BIO-DIVERSITY: MEASUREMENT OF BIOLOGICAL DIVERSITY
BIO-DIVERSITY: MEASUREMENT OF BIOLOGICAL DIVERSITY
Scientists from different disciplines are of different opinion regarding the methods of measurement of biodiversity.
Systematics, a fundamental discipline of bio-divefsity, provides the basic frame work for the whole of biology. The main task of systematics is to document and understand the extent and significance of biological diversity. A number of activities including classification, identification and Nomericla-ture often grouped as Taxonomy which forms four basic functions :
i. Differentiation (Recognition of taxa)ii. Identification (Universal diagnosis of taxa)iii. Symbolization (Application of universal names)iv. Comparison (Relative relationship of the taxa)
Individuals and characters are the most basic unit of biological classification on the basis of features hold in common (attributes or characters) individual can be grouped together into a large number of different classes, categories like genera, families and orders and so on in artificial natural or phylogenetic classification depending upon the characters on which it is based. On the basis of the shared and unshared attributes between taxa, a number of taxonomic diversity indices for example, root-weight, higher taxon richness and taxonomic dispersion have now been developed.
Diversity can also be expressed as percentages. A site with viable population of all species in a group would have diversity score of 100% while a site without any species of the group in question would score zero. Such assessment allows us to compare all sites with each other and rank them individually from highest to lowest diversity.
Ecologists measure diversity either by estimating species richness (number of species) in an area or by one or more indexes combining species richness and relative abundance within an area. Application of such methods for measuring biodiversity are limited.i) The species richness measures which is based onsamples (a complete cataloguing of all species in aparticular taxonomic group) is of limited interest, be-cause.Species richness take no account of the differences between species in relation to their place in the hierarchy.When the biological diversity of a very small area is compared with longer area in a global context.ii) Relative abundance is not a fixed property of speciesvarying widely from time to time and place to place.iii) Further, most taxa are virtually or even completelyunknown in many environments.
Conservationists measure the diversity either directly by measuring the genetic differences or indirectly through use of the taxanomic (cladistic) hierarchy.
Whittakar, introduced the concepts of alpha, beta and gamma diversity. Alpha diversity refers to the diversity value for single sites whereas, Beta and Gamma diversity concepts related to change in diversity between sites, the former at local, and latter at over larger area or geographical scale such as continents.An important and essential part of these relational concepts is the idea of species turnover, which simply means thje degree to which species present at one site are replaced by other at different sites.
PROBLEMS IN MEASURING BIODIVERSITY
One of the most important problem in the maintenance of biological diversity is an assessment of the relative importance in terms of diversity of different areas, habitats or ecosystems. This importance can be assessed in different related ways. The overall diversity of any given area will be reflection both of its range of habitats. The greater the differences between the various component habitat in terms of species composition, then the greater the overall diversity will be. By measuring species abundance, a number of models have been developed to find out diversity indices. As different mathematical and biological assumptions are made in these models, they often generate different diversity measures from the same set of data.
DIVERSITY AT DIFFERENT GRADIENT
The overall diversity of any given area is a reflection both of the range of habitat it includes and the diversity of the components habitats. In terms of species composition of differences between the various component is more, the overall diversity will also be more. Biological diversity is not evenly distributed throughout the world. It varies from region to region.
In terrestrial ecosystem diversity generally decreases with increasing altitude. This is apparently clear from an example showing very low species diversity at highest region at all altitudes. This is called as elevational gradients.
In aquatic ecosystems diversity almost invariably decreases when salinity increases above 35 ppt. in sea water and 2 ppt in fresh water. Oceanic islands (smaller) continental mountain regions are examples of geographical entities which typically have comparatively low species diversity. This may be due to problems of long distance dispersal for plants. But the low total number of species frequently include a large endemic element. In Mauritius, out of 878 higher plant species 329 are endemic, in Socotra, 268 species are endemic out of 788 flowering plant species and in Helena 74 out of 89 species. Larger oceanic islands in tropical and high temperate latitude show a high level of diversity and endemism. The richest island flora is probably that of Madagaskar estimated up to 10,000 species with 8,000 endemics including eight endemic families of flowering plants. Cuba has 6,400 species of higher plants out of which 3,233 of them are endemic. Japan has 2,000 endemic species out of 5,372 species, New Zealand has 1,942 out of 2,371.
On the other hand, relatively poor levels of diversity and endemisms can be seen in drier tropical and subtropical regions. In these regions drought resistant and economic plants are the main dominating species.
BIO-DIVERSITY VALUE
One of the most fundamental value of plants biodiversity is in supplying the world’s food. Originally plants were consumed directly from the wild and gathering of wild products continue throughout the world today. The evaluation of crop plants began between 5,000 and 10,000 years ago. It is now generally thought that plants of agriculture originated were more or less simultaneously in various parts of the world. Of the estimated 250,000 species of flowering plants only about 3,000 have been regarded as a food resource. Relatively few botanical families account for the world’s main domesticated plants. Gramineae and Leguminosae are most important families followed by the Cruciferae, Rosaceae, Umbelliferae, Solanaceae, and Labiatae. Other important families are the Chenopodiaceae, Araceae, Cucurbitaceae and Compositae.
The discovery, domestication and cultivation of ornamental plants have a long history comparable to that of food crops. Ornamental plants are important commodity in international trade. Today, the diversity of decorative plant species established in cultivation surpasses the variety of plant commonly grown for food around the world. In UK alone a estimated 3,000 species are in general cultivation in addition to the wide range of cultivers and hybrids. In Peru, fruits of 1 93 species are regularly consumed of these 1 20 species are exclusively wild.
The introduction of genes from wild and weed relatives increased the availability of crop genetic diversity for further selection and improvement by farmers. Many cultivated species may not have survived in domestication without the interchange of genes between wild and crop populations.
LOSS OF BIODIVERSITY
Plant diversity as a global resource remains poorly understood inadequately documental and often wasted, but still remains immense potential for further development of natural products. Human population explosion and application of economic processes to natural resources are the main causes for substantial losses of biological diversity. Humans continue to modify their natural environment so that it can better satisfy their needs. However, it is also predicted that this process is unlikely to target an adequate amount of diversity because persons deciding to com ert their local environment do not consider the global cost of so doing. Globally the forest has been reduced to 55% of ,ts original cover and the rate of deforestation is in excess ct 1,00,000 Sq.km. every year. In India the rate of destruction of forest is 13,000 sq.km. annually.*16\218\2*