Is Industrial Fluoride Pollution Harmful to Agricultural Crops? Farmers Need to Know
Shanti Lal Choubisa1,2*
1Department of Advanced Science and Technology, National Institute of Medical Science and Research, NIMS University Rajasthan, India
2Department of Zoology, Government Meera Girls College, India
*Corresponding author:Shanti Lal Choubisa, Department of Advanced Science and Technology, National Institute of Medical Science and Research, NIMS University Rajasthan, India
Submission:
June 14, 2023; Published: July 21, 2023
Industrialization is more important for running and strengthening the economic system of any country. But there are many industries that also emit fluoride along with other toxic gases, causing fluoride pollution. Due to this, not only air, soil, and water but also herbage, vegetation and agricultural crops get contaminated with fluoride. Among these industries, coal-burning power stations and brick kilns and the manufacture or production plants of steel, iron, aluminum, zinc, phosphorus, chemical fertilizers, glass, plastics, cement, oil refineries, etc. are the most common sources of fluoride pollution. Fluoride is released from these sources into the surrounding environment in both gaseous and particulate or dust forms. Studies have revealed that chronic exposure to this industrial fluoride is unsafe or harmful to agricultural crops and produces a variety of toxic effects. In fact, industrial fluoride enters crop plants mainly through the stomata of the leaves. However, it can also enter through the root in fluoride-contaminated soil. The bioaccumulation of fluoride in plants disturbs their morphological, physiological, and biochemical parameters. The persistence of fluoride bioaccumulation in crop plants adversely affects their photosynthesis, respiration, mineral nutrition, fertilization, germination, growth and development, bio-chemical processes, and agricultural productivity. The most common visible pathognomonic symptoms of industrial fluoride poisoning in crop plants have been found to be stunted growth (dwarfism), chlorosis, necrosis, abscission of leaves, flowers, and fruits, and decreased seed production. Once plants develop necrotic spots on their leaves, the damage cannot be reversed by any treatment. But most of the farmers are not aware of these side effects on crops or the economic loss caused by industrial fluoride emissions. The current communication focuses on whether industrial fluoride pollution is harmful for the health of agricultural crops. Simultaneously, research gaps are also highlighted for further research work on industrial fluoride toxicity in diverse agricultural crops.
Fluoride is found naturally in almost every ecosystem or environment with varying concentrations [1,2]. However, its presence in water and air is more important for the health of humans and domestic animals. It is clear from several research studies that repeated exposure to fluoride from any medium or source over a long period of time is unsafe and extremely harmful not only to humans [3-7] and domestic animals [8-13] but also to various agricultural crops [14-22]. However, chronic fluoride poisoning (fluorosis) in humans [23-32] and various species of domestic animals [33-55] through drinking fluoridated water has been more widely studied worldwide. In various agricultural crops, chronic fluoride poisoning or toxicity due to chronic exposure of fluoride through industrial fluoride pollution and fluoridated water has also been studied by many workers [14-22]. The current communication focuses on whether industrial fluoride pollution is unsafe or harmful for the health of agricultural crops. Along with this, research gaps have also been highlighted for further research work on the industrial fluoride-induced toxic effects on diverse species of agricultural crops.
It is a well-known fact that industrialization is more important than ever run and strengthen the economic system of any country. That is why every country pays special attention to
industrialization. But it is also true that, due to industrialization in
one way or another, our ecosystem or environment is also suffering
a lot of damage. Due to this, not only the health of humans and
animals but also agricultural production is deeply affected. The
main reason for this is the air and water pollution caused by them.
But most people do not know that there are many factories or
industries running around us that emit fluoride along with other
toxic gases in the environment, causing fluoride pollution. Due
to this, not only air, soil, and water but also herbage, vegetation,
and agricultural feed and crops get contaminated with fluoride.
Among these industries, coal-burning power stations and brick
kilns and the manufacture or production of steel, iron, aluminum,
zinc, phosphorus, chemical fertilizers, glass, plastics, cement, oil
refineries, and hydrofluoric acid plants or unites are common
sources of industrial fluoride pollution [1] (Figure 1). However,
coal-fired brick kilns are the commonest and main source of
industrial fluoride pollution in rural areas [11,12] and these are
mostly established on or near agricultural land or fields (Figure
2). These industrial sources or activities release fluoride into the
surrounding environment in both gaseous and particulate or dust
forms. However, the spread of fluoride pollution is more dependent
on wind direction and its velocity.
Figure 1:Potential sources of industrial fluoride pollution. Atomic power stations (Fig a) and cement plants
operating in or near various agriculture crops (Figs b-d).
Figure 2:Fluoride pollution from coal-burning brick-kilns operating in or near various agricultural crops.
Yes, industrial fluoride has the potential to harm a variety
of agricultural crops. This has been proven by several studies
conducted on a variety of agricultural crops [14-22]. In fact,
industrial fluoride contaminates not only crop plants but also
agriculture soil and freshwater ecosystems. Therefore, fluoride can
enter plants through two main routes. First, air-borne deposition of
gaseous fluoride due to industrial fluoride pollution occurs through
stomatal diffusion. Through leaf stomata, fluoride penetrates the
cell wall and migrates to the margins and tips of leaves, which
are the sites of greatest volatilization [56]. The second route is
through a passive diffusion process in the roots of plants in fluoride
contaminated soil and fresh water. Fluoride is subsequently
transported through the xylem via-apoplastic and simplistic
pathways in a directional distal movement to the shoot [57]. In fact,
fluoride moves into the transpiration stream from the roots and/
or through the stomata, where it eventually accumulates in the leaf
margins. Generally, fluoride accumulation follows the order of soil
> root > shoot > grain. The bio-availability of fluoride to plants is
mainly influenced by the presence of metal ions such as calcium
(Ca), aluminum (L), and phosphorus (P), the pH of the solution, and
the type of soil [58].
Repeated or chronic industrial fluoride exposure for long period
of time and its persistence bioaccumulation produces diverse
adverse toxic effects in both seasonal and off-season agricultural
crops, vegetables, and trees [14,17,20]. In fact, bioaccumulation
of fluoride in different parts of plants disturbs or causes adverse
changes in various physico-biochemical or metabolic processes
and ultimately triggers the development of various side effects or
ill effects. Ultimately, these effects reduce the annual productivity
or yield and harvest index of the agricultural crop.
The most common and earliest visible morphological changes
induced by fluoride in crop plants are stunted growth (dwarfism
syndrome), necrotic lesions or necrosis, chlorosis, abscission of
leaves, flowers, and fruits, leaf damage, tip burning, and curling
of leaves that spread inward (Figures 3 & 4) [14,20]. Once plants
develop necrotic spots on their leaves, the damage cannot be
reversed by any treatment. In fact, fluoride has the ability to inhibit
or alter the physiology of photosynthesis and other biological
processes such as seed germination, respiration, CO2 assimilation,
protein and nucleotide synthesis, carbohydrate metabolism,
hormonal imbalance, various enzyme activities, gene expression
patterns, inhibition of developmental and reproductive capabilities,
etc. These parameters have been well studied scientifically by
several researchers on a variety of agricultural crops [59-65].
Ultimately, these fluoride-induced morpho-physiological changes
affect the rate of agricultural productivity or yield due to which
the farmers suffer huge economic losses. Scientific evaluation has
not yet been done on such economic losses, which is also very
important. This type of evaluation is very important and helps in
the determination of economic policy. However, which agricultural
crop is more susceptible, sensitive, or less tolerant to industrial
fluoride is not yet clear. Therefore, there is still a need for more
comparative studies on the sensitivity of different species of
agricultural crops to fluoride.
Figure 3:Rice plants (Oryza sativa) showing leaf
necrosis with burnt margin due to chronic fluoride
exposure through industrial fluoride pollution [14].
Figure 4:Stunted growth in rice plants (Oryza sativa)
due to chronic fluoride exposure through industrial
fluoride pollution [14].
The magnitudes of these pathological changes in crop plants
are generally dependent on the industrial fluoride concentration,
the frequency and duration of exposure, and the density of its
bioaccumulation. However, more studies are needed on the diverse
factors that influence the severity of the toxic effects of industrial
fluoride in plants as studied in humans and animals [66-73]. The
findings of such studies are more useful in amelioration fluoride
toxicity in agricultural crops. Moreover, there is also a great need
for studies and guidelines for the correct diagnosis of fluoride
induced toxicity in crop plants as in humans and domestic animals
[74-77]. However, accurate detection of fluoride toxicity in crops
can be easily done by fluoride estimation in their feed [78].
“A major danger from industrial fluoride poisoning in crops is
the possibility of fluorosis in animals and humans by eating fodder
and grain from these crops, respectively. In fact, there are more
chances for the presence of fluoride in their fodder and grains [79-
81]. Interestingly, most people are unaware of this. So it is very
important and necessary to prevent or control industrial fluoride
pollution in rural or agricultural areas. This can be made possible
by adopting effective scientific techniques, thereby reducing
fluoride emissions. In addition, there is a need for regulators of
fluoride emissions, as well as stricter laws and their effective
implementation. Otherwise, the owners and management of these
fluoride-emitting industries will not pay attention to the fluoride
pollution and will also be careless towards it”.
In or around the agricultural lands, several industries, such as
coal-burning power stations and brick kilns and the manufacture
or production plants of steel, iron, aluminum, zinc, phosphorus,
chemical fertilizers, glass, plastics, cement, oil refineries, and
hydrofluoric acid are sources of fluoride pollution. Fluoride from
these sources is released into the surrounding environment,
contaminating various ecosystems and agriculture soil and
crops. The continuous bio-accumulation of industrial fluoride in
agricultural crop plants is not safe and harmful and causes many
mild to severe pathological changes (stunted growth, necrosis,
chlorosis, abscission of leaves, flowers, and fruits, leaf damage, tip
burning, curling of leaves, and various physiological processes) in
them and ultimately reduces their productivity. Fluoride-induced
necrosis is irreversible damage in crop plants. Furthermore, there
is also a great need for correct guidelines for the correct diagnosis
of fluoride-induced toxicity in plants. Prolonged consumption of
fodder and grains of fluoride affected crop plants, which are also
harmful for domestic animals and humans, respectively. Therefore,
it is very important to stop or reduce industrial fluoride pollution,
which is possible by making strict laws and implementing them
effectively.
Adler P, Armstrong WD, Bell ME, Bhussry BR, Büttner W, et al. (1970) Fluorides and human health. World Health Organization Monograph Series No. 59, World Health Organization, Switzerland, Geneva.
Choubisa SL (2018) A brief and critical review of endemic hydrofluorosis in Rajasthan, India. Fluoride 51(1): 13-33.
Choubisa SL (2023) A brief review of industrial fluorosis in domesticated bovines in India: focus on its socio-economic impacts on livestock farmers. Journal of Biomed Research 4(1): 8-15.
Gupta S, Banerjee S, Mondal S (2009) Phytotoxicity of fluoride in the germination of paddy (Oryza sativa) and its effect on the physiology and biochemistry of germinated seedlings. Fluoride 42(2):142-146.
Datta JK, Maitra A, Mondal NK, Banerjee A (2012) Studies on the impact of fluoride toxicity on germination and seedling growth of gram seed (Cicer arietinum cv. Anuradha). Journal of Stress Physiology & Biochemistry 8:194-202.
Pelc J, Snioszek M, Wróbel J, Telesiński A (2020) Effect of fluoride on germination, early growth and antioxidant enzymes activity of three winter wheat (Triticum aestivum L.) Appl Sci 10(19): 6971.
Mohapatra S, Tripathy SK, Mohanty AK, Tripathy S (2021) Fluoride toxicity in rice fields in the periphery of an aluminium smelter in Odisha, India. Fluoride 54(4): 298-308.
Choubisa SL (1996) An epidemiological study on endemic fluorosis in tribal areas of southern Rajasthan. A Technical Report. The Ministry of Environment and Forests, Government of India, New Delhi, pp. 1-84.
Choubisa SL, Sompura K, Bhatt SK, Choubisa DK, Pandya H, et al. (1996) Prevalence of fluorosis in some villages of Dungarpur district of Rajasthan. Indian Journal of Environmental Health 38(2): 119-126.
Choubisa SL, Sompura K (1996) Dental fluorosis in tribal villages of Dungarpur district (Rajasthan). Pollution Research 15(1): 45-47.
Choubisa SL (1996) Radiological skeletal changes due to chronic fluoride intoxication in Udaipur district (Rajasthan). Pollution Research 15(3): 227-229.
Choubisa SL, Choubisa DK, Joshi SC, Choubisa L (1997) Fluorosis in some tribal villages of Dungarpur district of Rajasthan, India. Fluoride 30(4): 223-228.
Choubisa SL (1998) Fluorosis in some tribal villages of Udaipur district (Rajasthan). Journal of Environmental Biology 19(4): 341-352.
Choubisa SL, Pandya H, Choubisa DK, Sharma OP, Bhatt SK, et al. (1996) Osteo-dental fluorosis in bovines of tribal region in Dungarpur (Rajasthan). Journal of Environmental Biology 17(2): 85-92.
Choubisa SL, Mali P (2009) Fluoride toxicity in domestic animals. In: Dadhich L, Sultana F (Eds.), Proceedings of the National Conference on Environmental Health Hazards, Kota, Rajasthan, India, p.103.
Choubisa SL (2010) Fluorosis in dromedary camels of Rajasthan, India. Fluoride 43(3): 194-199.
Choubisa SL, Mishra GV, Sheikh Z, Bhardwaj B, Mali P, et al. (2011) Toxic effects of fluoride in domestic animals. Advances in Pharmacology and Toxicology 12(2): 29-37.
Choubisa SL (2012) Study of natural fluoride toxicity in domestic animals inhabiting arid and sub-humid ecosystems of Rajasthan. A Technical Report. University Grants Commission, New Delhi, India, pp. 1-29.
Choubisa SL (2013) Fluoride toxicosis in immature herbivorous domestic animals living in low fluoride water endemic areas of Rajasthan, India: An observational survey. Fluoride 46(1): 19-24.
Choubisa SL (2021) Chronic fluoride exposure and its diverse adverse health effects in bovine calves in India: An epitomised review. Global Journal of Biology, Agriculture and Health Sciences 10(3): 1-6.
Choubisa SL (2022) A brief review of chronic fluoride toxicosis in the small ruminants, sheep and goats in India: focus on its adverse economic consequences. Fluoride 55(4): 296-310.
Choubisa SL (2023) Chronic fluoride poisoning in domestic equines, horses (Equus caballus) and donkeys (Equus asinus). Journal of Biomed Research 4(1): 29-32.
Choubisa SL (2023) A brief review of fluorosis in dromedary camels (Camelus dromedarius) and focus on their fluoride susceptibility. Austin Journal of Veterinary Science and Animal Husbandry 10(1):1-6.
Brewer RF, Creveling RK, Guillemet FB, Sutherland FH (1960) The effects of hydrogen fluoride on seven citrus varieties. Proceedings of the American Society for Horticultural Science 75: 236-243.
Panda D (2015) Fluoride toxicity stress: physiological and biochemical consequences on plants. International Journal of Bio-resource. Environment and Agricultural Sciences 1(1): 70-84.
Choubisa SL, Choubisa L, Sompura K, Choubisa D (2007) Fluorosis in subjects belonging to different ethnic groups of Rajasthan. J Commun Dis 39(3): 171-177.
Choubisa SL, Choubisa L, Choubisa D (2011) Reversibility of natural dental fluorosis. International Journal of Pharmacology and Biological Sciences 5(20): 89-93.
Choubisa SL (2013) Why desert camels are least afflicted with osteo-dental fluorosis? Current Science 105(12): 1671-1672.
Choubisa SL (2022) The diagnosis and prevention of fluorosis in humans. Journal of Biomedical Research and Environmental Sciences 3(3): 264-267.
Choubisa SL (2022) How can fluorosis in animals be diagnosed and prevented? Austin Journal of Veterinary Science and Animal Husbandry 9(3): 1-5.
Choubisa SL (2022) Radiological findings more important and reliable in the diagnosis of skeletal fluorosis. Austin Medical Sciences 7(2): 1-4.
Choubisa SL, Choubisa A (2021) A brief review of ideal bio-indicators, bio-markers and determinants of endemic of fluoride and fluorosis. Journal of Biomedical Research and Environmental Sciences 2(10): 920-925.
Gupta S, Banerjee S (2011) Fluoride accumulation in crops and vegetables and dietary intake in a fluoride-endemic area of west Bengal. Fluoride 44(3): 153-157.
Arora G, Bhateja S (2014) Estimating the fluoride concentration in soil and crops grown over it in and around Mathura, Uttar Pradesh, India. American Journal of Ethnomedicine 1: 36-41.
Professor, Chief Doctor, Director of Department of Pediatric Surgery, Associate Director of Department of Surgery, Doctoral Supervisor Tongji hospital, Tongji medical college, Huazhong University of Science and Technology
Senior Research Engineer and Professor, Center for Refining and Petrochemicals, Research Institute, King Fahd University of Petroleum and Minerals (KFUPM), Dhahran, Saudi Arabia
Interim Dean, College of Education and Health Sciences, Director of Biomechanics Laboratory, Sport Science Innovation Program, Bridgewater State University