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revisited 68 plots of forest vegetation in the San Bernardino Mountains that had been quantitatively described in 1929‐1935, from the California Vegetation Type Map (VTM) Survey. By using the same sampling methods, we documented changes—over approximately 60 years and during a period of fire suppression management—in tree density by both species and size class. In general, we found increasing stand densities, a transformation from old‐growth age structure to young growth, and a compositional shift from \u003Cjats:italic>Pinus ponderosa\u003C\u002Fjats:italic> and \u003Cjats:italic>P. jeffreyi\u003C\u002Fjats:italic> to \u003Cjats:italic>Abies concolor\u003C\u002Fjats:italic> and \u003Cjats:italic>Calocedrus decurrens\u003C\u002Fjats:italic>. Density of trees of more than 12 cm diameter at breast height (dbh) increased by 79%, including three to ten‐fold increases in the youngest cohorts 12–66 cm dbh. The magnitude of change depended upon initial forest composition and local annual precipitation. Monotypic stands of \u003Cjats:italic>P. jeffreyi\u003C\u002Fjats:italic> or those initially dominated by \u003Cjats:italic>Abies concolor\u003C\u002Fjats:italic> showed the least change in species composition; the most xeric stands of \u003Cjats:italic>P. jeffreyi\u003C\u002Fjats:italic> showed the least gain in density; and mesic mixed \u003Cjats:italic>P. ponderosa\u003C\u002Fjats:italic> stands showed the most dramatic change in composition and density. We compared these data to records of past and present forests in the Sierra Nevada and found parallel trends, but magnified by the increased precipitation of the Sierra Nevada. We also compared VTM data from the San Bernardino Mountains to mixed conifer forests in the Sierra San Pedro Martir of Baja California. These Mexican sites and forests are ecologically similar to those in California, but they still experience unmanaged fire regimes. Californian forests of 60 years ago are remarkably similar to modern forests in the Sierra San Pedro Martir. Thus, we conclude that forest changes in the San Bernardino Mountains are primarily due to lengthening fire intervals. Forest changes as a result of fire suppression have important conservation consequences for bird species diversity in general and for Spotted Owl and Neotropical migrants in particular.\u003C\u002Fjats:p>",{"EN":525},"Sixty Years of Change in Californian Conifer Forests of the San Bernardino Mountains",{"VOID":527},"10.1046\u002Fj.1523-1739.1995.09040902.x",{"VOID":529},"[\"11245051753117407721\"]",[196],"https:\u002F\u002Fconbio.onlinelibrary.wiley.com\u002Fdoi\u002F10.1046\u002Fj.1523-1739.1995.09040902.x",[533,553,572,587],{"id":534,"sortIndex":138,"researcher":24,"roles":535,"affiliations":536,"properties":548},"cfb01d6a-0f21-427e-8885-7e137c7470f6",[],[537],{"id":538,"sortIndex":25,"affiliation":539,"properties":24},"58c5c8e6-5156-4f72-92c5-3746de7fb87c",{"id":540,"createTime":541,"updateTime":542,"relativeEntities":543,"slug":544,"properties":545,"entityType":69,"verifyStatus":23,"verifyTime":24,"verifyNote":24,"syncStatus":23,"languages":24,"translateLanguages":24,"viewCount":25},"59f940db-2f58-4cef-a314-3e268c328b5c","2024-01-25T18:50:10.235+00:00","2024-09-26T05:09:10.363+00:00",[],"Department-of-Environmental-Horticulture-University-of-California-Davis-CA-95616-U-S-A-",{"title":546},{"VI":547},"Department of Environmental Horticulture University of California, Davis, CA 95616, U.S.A.",{"openalex":549,"title":551},{"VOID":550},"A5103839034",{"EN":552},"Michael G. 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We examined effects of river impoundments, one of the leading threats to freshwater biodiversity, on an important ecosystem service provided by large tropical rivers (i.e., artisanal fisheries). The societal and economic importance of this ecosystem service in developing countries may provide leverage to advance conservation agendas where future impoundments are being considered. We assessed impoundment effects on the energetic costs of fisheries production (embodied energy) and commercial market value of the artisanal fishery of the Paraná River, Brazil, before and after formation of Itaipu Reservoir. High‐value migratory species that dominated the fishery before the impoundment was built constituted a minor component of the contemporary fishery that is based heavily on reservoir‐adapted introduced species. Cascading effects of river impoundment resulted in a mismatch between embodied energy and market value: energetic costs of fisheries production increased, whereas market value decreased. This was partially attributable to changes in species functional composition but also strongly linked to species identities that affected market value as a result of consumer preferences even when species were functionally similar. Similar trends are expected in other large tropical rivers following impoundment. In addition to identifying consequences of a common anthropogenic impact on an important ecosystem service, our assessment provides insight into the sustainability of fisheries production in tropical rivers and priorities for regional biodiversity conservation\u003C\u002Fjats:italic>.\u003C\u002Fjats:p>",{"EN":665},"Effects of River Impoundment on Ecosystem Services of Large Tropical Rivers: Embodied Energy and Market Value of Artisanal Fisheries",{"VOID":667},"19459891",{"VOID":669},"10.1111\u002Fj.1523-1739.2009.01248.x","2024-09-04T23:36:31.639+00:00",[196],"https:\u002F\u002Fconbio.onlinelibrary.wiley.com\u002Fdoi\u002F10.1111\u002Fj.1523-1739.2009.01248.x",[674,695,714,731,779,796,813,848],{"id":675,"sortIndex":129,"researcher":24,"roles":676,"affiliations":677,"properties":688},"892fd632-c557-45c7-9bfe-650e4abf8ebd",[],[678],{"id":679,"sortIndex":25,"affiliation":680,"properties":24},"62e258a6-df23-4347-b664-171add07bb41",{"id":681,"createTime":682,"updateTime":682,"relativeEntities":683,"slug":684,"properties":685,"entityType":69,"verifyStatus":23,"verifyTime":24,"verifyNote":24,"syncStatus":23,"languages":24,"translateLanguages":24,"viewCount":25},"4d8b26df-ecef-4e60-86a9-f8ce7b0bfa0d","2024-09-04T23:36:31.660+00:00",[],"Section-of-Ecology-Evolutionary-Biology-and-Systematics-Department-of-Wildlife-and-Fisheries-Sciences-Texas-A-M-University-College-Station-TX-77843-2258-U-S-A-",{"title":686},{"EN":687},"Section of Ecology, Evolutionary Biology and Systematics, Department of Wildlife and Fisheries Sciences, Texas A&M University, College Station, TX 77843-2258, U.S.A.",{"openalex":689,"orcid":691,"title":693},{"VOID":690},"A5068429122",{"VOID":692},"https:\u002F\u002Forcid.org\u002F0000-0003-0236-5129",{"EN":694},"Kirk O. 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E.Sparks.1989.The flood pulse concept in river‐floodplain systems. Pages110–127inD. P.Dodge editor.Proceedings of the international large rivers symposium. 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M., 2004, The Upper Paraná River and its floodplain: physical aspects, ecology and conservation",{},{"id":24,"text":1097,"url":24,"identifiers":1098},"10.1016\u002FS0921-8009(03)00189-7",{"doi":1097},{"id":24,"text":1100,"url":24,"identifiers":1101},"Welcomme R. andA.Halls.2004.Dependence of tropical river fisheries on flow. Pages267–283inR.WelcommeandT.Petr editors.Proceedings of the second international symposium on the management of large rivers for fisheries. Volume II.FAO Regional Office for Asia and the Pacific Bangkok .",{},{"id":24,"text":1103,"url":24,"identifiers":1104},"10.1890\u002F1051-0761(1999)009[0772:EVOFES]2.0.CO;2",{"doi":1103},{"id":24,"text":1106,"url":24,"identifiers":1107},"Winemiller K. O.2004.Floodplain river food webs: generalizations and implications for fisheries management. Pages285–309inR.WelcommeandT.Petr editors.Proceedings of the second international symposium on the management of large rivers for fisheries Volume II.FAO Regional Office for Asia and the Pacific Bangkok .",{},{"id":24,"text":1109,"url":24,"identifiers":1110},"10.1111\u002Fj.1095-8649.1998.tb01032.x",{"doi":1109},{"id":24,"text":1112,"url":24,"identifiers":1113},"Winemiller K. O., 2004, Food webs at the landscape level, 115",{},{"id":1115,"createTime":1116,"updateTime":1116,"relativeEntities":1117,"slug":1118,"properties":1119,"entityType":192,"verifyStatus":193,"verifyTime":1116,"verifyNote":194,"syncStatus":23,"languages":1131,"translateLanguages":24,"viewCount":25,"primaryUrl":1132,"fullTextUrl":24,"authors":1133,"publicationType":295,"publisherRelationship":1174,"citationCount":1211,"citationInfo":1212,"publishDate":1223,"publishYear":1224,"citationAnalyzeStatus":23,"lastCitationAnalyze":24,"indexDatabases":24,"openAccess":24,"references":1225,"isForceReanalyzing":509},"fcb064db-3d7b-4bbe-b58b-f4fe9f06181e","2024-09-22T23:23:37.393+00:00",[],"Biological-Criteria-for-Buffer-Zones-around-Wetlands-and-Riparian-Habitats-for-Amphibians-and-Reptiles",{"mag":1120,"keywords":1122,"openalex":1123,"abstract":1125,"title":1127,"doi":1129},{"VOID":1121},"2025754220",{},{"VOID":1124},"W2025754220",{"EN":1126},"\u003Cjats:p>\u003Cjats:bold>Abstract:\u003C\u002Fjats:bold> Terrestrial habitats surrounding wetlands are critical to the management of natural resources. Although the protection of water resources from human activities such as agriculture, silviculture, and urban development is obvious, it is also apparent that terrestrial areas surrounding wetlands are core habitats for many semiaquatic species that depend on mesic ecotones to complete their life cycle. For purposes of conservation and management, it is important to define core habitats used by local breeding populations surrounding wetlands. Our objective was to provide an estimate of the biologically relevant size of core habitats surrounding wetlands for amphibians and reptiles. We summarize data from the literature on the use of terrestrial habitats by amphibians and reptiles associated with wetlands ( 19 frog and 13 salamander species representing 1363 individuals; 5 snake and 28 turtle species representing more than 2245 individuals ). Core terrestrial habitat ranged from 159 to 290 m for amphibians and from 127 to 289 m for reptiles from the edge of the aquatic site. Data from these studies also indicated the importance of terrestrial habitats for feeding, overwintering, and nesting, and, thus, the biological interdependence between aquatic and terrestrial habitats that is essential for the persistence of populations. The minimum and maximum values for core habitats, depending on the level of protection needed, can be used to set biologically meaningful buffers for wetland and riparian habitats. These results indicate that large areas of terrestrial habitat surrounding wetlands are critical for maintaining biodiversity.\u003C\u002Fjats:p>",{"EN":1128},"Biological Criteria for Buffer Zones around Wetlands and Riparian Habitats for Amphibians and Reptiles",{"VOID":1130},"10.1046\u002Fj.1523-1739.2003.02177.x",[196],"https:\u002F\u002Fconbio.onlinelibrary.wiley.com\u002Fdoi\u002F10.1046\u002Fj.1523-1739.2003.02177.x",[1134,1155],{"id":1135,"sortIndex":25,"researcher":24,"roles":1136,"affiliations":1137,"properties":1148},"ae9df7dd-473a-4806-8f3d-c8cbff8ba654",[],[1138],{"id":1139,"sortIndex":25,"affiliation":1140,"properties":24},"f2bff735-811c-4c71-ac8b-2c0cd4242d1e",{"id":1141,"createTime":1142,"updateTime":1142,"relativeEntities":1143,"slug":1144,"properties":1145,"entityType":69,"verifyStatus":23,"verifyTime":24,"verifyNote":24,"syncStatus":23,"languages":24,"translateLanguages":24,"viewCount":25},"d9a4b6ec-1e19-4870-bb8e-31d6100a8efd","2024-09-22T23:23:37.412+00:00",[],"Division-of-Biological-Sciences-105-Tucker-Hall-University-of-Missouri-Columbia-MO-65211-7400-U-S-A-email-semlitschr-missouri-edu",{"title":1146},{"EN":1147},"Division of Biological Sciences, 105 Tucker Hall, University of Missouri, Columbia, MO 65211–7400, U.S.A., email semlitschr@missouri.edu",{"openalex":1149,"orcid":1151,"title":1153},{"VOID":1150},"A5023466505",{"VOID":1152},"https:\u002F\u002Forcid.org\u002F0000-0002-7999-5762",{"EN":1154},"Raymond D. 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A., 1996, Comparative demography and habitat use of western pond turtles in northern California: the effects of damming and related alterations",{},{"id":24,"text":1541,"url":24,"identifiers":1542},"10.2307\u002F1563809",{"doi":1541},{"id":24,"text":1544,"url":24,"identifiers":1545},"10.2307\u002F1445720",{"doi":1544},{"id":24,"text":1547,"url":24,"identifiers":1548},"10.2307\u002F1566123",{"doi":1547},{"id":24,"text":1550,"url":24,"identifiers":1551},"10.2307\u002F1564283",{"doi":1550},{"id":24,"text":1553,"url":24,"identifiers":1554},"10.1046\u002Fj.1523-1739.2002.01085.x",{"doi":1553},{"id":24,"text":1556,"url":24,"identifiers":1557},"10.2307\u002F1564646",{"doi":1556},{"id":24,"text":1559,"url":24,"identifiers":1560},"10.2307\u002F3672055",{"doi":1559},{"id":24,"text":1562,"url":24,"identifiers":1563},"Scott A. F. and A. Bufalino. 1997. Dynamics of the amphibian communities at two small ponds in Land Between the Lakes over the past decade. Page 117 in A. F. Scott S. W. Hamilton E. W. Chester and D. S. White editors. Proceedings of the seventh symposium on the natural history of Lower Tennessee and Cumberland River valleys. Austin Peay State University Clarksville Tennessee.",{},{"id":24,"text":1565,"url":24,"identifiers":1566},"Seburn C. N. L., 1997, Amphibians in decline: Canadian studies of a global problem, 64",{},{"id":24,"text":1568,"url":24,"identifiers":1569},"10.1139\u002Fz81-047",{"doi":1568},{"id":24,"text":1571,"url":24,"identifiers":1572},"Semlitsch R. D., 1983, Terrestrial movements of an eastern tiger salamander, Ambystoma tigrinum., Herpetological Review, 14, 112",{},{"id":24,"text":1574,"url":24,"identifiers":1575},"10.1046\u002Fj.1523-1739.1998.97274.x",{"doi":1574},{"id":24,"text":1577,"url":24,"identifiers":1578},"10.2307\u002F3802732",{"doi":1577},{"id":24,"text":1580,"url":24,"identifiers":1581},"10.1046\u002Fj.1523-1739.1998.98166.x",{"doi":1580},{"id":24,"text":1583,"url":24,"identifiers":1584},"Semlitsch R. D., 2001, Core habitat, not buffer zone., National Wetlands Newsletter, 23, 5",{},{"id":24,"text":1586,"url":24,"identifiers":1587},"Semlitsch R. D., 1988, Annual emergence of juvenile mud snakes ( Farancia abacura ) at aquatic habitats., Copeia, 988, 244",{},{"id":24,"text":1589,"url":24,"identifiers":1590},"10.1016\u002FB978-012178075-3\u002F50010-6",{"doi":1589},{"id":24,"text":1592,"url":24,"identifiers":1593},"Shealy R. M., 1976, The natural history of the Alabama map turtle, Graptemys pulchra Baur, in Alabama., Bulletin of the Florida State Museum. Biological Science, 21, 47",{},{"id":24,"text":1595,"url":24,"identifiers":1596},"10.1007\u002FBF00377034",{"doi":1595},{"id":24,"text":1598,"url":24,"identifiers":1599},"10.1016\u002F0006-3207(94)00055-U",{"doi":1598},{"id":24,"text":1601,"url":24,"identifiers":1602},"10.2307\u002F1446031",{"doi":1601},{"id":24,"text":1604,"url":24,"identifiers":1605},"10.2307\u002F1566130",{"doi":1604},{"id":24,"text":1607,"url":24,"identifiers":1608},"10.2307\u002F1943562",{"doi":1607},{"id":24,"text":1610,"url":24,"identifiers":1611},"Tuttle S. E., 1997, Ecology and natural history of the wood turtle ( Clemmys insculpta ) in southern Hampshire., Chelonian Conservation Biology, 2, 447",{},{"id":24,"text":1613,"url":24,"identifiers":1614},"Wacasey J. W., 1961, An ecological study of two sympatric species of salamanders, Ambystoma maculatum and Ambystoma jeffersonianum, in southern Michigan",{},{"id":24,"text":1616,"url":24,"identifiers":1617},"10.2307\u002F1565660",{"doi":1616},{"id":24,"text":1619,"url":24,"identifiers":1620},"Wiest J. A., 1982, Herpetological communities, 39",{},{"id":24,"text":1622,"url":24,"identifiers":1623},"Williams P. K., 1973, Seasonal movements and population dynamics of four sympatric mole salamanders, genus Ambystoma",{},{"id":24,"text":1625,"url":24,"identifiers":1626},"10.2307\u002F1563484",{"doi":1625},{"id":24,"text":1628,"url":24,"identifiers":1629},"Zug G. R., 1979, The marine toad Bufo marinus: a natural history resume of native populations",{},{"id":1631,"createTime":1632,"updateTime":1632,"relativeEntities":1633,"slug":1634,"properties":1635,"entityType":192,"verifyStatus":193,"verifyTime":1632,"verifyNote":194,"syncStatus":23,"languages":1646,"translateLanguages":24,"viewCount":25,"primaryUrl":1647,"fullTextUrl":24,"authors":1648,"publicationType":295,"publisherRelationship":1668,"citationCount":144,"citationInfo":1706,"publishDate":1709,"publishYear":1710,"citationAnalyzeStatus":23,"lastCitationAnalyze":24,"indexDatabases":24,"openAccess":24,"references":1711,"isForceReanalyzing":509},"2e7607a5-0cec-48d8-aa07-6df63cbd96f0","2024-09-01T23:18:55.448+00:00",[],"Crocodile-Tears-and-Skins-International-Trade-Economic-Constraints-and-Limits-to-the-Sustainable-Use-of-Crocodilians",{"mag":1636,"keywords":1638,"openalex":1639,"abstract":1641,"title":1642,"doi":1644},{"VOID":1637},"1969247769",{},{"VOID":1640},"W1969247769",{},{"EN":1643},"Crocodile Tears and Skins: International Trade, Economic Constraints, and Limits to the Sustainable Use of Crocodilians",{"VOID":1645},"10.1046\u002Fj.1523-1739.1999.00011.x",[196],"https:\u002F\u002Fconbio.onlinelibrary.wiley.com\u002Fdoi\u002F10.1046\u002Fj.1523-1739.1999.00011.x",[1649],{"id":1650,"sortIndex":25,"researcher":24,"roles":1651,"affiliations":1652,"properties":1663},"d9b4d6fd-c566-4621-ad04-77eefc3ccec2",[],[1653],{"id":1654,"sortIndex":25,"affiliation":1655,"properties":24},"8f9d1ad3-c9fd-4196-a80a-dc16bc0454df",{"id":1656,"createTime":1657,"updateTime":1657,"relativeEntities":1658,"slug":1659,"properties":1660,"entityType":69,"verifyStatus":23,"verifyTime":24,"verifyNote":24,"syncStatus":23,"languages":24,"translateLanguages":24,"viewCount":25},"d793cc4c-9080-4c31-9c09-e86ecf2f012f","2024-09-01T23:18:55.460+00:00",[],"Wildlife-Conservation-Society-2300-Southern-Boulevard-Bronx-NY-10460-U-S-A-email-jcaiman-aol-com",{"title":1661},{"EN":1662},"Wildlife Conservation Society, 2300 Southern Boulevard, Bronx, NY 10460, U.S.A., email jcaiman@aol.com",{"openalex":1664,"title":1666},{"VOID":1665},"A5021522822",{"EN":1667},"John B. 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International alligator crocodile trade study",{},{"id":24,"text":1716,"url":24,"identifiers":1717},"Bezuijen M. R., 1997, Project Tomistoma: second report on the ecology of the false gharial (Tomistoma schlegelii) in Sumatra",{},{"id":24,"text":1719,"url":24,"identifiers":1720},"Child G., 1987, Wildlife management: crocodiles and alligators, 49",{},{"id":24,"text":1722,"url":24,"identifiers":1723},"Collins L., 1996, World trade in crocodilian skins, 1992–1993",{},{"id":24,"text":1725,"url":24,"identifiers":1726},"Crocodile Specialist Group, 1992, Crocodile conservation action. Special publication of the Crocodile Specialist Group",{},{"id":24,"text":1728,"url":24,"identifiers":1729},"Crocodile Specialist Group, 1998, Steering committee of the Crocodile Specialist Group, 13 July 1998., Crocodile Specialist Group Newsletter, 17, 7",{},{"id":24,"text":1731,"url":24,"identifiers":1732},"David D. N., 1994, Harvesting wild crocodilians: guidelines for developing a sustainable use program. Pages 274–309 in Crocodiles. Volume 1. Proceedings of the 12th working meeting of the Crocodile Specialist Group",{},{"id":24,"text":1734,"url":24,"identifiers":1735},"Gaski A. L., 1988, The ups and downs of the crocodilian skin trade., TRAFFIC (USA), 8, 1",{},{"id":24,"text":1737,"url":24,"identifiers":1738},"Glasgow V. L., 1991, A social history of the American alligator",{},{"id":24,"text":1740,"url":24,"identifiers":1741},"Hollands M., 1987, Wildlife management: crocodiles and alligators, 73",{},{"id":24,"text":1743,"url":24,"identifiers":1744},"Hutton J. M. 1992. Report of the coordinator of the CITES Nile crocodile project to the CITES Secretariat as presented to the Parties at the seventh meeting of the Conference of the Parties Lausanne Switzerland 1989. Pages 169–214 in J. M. Hutton and I. Games editors. Committee on International Trade in Endangered Species Gland Switzerland.",{},{"id":24,"text":1746,"url":24,"identifiers":1747},"Inskipp T., 1979, International trade in wildlife",{},{"id":24,"text":1749,"url":24,"identifiers":1750},"Jenkins M. and S. Broad. 1994. International trade in reptile skins. A review of the main consumer markets 1983–1991. TRAFFIC International Cambridge United Kingdom.",{},{"id":24,"text":1752,"url":24,"identifiers":1753},"Jenkins R. W. G., 1987, Wildlife management: crocodiles and alligators, 27",{},{"id":24,"text":1755,"url":24,"identifiers":1756},"Joanen T., 1997, Harvesting wild species, 465",{},{"id":24,"text":1758,"url":24,"identifiers":1759},"King F. W., 1978, Wildlife and America, 253",{},{"id":24,"text":1761,"url":24,"identifiers":1762},"Koh C. H., 1998, Asia report. Pages 233–240 in Crocodiles. Proceedings of the 14th working meeting of the Crocodile Specialist Group",{},{"id":24,"text":1764,"url":24,"identifiers":1765},"Luxmoore R., 1988, Significant trade in wildlife. A review of selected species in CITES Appendix II",{},{"id":24,"text":1767,"url":24,"identifiers":1768},"McIlhenny E. A., 1935, The alligator’s life history",{},{"id":24,"text":1770,"url":24,"identifiers":1771},"10.1017\u002FS003060530002891X",{"doi":1770},{"id":24,"text":1773,"url":24,"identifiers":1774},"Medem F., 1981, Los Crocodylia de Sur America. Volume I. Los Crocodylia de Colombia",{},{"id":24,"text":1776,"url":24,"identifiers":1777},"Messel H., 1991, Sustainable utilization: a program that conserves many crocodilians., Species, 16, 30",{},{"id":24,"text":1779,"url":24,"identifiers":1780},"Ross J. P., 1995, La conservación y manejo de caimanes y cocodrilos de América Latina, 19",{},{"id":24,"text":1782,"url":24,"identifiers":1783},"Ross P., 1997, Biological basis and application of sustainable use for the conservation of crocodilians. Pages 182–187 in Memorias de la 4ta. Reunion Regional del Grupo de Especialistas de Cocodrilos de America Latina y el Caribe",{},{"id":24,"text":1785,"url":24,"identifiers":1786},"Ross P. editor. 1998. Crocodiles. Status survey and conservation action plan. 2nd edition. Crocodile Specialist Group World Conservation Union Gland Switzerland.",{},{"id":24,"text":1788,"url":24,"identifiers":1789},"10.1016\u002F0006-3207(81)90033-1",{"doi":1788},{"id":24,"text":1791,"url":24,"identifiers":1792},"Takehara Y., 1998, Crocodile skin market in Japan. Pages 241–242 in Crocodiles. Proceedings of the 14th working meeting of the Crocodile Specialist Group",{},{"id":24,"text":1794,"url":24,"identifiers":1795},"Thorbjarnarson J. B. 1992. Crocodiles. An action plan for their conservation. H. Messel F. W. King and P. Ross editors. World Conservation Union Gland Switzerland.",{},{"id":24,"text":1797,"url":24,"identifiers":1798},"Thorbjarnarson J. B. and A. Velasco. 1998. Venezuela’s caiman harvest program. An historical perspective and analysis of its conservation benefits. Wildlife Conservation Society working paper 11. New York NY.",{},{"id":24,"text":1800,"url":24,"identifiers":1801},"Van Jaarsveldt K., 1992, Trade group report., Crocodile Specialist Group Newsletter, 11, 2",{},{"id":24,"text":1803,"url":24,"identifiers":1804},"Webb G. J. W., 1994, Crocodile management and research in the Northern Territory: 1992–1994. Pages 167–180 in Crocodiles. Proceedings of the 12th working meeting of the Crocodile Specialist Group",{},{"id":24,"text":1806,"url":24,"identifiers":1807},"Woodward A. R. D. N. David and R. L. Degner. 1994. The rise and fall of classic crocodilian skin prices: where do we go from here? Pages 577–592 in Crocodiles. Proceedings of the 2nd regional (Eastern Asia Oceania Australasia) meeting of the Crocodile Specialist Group. World Conservation Union Gland Switzerland.",{},{"id":24,"text":1809,"url":24,"identifiers":1810},"World Conservation Monitoring Centre, 1998, World trade in crocodilian skins, 1994–1996",{},{"id":24,"text":1812,"url":24,"identifiers":1813},"Youngprapakorn P., 1990, Hybrid CpsY",{},{"id":1815,"createTime":1816,"updateTime":1816,"relativeEntities":1817,"slug":1818,"properties":1819,"entityType":192,"verifyStatus":23,"verifyTime":1831,"verifyNote":1832,"syncStatus":23,"languages":1833,"translateLanguages":24,"viewCount":25,"primaryUrl":1834,"fullTextUrl":24,"authors":1835,"publicationType":295,"publisherRelationship":1916,"citationCount":1953,"citationInfo":1954,"publishDate":1960,"publishYear":1224,"citationAnalyzeStatus":23,"lastCitationAnalyze":24,"indexDatabases":24,"openAccess":24,"references":1961,"isForceReanalyzing":509},"825d4db6-78c4-4629-95e9-f71b7a37261e","2024-10-03T23:03:57.709+00:00",[],"Limiting-Depredation-by-African-Carnivores-the-Role-of-Livestock-Husbandry",{"mag":1820,"keywords":1822,"openalex":1823,"abstract":1825,"title":1827,"doi":1829},{"VOID":1821},"2140047032",{},{"VOID":1824},"W2140047032",{"EN":1826},"\u003Cjats:p>\u003Cjats:bold>Abstract: \u003C\u002Fjats:bold>  \u003Cjats:italic>Most large carnivore species are in global decline. Conflict with local people, particularly over depredation on livestock, is a major cause of this decline, affecting both nominally protected populations and those outside protected areas. For this reason, techniques that can resolve conflicts between large carnivores and livestock farmers may make important contributions to conservation. We monitored rates of livestock depredation by lions ( Panthera leo), leopards (Panthera pardus), cheetahs (Acinonyx jubatus), and spotted hyenas (Crocuta crocuta), and retributive killing of these species by farmers in livestock‐producing areas of Laikipia District, Kenya. Farmers killed more lions, leopards, and spotted hyenas where these predators killed more livestock. Livestock husbandry had a clear effect on rates of depredation and hence on the numbers of predators killed. Cattle, sheep, and goats experienced the lowest predation rates when attentively herded by day and enclosed in traditional corrals (bomas) by night. Construction of the boma, the presence of watchdogs, and high levels of human activity around the boma were all associated with lower losses to predators. Although most of this work was carried out on commercial ranches, local Maasai and Samburu pastoralists have practiced nearly identical forms of husbandry for generations. Our study shows that traditional, low‐tech husbandry approaches can make an important contribution to the conservation of large carnivores.\u003C\u002Fjats:italic> \u003C\u002Fjats:p>",{"EN":1828},"Limiting Depredation by African Carnivores: the Role of Livestock Husbandry",{"VOID":1830},"10.1111\u002Fj.1523-1739.2003.00061.x","2024-10-03T23:03:57.708+00:00","Author affiliation is blank",[196],"https:\u002F\u002Fconbio.onlinelibrary.wiley.com\u002Fdoi\u002F10.1111\u002Fj.1523-1739.2003.00061.x",[1836,1858,1869,1891],{"id":1837,"sortIndex":139,"researcher":24,"roles":1838,"affiliations":1839,"properties":1851},"820c0e46-5864-42b3-ad42-f17e09c1a435",[],[1840],{"id":1841,"sortIndex":25,"affiliation":1842,"properties":24},"e64b7867-d2d2-4b4f-8dcb-dec076500655",{"id":1843,"createTime":1844,"updateTime":1845,"relativeEntities":1846,"slug":1847,"properties":1848,"entityType":69,"verifyStatus":23,"verifyTime":24,"verifyNote":24,"syncStatus":23,"languages":24,"translateLanguages":24,"viewCount":25},"dbdc2577-36f5-4f03-b93c-e610668e8b6f","2024-01-13T08:46:29.535+00:00","2024-10-04T07:23:44.885+00:00",[],"Museum-of-Vertebrate-Zoology-University-of-California-Berkeley-CA-94720-U-S-A-",{"title":1849},{"VI":1850},"Museum of Vertebrate Zoology, University of California, Berkeley, CA 94720, U.S.A.",{"openalex":1852,"orcid":1854,"title":1856},{"VOID":1853},"A5074907911",{"VOID":1855},"https:\u002F\u002Forcid.org\u002F0000-0003-3091-6768",{"EN":1857},"Laurence Frank",{"id":1859,"sortIndex":138,"researcher":24,"roles":1860,"affiliations":1861,"properties":1862},"b5e70df3-d185-433a-906e-c7ce82d10601",[],[],{"openalex":1863,"orcid":1865,"title":1867},{"VOID":1864},"A5070834734",{"VOID":1866},"https:\u002F\u002Forcid.org\u002F0000-0003-2104-3133",{"EN":1868},"Roșie Woodroffe",{"id":1870,"sortIndex":136,"researcher":24,"roles":1871,"affiliations":1872,"properties":1884},"adf6b2bc-4115-44aa-a50a-c391db23d92f",[],[1873],{"id":1874,"sortIndex":25,"affiliation":1875,"properties":24},"c3d8f190-d217-44bc-864a-231cc2a1dd08",{"id":1876,"createTime":1877,"updateTime":1878,"relativeEntities":1879,"slug":1880,"properties":1881,"entityType":69,"verifyStatus":23,"verifyTime":24,"verifyNote":24,"syncStatus":23,"languages":24,"translateLanguages":24,"viewCount":25},"12cc4edc-ff99-47e2-a8ae-ccd8305a5fc2","2024-02-07T14:34:57.511+00:00","2024-10-03T23:03:57.724+00:00",[],"Department-of-Zoology-Kenyatta-University-Nairobi-Kenya",{"title":1882},{"VI":1883},"Department of Zoology, Kenyatta University, Nairobi, Kenya",{"openalex":1885,"orcid":1887,"title":1889},{"VOID":1886},"A5081003694",{"VOID":1888},"https:\u002F\u002Forcid.org\u002F0000-0002-4852-9363",{"EN":1890},"Nicholas Oguge",{"id":1892,"sortIndex":25,"researcher":24,"roles":1893,"affiliations":1894,"properties":1911},"42f35721-2980-4243-b31e-e5dec30d2c5b",[],[1895,1905],{"id":1896,"sortIndex":138,"affiliation":1897,"properties":24},"0e24da54-08c6-479a-aa6d-de13fca6f35e",{"id":1898,"createTime":1899,"updateTime":1899,"relativeEntities":1900,"slug":1901,"properties":1902,"entityType":69,"verifyStatus":23,"verifyTime":24,"verifyNote":24,"syncStatus":23,"languages":24,"translateLanguages":24,"viewCount":25},"461cb563-7058-465e-b5f7-5f71966a03da","2024-10-03T23:03:57.726+00:00",[],"Mpala-Research-Center-P-O-Box-555-Nanyuki-Kenya",{"title":1903},{"EN":1904},"Mpala Research Center, P.O. 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S. P.Arcese andM. K.Sam.2001.Human demography and reserve size predict wildlife extinction in West Africa.Proceedings of the Royal Society of London Series B268:2473–2478.",{"doi":1965},"10.1098\u002Frspb.2001.1815",{"id":24,"text":1967,"url":24,"identifiers":1968},"10.1017\u002FS0031182000075806",{"doi":1967},{"id":24,"text":1970,"url":24,"identifiers":1971},"Frank L. G., 1998, Development Alternatives",{},{"id":24,"text":1973,"url":24,"identifiers":1974},"Georgiadis N. andG.Ojwang'2001.Numbers and distributions of large herbivores in Laikipia Samburu and Isiolo Districts. Report. Laikipia Wildlife Forum Nanyuki Kenya .",{},{"id":24,"text":1976,"url":24,"identifiers":1977},"Ginsberg J. R., 1990, Foxes, wolves, jackals and dogs: an action plan for the conservation of canids",{},{"id":24,"text":1979,"url":24,"identifiers":1980},"10.1023\u002FA:1016680327755",{"doi":1979},{"id":24,"text":1982,"url":24,"identifiers":1983},"10.1046\u002Fj.1523-1739.2002.00559.x",{"doi":1982},{"id":24,"text":1985,"url":24,"identifiers":1986},"Hemson G.2001.Lion‐livestock conflict in the Makgadikgadi. Pages155–164inF.Monggae R.Mojaphoko T.Morule G.Tobedza D.McColaugh andP.Kaisara editors.National technical predator management and conservation workshop in Botswana. Department of Wildlife and National Parks Gaborone Botswana .",{},{"id":24,"text":1988,"url":24,"identifiers":1989},"Kruuk H., 1981, UNEP‐MAB integrated project in arid lands",{},{"id":24,"text":1991,"url":24,"identifiers":1992},"Linnell J. D. C., 1999, Large carnivores that kill livestock: do “problem individuals” really exist, Wildlife Society Bulletin, 27, 698",{},{"id":24,"text":1994,"url":24,"identifiers":1995},"Loveridge A. J., 2001, Conflicts with people",{},{"id":24,"text":1997,"url":24,"identifiers":1998},"Marker L., 1996, Cheetah survival on Namibian farmlands",{},{"id":24,"text":2000,"url":24,"identifiers":2001},"10.1046\u002Fj.1523-1739.1995.9020270.x",{"doi":2000},{"id":24,"text":2003,"url":24,"identifiers":2004},"Mills M. G. L. andH.Hofer.1998.Hyenas: status survey and conservation action plan. World Conservation Union Gland Switzerland .",{},{"id":24,"text":2006,"url":24,"identifiers":2007},"Nowell K. andP.Jackson.1996Wild cats: status survey and conservation action plan. World Conservation Union Gland Switzerland .",{},{"id":24,"text":2009,"url":24,"identifiers":2010},"Rhodes C. J. R. P. D.Atkinson R. M.Anderson andD. W.Macdonald.1998.Rabies in Zimbabwe: reservoir dogs and the implications for disease control.Philosophical Transactions of the Royal Society of London Series B353:999–1010.",{"doi":2011},"10.1098\u002Frstb.1998.0263",{"id":24,"text":2013,"url":24,"identifiers":2014},"10.1038\u002F379441a0",{"doi":2013},{"id":24,"text":2016,"url":24,"identifiers":2017},"Stander P. E., 1991, Demography of lions in Etosha National Park, 18, 1",{},{"id":24,"text":2019,"url":24,"identifiers":2020},"10.1046\u002Fj.1523-1739.2000.99013.x",{"doi":2019},{"id":24,"text":2022,"url":24,"identifiers":2023},"10.2307\u002F1307647",{"doi":2022},{"id":24,"text":2025,"url":24,"identifiers":2026},"Woodroffe R., 2001, Carnivore conservation, 61",{},{"id":24,"text":2028,"url":24,"identifiers":2029},"Woodroffe R.2002.African wild dogs and African people: conservation through coexistence. 2nd annual report. Samburu‐Laikipia Wild Dog Project University of California . Davis .",{},{"id":24,"text":2031,"url":24,"identifiers":2032},"10.1126\u002Fscience.280.5372.2126",{"doi":2031},{"id":24,"text":2034,"url":24,"identifiers":2035},"World Conservation Union (IUCN).2002.The IUCN red list of threatened species. IUCN Gland Switzerland . Available fromhttp:\u002F\u002Fwww.redlist.org(accessed January 2003).",{},{"id":2037,"createTime":2038,"updateTime":2038,"relativeEntities":2039,"slug":2040,"properties":2041,"entityType":192,"verifyStatus":193,"verifyTime":2038,"verifyNote":194,"syncStatus":23,"languages":2053,"translateLanguages":24,"viewCount":25,"primaryUrl":2054,"fullTextUrl":24,"authors":2055,"publicationType":295,"publisherRelationship":2098,"citationCount":2135,"citationInfo":2136,"publishDate":2139,"publishYear":2140,"citationAnalyzeStatus":23,"lastCitationAnalyze":24,"indexDatabases":24,"openAccess":24,"references":2141,"isForceReanalyzing":509},"a7ac4b17-4ed1-4a05-b45b-21e924708d0e","2024-10-13T22:46:16.611+00:00",[],"Fishery-Recovery-in-a-Coral-reef-Marine-Park-and-Its-Effect-on-the-Adjacent-Fishery",{"mag":2042,"keywords":2044,"openalex":2045,"abstract":2047,"title":2049,"doi":2051},{"VOID":2043},"2102422747",{},{"VOID":2046},"W2102422747",{"EN":2048},"\u003Cjats:p>Numbers offish and their wet weights were estimated in Kenyan coral‐reef lagoons on seven reefs over 6 years. Two sites were protected from fishing for over 20 years, whereas the other five sites were heavily fished in recent years. A heavily fished site was converted into a marine park (Mombasa Marine National Park, approximately 10 km\u003Cjats:sup>2\u003C\u002Fjats:sup> no fishing allowed), and the number of fishers allowed was slowly decreased between August 1991 and August 1992. The area adjacent to the park was converted into a marine reserve (only fishing traps, lines, and gill nets allowed) that provided fishing grounds for fishers excluded from the park. Data from a fish‐landing site adjacent to the newly created marine park were collected for 3 years and analyzed to determine the effect of the park’s creation on fish catches. Results suggest that fishing in the reserve reduced fish wet weight by about a factor of 10 and reduced fish numbers and species richness by a factor of two. Both field studies and landing data suggest harvesting at a bionomic equilibrium. For example, approximately 65% of the landing site’s fishing grounds were protected with the creation of the park, and 65% of the fishers quit the studied landing, leaving nearly the same density of fishers in the remaining area (∼ 12 fishers\u002Fkm\u003Cjats:sup>2\u003C\u002Fjats:sup>). Further, fishers using pull seines were excluded from the reserve, and their numbers were replaced by fishers using other gear (mostly basket traps). Although the overall catch per unit effort increased by about 110% after the park’s creation, the total fish landed decreased by 35% and the catch per unit effort decreased toward the end of the study period despite increasing fish abundance in the park. Although establishment of small parks elsewhere have increased the total catch, the large park we studied did not; one reason may have been the lower ratio of edge to park area of the large park. Alternatively, the park’s edge may have provided a good fishing area, so fishing effort may have been highest along the park’s edge. Consequently, a barrier may have been created that restricted fish dispersal to most of the reserve. Therefore, the area that had an increased catch was small (< 1 to 2 km from the edge) and could not compensate for the lost fishing area. Most fish species within the park showed recovery after fisher exclusion. Total fish wet weights 3 years after the fishers’ exclusion were 25% below the older marine parks. Poor recovery of the herbivoroas parrot and surgeonfish can account for much of this shortfall. Competition for resources with sea urchins appear to be slowing recovery of these two groups. A study site 2.5 km from the park’s southern boundary, in the reserve section of the protected area, showed no changes in fish abundance over the study period, despite changing gear regulations.\u003C\u002Fjats:p>",{"EN":2050},"Fishery Recovery in a Coral‐reef Marine Park and Its Effect on the Adjacent Fishery",{"VOID":2052},"10.1046\u002Fj.1523-1739.1996.10041187.x",[196],"https:\u002F\u002Fconbio.onlinelibrary.wiley.com\u002Fdoi\u002F10.1046\u002Fj.1523-1739.1996.10041187.x",[2056,2077],{"id":2057,"sortIndex":138,"researcher":24,"roles":2058,"affiliations":2059,"properties":2070},"dc1c2663-de30-4aa3-b718-06100e855cdd",[],[2060],{"id":2061,"sortIndex":25,"affiliation":2062,"properties":24},"24bf85cd-4fa1-4ccd-b828-bb908773b29f",{"id":2063,"createTime":2064,"updateTime":2064,"relativeEntities":2065,"slug":2066,"properties":2067,"entityType":69,"verifyStatus":23,"verifyTime":24,"verifyNote":24,"syncStatus":23,"languages":24,"translateLanguages":24,"viewCount":25},"21ba0a54-fb42-41d7-ac0e-2cdbeb8f63fa","2024-10-13T22:46:16.640+00:00",[],"Fisheries-Department-Moi-University-P-O-Box-1125-Eldoret-Kenya",{"title":2068},{"EN":2069},"Fisheries Department, Moi University, P.O. 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Surprisingly, although it is known that noise exposure strongly influences health in humans, studies on wildlife remain scarce. In order to gain insight into the consequences of traffic noise exposure, we experimentally manipulated traffic noise exposure as well as the endocrine status of animals to investigate physiological and phenotypic consequences of noise pollution in an anuran species. We showed that noise exposure increased stress hormone level and induced an immunosuppressive effect. In addition, both traffic noise exposure and stress hormone application negatively impacted \u003Cjats:italic>H. arborea\u003C\u002Fjats:italic> vocal sac coloration. Moreover, our results suggest profound changes in sexual selection processes because the best quality males with initial attractive vocal sac coloration were the most impacted by noise. Hence, our study suggests that the recent increases in anthropogenic noise worldwide might affect a broader range of animal species than previously thought, because of alteration of visual signals and immunity. Generalizing these results to other taxa is crucial for the conservation of biodiversity in an increasingly noisy world.\u003C\u002Fjats:p>",{"EN":2156},"Effects of traffic noise on tree frog stress levels, immunity, and color 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