Ozone flux-effect relationship for early and late sown Indian wheat cultivars: Growth, biomass, and yield
Introduction
Ground surface ozone (O3) is the most damaging air pollutant to horticultural and agricultural crop plants (Mills et al., 2007; Osborne et al., 2019). During the preindustrial time, the background O3 levels were 10−15 ppb. Owing to anthropogenic activity, the emissions of O3 precursors (NOx, CO, and VOCs) have been increased. The ambient O3 level has reached above the threshold of critical level over many regions of the world (Hartmann et al., 2013; Solberg et al., 2005). If current rising trends of O3 continue, the annual global concentration of O3 will reach up to 68 ppb by 2050 (Meehl et al., 2007). Air pollution and GHG emissions have risen dramatically in India over the past three decades due to tremendous growth in industrialization, urbanization, and transport. In recent decades, high O3 concentration has been detected in several regions of India (Lal et al., 2017; Sharma et al., 2019; Singh and Agrawal, 2017; Yadav et al., 2020).
Wheat is a staple crop in India and has been identified as O3 sensitive species (Feng et al., 2009; Singh et al., 2018). The deleterious effects of high O3 on wheat are described as visible leaf injury, premature leaf senescence, and reduced leaf area, plant height, and above-ground biomass, which collectively lead to a reduction in the economic yield (Liu et al., 2015; Mishra et al., 2013; Ojanpera et al., 1992; Singh et al., 2018). Long-term assessments on crop loss due to O3 have been documented since the 1980s in the USA under National Crop Loss Assessment Network (NCLAN), and in Europe under European Open-Top Chambers Programme (EOTCP) (Fuhrer, 1994; Heagle, 1989; Heck et al., 1984). Pleijel et al. (2014) have reported a 9% reduction in above-ground biomass and 14 % yield loss in wheat due to ambient O3 concentration over the Europe. However, globally O3 induced reduction in grain yield of wheat was established at 9.9 % in the northern hemisphere and 6.2 % in the southern hemisphere (Mills et al., 2018). The yield losses of 8.2–22.3 % in wheat were estimated for India because of high ambient O3 (Tang et al., 2013). India's breadbasket, the Indo-Gangetic Plain (IGP), is one of the most air-polluted regions in the country and estimated to suffer nine million tons of wheat loss annually due to high surface O3 (Lal et al., 2017).
Furthermore, the concentrations of O3 above the critical levels are known for significant impairment in plant growth and economic yield (Ainsworth et al., 2012; Feng et al., 2009; Singh et al., 2018). To derive the critical level of O3, cumulative exposure metrics such as AOT40 and cumulative stomatal flux-based metrics such as PODy have been used in many studies (Emberson et al., 2018; Mills et al., 2018). The stomatal O3 flux methods are quite useful for assessing O3 risk and provide a robust dose-response relationship between O3 uptake and yield of wheat cultivars (CLRTAP, 2017; Harmens et al., 2018; Osborne et al., 2019; Pleijel et al., 2014; Wu et al., 2016). But, this approach is more dependent on input data as compared to the exposure-based approach. In the past, various exposure-based field studies have been conducted in India to assess the yield losses of major crops under ambient and future O3 levels (Mishra et al., 2013; Mukherjee et al., 2020; Singh et al., 2018). In exposure-based metrics, we only consider the O3 concentration in the air nearby the plants to measure its impact on plants. However, many important factors such as stomatal conductance, soil moisture, weather condition, vegetation characteristics, phenology of plant are not considered, which play vital roles in stomatal O3 uptake (Feng et al., 2012; Mills et al., 2007).
As the sensitivity of a species to O3 mainly depends on the amount of O3 uptake and their intrinsic defense response (Dumont et al., 2013; Yadav et al., 2019), the flux-based concept is suggested to be the most preferred metrics over the exposure-based metrics (Anav et al., 2016; Pleijel et al., 2004). Over the last 20 years, many significant developments have been made in stomatal flux modelling to improve the O3 risk assessment (CLRTAP, 2017; Emberson et al., 2018, 2000; Grunhage et al., 2012; Pleijel et al., 2007). The previous studies have found a strong correlation of phytotoxic O3 dose above a flux-threshold of y (PODy) with grain yield and biomass of wheat (Grunhage et al., 2012; Harmens et al., 2018; Pleijel et al., 2014). Moreover, a significant negative flux-effect relationship has also been found, which helped in identifying the level of sensitivity of wheat cultivars under elevated O3 (Grunhage et al., 2012; Harmens et al., 2018; Pleijel et al., 2014).
In the present study, Deposition of Ozone and Stomatal Exchange (DO3SE) model was used for assessing the O3 risk and to identify the species-specific O3 sensitivity in Indian wheat cultivars. The DO3SE model estimates stomatal O3 flux of plant with a function of the O3 concentration at and the transfer of O3 across the boundary layer of leaf. Although several O3 flux-based studies have been attempted in Europe, Southeast Asia and China (Danh et al., 2016; Feng et al., 2012; Osborne et al., 2019), but this will be the first O3 flux-model based study for India to estimate stomatal O3 uptake of wheat cultivars using multiplicative algorithms. The study will be important for screening O3 tolerant Indian wheat cultivars to get the maximum yield against the future level of O3. For this purpose, early and late sown wheat cultivars were selected based on their differences in sowing time, life span, and popularity in the IGP region of India. On availability of field after rice harvest, it is a common practice to sow wheat either in early winter at the start of November using early sown cultivars (life span 5 months) or up to mid of December with late sown cultivars (life span 4 months). The aims of the present study are: (i) to determine the effects of elevated O3 on growth, biomass, and yield of early and late sown wheat cultivars; (ii) to parameterise the stomatal flux DO3SE model for Indian wheat cultivars to calculate the species-specific accumulated stomatal O3 flux (POD6SPEC); and (iii) to drive O3 flux-biomass and flux-yield relationships in early and late sown cultivars from the two years experimental data for O3 risk assessment.
Section snippets
Field location and experimental set-up
The experiments were conducted in open-top chambers (OTCs) for two consecutive years (2016−2017 and 2017−2018) from November to March. The site is located at the Botanical Garden in the campus of Banaras Hindu University (BHU), Varanasi (25°16ʹ N, 82°59ʹ E, 81 m above mean sea level) in Uttar Pradesh, India. The details of OTCs construction were described in (Dolker and Agrawal, 2019). The soil texture of the experimental site was sandy loam (coarse) and had slightly basic pH of 7.3 ± 0.1 with
Weather conditions and ozone exposure
During the two years of the experiment, the 24-h mean air temperature, VPD and daylight PAR were slightly lower in the second year (Table 1). The total rainfall was 17 and 13 mm for the first (2016−2017) and second-year (2017−2018) growing season, respectively (Table 1). The accumulated O3 over a threshold of 40 ppb (AOT40) was 11.8 and 6.8 ppm h for early sown cultivars and 8.4 and 6.2 ppm h for late sown cultivars under AO3 treatments during the first and second year of experiment,
Discussion
The ambient O3 levels are determined by existing environmental conditions; therefore, a variation can be expected between years (Hayes et al., 2019; Pleijel et al., 2007). The variations in meteorology, particularly temperature, can alter the ambient O3 concentration and thus stomatal uptake (Hayes et al., 2019). These changes are in agreement with our results, which also showed a decline of accumulated POD6SPEC due to the reduction in seasonal mean temperature and O3 concentration in the
Conclusion
The present results of both observed and modelled studies confirmed that early sown cultivars showed greater O3 induced yield losses compared to late sown cultivars. However, the magnitude of yield reduction varied under both approaches due to the uncertainty of weather conditions and some limitations in the model to accurately parameterise for specific cultivars. From the results of O3 flux-effect relationship, it was found that the critical level of POD6SPEC for 5% reduction of above-ground
CRediT authorship contribution statement
Durgesh Singh Yadav: Investigation, Methodology, Validation, Software, Data curation, Writing - original draft. S.B. Agrawal: Supervision, Formal analysis, Visualization, Project administration, Writing - review & editing. Madhoolika Agrawal: Supervision, Conceptualization, Funding acquisition, Project administration, Writing - review & editing.
Declaration of Competing Interest
Authors declare that they have no conflict of interest.
Acknowledgements
This work was carried out under Interaction of Climate Extremes, Air Pollution and Agro-ecosystems (CiXPAG) project (grant no. 244551) from Research Council of Norway, Centre for International Climate Research (CICERO), Oslo, Norway in collaboration with Dr Jana Sillmann. The authors are thankful to the Head, Department of Botany, Banaras Hindu University and coordinators, CAS in Botany and Interdisciplinary School of Life Sciences for providing the instruments and necessary facilities in order
References (57)
- et al.
Nitrogen availability does not affect ozone flux-effect relationships for biomass in birch (Betula pendula) saplings
Sci. Total Environ.
(2019) - et al.
Assessment of rice yield loss due to exposure to ozone pollution in Southern Vietnam
Sci. Total Environ.
(2016) - et al.
Negative impacts of elevated ozone on dominant species of semi-natural grassland vegetation in Indo-Gangetic plain
Ecotoxicol. Environ. Saf.
(2019) - et al.
Effects of ozone on stomatal responses to environmental parameters (blue light, red light, CO2 and vapour pressure deficit) in three Populus deltoides × Populus nigra genotypes
Environ. Pollut.
(2013) - et al.
Modelling stomatal ozone flux across Europe
Environmental Pollution
(2000) - et al.
Ozone effects on crops and consideration in crop models
Eur. J. Agron.
(2018) - et al.
A stomatal ozone flux-response relationship to assess ozone-induced yield loss of winter wheat in subtropical China
Environ. Pollut.
(2012) Effects of ozone on managed pasture: I. Effects of open-top chambers on microclimate, ozone flux, and plant growth
Environ. Pollut.
(1994)- et al.
Updated stomatal flux and flux-effect models for wheat for quantifying effects of ozone on grain yield, grain mass and protein yield
Environ. Pollut.
(2012) - et al.
Wheat yield responses to stomatal uptake of ozone: peak vs rising background ozone conditions
Atmos. Environ.
(2018)
Physiological and visible injury responses in different growth stages of winter wheat to ozone stress and the protection of spermidine
Atmos. Pollut. Res.
The effect of ozone on below-ground carbon allocation in wheat
Environ. Pollut.
A synthesis of AOT40-based response functions and critical levels of ozone for agricultural and horticultural crops
Atmos. Environ.
New stomatal flux-based critical levels for ozone effects on vegetation
Atmos. Environ.
Differential response of dwarf and tall tropical wheat cultivars to elevated ozone with and without carbon dioxide enrichment: growth, yield and grain quality
Field Crop. Res.
Effects of ozone on maize (Zea mays L.) photosynthetic physiology, biomass and yield components based on exposure- and flux-response relationships
Environ. Pollut.
Growth stage dependence of the grain yield response to ozone in spring wheat (Triticum aestivum L.)
Agric. Ecosyst. Environ.
Relationships between ozone exposure and yield loss in European wheat and potato - A comparison of concentration- and flux-based exposure indices
Atmos. Environ.
Differential ozone sensitivity in an old and a modern Swedish wheat cultivar - Grain yield and quality, leaf chlorophyll and stomatal conductance
Environ. Exp. Bot.
Ozone risk assessment for agricultural crops in Europe: further development of stomatal flux and flux-response relationships for European wheat and potato
Atmos. Environ.
Elevated ozone and two modern wheat cultivars: an assessment of dose dependent sensitivity with respect to growth, reproductive and yield parameters
Environ. Exp. Bot.
Revisiting the crop yield loss in India attributable to ozone
Atmos. Environ.
Phenological weighting of ozone exposures in the calculation of critical levels for wheat, bean and plantain
Environmental Pollution
Changes in Nordic surface ozone episodes due to European emission reductions in the 1990s
Atmos. Environ.
In vivo root growth dynamics of ozone exposed Trifolium subterraneum
Environ. Exp. Bot.
Evaluation of the chronic effects of ozone on biomass loss of winter wheat based on ozone flux-response relationship with dynamical flux thresholds
Atmos. Environ.
ROS production and its detoxification in early and late sown cultivars of wheat under future O3 concentration
Sci. Total Environ.
Responses of an old and a modern Indian wheat cultivar to future O3 level: physiological, yield and grain quality parameters
Environ. Pollut.
Cited by (11)
Wheat yield response to elevated O<inf>3</inf> concentrations differs between the world's major producing regions
2024, Science of the Total EnvironmentIntroduction of modelling the impact of ground-level ozone on crops at a local and global scale
2023, Advances in Botanical ResearchEthylenediurea offers moderate protection against ozone-induced rice yield loss under high ozone pollution
2022, Science of the Total EnvironmentCitation Excerpt :Ozone enters plants mainly through leaf stomata and damages tissues and inhibits photosynthesis due to its strong oxidative property (Wittig et al., 2007). It can reduce crop yield and change grain quality of major field crops such as wheat, rice, soybean, and maize (Yadav et al., 2021; Mills et al., 2018; Feng et al., 2019b; Tai et al., 2014; McGrath et al., 2015). A large number of studies also suggested that O3 can cause crop yield losses at regional scales based on exposure- or dose-response relationships derived from field experiments (Ren et al., 2020; Hu et al., 2020; Feng et al., 2020; Zhao et al., 2020; Tang et al., 2014).
Evaluation of Toxicity of Tropospheric Ozone on Tomato (Solanum lycopersicum L.) Cultivars: ROS Production, Defense Strategies and Intraspecific Sensitivity
2023, Journal of Plant Growth RegulationElevated tropospheric ozone and crop production: potential negative effects and plant defense mechanisms
2023, Frontiers in Plant Science