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Medicinal Plants and Threats to these Plants in and Around the Sariska National Park, Alwar, Rajasthan, India |
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Paper Id :
18678 Submission Date :
2024-04-05 Acceptance Date :
2024-04-21 Publication Date :
2024-04-25
This is an open-access research paper/article distributed under the terms of the Creative Commons Attribution 4.0 International, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited. DOI:10.5281/zenodo.11616871 For verification of this paper, please visit on
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Abstract |
The study of medicinal plants within Sariska National Park in
Alwar, Rajasthan, lean-tos light on the intricate relationships between
animals, humans, and plants. Many wild animals, including humans, consume
non-nutritional plants and nutrient-poor bark, yet little is understood about
their potential medicinal value and the reasons behind their consumption. In
recent years, there has been a growing interest in scientifically examining the
interactions between humans, animals, and plants in their natural environments.
Recent research on African great apes suggests that the ingestion of certain
non-nutritional plant species may help control parasite infections and
alleviate associated gastrointestinal issues. Moreover, local cultural
traditions regarding plant selection might be passed on when individuals of the
same species migrate from one group to another. |
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Keywords | Medicinal Plants, Threats Sariska National Park, Animals, Humans, Plants. | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Introduction | The fact that different animals and humans select the same
plant species, or species from related plant genera, strongly indicates a
shared criterion for medicinal plant selection. Furthermore, the observation
that animals and humans suffering from similar illnesses choose the same
medicinal plants offers insights into the evolution of medicinal behavior in
modern humans and the potential for self-medication among early hominids.
Specific self-medicative feeding behaviors, such as consuming repulsive plants,
feeding on gum, and geophagy (eating soil) in primates and other animal
species, suggest the presence of a robust mechanism linking different plant
parts and soil with common medicinal or functional properties. As a result, the
study of medicinal plants has become crucial in various fields, including
pharmacology, medical science, biodiversity conservation, and socio-economic
development. Understanding these interactions can inform research and
development efforts aimed at improving healthcare, managing natural resources,
and conserving biodiversity. |
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Objective of study |
The main objective of this research paper is to study the medicinal plants and threats to these plants in and around Sariska National Park, Alwar, Rajasthan, India. |
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Review of Literature | In addition to this, the number of persons entering forest collection was calculated during behavioural observations and phenological studies of langurs. Estimation of exotic species in the study area and their impact on native flora was estimated. To collect the information about the traditional ethnobotanical, ethnoveterinary and ethnomedical were collected from the villages in and around Sariska Tiger Reserve in Alwar district, Rajasthan, India. We were completed from 10 villages, 10 interview from each village. These random surveys were also undertaken during the study period of various survey and field visits during December, 2018 to December, 2023. |
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Methodology | Study Site: Sariska Tiger
Reserve is a tiger reserve in Alwar
district, Rajasthan, India. It stretches over an area of
881 km2 (340 sq mi) comprising scrub-thorn arid forests, dry deciduous forests, grasslands, and
rocky hills. This area was a hunting preserve of the Alwar state and was
declared a wildlife Sariska Tiger Reserve in 1958. It was given the status of a
tiger reserve making it a part of India's Project Tiger in
1978. The wildlife Sariska Tiger Reserve was declared a national park in 1982,
with a total area of about 273.8 km2 (105.7 sq mi).
Altitude varies from 900 to 3200 feet metric system above a level. Sariska is
characterized by distinct winter, summer and monsoon. During summer,
temperature fluctuates between 30 – 35oC, and reach may 48oC
during May and June. Mean winter temperature is 5oC, and may go down
to 2oC during December – January. The average annual rainfall is
about 825 mm; minimum 423 mm and maximum 950 mm. The forest is
broadly dry deciduous or woodland type dominated by dhawa (Anogeissus
pendula), ‘gorya dhawa’ (Anogeissus latifolia), salar (Boswellia
serrata), gol (Lannea coromandelica), kherni (Wrightia tinctoria),
kumbat (Acacia senegal), khair (Acacia catechu), ber (Zizyphus
mauritiana), dhonk (Butea monosperma). The undergrowth mainly
consists of jharber (Zizyphus nummularia), adusa (Adhatoda zeylanica),
gangan (Grewia tenex), franger (Grewia flavescens), kanter (Capparis
sepiaria), lantana (Lantana indicus). Some climbers and grasses are
also found. The main fauna of Sariska includes Tigers (Panthera
tigris), leopard (Panthera pardus), hyaena (Hyaena hyaena),
Indian Wolf (Canis lupus), Jackal (Canis aureus), Sloth bear (Melwisus
ursinus), Fourhorned antelope (Tetracerus quadricornis), Chinkara (Gazella
g. bennetti), Porcupine (Hystrix indica indica), Samber (Cervus
unicolor), Spotted dear (Axis axis), (Bluebull (Boselaphus
tragocamelus), Toddy cat (Paradoxurus hermaphroditus), Jungle cat (Felis
chaus), Fox (Vulpes bengalensis), Crocodile (Crocodylus palustris)
and Rock python (Python molurus). Methods: One or
two days in a month, sitting close to wood cutters’ route near the entrance of
the Sariska Tiger Reserve or forest, the number of men and women entering and
leaving with wood, grass, leaves, fruits, seeds, gum and other produce were
accounted for. |
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Result and Discussion |
Humans and
herbivores in and around Sariska Tiger Reserve, besides eating common food
plants also feed on certain unusual food items. This includes gum, bark, arial
roots, sand, licking of latex and rocks and chewing dry beehives and eating
repulsive alkaloid plants, etc. There were 10 plant species, which produces gum
in Sariska Tiger Reserve (Table 1). The maximum gum consumption and collection
was observed during March when 10 plant species which produce gum. Sand eating
by the birds and mammals were also observed in different protected and
unprotected areas of Rajasthan (Chhangani, 2000, Chhangani, 2004) Table 1: Gum
producing plants found in Sariska Tiger Reserve and consumption
Feeding on
repulsive plants: Wild animals were observed consuming parts of some repulsive species which
are avoided by most animals and livestock. These include Calotropis
procera, Lantana camara and Datura innoxia. In all
seasons, leaves flowers and unripe fruits of two shrubs Calotropis
procera and Lantana camara were eaten by langurs. During
monsoon months juvenile and adult langurs were observed to feed on leaves and
flowers of Datura innoxia. Role of food
plants in reproduction, milk production and self medication For example,
leaves of Acacia catechu and ripe and unripe fruits of Tamarindus
indica were frequently consumed in quantity by pregnant and infant
carrying langur females. Gum from 10 plant species was observed eaten by
langurs. It was found that gum feeding is slightly higher in pregnant langur
females before and after birth compared to other females. Similarly, langur
females carrying newborns eat more leaves of Butea monosperma,
Azadirachta indica, Ziziphus mauritiana, Wrightia tinctoria and
flowers and fruits of Bombex ceiba and Bauhinia
racemosa as compared to females without infants. Similar practice used
by local people and tribals around the Sariska Tiger Reserve, to increase the
milk yield of there livestock. They feed the same plant leaves to there
animals, which is collected from the forest regularly. Threats to
important flora of Sariska Tiger Reserve: Overgrazing: Overgrazing is the most serious
problem in the Sariska Tiger Reserve due to heavy pressure of livestock. Due to
unrestricted grazing the forest cover has degraded and ground cover is not
replenished in natural course. About 199800 animals, which includes 25000 cows,
18900 buffaloes, 90500 sheep, 5500 goats and 200 camels are living in and
around the Sariska Tiger Reserve. Besides this the regeneration and germination
of plants was highly effected due to regular grazing in the Sariska Tiger
Reserve, which leads to extension of important medicinal plants. Tree cutting: Food and feeding yielded data on
wood cutting in the study area. Out of these 16 tree species were felled by
people which are the food plants of wild animals and useful to humans for their
known important medicinal values. Wood cutters preferred species such as Acacia
senegal, Anogeissus pendula, A. latifolia, Albizia lebbeck, Acacia catechu,
Lannea coromandelica and Azadirachta indica, etc. Acacia
senegal was the single major tree species most commonly felled. It is
used mainly by temple mess for firewood. Out of 87 trees cut in the study area,
27.9% of them belongs to this species. This species is also used by animals and
humans year-round. Out of 16 tree species cut by woodcutters, 9 species of
trees were amongst the 10 top ranking food plant species and the product of
these trees are consumed by animals and humans year-round as their main food
source and medicinal use. Table:2. Tree
cutting and their uses by people in Sariska Tiger Reserve.
Exotic weed species:
Biotic pressure has resulted in the degradation of Sariska Tiger Reserve
Forest. Exotic weed species like Lantana (Lantana camara) and Vilayati
babul (Prospis juliflora) which invaded the forest area replacing native
species are blocking regeneration
of local flora
like Anogeissus latifolia,
A. pendula, Bauhinia racemosa, Boswellia serrata,
Ficus benghalensis, F.
racemosa, Ziziphus mauritiana,
Z. nummularia and
shrub species like Grewia
flavescens, G. tenex, Helicteres isora, Annona squamosa, etc. These species
constitute main food of domestic and wild animals in different seasons. Buffer
and part of core area is covered by Lantana camara and along the road side and
forest tracts by Prosopis juliflora, which is spreading with great speed. Forest fire: It
is damaging flora and fauna of
Sariska Tiger Reserve. Due to deciduous nature of forest leaf fall occurs in
December to February. Fires takes place during summer months after April.
Sporadic fires continue till June. These fires appear to be accidental. In
tribal areas however it may sometimes be caused by advasis themselves
during festivities of Bolma (Worship) in which they
offer Magara Pooja by burning forest area. The fires are also
caused due to negligence of right holders living inside the Sariska Tiger
Reserve. The heavy traffic between Sariska Tiger Reserve area is also the cause
of forest fires, because half burnt cigarettes and biris are
thrown along the roadside which often fall on the dry leaves and catch fire. In small-bodied
primates (such as Prosimians and Callitrichids), the ecological and
evolutionary significance of gum feeding has been considered in a number of
studies. (Martin, 1972; Charles – Dominique et al.
1979; Pitter, 1978; Hladik, 1979; Bearder and Martin, 1980 and Harcourt, 1986).
In Jodhpur gum ooz from the trunk of Prosopis juliflora was
frequently licked by langurs (Mohnot, 1974).
Bark eating was observed from seven plant species. The bark eating was
restricted during scarcity of food in summer months and droughts. But, some
times in the presence of predators when langurs cannot come down to ground and
move from one tree to another, they were observed to feed on stem bark. Whether
it was to release the stress or to over come the stress or in absence of normal
feeding they eat bark we do not know! Arial roots: Feeding on arial roots of two
ficus species, Ficus benghalensis and F.
racemosa was observed at Sariska Tiger Reserve. Similarly, a semi-stem
parasite Dendrophthoefalcata (host plant, Boswella
serrata) was observed eaten. It was for the first time we reported this
from Sariska Tiger Reserve. Feeding on arial roots were confined to summer and
monsoon months. During this period arial roots contain lot of water and some
quantity of carbohydrates. Langurs at Sariska Tiger Reserve were observed to
eat Calotropis procera in all seasons apparently without ill
effects. Such repulsive and evil smelling latex – bearing plants are avoided by
most animals and even insects but eaten by langurs. It is quite likely that
bacteria in the forestomach of langurs may reduce the toxic effect of chemicals
and alkaloids. Langurs therefore can consume alkaloid containing
food. In addition to unusual food habits many wild animals specially
Rhesus monkey and langurs lick rocks. This is probably to balance the
requirement of salts and minerals. Regular licking of rocks and hard earth from
termite mounts is commonwhich might help them to obtain requirements of salt
and minerals like calcium, mangesium and trace elements (for example copper);
for this purpose, it may have some special licking places. Vogel (1970, 1971) noted such earth licking in
Sariska and Kumaun hills. Latex
from food plants like, Ficus benghalensis,
Calotropis procera and Euphorbia caducifolia which
often sticks on langurs hands and other parts of the body when
former are busy plucking flowers, fruits or leaves. The latex stick to fingers
and nails and other parts of body was often licked by langurs. Role of food
plants in reproduction, milk production and medication It is difficult
to asses the food requirements of langurs of both sexes in nature and their
role in body physiology. In this study attempt was made to understand the role
of food plants in reproduction, milk production and medication by observing
them as to how much time they spend on particular plant part eaten by langur
males and females. By and large food requirements may vary in males and females
depending on their physical and physiological condition. It was observed that
adult males spent less time feeding as compared to adult females, because
females need to invest in reproduction and rearing of young ones. As such
requirements of non-pregnant females are different than pregnant females; a
fact emerged out in this study. The leaves of Azadirachta indica when
fed to cattle and camel with other feed increases the milk yield. In Andhra
Pradesh people regularly feed cattle and goats to increase milk production
immediately following parturition. A. indica leaves are
criminative and aid in digestion (Manjunath,
1948). It was found in this study that the local tribes of Aravalli
ranges also feed their cattle with A. indica leaves. Analysis
of mature leaves of various subspecies of A. indica includes
protein, fat, fiber, carbohydrates and minerals, calcium, phosphorous, iron,
thiamine, niacin, vitamin in different proportions. The above characteristics
suggest significance of A. indica leaves consumed by langur females
with infants probably to provide proper and rich nutrition to their upcoming
infants. Langur females with infants therefore feed more on leaves of Azadirachta
indica and Butca monosperma. Although in spite of the
availability of other plants and their leaves during the lactation period this
doesn’t attract females to feed on these species. Females with suckling infants
feed more on Butea monosperma and Azadirachta
indica leaves. Table.3: Plant
parts consumed by wild animals, livestock and humans in and around Sariska
Tiger Reserve and their known medicinal value.
Livestock: Like several national parks,
sanctuaries and closed areas, Sariska Tiger Reserve is facing
constant threat of livestock grazing, tree cutting, spread of weeds, forest
fires and at times floods besides road accidents. Of these, livestock pressure
is perhaps the most serious threat because of legal and illegal grazing. There
is a decline in ground foliage, bush and herb density due to overgrazing and
trimming off of tree canopy as a result of browsing by goats and camels. This
situation is common on the periphery of the Sariska Tiger Reserve. But, quite
often large herds of goat, sheep, cow and camel enter into core areas as well.
Their numbers often exceed 2 – 3 thousand at one time. This leads to
competition amongst the livestock and native wild fauna including langurs. The
livestock carry a variety of diseases with them to Sariska Tiger Reserve like,
foot and mouth, skin, viral, bacterial, protozoan and helminthes diseases.
These may spread in langurs and other wild animals. This threat is mounting
every day because of lack of control on livestock entry into the Sariska Tiger
Reserve and increasing numbers of animals available in and around the Sariska
Tiger Reserve. Tree cutting is a serious threat. The Sariska Tiger Reserve is
deprived of trees and its products, which are important for the endemic fauna
of Sariska Tiger Reserve including arboreal mammals. These trees provide food,
fodder, shelter and sleeping support to a large number of species of mammals
(Chhangani, 2002, in addition to nesting of birds. Weeds: The entry and spread of weeds in
any forest ecosystem or non-forest habitat is not uncommon. Sariska Tiger
Reserve is one such area loaded heavily by exotic weeds. These species are not
only degrading the ecosystem but are replacing the endemic plant species. The
two main exotic weed species which have entered Sariska Tiger Reserve in the
past 40 – 50 years are Lantana camara, a
shrub and Prosopis juliflora, a tree species. These remain green
year-round, grow fast and provide plenty of biomass. Prosopis provide
fodder, but leaves are unpalatable by wild animals. Only langurs eat them.
Langurs can eat every part of this plant and same is the case with
Lantana. Prosopis juliflora is available on the periphery of
the Sariska Tiger Reserve along with forest tracks and routes, but have not
reached in the core area. This species has spread in the Sariska Tiger Reserve
from livestock and its spread is limited to those areas where the livestock
could go for grazing. Lanatana is found in whole of the study
area including the home ranges of focal troops. The species was brought for
ornamental purposes and have now become a menace. Interestingly langurs eat all
parts of Lantana regularly without any ill effect while all
other wild animals and livestock avoid this bush. Forest
fire: It causes
serious damage to the young generation of tender plants which dies off while
resistant plants may survive like Butea monosperma, Acacia senegal,
Anogeissus pendula and A. latifolia. It causes tremendous
damage to ground cover and to shrubs which forms ideal habitat for wild
animals. Due to fire many animals like, insects, reptiles and birds are killed
and their eggs destroyed. However, it creates problem for ground dwellers
including langurs because of whipping out of forage species and loss of large
numbers of vertebrates, reptiles and mammals, particularly those which are
subterranean or burrowing in habits. A large number of bird nests and eggs were
destroyed in these fires, which create local imbalance of fauna and flora.
Similar observations of the forest fireswere also made in the Kumbhalgarh wildlife
sanctuary (Chhangani and Mohnot, 1997) Pesticides Threat to the Wildlife: Another potential threat which has been quite neglected by the wildlife researchers till date is pesticide contamination through the consumption of the pesticide contaminated food and water by both carnivores and herbivores animals. This aspect needs to be highlighted here is the pesticide contamination of the environment leading to the decline in the population of the animals especially by organochlorine pesticides (OCPs). Since many animals live in water and on shores and thrive on fishes and other aquatic animals therefore, they get exposed to OCPs because of bioconcentration and biomagnification of these xenobiotics. Here an example of bald eagle from USA needs to be considered. The bald eagle is the North American species with a historic range from Alaska and Canada to northern Mexico, is the national bird of the USA which has been an endangered species for many years. The reasons being the Habitat destruction and degradation, illegal shooting, and the contamination of its food source, because of DDT contamination, there is a decline in the eagle population, The banning of DDT by the Federal government of USA and related pesticides, habitat protection done by the Endangered Species Act, and conservation actions taken by the general American public have helped bald eagles to survive. Nevertheless DDT and its residues contaminated nearby water areas, where aquatic plants and fish absorbed it and biomagnified it . Bald eagles, in turn, were poisoned with DDT as and when they consumed the contaminated fish. As a consequence, their eggs had shells so thin that they usually broke during incubation or otherwise failed to hatch at all. DDT contamination and its residues also affected other species such as peregrine falcons and brown pelicans. Many Other pesticides having the same structure as DDT are suspected to have caused increased death, in addition to the harmful effects on reproduction. By 1963, with only 417 nesting pairs of bald eagles existing, the species was facing the danger of extinction. At the time, a controversial step of banning the use of DDT and some related pesticides in the United States was taken by the federal government of the USA. That was in 1972, and it was the first step on the road to recovery for the bald eagle (U.S. Fish & Wildlife Service Migratory Bird Program, February 2021). This shows how dangerous DDT contamination is how disastrous it can be for the avian fauna. More scary studies have indicated that we have largely over looked the darker side of these chemicals as OCPs are reported to be carcinogenic (Mathur et al, 2002 &Ingber et al 2013) mutagenic (Ingber et al 2013&Yaduvanshi et al 2012) teratogenic (Yaduvanshi et al 2012 & ATSDR. Atlanta, GA.1994) immunosuppressive (Repetto. R & Baliga. S.S, 1997 &Corsinia et al, 2003) create endocrine dysfunction such as hypothyroidism or high estrogenic activity (Dewailly et al, 2000 & Rathore et al, 2002) disturb reproductive processes (Pant et al ,2007 & Tiemann.U. 2008) growth depressants (Colborn et al, 1993&Mercier. M, 1981) induces several psychogenic and neurogenic abnormalities in adult stages (Mactutus & Tilson, 1986 & Van Wendel de Jood et al,2001) and are associated with abortions, premature deliveries, still births and infants with low birth weights (Saxena et al, 1981; Saxena et al, 1980; Tyagi et al 2015; Chen. Q et al 2014 & Sharma & Bhatnagar, 1996). OCPs have been in use in India nearly for a half century now. Even after having clear cut evidence suggesting that these chemicals have the ability to eliminate entire species from the planet, the annual consumption of pesticides in India is about 85,000 tons of which OCPs comprise the bulk (India Environment Portal Knowledge for change, 30/10/1998.). Therefore, today OCPs are perhaps the most ubiquitous of the potentially harmful chemicals encountered in the environment and are still widely detected in humans despite the considerable decline in environmental concentrations (Dewan et al. 2003). This kind of environmental Contamination with organochlorine pesticides (OCPs) has also been reported by Sharma and her coworkers in 1996 from Jaipur City. She reported contamination of human samples like mothers’ blood, cord blood, placenta and mothers’ milk with OCPs. Presence of pesticides with OCPs shows that how these xenobiotics have contaminated our Mother Nature and now faunal diversity is facing danger of existence and Smooth-coated Otters is not staying away from this potential danger. It can be concluded that the magnitude of pollution is quantitatively enough to contaminate the food and environment and reaching out to all faunal diversity. |
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Conclusion |
It can be concluded that the magnitude of pollution is
quantitatively enough to contaminate the food and environment and the pesticides
reach the human body through various sources mainly by absorption form the
gastrointestinal tract through contaminated food chain, are circulated in
blood, stored milk and secreted during lactation resulting in sufficient
neonatal intake. The battle against the harmful insects would be much less
costly and more efficient, and the problem of contamination of the environment
by toxic materials would be vastly reduced, if insect activities are controlled
by natural means. The use of pest-specific predators; parasites or pathogens;
sterilization of insects with the help of radiations; trapping insects using
insect attractants like pheromones; use of juvenile hormones or hormone
inhibitors may therefore be suggested as alternate ways of pest control
(Sharma, 1996; 2021a; 2021b;2021c;2021d), Sharma & Bhatnagar, 1996 &
2017; Sharma and Singh. (2021). |
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References | 1. Agency for Toxic Substances and Diseases Registry (ATSDR)/US Public Health Service, Toxicological Profile for 4,4'-DDT, 4,4'-DDE, 4, 4'-DDD (Update). ATSDR. Atlanta, GA.1994. 2. Bearder, S.K. and Martin, R.D. 1980. Acacia gum and its use by lesser bushbabies, Galago senegalensis (Primates : Lorisidae). Int. J. Primatol., 1 : 102 – 28. 3. Charls –Dominique, P. and Bearder, S.K. 1979. Field Studies of Lorisid Behaviour : The lorisids of Gabon: The Galagines of South Africa. In The Study of Prosimain Behaviour. Pp. 567 – 629. (Ed. by G.A. Doyle and R.D. Martin), Academic Press, New York. 4. Chen.Q., Zheng.T., Bassig.B., Cheng.Y., Leaderer.B., Lin.S., Holford.T., Qiu.J., Zhang.Y., Shi.K., Zhu.Y., Niu.J., Li.Y., Guo.Y.H., Huand.X and Jin.Y.(2014): Prenatal Exposure to Polycyclic Aromatic Hydrocarbons and Birth Weight in China,” Open Journal of Air Pollution, vol.3, pp. 100-110. 5. Chhangani, A.K. (2002). Food and feeding of sloth bear (Melursus ursinus) in Aravalli Hills of Rajasthan, India: Tigerpaper, 29 (2): 1-6. 6. Chhangani, A.K. (2004). Geophagy by three species of crows near carcuss dumping ground at Jodhpur, Rajasthan. Newsletter for Ornithologists, 1(5): 71-72. 7. Chhangani, A.K. 2000. Ecobehavioural diversity of langurs, Presbytis entellus living in different ecosystems. Ph.d. Thesis, J.N.V. Univ., Jodhpur. 8. Chhangani, A.K. and Mohnot, S.M. (1997). Kumbhalgarh Wildlife Sanctuary under stress. Abstract-National Symposium on Public Participation in Environmental Protection. 22-23 December 1997. P. 15. 9. Chhangani, A.K; Pandey, R.P. and Mohnot, S.M. (2002). Consumption of different plant parts by wild Hanuman langur and their known medicinal practice by local people in the Aravallis of Rajasthan, India. Journal of Economic and Taxonomic Botany, 26(2): 419-439. 10. Colborn.T., Vom Saal. F.S., Soto A.M (1993): Developmental Effects of Endocrine-Disrupting Chemicals in Wildlife and Human,” Environ. Health. Perspect, vol. 101, no. 5, pp.378-384, October. 11. Corsinia. E., Sokootib. M., Gallia. C.L., Morettoc.A and Colosiob. C. (2013): Pesticide induced immunotoxicity in humans: A comprehensive review of the existing evidence,Toxicology. vol. 307, pp. 123–135, May. 12. Dewailly. E., Ayotte. P., Bruneau. S., Gingras. S., Belles-Isles. M and Roy. R. (2000): Susceptibility to infections and immune status in Inuit infants exposed to organochlorines, Environ Health Perspect., vol.108, no.3, 205–211, March. 13. Dewan, P., Jain, V., Gupta, P., & Banerjee, B. D. (2013). Organochlorine pesticide residues in maternal blood, cord blood, placenta, and breastmilk and their relation to birth size. Chemosphere, 90(5), 1704-1710. 14. Hartcurt, C. 1986. Seasonal variation in the diet of South African Galagos. Internat. J. Primatol., 7 : 491 – 506. 15. Hladik, C.M. 1979. Diet and Ecology of Prosimians. In The Study of Prosimian Behaviour, (Ed. by G.A. Doyla and R.D. Martin), Pp. 307 – 357. New York, Academic Press. 16. India Environment Portal Knowledge for change, 30/10/1998. 17. Ingber, S.Z., Buser, M.C., Pohl, H.R., Abadin, H.G., Murray, H.E., Scinicariello. F. (2013): DDT/DDE and breast cancer: a meta-analysis. Regul Toxicol Pharmacol., vol. 67, no. 3, pp. 421-33. 18. Jaipur, ISBN no:978-81-953150-7-9 in the edition, page no-171-182, March 2021. 19. Mactutus, C.F and Tilson, H.A (1986): Psychogenic and neurogenic abnormalities after perinatal insecticide exposure. In: Hand book of behavioral teratology. Ed. by Edward, P.R. and Charles, V.V. Plenum Press, NY, 335-91. 20. Manjunath, B.L. 1948. The Wealth of India. A Dictionary of Indian Raw Materials and Industrial Products. Vol. 1. CSIR, New Delhi. 21. Martin, R.D. 1972. Adaptive radiation and behaviour of the Malagary lemurs. Phil. Trans. Royal Soc. London. 264 : 295 – 352. 22. Mathur, V., Bhatnagar, P., Sharma, R. G., Acharya, V., & Sexana, R. (2002): Breast cancer incidence and exposure to pesticides among women originating from Jaipur. Environment international, 28(5), 331-336. 23. Mercier. M (1981): Criteria (Dose Effect Relationships) for Organochlorine Pesticides Report, Published for the Committee of the European Communities by Pergamon Press. 24. Mohnot, S.M. 1974. Ecology and Behaviour of the Common Indian Langur, Presbytis entellus. Ph.D. thesis, Univ. of Jodhpur, Jodhpur. 25. Pant.N., Kumar.R., Mathur.N., Srivastava.S.P.,Saxena. D.K and Gujrati.V.R.(2007): Chlorinated pesticide concentration in semen of fertile and infertile men and correlation with sperm quality” Environ Toxicol and Pharmacol., vol. 23, no. 2, pp. 135–139, March. 26. Rathore. M., Bhatnagar. P., Mathur. D and Saxena. G.N. (2002): Burden of organochlorine pesticides in blood and its effect on thyroid hormones in women,” Sci Total Environ., vol. 295, no. 1–3, pp. 207–215, August. 27. Repetto. R and Baliga. S.S. (1997): Pesticides and Immunosuppression: The Risks to Public Health,” Health Policy Plan., vol. 12, no. 2, pp.97-106. 28. Saxena, M.C., Siddiqui, M.K.J., Bhargava, A.K., Seth, T.D., Krishnamurti, C.R and Kutty, D. (1980): Role of chlorinated hydrocarbon pesticides in abortions and premature labour. Toxicology. 17. 323-31 29. Saxena, M.C., Siddiqui, M.K.J., Seth, T.D and Krishnamurti, C.R. (1981): Organochlorine pesticides in specimens from women undergoing abortion, premature and full-term delivery. J. of Anal. Toxicol.5, Jan/ Feb. 30. Sharma, M and Singh. (2021). Organochlorine Pesticides in Human Milk: A Recap.” in an International Journal of Current Trends in Engineering & Technology-IJCTET Vol-7, Issue-3, 29-41. 31. Sharma, M. & Bhatnagar, P. (2017). Pesticide burden in women from Jaipur in relation to ethnicity, religion and addiction habit. International Journal of Environmental Science and Development, Vol. 8, No. 3, 216-220. 32. Sharma, M. (2021 a). Pesticide Residues in Drinking Water and Cattle Milk. High Time to find an alternative to Chlorinated Hydrocarbons” in a journal of Innovative Research in Clinical and Medical Sciences (JIRCMS), Vol-5, Issue-1, 1-6. 33. Sharma, M. (2021b) Organochlorine Pesticides in Cord Blood: A Threat to the Safety of Prenates. Journal of Innovative Research in Clinical & Medical Sciences. Vol.4, (4), 6-16. 34. Sharma, M. (2021c) Organochlorine Pesticides in Human Placenta: A Threat for Prenates. Journal of Innovative Research in Clinical & Medical Sciences. Vol.05, (2) ,1-11. 35. Sharma, M. (2021d) Organochlorine Pesticides in Human Milk: A Source of toxicants for Neonates, research article for a book on science and technology entitled “Emerging Trends in Science and Technology” Edited by Dr. M.K. Kumawat & Dr. N. Singh. IISN No-978-81-951982-2-1 by Bhumi Publishing, Nigave Khalasa, Kolhapur 416207, Maharashtra, India, 2021. 36. Sharma, M., & Bhatnagar, P. (1996). Organochlorine pesticides and preterm labour in human beings. Current Science, Vol. 71, No. 8, pp. 628-631. 37. Sharma. M. (1996). Transplacental movement of pesticides in women from Jaipur. Ph.D. thesis submitted to department of Zoology, University of Rajasthan, Jaipur, Rajasthan, India. 38. Tiemann.U. (2008): In vivo and in vitro effects of the organochlorine pesticides DDT, TCPM, methoxychlor, and lindane on the female reproductive tract of mammals: A review, Reproductive Toxicology., vol.25, no. 3, pp. 316–326, April. 39. Tyagi.V., Garg.N., Mustafa. M.D., Banerjee, B.D and Guleria. K. (2015): Organochlorine pesticide levels in maternal blood and placental tissue with reference to preterm birth: A recent trend in North Indian population, Environ Monit Assess., vol.187, no. 7, pp. 471, July. 40. U.S. Fish & Wildlife Service Migratory Bird Program 5275 Leesburg Pike, MS: MB Falls Church, VA 22041 703/358-1714 www.fws.gov/birds/ February 2021 41. Van Wendel de Joode.B., Wesseling.C., Kromhout.H., Monge. P., García. M and Mergler. D. (2001): Chronic nervous-system effects of long-term occupational exposure to DDT, Lancet, vol. 357, no. 9261, pp. 1014–1016, March. 42. Vogel, C. 1971. Behavioural differences of Presbytis entellus in two different habitats. In Proc. 3rd Internat. Cong. Primatol., pp. 41 – 47, Zurich. 43. Yaduvanshi. S.K, Srivastava. N, F. Marotta. F, S. Jain. S and H. Yadav. H. (2012): Evaluation of micronuclei induction capacity and mutagenicity of organochlorine and organophosphate pesticides, Drug Metab Lett., vol. 6, no. 3, pp. 187-97. |