Cross-taxon surrogacy of biodiversity in the Indian Garhwal Himalaya

https://doi.org/10.1016/S0006-3207(01)00158-6Get rights and content

Abstract

Biodiversity surveys were conducted in 13, 10×50 m2 plots located between 1400 to 3700 m above mean sea level in a range of habitats in temperate mixed Oak and Coniferous forests through sub-alpine to the alpine grasslands in Chamoli district of Uttaranchal state in the Indian Garhwal Himalaya. Cross-taxon congruence in biodiversity (α-diversity and β-diversity) across macrolichens, mosses, liverworts, woody plants (shrubs and trees) and ants was investigated, so as to examine the extent to which these groups of organisms can function as surrogates for each other. Although woody plants provided a major substrate for macrolichens and mosses, there was no species-specific association between them. Woody plant species richness was highly positively correlated with mosses (r2=0.63, P<0.001), but the relationship was not particularly very strong with lichens and liverworts. While there was a significant correlation in the species turnover (β-diversity) of macrolichens with mosses (r2=0.21, P<0.005), the relationship was relatively poor with the woody plants. On the other hand, negative correlations emerged in the species richness of ants with those of macrolichens, mosses and woody plants (r2=−0.44, P<0.05), but most of the complementarity (turnover) relationships among them were positive. Since diversity between taxonomic hierarchies within the group was consistently significantly positively correlated in all these taxa, the higher taxonomic categories such as genus and family may be employed as surrogates for rapid assessment and monitoring of species diversity. Although no single group other than macrolichens has emerged as a good indicator of changes in species richness in all other groups, some concordant relationships between them conform to the hypothesis that species assemblages of certain taxonomic groups could still be used as surrogates for efficient monitoring of species diversity in other groups whose distribution may further predict the importance of conserving overall biodiversity in landscapes such as the Garhwal Himalaya.

Introduction

Exploring distribution of biological diversity and the extent of surrogacy among different sets of organisms are importantly challenging scientific problems in conservation biology (UNEP, 1992, Heywood, 1995, Faith & Walker, 1996, Gaston, 1996, Gaston, 2000, Negi, 1999). The problem has been particularly investigated in the context of designing efficient programs of monitoring biodiversity and setting out conservation priorities (Pollard & Yates, 1993, Oliver & Beattie, 1993, Balmford & Long, 1995, Gadgil, 1996, Howard et al., 1998, Swengel & Swengel, 1999, Myers et al., 2000). In these contexts, there is a need to assess the extent to which high levels of diversity are correlated among different taxonomic groups in different bio-geographical regions. The organismic groups may be distinctive taxa such as ants and flowering plants, or nested taxonomic groups such as liverworts, mosses and bryophytes. By and large, no consistent levels of positive correlations have been found among distinct taxa, at levels of different types of habitats, such as forests with different levels of human disturbance, or large geographical regions, such as different grids into which the British Isles are divided (Prendergast et al., 1993, Lawton et al., 1998, Kunte et al., 1999, Pharo et al., 1999). As may be expected, higher, though variable, levels of correlations have been recorded among groups within a nested taxonomic hierarchy at different spatial scales (Noss, 1990, Williams & Gaston, 1994, Andersen, 1995). This is because organisms within such a hierarchy have similar responses to a variety of environmental parameters. In fact, one may postulate that the extent of correlation in levels of diversity in different habitats or geographical locales among different taxa would depend upon similarities or differences in their responses to biotic as well as abiotic parameters and mutualistic, competitive, or antagonistic (prey–predator, host–parasite) relationships amongst the different taxa. In the present study, an attempt is made to explore the possible influence of such factors by looking at five distinctive groups of organisms with variable levels of differences in their responses to environmental parameters and types of biotic interactions. The groups under investigation include macrolichens, mosses, liverworts, woody plants and ants. The lichens and bryophytes accounting for the first three groups occur on soil, rock and wood substrates. Shrubs and trees primarily growing on soil serve as wood substrate for macrolichens and mosses. The ants prefer drier soils underneath rocks, logs and thick moss beds for nesting whereas terricolous liverworts exclusively prefer wet soil. Owing to these habitat preferences, patterns of diversity of macrolichens, mosses and woody plants may be expected to be positively correlated, but be uncorrelated, or perhaps even be negatively correlated with those of liverworts and ants. Another hypothesis of interest may be postulated as while macrolichens and mosses extensively use live woody substrates, they may not be species specific. So while the species richness (α-diversity) of macrolichens and mosses may be positively correlated with that of woody plants, their levels of species turnover (β-diversity) may show little correlation. This investigation further addresses the environmental variables including the local land use factors that may explain significant variation in species richness and turnover in one group of organisms also explaining the variations in other surrogate groups. For example, livestock grazing, excessive lopping and fuel wood collection, especially for sustaining growing tourism in the area urgently needs to be regulated with high priority. If we do not control and monitor such land use patterns and their biodiversity implications, future generation will have to face with local extinction of many species, including wood loving macrolichens and mosses, some of which are medicinal and critical for the survival of the highly endangered Musk deer in the higher Himalaya (Negi, 1996, Negi, 1999, Negi, 2000a, Negi & Gadgil, 1996).

Section snippets

Study area

The study area (30°20′ N–30°35′N latitude; 79°10′ E–79°20′E longitude) is located in Chamoli district of Uttaranchal state in the Indian Garhwal Himalaya (Fig. 1). The mountainous landscape with steep to moderate slopes spreads over 500 sq km with elevation ranging between 1400 and 3700 m above mean sea level. The weathering bedrock that provides the bulk of the loose material in these mountains is crystalline and metamorphic with sedimentary deposits formed during the Paleaozoic (Ganser, 1964,

α-diversity

This investigation involving sampling of a total area of 6500 sq m yielded 13 families with 15 genera and 85 species of macrolichens, 34 families with 87 genera and 177 species of mosses, 13 families with 15 genera and 19 species of liverworts, 15 families with 19 genera and 24 species of wood plants and four sub-families with 18 genera and 26 species of ants. Average species richness of macrolichens at a plot was 18.15±1.60 (S.E.) with an average of 36.15±2.22 for moss species and 3.38±1.67

Discussion

The study attempted to identify surrogates across and within taxonomic groups to simplify the task of landscape level biodiversity assessment and monitoring. In India, biodiversity surveys are rarely comprehensive enough to sample and identify all the species in a given area. This is mainly because numbers of species are generally very high and the identification is time consuming. Moreover the species level taxonomy of Indian taxa, particularly in ants and lower plant groups, is poorly

Acknowledgements

This study would not have been complete without taxonomic support of Drs. D. K. Upreti, Nehal Aziz, Virendra Nath, Ashish Asthana, Ms. Padmini Nair. Bharat Singh Rawat assisted in the field work and Srinidhi and Robert in computer programming and simulations. Dr. N.V. Joshi enlightened us on statistical analysis. We thank Padmashri Chandi Prasad Bhatt and other members of DGSM for their cooperation during the field surveys. Financial support by the Ministry of Environment and Forests and

References (60)

  • A.N. Andersen

    Measuring more of biodiversitygenus richness as a surrogate for species richness in Australian ant faunas

    Biological Conservation

    (1995)
  • S.R. Swengel et al.

    Correlations in abundance of grassland songbirds and prairie butterflies

    Biological Conservation

    (1999)
  • P.H. Williams et al.

    Measuring more of biodiversity: can higher-taxon richness predict wholesale species richness?

    Biological Conservation

    (1994)
  • D.D. Awasthi

    A key to the macrolichens of India and Nepal

    Journ. Hattori Bot. Lab.

    (1988)
  • A. Balmford et al.

    Across country analyses of biodiversity congruence and current conservation effort in the tropics

    Conservation Biology

    (1995)
  • P. Basu

    Seasonal and spatial patterns in ground foraging ants in a rain forest in the Western Ghats, India

    Biotropica

    (1997)
  • R.S. Chopra

    Taxonomy of Indian Mosses. Publications & Information Directorate

    (1975)
  • S. Crites et al.

    Diversity and abundance of bryophytes, lichens and fungi in relation to woody substrate and successional stage in aspen mixedwood boreal forests

    Canadian Journal of Botany

    (1998)
  • R.J.R. Daniels et al.

    On the relationship between birds and woody plant species diversity in the Uttar Kannada district of South India

    Proc, Natl. Acad. Sci. (U.S.A.)

    (1992)
  • D.P. Faith et al.

    How do indicator groups provide information about the relative biodiversity of different sets of areas? On hotspots, complementarity and pattern based approaches

    Biodiversity Letters

    (1996)
  • M. Gadgil

    Documenting diversityan experiment

    Current Science

    (1996)
  • M. Gadgil et al.

    Ecological diversity

  • R. Gadagkar et al.

    Ant species richness and diversity in some selected localities in Western Ghats, India

    Hexapoda

    (1993)
  • H. Ganser

    Geology of the Himalaya

    (1964)
  • K.J. Gaston

    Biodiversity: a Biology of Numbers and Difference

    (1996)
  • K.J. Gaston

    Global patterns in biodiversity

    Nature

    (2000)
  • B. Groombridge

    Global Biodiversity: Satus of the Earth's Living Resources

    (1992)
  • P. Greig-Smith

    Quantitative Plant Ecology, 3rd edition

    (1983)
  • R.K. Gupta

    Forest types of Garhwal Himalayas in relation to edaphic and geological formations

    Journ. Soc. Indian For

    (1964)
  • V.H. Heywood

    Global Biodiversity Assessment

    (1995)
  • B. Holldobler et al.

    The Ants

    (1990)
  • P.C. Howard et al.

    Complementarity and the use of indicator groups for reserve selection in Uganda

    Nature

    (1998)
  • C.J. Krebs

    Ecological methodology

    (1989)
  • K. Kunte et al.

    Patterns of butterfly, bird and tree diversity in the Western Ghats

    Current Science

    (1999)
  • J.H. Lawton et al.

    Biodiversity inventories, indicator taxa and effects of habitat modification in tropical forest

    Nature

    (1998)
  • J.A. Ludwig et al.

    Statistical Ecology: A Primer on Methods and Computing

    (1988)
  • W.P. Mackay et al.

    Impact of slashing and burning of a tropical rain forest on the native ant fuana (HymenopteraFormicidae)

    Sociobiology

    (1991)
  • Magurran, A.E., 1988. Ecological Diversity and its Measurements. Princeton University...
  • B. McCune et al.

    Diversity relationships of forest layers in the Swan Valley, Montana

    Ecology

    (1981)
  • N. Myers

    Threatened biotas“hot-spots” tropical forests

    The Environmentalists

    (1988)
  • Cited by (74)

    • Remote sensing of terrestrial plant biodiversity

      2019, Remote Sensing of Environment
    • Cost-efficiency of cross-taxon surrogates in temperate forests

      2018, Ecological Indicators
      Citation Excerpt :

      This might partly explain variations in past results and calls for a greater attention to these statistical issues (in line with Biggs et al., 2009). Most studies have found weak cross-taxon congruence (e.g. Grand et al., 2004; Lovell et al., 2007; Negi and Gadgil, 2002; Ricketts et al., 2002). Prendergast et al. (1993), Lombard (1995), Oliver and Beattie (1996), Kerr (1997), Kati et al. (2004) and, in a review, Wolters et al. (2006) concluded that no taxon has as yet proved to be universal (in accordance with Nordén et al., 2007) or even to be a good predictor for the species richness of other taxa.

    • Birds as surrogates for mammals and reptiles: Are patterns of cross-taxonomic associations stable over time in a human-modified landscape?

      2016, Ecological Indicators
      Citation Excerpt :

      We quantified species composition using Bray–Curtis dissimilarity metric between pairs of sites for all landscapes contexts. The advantage of partial Mantel tests over simple Mantel tests is that they can measure the correlation between two matrices (Paszkowski and Tonn, 2000; Su et al., 2004) after considering variation associated with a matrix of spatial (Euclidean) distances, thus accounting for potential problems of spatial autocorrelation. Significance of all partial Mantel tests was assessed using a Monte Carlo procedure with 999 permutations.

    View all citing articles on Scopus
    View full text