scholarly journals Biodiversity

EDIS ◽  
1969 ◽  
Vol 2003 (4) ◽  
Author(s):  
Center For Natural Resources

Biodiversity or biological diversity is a relatively new term in ecology. It became popular in the 1980s and is not yet properly understood by all non-ecologists. Biodiversity refers to the variety and richness among living organisms and the ecological systems and processes of which they are a part. There are three levels of biodiversity: habitat or ecosystem diversity, genetic diversity, and species diversity. This publication was produced by the Center for Natural Resources at the University of Florida. CNR 4 is part of a Program Summary Series. First published: September 2000. Minor revision: March 2003.  https://edis.ifas.ufl.edu/cr004

EDIS ◽  
1969 ◽  
Vol 2003 (4) ◽  
Author(s):  
Center For Natural Resources

This publication was produced by the Center for Natural Resources at the University of Florida. CNR 15 is part of a Program Summary Series. First published: 3/26/2002. Minor revision: March 2003.


EDIS ◽  
1969 ◽  
Vol 2003 (4) ◽  
Author(s):  
Center For Natural Resources

This publication was produced by the Center for Natural Resources at the University of Florida. CNR 6 is part of a Program Summary Series. First published: September 2000. Minor revision: March 2003. https://edis.ifas.ufl.edu/cr006


EDIS ◽  
1969 ◽  
Vol 2003 (4) ◽  
Author(s):  
Wendy-Lin Bartels ◽  
Marshall Breeze ◽  
Nancy Peterson

This publication was produced by the Center for Natural Resources at the University of Florida. CNR 14 is part of a Program Summary Series. First published: 11/25/2002, Minor revision: March 2003.   


EDIS ◽  
1969 ◽  
Vol 2003 (4) ◽  
Author(s):  
Center For Natural Resources

Though the concept of nature-based tourism is not new, the term "ecotourism" is. Once referred to as "green travel", ecotourism is defined as a "recreational and educational experience that encourages greater understanding of the natural and cultural resources of an area". This publication was produced by the Center for Natural Resources at the University of Florida. CNR 7 is part of a Program Summary Series. First published: September 2000. Minor revision: March 2003.


EDIS ◽  
1969 ◽  
Vol 2003 (4) ◽  
Author(s):  
Center For Natural Resources

Florida's natural ecosystems are increasingly coming under attack by invading exotic species which displace native species, thereby degrading the diversity of floral and faunal resources. This publication was produced by the Center for Natural Resources at the University of Florida. CNR 8 is part of a Program Summary Series. Firstpublished: September 2000. Minor revision: March 2003.  


Author(s):  
Aurel MAXIM ◽  
Mignon ŞANDOR ◽  
Lucia MIHALESCU ◽  
Ovidiu MAXIM ◽  
Oana MARE ROŞCA

During the second part of the twentieth century the cultivated plants have been faced with genetic erosion, because of the expandinding industrial farming systems. The sustainable agriculture can not exist without a rich genetic diversity. After the United Nations Conference from Rio de Janeiro (1992), when the Convention on Biological Diversity was adopted, a series of acts and european references that protect agrobiodiversity had emerged. Between 2007 and 2010, at the University of Agricultural Sciences and Veterinary Medicine a program which aims to identify and conserve local vegetable varieties was conducted. Out of 290 cultivars, 171 (58.9%) were genuine local varieties. There were collected 12 cucumber cultivars from the following counties: Salaj (7), Cluj (3), Bistrita-Nasaud (1) and Satu-Mare (1). The morphologic caractheristics proved that all this 12 cultivars were authentic and valuable local varieties. The local varieties were agronomical, biological and biochemical characterized, both in field and laboratory. The seeds achieved from those 12 local varieties were preserved in the Suceava Gene Bank, from where stakeholders (farmers, agronomists, researchers) can obtain seeds.


Author(s):  
Sergei Volis ◽  
Salit Kark

The study of biodiversity has received wide attention in recent decades. Biodiversity has been defined in various ways (Gaston and Spicer, 1998, Purvis and Hector 2000, and chapters in this volume). Discussion regarding its definitions is dynamic, with shifts between the more traditional emphasis on community structure to emphasis on the higher ecosystem level or the lower population levels (e.g., chapters in this volume, Poiani et al. 2000). One of the definitions, proposed in the United Nations Convention on Biological Diversity held in Rio de Janeiro (1992) is “the diversity within species, between species and of ecosystems.” The within-species component of diversity is further defined as “the frequency and diversity of different genes and/or genomes . . .” (IUCN 1993) as estimated by the genetic and morphological diversity within species. While research and conservation efforts in the past century have focused mainly on the community level, they have recently been extended to include the within-species (Hanski 1989) and the ecosystem levels. The component comprising within-species genetic and morphological diversity is increasingly emphasized as an important element of biodiversity (UN Convention 1992). Recent studies suggest that patterns of genetic diversity significantly influence the viability and persistence of local populations (Frankham 1996, Lacy 1997, Riddle 1996, Vrijenhoek et al. 1985). Revealing geographical patterns of genetic diversity is highly relevant to conservation biology and especially to explicit decision-making procedures allowing systematic rather than opportunistic selection of populations and areas for in situ protection (Pressey et al. 1993). Therefore, studying spatial patterns in within-species diversity may be vital in defining and prioritizing conservation efforts (Brooks et al. 1992). Local populations of a species often differ in the ecological conditions experienced by their members (Brown 1984, Gaston 1990, Lawton et al. 1994). These factors potentially affect population characteristics, structure, and within-population genetic and morphological diversity (Brussard 1984, Lawton 1995, Parsons 1991). The spatial location of a population within a species range may be related to its patterns of diversity (Lesica and Allendorf 1995). Thus, detecting within-species diversity patterns across distributional ranges is important for our understanding of ecological and evolutionary (e.g., speciation) processes (Smith et al. 1997), and for the determination of conservation priorities (Kark 1999).


Author(s):  
James R. Gosz ◽  
Avi Perevolotsky

Biodiversity is regarded as a scientific concept, a measurable entity, as well as a social–political construct (Gaston 1996, Wilson 1993). The aim of this volume is to develop the scientific basis for biodiversity studies, and for the integration of the concept into management practice. We emphasize biodiversity as a powerful, integrative concept—one that requires careful articulation and further conceptualization before application. Diversity is a concept that refers to the range of variation or differences among a set of entities; biological diversity then refers to variety within the living world. An example of biological diversity is “species diversity,” which is commonly used to describe the number, variety, and variability of the assemblage of living organisms in a defined area or space. However, biodiversity as a concept has evolved. Current definitions expand the biological diversity concept to emphasize the multiple dimensions and ecological realms in which biodiversity can be observed. These definitions stress that biodiversity encompasses at least four kinds of diversities: genetic diversity, species or taxonomic diversity, ecosystem diversity, and landscape diversity (McAllister 1991; Solbrig 1993, Stuart and Adams 1991; Groombridge 1992; Heywood 1994, Wilson 1993). Two main problems emerge as a consequence of the broad scope that the biodiversity concept has taken at present. Cast as questions, the problems are: (1) How do we incorporate processes (e.g., foraging, energy and nutrient flows, patch dynamics) into a concept that is based on seemingly static entities (i.e., individual organisms, species, habitat types, patch types)? (2) How do we integrate across ecological subdisciplines (e.g., ecosystem, population, landscape ecology) and across scales that are involved in biodiversity studies? The two problems are not mutually exclusive. Indeed, they are inseparable and complementary. For example, to determine how species diversity and ecosystem processes interact requires incorporation of entities and processes, as well as integration of community and ecosystem ecology. The focus on both entities and processes reflects the long-recognized dichotomy of structure and function in biology and ecology. Clearly, both structure and function must be integrated in order to successfully solve ecological questions. Dealing with biodiversity brings this needed integration into focus.


2014 ◽  
Vol 10 (5) ◽  
pp. 1399-1417 ◽  
Author(s):  
Dario J. Chavez ◽  
Thomas G. Beckman ◽  
Dennis J. Werner ◽  
José X. Chaparro

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