4. A GLIMPSE OF OUR RESEARCH ACTIVITIES
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a) Behaviour & Sociobiology
Colonies of social insects (ants, bees, wasps, termites)
a number of workers. The workers usually work for the well-being
of their colony-mates and die without leaving behind any of their
own progeny. How can natural selection, which is based on
survival of the fittest, give rise to such altruism on the part
of workers ? This question has bothered evolutionary biologists
starting from the time of Darwin who termed it "...one special
difficulty, which at first appeared to me to be insuperable, and
facts that new nests are often initiated by one or a group of
females (Fig.1) and that newly eclosed individuals may either
leave to found new nests of their own, stay back and become
workers or stay back and eventually become queens in their nests
of birth (Fig.2).
By studying the behaviour of individually marked members of
several colonies of Ropalidia marginata and R. cyathiformis we
have discovered a large amount of inter-individual variability in
behaviour. By multivariate statistical analysis of this
variation, we have been able to classify the members of a colony
into three behavioural castes which we have called Sitters,
Fighters and Foragers (Fig.3). Of these, Foragers do bulk of the
extra-nidal tasks of food gathering and have the most poorly
developed ovaries. Sitters and Fighters have relatively better
developed ovaries and share the intra-nidal tasks of building the
nest and caring for the brood (Fig.4).
The first serious attempt to solve the puzzle of the
apparently altruistic behaviour of the sterile workers in social
insect colonies was made by W.D.Hamilton. He argued that, while
producing offspring is one way of obtaining fitness, aiding
genetic relatives is another. Hamilton's theory seems
particularly applicable to the evolution of sterile worker castes
in the Hymenoptera because they are haplodiploid and thus exhibit
an asymmetry in genetic relatedness such that full-sisters are
more closely related to each other than a female is to her
offspring.
Our researches indicate however that this genetic asymmetry
is broken down in R.marginata by two phenomena. First, queens
are Polyandrous; they mate with more than one male, store sperm
from each of their mates in their spermathecae and simultaneously
produce different patrilines of daughters. In other words, not
all daughters of a queen are full-sisters; colonies consist of a
mixture of full-sisters and half-sisters. Because colonies of
R.marginata are perennial, they often outlive their queens,
providing opportunities for some of the workers to become queens.
Such Serial Polygyny results in the simultaneous presence of
different matrilines in a colony (Fig.5). We have shown that
these two phenomena result in a sufficient decrease in genetic
relatedness between workers and brood so that the advantage of
haplodiploidy for the evolution of sociality postulated by
Hamilton is largely forfeited in this species.
To test if there is variation in fertility between
individuals which may make it "easier" for some individuals to
accept worker roles, we isolated a large number of female R.
marginata at eclosion and tested them for their ability to start
new nests and lay eggs. The results of such an experiment
showed that only about half the eclosing females are capable of
doing so. We have also demonstrated that nests in which larvae
are fed at a relatively higher rate produce a relatively greater
proportion of females that can initiate nests on their own.
However, in natural colonies, most individuals are workers and
only a small number become queens whereas in our experiments
about 50% of the individuals were capable of reproducing. The
question remains therefore as to why only a small proportion of
these 50% become queens in nature.
If wasps are programmed not to be sterile or fertile but to
choose between solitary and group life and if the roles of queen
and worker in the group mode are decided by chance factors, then
it is possible that individuals who are programmed to "gamble"
and join a group will do better, on the average, compared to
those who shy away from the risk of group life and remain
solitary. The fact that colonies of Ropalidia consist of several
individuals who are capable of reproducing and that workers quite
often succeed in driving away the queens of their colony and
taking over the role of the queen lends credence to this gambling
hypothesis ; females who stay back and work are not doomed to be
sterile - some of them at least can become queens and inherit the
whole colony which may be much more profitable than trying to
start a new single foundress nest.
The role of demographic factors in promoting the evolution
of insect societies has so far been relatively unexplored. We
have therefore recently constructed a hierarchy of models to
illustrate, within the framework of inclusive fitness theory,
that demographic factors can select for a worker caste in social
insects. The first model in the series shows that Delayed
attainment of reproductive maturity lowers the inclusive fitness
of a solitary foundress relative to that of workers. The second
model shows that Variation in age at reproductive maturity makes
the worker strategy more profitable to some individuals than to
others and thus predicts the co-existence of single-foundress and
multiple-foundress nests. The third model demonstrates the
possibility of Mixed reproductive strategies so that, some
individuals whose attainment of reproductive maturity is expected
to be delayed can first act as workers and later switch over to
the role of a queen or nest foundress. The fourth model shows
that identical adult mortality rates can have different
consequences for workers and solitary nest foundresses. This is
because a solitary foundress will have to necessarily survive for
the entire duration of development of her brood while a worker
can hope to get proportional fitness returns for short periods of
work. Workers may therefore be said to have Assured fitness
returns.
These theoretical models have been tested using field and
laboratory demographic data on R.marginata and demonstrate that
such factors provide a consistently more powerful selective
advantage for the worker strategy than genetic asymmetries
created by haplodiploidy. We believe that a combination of
empirical and theoretical investigations on a model system such
as R.marginata, such as that pursued by us, can throw
considerable light on the forces responsible for the evolution of
altruism in insects in particular and animals in general.
Sociobiology has yielded major insights into the
evolutionary basis of a variety of traits observed in animals -
altruism and spite, selfishness and co-operation, parent-
offspring conflict and sibling rivalry, to name a few. Somewhat
more recently, these ideas have been successfully extended to
plant systems as well. In collaboration with the University of
Agricultural Sciences, the Centre for Ecological Sciences has
begun to explore some key issues in plant sociobiology.
Polyembryony is a phenomenon where a seed contains two kinds
of embryos - one obtained by the normal process of fertilization,
and the other produced asexually. Using inclusive fitness models
as well as explicit population genetic models, the conditions
favourable for the evolution of polyembryony (in terms of
maternal investments in the two embryos, the efficiency of
conversion of resources into fitness etc.) were obtained. Brood
reduction in plants, where some of the seeds in a developing
fruit are aborted, is believed to result at least partly from
sibling rivalry (antagonistic interaction between seeds).
Polyembryony, whereby the parent plant can compensate for a loss
of such seeds by producing additional embryos, can thus be viewed
as a counter strategy to brood reduction. A survey of the
reproductive characteristics and strategies of a large number of
plant species revealed patterns supporting this conjecture; brood
reduction itself as well as factors associated with brood
reduction (e.g. larger number of seeds per fruit) were seen to be
associated with polyembryony (Fig.6).
The conflict between developing seeds within a fruit over
resources, allocated to the fruit by the maternal plant, has also
been investigated by population genetic models. The intensity of
conflict was seen to decrease with the increasing number of seeds
per fruit. Since in single seeded fruits there is no
competition, this result implies that the parental plant should
favour production of either a single ovule, or very many ovules.
In particular, conflict would be highest in two ovuled flower,
indicating it to be a suboptimal choice. A frequency
distribution of number of ovules per flower, obtained from over
600 plant species, strikingly confirmed this prediction.
b) Conservation Biology, Biodiversity & Forest Dynamics
In the area of conservation biology we have looked at
biodiversity and its conservation both at the population-level
and the community-level.
One of the earliest scientific studies on Asian elephant
(Elephas maximus) ecology was carried out by our centre. This
study of a southern Indian population looked at elephant-human
interactions within the framework of the natural life-history of
the elephant. It showed how movement and habitat utilization were
interrelated with foraging behaviour of elephants, and that crop
raiding was an extension of the optimal foraging strategy. A much
higher propensity of adult male elephants to raid crops and kill
people was the outcome of a "high risk - high gain" strategy by
the males to enhance reproductive success; this had important
implications for conflict management (Fig.7). The impact of the
elephant-human interaction, in particular, the selective poaching
of males for tusks, on population dynamics and viability was also
analyzed. Several recommendations for elephant conservation and
management emerged out of this study.
More recently, using the stable carbon isotope technique, we
have shown that browse plants (C3 plant type) contribute a
substantially higher proportion of protein for organic synthesis
than do the grasses (of the C4 type). This again has important
implications for the scientific management of elephant habitats.
Our ongoing work on elephants includes a long-term assessment of
elephant-vegetation interaction, population dynamics and
behavioural changes caused by skewed sex ratios in the Mudumalai
Sanctuary.
As part of a long-term programme of monitoring large mammals
in Mudumalai Sanctuary, we have been censusing the populations of
elephant (Elephas maximus), gaur (Bos gaurus), sambar (Cervus
unicolor), chital (Axis axis), muntjac (Muntiacus muntjac), four-
horned antelope (Tetracerus quadricornis) and common langur
(Presbytis entellus) since 1989 (Table 1). This has led to the
development of standard census technique for large mammals in
tropical forests. In addition, a detailed study of the ecology of
the dhole (Cuon alpinus), its population dynamics, movement
patterns, home range size, hunting strategy and interaction with
the principal prey species has also been carried out. This study
is now being extended to the reproductive behaviour of this
highly social canid.
The role of parasites as selective agents in moulding the
life-histories of their host species has been recognized only in
recent years. We have studied the faecally-dispersed parasites in
twelve species of wild mammals in Mudumalai Sanctuary. More than
any other factor parasite communities were found to be shaped by
the host predatory pressure. Several results from the study would
have implications for the management of wild mammal populations.
The disappearance of tropical forests, among the richest
biological communities on earth, has stimulated world-wide
interest in understanding their structure and dynamics. As part
of an international network of large plots to study tropical
vegetation dynamics on a long-term basis we have set up a
permanent plot of 50-hectares during 1988-89 in the deciduous
forests of Mudumalai Sanctuary. Within this plot nearly 26000
individual woody plants above 1 cm dbh belonging to 72 species
have been identified, measured, tagged and mapped (Figs. 8 and
9). This plot is being annually re-censused to look at changes
particular, the dynamics of this vegetation type is influenced by
fire and large mammals such as elephants which damage trees.
Tropical montane forests are the most poorly studied among
forest communities. In the Nilgiri hills the montane evergreen
forests occur in patches, known locally along as sholas, along
the folds of the hills and interspersed with extensive
grasslands. Our studies on the past history of the shola forests
and grasslands indicates that their extent has fluctuated
considerably in the past as a result of climatic change. In
recent centuries the forests have also been degraded by human
activity. We have recently begun setting up permanent plots in
the shola forests to study their dynamics in detail and come up
with strategies for their regeneration (Table 2).
To complement the studies on forest dynamics we have also
taken up phenological studies in these forests. Vegetative and
reproductive phenology of trees in the deciduous forests of
Mudumalai Sanctuary was monitored during 1988-90. Leaf flushing
during the peak of the dry season much before the onset of rains
seemed to be influenced by the need to avoid herbivory by insects
which emerge after the rains. Flowering and fruiting phenologies
were influenced by both abiotic and biotic factors. Reproductive
success of an individual was maximized if it flowered during the
peak flowering phase of the population (Fig.10).
Our studies on different taxonomic groups in the same
locality have shown that diversity levels in these groups may not
be necessarily correlated; for example in the district of Uttara
Kannada bird and woody plant species richness is inversely
correlated. We have also shown that amphibian species richness on
the Western Ghats appears to peak in the district of Coorg,
although the Western Ghats further south are believed to be on
the whole much richer in biodiversity (Table 3).
We have also worked on the problem of objectively assigning
conservation values at the level of taxa as well as localities.
These developments are of basic theoretical interest; they have
been fleshed out through concrete studies of bird and flowering
plant diversity in the district of Uttara Kannada (Table 4).
c) Ecodevelopment
Degradation of natural resources like vegetation, soil,
water and air is at the centre of environmental deterioration,
threatening the sustainability of development and quality of life
at global and local level. Sustainable development is at the top
of the agenda of researchers as well as policy makers worldwide.
The centre for Ecological Sciences has been working on the
concept of participatory eco-development; aimed at participatory,
equitable and sustainable development. All these three paradigms
of development have received little or no attention of planners
or policy makers. Even when there was awareness, an approach and
methodology was lacking to incorporate the three components of
Participatory equitable and sustainable development. We have
developed a methodology for Participatory, equitable and
sustainable development and field tested it in two village
ecosystems in western ghat region, with the participation of
local community and developmental agencies.
We aimed at understanding the features of natural resources
and their use, involved the local community to identify the needs
and to learn about traditional knowledge and practices, jointly
developed a set of developmental options and modes of sustainable
management of resources and monitoring of the process. One of
the major lessons was that without genuine empowerment of local
communities sustainable management of natural resources is not
possible.
We have conducted several ecological studies that would
contribute to promotion of ecodevelopment and sustainable
management of natural resources.
1. The current practices of extraction of biomass like leaf
biomass for manure purpose from forests is in a non-sustable way.
Our studies show that a leaf lopping intensity of 50% had no
negative impact on growth of trees.
2. Livestock grazing is considered to be one of the major factors
contributing to forest degradation affecting regeneration. The
fodder and grass balance studies in western ghats village
ecosystem have shown that the availability of grass + fodder is
inadequate and thus grass productivity from nearby forest lands
is required. Thus there is a need to evolve grazing or grass
harvesting practices such that forest regeneration is not
affected. Studies are also being conducted to understand the
sustainability of different grazing and land management practices
on sustainability of grass productivity.
3. Revegetation programmes in India are dominated by a few exotic
tree species, which do not meet the diverse biomass needs of
local communities. A study to assess the performance of
polycultural trials including local tree and shrub species, aimed
at meeting different biomass needs is being conducted in a
western ghat location. Some promising local tree species are
being identified.
4. Biomass fuel consumption has been projected to contribute to
forest degradation. Efficient use of biomass is one of the
options to mitigate biomass shortages and to conserve tree
resources. A large biomass conservation programme is being
implemented. Monitoring of the biomass conservation programme in
Western Ghat region shows that it is possible to conserve nearly
50% of the biomass currently used and at the same time improve
the quality of life of rural women through the programmes like
biogas and efficient stoves, both of which are environmentally
sound.
5. To enable inclusion of a diversity of local tree, shrub,
climber and lianna species, knowledge of their propagation
methods is necessary. We have completed a study to identify the
suitable propagation methods for several trees, shrubs, climbers
and lianna species. Suitable methods for most species have been
developed and problem species have been identified. Such locally
valuable species do not receive the attention of conventional
silviculturists and thus do not find any place in the
revegetation programmes.
6. In India with a high human and livestock population densities
and dependency on forests, it is hypothesized that forests are
subjected to degradation due to anthropogenic disturbances. To
assess the dynamics of vegetation status, nine forest locations
with one ha plot each, representing different vegetation types
and anthropogenic situations western ghats have been selected
and vegetation status is being monitored annually for the last
eight years and the results are being analysed.
7. India has vast extents of degraded lands. Prevention of
further degradation, revegetation and meeting the growing biomass
needs is one of the important challenges facing India.
Currently, revegetation programme is mainly a forest department
managed and exotic species dominated-conventional block
plantation approach, which is wholly based on expensive
artificial revegetation techniques. An alternate revegetation
approach is emerging where natural regeneration is promoted in
degraded lands either under a wholly community managed system or
under joint management system involving local community and
forest department. This low cost and participatory approach is
being assessed in a multilocational study. Preliminary analysis
shows the high potential of natural resources approach under
community management.
8. Climate change is one of the major environmental problems
facing the world today. Efforts are on to understand the factors
contributing to climate change and to identify mitigation
options. Deforestation is one of the contributing factors. We
analysed the deforestation rates and carbon flows for Indian
forests. The findings show that currently carbon emission rates
from forestry sector are nearly offset by sequestration in
forests under succession and forest plantations. Afforestation
in degraded lands is shows to have a potential to offset about
50% of national carbon emission.
The Centre has sustained interest in evolving sustainable
management practices for using natural resources and in evolving
a methodology for promoting sustainable and participatory
development under different ecological and socio-economic
situations.
d) Environmental History
Our work in the field of environmental history spans both
the geological and historical time scales.
In order to understand future vegetational and climate
change as a result of human activity, it is important to first
reconstruct past change in response to natural forces. In
collaboration with Physical Research Laboratory (Ahmedabad) and
Birbal Sahni Institute of Palaeobotany (Lucknow) we are currently
studying climatic (monsoonal) and vegetational change in
peninsular India during the late Quaternary period. The first
phase of the study involved analyzing carbon isotopes in peat
deposits of the upper Nilgiri plateau. Samples are dated by
radiocarbon (14C) method, while the stable carbon isotope
(13C/12C) ratio reflects the proportional contribution of C3
versus C4 plants, which in turn are good indicators of moisture
availability. The results indicate a very arid period during the
last glacial maximum (18000 years ago), a peak in monsoonal
activity at the beginning of the Holocene (10000 years ago), and
a weaker monsoon between 6000 and 3500 years ago. Further there
is some evidence for a short, wet period around 600 years back
which corresponds to the well-known Mediaeval Warm Period in
Europe. With newer samples this study is being extended back to
at least 40000 years before present through a combination of
stable isotope (carbon, oxygen and hydrogen) and pollen analyses
(Fig.11).
In a book entitled, "This Fissured Land : an ecological
History of India" we attempt to interpret the entire panorama of
India's ecological history from the time the land mass bumped
onto the Asian continent, through its colonization by hunter-
gatherers, agriculturists, industrial powers of Europe, to the
present day. We do this by tracing the differential impact of
different modes of resource use, and the accompanying economic,
societal and ideological formations. The book provides an
especially detailed picture of the forest history over the last
two centuries.
This forest history is characterized by continual
overuse and exhaustion of particular resource elements, followed
by shifts towards elements which are either less profitable to
exploit because of reasons such as difficulty of access, or call
for much greater technological sophistication to permit
exploitation. Such a sequence has been illustrated in rich detail
by a study of environmental change in Nilgiris; a massif in
Southern Western Ghats where an excellent data base is available
in the form of maps and other documents beginning as early as
1830's (Fig.12).
e) Environmental Policy
Issues of environmental and development are especially
complex in the Indian context given the diversity of modes of
resource use which ranges over hunting - gathering, shifting
cultivation, nomadic sheepkeeping, basketry and pottery to modern
intensive agriculture and industry. It is therefore especially
pertinent to enquire who benefits and who loses from the many
different development initiatives, and who incur the costs of
environmental degradation. Our group has actively pursued such
enquiries to generate worthwhile insights. It has also
participated in policy formulation with Government agencies, as
well as worked with the voluntary sector and local communities in
implementing new policies at the ground level.
An important theme of such activities has been the
value of the considerable detailed understanding of the behaviour
of complex ecosystems of each locality with the local
communities. We have therefore worked with state agencies and the
voluntary sector in devising appropriate institutions for the
meaningful involvement of local communities in devising
environmentally sound development strategies. This work has been
focused on two village clusters in Karnataka Western Ghats, where
we have investigated patterns of natural resource use,
identified elements of non-sustainable use and involved local
people in working out packages of environmentally more desirable
schemes of development. This experience was then extended to work
out the modalities for microplanning exercises for integrated
development of wastelands on behalf of the National Wastelands
Development Board (Fig.13).
We have also contributed to the forest policy debate,
highlighting the non-sustainable use of forest resources both on
open access public lands by local people, as well as in
consequence of commercial demands on resources of reserved forest
lands. We have proposed concrete alternatives, working with
various groups including parliamentary committees. These
alternatives have emphasized the primacy of environmental
services and livelihood security of rural poor; priorities that
are being increasingly emphasized (Fig.14).
Our group has been active in biodiversity conservation
issues, especially in molding newer approaches like the Biosphere
Reserves. We were involved in preparing the project document as
well as delineating various zones for the country's first
Biosphere Reserve in the Nilgiris (Fig.15). We have also been
engaged to assess the countrywide Biosphere Reserve programme by
the Ministry of Environment and Forests of the Government of
India. Along with these official programmes with a thrust on
fruitfully combining conservation and development; we have also
emphasized the positive role of traditional conservation
practices such as the sacred groves.
We have participated in several environmental impact
assessment and drawn attention to ways they may be rendered
effective, especially through a more open public process.
f) Human Ecology
Today humans are undoubtedly the most significant of
actors on the ecological stage, and an elucidation of their role
in bringing about environmental change is an important challenge.
Much of the ongoing work at the Centre for Ecological Sciences
addresses this challenge. This work encompasses theory, field
investigations as well as applied action research and relates to
historical as well as policy studies. At the theoretical level it
has involved looking at people -natural resource interactions in
terms of three major categories, namely, (i) ecosystem people,
who gather/produce most of the resources they depend on through
their own labour within a restricted resource catchment, (ii)
biosphere people, for whom market permit access to resources of
much of the entire globe, (iii) ecological refugees who have lost
access to resources through the market (Fig.16).
The Indian society is a complex mosaic of ecosystem
people, biosphere people and ecological refugees divided into
thousands of endogamous caste groups. A significant proportion of
these caste groups continue to pursue traditionally determined
resource use strategies. We have investigated quantitatively the
extent to which genetic as well as cultural transmission in the
Indian society is constrained by the boundaries of endogamous
caste groups. We have also documented the traditional patterns of
partitioning of resources amongst different endogamous groups in
a given locality. Such partitioning tended to ensure monopoly of
access to specific resources for members of a given caste group
in any locality. We have looked at how such a system facilitated
co-operative action in contexts ranging from communal hunting and
fishing to management of village woodlots and irrigation tanks
(Fig.17).
Indeed the traditional systems had a number of elements
of sustainable resource use, as well as conservation of
biodiversity. We have documented such practices are still
surviving based on field studies. These include, for instance,
protection to sacred groves and restrained harvests from
community woodlots. We have explored mathematical models of how
human groups may have arrived at thumb rules of resource use
through a trial and error process, and demonstrated that refugia,
such as sacred groves constitute a potentially very viable
element of a system of sustainable resource use (Fig.18).
We have documented current systems of resource
management by tribal and rural societies, as well as industries
in the modern sector and by the state apparatus. These
investigations point to the very positive role local communities
may play in conservation and sustainable use; not only through
traditional practices like sacred groves, but modern practices
like community based forest protection. Such forest protection
has been spontaneously initiated by a number of village
communities in Karnataka; and we have investigated the working of
such systems and the lessons it has for the systems of joint
forest protection and management being planned currently
(Fig.19).
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