Department of Horticulture & Food Processing, Uttar Pradesh UTTAR PRADESH.
Molluscicides from some common medicinal plants of eastern Uttar Pradesh, India
-
Upload
sunil-kumar-singh -
Category
Documents
-
view
222 -
download
4
Transcript of Molluscicides from some common medicinal plants of eastern Uttar Pradesh, India
J. Appl. Toxicol. 2010; 30: 1–7 Copyright © 2009 John Wiley & Sons, Ltd.
Review
Received 4 June 2009, Revised 8 October 2009, Accepted 13 October 2009, Published online in Wiley InterScience: 27 November 2009
(www.interscience.wiley.com) DOI 10.1002/jat.1498
Molluscicides from some common medicinal plants of eastern Uttar Pradesh, India
Sunil Kumar Singh, Ram P. Yadav and Ajay Singha*
ABSTRACT: Many aquatic snails act as intermediate hosts for the larvae of trematodes, Fasciola hepatica and Fasciola gigan-tica, which cause the diseases fascioliasis and schistosomiasis. The WHO has tested several thousands of synthetic compounds for the control of the snail host. Although eff ective, these molluscicides have so far not proved themselves to be entirely satisfactory. With a growing awareness of environmental pollution, eff orts are being made to discover molluscicidal products of plant origin. Being products of biosynthesis, these are potentially biodegradable in nature. Several groups of compounds present in various plants have been found to be toxic to target organisms at acceptable doses ranging from <1 to 100 ppm. Common medicinal plants, i.e. Thevetia peruviana, Alstonia scholaris (Family; Apocynaceae), Euphorbia pulcherima and Euphorbia hirta (Family; Euphorbiaceae), have potent molluscicidal activity against freshwater snails. The toxicological actions of Thevetia peruviana may be due to the presence of apigenin-5-methyl ether (fl avonoid) and triterpenoid glycosides, while a number of alkaloids (pseudo-akuammigine in addition to betulin, ursolic acid and β-sitosterol), steroids and triterpenoids are present in Alstonia scholaris and the diterpenoids, pulcherrol, β-sitosterol, hentriacontane, ellagic acid and β-amyrin are present in Euphorbia hirta and in Euphorbia pulcherima. Although, at present very little literature is available on the control of vector snails through plant origin pesticides, an attempt has been made in this review to assemble all the known informa-tion on molluscicidal properties of common medicinal plants of eastern Uttar Pradesh, India, which might be useful for the control of harmful snails. Copyright © 2009 John Wiley & Sons, Ltd.
Keywords: molluscicides; snail; Thevetia peruviana; Alstonia scholaris; Euphorbia pulcherima; Euphorbia hirta
*Correspondence to: A. Singh, Department of Zoology, DDU Gorakhpur University,
Gorakhpur 273 009 (U.P.), India.
E-mail: singhajay_gkp@rediff mail.com
aDepartment of Zoology, DDU Gorakhpur University, Gorakhpur 273 009
(UP), India
INTRODUCTION
Molluscs comprise the second largest group of invertebrate
animals, although the exact number of existing mollusc species
is still a matter of speculation. Abbott (1954) has estimated a total
of about 110 000 living species, 80 000 of which are gastropods,
10 000 bivalves and 5000 belong to the other three classes of
mollusk. Godan (1983), on the other hand, believes the number
of living species to be about 120 000.
Terrestrial snails and slugs cause considerable damage to both
cultivated and useful non-cultivated plants. These animals can
make their appearance in any damp areas; snails also cause con-
siderable damage to vegetable gardens, agriculture crops and
fruit orchards. Singh and Agarwal (1981) reported that Pila
globosa, an amphibious snail, causes damage to paddy crops in
the northern part of India. The larvae of parasite trematodes also
pass part of their life in fresh water. Many aquatic snails act as
vectors for the larvae of trematodes and thereby cause a number
of diseases. Schistosomiasis is caused by Schistosoma. It is a
devastat ing disease of mankind second only to malaria in its
deleterious eff ect (Lambert, 1966; Jobin, 1973). Fascioliasis is
caused by Fasciola hepatica, the large liver fl uke, common in
sheep, cattle, goat and other herbivorous ani mals throughout
the world. Froyed (1975) reported that about 21% cattle and 7%
sheep were infected with liver fl uke in Great Britain. In India, the
freshwater snails Lymnaea acuminata and Indoplanorbis exustus
are the intermediate hosts of Fasciola hepatica and Fasciola
gigantica (Hyman, 1970), which cause immense harm to domes-
tic animals of this country (Singh and Agarwal, 1981; Singh, 2000;
Singh et al., 2000, 2004a, b, 2005, 2009; Yadav and Singh, 2001,
2002, 2006, 2007; Yadav et al., 2002, 2005, 2006, 2009; Singh and
Singh, 2003a–c).
The best method of controlling both diseases such as schis-
tosomiasis and fascioliasis is chemotherapy, using orally admin-
istered drugs for individuals with moderate or severe level of
infection. The disadvantage of this approach is that it does not
eliminate the infection entirely, the cost of recurrent treatment
may become prohibitive and drug resistance may become a
problem. A better way to tackle the problem of schistosomiasis
and fascioliasis is destroy the carrier snails and remove an essen-
tial link in the life cycle of the fl ukes. This can be accom plished in
a number of ways, including the use of many synthetic or plant
molluscicides (Agarwal and Singh, 1988; Singh and Agarwal,
1988a; Singh et al., 1996).
SYNTHETIC MOLLUSCICIDE
Godan (1983) and Agarwal and Singh (1988) reviewed the various
types of synthetic molluscicides available for the control of snails.
The major synthetic molluscicides are metaldehyde, niclosamide,
1
S. K. Singh et al.
www.interscience.wiley.com/journal/jat Copyright © 2009 John Wiley & Sons, Ltd. J. Appl. Toxicol. 2010; 30: 1–7
carbamate, organophosphate and synthetic pyrethroids. Singh
and Agarwal (1988b) suggested that Lymnaea acuminata, which
is very fast breeder throughout the year, may be possibly be
controlled through chemo sterilization.
The molluscicidal eff ects of metaldehyde have been found
to depend to a great extent on the ambient temperature and
humidity. Moens (1970) established the relationship between
toxicity and temperature for slugs, and demonstrated that the
toxicity of metaldehyde increased with a rise in temperature.
The carbamate pesticides which are currently being used for the
control of various species of gastropods pests are carbaryl (Barry,
1969; Brar and Simwat, 1973), mexacarbamate (Barry, 1969), aldi-
carb (Judge, 1969; Brar and Simwat, 1973) and isolan (Daxl, 1971).
The organophosphorus compound is powerful inhibitors of
cholinesterase and is therefore similar to carbamates in their
mode of action. Unlike carbamate, however, the inhibition
caused by most of these compounds is irreversible (Koelle, 1975;
O’Brien, 1976; Taylor, 1980). Synthetic pyrethroid, a synthetic ana-
logue of pyrethrum, which is extracted from several species of
chrysanthemum plants, has no lethal eff ect on terrestrial snails
while Sahay et al. (1991) reported the toxicity of three synthetic
pyrethroids (cypermethrin, fenvalerate and deltamethrin) singly
and with the synergist piperonyl butoxide against freshwater
snails Lymnaea acuminata and Indoplanorbis exustus. Pyrethroids
primarily act on the nerve membrane by changing its permeabil-
ity to Na+ and K+. This causes repetitive discharges of nerves at
the synapses and neuromuscular junctions (Wilkinson, 1976;
Narahashi, 1983).
The use of synthetic or petroleum-based molluscicides for con-
trolling of snails and other target organisms causes serious envi-
ronmental pollution (Redinger, 1976; Mian and Mulla, 1992; Dua
et al., 1998; Susan et al., 1999; Waliszewski et al., 1999). To over-
come the problem, basic research for over 50 years in biology
and biochemistry has made it possible to envisage not only how
new pesticides may be synthesized, but also a completely new
approach to the control of vectors using secondary plant prod-
ucts which may be toxic to a specifi c vector yet harmless to
non-target organisms. In recent years, considerable attention
has been directed to the research and application of mollusci-
cides, insecticides, larvicides and insect growth regulators of
juvenile hormone analogs in protection of human beings and
their domestic animals. These substances have been used suc-
cessfully on large scale in vector management programmes
(Srivastava et al., 2003).
PLANT ORIGIN MOLLUSCICIDE
In recent times, the use of plant products has gained unprece-
dented impetus all over the world. The people of the northeast-
ern region of India, in particular the rural and tribal people living
in some remote areas, primarily depend upon folk and traditional
medicine, and indigenous knowledge of how these plants are
used for diff erent purposes in diff erent areas. A large number of
plant families have furnished many classes of product, which may
vary in the degree of pesticidal activity. Several countries have
promoted the use of plant products due to their wide range of
ideal properties, such as high target toxicity, low mammalian
toxicity, low cost, solubility in water, easy bio-degradability,
abundant growth in endemic areas and operator safety (Kinghorn
and Evans, 1975; Marston and Hostettmann, 1985; Singh et al.,
1996; Singh et al., 2000)
The above-mentioned properties of plant products have
opened up a new vista. India possesses a rich biodiversity of
medicinal plants that are used for many purposes. The plant
products (as well as extracts) have been used from time imme-
morial. The Vrikshayurveda is the branch of Ayurveda that deals
with plant health and recommends drugs possessing specifi c
qualities of treatment for insect attack. During the co-evolution
of plants and insects, plants have bio-synthesized a number of
secondary metabolites to serve as defense chemicals against
pest attack. Although only 10 000 secondary metabolites have
been chemically identifi ed so far, the total number may exceed
400 000 (Swain, 1977).
Snails exposed to latex of Euphorbia roylea na plant of family
euphorbiaceae exhibited typical symptoms of nerve poisoning
and death took place within 24 h. It was shown that the latex was
an acetylcho linesterase inhibitor and its anti-AChE activity in the
snail Lymnaea acuminata was very high in comparison to any
synthetic organic pesticides (Singh and Agarwal, 1984a). In
another study, Singh and Agarwal (1984b) also observed that the
latex of Euphorbia royleana reduced the level of 5-hydrodxy-trypt-
amine (5-HT) and dopamine in the nervous tissues of Lymnaea
acuminata. Singh and Agarwal (1992a) reported that the latexes
of several euphorbious plants signifi cantly reduced the alkaline
and acid phosphatase activity in nerve tissue of Lymnaea acumi-
nata. Cheng (1971) and Amin (1972) have recorded the mollusci-
cidal properties of Thea oleso sa, Croton tiglium, Sehima argenta
and Jatropha spp. Adewunmi and Morquis (1980) studied the
molluscicidal properties of methanolic extracts of the fruit of
Jatropha gossypifolia and Jatropha podagrica.
Pharmacological action of Croton tiglium is due to the pres-
ence of alkaloids (Rizk, 1987). The alkaloids are naturally occur-
ring organic bases, which contain at least one nitrogen atom
either in the heterocyclic ring or linked to an aliphatic skele ton.
They are found in vascular plants and rarely occur in gymno-
sperms cryptogams and monocotyledons. Okunji and Iwu (1988)
screened several plants of diff erent families for molluscicidal
properties and suggested that the toxic properties of these
plants may be due to the presence of alkaloids. Toxicity in
Codiaeum spp. is due to the presence of tanin in the latex (Wealth
of India, 1985). Tanin are complex phenolic compounds, divided
into two groups: (i) the hydrolysable tanins, which are esters of
garlic acid and also glycosides of these esters; and (ii) the con-
densed tanins, which are polymers derived from various fl avo-
noids. The molluscicidal activity was found to be related to the
free phenolic groups of the tanins. Ayoub and Yankov (1986)
screened several tanin-bearing plants of diff erent families for
their molluscicidal activity. On assumption was made by him,
that the molluscicidal activity of the tanin-bearing plants is pro-
portional to the amount of tanin present in the various morpho-
logical parts.
Several species of family euphorbiaceae, which contain diter-
penes, show molluscicidal properties. Those with known mol-
luscicidal properties are Euphorbia royleana, E. antisyphilitica,
E. lacteal acristata, E. pulcherima, E. neutra, Jatropha gossypifolia,
Croton tiglium and Codiaeum variegatum (Singh and Agarwal,
1984a, b, 1988a, b, 1990, 1991, 1992a, b; Singh, 1991, 2000; Singh
and Singh, 2003a–c, 2005; Singh et al., 2004a–c, 2009; Yadav,
2000; Yadav and Singh, 2001, 2002, 2003, 2007; Yadav et al., 2005,
2006, 2009). Recent work has demonstrated that the toxicologi-
cal actions of the latex can be attributed to a new class of
diterpenes, which are esters of phorbol (12-deoxyphorbol,
12-deoxy-16-hydroxy-phorbol, ingenol, 5-deoxy-ingenol, resinif-2
Molluscicides from some common medicinal plants
J. Appl. Toxicol. 2010; 30: 1–7 Copyright © 2009 John Wiley & Sons, Ltd. www.interscience.wiley.com/journal/jat
erotoxin and tinyatoxin; Kinghorn and Evans, 1975). It has been
reported that phorbol esters interact with and activate the
recently discovered protein kinase-C (Takai et al., 1977).
The medicinal plant Euphorbia pulcherima is useful for a variety
of conditions, such as rheumatism, snakebite, asthma, obstipa-
tion and skin diseases (Vlietink, 1987), while Euphorbia hirta is
also used in cough, asthma, colic, dysentery and genito-urinary
diseases (Wealth of India, 1985; Jain, 1996; Bhatnagar et al., 2000).
Singh and Singh (2005) reported that both the plants have
potent molluscicidal activity against the snails Lymnaea acumi-
nata and Indoplanorbis exustus (Table 2).
Thevetia peruviana and Alstonia scholaris are common medi-
cinal plants of the family apocynaceae. The latex of Thevetia
peruviana is used in tooth cavities for relief from toothache and
the latex of Alstonia scholaris is applied to ulcers, sores, tumors
and rheumatic pain, and is used for curing toothache (Rama
Rao, 1967). Both the plants have potent molluscicidal and anti-
cholinesterase activity against harmful snails and slugs (Panigrahi
and Raut, 1994; Singh et al., 2000, 2004b, 2009; Singh and Singh,
2003a). The toxicological actions of Thevetia peruviana may be
due to the presence of apigenin-5-methyl ether (fl avonoid) and
triterpenoid glycosides (Voigtlander and Balsam, 1970) while a
number of alkaloids (pseudo-akuammigine in addition to betulin,
ursolic acid and β-sitosterol), steroids and triterpenoids are
present in Alstonia scholaris (Banerji and Banerji, 1977).
ACTIVE COMPOUNDS IN PLANTS
Plants are the richest source of renewable bioactive organic
chemicals. The total number of plant chemicals may exceed
400 000; of these, 10 000 are secondary metabolites whose major
role in the plants is reportedly defensive (Swain, 1977; Cooper
and Johnson, 1984). Numerous defensive chemicals belonging
to various categories (terpenoids, alkaloids, glycosides, phenols,
tannins, etc.) that cause behavioral and physiological eff ects on
pests have already been identifi ed. Some important compounds
are as given below.
Saponins
Saponins are naturally occurring plant glycosides, which form a
soapy lather with water. They consist of a sugar moiety and an
aglycone unit. Monodesmosidic saponins (sugar moiety only at
position C-3) possess toxic activity whereas bidesmosidic sapo-
nins (sugar moiety both at C-3 and C-28) are inactive. There is a
high correlation between plants employed as fi sh poisons or
soap substances and their molluscicidal activity. Phytolacca
dodecandra (Phytolaccaceae) is an example of such a plant. The
molluscicidal activity of its berries was fi rst noticed by Lemma
(1965) in Ethiopia. It was found that stretches of the river where
Table 1. Comparison of toxic potentials of some synthetic and plant origin molluscicides
Molluscicides Molluscicidal activity mg L−1
(LC50) with in hour
Snails References
SyntheticMexacarbate 3.5/24 h Lymnaea acuminata Singh and Agarwal (1981)Aldicarb 30/24 h L. acuminata Singh and Agarwal (1981)Carbaryl 14.4/96 h L. acuminata Singh and Agarwal (1981)Formothion 27/24 h L. acuminata Singh and Agarwal (1981)Phorate 15/96 h L. acuminata Singh and Agarwal (1981)Trichlorofon 14.4/96 h L. acuminata Singh and Agarwal (1981)Niclosamide 11.8/24 h L. acuminata Singh and Agarwal (1984a)Cypermethrin 0.8/24 h L. acuminata Singh and Agarwal (1986)Permethrin 0.73/24 h L. acuminata Singh and Agarwal (1986)Fenvalerate 2.5/24 h L. acuminata Sahay et al. (1991)Deltamethrin 0.57/24 h L. acuminata Sahay et al. (1991)
PlantNerium indicum (Latex) 0.118/24 h L. acuminata Singh et al. (1993)Euphorbia royleana (Latex) 0.125/24 h L. acuminata Singh and Agarwal (1988a)E. antisyphlitca (Latex) 0.120/24 h L. acuminata Singh and Agarwal (1988a)E. lactea cristata (Latex) 0.118/24 h L. acuminata Singh and Agarwal (1988a)Jatropha gossypifolia (Latex) 0.200/24 h L. acuminata Singh and Agarwal (1988a)Thevetia peruviana (Latex) 0.43/24 h L. acuminata Singh and Singh (2005)Alstonia scholaris (Latex) 4.76/24 h L. acuminata Singh and Singh (2005)Euphorbia pulcherima (Latex) 0.09/24 h L. acuminata Singh and Singh (2005)Euphorbia hirta (Latex) 1.29/24 h L. acuminata Singh et al. (2004a)Anacardium occidentale (Trine) 0.35/24 h Biomphalaria glabrata Sullivan et al. (1982)Anacardium occidentale (Dine) 0.9/24 h B. glabrata Sullivan et al. (1982)Anacardium occidentale (Monoene) 1.4/24 h B. glabrata Sullivan et al. (1982)Ambrosia maritima 10–14/24 ha B. alexandra Shoeb and El-Eman (1978)
B. truncatus Shoeb and El-Eman (1978)Podachaenum emineus 1/24 h B. glabrata Fronczek et al. (1984)
aLC100 dose.
3
S. K. Singh et al.
www.interscience.wiley.com/journal/jat Copyright © 2009 John Wiley & Sons, Ltd. J. Appl. Toxicol. 2010; 30: 1–7
Table 2. Toxicity (LC50) of aqueous latex, stem bark and leaf extracts of Thevetia peruviana, Alstonia scholaris, Euphorbia pulcherima
and Euphorbia hirta plants against freshwater harmful snails Lymnaea acuminata and Indoplanorbis exustus at diff erent time
intervals
Plant Plant parts Exposure periods (LC50, mg L−1) Snails References
Thevetia
peruviana
Latex 24 h 0.43 L. acuminata Singh (2000); Singh et al. (2000, 2004b,
2009); Singh and Singh (2003a, c, 2005)96 h 0.1724 h 0.38 I. exustus96 h 0.16
Stem bark 24 h 691.91 L. acuminata96 h 165.5324 h 350.46 I. exustus96 h 95.88
Leaf 24 h 272.51 L. acuminata96 h 58.7824 h 250.00 I. exustus96 h 73.00
Alstonia
scholaris
Latex 24 h 4.76 L. acuminata Singh (2000); Singh et al. (2000, 2004b,
2009); Singh and Singh (2003a, c, 2005)96 h 1.7624 h 2.36 I. exustus96 h 0.98
Stem bark 24 h 665.82 L. acuminata96 h 138.3224 h 263.58 I. exustus96 h 53.62
Leaf 24 h 940.45 L. acuminata96 h 485.0624 h 750.00 I. exustus96 h 281.23
Euphorbia
pulcherima
Latex 24 h 0.09 L. acuminata Singh and Singh (2003b, d, 2005);
Singh et al. (2004a, c)96 h 0.0224 h 0.06 I. exustus96 h 0.02
Stem bark 24 h 91.35 L. acuminata96 h 23.0624 h 89.02 I. exustus96 h 16.36
Leaf 24 h 138.23 L. acuminata96 h 38.8824 h 102.12 I. exustus96 h 39.31
Euphorbia
hirta
Latex 24 h 1.29 L. acuminata Singh and Singh (2003d, 2005);
Singh et al. (2004a, c, 2005)96 h 0.5924 h 0.97 I. exustus96 h 0.34
Stem bark 24 h 102.41 L. acuminata96 h 39.9724 h 120.75 I. exustus96 h 28.45
Leaf 24 h 122.09 L. acuminata96 h 44.3624 h 108.372 I. exustus96 h 2.094
Molluscicides from some common medicinal plants
J. Appl. Toxicol. 2010; 30: 1–7 Copyright © 2009 John Wiley & Sons, Ltd. www.interscience.wiley.com/journal/jat
these berries were used for washing cloths were remarkably free
of snails. Based on this observation, a fi ve-year pilot snail control
program was launched in Ethiopia which resulted in a signifi cant
reduction in the incidence of Schistosoma mansoni infection. The
compounds responsible for the molluscicidal activity were found
to be triterpenoid saponins, with LC100 values as low as 2 ppm
(Hostettmann et al., 1982).
Alkaloids
Alkaloids are naturally occurring organic bases, which contain at
least one nitrogen atom either in the hetrocyclic ring or linked to
an aliphatic skeleton. They are usually colorless, crystalline, non-
volatile solids, slightly soluble in water but soluble in ethanol,
ether and chloroform. Alkaloids have been isolated from the
seeds, roots, leaves and bark of the stem. In the leaves of some
species they constitute 0.5–8% of the dry weight. They are stored
in the vacuoles or in the cytoplasm in a solid form (Srivastava,
1991).
A quinolizene alkaloid virgilin, isolated from the leaves of
Calpurnia aurea (Mimosaceae), kills 100% of Biomphalaria gla-
brata at 130 ppm, within 48 h. Vieira and Kubo (1990) reported
four quinoline alkaloids from dichloromethane extracts of
Galipea bracteata. Out of the quinoline caused 100% mortalities
of snail B. glabrata.
Flavonoids
The term fl avonoids embraces all compounds whose structure is
based on fl avone. Flavonoids are C15 compounds (exclusive of
O-alkyl groups and secondary substituents), which are com-
posed of two phenolic nuclei connected by three Carbon unit.
Dossaji and Kubo (1980) reported that the leaves of Polygonum
senegalense have a known fl avonoid quercetin. This compound
possesses signifi cant molluscicidal activity at 10 ppm, causing
100% mortality of three species of snails, Lymnaea natalensis,
Biomphalaria peiff eri and B. glabrata within 24 h. Likewise, a
eupatorin compound isolated from the plant Baccharis timera
killed 100% of B. glabrata at 100 ppm, but other fl avone glyco-
sides from Asparagus plumosus was found to be completely
harmless to snails (Marston and Hostettmann, 1985).
Diterpeneoids
The diterpenoids form a group of compounds having general
molecular formula C20H32. They are not steam volatile and are
usually obtained from plants. A new class of diterpenes which are
esters of phorbol (12-deoxyphorbol, 12-deoxy-16 hydroxy-
phorbol, ingenol, 5-deoxy-ingenol resiniferotoxin and tinyatoxin)
possess highly toxic activity against pests. Cheng (1971) and
Amin (1972) have recorded the molluscicidal properties of Thea
olesosa, Croton tiglium, Schima argenta and Jatropha spp.
Adewunmi and Morquis (1980) studied the molluscicidal proper-
ties of methanolic extracts of the fruit of J. podagrica. The extracts
of these plants were found to be very active against the snail
Bulinus globosus.
Singh and Agarwal (1991, 1992a, b) reported that the aqueous
extracts of Euphorbia lactea cristata, E. royleana, E. antisyphlitica
and Jatropha gossypifolia are lethal to the snails Lymnaea acumi-
nata and Indoplanorbis exustus. The order of toxicity at all the
exposure periods ranging from 24 to 96 h in the case of L. acumi-
nata was E. lactea cristata > E. antisyphlitica > E. royleana >
J. gossypifolia. In the case of I. exustus, however the order of
toxicity was E. royleana > E. antisyphlitica > E. lacteal cristata >
J. gossypifolia.
In order to assess the toxicity of the euphorbiales to other
animals sharing the ecosystem with the snails, toxicological
experiments were carried out on the fi sh Colisa fasciatus. The
results demonstrated that the lattices were indeed lethal to
fi shes but at doses much higher than the dose required for killing
snails.
Monoterpenoids
Monoterpenoids are made up of two isoprene units (C10H16) and
are the chief constituents of essential oils. Molluscicidal activity
of thymol, carvacrol and limonene from plants of the genus
Lippia, has been briefl y reported against Biomphalaria glabrata
(Marston and Hostettmann, 1985).
Sesquiterpenes Lactones
Sesquiterpenoid lactones are those compounds, which possess
a sesquiterpene skeleton having an additional lactone ring.
These are present essentially in the leaves and fl owering head,
but rarely in the stem and roots of the family Compositae. Up to
now 21 sesquiterpene lactones, mainly pseudoguaianolides and
norsesquiterpenes, have been identifi ed in the leaves, fl owers
and seeds of Ambrosia maritima. This plant is a herbaceous weed,
which is widely distributed over the Mediterranean region of
Africa.
There is much variation in the susceptibility of diff erent snail
species to Ambrosia maritima. LC50 doses of dried leaves of A.
maritima against the snails Bulinus foskalli, B. globosus, B. pfeiff eri
and Lymnaea natalensis were 165, 149, 227 and 108 ppm, res-
pectively (Belot et al., 1991). The alcoholic extracts of the leaves
of this plant, however, are more potent because of the miscibility
of alcohol in water. Thus, the LC50 of the ethanol extracts of
dried leaves of A. maritima against the snails Bulinus foskalli,
Biomphalaria pfeiff eri and Lymnaea natalensis was 62, 87 and
42 ppm, respectively, expressed in terms of dried leaves (Belot
et al., 1991).
Tannins
Tannins are complex phenolic compounds which can be divided
into two groups: (i) the hydrolysable tannins, which are esters of
gallic acid and also glycosides of these esters; and (ii) the con-
densed tannins, which are polymers derived from various fl avo-
noids. Methanolic and aqueous extracts of 12 tannin-containing
plants against the snail Biomphalaria glabrata have been studied:
Quercus spp. (Fagaceae), Camellia spp. (Theaceae) (black tea and
green tea), Hamamelis virginiana (Hamammelidaceae), Potentilla
erecta (Rosaceae), Alchemilla ssp. (Rosaceae), Acaccia catechu
(Mimosaceae), Dalbergia nitidula (Mimosaceae), Krameria trian-
dra (Krameriaceae), Eucalyptus spp. (Myrtaceae), Arctostaphylos
uva-ursi (Ericaceae) and Cinchona succirubra (Rubiaceae). As mol-
luscicides, extracts of Krameria triandra and Arctostaphylos uva-
ursi are the most eff ective as they cause 100% kill at concentrations
as low as 50 ppm. The methanolic extracts of these exhibit even
stronger molluscicidal activity than the aqueous extracts
(Schaufelberger and Hostettmann, 1983). 5
S. K. Singh et al.
www.interscience.wiley.com/journal/jat Copyright © 2009 John Wiley & Sons, Ltd. J. Appl. Toxicol. 2010; 30: 1–7
CONCLUSION
There are a very large number of plants, which contain com-
pounds lethal to target as well as non-target organism at doses
which are much below those for synthetic pesticides (Amusan
et al., 1997; Schall et al., 1988; Marston et al., 1996; Singh et al.,
1996, 2000, 2004b, c, 2005, 2009; Singh, 1991; Singh and Singh,
2003a–c; Yadav and Singh, 2001, 2006, 2007; Yadav et al., 2005,
2006, 2009). Use of such products has the additional advantage
that they contain biodegradable compounds, which are less
likely to cause environmental contamination. After all, such com-
pounds are not only confi ned to the plants in which they are
found, but are also possibly distributed in the environment. We
feel strongly that if these herbaceous products were used as mol-
luscicides they would not only control the vector snail but they
would also have the advantage of easy availability, low cost,
biodegradability and greater acceptance amongst users.
Furthermore, we feel that, with further progress in biotechnol-
ogy, such products could be raised form sources other than those
plants in which they are currently found. Production of plant
pesticides could, in long run also become an important industry
using biotechnological methods.
Further studies are ongoing on these plants to elaborate the
activity of their constituents. There are many plant uses men-
tioned in Ayurveda that may form the basis of further studies.
Acknowledgments
One of the authors (Sunil Kumar Singh) is thankful to Ministry of
Science and Technology, Department of Science and Technology,
New Delhi, Government of India, for the award of the SERC ‘Fast
Track’ Young Scientist Fellowship (no. SR/FT/L-44/2006 dated 18
June 2007) for fi nancial assistance.
REFERENCES
Abbott RT. 1954. The Marine Mollusks of Grand Cayman Island. Mono-graphs of the Academy of Natural Science: Philadelphi, PA.
Adewunmi CO, Morquis VO. 1980. Molluscicidal evaluation of some Jat-ropha species. J Crude Drug Res. 18: 141–145.
Agawaral RA, Singh DK, 1998. Harmful gastropods and their control. Acta Hydrochim. Hydrobid. 16: 113–138.
Amin MA, 1972. Preliminary on the molluscicidal properties of Habit El-Mollok, Jatropha sp. Trans. R. Soc. Trop. Med. Hyg. 66: 805–806.
Amusan OOG, Msonthi JD, Makhuba LP. 1997. Molluscicidal activity of Urginia epigea. Fitot 68: 185–186.
Ayoub SMH, Yankov LK. 1986. The molluscicidal factor of tannin-bearing plants. Int. J. Crude Drug Res. 24: 16–18.
Banerji A, Banerji J. 1977. Isolation of Pseudo-akuammigin from the leaves of Alstonia scholaris R.Br. Indian J. Chem. 15(B): 390–391.
Barry BD. 1969. Evaluation of chemicals for control of slugs on fi eld corn in Ohio. J. Econ. Entomol. 62: 1277–1279.
Belot J, Bornarel P, Diouf M, Polderman AM. 1991. Ambrosia maritima L. molluscicidal eff ects on the land snails Lymnaea natalensis, Bulinus forskalii, Bulinus globosus and Biomphalaria pfeiff eri from Senegal. Plant Sci. 74: 167–170.
Bhatnagar VP, Anil K, Srivastava, JN. 2000. Wild medicinal herbs of Agra. J. Med. Arom. Plant Sci. 22(4A)–23(1A): 464–467.
Brar HS, Simwat GS. 1973. Control of the common slugs Laevicaulis alte Ferussae (Gastrpoda), with certain chemicals. J. Res. Punjab Agric. Univ. 10: 99–101.
Cheng TH, 1971. Schostosomiasis in mainland China: A review of research and control programme since 1949. Am. J. Trop. Med. Hyg. 20: 26–53.
Cooper MR, Johnson AW. 1984. Reference Book 161. Ministry of Agricul-ture, Fisheries and Food: London.
Daxl R. 1971. The behaviour of the molluscicidal compounds metalde-hyde, isolan and ioxynil against slugs in fi eld conditions. Z. Angew. Zool. 58: 203–241.
Dossaji S, Kubo I 1980. Quercetin 3-(2′′-galloyl glycoside), a molluscicidal fl avonoid from Polygonum senegalense. Phytochemistry 19: 482.
Dua VK, Pant CS, Sharma VP, Pathak GK. 1998. Determination of HCH and DDT in fi nger-prick whole blood dried on fi lter papers and its fi eld application for monitoring concentrations in blood. Bull. Environ. Contam. Toxicol. 56: 50–57.
Fronczek FR, Vargas d, Fischer NH, Hostettmann K. 1984. The molecular structure of 7-alpha-hydroxy-3-desoxy-zaluzanin-c a molluscicidal sequiterpene lactone. J. Nat. Prod. 47: 1036.
Froyed G. 1975. Liver fl uke in Great Britain: a survey of aff ected livers. Vet. Res. 97: 492–495.
Godan D. 1983. Pests, Slugs and Snails, Biology and Control. Springer: Berlin.Hostettmann K, Kizu H. Tomimori T. 1982. Molluscicidal properties of
various saponins. Planta Med. 44: 34–35.Hyman LH. 1970. The Invertebrate. Vol. VI. Mollusca I. McGraw–Hill, New
York.Jain SK. 1996. Medicinal Plants, 6th edn. National Book Trust: New Delhi.Jobin WR. 1973. Environmental control of bilharzia snail in small reservoir.
J. Irrig. Drain Div. 99: 365–373.Judge FD. 1969. Preliminary screening of candidate molluscicides. J. Econ.
Entomol. 62: 1393–1397.Kinghorn AD, Evans FJ. 1975. A Biological screen of selected species of the
genus Euphorbia for skin irritant eff ects. Planta Med. 28: 325–335.Koelle GB. 1975. Neurohumoral transmission and the autonomic nervous
system anticholinesterase agents. In The Pharmacological basis of Therapeutics, 8th edn, Gilman AG, Rall TW, Nies AS, Taylor P (eds.). Pergamon Press: New York.
Lambert CR. 1966. Bilharziasis. CIBA Symposium, Vol. 14; 3–14.Lemma A. 1965. A preliminary report on the molluscicidal properties of
Endod (Phytolacca dodecandra). Ethiopian Med. J. 3: 187–190.Marston A, Hostettmann K. 1985. Plant molluscicides. Phytochemistry 24:
639–652.Marston A, Dudan G, Gupta MP, Sois PN, Correa MD, Hostettman K. 1996.
Screening of Panamanian plants for molluscicidal activity. Int. J. Phar-macol. 34: 15–18.
Mian LS, Mulla MS. 1992. Eff ects of pyrethroid insecticides on non-target invertebrates in aquatic ecosystem. J. Agric. Entomol. 9(2): 73–98.
Moens R. 1970. Techniques chimiques de destruction edes gites a Limnees dans les prairies. College d information, scient., l’assainissement des per les traitemenes molluscicides gembloux. Center Rech. Argon 32–55.
Narahashi T. 1983. Pesticide Chemistry: Human Welfare and rhe Environ-ment, Miyamoto J, Kearney PC (eds). Pergamon Press: New York.
Okunji CO, Iwu MM. 1988. Control of schistosomiasis using Nigerian medicinal plants as molluscicides. Int. J. Crude Drug Res. 26: 246–252.
O’Brien RD. 1976. Acetylcholinesterase and its inhibition. In Insecticide Biochemistry and Physiology, Wilkinson CF (eds). Plenum Press: New York; 271–273.
Panigrahi A, Raut SK. 1994. Thevetia peruviana (family: Apocynaceae) in the control of slug and snail pests. Mem. Ins. Oswaldo Cruz Rio de Jan. 89(2): 247.
Rama Rao. 1967. Poisonous Plants of India, Vol. IA. ICAR: New Delhi; 201.Redinger RF. 1976. Organochlorine residues in adults of six South-
Western bat species. J. Wil. Li Mana 40: 677–680.Rizk 1987. The chemical constituents and economic plants of the euphor-
biaceae. Bot. J. Linean Soc. 94: 293–326.Sahay N, Singh DK, Agarwal RA. 1991. Synergistic eff ect of piperonyl
butoxide on the toxicity of synthetic pyrethroids in the snail Lymnaea acuminata. J. Med. Appl. Malacol. 3: 107–111.
Schall VT, Vasconcellos MC, Souza CP, Baptista DF. 1988. The molluscicidal activity of crown of Christ (Euphorbia spelendens var, hisloppi) latex on snails acting as intermediate hosts of Schistosoma mansoni and Schistosoma haemotobium. J. Trop. Med. Hyg. 58: 7–10.
Schaufelberger D, Hostettmann K. 1983. On the molluscicidal activity of tannin containing plants. Planta Med. 48: 105–107.
Shoeb HA, El-Emam MA. 1978. Proceedings of International Conference on Schistosomiasis, Cairo;1975.
Singh A. 1991. Molluscicides of plant origin against harmful snails. PhD thesis, Gorakhpur University, Gorakhpur (UP), India.
Singh A, Agarwal RA. 1988a. Possibility of using latex of euphorbiales for snail control. Sci. Total Environ. 77: 231–236.
6
Molluscicides from some common medicinal plants
J. Appl. Toxicol. 2010; 30: 1–7 Copyright © 2009 John Wiley & Sons, Ltd. www.interscience.wiley.com/journal/jat
Singh A, Agarwal RA. 1990. Molluscicidal properties of synthetic pyre-throids. J. Med. Appl. Malacol. 2: 141–144.
Singh A, Agarwal RA. 1991. Kinetics of acetylcholinesterase inhibition by the latex of euphorbiales in the snail Lymnaea acuminata. J. Med. Appl. Malacol. 3: 101–105.
Singh A, Agarwal RA. 1992a. Toxicity of the latex of euphorbiales. Eff ect on acid and alkaline phosphatase of the snail Lymnaea acuminata. Biol. Agric. Hortic. 8: 211–219.
Singh A, Agarwal RA. 1992b. Molluscicidal activity of euphorbiales against the snails Indoplanorbis exustus. Acta Hydrochim. Hydrobiol. 20: 262–264.
Singh A, Singh SK. 2005. Molluscicidal evaluation of three common plant species of India. Fitot 76: 747–751.
Singh A, Singh DK, Mishra TN, Agarwal RA. 1996. Molluscicides of plant origin. Biol. Agric. Hortic. 13: 205–252.
Singh DK, Agarwal RA. 1984a. Correlation of the anticholinesterase and molluscicidal activity of the latex of Euphorbia royleana Bloss. on Lymnaea acuminata. J. Nat. Prod. 47: 702–705.
Singh DK, Agarwal RA. 1984b. Alteration of biogenic amine level in the snail Lymnaea acuminata by the latex of Euphorbia royleana. Toxicol. Lett. 21: 309–314.
Singh DK, Agarwal RA. 1986. Synergistic eff ect of sulfoxide with carbaryl on in vivo acetylchlonesterase activity and carbohydrate netabolism of snail Lymnaea acuminata. Acta Hydrochim. Hydrobiol. 14: 421–427.
Singh DK, Singh A, Agarwal RA. 1993. Nerium indicum as potent mollus-cicides of plant origin. J. Med. Appl. Malacol. 5: 93–95.
Singh O, Agarwal RA. 1981. Toxicity of certain pesticides to two economic species of snails in northern India. J. Econ. Entomol. 74: 568–571.
Singh SK. 2000. Studies on molluscicidal properties of some local plants of eastern Uttar Pradesh against harmful snails. PhD thesis, DDU Gora-khpur University, Gorakhpur (UP), India.
Singh SK, Agarwal RA. 1988b. Eff ect of eyestalk ablation on oviposition in the snail Lymnaea acuminata. Veliger 30(3): 291–294.
Singh SK, Singh A. 2003a. Toxic eff ect of Thevetia peruviana and Alstonia scholaris lattices on the freshwater snail Lymnaea acuminata. Iberus 21(2): 19–27.
Singh SK, Singh A. 2003b. Molluscicidal and anti-cholinesterase activity of diff erent solvent extracts of stem bark and leaf of Euphorbia pulcherima against freshwater harmful snail. First National and Inter-national Meeting on Medicinal and Aromatic Plants; 337–344.
Singh SK, Singh A. 2003c. Eff ect of the plants Thevetia peruviana and Alstonia scholaris (Family: Apocynaceae) on Acetylcholinesterase activity of Lymnaea acuminata snails. Egypt. J. Schis. Infect. End. Dis. 25: 31–40.
Singh SK, Singh A. 2003d. Molluscicidal activity of Euphorbia hirta plant against freshwater vector snails. Proceedings of National Symposium on Biochemical Science: Health and Environ Aspects; 290–294.
Singh SK, Yadav RP, Singh A. 2000. Molluscicidal activity of Thevetia peru-viana a common medicinal plant of India. J. Med. Arom. Plant Sci. 22(4A)–23(1A): 113–116.
Singh SK, Yadav RP, Singh D, Singh A. 2004a. Toxic eff ect of two common Euphorbiales lattices on the freshwater snail Lymnaea acuminata. Environ. Toxicol. Pharmacol. 15: 87–93.
Singh SK, Yadav RP, Singh D, Singh A. 2004b. Toxicological eff ects of stem bark of Thevetia peruviana and Alstonia scholaris on the freshwater snail Lymnaea acuminata. Malaysian Appl. Biol. 33(1): 61–68.
Singh SK, Yadav RP, Singh A. 2004c. Molluscicidal activity of diff erent organic solvent latex extracts of some common euphorbiales against freshwater harmful snails. J. Sci. Islamic Repub. Iran 15(1): 59–63.
Singh SK, Yadav RP, Tiwari S, Singh A. 2005. Toxic eff ect of stem bark and leaf of Euphorbia hirta plant against freshwater vector snail Lymnaea acuminata. Chemosphere 59(2): 263–270.
Singh SK, Yadav RP, Singh A. 2009. The toxicity of Thevetia peruviana and Alstonia scholaris plants to target and non-target aquatic organism. Proceedings of the Symposium on Functional Biodynamics and Ecophys-iology of Animals; 301–307.
Srivastava HS, 1991. Elements of Biochemistry, 3rd edn. Rastogi Publica-tions: Meerut.
Srivastava VK. Singh SK. Rai M. Singh A. 2003. Toxicity of Nerium indicum and Euphorbia royleana lattices against Culex quinquefasciatus mos-quito larvae. Nigerian J. Med. Nat. Prod. 7L 61–64.
Sullivan JT, Richards CS, Lioyed HA, Krishna G. 1982. Anacardic acid: mol-luscicide in cashew nut shell liquid. Planta Med. 44: 175–177.
Susan T, Anita Veeraiah K, Tilak KS. 1999. A study on the bioaccumulation of fenvalerate a synthetic pyrethroid, in the whole body tissue of Labeo rohita, Catla catla, Cirrhinus mrigala (Ham.) by gas–liquid chro-matography. Pollut. Res. 18(1): 57–59.
Swain T. 1977. Secondary plant compounds as protective agents: A. Annu. Rev. Plant Physiol. 28: 479–501.
Takai Y. Kishimoto A. Inoue Y. Nishizuku Y. 1977. Studies on a cyclic nucleo-tide independent protein kinase and its proenzyme in mammalian tissues i.e. purifi cation and characterization of an active enzyme from bovine cerebellum. J. Biol. Chem. 252: 7610–7616.
Taylor P. 1980. Anticholinesterase agents. In Pharmacological Basis of Therapeutics, Goodman AS, Milan AG, Roll TW, Murad F (eds); Mac-millan: New York; 110–129.
Vieira PC, Kubo I. 1990. Molluscicidal quinoline alkaloids from Galipea bracteata. Phytochemistry 29: 813–815.
Vlietink KJ. 1987. Biologically Active Substances from Traditional Drug Bio-logically Active Natural Product, Hostettmann K, Lea PJ (eds). Macmil-lan: New York.
Voigtlander HW, Balsam G. 1970. Apigenin 5-methyl ether, ein neues Flavon aus, Thevetia peruviana. Arch. Pharmacol. (Weinheim) 303: 792.
Waliszewski SM, Aguirre AA, Benitez A, Infanzon RM, Infazon R, Rivera J. 1999. Organo-pesticides residues in Human blood serum of inhabit-ants of Veracuz, Mexico. Bull. Environ. Contam. Toxicol. 62: 397–402.
Wealth of India. 1985. Publications and Information Directorate, CSIR: New Delhi; 201–204.
Wilkinson CG. 1976. Insecticide Biochemistry and Physiology. Plenum Press: New York.
Yadav RP. 2000. Studies on molluscicidal properties of some common plants of family Euphorbiceae and their environmental impact on non-target organism. PhD thesis DDU Gorakhpur University, Gorakh-pur, UP, India.
Yadav RP, Singh A. 2001. Environmentally safe molluscicides from two common euphorbiales. Iberus 19(2): 65–73.
Yadav RP, Singh A. 2002. Toxic eff ect of latex of Croton tiglium on Lymnaea acuminata and Channa punctatus. Iberus 20(2): 33–45.
Yadav RP, Singh A. 2003. Eff ect of sub-lethal concentrations of Codiaeum variegatum, latex on freshwater target snail Lymnaea acuminata non-target fi sh Channa punctatus. Nigerian J. Nat. Prod. Med. 7: 20–24.
Yadav RP, Singh A. 2006. Toxic eff ects of Jatropha gossypifolia and its binary and tertiary combinations with other plant molluscicides in natural ponds. Iberus 24(2): 47–54.
Yadav RP, Singh A. 2007. Toxic eff ects of Euphorbials on freshwater snail Lymnaea acuminata in ponds. J. Herb. Spice Med. Plants 13(2): 87–94.
Yadav RP, Singh SK, Singh A. 2002. Molluscicidal activity of Codiaeum variegatum, eff ect on snail metabolism. J. Ecophys. Occup. Health 2: 74–84.
Yadav RP, Tiwari S, Singh A. 2005. Toxic eff ects of taraxerol extracted from Codiaeum variegatum stem bark on target vector snail Lymnaea acu-minata and non-target fi sh. Iberus 23(1): 1–13.
Yadav RP, Singh D, Singh SK, Singh A. 2006. Toxic eff ect of stem bark of Croton tiglium on metabolism of freshwater snail Lymnaea acuminata. American Malacol. Bull. 21: 87–92.
Yadav RP, Singh SK, Singh A. 2009. Toxic eff ects of euphorbious plants against freshwater vector snails in ponds. Proceedings of the Symposium on Functional Biodynamics and Ecophysics of Animals; 293–300.
7