Implications for Biogeographical Theory and the Conservation of Nature
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
Rethinking Easter Island's Ecological Catastrophe
ARTICLE IN PRESS + MODEL Journal of Archaeological Science xx (2006) 1e18 http://www.elsevier.com/locate/jas Rethinking Easter Island’s ecological catastrophe Terry L. Hunt Department of Anthropology, University of Hawai’i-Manoa, 2424 Maile Way Honolulu, HI 96822, USA Received 25 June 2006; received in revised form 1 October 2006; accepted 2 October 2006 Abstract Rapa Nui (Easter Island) has become a paragon for prehistoric human induced ecological catastrophe and cultural collapse. A popular nar- rative recounts an obsession for monumental statuary that led to the island’s ecological devastation and the collapse of the ancient civilization. Scholars offer this story as a parable of today’s global environmental problems. In this paper, I review new and emerging Rapa Nui evidence, compare ecological and recently acquired palaeo-environmental data from the Hawaiian and other Pacific Islands, and offer some perspectives for the island’s prehistoric ecological transformation and its consequences. The evidence points to a complex historical ecology for the island; one best explained by a synergy of impacts, particularly the devastating effects of introduced rats (Rattus exulans). This perspective questions the simplistic notion of reckless over-exploitation by prehistoric Polynesians and points to the need for additional research. Ó 2006 Elsevier Ltd. All rights reserved. Keywords: Easter Island; Rapa Nui; Deforestation; Ecocide; Collapse; Rats; Rattus exulans; Invasive species ‘‘It ain’t what you don’t know that gets you into trouble. It’s archaeological records also reveals a more complex historical what you know for sure that just ain’t so.’’ Mark Twain ecology for the island; one best explained by a synergy of impacts, rather than simply the reckless over-exploitation by Easter Island (Rapa Nui) has become the paragon for pre- prehistoric Polynesians. -
Channel Islands National Park National Park Service Channel Islands California U.S
The Channel Islands from the Ice Ages to Today Nowhere Else On Earth Living Alone Lower ocean levels Kinship of Islands and Sea A islands, and Gabrieliño/Tongva in the 1800s fur traders searched Protection and Restoration Something draws us to the sea and its islands. during the ice ages narrowed the powerful bond between the land settled the southern islands. the coves for sea otters, seals, and Pro tection for the islands began distance across the Santa Barbara and sea controls everything here, Prosperous and industrious, the sea lions, nearly hunting them to in 1938 when Anacapa and Santa Maybe it is the thrill of traveling over water to an Channel and exposed some of the from where plants grow to when tribes joined in a trading net work extinction. Barbara became Channel Islands unfamiliar land or the yearning for tranquility—to seafloor. The land offshore, easier seals breed. Together, water cur that extended up and down the National Monu ment. In 1980 Con walk on a deserted beach with birds, salty breezes, to reach then, allowed some spe rents, winds, and weather create coast and inland. The island Chu By 1822 most Chu mash had been gress designated San Miguel, cies to venture into this new terri an eco system that supports a rich mash used purple olivella shells to moved to mainland missions. Fish Santa Rosa, Santa Cruz, Ana capa, and the rhyth mic wash of waves as our compan- tory. Mammoths swam the chan diversity of life. Among the 2,000 manufacture the main currency ing camps and ranching had be Santa Barbara, and the submerged ions. -
Towards a Glacial‐Sensitive Model of Island Biogeography
Global Ecology and Biogeography, (Global Ecol. Biogeogr.) (2016)(2015) 25, 817–830 SPECIAL Towards a glacial-sensitive model of ISSUE island biogeography José María Fernández-Palacios1,2*, Kenneth F. Rijsdijk3, Sietze J. Norder3, Rüdiger Otto1, Lea de Nascimento1,2, Silvia Fernández-Lugo1, Even Tjørve4 and Robert J. Whittaker2,5 1Island Ecology and Biogeography Research ABSTRACT Group. Instituto Universitario de Although the role that Pleistocene glacial cycles have played in shaping the present Enfermedades Tropicales y Salud Pública de Canarias (IUETSPC), Universidad de La biota of oceanic islands world-wide has long been recognized, their geographical, Laguna, Tenerife, Canary Islands 38206, biogeographical and ecological implications have not yet been fully incorporated Spain, 2Conservation Biogeography and within existing biogeographical models. Here we summarize the different types of Macroecology Group, School of Geography and impacts that glacial cycles may have had on oceanic islands, including cyclic the Environment, South Parks Road, Oxford changes in climate, shifts in marine currents and wind regimes and, especially, OX1 3QY, UK, 3Computation GeoEcology cycles of sea level change. The latter have affected geographical parameters such as Group, Institute for Biodiversity and Ecosystem island area, isolation and elevation. They have also influenced the configurations of Dynamics & Institute for Interdisciplinary archipelagos via island fusion and fission, and cycles of seamount emergence and Studies, University of Amsterdam, Sciencepark submergence. We hypothesize that these sea level cycles have had significant 904, 1098 XH Amsterdam, The Netherlands, impacts on the biogeographical processes shaping oceanic island biotas, influencing 4Faculty of Economics and Organisation the rates and patterns of immigration and extinction and hence species richness. -
On the Nature and Nomenclature of Ecology's Fourth Level
Biol. Rev. (2008), 83, pp. 71–78. 71 doi:10.1111/j.1469-185X.2007.00032.x Levels of organization in biology: on the nature and nomenclature of ecology’s fourth level William Z. Lidicker, Jr.* Museum of Vertebrate Zoology, University of California, Berkeley, CA 94720, USA (Received 30 May 2007; revised 15 October 2007; accepted 22 October 2007) ABSTRACT Viewing the universe as being composed of hierarchically arranged systems is widely accepted as a useful model of reality. In ecology, three levels of organization are generally recognized: organisms, populations, and communities (biocoenoses). For half a century increasing numbers of ecologists have concluded that recognition of a fourth level would facilitate increased understanding of ecological phenomena. Sometimes the word ‘‘ecosystem’’ is used for this level, but this is arguably inappropriate. Since 1986, I and others have argued that the term ‘‘landscape’’ would be a suitable term for a level of organization defined as an ecological system containing more than one community type. However, ‘‘landscape’’ and ‘‘landscape level’’ continue to be used extensively by ecologists in the popular sense of a large expanse of space. I therefore now propose that the term ‘‘ecoscape’’ be used instead for this fourth level of organization. A clearly defined fourth level for ecology would focus attention on the emergent properties of this level, and maintain the spatial and temporal scale-free nature inherent in this hierarchy of organizational levels for living entities. Key words: ecoscape, landscape, ecosystem, ecological system, spatial ecology, hierarchy theory, community ecology, emergent properties, holism, spatial and temporal scales. CONTENTS I. Introduction ......................................................................................................................................... -
Biodiversity and Ecological Potential of Plum Island, New York
Biodiversity and ecological potential of Plum Island, New York New York Natural Heritage Program i New York Natural Heritage Program The New York Natural Heritage Program The NY Natural Heritage Program is a partnership NY Natural Heritage has developed two notable between the NYS Department of Environmental online resources: Conservation Guides include the Conservation (NYS DEC) and The Nature Conservancy. biology, identification, habitat, and management of many Our mission is to facilitate conservation of rare animals, of New York’s rare species and natural community rare plants, and significant ecosystems. We accomplish this types; and NY Nature Explorer lists species and mission by combining thorough field inventories, scientific communities in a specified area of interest. analyses, expert interpretation, and the most comprehensive NY Natural Heritage also houses iMapInvasives, an database on New York's distinctive biodiversity to deliver online tool for invasive species reporting and data the highest quality information for natural resource management. planning, protection, and management. In 1990, NY Natural Heritage published Ecological NY Natural Heritage was established in 1985 and is a Communities of New York State, an all inclusive contract unit housed within NYS DEC’s Division of classification of natural and human-influenced Fish, Wildlife & Marine Resources. The program is communities. From 40,000-acre beech-maple mesic staffed by more than 25 scientists and specialists with forests to 40-acre maritime beech forests, sea-level salt expertise in ecology, zoology, botany, information marshes to alpine meadows, our classification quickly management, and geographic information systems. became the primary source for natural community NY Natural Heritage maintains New York’s most classification in New York and a fundamental reference comprehensive database on the status and location of for natural community classifications in the northeastern rare species and natural communities. -
Ecosystem Ecology Living Organisms and Their Non Living (Abiotic) Environment Are Interrelated and Interact with Each Other
1 | P a g e Ecosystem Ecology Living organisms and their non living (abiotic) environment are interrelated and interact with each other. The term ‘ecosystem’ was proposed by A. G. Tansley and it was defined as the system resulting from the integration of all living and non living factors of the environment. Some parallel terms such as biocoenosis, microcosm, geobiocoenosis, holecoen, biosystem, bioenert body and ecosom were used for each ecological systems. However, the term ‘ecosystem’ is most preferred, where ‘eco’ stands for the environment, and ‘system’ stands for an interacting, interdependent complex. Any unit that includes all the organisms, i.e. communities, in a given area, interacts with the physical environment so that a flow of energy leads to a clearly defined trophic structure, biotic diversity and material cycle within the system, is known as an ecological system or ecosystem. It is usually an open system with regular but variable influx and loss of materials and energy. It is a basic functional unit with unlimited boundaries. Types of ecosystems The ecosystems can be broadly divided into the following two types; 1. Natural ecosystems 2. Artificial (man cultured ecosystems Natural ecosystems The ecosystems which are self-operating under natural conditions with any interference by man, are known as natural ecosystems. These ecosystems may be classified as follows: 1. Terrestrial ecosystems, e.g. Forests, grasslands and deserts 2. Aquatic ecosystems, which may be further classified as i) Freshwater: ecosystem, which in turn is divided into lentic (running water like streams, springs, rivers, etc.) and lentic (standing water like lakes, bonds, pools, swamps, ditches, etc.) ii) Marine ecosystem, e.g. -
Structure of Soil Biocoenosis and Biodiversity in Olive Orchards of Three Eastern Mediterranean Islands
ENTOMOLOGIA HELLENICA 23 (2014): 1-9 Structure of soil biocoenosis and biodiversity in olive orchards of three eastern Mediterranean islands Z. LIANTRAKI, I. TZOKAS AND D. KOLLAROS* School of Agricultural Technology, ΤΕΙ Crete, Stavromenos PC 71004, Herakleion, Crete, Greece ABSTRACT In this work the structure of soil arthropods’ biocoenosis was compared among 11 olive orchards from six localities of Crete (three of the localities from Messara’s valley, including two olive orchards each one, plus three localities near to Herakleion city) and other two ones each from the island of Kos and Cyprus. Pitfall traps were used and totally 35 taxa were captured. The order Coleoptera and the family Formicidae were the two main taxa at the 8 of the 11 olive orchards. Statistically significant differences in biodiversity were recorded among the orchards separating them in three groups, the first group included Messara’s olive orchards, the second the olive orchards of the rest of the Crete and the third group the olive groves of the other two islands. Messara’s group had higher biodiversity than the third group. By studying the similarities of biological communities, some pairs of Messara’s olive groves, have the highest ones. Among the 15 highest values, the 14 belonged to pairs between Messara’s olive orchards. Generally, biocoenosis in all 11 olive orchards of the three different islands follows a similar pattern, despite of differences in cultural practices and changes of climatic factors from a year to another. KEY WORDS: Biodiversity, biological communities, olive orchards, pitfall traps. Introduction order, such as Coleoptera in Spain (Cotes et al. -
Integrated Island Ecosystem Ecology in Hawaii
Technical Report No. 54 INTEGRATED ISLAND ECOSYSTEM ECOLOGY IN HAWAII INTRODUCTORY SURVEY Part I of Proposed Synthesis Volume for US/tBP Series Dieter Mueller-Dombois Department of Botany University of Hawaii Honolulu, Hawaii 96822 ISLAND ECOSYSTEMS IRP u. s. International Biological Program February 1975 Preface This is the draft manuscript of Part I of our synthesis volume. It is reproduced only for distribution within our group so that each Hawaii IBP participant will have an idea of what we are putting down before our volume -~, appears in print. We intend to do the same with the other parts as they come out. For Chapter 3 I drew heavily on our original IBP proposal. This chapter reflects the efforts of several individuals, including A.J. Berger, Sheila Conant, Allison Kay, C.H. Lamoureux, J.L. Gressitt, F.R. Fosberg, F.J. Radovsky, and others. But also the ideas put down in the other introductory chapters reflect the thinking that developed through our activity as a research team. Authorship for sections in the synthesis volume, therefore, must be viewed more as responsibilities assigned to us as writers and editors rather than (in the traditional sense) as authorship of a piece of original research. This applies to all remaining synthesis parts, chapters, and sections. The manuscript may still be subjected to several editorial changes before final printing. I would appreciate comments on the manuscript. Please transmit them to me. D. Mueller-Dombois January 1975 - i - ABSTRACT This report is a draft manuscript of Part I (Introductory Survey) of the synthesis volume of the US/IBP Island Ecosystems Stability and Evolution Subprogram. -
Glossary of Landscape and Vegetation Ecology for Alaska
U. S. Department of the Interior BLM-Alaska Technical Report to Bureau of Land Management BLM/AK/TR-84/1 O December' 1984 reprinted October.·2001 Alaska State Office 222 West 7th Avenue, #13 Anchorage, Alaska 99513 Glossary of Landscape and Vegetation Ecology for Alaska Herman W. Gabriel and Stephen S. Talbot The Authors HERMAN w. GABRIEL is an ecologist with the USDI Bureau of Land Management, Alaska State Office in Anchorage, Alaskao He holds a B.S. degree from Virginia Polytechnic Institute and a Ph.D from the University of Montanao From 1956 to 1961 he was a forest inventory specialist with the USDA Forest Service, Intermountain Regiono In 1966-67 he served as an inventory expert with UN-FAO in Ecuador. Dra Gabriel moved to Alaska in 1971 where his interest in the description and classification of vegetation has continued. STEPHEN Sa TALBOT was, when work began on this glossary, an ecologist with the USDI Bureau of Land Management, Alaska State Office. He holds a B.A. degree from Bates College, an M.Ao from the University of Massachusetts, and a Ph.D from the University of Alberta. His experience with northern vegetation includes three years as a research scientist with the Canadian Forestry Service in the Northwest Territories before moving to Alaska in 1978 as a botanist with the U.S. Army Corps of Engineers. or. Talbot is now a general biologist with the USDI Fish and Wildlife Service, Refuge Division, Anchorage, where he is conducting baseline studies of the vegetation of national wildlife refuges. ' . Glossary of Landscape and Vegetation Ecology for Alaska Herman W. -
Biological Control and Eradication of Feral Honey Bee Colonies on Santa Cruz Island, California: a Summary
Pages 327–335 in Damiani, C.C. and D.K. Garcelon (eds.). 2009. Proceedings of 327 the 7th California Islands Symposium. Institute for Wildlife Studies, Arcata, CA. BIOLOGICAL CONTROL AND ERADICATION OF FERAL HONEY BEE COLONIES ON SANTA CRUZ ISLAND, CALIFORNIA: A SUMMARY ADRIAN M. WENNER,1 ROBBIN W. THORP,2 AND JOHN F. BARTHELL3 1Department of Ecology, Evolution, and Marine Biology, University of California, Santa Barbara, CA 93106; [email protected] 2Department of Entomology, University of California, Davis, CA 95616 3Department of Biology, University of Central Oklahoma, Edmond, OK 73034 Abstract—After 1880, feral colonies of European honey bees (Apis mellifera) spread over all of Santa Cruz Island, though never invading any of the other northern Channel Islands. In line with other exotic animal removal programs (e.g., cattle, sheep, pigs), we outlined a program in October 1987 to eradicate all honey bee colonies on that island. That project evolved through four phases: 1) mapping and eradication of many colonies on the eastern half of the island (1988–1993), 2) introduction of a parasitic mite as a biological control (1994–1998), 3) monitoring residual honey bee activity (1999–2004), and 4) continued monitoring and certification of honey bee absence (2005–2008). We located the last known feral colony at the top of the Matanza grade on August 6, 2002 and found that same colony dead on March 31, 2003. The number of target foraging sites visited by honey bees declined steadily through the years, with the last visitors seen on rosemary plants at the ranch headquarters in August of 2004. -
Colonization, Speciation, and Conservation
30 Oct 2001 16:31 AR AR147-20.tex AR147-20.SGM ARv2(2001/05/10) P1: GJC Annu. Rev. Entomol. 2002. 47:595–632 Copyright c 2002 by Annual Reviews. All rights reserved ARTHROPODS ON ISLANDS: Colonization, Speciation, and Conservation Rosemary G. Gillespie and George K. Roderick Environmental Science, Policy, and Management, Division of Insect Biology, University of California, Berkeley, California 94720-3112; e-mail: [email protected]; [email protected] Key Words adaptive radiation, fragments, oceanic, endemism, disharmony, isolation ■ Abstract Islands have traditionally been considered to be any relatively small body of land completely surrounded by water. However, their primary biological char- acteristic, an extended period of isolation from a source of colonists, is common also to many situations on continents. Accordingly, theories and predictions developed for true islands have been applied to a huge array of systems, from rock pools, to single tree species in forests, to oceanic islands. Here, we examine the literature on islands in the broadest sense (i.e., whether surrounded by water or any other uninhabitable matrix) as it pertains to terrestrial arthropods. We categorize islands according to the features they share. The primary distinction between different island systems is “darwinian” islands (formed de novo) and “fragment” islands. In the former, the islands have never been in contact with the source of colonists and have abundant “empty” ecological niche space. On these islands, species numbers will initially increase through immigration, the rate depending on the degree of isolation. If isolation persists, over time species formation will result in “neo-endemics.” When isolation is extreme, the ecological space will gradually be filled through speciation (rather than immigration) and adaptive radiation of neo-endemics. -
Ecosystems Ecosystems
Presentation Ecosystems Ecosystems What is an ecosystem? An ecosystem includes all of the living and non-living things in a particular place. An ecosystem is made up of two parts, the biotope and the biocoenosis. Ecosystems biotope biocoenosis It includes all of the non-living It includes all the living things in things in an ecosystem. an ecosystem. Ecosystems What kind of relationships are there in an ecosystem? Intraspecific relationship: Interspecific relationship: exist between individual exist between individual members of the same species members of different species. Trophic relationships What are trophic relationships? Trophic relationships exist between the organisms that eat and the organisms that are eaten. A food chain shows the trophic relationships between organisms that live in the same ecosystem. A food web shows all the different food chains in an ecosystem. Trophic relationships How do we classify living things according to their trophic relationships? Plants are producers: they make their own food. Caterpillar are herbivores. They are primary consumers Praying mantis are carnivores. They are secondary consumers. Owls are carnivore. They are tertiary consumers, they feed on secondary consumers. Fungi and bacteria are decomposers: they break down the remains of dead organisms. The classification of ecosystems How do we classify ecosystems? A natural ecosystem is an ecosystem where no human activity has altered the biotope. Natural ecosystems can be classified into: 1. Terrestrial ecosystems 2. Prairie or savannah ecosystems 3. Forest and woodlands ecosystems 4. Tropical rainforest ecosystem 5. Aquatic ecosystems The classification of ecosystems How do we classify ecosystems? Artificial ecosystems include cities, towns, villages and artificial aquatic ecosystems, such as reservoirs or garden An artificial ecosystem is an ponds.