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Journal of Agricultural Technology 2012, Vol. 8(2): 403-415
403
Role of Earthworms in Vermitechnology
A.A. Ansari1* and S.A. Ismail2
1Department of Biological Sciences, Faculty of Science, Kebbi State University of Science and
Technology, Aliero, Kebbi State, Nigeria, 2Managing Director, Ecoscience Research
Foundation, 98, Baaz Nagar, 3/621 East Coast Road, Chennai, India
A.A. Ansari and S.A. Ismail (2012) Role of Earthworms in Vermitechnology. Journal of
Agricultural Technology 8(2): 405-415.
Earthworms are essential detritus feeders that play a vital role in the process of decomposition
of organic matter and soil metabolism. They are referred to as indicators of soil health. The
complex process of partial breakdown of organic matter and mixing with mucous and gut
microbial flora in the form of earthworm cast results in the enhancement of soil fertility status.
They influence the soil by formation of drilosphere contributing towards soil porosity.The
beneficial role of earthworm is very important for plant growth and productivity. The
significance of earthworm has resulted in development of vermitechnology that involves the
use of surface and subsurface local varieties of earthworms in composting and soil
management. Thus the organic waste can be excellently recycled by vermicomposting process
thereby resulting in the production of vermicompost and vermiwash that have been proved to
be essential component in plant growth and productivity.
Key words: Earthworms, Soil fertility, Vermitechnology, Vermicomposting, Vermiwash,
Vermicast, Plant growth
Introduction
Earthworms are terrestrial invertebrates belonging to the Order
Oligochaeta, Class Chaetopoda, Phylum Annelida, which have originated about
600 million years ago, during the pre-Cambrian era (Piearce et al., 1990).
Earthworms occur in diverse habitat, exhibiting effective activity, by bringing
about physical and chemical changes in the soil leading to improvement in soil
fertility. An approach towards good soil management, with an emphasis on the
role of soil dwellers like earthworms, in soil fertility, is very important in
maintaining balance in an ecosystem (Shuster et al., 2000). The role of
earthworms in soil formation and soil fertility is well documented and
recognised (Darwin, 1881; Edwards et al., 1995; Kale, 1998; Lalitha et al.,
* Corresponding author: A.A. Ansari; e-mail: ansari_adil@hotmail.com
Journal of Agricultural Technology
2012 Vol. 8(2): 403-415
Available online http://www.ijat-aatsea.com
ISSN 1686-9141
404
2000). The main activity of earthworms involves the ingestion of soil, mixing
of different soil components and production of surface and sub surface castings
thereby converting organic matter into soil humus (Jairajpuri, 1993).
Earthworms play an important role in the decomposition of organic matter and
soil metabolism through feeding, fragmentation, aeration, turnover and
dispersion (Shuster et al., 2000).
Earthworms were referred by Aristotle as “the intestines of earth and the
restoring agents of soil fertility” (Shipley, 1970). They are biological indicators
of soil quality (Ismail, 2005), as a good population of earthworms indicates the
presence of a large population of bacteria, viruses, fungi, insects, spiders and
other organisms and thus a healthy soil (Lachnicht and Hendrix, 2001). The
role of earthworms in the recycling of nutrients, soil structure, soil productivity
and agriculture, and their application in environment and organic waste
management is well understood (Edwards et al., 1995; Tomlin et al., 1995;
Shuster et al., 2000; Ansari and Ismail, 2001a,b; Ismail, 2005; Ansari and
Ismail, 2008; Ansari and Sukhraj, 2010).
Ecological strategies of earthworms
Lee (1985) recognised three main ecological groups of earthworms,
based on the soil horizons in which the earthworms were commonly found i.e.,
litter, topsoil and sub soil. Bouché (1971, 1977), also recognised three major
groups based on ecological strategies: the epigeics (Épigés), anecics
(Anéciques) and endogeics (Éndogés). Epigeic earthworms live on the soil
surface and are litter feeders. Anecic earthworms are topsoil species, which
predominantly form vertical burrows in the soil, feeding on the leaf litter mixed
with the soil. Endogeic earthworms preferably make horizontal burrows and
consume more soil than epigeic or anecic species, deriving their nourishment
from humus.
Distribution of earthworms
Earthworms occur all over the world, but are rare in areas under constant
snow and ice, mountain ranges and areas almost entirely lacking in soil and
vegetation (Edwards and Bohlen, 1996). Some species are widely distributed,
which are called peregrine, whereas others, that are not able to spread
successfully to other areas, are termed as endemic (Edwards and Lofty, 1972).
Journal of Agricultural Technology 2012, Vol. 8(2): 403-415
405
Factors affecting earthworm distribution
The distribution of earthworms in soil is affected by physical and
chemical characters of the soil, such as temperature, pH, moisture, organic
matter and soil texture (Edwards and Bohlen, 1996).
Temperature
The activity, metabolism, growth, respiration and reproduction of
earthworms are all influenced greatly by temperature (Edwards and Bohlen,
1996).
pH
pH is a vital factor that determines the distribution of earthworms as they
are sensitive to the hydrogen ion concentration (Edwards and Bohlen, 1996;
Chalasani et al., 1998). pH and factors related to pH influence the distribution
and abundance of earthworms in soil (Staaf, 1987). Several workers have stated
that most species of earthworms prefer soils with a neutral pH (Jairajpuri, 1993;
Edwards and Bohlen, 1996). There is a significant positive correlation between
pH and the seasonal abundance of juveniles and young adults (Reddy and
Pasha, 1993).
Moisture
Prevention of water loss is a major factor in earthworm survival as water
constitutes 75-90% of the body weight of earthworms (Grant, 1955). However,
they have considerable ability to survive adverse moisture conditions, either by
moving to a region with more moisture (Valle et al., 1997) or by means of
aestivation (Baker et al., 1992). Availability of soil moisture determines
earthworm activity as earthworm species have different moisture requirements
in different regions of the world (Zaller and Arnone, 1999). Soil moisture also
influences the number and biomass of earthworms (Olson, 1928; el–Duweini
and Ghabbour, 1965; Wood, 1974).
Organic matter
The distribution of earthworms is greatly influenced by the distribution of
organic matter. Soils that are poor in organic matter do not usually support
large numbers of earthworms (Edwards and Bohlen, 1996). Several workers
406
have reported a strong positive correlation between earthworm number and
biomass and the organic matter content of the soil (Doube et al., 1997; Ismail,
2005).
Soil texture
Soil texture influences earthworm populations due to its effect on other
properties, such as soil moisture relationships, nutrient status and cation
exchange capacity, all of which have important influences on earthworm
populations (Lavelle, 1992).
Effect of earthworms on soil quality
Earthworms, which improve soil productivity and fertility (Edwards et
al., 1995), have a critical influence on soil structure. Earthworms bring about
physical, chemical and biological changes in the soil through their activities and
thus are recognised as soil managers (Ismail, 2005).
Effects on physical properties of soil
Soil structure is greatly influenced by two major activities of earthworms:
Ingestion of soil, partial breakdown of organic matter, intimate mixing of these
fractions and ejection of this material as surface or subsurface casts. Burrowing
through the soil and bringing subsoil to the surface. During these processes,
earthworms contribute to the formation of soil aggregates, improvement in soil
aeration and porosity (Edwards and Bohlen, 1996). Earthworms contribute to
soil aggregation mainly through the production of casts, although earthworm
burrows can also contribute to aggregate stability since they are often lined with
oriented clays and humic materials (Lachnicht and Hendrix, 2001). Most
workers have agreed that earthworm casts contains more water-stable
aggregates than the surrounding soil and by their activity influence both the
drainage of water from soil and the moisture holding capacity of soil, both of
which are important factors for plant productivity (Edwards and Bohlen, 1996;
Lachnicht and Hendrix, 2001).
Effect on chemical properties of soil
Earthworms bring about mineralisation of organic matter and thereby
release the nutrients in available forms that can be taken up by the plants
(Edwards and Bohlen, 1996). Organic matter that passes through the earthworm
gut is egested in their casts, which is broken down into much finer particles, so
Journal of Agricultural Technology 2012, Vol. 8(2): 403-415
407
that a greater surface area of the organic matter is exposed to microbial
decomposition (Martin, 1991). Earthworms have major influences on the
nutrient cycling process in many ecosystems (Edwards and Bohlen, 1996).
These are usually based on four scales (Lavelle and Martin, 1992), during
transit through the earthworm gut, in freshly deposited earthworm casts, in
aging casts, and during the long-term genesis of the whole soil profile.
Earthworms contribute nutrients in the form of nitrogenous wastes
(Ismail, 2005). Their casts have higher base-exchangeable bases, phosphorus,
exchangeable potassium and manganese and total exchangeable calcium.
Earthworms favour nitrification since they increase bacterial population and
soil aeration. The most important effect of earthworms may be the stimulation
of microbial activity in casts that enhances the transformation of soluble
nitrogen into microbial protein thereby preventing their loss through leaching to
the lower horizons of the soil. C: N ratios of casts are lower than that of the
surrounding soil (Bouché, 1983). Lee (1983) summarised the influence of
earthworms on soil nitrogen and nitrogen cycling. According to him,
nitrogenous products of earthworm metabolism are returned to the soil through
casts, urine, mucoproteins and dead tissues of earthworms.
Earthworms and microorganisms
There is a complex inter-relationship between earthworms and
microorganisms. Most of the species of microorganisms that occur in the
alimentary canal of earthworms are the same as those in the soils in which the
earthworms live. The microbial population in earthworm casts is greatly
increased compared with the surrounding soil (Haynes et al., 1999). Earthworm
casts usually have a greater population of fungi, actinomycetes and bacteria and
higher enzyme activity than the surrounding soil (Lachnicht and Hendrix,
2001). Microbial activity in earthworm casts may have an important effect on
soil crumb structure by increasing the stability of the worm-cast-soil relative to
that of the surrounding soil (Edwards and Bohlen, 1996). Earthworms are very
important in inoculating soils with microorganisms. Many microorganisms in
the soil are in a dormant stage with low metabolic activity, awaiting suitable
conditions like the earthworm gut (Lachnicht and Hendrix, 2001) or mucus
(Lavelle et al., 1983) to become active. Earthworms have been shown to
increase the overall microbial respiration in soil, thereby enhancing microbial
degradation of organic matter.
Earthworms and plant growth
408
Earthworms prepare the ground in an excellent manner for the growth of
plants (Darwin, 1881). Darwin’s findings that earthworms play a beneficial role
in soil fertility that is important for plant growth have been acknowledged by
many workers (Lee and Foster, 1991; Alban and Berry, 1994; Nooren et al.,
1995; Decaens et al., 1999). Earthworms have beneficial effects on soil and
many workers have attempted to demonstrate that these effects increase plant
growth and yields of crops (Decaens et al., 1999; Lalitha et al., 2000).
Earthworms release substances beneficial to plant growth like auxins and
cytokinins (Krishnamoorthy and Vajranabhaiah, 1986). The beneficial effect of
earthworms on plant growth may be due to several reasons apart from the
presence of macronutrients and micronutrients in vermicast and in their
secretions in considerable quantities (Lalitha et al., 2000; Ismail, 2005).
Reports suggest that certain metabolites produced by earthworms may be
responsible for stimulating plant growth.
Earthworms and land reclamation
The success of land reclamation by conventional techniques is often
limited by poor soil structure and low inherent soil fertility, and even in
productive soils, a marked deterioration in the botanical composition of the
sward can occur within a number of years (Hoogerkamp et al., 1983). A
number of studies indicate that earthworms play an important part in improving
reclaimed soils (Boyle et al., 1997; Butt, 1991). Some experiments on
improving impoverished soils by stimulating earthworm populations have been
reported (Butt et al., 1997). A successful introduction of earthworms in
reclaimable soil could be achieved by overcoming factors like unfavorable
moisture conditions, excessive fluctuation of surface temperature and lack of
suitable food (Satchell, 1983).
Earthworms and organic solid waste management
In recent years, disposal of organic wastes from various sources like
domestic, agriculture and industrial has caused serious environmental hazards
and economic problems. Burning of organic wastes contributes tremendously to
environmental pollution thus, leading to polluted air, water and land. This
process also releases large amounts of carbon dioxide in the atmosphere, a main
contributor to global warming together with dust particles. Burning also
destroys the soil organic matter content, kills the microbial population and
affects the physical properties of the soil (Livan and Thompson, 1997). It has
been demonstrated that earthworms can process household garbage, city refuse,
sewage sludge and waste from paper, wood and food industries (Kale et al.,
Journal of Agricultural Technology 2012, Vol. 8(2): 403-415
409
1982; Senapati and Dash, 1982; Muyima et al., 1994; Edwards and Bohlen,
1996; Ismail, 2005). In tropical and subtropical conditions Eudrilus eugeniae
and Perionyx excavatus are the best vermicomposting earthworms for organic
solid waste management (Kale, 1998). The use of earthworms in composting
process decreases the time of stabilisation of the waste and produces an
efficient bio-product, i.e., vermicompost.
Organic farming system is gaining increased attention for its emphasis on
food quality and soil health. Vermicompost and vermiculture associated with
other biological inputs have been actually used to grow vegetables and other
crops successfully and have been found to be economical and productive
(Ismail, 2005; Ansari and Ismail, 2008; Ansari and Jaikishun, 2011). In this
regard, recycling of organic waste is feasible to produce useful organic manure
for agricultural application. Compost is becoming an important aspect in the
quest to increase productivity of food in an environmentally friendly way.
Compost is becoming an important aspect in the quest to increase productivity
of food in an environmentally friendly way. Vermicomposting offers a solution
to tonnes of organic agro-wastes that are being burned by farmers and to
recycle and reuse these refuse to promote our agricultural development in more
efficient, economical and environmentally friendly manner. Both the sugar and
rice industries burn their wastes thereby, contributing tremendously to
environmental pollution thus, leading to polluted air, water and land. This
process also releases large amounts of carbon dioxide in the atmosphere, a main
contributor to global warming together with dust particles. Burning also
destroys the soil organic matter content, kills the microbial population and
affects the physical properties of the soil (Livan and Thompson, 1997).
Therefore organic farming helps to provide many advantages such as; eliminate
the use of chemicals in the form of fertilizers/pesticides, recycle and regenerate
waste into wealth; improve soil, plant, animal and human health; and creating
an ecofriendly, sustainable and economical bio-system models (Ansari and
Ismail, 2001a, b).
Vermitechnology
Vermitechnology is the use of surface and subsurface local varieties of
earthworm in composting and management of soil (Ismail, 2005). Darwin
(1881) has made their activities the object of a careful study and concluded that
‘it may be doubted if there are any other animals which have played such an
important part in the history of the world as these lowly organized creatures’. It
has been recognized that the work of earthworms is of tremendous agricultural
importance. Earthworms along with other animals have played an important
role in regulating soil processes, maintaining soil fertility and in bringing about
410
nutrient cycling (Ismail, 1997). Earthworms have a critical influence on soil
structure, forming aggregates and improving the physical conditions for plant
growth and nutrient uptake. They also improve soil fertility by accelerating
decomposition of plant litter and organic matter and, consequently, releasing
nutrients in the form that are available for uptake by plants.
Vermicomposting
Vermicomposting is the biological degradation and stabilization of
organic waste by earthworms and microorganisms to form vermicompost. This
is an essential part in organic farming today. It can be easily prepared, has
excellent properties, and is harmless to plants. The earthworms fragment the
organic waste substrates, stimulate microbial activity greatly and increase rates
of mineralization. These rapidly convert the waste into humus-like substances
with finer structure than thermophilic composts but possessing a greater and
more diverse microbial activity. Vermicompost being a stable fine granular
organic matter, when added to clay soil loosens the soil and improves the
passage for the entry of air. The mucus associated with the cast being
hydroscopic absorbs water and prevents water logging and improves water-
holding capacity. The organic carbon in vermicompost releases the nutrients
slowly and steadily into the system and enables the plant to absorb these
nutrients. The soil enriched with vermincompost provides additional substances
that are not found in chemical fertilizers (Kale, 1998). Vermicomposting offers
a solution to tonnes of organic agro-wastes that are being burned by farmers
and to recycle and reuse these refuse to promote our agricultural development
in more efficient, economical and environmentally friendly manner. The role of
earthworms in organic solid waste management has been well established since
first highlighted by Darwin (1881) and the technology has been improvised to
process the waste to produce an efficient bio-product vermicompost (Kale et
al., 1982; Ismail, 1993, Ismail, 2005). Epigeic earthworms like Perionyx
excavatus, Eisenia fetida, Lumbricus rubellus and Eudrilus eugeniae are used
for vermicomposting but the local species like Perionyx excavatus has proved
efficient composting earthworms in tropical or sub-tropical conditions (Ismail,
1993; Kale, 1998). The method of vermicomposting involving a combination of
local epigeic and anecic species of earthworms (Perionyx excavatus and
Lampito mauritii) is called Vermitech (Ismail, 1993; Ismail, 2005). The
compost prepared through the application of earthworms is called
vermicompost and the technology of using local species of earthworms for
culture or composting has been called Vermitech (Ismail, 1993). Vermicompost
is usually a finely divided peat-like material with excellent structure, porosity,
aeration, drainage and moisture holding capacity (Edwards, 1982, 1988). The
Journal of Agricultural Technology 2012, Vol. 8(2): 403-415
411
nutrient content of vermicompost greatly depends on the input material. It
usually contains higher levels of most of the mineral elements, which are in
available forms than the parent material (Edwards and Bohlen, 1996).
Vermicompost improves the physical, chemical and biological properties
of soil (Kale, 1998). There is a good evidence that vermicompost promotes
growth of plants (Lalitha et al., 2000) and it has been found to have a
favourable influence on all yield parameters of crops like wheat, paddy and
sugarcane (Ismail, 2005). Vermiculture is the culture of earthworms and
vermicast is the fecal matter released by the earthworms (Ismail, 2005). Many
agricultural industries use compost, cattle dung and other animal excreta to
grow plants. In today’s society, we are faced with the dilemma of getting rid of
waste from our industries, household etc. In order for us to practice effective
waste management we can utilize the technology of vermicomposting to
effectively manage our waste. This process allows us to compost the degradable
materials and at the same time utilize the products obtained after composting to
enhance crop production and eliminate the use of chemical fertilizers. As
indicated by Ansari and Ismail (2001), the application of chemical fertilizers
over a period has resulted in poor soil health, reduction in produce, and increase
in incidences of pest and disease and environmental pollution. In order to cope
with these trenchant problems, the vermin-technology has become the most
suitable remedial device (Edwards and Bohlen, 1996; Kumar, 2005).
Vermiwash
Vermiwash is a liquid that is collected after the passage of water through
a column of worm action and is very useful as a foliar spray. It is a collection of
excretory products and mucus secretion of earthworms along with
micronutrients from the soil organic molecules. These are transported to the
leaf, shoots and other parts of the plants in the natural ecosystem. Vermiwash,
if collected properly, is a clear and transparent, pale yellow coloured fluid
(Ismail, 1997). Vermiwash, a foliar spray, is a liquid fertilizer collected after
the passage of water through a column of worm activation. It is a collection of
excretory and secretory products of earthworms, along with major
micronutrients of the soil and soil organic molecules that are useful for plants
(Ismail, 1997). Vermiwash seems to possess an inherent property of acting not
only as a fertilizer but also as a mild biocide (Pramoth, 1995).
Conclusion
Environmental Hazards are compounded by accumulation of organic
waste from different sources like domestic, agricultural and industrial wastes
412
that can be recycled by improvised and simple technologies. Vermicompost
could be effectively used for the cultivation of many crops and vegetables,
which could be a step towards sustainable organic farming. Such technologies
in organic waste management would lead to zero waste techno farms without
the organic waste being wasted and burned rather then would result in recycling
and reutilization of precious organic waste bringing about bioconservation and
biovitalization of natural resources.
References
Alban, D.H. and Berry, E.C. (1994). Effects of earthworm invasion on morphology, carbon and
nitrogen of forest soil. Appl. Soil Ecol., 1: 243- 249.
Ansari, A.A. and S.A. Ismail (2001a). Vermitechnology in Organic Solid Waste Management.
Journal of Soil Biology and Ecology 21:21-24.
Ansari, A.A. and Ismail, S.A. (2001b). A Case Study on Organic Farming in Uttar Pradesh.
Journal of Soil Biology and Ecology. 27: 25-27.
Ansari, A.A. and Ismail, S.A. (2008). Reclamation of sodic soils through Vermitechnology.
Pakistan Journal of Agricultural Research, Volume 21, Number (1-4): 92-97.
Ansari, A.A. and Sukhraj, K. (2010). Effect of vermiwash and vermicompost on soil
parameters and productivity of okra (Abelmoschus esculentus) in Guyana. Pakistan
Journal of Agricultural Research, Volume 23 Number (3-4): 137-142.
Ansari, A.A. and Jaikishun, S. (2011). Vermicomposting of sugarcane bagasse and rice straw
and its impact on the cultivation of Phaseolus vulgaris L. in Guyana, South America.
Journal of Agricultural Technology 7(2): 225-234.
Baker, G.H., Barret, V.J., Gray-Gardner, R. and Buckerfield, J.C. (1992). The life history and
abundance of the introduced earthworms Aporrectodea trapezoides and Aporrectodea
caliginosa in pasture soils in the Mount Lofty Range, South Australia. Aust. J. Ecol., 17:
177-188.
Bouché, M.B. (1971). Relations entre les structures spatiales et fonctionelles des écosystemes,
illustrées par le rôle pédobiologique des vers de terre, In: La Vie dans les Sols, Aspects
Nouveaux, Études Experimentales, (Pesson, P. ed.), Gauthier-Villars, Paris. pp: 187-
209.
Bouché, M.B. (1977). Strate’gies lombriciennes. In: Soil organisms components of
ecosystems. (Lohm, U., and Persson, T. eds.), Biol Bull., Stockholm, 25: 122-132.
Bouché, M.B. (1983). Ecophysiologie des lombriciens: Acquis récentes et perspectives In: New
trends in soil biology. (Leprun, Ph., André, H. M., de Medts, A., Grégoire-Wibo, C. and
Wauthy, G. eds.), pp: 321-333.
Boyle, K.E., Curry, J.P. and Farrell, E.P. (1997). Influence of earthworms on soil properties and
gross production in reclaimed cutover peat. Biol. and Fertil. Soils., 25: 20-26.
Butt, K. (1991). The effect of temperature on the intensive production of Lumbricus terrestris
(Oligochaeta: Lumbricidae). Pedobiologia., 35: 257-264.
Butt, K.R., Fredrickson, J., Morris, R.M. and Edwards, C.A. (1997). The earthworm inoculation
unit technique: an integrated system for cultivation and soil-inoculation of earthworms.
Soil Biol. Biochem., 29: 251-257.
Chalasani, D., Krishna, S.R., Reddy, A.V.S. and Dutt, C. (1998). Vermiculture biotechnology
for promoting sustainable agriculture. Asia Pacific Journal of Rural Development., 8:
105-117.
Journal of Agricultural Technology 2012, Vol. 8(2): 403-415
413
Darwin, C. (1881). The formation of vegetable mould through the action of worms, with
observations on their habitats. Murray, London. 326 pp.
Decaens, T., Jimenez, J.J., Lavelle, P., Diaz-Cosin, D.J., Jesus, J.B., Trigo, D. and Garvin, M.
H. (1999). Effect of exclusion of the anecic earhtworm Martiodrilus carimaguensis
Jimenez and Moreno on soil properties and plant growth in grasslands of the eastern
plains of Colombia. 6th International Symposium on Earthworm Ecology, Vigo, Spain,
Pedobiologia., 43 (6): 835-841.
Doube, B.M., Schimdt, O., Killham, K. and Correll, R. (1997). Influence of mineral soil on the
palatability of organic matter for the lumbricid earhtworms: A simple food preference
study. Soil. Biol. Biochem., 29: 569-575.
Edwards, C.A. (1982). Production of earthworm protein for animal feed from potato waste. In:
Upgrading waste for feed and food. (Ledward, D. A., Taylor, A. J. and Lawrie, R. A.
eds.), Butterworths, London.
Edwards, C.A. (1988). Breakdown of animal, vegetable and industrial organic waste by
earhtworms. Agric. Ecosyst. Environ., 24: 21-31.
Edwards, C.A. and Bohlen, P.J. (1996). Biology and ecology of earthworm. (3rd edn.),
Chapman and Hall, London. 426 pp.
Edwards, C.A. and Lofty, J.R. (1972). Biology of earthworms. Chapman & Hall, London. 283 pp.
Edwards, C.A., Bohlen, P.J., Linden, D.R. and Subler, S. (1995). Earthworms in
agroecosystems. In: Earthworm Ecology and Biogeography in North America. (Hendrix,
P. F. eds.), Lewis Publisher, Boca Raton, FL, pp: 185-213.
El-Duweini, A.K. and Ghabbour, S.I. (1965). Population density and biomass of earthworms in
different types of Egyptian soils. J. Appl. Ecol., 2: 271-287.
Grant, W. C. 1955. Studies on moisture relationships in earthworms. Ecology., 36: 400-407.
Haynes, R.J., Fraser, P.M., Tregutha, R.J., Piercy, J.E., Diaz-Cosin, D.J., Jesus, J.B., Trigo, D.
and Garvin, M.H. (1999). Size and the activity of the microbial biomass and N, S and P
availability in earthworm casts derived from arable and pastoral soil amended with plant
residues. 6th International symposium on Earthworm Ecology., Vigo, Spain.
Pedobiologia., 43: 568-573.
Hoogerkamp, M., Rogaar, H. and Eijsackers, H.J.P. (1983). Effect of earthworms on grassland
on recently reclaimed polder soils in the Netherlands. In: Earthworm ecology, from
Darwin to Vermiculture. (Satchell, J. E. eds.), Chapman and Hall, London, pp: 85-105.
Ismail, S.A. (1993). Keynote Papers and Extended Abstracts. Congress on traditional sciences
and technologies of India, I.I.T., Mumbai. 10: 27-30.
Ismail, S.A. (1997). Vermicology: The Biology of Earthworms. Orient longman Press,
Hyderabad. 92 pp.
Ismail, S.A. (2005). The Earthworm Book. Other India Press, Mapusa, Goa. 101p.
Ismail, S.A., Seshadri, C.V., Jeeji Bai, N. and Surya Kumar, C.R. (1993). Composting through
earthworms. Monograph series, Volume 35. Shri AMM Murugappa Chettier Research
Centre, Chennai, 38pp.
Jairajpuri, M.S. (1993). Earthworms and vermiculture: an introduction. In: Earthworm
resources and vermiculture, ZSI, Kolkata, India. pp: 1-5.
Kale, R.D. (1998). Earthworm Cinderella of Organic Farming. Prism Book Pvt Ltd, Bangalore,
India. 88 pp.
Kale, R.D., Bano, K. and Krishnamoorthy, R.V. (1982). Potential of Perionyx excavatus for
utilising organic wastes. Pedobiologia., 23 : 419-425.
Krishnamoorthy, R.V. and Vajranabhaiah, S.N. (1986). Biological activity of earthworm casts:
An assessment of plant growth promoter levels in the casts. Proc. Indian Acad. Sci.(
Anim. Sci.)., 95: 341-351.
414
Kumar, A. (2005). Verms and Vermitechnology. Vedams eBooks (P) Ltd, New Delhi India. pp.
110-034.
Lachnicht, S.L. and Hendrix, P.F. (2001). Interaction of earthworm Diplocardia
mississippiensis (Megascolecidae) with microbial and nutrient dynamics in subtropical
Spodosol. Soil Biol. Biochem., 33: 1411-1417.
Lalitha, R., Fathima, K. and Ismail, S.A. (2000). Impact of biopesticides and microbial
fertilizers on productivity and growth of Abelmoschus esculentus. Vasundhara The
Earth., 1 & 2: 4-9.
Lavelle, P. (1992). Conservation of soil fertility in low-input agricultural systems of the humid
tropics by manipulating earthworm communities (macrofauna project). European
Economic Community Project No.TS2-0292-F (EDB).
Lavelle, P. and Martin, A. (1992). Small scale and large scale effects of endogeic earthworms
on soil organic matter dynamics in soil of the humid tropics. Soil Biol. Biochem., 24:
1491-1498.
Lee, K.E. (1983). The influence of earthworms and termites on soil nitrogen cycling. In: New
trends in Soil Biology. (Lebrun, P. H., Andre, H. M., de Medts, A., Gregoire-Wibo, C.
and Wathy, G. eds.), pp: 35-48.
Lee, K.E. (1985). Earthworms: Their ecology and relationships with soils and land use.
Academic Press, Sydney. 411 pp.
Lee, K. and Foster, R.C. (1991). Soil fauna and soil structure. Aust. J. Soil Res., 29: 745-776.
Livan, M.A and W. Thompson (1997). NARI Annual Report.
Martin, A. (1991). Short- and long-term effects of the endogeic earthworm Millsonia anomala
(Omodeo) (Megascolecidae, Oligochaeta) of tropical savannas on soil organic matter.
Biol. Fertil. Soils., 11: 234-238.
Muyima, N.Y.O., Reinecke, A.J. and Viljoen-Reinecke, S.A. (1994). Moisture requirements of
Dendrobaena veneta- a candidate for vermicomposting. Soil Biol. Biochem., 26: 973-
976.
Nooren, C.A.M., Van Breeman, N., Stoorvogel, J.J. and Jongmans, A.G. (1995). The role of
earthworms in the formation of sandy surface soils in a tropical forest in Ivory Coast.
Geoderma., 65: 135-148.
Olson, H.W. (1928). The earthworms of Ohio. Ohio Biol. Surv. Bull., 17: 47-90.
Piearce, T.G., Oates, K. and Carruthers, W.J. (1990). A fossil earthworm embryo (Oligochaeta)
from beneath a late bronze age midden at Potterna, Wiltshire, UK. J. Zool. Land., 220:
537-542.
Pramoth, A. (1995). Vermiwash-A potent bio-organic liquid “Ferticide”. M.Sc., dissertation,
University of Madras. 29 pp.
Reddy, M.V. and Pasha, M. (1993). Influence of rainfall, temperature and some soil
physicochemical variables on seasonal population structure and vertical distribution of
earthworms in two semi- and tropical grassland soils. Int. J. Biotech., 37: 19-26.
Satchell, J.E. (1983). Earthworm microbiology. In: Earthworm ecology: From Darwin to
Vermiculture. (Satchell, J. E. ed.), Chapman and Hall, London, UK. pp: 351-364.
Senapati, B.K. and Dash, M.C. (1982). Earthworms as waste conditioners. Indust. Eng. J., 11:
53-58.
Shipley, A.E. (1970). In: The Cambridge Natural History. (Harmer, S. F. and Shipley, A. E.
eds.). Codicote, England.
Shuster, W.D., Subler, S. and McCoy, E.L. (2000). Foraging by deep-burrowing earthworms
degrades surface soil structure of a fluventic Hapludoll in Ohio. Soil & Tillage
Research., 54: 179-189.
Journal of Agricultural Technology 2012, Vol. 8(2): 403-415
415
Staaf, H. (1987). Foliage litter turnover and earthworm populations in three beech forests of
contrasting soil and vegetation types. Oecologia., 72: 58-64.
Tomlin, A.D., Shipitalo, M.J., Edwards, W.M. and Protz, R. (1995). Earthworms and their
influence on soil structure and infilteration. In: Earthworm ecology and biogeography in
North America. (Hendrix, P.F. ed.), Lewis Publishers, Chelsea. pp: 159-184.
Valle, J.V., Moro, R.P., Garvin, M.H., Trigo, D. and Diaz Cosin, D.J. (1997). Annual dynamics
of the earthworms Hormogaster elisae (Oligochaeta, Hormogastridae) in Central Spain.
Soil Biol. Biochem., 29: 309-312.
Wood, T.G. (1974). The distribution of earthworms (Megascolecidae) in relation to soils,
vegetation and altitude on the slopes of Mt. Kosciusko, Australia. J. Anim. Ecol., 43:
87-106.
Zaller, J.G. and Arnone, J.A. (1999). The earthworms and soil moisture effects on the
productivity and structure of grassland communities. Soil Biol. Biochem., 31: 517-
523.
(Published in March 2012)