WRI/OFR 83-698): U.S. Geological Survey Water-Resources Investigations Report 83-698, v, 66 p., https://doi.org/10.3133/wri83698.","productDescription":"v, 66 p.","costCenters":[{"id":595,"text":"U.S. Geological Survey","active":false,"usgs":true}],"links":[{"id":124643,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/of/1983/0698/report-thumb.jpg"},{"id":91373,"rank":300,"type":{"id":11,"text":"Document"},"url":"https://pubs.usgs.gov/of/1983/0698/report.pdf","linkFileType":{"id":1,"text":"pdf"}}],"geographicExtents":"{ \"type\": \"FeatureCollection\", \"features\": [ { \"type\": \"Feature\", \"properties\": {}, \"geometry\": { \"type\": \"Polygon\", \"coordinates\": [ [ [ -110,34 ], [ -110,36 ], [ -107.5,36 ], [ -107.5,34 ], [ -110,34 ] ] ] } } ] }","edition":"WRI/OFR 83-698","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4a17e4b07f02db604a3c","contributors":{"authors":[{"text":"Roybal, F.E.","contributorId":62998,"corporation":false,"usgs":true,"family":"Roybal","given":"F.E.","email":"","affiliations":[],"preferred":false,"id":291539,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Wells, J.G.","contributorId":85198,"corporation":false,"usgs":true,"family":"Wells","given":"J.G.","email":"","affiliations":[],"preferred":false,"id":291541,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Gold, R.L.","contributorId":97918,"corporation":false,"usgs":true,"family":"Gold","given":"R.L.","email":"","affiliations":[],"preferred":false,"id":291542,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Flager, J.V.","contributorId":72799,"corporation":false,"usgs":true,"family":"Flager","given":"J.V.","email":"","affiliations":[],"preferred":false,"id":291540,"contributorType":{"id":1,"text":"Authors"},"rank":4}]}}
,{"id":71002,"text":"wdrFL824 - 1984 - Water resources data, Florida, water year 1982, Volume 4: Northwest Florida","interactions":[],"lastModifiedDate":"2012-02-02T00:13:46","indexId":"wdrFL824","displayToPublicDate":"2005-08-09T00:00:00","publicationYear":"1984","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":340,"text":"Water Data Report","code":"WDR","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"FL-82-4","title":"Water resources data, Florida, water year 1982, Volume 4: Northwest Florida","language":"ENGLISH","doi":"10.3133/wdrFL824","usgsCitation":"Geological Survey, U., 1984, Water resources data, Florida, water year 1982, Volume 4: Northwest Florida: U.S. Geological Survey Water Data Report FL-82-4, 310 p., https://doi.org/10.3133/wdrFL824.","productDescription":"310 p.","costCenters":[],"links":[{"id":185748,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/wdr/1982/fl-82-4/report-thumb.jpg"},{"id":90530,"rank":300,"type":{"id":11,"text":"Document"},"url":"https://pubs.usgs.gov/wdr/1982/fl-82-4/report.pdf","linkFileType":{"id":1,"text":"pdf"}}],"noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e49f6e4b07f02db5f146d","contributors":{"authors":[{"text":"Geological Survey, U.S.","contributorId":26017,"corporation":false,"usgs":true,"family":"Geological Survey","given":"U.S.","affiliations":[],"preferred":false,"id":283473,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":70138,"text":"wri844 - 1984 - Simulation of dynamic floodflows at gaged stations in the southeastern United States","interactions":[],"lastModifiedDate":"2012-02-02T00:13:52","indexId":"wri844","displayToPublicDate":"2005-01-01T00:00:00","publicationYear":"1984","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":342,"text":"Water-Resources Investigations Report","code":"WRI","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"84-4","title":"Simulation of dynamic floodflows at gaged stations in the southeastern United States","language":"ENGLISH","doi":"10.3133/wri844","usgsCitation":"Faye, R.E., and Blalock, M.E., 1984, Simulation of dynamic floodflows at gaged stations in the southeastern United States: U.S. Geological Survey Water-Resources Investigations Report 84-4, 114 p., https://doi.org/10.3133/wri844.","productDescription":"114 p.","costCenters":[],"links":[{"id":101499,"rank":300,"type":{"id":11,"text":"Document"},"url":"https://pubs.usgs.gov/wri/1984/0004/report.pdf","size":"5716","linkFileType":{"id":1,"text":"pdf"}},{"id":191175,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/wri/1984/0004/report-thumb.jpg"}],"scale":"100000","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e49f8e4b07f02db5f2efd","contributors":{"authors":[{"text":"Faye, Robert E.","contributorId":92221,"corporation":false,"usgs":true,"family":"Faye","given":"Robert","email":"","middleInitial":"E.","affiliations":[],"preferred":false,"id":281931,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Blalock, Merritt E.","contributorId":14065,"corporation":false,"usgs":true,"family":"Blalock","given":"Merritt","email":"","middleInitial":"E.","affiliations":[],"preferred":false,"id":281930,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":70013169,"text":"70013169 - 1984 - Late quaternary sediments, minerals, and inferred geochemical history of Didwana Lake, Thar Desert, India","interactions":[],"lastModifiedDate":"2025-06-16T15:28:26.891809","indexId":"70013169","displayToPublicDate":"2003-04-22T00:00:00","publicationYear":"1984","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":2996,"text":"Palaeogeography, Palaeoclimatology, Palaeoecology","printIssn":"0031-0182","active":true,"publicationSubtype":{"id":10}},"title":"Late quaternary sediments, minerals, and inferred geochemical history of Didwana Lake, Thar Desert, India","docAbstract":"<p>Variations in clastic sediment texture, mineralogy of both evaporites formed at the surface and precipitates formed below the lake floor, and the relative chemical activities of the major dissolved components of the chemical precipitates, have allowed reconstruction of the history of salinity and water-level changes in Didwana Lake, Thar Desert, India. Hypersaline conditions prevailed at about the Last Glacial Maximum, with little evidence of clastic sediments entering the lake. Between ca. 13,000 and 6000 B.P. the lake level fluctuated widely, the lake alternately hypersaline and fresh, and clastic sediments were delivered to the lake at a low rate. Deep-water conditions occurred ca. 6000 B.P. and clastic influx increased abruptly. The water level dropped towards 4000 B.P. when the lake dried briefly. Since 4000 B.P. the lake has been ephemeral with a lowered rate of sedimentation and mildly saline conditions rather like those of today. This sequence of changes documented in the lake parallels changes in vegetation recorded in published pollen diagrams from both the Thar and the Arabian Sea. Correlation of the various lines of evidence suggests that the climate of the Last Glacial Maximum at Didwana was dry and windy with a weak monsoon circulation. The monsoon was re-established between ca. 13,000 and a little before 6000 B.P., and, when winter rainfall increased ca. 6000 B.P., the lake filled to its maximum depth.&nbsp;</p>","language":"English","publisher":"Elsevier","doi":"10.1016/0031-0182(84)90006-3","issn":"00310182","usgsCitation":"Wasson, R., Smith, G., and Agrawal, D., 1984, Late quaternary sediments, minerals, and inferred geochemical history of Didwana Lake, Thar Desert, India: Palaeogeography, Palaeoclimatology, Palaeoecology, v. 46, no. 4, p. 345-372, https://doi.org/10.1016/0031-0182(84)90006-3.","productDescription":"28 p.","startPage":"345","endPage":"372","costCenters":[],"links":[{"id":220293,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"India","otherGeospatial":"Didwana Lake, Thar Deser","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"coordinates\": [\n          [\n            [\n              74.20830973397764,\n              27.538838395300488\n            ],\n            [\n              74.20830973397764,\n              27.201083582211524\n            ],\n            [\n              74.785913156556,\n              27.201083582211524\n            ],\n            [\n              74.785913156556,\n              27.538838395300488\n            ],\n            [\n              74.20830973397764,\n              27.538838395300488\n            ]\n          ]\n        ],\n        \"type\": \"Polygon\"\n      }\n    }\n  ]\n}","volume":"46","issue":"4","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505a4558e4b0c8380cd67238","contributors":{"authors":[{"text":"Wasson, R.J.","contributorId":34780,"corporation":false,"usgs":true,"family":"Wasson","given":"R.J.","email":"","affiliations":[],"preferred":false,"id":365458,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Smith, G.I.","contributorId":103694,"corporation":false,"usgs":true,"family":"Smith","given":"G.I.","email":"","affiliations":[],"preferred":false,"id":365459,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Agrawal, D.P.","contributorId":16712,"corporation":false,"usgs":true,"family":"Agrawal","given":"D.P.","email":"","affiliations":[],"preferred":false,"id":365457,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
,{"id":70013909,"text":"70013909 - 1984 - An overview of paleogene molluscan biostratigraphy and paleoecology of the Gulf of Alaska region","interactions":[],"lastModifiedDate":"2025-06-16T15:15:08.632102","indexId":"70013909","displayToPublicDate":"2003-04-22T00:00:00","publicationYear":"1984","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":2996,"text":"Palaeogeography, Palaeoclimatology, Palaeoecology","printIssn":"0031-0182","active":true,"publicationSubtype":{"id":10}},"title":"An overview of paleogene molluscan biostratigraphy and paleoecology of the Gulf of Alaska region","docAbstract":"<p><span>Paleogene marine strata in the Gulf of Alaska region occur in three geographic areas and may be characterized by their molluscan faunal composition and paleoecology: a western area consisting of the Alaska Peninsula, Kodiak Island, and adjacent islands; a central area encompassing Prince William Sound; and an eastern area extending from the mouth of the Copper River to Icy Point in the Lituya district. Strata in the western area include the Ghost Rocks, Narrow Cape (in part), Sitkalidak, Stepovak, Belkofski, and Tolstoi Formations; in the central area Paleogene strata are assigned entirely to the Orca Group; Paleogene strata in the eastern area include the Kulthieth and Poul Creek Formations and several coeval units. Environments ranging from marginal marine to bathyal and from subtropical to cool-temperate are inferred for the various molluscan faunas. Sediments range from interbedded coal and marine sands to deep-water turbidites. The known Paleogene molluscan faunas of these three southern Alaskan areas permit recognition of biostratigraphic schemes within each area, preliminary correlations between faunas of the three areas, and more general correlations with faunas of the Pacific Northwest, the Far Eastern U.S.S.R., and northern Japan.</span></p>","language":"English","publisher":"Elsevier","doi":"10.1016/0031-0182(84)90082-8","issn":"00310182","usgsCitation":"Marincovich, L., and McCoy, S., 1984, An overview of paleogene molluscan biostratigraphy and paleoecology of the Gulf of Alaska region: Palaeogeography, Palaeoclimatology, Palaeoecology, v. 47, no. 1-2, p. 91-102, https://doi.org/10.1016/0031-0182(84)90082-8.","productDescription":"12 p.","startPage":"91","endPage":"102","costCenters":[],"links":[{"id":226118,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.er.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"Alaska","otherGeospatial":"Gulf of Alaska","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"coordinates\": [\n          [\n            [\n              -170.16016898665896,\n              52.53370257192515\n            ],\n            [\n              -165.87722752127797,\n              53.011068953297425\n            ],\n            [\n              -150.56744496884684,\n              57.07373444976588\n            ],\n            [\n              -152.06112809170114,\n              58.543491125197704\n            ],\n            [\n              -157.20426229979498,\n              58.73570361951738\n            ],\n            [\n              -170.08830120094672,\n              53.82391633092445\n            ],\n            [\n              -170.16016898665896,\n              52.53370257192515\n            ]\n          ]\n        ],\n        \"type\": \"Polygon\"\n      }\n    }\n  ]\n}","volume":"47","issue":"1-2","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"5059eaace4b0c8380cd489e4","contributors":{"authors":[{"text":"Marincovich, L. Jr.","contributorId":16157,"corporation":false,"usgs":true,"family":"Marincovich","given":"L.","suffix":"Jr.","affiliations":[],"preferred":false,"id":367145,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"McCoy, S. Jr.","contributorId":75287,"corporation":false,"usgs":true,"family":"McCoy","given":"S.","suffix":"Jr.","email":"","affiliations":[],"preferred":false,"id":367146,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":70014066,"text":"70014066 - 1984 - Distribution and ecology of deep-water benthic foraminifera in the Gulf of Mexico","interactions":[],"lastModifiedDate":"2025-06-16T15:08:16.465443","indexId":"70014066","displayToPublicDate":"2003-04-14T00:00:00","publicationYear":"1984","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":2996,"text":"Palaeogeography, Palaeoclimatology, Palaeoecology","printIssn":"0031-0182","active":true,"publicationSubtype":{"id":10}},"title":"Distribution and ecology of deep-water benthic foraminifera in the Gulf of Mexico","docAbstract":"<p><span>Bathyal and abyssal foraminifera in the Gulf of Mexico are distributed among thirteen generic predominance facies. Five predominance facies nearly encircle the Gulf basin along the slope and rise; a sixth predominance facies blankets the Sigsbee Plain, and a seventh is restricted to the Mississippi Fan. The remaining eight predominance facies have more restricted distributions. The areal patterns of these predominance facies can be related chiefly to water mass and substrate characteristics; modifications are brought about by calcite dissolution, upwelling, and sill depth. Analysis of ancient generic predominance facies is useful in predicting relative paleobathymetry and other paleoenvironmental properties.</span></p>","language":"English","publisher":"Elsevier","doi":"10.1016/0031-0182(84)90090-7","issn":"00310182","usgsCitation":"Poag, C.W., 1984, Distribution and ecology of deep-water benthic foraminifera in the Gulf of Mexico: Palaeogeography, Palaeoclimatology, Palaeoecology, v. 48, no. 1, p. 25-37, https://doi.org/10.1016/0031-0182(84)90090-7.","productDescription":"13 p.","startPage":"25","endPage":"37","costCenters":[],"links":[{"id":225487,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"Alabama, Florida, Louisiana, Mississippi, Texas","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"coordinates\": [\n          [\n            [\n              -97.13858134169811,\n              29.197248880700073\n            ],\n            [\n              -97.13858134169811,\n              21.67225015871294\n            ],\n            [\n              -83.08875993352926,\n              21.67225015871294\n            ],\n            [\n              -83.08875993352926,\n              29.197248880700073\n            ],\n            [\n              -97.13858134169811,\n              29.197248880700073\n            ]\n          ]\n        ],\n        \"type\": \"Polygon\"\n      }\n    }\n  ]\n}","volume":"48","issue":"1","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505a028ae4b0c8380cd500bc","contributors":{"authors":[{"text":"Poag, C. W.","contributorId":16402,"corporation":false,"usgs":true,"family":"Poag","given":"C.","email":"","middleInitial":"W.","affiliations":[],"preferred":false,"id":367485,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":70014084,"text":"70014084 - 1984 - Neogene stratigraphy of the submerged U.S. Atlantic margin","interactions":[],"lastModifiedDate":"2025-06-13T16:12:42.564623","indexId":"70014084","displayToPublicDate":"2003-04-14T00:00:00","publicationYear":"1984","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":2996,"text":"Palaeogeography, Palaeoclimatology, Palaeoecology","printIssn":"0031-0182","active":true,"publicationSubtype":{"id":10}},"title":"Neogene stratigraphy of the submerged U.S. Atlantic margin","docAbstract":"<p><span>Thirty boreholes and several hundred sea-floor samples provide a detailed but incomplete record of Neogene strata and depositional environments along the submerged part of the United States Atlantic margin. Three major sedimentary basins, the Blake Plateau Basin, the Baltimore Canyon Trough, and the Georges Bank Basin, contain Neogene sedimentary prisms as thick as 1200 m, comprising bathyal marine to nonmarine strata. Middle Miocene rocks compose the most widely represented and thickest unit (&gt; 600 m in the Baltimore Canyon Trough). Calcareous microfossils provide excellent biostratigraphic and paleoenvironmental indicators except in some sparsely fossilferous shallow-water intervals and where shallow-water diatomaceous assemblages predominate. However, in outer sublittoral assemblages of the Blake Plateau Basin and Baltimore Canyon Trough, the co-occurrence of abundant diatoms, radiolarians, and planktic foraminifera provide an excellent opportunity for intercalibration of biozones. Preliminary correlations between chronostratigraphic and paleoenvironmental interpretations indicate a close association of depositional sequences with sea-level fluctuations, but some local exception persist.</span></p>","language":"English","publisher":"Elsevier","doi":"10.1016/0031-0182(84)90083-X","issn":"00310182","usgsCitation":"Poag, C.W., 1984, Neogene stratigraphy of the submerged U.S. Atlantic margin: Palaeogeography, Palaeoclimatology, Palaeoecology, v. 47, no. 1-2, p. 103-127, https://doi.org/10.1016/0031-0182(84)90083-X.","productDescription":"25 p.","startPage":"103","endPage":"127","costCenters":[],"links":[{"id":225813,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","otherGeospatial":"U.S. Atlantic margin","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"coordinates\": [\n          [\n            [\n              -67.21473626467579,\n              45.56400160658059\n            ],\n            [\n              -75.89249608207597,\n              40.57001008222211\n            ],\n            [\n              -81.63246101855188,\n              32.43539505606307\n            ],\n            [\n              -82.04072839900807,\n              30.364306803599554\n            ],\n            [\n              -80.52464146673184,\n              25.886508698926903\n            ],\n            [\n              -77.03753292314397,\n              27.57808131902972\n            ],\n            [\n              -65.43896538425625,\n              43.37717206733501\n            ],\n            [\n              -67.21473626467579,\n              45.56400160658059\n            ]\n          ]\n        ],\n        \"type\": \"Polygon\"\n      }\n    }\n  ]\n}","volume":"47","issue":"1-2","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505a6450e4b0c8380cd72983","contributors":{"authors":[{"text":"Poag, C. Wylie","contributorId":52714,"corporation":false,"usgs":true,"family":"Poag","given":"C.","email":"","middleInitial":"Wylie","affiliations":[],"preferred":false,"id":367533,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":70013319,"text":"70013319 - 1984 - Neogene molluscan stages of the West Coast of North America","interactions":[],"lastModifiedDate":"2025-06-16T15:21:26.470744","indexId":"70013319","displayToPublicDate":"2003-04-14T00:00:00","publicationYear":"1984","noYear":false,"publicationType":{"id":2,"text":"Article"},"publicationSubtype":{"id":10,"text":"Journal Article"},"seriesTitle":{"id":2996,"text":"Palaeogeography, Palaeoclimatology, Palaeoecology","printIssn":"0031-0182","active":true,"publicationSubtype":{"id":10}},"title":"Neogene molluscan stages of the West Coast of North America","docAbstract":"<p><span>Neogene marine sediments of the West Coast of North America were deposited in a series of widely spaced basins that extended geographically from the western and northern Gulf of Alaska (60°N) to southern California (33°N). Rich molluscan faunas occur extensively throughout these deposits and form the basis for biostratigraphic schemes that are useful for correlating within and between individual basins. Early biostratigraphic work was concerned with faunas from particular horizons and with the stratigraphic range of diverse taxa, such as&nbsp;</span><i>Pecten</i><span>&nbsp;and&nbsp;</span><i>Turritella</i><span>, without reference to other fossil groups. Succeeding work increasingly dealt with the relationships of molluscan zones to benthic and, later, planktonic foraminiferal stages. In recent years the age limits of Neogene molluscan stages have become better documented by reference to planktonic microfossils from dated DSDP cores and onshore faunas.</span></p><p><span>Neogene molluscan faunas from California, the Pacific Northwest states (Oregon and Washington), and southern Alaska have been treated separately due to differences in faunal composition and geographic isolation. As a result, a different biostratigraphic sequence has been described for each region. Pacific Northwest stages have been formally named and defined, and their names are also used informally for Alaskan faunas. California Neogene stages were proposed early in this century, are in need of redescription, and their usage is informal. Precise correlations between the three regional sequences have not yet been achieved, due to the low number of co-occurring species and the general lack of planktonic microfossils in these largely shallow-water faunas. The objectives of ongoing research include: fuller documentation of the faunas of California and Pacific Northwest stages; formal description of California stages; improved correlation between regional stage sequences; refinement of age estimates for stage boundaries; and, establishment of Neogene stages for Alaskan faunas.</span></p>","language":"English","publisher":"Elsevier","doi":"10.1016/0031-0182(84)90022-1","issn":"00310182","usgsCitation":"Marincovich, L., 1984, Neogene molluscan stages of the West Coast of North America: Palaeogeography, Palaeoclimatology, Palaeoecology, v. 46, no. 1-3, p. 11-24, https://doi.org/10.1016/0031-0182(84)90022-1.","productDescription":"14 p.","startPage":"11","endPage":"24","costCenters":[],"links":[{"id":220528,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"Canada, United States","state":"California, Oregon, Washington","otherGeospatial":"British Columbia","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"coordinates\": [\n          [\n            [\n              -140.62983472920033,\n              60.58400932046334\n            ],\n            [\n              -121.64960121391485,\n              33.52522907665377\n            ],\n            [\n              -118.0675797095897,\n              32.45484505685331\n            ],\n            [\n              -114.11428012825937,\n              32.82730499941407\n            ],\n            [\n              -114.5983833681297,\n              35.57473668760612\n            ],\n            [\n              -119.49611318026915,\n              39.15156796516043\n            ],\n            [\n              -119.80273808795062,\n              41.88223308573585\n            ],\n            [\n              -117.17898657848735,\n              42.25894561686526\n            ],\n            [\n              -116.61248280646399,\n              46.341056999454025\n            ],\n            [\n              -116.64659824810718,\n              48.677806603546586\n            ],\n            [\n              -114.77408096538828,\n              49.81429632925091\n            ],\n            [\n              -120.81774730494959,\n              60.19576593940528\n            ],\n            [\n              -140.62983472920033,\n              60.58400932046334\n            ]\n          ]\n        ],\n        \"type\": \"Polygon\"\n      }\n    }\n  ]\n}","volume":"46","issue":"1-3","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505a644ce4b0c8380cd72978","contributors":{"authors":[{"text":"Marincovich, L. Jr.","contributorId":16157,"corporation":false,"usgs":true,"family":"Marincovich","given":"L.","suffix":"Jr.","affiliations":[],"preferred":false,"id":365809,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":70013436,"text":"70013436 - 1984 - Transport and concentration controls for chloride, strontium, potassium and lead in Uvas Creek, a small cobble-bed stream in Santa Clara County, California, U.S.A.: 1. Conceptual model","interactions":[],"lastModifiedDate":"2025-04-15T16:08:38.668793","indexId":"70013436","displayToPublicDate":"2003-03-27T00:00:00","publicationYear":"1984","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":"Transport and concentration controls for chloride, strontium, potassium and lead in Uvas Creek, a small cobble-bed stream in Santa Clara County, California, U.S.A.: 1. Conceptual model","docAbstract":"<p><span>Stream sediments adsorb certain solutes from streams, thereby significantly changing the solute composition; but little is known about the details and rates of these adsorptive processes. To investigate such processes, a 24-hr. injection of a solution containing chloride, strontium, potassium, sodium and lead was made at the head of a 640-m reach of Uvas Creek in west-central Santa Clara County, California. Uvas Creek is a cobble-bed pool-and-riffle stream draining the eastern slopes of the Santa Cruz Mountains. By September 12, 1973, after a long dry season, Uvas Creek had a low (0.0215 m</span><sup>3</sup><span>s</span><sup>−1</sup><span>&nbsp;average) flow which varied diurnally, from 0.018 to 0.025 m</span><sup>3</sup><span>s</span><sup>−1</sup><span>. Because stream discharge varied while the injection rate was constant, the concentration of tracers (injected solutes), after mixing in the stream, varied inversely with discharge.</span></p><p><span>Chloride, a nonreactive solute, served as a tracer of water movement. Analysis of extensive chloride concentration data at five sites below the injection point during and after the injection demonstrated that there was considerable underflow of water through the stream gravels; however, the extent of underflow varied greatly within the study reach. Pre-injection water, displaced by tracer-laden water percolating through the gravels, diluted tracers in the stream channel, giving the mistaken impression of groundwater inflow at some points. Accurate measurement of total discharge in such streams requires prolonged tracer injection unless a reach can be found where underflow is negligible.</span></p><p><span>Strontium and potassium were adsorbed by the bed sediments to a moderate extent and lead was strongly adsorbed. A high proportion of these metals could be removed by adsorption from percolating underflow because of extensive and intimate contact with bed sediments. After channel clearing following injection cutoff, 51% of the added strontium and 96% of the lead remained in the study reach, whereas only 19% of the chloride remained. Packets of sized sediment, placed in the stream before the experiment and withdrawn during and after the injection, indicated that the strontium absorbed on the 0.42–0.50-mm size sediment appeared to achieve near equilibrium with dissolved strontium within less than 2 hr. whereas 3.4–4.0-mm grains had not reached that stage after 24 hr.</span></p><p><span>The cation-exchange capacity (CEC) of the sediments shows a “bimodal” distribution with grain size. Largest values are in the finest sizes, lower values in the fine-to-medium sand-size range, intermediate values in the coarse- to very coarse-grained sand, and decreasing values with size above very coarse-grained sand. This considerable exchange capacity in coarse-sand to granule-size particles means that a streambed, that has not been infilled with fines to reduce permeability, can be highly reactive and accessible throughout a rather thick sediment layer and hence have a large and available reactive capacity.</span></p><p><span>As stream discharge increases from low flow, the ratio of underflow to channel flow should decrease rapidly with resultant diminution in percent of solutes sorbed within a particular stream reach.</span></p>","language":"English","publisher":"Elsevier","doi":"10.1016/0022-1694(84)90046-5","issn":"00221694","usgsCitation":"Kennedy, V.C., Jackman, A.P., Zand, S., Zellweger, G.W., and Avanzino, R., 1984, Transport and concentration controls for chloride, strontium, potassium and lead in Uvas Creek, a small cobble-bed stream in Santa Clara County, California, U.S.A.: 1. Conceptual model: Journal of Hydrology, v. 75, no. 1-4, p. 67-110, https://doi.org/10.1016/0022-1694(84)90046-5.","productDescription":"44 p.","startPage":"67","endPage":"110","costCenters":[],"links":[{"id":220588,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"California","county":"Santa Clara County","geographicExtents":"{\"type\":\"FeatureCollection\",\"features\":[{\"type\":\"Feature\",\"id\":227,\"properties\":{\"name\":\"Santa Clara\",\"state\":\"CA\"},\"geometry\":{\"type\":\"MultiPolygon\",\"coordinates\":[[[[-121.983,37.4615],[-121.981,37.4612],[-121.978,37.4613],[-121.97,37.4619],[-121.961,37.4629],[-121.955,37.4604],[-121.947,37.466],[-121.939,37.462],[-121.933,37.4594],[-121.927,37.4541],[-121.923,37.4542],[-121.92,37.4574],[-121.908,37.464],[-121.897,37.467],[-121.89,37.4675],[-121.887,37.4708],[-121.881,37.4714],[-121.865,37.4848],[-121.471,37.4818],[-121.477,37.4781],[-121.484,37.4735],[-121.482,37.4667],[-121.472,37.4573],[-121.464,37.4511],[-121.46,37.4398],[-121.467,37.437],[-121.469,37.4334],[-121.471,37.4297],[-121.472,37.4243],[-121.468,37.4162],[-121.462,37.4144],[-121.458,37.4109],[-121.456,37.4041],[-121.458,37.3968],[-121.45,37.3951],[-121.449,37.392],[-121.444,37.3921],[-121.435,37.3945],[-121.422,37.3933],[-121.42,37.3897],[-121.411,37.3876],[-121.409,37.3776],[-121.416,37.3744],[-121.418,37.3666],[-121.424,37.3615],[-121.421,37.353],[-121.419,37.3444],[-121.414,37.3386],[-121.409,37.3341],[-121.41,37.3264],[-121.407,37.3187],[-121.41,37.3123],[-121.424,37.2999],[-121.433,37.2961],[-121.442,37.2991],[-121.449,37.2977],[-121.45,37.2918],[-121.454,37.2885],[-121.459,37.2839],[-121.454,37.279],[-121.454,37.2713],[-121.455,37.2491],[-121.45,37.2419],[-121.441,37.2325],[-121.43,37.2286],[-121.426,37.2237],[-121.421,37.2147],[-121.419,37.2047],[-121.413,37.1912],[-121.414,37.1763],[-121.41,37.1632],[-121.404,37.1542],[-121.396,37.1525],[-121.39,37.1549],[-121.386,37.1549],[-121.385,37.1608],[-121.386,37.1681],[-121.376,37.175],[-121.37,37.181],[-121.365,37.1843],[-121.358,37.1857],[-121.352,37.1849],[-121.344,37.1778],[-121.337,37.1747],[-121.331,37.1712],[-121.322,37.1691],[-121.312,37.1719],[-121.307,37.1706],[-121.301,37.1698],[-121.296,37.1708],[-121.29,37.1795],[-121.287,37.1832],[-121.281,37.1819],[-121.275,37.1761],[-121.268,37.1694],[-121.262,37.1622],[-121.253,37.161],[-121.247,37.1602],[-121.242,37.158],[-121.24,37.1517],[-121.235,37.1413],[-121.227,37.1369],[-121.222,37.1283],[-121.219,37.1243],[-121.219,37.1171],[-121.225,37.112],[-121.227,37.1065],[-121.231,37.1015],[-121.231,37.0969],[-121.238,37.0937],[-121.244,37.0891],[-121.241,37.0864],[-121.231,37.0833],[-121.225,37.0771],[-121.218,37.0717],[-121.209,37.0655],[-121.21,37.0582],[-121.225,37.0535],[-121.223,37.0399],[-121.234,37.0366],[-121.248,37.0314],[-121.245,37.0237],[-121.237,37.0152],[-121.237,37.0071],[-121.233,37.0008],[-121.245,36.9947],[-121.247,36.9902],[-121.247,36.9838],[-121.242,36.9748],[-121.231,36.97],[-121.212,36.9607],[-121.257,36.9596],[-121.345,36.9606],[-121.377,36.9601],[-121.42,36.9608],[-121.428,36.9684],[-121.434,36.9769],[-121.444,36.9853],[-121.458,36.986],[-121.463,36.9818],[-121.468,36.979],[-121.471,36.9785],[-121.487,36.9837],[-121.49,36.9805],[-121.499,36.9717],[-121.505,36.9639],[-121.513,36.9584],[-121.512,36.9525],[-121.515,36.947],[-121.518,36.9415],[-121.519,36.9419],[-121.529,36.9336],[-121.537,36.9271],[-121.539,36.9221],[-121.544,36.9184],[-121.553,36.9146],[-121.559,36.9095],[-121.559,36.9063],[-121.56,36.8968],[-121.562,36.8963],[-121.571,36.8966],[-121.575,36.8929],[-121.58,36.8996],[-121.58,36.919],[-121.59,36.9188],[-121.59,36.9262],[-121.609,36.926],[-121.624,36.9409],[-121.637,36.939],[-121.644,36.933],[-121.646,36.9357],[-121.652,36.9396],[-121.653,36.9461],[-121.652,36.9496],[-121.653,36.951],[-121.656,36.9504],[-121.661,36.951],[-121.662,36.9519],[-121.664,36.9641],[-121.67,36.9644],[-121.68,36.9677],[-121.681,36.9681],[-121.69,36.968],[-121.698,36.9737],[-121.696,36.9842],[-121.704,36.9868],[-121.712,36.9902],[-121.717,36.9956],[-121.711,37.0039],[-121.712,37.0134],[-121.717,37.0137],[-121.743,37.0314],[-121.746,37.0372],[-121.754,37.0448],[-121.754,37.0516],[-121.761,37.0515],[-121.772,37.0535],[-121.781,37.0588],[-121.787,37.0641],[-121.803,37.0684],[-121.81,37.0714],[-121.817,37.0799],[-121.821,37.0834],[-121.824,37.0875],[-121.839,37.094],[-121.848,37.0974],[-121.861,37.1008],[-121.866,37.103],[-121.893,37.1115],[-121.899,37.1137],[-121.915,37.1156],[-121.927,37.1231],[-121.935,37.1234],[-121.946,37.1268],[-121.954,37.1302],[-121.962,37.1333],[-121.968,37.1386],[-121.978,37.1447],[-121.987,37.1459],[-121.991,37.1458],[-121.997,37.1525],[-122.006,37.1596],[-122.019,37.1674],[-122.036,37.1848],[-122.035,37.1939],[-122.042,37.201],[-122.045,37.2041],[-122.058,37.2129],[-122.068,37.2118],[-122.071,37.2176],[-122.074,37.2198],[-122.08,37.2233],[-122.082,37.2219],[-122.095,37.2253],[-122.101,37.2333],[-122.103,37.2405],[-122.108,37.2486],[-122.117,37.2593],[-122.132,37.2585],[-122.145,37.27],[-122.143,37.2732],[-122.152,37.2862],[-122.155,37.292],[-122.167,37.2953],[-122.162,37.3036],[-122.161,37.3077],[-122.168,37.3135],[-122.186,37.3099],[-122.189,37.3193],[-122.183,37.3245],[-122.176,37.3283],[-122.181,37.334],[-122.192,37.3442],[-122.2,37.3586],[-122.202,37.3658],[-122.199,37.3726],[-122.193,37.3778],[-122.186,37.3888],[-122.189,37.3973],[-122.189,37.4023],[-122.192,37.4086],[-122.189,37.4155],[-122.19,37.4187],[-122.191,37.42],[-122.189,37.4227],[-122.189,37.425],[-122.189,37.4259],[-122.19,37.4282],[-122.19,37.4295],[-122.189,37.4314],[-122.185,37.4351],[-122.182,37.4392],[-122.18,37.4411],[-122.177,37.4425],[-122.17,37.4481],[-122.166,37.4532],[-122.162,37.4546],[-122.159,37.4551],[-122.157,37.4552],[-122.154,37.4566],[-122.152,37.4571],[-122.149,37.4567],[-122.146,37.4573],[-122.144,37.4564],[-122.139,37.4547],[-122.137,37.4543],[-122.135,37.4543],[-122.131,37.4526],[-122.127,37.4527],[-122.119,37.4524],[-122.111,37.4535],[-122.11,37.458],[-122.103,37.4564],[-122.101,37.4582],[-122.101,37.4575],[-122.101,37.4569],[-122.1,37.4572],[-122.098,37.4578],[-122.098,37.4581],[-122.097,37.4581],[-122.097,37.4578],[-122.095,37.4564],[-122.095,37.4558],[-122.094,37.455],[-122.094,37.4547],[-122.092,37.4528],[-122.092,37.4525],[-122.091,37.4519],[-122.091,37.4519],[-122.089,37.4517],[-122.088,37.4514],[-122.086,37.4506],[-122.082,37.452],[-122.081,37.452],[-122.08,37.4517],[-122.079,37.4508],[-122.078,37.4493],[-122.078,37.4491],[-122.077,37.4493],[-122.076,37.4499],[-122.075,37.4496],[-122.071,37.4503],[-122.069,37.4509],[-122.068,37.4507],[-122.065,37.4478],[-122.064,37.4467],[-122.064,37.4462],[-122.064,37.4445],[-122.065,37.4436],[-122.067,37.4417],[-122.067,37.4414],[-122.067,37.4389],[-122.067,37.4361],[-122.067,37.4358],[-122.067,37.435],[-122.067,37.4347],[-122.067,37.4339],[-122.067,37.4336],[-122.067,37.4328],[-122.067,37.4325],[-122.064,37.4319],[-122.063,37.4303],[-122.063,37.4297],[-122.063,37.4291],[-122.061,37.4289],[-122.06,37.4286],[-122.059,37.4283],[-122.058,37.4281],[-122.058,37.4283],[-122.056,37.43],[-122.056,37.4303],[-122.055,37.4303],[-122.054,37.4311],[-122.054,37.4311],[-122.051,37.4314],[-122.051,37.4308],[-122.051,37.4294],[-122.05,37.4294],[-122.049,37.4289],[-122.049,37.4283],[-122.049,37.4281],[-122.049,37.4275],[-122.049,37.4272],[-122.048,37.4267],[-122.046,37.4267],[-122.046,37.4269],[-122.045,37.4269],[-122.045,37.4272],[-122.044,37.4269],[-122.042,37.4269],[-122.042,37.4272],[-122.04,37.4275],[-122.04,37.4272],[-122.037,37.4275],[-122.037,37.4272],[-122.036,37.4272],[-122.036,37.4267],[-122.031,37.4239],[-122.031,37.4239],[-122.031,37.4244],[-122.03,37.4244],[-122.029,37.4233],[-122.028,37.4233],[-122.028,37.4236],[-122.027,37.4236],[-122.027,37.4239],[-122.026,37.4236],[-122.025,37.4232],[-122.024,37.4231],[-122.023,37.4231],[-122.023,37.4228],[-122.022,37.4228],[-122.022,37.4225],[-122.021,37.4225],[-122.021,37.4219],[-122.021,37.4219],[-122.019,37.4222],[-122.018,37.4222],[-122.018,37.4231],[-122.018,37.4233],[-122.017,37.4247],[-122.018,37.4253],[-122.018,37.4258],[-122.017,37.4261],[-122.017,37.4261],[-122.015,37.4253],[-122.015,37.4258],[-122.014,37.4258],[-122.013,37.4264],[-122.013,37.4264],[-122.012,37.4278],[-122.012,37.4283],[-122.01,37.4303],[-122.009,37.4303],[-122.009,37.43],[-122.009,37.4308],[-122.009,37.4314],[-122.01,37.4314],[-122.01,37.4317],[-122.011,37.4322],[-122.011,37.4319],[-122.016,37.4319],[-122.016,37.4317],[-122.018,37.4311],[-122.018,37.4314],[-122.02,37.4314],[-122.021,37.4317],[-122.023,37.4317],[-122.023,37.4319],[-122.025,37.4327],[-122.025,37.4331],[-122.026,37.4331],[-122.028,37.4348],[-122.029,37.4354],[-122.029,37.4364],[-122.029,37.4369],[-122.029,37.4378],[-122.03,37.4381],[-122.03,37.4386],[-122.03,37.4389],[-122.03,37.44],[-122.031,37.4408],[-122.032,37.4408],[-122.033,37.4406],[-122.034,37.4397],[-122.034,37.4397],[-122.034,37.4394],[-122.035,37.4397],[-122.037,37.4397],[-122.037,37.44],[-122.038,37.44],[-122.039,37.4406],[-122.039,37.4406],[-122.04,37.4411],[-122.04,37.4419],[-122.04,37.4422],[-122.041,37.4431],[-122.041,37.4442],[-122.041,37.4444],[-122.041,37.445],[-122.041,37.4453],[-122.041,37.4458],[-122.04,37.4464],[-122.04,37.4467],[-122.039,37.4475],[-122.039,37.4475],[-122.039,37.4481],[-122.038,37.4481],[-122.037,37.4483],[-122.036,37.4481],[-122.036,37.4478],[-122.035,37.4478],[-122.035,37.4475],[-122.034,37.4475],[-122.033,37.447],[-122.032,37.4468],[-122.031,37.448],[-122.031,37.4489],[-122.031,37.4492],[-122.032,37.4506],[-122.033,37.4506],[-122.034,37.4519],[-122.035,37.453],[-122.035,37.4532],[-122.038,37.4536],[-122.038,37.4536],[-122.039,37.4539],[-122.039,37.4555],[-122.038,37.4555],[-122.037,37.4563],[-122.037,37.4571],[-122.034,37.4592],[-122.034,37.4594],[-122.033,37.4605],[-122.032,37.4609],[-122.031,37.4611],[-122.031,37.4614],[-122.029,37.4617],[-122.029,37.4619],[-122.028,37.4622],[-122.027,37.4619],[-122.027,37.4622],[-122.026,37.4628],[-122.026,37.4628],[-122.024,37.4622],[-122.024,37.4619],[-122.022,37.4628],[-122.022,37.4636],[-122.021,37.4639],[-122.019,37.4644],[-122.019,37.4647],[-122.019,37.4647],[-122.018,37.465],[-122.017,37.465],[-122.017,37.4653],[-122.016,37.4653],[-122.015,37.465],[-122.014,37.4653],[-122.014,37.4656],[-122.013,37.4656],[-122.013,37.4658],[-122.012,37.4658],[-122.011,37.4661],[-122.01,37.4661],[-122.01,37.4664],[-122.009,37.4664],[-122.008,37.4667],[-122.007,37.4667],[-122.006,37.4667],[-122.006,37.4669],[-122.004,37.4667],[-122.004,37.4669],[-122.003,37.4667],[-122.003,37.4664],[-122.001,37.4664],[-122,37.4661],[-121.998,37.4661],[-121.998,37.4658],[-121.995,37.4644],[-121.995,37.4644],[-121.994,37.4639],[-121.994,37.4639],[-121.994,37.4636],[-121.988,37.4619],[-121.988,37.4617],[-121.987,37.4617],[-121.987,37.4614],[-121.986,37.4614],[-121.986,37.4611],[-121.985,37.4611],[-121.985,37.4608],[-121.984,37.4608],[-121.984,37.4606],[-121.983,37.4606],[-121.983,37.4603],[-121.982,37.4603],[-121.982,37.46],[-121.98,37.4597],[-121.98,37.4594],[-121.979,37.4606],[-121.98,37.4606],[-121.98,37.4608],[-121.981,37.4608],[-121.982,37.4611],[-121.983,37.4611],[-121.983,37.4615]]],[[[-121.9828,37.4615],[-121.9836,37.4614],[-121.9839,37.4616],[-121.9828,37.4615]]]]}}]}","volume":"75","issue":"1-4","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505bb735e4b08c986b327106","contributors":{"authors":[{"text":"Kennedy, V. C.","contributorId":46080,"corporation":false,"usgs":true,"family":"Kennedy","given":"V.","email":"","middleInitial":"C.","affiliations":[],"preferred":false,"id":366059,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Jackman, A. P.","contributorId":46957,"corporation":false,"usgs":true,"family":"Jackman","given":"A.","email":"","middleInitial":"P.","affiliations":[],"preferred":false,"id":366060,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Zand, S.M.","contributorId":25699,"corporation":false,"usgs":true,"family":"Zand","given":"S.M.","email":"","affiliations":[],"preferred":false,"id":366057,"contributorType":{"id":1,"text":"Authors"},"rank":3},{"text":"Zellweger, G. W.","contributorId":55445,"corporation":false,"usgs":true,"family":"Zellweger","given":"G.","email":"","middleInitial":"W.","affiliations":[],"preferred":false,"id":366061,"contributorType":{"id":1,"text":"Authors"},"rank":4},{"text":"Avanzino, R.J.","contributorId":37336,"corporation":false,"usgs":true,"family":"Avanzino","given":"R.J.","affiliations":[],"preferred":false,"id":366058,"contributorType":{"id":1,"text":"Authors"},"rank":5}]}}
,{"id":70013401,"text":"70013401 - 1984 - Use of a digital model to evaluate hydrogeologic controls on groundwater flow in a fractured rock aquifer at Niagara Falls, New York, U.S.A.","interactions":[],"lastModifiedDate":"2025-04-15T15:51:34.651381","indexId":"70013401","displayToPublicDate":"2003-03-27T00:00:00","publicationYear":"1984","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":"Use of a digital model to evaluate hydrogeologic controls on groundwater flow in a fractured rock aquifer at Niagara Falls, New York, U.S.A.","docAbstract":"<p>The Hyde Park landfill is a 15-acre (6.1 ha) chemical waste disposal site located north of Niagara Falls, New York. Underlying the site in descending order are: (1) low-permeability glacial till and lacustrine deposits; (2) a moderately permeable fractured rock aquifer - the Lockport Dolomite; and (3) a low-permeability unit - the Rochester Shale. The site is bounded on three sides by groundwater drains; the Niagara River gorge, the Niagara Power Project canal, and the Niagara Power Project buried conduits. </p><p>The mechanism by which groundwater moves through fractured rocks underlying a hazardous waste site was investigated using a digital simulation approach. Three hypotheses were tested related to flow in the fractured rocks underlying Hyde Park landfill. For this purpose we used a Galerkin finite-element approximation to solve a saturated-unsaturated flow equation. </p><p><span>A primary focus was to investigate anisotropy in the Lockport Dolomite, that is the effectiveness of horizontal (bedding) joints vs. vertical joints as water-transmitting openings. Three hydrogeologic scenarios were set up — each with prescribed limits on the hydrologic parameters. Scenario&nbsp;</span><i>1</i><span>&nbsp;specified strongly anisotropic conditions in the Lockport Dolomite (horizontal hydraulic conductivity along bedding joints exceeds vertical conductivity by 2–3 orders of magnitude), uniform areal recharge (5 in. yr.</span><sup>−1</sup><span>&nbsp;or 12.7 cm yr.</span><sup>−1</sup><span>) except at the landfill where there is no recharge, and no flow through the base of the Rochester Shale. Scenario&nbsp;</span><i>2</i><span>&nbsp;also specified strongly anisotropic conditions in the Lockport; however, areal recharge was 6 in. yr.</span><sup>−1</sup><span>&nbsp;(15.2 cm yr.</span><sup>−1</sup><span>) except at the landfill where the recharge was 2 in. yr.</span><sup>−1</sup><span>&nbsp;(5.1 cm yr.</span><sup>−1</sup><span>), and outflow from the Rochester occurred. Scenario&nbsp;</span><i>3</i><span>&nbsp;specified isotropic conditions (that is, permeability along horizontal and vertical joints is the same in the Lockport Dolomite), recharge rates were the same as in scenario&nbsp;</span><i>2</i><span>&nbsp;and outflow through Rochester occurred.</span></p><p>Scenario 2 provided the closest agreement between the simulated and measured heads while scenario 3 provided the poorest agreement. Among the three scenarios tested, scenario 2 (with strongly anisotropic conditions in the Lockport Dolomite with added recharge through the landfill cap and limited flow through the Rocherster Shale) is considered the most realistic hydrogeologic model. </p><p>Based on simulation with the hydrogeologic parameters of scenario 2, groundwater flow near the Hyde Park site can be summarized as follows: </p><p>1. (1) <span>Specific discharge (Darcy velocity) ranges from ≈0.01 to 0.1 ft. day</span><sup>−1</sup><span>&nbsp;(0.003 to 0.03 m day</span><sup>−1</sup><span>) in the upper unit of the Lockport Dolomite to slightly more than 0.0001 ft. day</span><sup>−1</sup><span>&nbsp;(0.00003 m day</span><sup>−1</sup><span>) in the Rochester Shale. Real velocities are highest in the upper unit of the Lockport, ranging from ≈1 to 5 ft. day</span><sup>−1</sup><span>&nbsp;(0.3 to 1.5 m day</span><sup>−1</sup><span>) if the average effective porosity is assumed to be 0.02.</span></p><p>2. (2) A groundwater divide exists east of the landfill, indicating that all groundwater originating near or flowing beneath the landfill will flow toward and discharge in the gorge. </p><p>3. (3) Highest flow velocities (and presumably greatest potential for transporting chemical contaminants) occur in the upper unit of the Lockport and part of the lower unit of the Lockport Dolomite between the landfill and the gorge. The average time required for groundwater to move from the landfill to the discharge points at the gorge along selected flow paths in the Lockport Dolomite is estimated to be 5-6 yr.&nbsp;</p>","language":"English","publisher":"Elsevier","doi":"10.1016/0022-1694(84)90049-0","issn":"00221694","usgsCitation":"Maslia, M., and Johnston, R., 1984, Use of a digital model to evaluate hydrogeologic controls on groundwater flow in a fractured rock aquifer at Niagara Falls, New York, U.S.A.: Journal of Hydrology, v. 75, no. 1-4, p. 167-194, https://doi.org/10.1016/0022-1694(84)90049-0.","productDescription":"28 p.","startPage":"167","endPage":"194","costCenters":[],"links":[{"id":220091,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"New York","otherGeospatial":"Niagara Falls","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"coordinates\": [\n          [\n            [\n              -79.07144327825095,\n              43.09286795115449\n            ],\n            [\n              -79.07144327825095,\n              43.07801889165893\n            ],\n            [\n              -79.05037086913583,\n              43.07801889165893\n            ],\n            [\n              -79.05037086913583,\n              43.09286795115449\n            ],\n            [\n              -79.07144327825095,\n              43.09286795115449\n            ]\n          ]\n        ],\n        \"type\": \"Polygon\"\n      }\n    }\n  ]\n}","volume":"75","issue":"1-4","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505bbe8fe4b08c986b329661","contributors":{"authors":[{"text":"Maslia, M.L.","contributorId":24090,"corporation":false,"usgs":true,"family":"Maslia","given":"M.L.","affiliations":[],"preferred":false,"id":365990,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Johnston, R.H.","contributorId":19536,"corporation":false,"usgs":true,"family":"Johnston","given":"R.H.","email":"","affiliations":[],"preferred":false,"id":365989,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":70013618,"text":"70013618 - 1984 - Transport and concentration controls for chloride, strontium, potassium and lead in Uvas Creek, a small cobble-bed stream in Santa Clara County, California, U.S.A.: 2. Mathematical modeling","interactions":[],"lastModifiedDate":"2025-04-15T16:00:11.629528","indexId":"70013618","displayToPublicDate":"2003-03-27T00:00:00","publicationYear":"1984","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":"Transport and concentration controls for chloride, strontium, potassium and lead in Uvas Creek, a small cobble-bed stream in Santa Clara County, California, U.S.A.: 2. Mathematical modeling","docAbstract":"<p>Three models describing solute transport of conservative ion species and another describing transport of species which adsorb linearly and reversibly on bed sediments are developed and tested. The conservative models are based on three different conceptual models of the transient storage of solute in the bed. One model assumes the bed to be a well-mixed zone with flux of solute into the bed proportional to the difference between stream concentration and bed concentration. The second model assumes solute in the bed is transported by a vertical diffusion process described by Fick's law. The third model assumes that convection occurs in a selected portion of the bed while the mechanism of the first model functions everywhere. The model for adsorbing species assumes that the bed consists of particles of uniform size with the rate of uptake controlled by an intraparticle diffusion process. </p><p>All models are tested using data collected before, during and after a 24-hr. pulse injection of chloride, strontium, potassium and lead ions into Uvas Creek near Morgan Hill, California, U.S.A. All three conservative models accurately predict chloride ion concentrations in the stream. The model employing the diffusion mechanism for bed transport predicts better than the others. </p><p>The adsorption model predicts both strontium and potassium ion concentrations well during the injection of the pulse but somewhat overestimates the observed concentrations after the injection ceases. The overestimation may be due to the convection of solute deep into the bed where it is retained longer than the 3-week post-injection observation period. The model, when calibrated for strontium, predicts potassium equally well when the adsorption equilibrium constant for strontium is replaced by that for potassium.&nbsp;</p>","language":"English","publisher":"Elsevier","doi":"10.1016/0022-1694(84)90047-7","issn":"00221694","usgsCitation":"Jackman, A.P., Walters, R.A., and Kennedy, V.C., 1984, Transport and concentration controls for chloride, strontium, potassium and lead in Uvas Creek, a small cobble-bed stream in Santa Clara County, California, U.S.A.: 2. Mathematical modeling: Journal of Hydrology, v. 75, no. 1-4, p. 111-141, https://doi.org/10.1016/0022-1694(84)90047-7.","productDescription":"31 p.","startPage":"111","endPage":"141","costCenters":[{"id":154,"text":"California Water Science Center","active":true,"usgs":true}],"links":[{"id":220155,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"California","county":"Santa Clara County","geographicExtents":"{\"type\":\"FeatureCollection\",\"features\":[{\"type\":\"Feature\",\"id\":227,\"properties\":{\"name\":\"Santa Clara\",\"state\":\"CA\"},\"geometry\":{\"type\":\"MultiPolygon\",\"coordinates\":[[[[-121.983,37.4615],[-121.981,37.4612],[-121.978,37.4613],[-121.97,37.4619],[-121.961,37.4629],[-121.955,37.4604],[-121.947,37.466],[-121.939,37.462],[-121.933,37.4594],[-121.927,37.4541],[-121.923,37.4542],[-121.92,37.4574],[-121.908,37.464],[-121.897,37.467],[-121.89,37.4675],[-121.887,37.4708],[-121.881,37.4714],[-121.865,37.4848],[-121.471,37.4818],[-121.477,37.4781],[-121.484,37.4735],[-121.482,37.4667],[-121.472,37.4573],[-121.464,37.4511],[-121.46,37.4398],[-121.467,37.437],[-121.469,37.4334],[-121.471,37.4297],[-121.472,37.4243],[-121.468,37.4162],[-121.462,37.4144],[-121.458,37.4109],[-121.456,37.4041],[-121.458,37.3968],[-121.45,37.3951],[-121.449,37.392],[-121.444,37.3921],[-121.435,37.3945],[-121.422,37.3933],[-121.42,37.3897],[-121.411,37.3876],[-121.409,37.3776],[-121.416,37.3744],[-121.418,37.3666],[-121.424,37.3615],[-121.421,37.353],[-121.419,37.3444],[-121.414,37.3386],[-121.409,37.3341],[-121.41,37.3264],[-121.407,37.3187],[-121.41,37.3123],[-121.424,37.2999],[-121.433,37.2961],[-121.442,37.2991],[-121.449,37.2977],[-121.45,37.2918],[-121.454,37.2885],[-121.459,37.2839],[-121.454,37.279],[-121.454,37.2713],[-121.455,37.2491],[-121.45,37.2419],[-121.441,37.2325],[-121.43,37.2286],[-121.426,37.2237],[-121.421,37.2147],[-121.419,37.2047],[-121.413,37.1912],[-121.414,37.1763],[-121.41,37.1632],[-121.404,37.1542],[-121.396,37.1525],[-121.39,37.1549],[-121.386,37.1549],[-121.385,37.1608],[-121.386,37.1681],[-121.376,37.175],[-121.37,37.181],[-121.365,37.1843],[-121.358,37.1857],[-121.352,37.1849],[-121.344,37.1778],[-121.337,37.1747],[-121.331,37.1712],[-121.322,37.1691],[-121.312,37.1719],[-121.307,37.1706],[-121.301,37.1698],[-121.296,37.1708],[-121.29,37.1795],[-121.287,37.1832],[-121.281,37.1819],[-121.275,37.1761],[-121.268,37.1694],[-121.262,37.1622],[-121.253,37.161],[-121.247,37.1602],[-121.242,37.158],[-121.24,37.1517],[-121.235,37.1413],[-121.227,37.1369],[-121.222,37.1283],[-121.219,37.1243],[-121.219,37.1171],[-121.225,37.112],[-121.227,37.1065],[-121.231,37.1015],[-121.231,37.0969],[-121.238,37.0937],[-121.244,37.0891],[-121.241,37.0864],[-121.231,37.0833],[-121.225,37.0771],[-121.218,37.0717],[-121.209,37.0655],[-121.21,37.0582],[-121.225,37.0535],[-121.223,37.0399],[-121.234,37.0366],[-121.248,37.0314],[-121.245,37.0237],[-121.237,37.0152],[-121.237,37.0071],[-121.233,37.0008],[-121.245,36.9947],[-121.247,36.9902],[-121.247,36.9838],[-121.242,36.9748],[-121.231,36.97],[-121.212,36.9607],[-121.257,36.9596],[-121.345,36.9606],[-121.377,36.9601],[-121.42,36.9608],[-121.428,36.9684],[-121.434,36.9769],[-121.444,36.9853],[-121.458,36.986],[-121.463,36.9818],[-121.468,36.979],[-121.471,36.9785],[-121.487,36.9837],[-121.49,36.9805],[-121.499,36.9717],[-121.505,36.9639],[-121.513,36.9584],[-121.512,36.9525],[-121.515,36.947],[-121.518,36.9415],[-121.519,36.9419],[-121.529,36.9336],[-121.537,36.9271],[-121.539,36.9221],[-121.544,36.9184],[-121.553,36.9146],[-121.559,36.9095],[-121.559,36.9063],[-121.56,36.8968],[-121.562,36.8963],[-121.571,36.8966],[-121.575,36.8929],[-121.58,36.8996],[-121.58,36.919],[-121.59,36.9188],[-121.59,36.9262],[-121.609,36.926],[-121.624,36.9409],[-121.637,36.939],[-121.644,36.933],[-121.646,36.9357],[-121.652,36.9396],[-121.653,36.9461],[-121.652,36.9496],[-121.653,36.951],[-121.656,36.9504],[-121.661,36.951],[-121.662,36.9519],[-121.664,36.9641],[-121.67,36.9644],[-121.68,36.9677],[-121.681,36.9681],[-121.69,36.968],[-121.698,36.9737],[-121.696,36.9842],[-121.704,36.9868],[-121.712,36.9902],[-121.717,36.9956],[-121.711,37.0039],[-121.712,37.0134],[-121.717,37.0137],[-121.743,37.0314],[-121.746,37.0372],[-121.754,37.0448],[-121.754,37.0516],[-121.761,37.0515],[-121.772,37.0535],[-121.781,37.0588],[-121.787,37.0641],[-121.803,37.0684],[-121.81,37.0714],[-121.817,37.0799],[-121.821,37.0834],[-121.824,37.0875],[-121.839,37.094],[-121.848,37.0974],[-121.861,37.1008],[-121.866,37.103],[-121.893,37.1115],[-121.899,37.1137],[-121.915,37.1156],[-121.927,37.1231],[-121.935,37.1234],[-121.946,37.1268],[-121.954,37.1302],[-121.962,37.1333],[-121.968,37.1386],[-121.978,37.1447],[-121.987,37.1459],[-121.991,37.1458],[-121.997,37.1525],[-122.006,37.1596],[-122.019,37.1674],[-122.036,37.1848],[-122.035,37.1939],[-122.042,37.201],[-122.045,37.2041],[-122.058,37.2129],[-122.068,37.2118],[-122.071,37.2176],[-122.074,37.2198],[-122.08,37.2233],[-122.082,37.2219],[-122.095,37.2253],[-122.101,37.2333],[-122.103,37.2405],[-122.108,37.2486],[-122.117,37.2593],[-122.132,37.2585],[-122.145,37.27],[-122.143,37.2732],[-122.152,37.2862],[-122.155,37.292],[-122.167,37.2953],[-122.162,37.3036],[-122.161,37.3077],[-122.168,37.3135],[-122.186,37.3099],[-122.189,37.3193],[-122.183,37.3245],[-122.176,37.3283],[-122.181,37.334],[-122.192,37.3442],[-122.2,37.3586],[-122.202,37.3658],[-122.199,37.3726],[-122.193,37.3778],[-122.186,37.3888],[-122.189,37.3973],[-122.189,37.4023],[-122.192,37.4086],[-122.189,37.4155],[-122.19,37.4187],[-122.191,37.42],[-122.189,37.4227],[-122.189,37.425],[-122.189,37.4259],[-122.19,37.4282],[-122.19,37.4295],[-122.189,37.4314],[-122.185,37.4351],[-122.182,37.4392],[-122.18,37.4411],[-122.177,37.4425],[-122.17,37.4481],[-122.166,37.4532],[-122.162,37.4546],[-122.159,37.4551],[-122.157,37.4552],[-122.154,37.4566],[-122.152,37.4571],[-122.149,37.4567],[-122.146,37.4573],[-122.144,37.4564],[-122.139,37.4547],[-122.137,37.4543],[-122.135,37.4543],[-122.131,37.4526],[-122.127,37.4527],[-122.119,37.4524],[-122.111,37.4535],[-122.11,37.458],[-122.103,37.4564],[-122.101,37.4582],[-122.101,37.4575],[-122.101,37.4569],[-122.1,37.4572],[-122.098,37.4578],[-122.098,37.4581],[-122.097,37.4581],[-122.097,37.4578],[-122.095,37.4564],[-122.095,37.4558],[-122.094,37.455],[-122.094,37.4547],[-122.092,37.4528],[-122.092,37.4525],[-122.091,37.4519],[-122.091,37.4519],[-122.089,37.4517],[-122.088,37.4514],[-122.086,37.4506],[-122.082,37.452],[-122.081,37.452],[-122.08,37.4517],[-122.079,37.4508],[-122.078,37.4493],[-122.078,37.4491],[-122.077,37.4493],[-122.076,37.4499],[-122.075,37.4496],[-122.071,37.4503],[-122.069,37.4509],[-122.068,37.4507],[-122.065,37.4478],[-122.064,37.4467],[-122.064,37.4462],[-122.064,37.4445],[-122.065,37.4436],[-122.067,37.4417],[-122.067,37.4414],[-122.067,37.4389],[-122.067,37.4361],[-122.067,37.4358],[-122.067,37.435],[-122.067,37.4347],[-122.067,37.4339],[-122.067,37.4336],[-122.067,37.4328],[-122.067,37.4325],[-122.064,37.4319],[-122.063,37.4303],[-122.063,37.4297],[-122.063,37.4291],[-122.061,37.4289],[-122.06,37.4286],[-122.059,37.4283],[-122.058,37.4281],[-122.058,37.4283],[-122.056,37.43],[-122.056,37.4303],[-122.055,37.4303],[-122.054,37.4311],[-122.054,37.4311],[-122.051,37.4314],[-122.051,37.4308],[-122.051,37.4294],[-122.05,37.4294],[-122.049,37.4289],[-122.049,37.4283],[-122.049,37.4281],[-122.049,37.4275],[-122.049,37.4272],[-122.048,37.4267],[-122.046,37.4267],[-122.046,37.4269],[-122.045,37.4269],[-122.045,37.4272],[-122.044,37.4269],[-122.042,37.4269],[-122.042,37.4272],[-122.04,37.4275],[-122.04,37.4272],[-122.037,37.4275],[-122.037,37.4272],[-122.036,37.4272],[-122.036,37.4267],[-122.031,37.4239],[-122.031,37.4239],[-122.031,37.4244],[-122.03,37.4244],[-122.029,37.4233],[-122.028,37.4233],[-122.028,37.4236],[-122.027,37.4236],[-122.027,37.4239],[-122.026,37.4236],[-122.025,37.4232],[-122.024,37.4231],[-122.023,37.4231],[-122.023,37.4228],[-122.022,37.4228],[-122.022,37.4225],[-122.021,37.4225],[-122.021,37.4219],[-122.021,37.4219],[-122.019,37.4222],[-122.018,37.4222],[-122.018,37.4231],[-122.018,37.4233],[-122.017,37.4247],[-122.018,37.4253],[-122.018,37.4258],[-122.017,37.4261],[-122.017,37.4261],[-122.015,37.4253],[-122.015,37.4258],[-122.014,37.4258],[-122.013,37.4264],[-122.013,37.4264],[-122.012,37.4278],[-122.012,37.4283],[-122.01,37.4303],[-122.009,37.4303],[-122.009,37.43],[-122.009,37.4308],[-122.009,37.4314],[-122.01,37.4314],[-122.01,37.4317],[-122.011,37.4322],[-122.011,37.4319],[-122.016,37.4319],[-122.016,37.4317],[-122.018,37.4311],[-122.018,37.4314],[-122.02,37.4314],[-122.021,37.4317],[-122.023,37.4317],[-122.023,37.4319],[-122.025,37.4327],[-122.025,37.4331],[-122.026,37.4331],[-122.028,37.4348],[-122.029,37.4354],[-122.029,37.4364],[-122.029,37.4369],[-122.029,37.4378],[-122.03,37.4381],[-122.03,37.4386],[-122.03,37.4389],[-122.03,37.44],[-122.031,37.4408],[-122.032,37.4408],[-122.033,37.4406],[-122.034,37.4397],[-122.034,37.4397],[-122.034,37.4394],[-122.035,37.4397],[-122.037,37.4397],[-122.037,37.44],[-122.038,37.44],[-122.039,37.4406],[-122.039,37.4406],[-122.04,37.4411],[-122.04,37.4419],[-122.04,37.4422],[-122.041,37.4431],[-122.041,37.4442],[-122.041,37.4444],[-122.041,37.445],[-122.041,37.4453],[-122.041,37.4458],[-122.04,37.4464],[-122.04,37.4467],[-122.039,37.4475],[-122.039,37.4475],[-122.039,37.4481],[-122.038,37.4481],[-122.037,37.4483],[-122.036,37.4481],[-122.036,37.4478],[-122.035,37.4478],[-122.035,37.4475],[-122.034,37.4475],[-122.033,37.447],[-122.032,37.4468],[-122.031,37.448],[-122.031,37.4489],[-122.031,37.4492],[-122.032,37.4506],[-122.033,37.4506],[-122.034,37.4519],[-122.035,37.453],[-122.035,37.4532],[-122.038,37.4536],[-122.038,37.4536],[-122.039,37.4539],[-122.039,37.4555],[-122.038,37.4555],[-122.037,37.4563],[-122.037,37.4571],[-122.034,37.4592],[-122.034,37.4594],[-122.033,37.4605],[-122.032,37.4609],[-122.031,37.4611],[-122.031,37.4614],[-122.029,37.4617],[-122.029,37.4619],[-122.028,37.4622],[-122.027,37.4619],[-122.027,37.4622],[-122.026,37.4628],[-122.026,37.4628],[-122.024,37.4622],[-122.024,37.4619],[-122.022,37.4628],[-122.022,37.4636],[-122.021,37.4639],[-122.019,37.4644],[-122.019,37.4647],[-122.019,37.4647],[-122.018,37.465],[-122.017,37.465],[-122.017,37.4653],[-122.016,37.4653],[-122.015,37.465],[-122.014,37.4653],[-122.014,37.4656],[-122.013,37.4656],[-122.013,37.4658],[-122.012,37.4658],[-122.011,37.4661],[-122.01,37.4661],[-122.01,37.4664],[-122.009,37.4664],[-122.008,37.4667],[-122.007,37.4667],[-122.006,37.4667],[-122.006,37.4669],[-122.004,37.4667],[-122.004,37.4669],[-122.003,37.4667],[-122.003,37.4664],[-122.001,37.4664],[-122,37.4661],[-121.998,37.4661],[-121.998,37.4658],[-121.995,37.4644],[-121.995,37.4644],[-121.994,37.4639],[-121.994,37.4639],[-121.994,37.4636],[-121.988,37.4619],[-121.988,37.4617],[-121.987,37.4617],[-121.987,37.4614],[-121.986,37.4614],[-121.986,37.4611],[-121.985,37.4611],[-121.985,37.4608],[-121.984,37.4608],[-121.984,37.4606],[-121.983,37.4606],[-121.983,37.4603],[-121.982,37.4603],[-121.982,37.46],[-121.98,37.4597],[-121.98,37.4594],[-121.979,37.4606],[-121.98,37.4606],[-121.98,37.4608],[-121.981,37.4608],[-121.982,37.4611],[-121.983,37.4611],[-121.983,37.4615]]],[[[-121.9828,37.4615],[-121.9836,37.4614],[-121.9839,37.4616],[-121.9828,37.4615]]]]}}]}","volume":"75","issue":"1-4","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505bb736e4b08c986b32710c","contributors":{"authors":[{"text":"Jackman, A. P.","contributorId":46957,"corporation":false,"usgs":true,"family":"Jackman","given":"A.","email":"","middleInitial":"P.","affiliations":[],"preferred":false,"id":366495,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Walters, R. A.","contributorId":34174,"corporation":false,"usgs":true,"family":"Walters","given":"R.","email":"","middleInitial":"A.","affiliations":[],"preferred":false,"id":366493,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Kennedy, V. C.","contributorId":46080,"corporation":false,"usgs":true,"family":"Kennedy","given":"V.","email":"","middleInitial":"C.","affiliations":[],"preferred":false,"id":366494,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
,{"id":70013271,"text":"70013271 - 1984 - Groundwater-flow parameter estimation and quality modeling of the Equus Beds aquifer in Kansas, U.S.A.","interactions":[],"lastModifiedDate":"2025-04-14T16:53:54.718216","indexId":"70013271","displayToPublicDate":"2003-03-27T00:00:00","publicationYear":"1984","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":"Groundwater-flow parameter estimation and quality modeling of the Equus Beds aquifer in Kansas, U.S.A.","docAbstract":"<p>The salinity problems created in the Burrton area as a result of poor oil-field brine disposal practices of the past continue to be a major concern to the area depending on the Equus Beds aquifer for water, including the City of Wichita, Kansas. In this paper, an attempt is made to predict where and how fast the brine plume will move in this area, and what the average chloride concentrations in different parts of the aquifer are. In order to make such predictions, it was necessary to get a calibrated model of the groundwater-flow velocity field. Multiple regression analysis is used for parameter estimation of the steady-state groundwater-flow equation applied in the most critical area of the Equus Beds aquifer. Results of such an analysis produced a correlation coefficient of 0.992 between calculated and observed values of hydraulic head. A chloride transport modeling effort is then carried out despite some serious data deficiencies, the significance of which are evaluated through sensitivity analysis. Thus, starting with the quasi steady-state conditions of the early 1940's, it was possible to match the present chloride distribution satisfactorily. Chloride concentration predictions made for the year 2000 indicate that the quality of the Wichita well-field waters will not generally deteriorate from their present condition by that time.&nbsp;</p>","language":"English","publisher":"Elsevier","doi":"10.1016/0022-1694(84)90164-1","issn":"00221694","usgsCitation":"Sophocleous, M., 1984, Groundwater-flow parameter estimation and quality modeling of the Equus Beds aquifer in Kansas, U.S.A.: Journal of Hydrology, v. 69, no. 1-4, p. 197-222, https://doi.org/10.1016/0022-1694(84)90164-1.","productDescription":"26 p.","startPage":"197","endPage":"222","costCenters":[],"links":[{"id":219846,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"Kansas","otherGeospatial":"Equus Beds aquifer","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"coordinates\": [\n          [\n            [\n              -97.75234872951685,\n              38.17839167762153\n            ],\n            [\n              -97.75234872951685,\n              37.4855633758371\n            ],\n            [\n              -96.79405394886194,\n              37.4855633758371\n            ],\n            [\n              -96.79405394886194,\n              38.17839167762153\n            ],\n            [\n              -97.75234872951685,\n              38.17839167762153\n            ]\n          ]\n        ],\n        \"type\": \"Polygon\"\n      }\n    }\n  ]\n}","volume":"69","issue":"1-4","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505a2dcde4b0c8380cd5c02c","contributors":{"authors":[{"text":"Sophocleous, M.A.","contributorId":18032,"corporation":false,"usgs":true,"family":"Sophocleous","given":"M.A.","email":"","affiliations":[],"preferred":false,"id":365692,"contributorType":{"id":1,"text":"Authors"},"rank":1}]}}
,{"id":70013221,"text":"70013221 - 1984 - Experimental studies in natural groundwater recharge dynamics: Assessment of recent advances in instrumentation","interactions":[],"lastModifiedDate":"2025-04-14T17:00:46.569772","indexId":"70013221","displayToPublicDate":"2003-03-25T00:00:00","publicationYear":"1984","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":"Experimental studies in natural groundwater recharge dynamics: Assessment of recent advances in instrumentation","docAbstract":"<p>To quantify and model the natural groundwater-recharge process, two sites in south-central Kansas, U.S.A., were instrumented with various modern sensors and data microloggers. The atmospheric-boundary layer and the unsaturated and saturated soil zones were monitored as a unified regime. Data from the various sensors were collected using microloggers in combination with magnetic-cassette tape, graphical and digital recorders, analog paper-tape recorders, and direct observations to evaluate and automate data collection and processing. </p><p>Atmospheric sensors included an anemometer, a tipping-bucket raingage, an air-temperature thermistor, a relative-humidity probe, a net radiometer, and a barometric-pressure transducer. Sensors in the unsaturated zone consisted of soil-temperature thermocouples, tensiometers coupled with pressure transducers and dial gages, gypsum blocks, and a neutron moisture probe operated by an observer. The saturated-zone sensors consisted of a water-level pressure transducer, a conventional float gage connected to a variable potentiometer, soil thermocouples, and a number of multiple-depth piezometers. </p><p>Evaluation of the operation of these sensors and recorders indicated that certain types of equipment such as pressure transducers are very sensitive to environmental conditions. Extraordinary steps had to be taken to protect some of the equipment, whereas other equipment seemed to be reliable under all conditions. Based on such experiences, a number of suggestions aimed at improving such investigations are outlined.&nbsp;</p>","language":"English","publisher":"Elsevier","doi":"10.1016/0022-1694(84)90133-1","issn":"00221694","usgsCitation":"Sophocleous, M., and Perry, C.A., 1984, Experimental studies in natural groundwater recharge dynamics: Assessment of recent advances in instrumentation: Journal of Hydrology, v. 70, no. 1-4, p. 369-382, https://doi.org/10.1016/0022-1694(84)90133-1.","productDescription":"14 p.","startPage":"369","endPage":"382","costCenters":[],"links":[{"id":220081,"rank":1,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/outside_thumb.jpg"}],"country":"United States","state":"Kansas","geographicExtents":"{\n  \"type\": \"FeatureCollection\",\n  \"features\": [\n    {\n      \"type\": \"Feature\",\n      \"properties\": {},\n      \"geometry\": {\n        \"coordinates\": [\n          [\n            [\n              -99.1748871630371,\n              38.507940104645996\n            ],\n            [\n              -99.1748871630371,\n              37.64917420455242\n            ],\n            [\n              -97.68600447634276,\n              37.64917420455242\n            ],\n            [\n              -97.68600447634276,\n              38.507940104645996\n            ],\n            [\n              -99.1748871630371,\n              38.507940104645996\n            ]\n          ]\n        ],\n        \"type\": \"Polygon\"\n      }\n    }\n  ]\n}","volume":"70","issue":"1-4","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"505a0ddfe4b0c8380cd53226","contributors":{"authors":[{"text":"Sophocleous, M.","contributorId":13373,"corporation":false,"usgs":true,"family":"Sophocleous","given":"M.","email":"","affiliations":[],"preferred":false,"id":365571,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Perry, C. A.","contributorId":106149,"corporation":false,"usgs":true,"family":"Perry","given":"C.","email":"","middleInitial":"A.","affiliations":[],"preferred":false,"id":365572,"contributorType":{"id":1,"text":"Authors"},"rank":2}]}}
,{"id":60252,"text":"mf1246L - 1984 - Maps showing distribution of pH, copper, zinc, fluoride, uranium, molybdenum, arsenic, and sulfate in water, Richfield 1° x 2° quadrangle, Utah","interactions":[],"lastModifiedDate":"2021-10-25T19:02:48.751765","indexId":"mf1246L","displayToPublicDate":"1994-01-01T07:00:00","publicationYear":"1984","noYear":false,"publicationType":{"id":18,"text":"Report"},"publicationSubtype":{"id":5,"text":"USGS Numbered Series"},"seriesTitle":{"id":325,"text":"Miscellaneous Field Studies Map","code":"MF","active":false,"publicationSubtype":{"id":5}},"seriesNumber":"1246","chapter":"L","title":"Maps showing distribution of pH, copper, zinc, fluoride, uranium, molybdenum, arsenic, and sulfate in water, Richfield 1° x 2° quadrangle, Utah","docAbstract":"<p>These maps show the regional distribution of copper, zinc, arsenic, molybdenum, uranium, fluoride, sulfate, and pH in surface and ground water from the Richfield 1° x 2° quadrangle. This study supplements (Miller and others, 1984a-j) the regional drainage geochemical study done for the Richfield quadrangle under the U.S. Geological Survey’s Conterminuous United States Mineral Assessment Program (CUSMAP). Regional sampling was designed to define broad geochemical patterns and trends which can be used, along with geologic and geophysical data, to assess the mineral resource potential of the Richfield quadrangle. Analytical data used in compiling this report were published previously (McHugh and others, 1981).</p>\n<br/>\n<p>The Richfield quadrangle in west-central Utah covers the eastern part of the Pioche-Marysvale igneous and mineral belt that extends from the vicinity of Pioche in southeastern Nevada, east-northeastward for 250 km into central Utah. The western two-thirds of the Richfield quadrangle is in the Basin and Range Province, and the eastern third in the High Plateaus of Utah subprovince of the Colorado Plateau.</p>\n<br/>\n<p>Bedrock in the northern part of the Richfield quadrangle consists predominantly of latest Precambrian and Paleozoic sedimentary strata that were thrust eastward during the Sevier orogeny in Cretaceous time onto an autochthon of Mesozoic sedimentary rocks in the eastern part of the quadrangle. The southern part of the quadrangle is largely underlain by Oligocene and younger volcanic rocks and related intrusions. Extensional tectonism in late Cenozoic time broke the bedrock terrane into a series of north-trending fault blocks; the uplifted mountain areas were deeply eroded and the resulting debris deposited in the adjacent basins. Most of the mineral deposits in the Pioche-Marysvale mineral belt were formed during igneous activity in the middle and late Cenozoic time.</p>","language":"English","publisher":"U.S. Geological Survey","publisherLocation":"Denver CO","doi":"10.3133/mf1246L","usgsCitation":"McHugh, J.B., Miller, W.R., and Ficklin, W.H., 1984, Maps showing distribution of pH, copper, zinc, fluoride, uranium, molybdenum, arsenic, and sulfate in water, Richfield 1° x 2° quadrangle, Utah: U.S. Geological Survey Miscellaneous Field Studies Map 1246, 1 Plate: 40.89 x 32.77 inches, https://doi.org/10.3133/mf1246L.","productDescription":"1 Plate: 40.89 x 32.77 inches","costCenters":[],"links":[{"id":182629,"rank":0,"type":{"id":24,"text":"Thumbnail"},"url":"https://pubs.usgs.gov/thumbnails/mf1246l.jpg"},{"id":283659,"type":{"id":17,"text":"Plate"},"url":"https://pubs.usgs.gov/mf/1246-L/plate-1.pdf"},{"id":390899,"rank":3,"type":{"id":36,"text":"NGMDB Index Page"},"url":"https://ngmdb.usgs.gov/Prodesc/proddesc_6856.htm"}],"scale":"500000","country":"United States","state":"Utah","otherGeospatial":"Richfield 1° x 2° quadrangle","geographicExtents":"{ \"type\": \"FeatureCollection\", \"features\": [ { \"type\": \"Feature\", \"properties\": {}, \"geometry\": { \"type\": \"Polygon\", \"coordinates\": [ [ [ -114.0,38.0 ], [ -114.0,39.0 ], [ -112.0,39.0 ], [ -112.0,38.0 ], [ -114.0,38.0 ] ] ] } } ] }","noUsgsAuthors":false,"publicationStatus":"PW","scienceBaseUri":"4f4e4a19e4b07f02db60578b","contributors":{"authors":[{"text":"McHugh, J. B.","contributorId":79462,"corporation":false,"usgs":true,"family":"McHugh","given":"J.","email":"","middleInitial":"B.","affiliations":[],"preferred":false,"id":263391,"contributorType":{"id":1,"text":"Authors"},"rank":1},{"text":"Miller, W. R.","contributorId":92239,"corporation":false,"usgs":true,"family":"Miller","given":"W.","email":"","middleInitial":"R.","affiliations":[],"preferred":false,"id":263393,"contributorType":{"id":1,"text":"Authors"},"rank":2},{"text":"Ficklin, W. H.","contributorId":89517,"corporation":false,"usgs":true,"family":"Ficklin","given":"W.","email":"","middleInitial":"H.","affiliations":[],"preferred":false,"id":263392,"contributorType":{"id":1,"text":"Authors"},"rank":3}]}}
]}