Abstract
Plants are regarded as the crucial creatures in the formation of life on the planet Earth. Unfortunately, the climate of the Earth is rapidly deteriorating, primarily because of the increasing concentration of pollutant gases in the atmosphere, and the consequent rise of temperature and its after effects. Emissions from power plants and various factories (mostly a combination of oxides of carbon, nitrogen, and sulphur) and the release of greenhouse gases (carbon dioxide, methane, nitrous oxide, ozone, chlorofluorocarbons, etc.) are mainly responsible for this grave situation. The presence of these unwanted molecules in the atmosphere has a big impact on plants’ growth and productivity. Since plants cannot move away from harmful conditions due to their sessile nature, they have to face the harsh environment and undergo various alterations in their form and function. Metabolic alterations, or more precisely, fluctuation in the concentration of secondary metabolites, are thought to be one of the plants’ defense mechanisms against unfavorable environments. Secondary metabolites, although not required for a plant’s usual functions, do form the immune system of plants. Climate change has the potential to alter the quality of natural products, as well as the flavor and medicinal value of various plant species. Rising temperatures, drought, salinity, and erratic rainfall, which are an outcome of all these gaseous emissions, have an obvious impact on plant growth and physiology. This chapter presents a brief discussion of these atmospheric impacts on the form and function of medicinal plants with a special focus on their secondary metabolism.
Access provided by Autonomous University of Puebla. Download chapter PDF
Similar content being viewed by others
Keywords
1 Introduction
Climate change is associated with changes in climate over a comparable length of time that is related to human activities and modifies the composition of the global atmosphere, either directly or indirectly. Over the last century, the global mean temperature of the earth’s surface has risen by 0.74 °C. According to the fluctuation in surface temperature, the 1990s decade was the warmest in the past millennium, with 1998 being the warmest year. The temperature rise is ascribed to an alarming increase in atmospheric concentrations of a variety of toxic gases (largely oxides of carbon, nitrogen, and sulphur) emitted from households, various industries, and thermal power plants, and the so-called greenhouse gases such as carbon dioxide (CO2), methane (CH4), nitrous oxide (N2O), and chlorofluorocarbons (CFCs), primarily as a result of increased industrialization (Fig.1). Carbon dioxide concentrations are expected to be 100% greater in 2100 than they were in the pre-industrial era. With global temperatures anticipated to climb by up to 6 °C by the end of the century in comparison to the pre-industrial levels, this agroclimatic indicator is unlikely to remain steady (Singh 2010). The presence of these toxic elements in the air, soil, and water gives rise to some secondary stress factors like increased temperature, rising sea level, drought, salinity, and excess of heavy metals, among others. All these pollutants and the consequent environmental conditions are active in the growing plants individually or collectively at the same time (Aref et al. 2013a, b; Hussein et al. 2017; Iqbal and Ghouse 1982; Iqbal et al. 2000b; Qureshi et al. 2006; Husen 2022a; Husen et al. 2014, 2016, 2017, 2018, 2019; Getnet et al. 2015; Embiale et al. 2016). The physiological status of plants is determined solely by the local climatic factors; for example, photosynthesis is influenced by temperature, carbon dioxide, water, and nutritional ingredients. Planting a crop in an ecologically unsuitable location increases production costs and, as a result, diminishes the likelihood of economic success. Environmental conditions of the habitat determine the size of plants, the duration of phenological stages, and the time and volume of harvest at a specific location (Iqbal and Khudsar 2000; Kumar et al. 2020). Plant growth and development are influenced by a variety of environmental conditions and soil characteristics (Iqbal and Ghouse 1985; Hamdo et al. 2010; Husen 2022a). Climate change is responsible for the variations in environmental conditions across the globe, which have a big impact on chemical constituents, especially the secondary metabolites in plants (Iqbal et al. 2011). Significant biological and pharmacological functions are attributed to these plant components.
Climate change has a wide range of negative consequences for various sectors, including human health, water, air, soil, microbial populations, plants, and their medicinal components (Ahmad et al. 2011). Climate change is caused by several variables, including a growing global population, fast industrialization, and the widespread use of chemical fertilizers and pesticides in agricultural fields. Rising temperatures, drought, and changes in rainfall patterns are all examples of changing climatic conditions. All these characteristics have an impact on how humans, plants, and microbial population function. Anthropogenic activities have played a significant role in causing global climate change. Excessive emissions of gases like CO2, SO2, NO2, and O3 have resulted in global warming and consequently climatic shift (Mishra 2016). Plants, unlike humans, cannot move away from harmful conditions due to their sessile nature; they have to resort to additional mechanisms to ensure their protection and survival (Iqbal et al. 1996; Anjum et al. 2012b; Husen 2021a, b, c, d). Metabolic alterations, or more precisely, fluctuation in the nature and content of secondary metabolites, are thought to be one of the plant’s defense strategies against the unfavorable environments (Pichersky and Gang 2000; Ober 2005). Secondary metabolites are molecules that aren’t required for a plant’s usual functions, but together with alkaloids, terpenes, and cyanogenic glycosides, they form a plant’s immune system (Wink 2003; Hartmann 2007). Climate change has the potential to alter the quality of natural products, as well as the flavor and medicinal value of particular plants (Gore 2006). Secondary metabolite production is increased in stressed situations; nevertheless, secondary metabolite production is influenced by several elements such as plant competition, intensity and duration of light, soil characteristics, and degree of humidity, among others (Das 2012). In comparison to other living organisms, medicinal and aromatic plants are less resistant to climate change. Because climate change has a profound impact on plant life cycles and distributions, many medicinal plants have become indigenous to specific geographic locations. Global warming is supposed to cause a widespread plant extinction around the world. It is estimated that due to further increases in greenhouse gas emissions, more than half of the plants would be damaged by 2080 (Das and Mukherjee 2018). The reaction of plants to climate change varies depending on the plant species and developmental stage. Various plants have different species-specific thresholds, and their reactions, such as root elongation, root growth angle disruption, and yield loss, differ with species (Malhi et al. 2021).
This chapter discusses the impact of gaseous pollutants and the climate change on medicinal plants and their products, particularly on secondary metabolites (SMs). Special attention has been paid to the natural behavior, physiology and metabolism under harsh environmental conditions.
2 Medicinal Plants and their Importance
Plants play a vital role in the medicinal and healthcare regimes of people living in remote locations as in mountainous or desert regions, who often have a strong faith in the efficacy of herbal medicines, and generally lack access to contemporary healthcare facilities (Anis et al. 2000; Beigh et al. 2002, 2003a, b). Ayurvedic, Unani, and other traditional medicinal systems, as well as plant-based pharmaceutical enterprises, amply utilize the medicinal plants (Kumar et al. 2017; Parveen et al. 2020a, b, 2022; Husen 2021f, 2022b).
Medicinal plants are particularly important because of their secondary metabolites of pharmacological qualities, which are widely used in the pharmaceutical, cosmetic, and nutritional industries (Beigh et al. 2002; Hassan et al. 2012). According to the World Health Organization, about 80% of the world’s population and 65% of Indians utilize natural and traditional methods of healing and curing with medicinal herbs (Bannerman 1980; Prashantkumar and Vidyasagar 2008). In Indian society, there are people, known as ‘Vaidyas’ and ‘Hakeems’, who have a deep understanding of medicinal plants and their applications for healing. They utilize the native herbal plants as a source of raw materials to create medications for disease therapy (Chopra and Khoshoo 1986). Herbal medication is now gaining ground in India as an alternative to modern Allopathy for treating chronic disorders. Plants produce a variety of secondary metabolites with unique properties that help improving the human immune system and treating various ailments (Husen and Iqbal 2022). In terms of toxicity or side effects, plant extracts have more positive points than negative ones (Van Huyssteen 2007). Even those living in developed countries are now opting for herbal medicine because of their low cost and negligible side effects. Terpenoids, phenols, steroids, flavonoids, tannins, and aromatic compounds are only a few of the chemicals derived from plants. Secondary metabolites are employed by plants for immunity against pathogens and herbivores; over 12,000 secondary metabolites have been isolated, with many more in the process of identification. Different components of plants are consumed more frequently than their derived oil during eating. By now, just a small number of medicinal plants, about half a million plants, have been identified; therefore, medical plant research has a bright future.
3 Secondary Metabolites under Changed Climate
Isolated plant metabolites, such as phenols, terpenes, and alkaloids, have been used in a variety of ways, including alterations to the core skeleton of products and medications. The isoprenoid, polyketide, and shikimate pathways are the primary pathways for the synthesis of secondary metabolites in plants (Verpoorte and Memelink 2002). Secondary metabolites have been proven in numerous studies to lessen the risk of a variety of major diseases and syndromes, including diabetes, TB, ulcers, asthma, cancer, Alzheimer’s disease, and cardiovascular disease (Basu and Imrhan 2007; Holst and Williamson 2008; Crozier et al. 2009; Fang et al. 2011; Akula and Ravishankar 2011; Miller and Snyder 2012). According to studies, within 10 years (2005–2015), around 60 plant extracts and 110 purified compounds were obtained from 112 medicinal plants, and they showed efficacy in the treatment of multidrug-resistant pathogenic disorders (Gupta et al. 2019). Anthropogenic activities of the modern world have played a major role in polluting the atmosphere with a variety of toxic gases and particulate matters, although some natural events taking place occasionally also cause environmental degradation (Yunus and Iqbal 1996; Iqbal et al. 2000b). The pollutants so produced are responsible for increase in the atmospheric temperature, thus affecting the climatic condition. The gaseous as well as particulate pollutants not only remain suspended in the air but also settle down on the earth surface, thus rendering the air, soil and water toxic and unhealthy for life activities (Ansari et al. 2012; Iqbal et al. 2000a). These atmospheric changes result in conditions like drought, salinity, flooding, and extreme low or high temperature swings (Gupta et al. 2019). Plant growth and development are bound to be influenced by abiotic variables, as each plant species requires specific environmental conditions to thrive (Table 1).
Under harsh environmental conditions, plants tend to alter their set patterns of metabolic and functional activities in order to adapt to the changed environment (Anjum et al. 2012a; Iqbal and Khudsar 2000; Iqbal et al. 2005). This results in alteration of their physiological, structural and developmental traits (Aquil et al. 2003; Dhir et al. 1999; Singh et al. 2000). Finally, both the primary and secondary growth patterns get affected and exhibit a drastically modified picture (Hussein et al. 2017; Iqbal and Ghouse 1982; Iqbal et al. 2000b, 2010c; Verma et al. 2006), to the extent that even the schedule and duration of the formation of secondary vascular tissues (wood and bark) and also their composition (i.e. relative proportion of the component cell types, like axial parenchyma, fibres, tracheids/vessel elements, sieve-tube elements, ray cells, etc.) may undergo alteration (Gupta and Iqbal 2005; Iqbal et al. 2000a, 2010a, b; Mahmooduzzafar et al. 2010).
Currently, increase in normal temperature is a common and predictable feature all over the globe (Bhatla and Tripathi 2014). Temperature increases up to 5 °C have been observed recently, and this can have a drastic impact on many plant species with reference to their survival, growth and yield (Cleland et al. 2012; Noor et al. 2019). Temperature spikes affect plant metabolic and growth performances due to changes in metabolic pathways that control signaling, functioning and defense programs within the plant. Consequent upon these conditions, production of primary metabolites, such as amino acids, carbohydrates, and Krebs cycle intermediate products, and also of various nitrogenous as well as non-nitrogenous secondary metabolites, gets affected. In general, an increased production of secondary metabolite protects plants from biotic stress, thus providing a connecting link between the biotic and abiotic stresses (Arbona et al. 2013). Some genotypic adjustments or changes could aid in the damage mitigation or plant adaptation to changing environmental conditions (Springate and Kover 2014). By way of an early activation of metabolic reactions, plants can overcome chemical imbalances, which is a must for their survival. Plants capable to modify their morphology and physiology in response to environmental changes can survive well under harsh environments (Millar et al. 2007; Noor et al. 2019).
3.1 Impact of CO2 on Secondary Metabolites
Since the industrial revolution, CO2 levels have risen substantially, posing a serious threat to human life and plant physiology. Since 1750, CO2 emissions have increased considerably as a result of anthropogenic activity (Gupta et al. 2019). Although CO2 basically favours photosynthesis and hence the phenomenon of plant growth (Ruhil et al. 2015), yet its excessive concentrations become toxic for plants. Medicinal plants have the ability to adapt to changing environmental circumstances. Secondary metabolites provide elasticity to their metabolic pathways, but this may have an impact on metabolite production, which is the foundation of their therapeutic efficacy (Mishra 2016). Secondary metabolite concentrations in plants are regulated not only by CO2 concentration, but also by the exposure period. Digitalis lanata is used to treat heart failure and contains medicinal qualities (Rahimtoola 2004). When exposed to high levels of CO2, however, digoxin (a cardenolide glycoside) concentrations increased by 3.5-fold, whereas other glycoside concentrations, such as digoxin-monodigitoxoside, digitoxin, and digitoxigenin, declined dramatically (Table 1). According to Weinmann et al. (2010), Ginkgo biloba is used to treat Alzheimer’s disease, vascular dementia, and mixed dementia. When G. biloba is exposed to high levels of CO2 and O3 together, the terpenoid content changes, with a 15% increase in quercetin aglycon but a 10%, 15%, and to some extent, a drop in kaempferol aglycon, isorhamnetin, and bilobalide concentrations, respectively. Ghasemzadeh et al. (2010a, b) reported an increase in the concentrations of phenolic and flavonoid in Zingiber officinale due to increases in CO2 levels. (Stiling and Cornelissen 2007) observed elevation in the concentrations of phenols and tannins in Quercus ilicifolia related to increases in CO2 levels. Similar studies with Elaeis guineensis (oil palm) revealed an increase in phenols and flavonoids, and also in the primary metabolite phenylalanine, which is a precursor of various secondary metabolites (Ibrahim and Jaafar 2012; Rehman et al. 2021).
3.2 Impact of Ozone on Secondary Metabolites
Ozone layer in the stratosphere absorbs damaging ultraviolet light with wavelengths in the UV-B band between 280 and 320 nm, which can injure plants and animals (Montzka et al. 2018). Although ozone is prevalent in the stratosphere, it is considered a pollutant when present in the lower atmosphere (troposphere). It should, therefore, have harmful effects on plants also. Because the effects of O3 on medicinal plants are little studied, it is important to extend future research in this direction (Table 1). Melissa officinalis is utilized to treat central nervous system issues, dementia, and anxiety. However, when exposed to high levels of O3, its levels of phenols, tannins, and anthocyanins were slightly enhanced (Pellegrini et al. 2011; Shakeri et al. 2016). When a suspension culture of Pueraria thomsonii was exposed to O3, it showed no elevation in the production of puerarin after 20 hours of exposure (Sun et al. 2012). However, a maximum of 2.6-fold increase in puerarin could be obtained after 35 hours (Gupta et al. 2019).
3.3 Plant Response to SO2 and NOx
Plants have long been used to pattern the degree of ambient air pollution because they are the first recipients of contaminants and act as their scavengers (Kaler et al. 2017). Pollutants emitted from various sources are normally the oxides of carbon, nitrogen and sulphur in gaseous form. They accumulate or impose themselves on the plant’s leaf surface in particular and enter the leaf through stomata. Thus, they penetrate into the intercellular spaces of mesophyll cells and progressively diffuse into the cell sap. Air pollution has a negative impact on the health of plants; plant cells become inactive when pollutants are present in large concentrations (Iqbal et al. 1996; Munsif et al. 2021). Pollutants such as SO2, NO2, and H2S cause a greater depletion of soluble sugars in the leaves of plants grown in polluted locations. Changes in the biochemical parameters of plant tissues are normally proportional to the load of contaminants inside the plant. Plant symptoms produced by air pollution may be chronic or acute, depending on the nature and extent of injury or damage (Dhanam et al. 2014). A chronic injury can kill a whole tissue or ruin the entire area of a leaf or needle. Acute damage occurs when a plant is overly sensitive to a particular pollutant or is exposed to high levels of pollution for a brief period of time. SO2 is oxidized inside the leaf to sulphur trioxide (SO3), which then reacts with water to generate sulfuric acid (H2SO4). As a result, acid production in the plant’s body disrupts metabolic activities and reduces the plant’s output (Sharma et al. 2017). Similarly, NO2 interacts with the cell walls to create nitrous acid (HNO2) and nitric acid (HNO3), which lower the cellular pH, inhibit metabolism, and cause toxicity and growth suppression. Discolored spots or light brown hue, as well as bleached or necrotic spots in interveinal sections of leaves, are the morphological signs induced by NO2 (Das and Mukherjee 2018; Adak and Kour 2021).
Sulphur gases are substantial air pollutants that can be created naturally by volcanic activity, but large concentrations owe to anthropogenic emissions from fossil fuel combustion (Sun et al. 2018). Plant metabolism can be significantly altered by air pollutants such as SO2, H2S, NO2, or O3, which affect a variety of molecules such as sugars, polyamines, phenylpropanoids, and several specialized phytochemicals (Khaling et al. 2015; Papazian et al. 2016). The majority of air pollutants, such as CO, SO2, NO2, and O3, interact with plants near the leaf surface, where they can diffuse through stomatal pores and enter intracellular regions (Castagna and Ranieri 2009; Räsänen et al. 2017). Once absorbed, these hazardous chemicals disrupt stomatal functioning, leaf transpiration, gas exchange, and CO2 fixation (Nighat et al. 2000; Rai et al. 2011). Chlorophyll content and photosynthetic rate are the main target and the major sufferers, and their disruption affects the entire form and function of the plant (Dhir et al. 2001; Wali et al. 2004, 2007). The reduced CO2 availability and photosynthetic efficiency have a significant impact on plant central carbon metabolism. Oxidative stress caused by the production of reactive oxygen species (ROS) in tissues then compels the plant to develop appropriate responses to the pollutants load through activation of enzymatic and/or non-enzymatic antioxidant system and the production of specific secondary metabolites (Ainsworth et al. 2012; Yendrek et al. 2015; Aref et al. 2016).
3.4 Role of Methane and CFC’s
Methane (CH4), one of the most significant greenhouse gases, was previously thought to be a physiologically inert gas. However, the discovery that CH4 has a variety of biological activities in animals, including anti-inflammatory, antioxidant, and anti-apoptosis activities, has cast doubt on this viewpoint. Meanwhile, it has been identified as a potential gaseous signaling molecule in plants, however the biosynthetic and metabolic pathways, as well as the mechanisms of CH4 signaling, are yet unknown. Plants have traditionally been thought of as conduits for CH4 transport and emission from the soil to the atmosphere (Li et al. 2020). Agricultural soils are the major source of methane and nitrous oxide gases and a sink of carbon dioxide. About 30% and 11% of the global agricultural output of methane and nitrous oxide, respectively, come from rice fields. Alterations in the conventional crop management regimes may likely cause reductions in the emission of these gases from the rice field. Organic soil amendments reportedly increase CH4 emission from rice fields and improve the flag leaf photosynthesis of the rice crop over the control (NPK application alone). The combined application of NPK and Azolla compost caused a 15.66% higher CH4 emission with 27.43% more yield over the control and increased the capacity of soil carbon storage, with a high carbon efficiency ratio (Bharali et al. 2018; Gupta et al. 2021). FCs (chlorofluorocarbons) are normally harmless and non-flammable compounds made up of carbon, chlorine and fluorine atoms. However, they are known to destroy the ozone layer, and this is likely to allow greater amounts of the sun’s radiation reach the earth and affect the plants. It is, therefore, apprehended that the plants may consequently experience abnormal and reduced growth due to possible protein denaturation and DNA damage (Gupta 2018).
4 Conclusion
Plants have a wide range of species and produce a large number of secondary metabolites, many of which are physiologically active and extremely beneficial to humans, being utilized mainly for therapeutic purposes. Medicinal plants have been used to develop new allopathic medicines for the past few decades. Changing climatic circumstances and abiotic stress factors have an impact on plants’ natural behavior and physiology, which has an impact on essential secondary metabolites. Gaseous pollutants (such as SO2 and NO2) and greenhouse gases (like CO2, ozone, methane, and CFCs) have direct toxic effects on plants and also change climatic conditions, affecting water, pH level, and salinity, which again have a bearing on metabolite production in plants. Some environmental factors, such as temperature and elevated CO2, basically enhance the secondary metabolism in plants, whereas extreme temperatures (too hot or too cold), drought, and high salinity negatively affect the metabolites, growth, and productivity of plants.
Abbreviations
- CFC :
-
Chlorofluorocarbons
- TCM:
-
Traditional Chinese Medicine
- UV light:
-
Ultraviolet light
- WHO:
-
World health organization
References
Adak P, Kour N (2021) A review on the effects of environmental factors on plants tolerance to air pollution. J Environ Treatment Tech 9(4):839–848
Ahmad A, Siddiqi TO, Iqbal M (2011) Medicinal plants in changing environment. Capital Publishing Company, New Delhi
Ainsworth EA, Yendrek CR, Sitch S, Collins WJ, Emberson LD (2012) The effects of tropospheric ozone on net primary productivity and implications for climate change. Annu Rev Plant Biol 63:637–661
Akula R, Ravishankar GA (2011) Influence of abiotic stress signals on secondary metabolites in plants. Plant Signal Behav 6(11):1720–1731
Anis M, Sharma MP, Iqbal M (2000) Herbal ethnomedicine of the Gwalior-forest division in Madhya Pradesh, India. Pharm Biol 38:241–253
Anjum NA, Ahmad I, Pacheco M, Duarte AC, Pereira E, Umar S, Ahmad A, Iqbal M (2012a) Modulation of glutathione, its redox couple and related enzymes in plants under abiotic stresses. In: Anjum NA, Umar S, Ahmad A (eds) Oxidative stress in plants: causes, consequences and tolerance. I.K. International Publishing House, New Delhi, pp 467–498
Anjum NA, Gill SS, Ahmad I, Tuteja N, Soni P, Pareek A, Umar S, Iqbal M, Pacheco M, Duarte AC, Pereira E (2012b) Understanding stress-responsive mechanisms in plants: an overview of transcriptomics and proteomics approaches. In: Tuteja N, Tiburcio AF, Singh S et al (eds) Improving crop resistance to abiotic stress – omics approaches. Wiley-VCH Verlag GmbH & Co., Weinheim, pp 337–355
Ansari MKA, Anjum NA, Ahmad A, Umar S, Iqbal M (2012) Heavy metals in soil and plants: an overview of arsenic, cadmium, chromium and mercury. In: Anjum NA, Umar S, Ahmad A (eds) Oxidative stress in plants: causes, consequences and tolerance. I.K. International Publishing House, New Delhi, pp 499–518
Aquil S, Ahmad SH, Reshi ZA, Mahmooduzzafar, Iqbal M (2003) Physiological and biochemical response of Albizia lebbeck Benth. To coal smoke pollution. Pollut Res 22(4):489–493
Arbona V, Manzi M, Ollas CD, Gómez-Cadenas A (2013) Metabolomics as a tool to investigate abiotic stress tolerance in plants. Int J Mol Sci 14(3):4885–4911
Aref MI, Ahmed AI, Khan PR, El-Atta H, Iqbal M (2013a) Drought-induced adaptive changes in the seedling anatomy of Acacia ehrenbergiana and Acacia tortilis subsp. raddiana. Trees Struct Funct 27(4):959–971
Aref MI, El-Atta H, El-Obeid M, Ahmed A, Khan PR, Iqbal M (2013b) Effect of water stress on relative water and chlorophyll contents of Juniperus procera Hochst. Ex Endlicher in Saudi Arabia. Life Sci J 10(4):681–685
Aref IM, Khan PR, Khan S, El-Atta H, Ahmed AI, Iqbal M (2016) Modulation of antioxidant enzymes in Juniperus procera needles in relation to habitat environment and dieback incidence. Trees Struct Funct 30:1669–1681
Bannerman RH (1980) Traditional medicine in modern health care services. Int Relat 6(5):731–748
Basu A, Imrhan V (2007) Tomatoes versus lycopene in oxidative stress and carcinogenesis conclusions from clinical trials. Eur J Clin Nutr 61(3):295–303
Beigh SY, Nawchoo IA, Iqbal M (2002) Herbal drugs in India: past and present uses. J Trop Med Plants 3:197–204
Beigh SY, Nawchoo IA, Iqbal M (2003a) Traditional veterinary medicine among the tribes of Kashmir Himalaya. J Spices Med Plants 10(4):121–127
Beigh SY, Nawchoo IA, Iqbal M (2003b) Plants in traditional medicine of Kashmir Himalayas. J Econ Taxon Botany 27(1):99–104
Bharali A, Baruah KK, Baruah SG, Bhattacharyy P (2018) Impacts of integrated nutrient management on methane emission, global warming potential and carbon storage capacity in rice grown in a Northeast India soil. Environ Sci Pollut Res Int 25(6):5889–5901
Bhatla R, Tripathi A (2014) The study of rainfall and temperature variability over Varanasi. Int J Earth Atmos Sci 1(2):90–94
Bortolin RC, Caregnato FF, Junior AMD, Zanotto-Filho A, Moresco KS, de Oliveira RA, Moreira JCF (2016) Chronic ozone exposure alters the secondary metabolite profile antioxidant potential anti-inflammatory property and quality of red pepper fruit from Capsicum baccatum. Ecotoxicol Environ Saf 129:16–24
Castagna A, Ranieri A (2009) Detoxification and repair process of ozone injury: from O 3 uptake to gene expression adjustment. Environ Pollut 157:146–1469
Chopra VL, Khoshoo TN (1986) Conservation for productive agriculture. ICAR, New Delhi
Cleland EE, Allen JM, Crimmins TM, Dunne JA, Pau S, Travers SE, Wolkovich EM (2012) Phenological tracking enables positive species responses to climate change. Ecology 93(8):1765–1771
Crozier A, Jaganath IB, Clifford MN (2009) Dietary phenolics chemistry bioavailability and effects on health. Nat Prod Rep 26(8):1001–1043
Das HP (2012) Agrometeorology in extreme events and natural disasters. CRC Press Inc
Das M, Mukherjee A (2018) Air pollution tolerance index (APTI) used for assessing air quality to alleviate climate change: a review. Res J Pharmaceut Biol Chem Sci 9(1):45–54
Dhanam S, Rajapandian P, Elayaraj B (2014) Air pollution tolerance index and biochemical constituents of some plants growing in Neyveli lignite corporation (NLC), Tamil Nadu, India. J Environ Treatment Tech 2(4):171–175
Dhir B, Mahmooduzzafar, Siddiqi TO, Iqbal M (2001) Stomatal and photosynthetic responses of Cichorium intybus leaves to Sulphur dioxide treatment at different stages of plant development. J Plant Biol 44:97–102
Dhir B, Sharma MP, Mahmooduzzafar, Iqbal M (1999) Form and function of Achyranthes aspera Linn. Under air pollution stress. J Environ Biol 20:19–24
Embiale A, Hussein M, Husen A, Sahile S, Mohammed K (2016) Differential sensitivity of Pisum sativum L. cultivars to water-deficit stress: changes in growth, water status, chlorophyll fluorescence and gas exchange attributes. J Agron 15:45–57. https://doi.org/10.3923/ja.2016.45.57
Fang J, Nakamura H, Maeda H (2011) The EPR effect: unique features of tumor blood vessels for drug delivery factors involved and limitations and augmentation of the effect. Adv Drug Deliv Rev 63(3):136–151
Getnet Z, Husen A, Fetene M, Yemata G (2015) Growth, water status, physiological, biochemical and yield response of stay green sorghum {Sorghum bicolor (L.) Moench} varieties-a field trial under drought-prone area in Amhara regional state, Ethiopia. J Agron 14:188–202
Ghasemzadeh A, Jaafar HZ, Rahmat A (2010a) Elevated carbon dioxide increases contents of flavonoids and phenolic compounds and antioxidant activities in Malaysian young ginger (Zingiber officinale roscoe.) varieties. Molecules 15(11):7907–7922
Ghasemzadeh A, Jaafar HZ, Rahmat B (2010b) Antioxidant activities total phenolics and flavonoids content in two varieties of Malaysia young ginger (Zingiber officinale roscoe). Molecules 15(6):4324–4333
Gore A (2006) An inconvenient truth: the planetary emergency of global warming and what we can do about it. Rodale Books, New York, p 325
Gupta A, Singh PP, Singh P, Singh K, Singh AV, Singh SK, Kumar A (2019) Medicinal plants under climate change impacts on pharmaceutical properties of plants. In: Climate change and agricultural ecosystems. Woodhead Publishing, pp 181–209
Gupta K, Kumar R, Baruah KK, Hazarika S, Karmaka S, Bordoloi N (2021) Greenhouse gas emission from rice fields: a review from Indian context. Environ Sci Pollut Res Int 28(24):30551–30572
Gupta MC, Iqbal M (2005) Ontogenetic histological changes in the wood of mango (Mangifera indica L. cv Deshi) exposed to coal-smoke pollution. Environ Exp Bot 54:248–255
Gupta S (2018) The effects of radiation on plants and the ecosystem. Res Rev J Botanical Sci 7(2):44–48
Hamdo SH, Umar S, Iqbal M, Bansal SK (2010) Effect of nitrogen-potassium interaction on leaching of NO3− and K+ under sorghum-wheat cropping system. In: Brar MS (ed) Proceedings of IPI-OUAT-IPNI international Symposium-2009, Bhubaneswar, India, pp 380–383
Hartmann T (2007) From waste products to eco chemicals fifty years research of plant secondary metabolism. Phytochemistry 68(22–24):2831–2846
Hassan BAR, Yusoff ZBM, Hassali MA, Othman SB, Weiderpass E (2012) Impact of chemotherapy on hypercalcemia in breast and lung cancer patients. Asian Pac J Cancer Prev 13(9):4373–4378
Holst B, Williamson G (2008) Nutrients and phytochemicals from bioavailability to bio efficacy beyond antioxidants. Curr Opin Biotechnol 19(2):73–82
Husen A (2021a) Harsh environment and plant resilience (molecular and functional aspects). Springer Nature, Cham. https://doi.org/10.1007/978-3-030-65912-7
Husen A (2021b) Plant performance under environmental stress (hormones, Biostimulants and Sustainable Plant Growth Management). Springer Nature, Cham. https://doi.org/10.1007/978-3-030-78521-5
Husen A (2021c) Morpho-anatomical, physiological, biochemical and molecular responses of plants to air pollution. In: Husen A (ed) Harsh environment and plant resilience. Springer International Publishing, Cham, pp 203–234. https://doi.org/10.1007/978-3-030-65912-7_9
Husen A (2021d) Cross talk between autophagy and hormones for abiotic stress tolerance in plants. In: Husen A (ed) Plant performance under environmental stress. Springer, Cham, pp 1–15. https://doi.org/10.1007/978-3-030-78521-5_1
Husen A (2021f) Traditional herbal therapy for the human immune system. CRC Press, Boca Raton, FL. https://doi.org/10.1201/9781003137955
Husen A (2022b) Herbs, shrubs and trees of potential medicinal benefits. CRC Press, Boca Raton, FL. https://doi.org/10.1201/9781003205067
Husen A (2022a) Environmental pollution and medicinal plants. CRC Press, Boca Raton, FL. https://doi.org/10.1201/9781003178866
Husen A, Iqbal M (2022) Plant-based potential nutraceuticals for improving human immune system. In: Husen H (ed) Traditional herbal therapy for human immune system. Springer Nature, Cham. https://doi.org/10.1201/9781003137955-1
Husen A, Iqbal M, Aref IM (2014) Growth, water status and leaf characteristics of Brassica carinata under drought and rehydration conditions. Rev Bras Bot 37(3):217–227
Husen A, Iqbal M, Aref IM (2016) IAA-induced alteration in growth and photosynthesis of pea (Pisum sativum L.) plants grown under salt stress. J Environ Biol 37(3):421–429
Husen A, Iqbal M, Aref IM (2017) Plant growth and foliar characteristics of faba bean (Vicia faba L.) as affected by indole-acetic acid under water-sufficient and water-deficient conditions. J Environ Biol 38(2):179–186
Husen A, Iqbal M, Khanam N, Aref IM, Sohrab SS, Masresha G (2019) Modulation of salt-stress tolerance of Niger (Guizotia abyssinica), an oilseed plant, by application of salicylic acid. J Environ Biol 40(1):96–104
Husen A, Iqbal M, Sohrab SS, Ansari MKA (2018) Salicylic acid alleviates salinity-caused damage to foliar functions, plant growth and antioxidant system in Ethiopian mustard (brassica carinataA. Br). Agric Food Secur 7:14
Hussein M, Embiale A, Husen A, Aref IM, Iqbal M (2017) Salinity-induced modulation of plant growth and photosynthetic parameters in faba bean (Vicia faba) cultivars. Pak J Bot 49(3):867–877
Ibrahim MH, Jaafar HZ (2012) Impact of elevated carbon dioxide on primary secondary metabolites and antioxidant response of Eleais guineensis Jacq (oil palm) seedlings. Molecules 17(5):5195–5211
Idso SB, Kimball BA, Pettit GR III, Garner LC, Pettit GR, Backhaus RA (2000) Effects of atmospheric CO2 enrichment on the growth and development of Hymenocallis littoralis (Amaryllidaceae) and the concentrations of several antineoplastic and antiviral constituents of its bulbs. Am J Bot 87(6):769–773
Iqbal M, Abdin MZ, Mahmooduzzafar, Yunus M, Agrawal M (1996) Resistance mechanism in plants against air pollution. In: Yunus M, Iqbal M (eds) Plant response to air pollution. John Willey & Sons, Chichester, pp 195–240
Iqbal M, Ahmad A, Siddiqi TO (2011) Characterization of controversial plant drugs and effect of changing environment on active ingredients. In: Ahmad A, Siddiqi TO, Iqbal M (eds) Medicinal plants in changing environment. Capital Publishing Company, New Delhi, pp 1–10
Iqbal M, Bano R, Wali B (2005) Plant growth responses to air pollution. In: Chaturvedi SN, Singh KP (eds) Plant biodiversity, microbial interaction and environmental biology. Avishkar Publishers, Jaipur, pp 166–188
Iqbal M, Ghouse AKM (1982) Environmental influence on growth activities of Prosopis spicigera. In: Khosla PK (ed) Improvement of Forest biomass. ISTS, Solan, pp 387–393
Iqbal M, Ghouse AKM (1985) Impact of climatic variation on the structure and activity of vascular cambium in Prosopis spicigera. Flora 177:147–156
Iqbal M, Jura-Morawiec J, Wloch W, Mahmooduzzafar (2010a) Foliar characteristics, cambial activity and wood formation in Azadirachta indica a. Juss. As affected by coal-smoke pollution. Flora 205:61–71
Iqbal M, Khudsar T (2000) Heavy metal stress and forest cover: plant performance as affected by cadmium toxicity. In: Kohli RK, Singh HP, Vij SP, Dhir KK, Batish DR, Khurana DK (eds) Man and forests. DNES, IUFRO, ISTS and Punjab University, Chandigarh, pp 85–112
Iqbal M, Mahmooduzzafar, Abdin MZ (2000a) Studies on anatomical, physiological and biochemical response of trees to coal-smoke pollution around a thermal power plant. Research project 14/62/89-MAB/Re. Ministry of Environment & Forests (Govt. of India), New Delhi, p 335
Iqbal M, Mahmooduzzafar, Aref IM, Khan PR (2010b) Behavioral responses of leaves and vascular cambium of Prosopis cineraria (L.) Druce to different regimes of coal-smoke pollution. J Plant Interact 5(2):117–133
Iqbal M, Mahmooduzzafar, Nighat F, Khan PR (2010c) Photosynthetic, metabolic and growth responses of Triumfetta rhomboidea to coal-smoke pollution at different stages of plant ontogeny. J Plant Interact 5(1):11–19
Iqbal M, Srivastava PS, Siddiqi TO (2000b) Anthropogenic stresses in the environment and their consequences. In: Iqbal M, Srivastava PS, Siddiqi TO (eds) Environmental hazards: plants and people. CBS Publishers, New Delhi, pp 1–38
Kaler NS, Kashyap P, Prasad H, Singh TJ (2017) Air pollution tolerance index (APTI) of tree species: a review. Int J Chem Studies 5(4):716–720
Khaling E, Papazian S, Poelman EH, Holopainen JK, Albrectsen BR, Blande JD (2015) Ozone affects growth and development of Pieris brassicae on the wild host plant Brassica nigra. Environ Pollut 199:119–129
Kumar A, Singhal P, Shukla S, Kumar V (2020) Impact of greenhouse gases on fruits production. J Med Plant Res 8(2):133–134
Kumar S, Dobos GJ, Rampp T (2017) The significance of Ayurvedic medicinal plants. J Evid Based Complement Altern Med 22(3):494–501
Li L, Wei S, Shen W (2020) The role of methane in plant physiology: a review. Plant Cell Rep 39(2):171–179
Mahmooduzzafar, Hegazy SS, Aref IM, Iqbal M (2010) Anatomical changes in the wood of syzygium cumini exposed to coal-smoke pollution. J Food Agric Environ 8(3–4):959–964
Malhi GS, Kaur M, Kaushik P (2021) Impact of climate change on agriculture and its mitigation strategies: a review. Sustainability 13(3):1318
Millar CI, Stephenson NL, Stephens SL (2007) Climate change and forests of the future managing in the face of uncertainty. Ecol Appl 17(8):2145–2151
Miller PE, Snyder DC (2012) Phytochemicals and cancer risk a review of the epidemiological evidence. Nutr Clin Pract 27(5):599–612
Mishra T (2016) Climate change and production of secondary metabolites in medicinal plants: a review. Int J Herb Med 4(4):27–30
Montzka SA, Dutton GS, Yu P, Ray E, Portmann RW, Daniel JS, Elkins JW (2018) An unexpected and persistent increase in global emissions of ozone-depleting CFC-11. Nature 557(7705):413–417
Munsif R, Zubair M, Aziz A, Zafar MN (2021) Industrial air emission pollution: potential sources and sustainable mitigation. In: Viskup R (ed) Environmental Emissions. Intech Open, London, p 13. https://doi.org/10.5772/intechopen.93104
Nighat F, Mahmooduzzafar, Iqbal M (2000) Stomatal conductance, photosynthetic rate, and pigment content in Ruellia tuberosa leaves as affected by coal-smoke pollution. Biol Plant 43:263–267
Noor JJ, Vinayan MT, Umar S, Devi P, Iqbal M, Seetharam K, Zaidi PH (2019) Morpho-physiological traits associated with heat stress tolerance in tropical maize (Zea mays L.) at the reproductive stage. Aust J Crop Sci 13(4):536–545
Ober D (2005) Seeing double gene duplication and diversification in plant secondary metabolism. Trends Plant Sci 10(9):444–449
Papazian S, Khaling E, Bonnet C, Lassueur S, Reymond P, Moritz T, Blande JD, Albrectsen BR (2016) Central metabolic responses to ozone and herbivory affect photosynthesis and stomatal closure. Plant Physiol 172:2057–2078
Parveen A, Ahmad M, Parveen B, Parveen R, Iqbal M (2022) Unani system of medicine, its origin, evolution and Indianization: a critical appraisal. Indian J Tradit Knowl 21(2):511–521
Parveen A, Parveen R, Akhatar A, Parveen B, Siddiqui KM, Iqbal M (2020a) Concepts and quality considerations in Unani system of medicine. J AOAC Int 103:609–633
Parveen B, Parveen A, Parveen R, Ahmad S, Ahmad M, Iqbal M (2020b) Challenges and opportunities for traditional herbal medicine today, with special reference to its status in India. Ann Phytomed 9(2):97–112
Pellegrini E, Carucci MG, Campanella A, Lorenzini G, Nali C (2011) Ozone stress in Melissa officinalis plants assessed by photosynthetic function. Environ Exp Bot 73:94–101
Pichersky E, Gang DR (2000) Genetics and biochemistry of secondary metabolites in plants an evolutionary perspective. Trends Plant Sci 5(10):439–445
Prashantkumar P, Vidyasagar GM (2008) Traditional knowledge on medicinal plants used for the treatment of skin diseases in Bidar district Karnataka. Indian J Tradit Knowl 7(2):273–276
Qureshi MI, Abdin MZ, Qadir S, Kamaluddin IM (2006) Responses of some medicinal plants to heavy metal, salinity and oxidative stress. In: Abdin MZ, Abrol YP (eds) Traditional systems of medicine. Narosa Publishing House, New Delhi, pp 522–533
Rahimtoola SH (2004) Digitalis therapy for patients in clinical heart failure. Circulation 109(24):2942–2946
Rai R, Rajput M, Agrawal M, Agrawal SB (2011) Gaseous air pollutants: a review on current and future trends of emissions and impact on agriculture. J Sci Res 55:77–102
Räsänen JV, Leskinen JTT, Holopainen T, Joutsensaari J, Pasanen P, Kivimäenpaa M (2017) Titanium dioxide (TiO2) fine particle capture and BVOC emissions of Betula pendula and Betula pubescens at different wind speeds. Atmos Environ 152:345–353
Rehman A, Ma H, Ahmad M, Irfan M, Traore O, Chandio AA (2021) Towards environmental sustainability: devolving the influence of carbon dioxide emission to population growth, climate change, forestry, livestock and crops production in Pakistan. Ecol Indic 125:107460
Ruhil K, Sheeba AA, Iqbal M, Tripathy BC (2015) Photosynthesis and growth responses of mustard (Brassica juncea L. cv. Pusa bold) plants to free air carbon-dioxide enrichment (FACE). Protoplasma 252(4):935–946
Shakeri A, Sahebkar A, Javadi B (2016) Melissa officinalis L. a review of its traditional uses phytochemistry and pharmacology. J Ethnopharmacol 188:204–228
Sharma B, Sharma S, Bhardwaj SK, Alam NM, Parmar YS (2017) Effect of pollution on total chlorophyll content in temperate species growing along national highway 5 in Himachal Pradesh. Int J Adv Sci Eng Technol 5(3):72–75
Singh HP (2010) Impact of climate change on horticultural crops. In: Challenges of climate change in indian horticulture. Westville Publishing House, New Delhi, pp 1–8
Singh N, Ali G, Soh WY, Iqbal M (2000) Growth responses and hyoscyamine content of Datura innoxia under the influence of coal-smoke pollution. J Plant Biol 43:69–75
Springate DA, Kover PX (2014) Plant responses to elevated temperatures: a field study on phenological sensitivity and fitness responses to simulated climate warming. Glob Change Biol 20(2):456–465
Stiling P, Cornelissen T (2007) How does elevate carbon dioxide (CO2) affect plant–herbivore interactions? A field experiment and meta-analysis of CO2-mediated changes on plant chemistry and herbivore performance. Glob Change Bio 13(9):1823–1842
Sun L, Su H, Zhu Y, Xu M (2012) Involvement of abscisic acid in ozone-induced puerarin production of Pueraria thomsnii Benth suspension cell cultures. Plant Cell Rep 31(1):179–185
Sun W, Shao M, Granier C, Liu Y, Ye CS, Zheng JY (2018) Long -term trends of anthropogenic SO 2, NO x, CO, and NMVOCs emissions in China. Earth ‘s Future 6(111):2–1133
Van Huyssteen M (2007) Collaborative research with traditional African health practitioners of the Nelson Mandela metropole antimicrobial, anticancer and anti-diabetic activities of five medicinal plants (doctoral dissertation, unpublished PhD thesis, Nelson Mandela Metropolitan University, Port Elizabeth)
Verma RB, Mahmooduzzafar, Siddiqi TO, Iqbal M (2006) Foliar response of Ipomea pes-tigridis L. to coal-smoke pollution. Turk J Bot 30:413–417
Verpoorte R, Memelink J (2002) Engineering secondary metabolite production in plants. Curr Opin Biotechnol 13(2):181–187
Wali B, Iqbal M, Mahmooduzzafar (2007) Anatomical and functional responses of Calendula officinalis L to SO2 stress as observed at different stages of plant development. Flora 202:268–280
Wali B, Mahmooduzzafar, Iqbal M (2004) Plant growth, stomatal response, pigments and photosynthesis of Althea officinalis as affected by SO2 stress. Indian J Plant Physiol 9:224–233
Weinmann S, Roll S, Schwarzbach C, Vauth C, Willich SN (2010) Effects of Ginkgo biloba in dementia: systematic review and meta-analysis. BMC Geriatr 10(1):1–12
Wink M (2003) Evolution of secondary metabolites from an ecological and molecular phylogenetic perspective. Phytochemistry 64(1):3–19
Yendrek CR, Koester RP, Ainsworth EA (2015) A comparative analysis of transcriptomic, biochemical, and physiological responses to elevated ozone identifies species -specific mechanisms of resilience in legume crops. J Exp Bot 66:7101–7112
Yunus M, Iqbal M (1996) Plant response to air pollution. John Willey and Sons, Chichester
Ziska LH, Panicker SH, Wojno HL (2008) Recent and projected increases in atmospheric carbon dioxide and the potential impacts on growth and alkaloid production in wild poppy (Papaver setigerum DC.). Clim Chang 91(3):395–403
Author information
Authors and Affiliations
Editor information
Editors and Affiliations
Rights and permissions
Copyright information
© 2023 The Author(s), under exclusive license to Springer Nature Singapore Pte Ltd.
About this chapter
Cite this chapter
Sharma, N., Radha, Prakash, S., Pundir, A., Puri, S. (2023). Effects of Gaseous Pollutants on Medicinal Plants. In: Husen, A., Iqbal, M. (eds) Medicinal Plants. Springer, Singapore. https://doi.org/10.1007/978-981-19-5611-9_7
Download citation
DOI: https://doi.org/10.1007/978-981-19-5611-9_7
Published:
Publisher Name: Springer, Singapore
Print ISBN: 978-981-19-5610-2
Online ISBN: 978-981-19-5611-9
eBook Packages: Biomedical and Life SciencesBiomedical and Life Sciences (R0)