Review articleGenetic regulation of homeostasis, uptake, bio-fortification and efficiency enhancement of iron in rice
Introduction
Iron (Fe) is an essential micronutrient for growth, development and higher grain yield of rice (Wu et al., 2014; Aung et al., 2019; Zhang et al., 2018; Pradhan et al., 2020). It plays an important role in chloroplast development, chlorophyll synthesis, photosynthesis, nitrogen metabolism, respiration, enzymatic redox reactions and acts as an important electron donor (Taiz and Zeiger, 1991; Marschner, 1995; Sahrawat, 2005; Kobayashi and Nishizawa, 2012; Rout and Sahoo, 2015; Zhang et al., 2017). Abiotic stresses due to deficiency or excess of available Fe in soil cause nutritional disorder in rice plants. Fe-related soil stresses are commonly seen in many rice growing countries of the world. Deficiency of this nutrient in human also results serious health issues. More than two billion people suffer from Fe deficiency annually, which results in mortality of about 0.8 million people in the world (Stoltzfus and Dreyfuss, 1998; Wessells and Brown, 2012; Arcanjo et al., 2013; Simbauranga et al., 2015; Freitas et al., 2016: Trijatmiko et al., 2016; WHO, 2016; Dos Santos et al., 2017; Swamy et al., 2018). More than half of the world population, mostly from developing countries, is suffering from bioavailable micronutrient deficiencies (Seshadri, 2001; Shahzad et al., 2014; Mahender et al., 2016; Sarma et al., 2018). Micronutrient supplementation, food fortification and biofortification are the common ways to overcome this deficiency related problems. Fe-biofortification in rice will be a useful strategy to solve the problem of Fe-deficiency for the poor people in developing countries, for whom rice is the staple food (Nakandalage et al., 2016; Swamy et al., 2016; Trijatmiko et al., 2016).
High yielding modern rice varieties are poor in grain-Fe content (Zimmermann and Hurrell, 2002; Brinch-Pedersen et al., 2007; Mahender et al., 2016). However, genetic variations exists for Fe content in grains of rice germplasms (Yang et al., 1998; Jiang et al., 2008; Jahan et al., 2013; Zeng et al., 2010; Mahender et al., 2016; Trijatmiko et al., 2016). Commonly grown rice varieties contain only 7–8 μg g−1, however, few germplasm lines contain upto 147 μg g−1 in brown rice (Zeng et al., 2010). Fe content in rice grain can be enhanced many folds using transgenic approach. Once stable transgenic donor line is obtained, the increased Fe-content can be transferred to high yielding varieties through molecular breeding approaches (Masuda et al., 2013).
The deficiency of Fe is a major constraint for achieving higher yield in rice under alkaline calcareous soil with higher pH (Marcher, 1995; Kim and Guerinot, 2007). About 30% of the global soils are alkaline in nature which suffer from Fe-deficiency. Rice grown in such soils produces low yield with poor quality (Abadia et al., 2011; Swamy et al., 2018). Low availability of Fe in soils often causes leaf chlorosis and less photosynthesis, leading to reduction in yield and quality of rice. However, tolerant rice plants cope up with the soil deficiency condition through various morphological, physiological and differential gene expression strategies. Under such insufficient soil Fe condition, two absorption strategies have been developed by rice plants. Rice root shows symptoms of cluster roots and swelling of apical root tips under deficiency of iron (Schmidt et al., 2000; Schikora and Schmidt, 2002). Again, the practice of consuming polished rice reduces Fe content in the grains.
Accumulation in higher concentration of Fe is toxic to rice plant (Howeler, 1973; Prade et al., 1993; Jugsujinda and Patrick, 1993; Genon et al., 1994; Audebert, 2006; Becker and Asch, 2005; Chérif et al., 2009; Audebert and Fofana, 2009; Stein et al., 2009; Sikirou et al., 2015, 2016; Zhang et al., 2018). Rice rhizosphere is considered as the first line of defence against excess Fe-uptake. Toxicity is commonly observed in lowland rice ecology showing abundance of soluble ferrous (Fe2+) in soil. It generates reactive oxygen species (ROS) and hydroxyl radicals (OH) under the toxic situation. These compounds damage the rice plants there by reduce grain yield. The problem is very severe in West and Central African countries (Sikirou et al., 2015; Oort, 2018). The toxicity is also observed in Burundi, Benin, Ivory Coast, Burkina Faso, Niger, Gambia, Guinea, Guinea-Bissau, Liberia, Nigeria, Senegal, Sierra Leone, Togo, India, China, Indonesia, Malaysia, Thailand, Philippines, Sri Lanka, Colombia, Vietnam and Brazil (Moorman and Van Breeman, 1978; Oort, 2018). The area coverage with Fe-rich soils in Africa is estimated to be about 427 million ha (Oort, 2018). Rice yield loss due to this problem in Africa varies from 12% to 100% (Audebert and Sahrawat, 2000). In India, around 2 million ha of rice area are affected by Fe-toxicity (Prasad et al., 2020). Parts of Odisha, Kerala, Tamil Nadu and north-eastern states of India face this problem (Pawar et al., 2017).
Biofortification usually refers to the process of enriching food grains for nutritive elements in crop plants through genetic approaches. This way of enriching food grains is an easy, effective and cheaper way to supplement micronutrient deficiencies in cereal crops and much cheaper to grains fortification. The popular high yielding varieties are poor in essential micronutrients and need to be biofortified to enhance the nutritive value. Adequate variability for Fe-content exists in natural rice population. By over-expressing ferritin gene, Fe-content was increased to many folds in transgenic rice lines compared to the control genotypes. Transgenic rice lines with higher Fe-content derived from other crops are already available for successful crop improvement programme (Goto et al., 1999; Lee et al., 2009; Ogo et al., 2011; Kobayashi and Nishizawa, 2012; Lee et al., 2012; Paul et al., 2012; Bashir et al., 2013; Masuda et al., 2013; Slamet-Loedin et al., 2015; Trijatmiko et al., 2016; Boonyaves et al., 2017). These transgenic lines may be useful as potential donors by the rice breeders for enhancing of grain-Fe content in popular rice varieties through molecular breeding approach. Micronutrients improvement may not be antagonistic to grain yield enhancement in rice as there is the presence of separate genomic regions controlling micronutrient traits in major crops (Welch and Graham, 2004; Pradhan et al., 2019, 2020).
Section snippets
Fe uptake mechanisms from rhizosphere to rice roots
Fe is commonly available in ferric (Fe3+) and ferrous (Fe2+) forms in soil. This element is abundantly found in aerobic soils as Fe3+ polymeric insoluble form, which is not available for uptake by rice plants and causing Fe-deficiency. Under alkaline soil, Fe2+ oxidizes to Fe3+ during electron transfer process. Deficiency of this element results in reduction of non-heme Fe-proteins involved in photosynthesis, N2 fixation and respiration (Taiz and Zeiger, 1991). It also reduces functioning of
Strategies of maintaining Fe-toxicity tolerance by rice plants
Increased metabolism of scavengers protein in tolerant plants helps avoiding oxidative stress in the plants. For scavenging of hydroxyl radicals and ROS, plant produces wide varieties of phenolic compounds scavengers such as tannins, lignin and flavonoids (Blokhina et al., 2003). Plant store Fe2+ in leaf sheath which is harmful for photosynthesis and yield (Engel et al., 2012). Excess metal ions are stored in the vacuole and are released during deficiency condition (Moore et al., 2014). The
Enhancing Fe uptake in rice using genes/QTLs under Fe-deficiency situations
Fe-deficiency stress to plants can be tolerated by improving the transporter genes. Two transporter genes, OsIRT1 and OsYSL15 are used to increase the Fe concentrations in seeds produced under low Fe availability condition by over expression approach (Table 1). Expression of transporter gene, OsYSL15 increases the level of Fe3+–MAs under Fe-deficiency situations to increase the uptake of Fe (Curie et al., 2001; Lee et al., 2009; Ueno et al., 2009; Li et al., 2016). Nicotianamine
Genes/QTLs useful for enhancing tolerance under Fe toxicity condition
Genes governing tolerance to Fe toxicity have been reported in rice using various mapping populations (Table 2). Using Azucena and IR64 derived population, it was observed that leaf bronzing index (LBI) is controlled by QTL present on chromosome 1 (Dufey et al., 2009). Seven QTLs were detected for LBI on chromosome 1, 2, 7, 8 and 12 showing 99% of phenotypic variation by analyzing the mapping population of Gimbozu and Kasalath (Shimizu, 2009). These chromosomal regions were also detected
Genes/QTLs identified for enhancing grain Fe content
A wide genotypic variation for grain Fe content is available in rice germplasms (Qui et al., 1995; Ahmed et al., 1998; Graham et al., 1999; Gregorio et al., 2000; Zhang et al., 2005; Anuradha et al., 2012a, b; Mahender et al., 2016; Swamy et al., 2016). Increasing the iron content in rice grain through breeding approach is a cheaper way and an easier option. Knowledge on genes/QTLs controlling grain Fe is pre-requisite for enhancement of the trait. Few reports on mapping results on grain-Fe
Iron deficiency and toxicity symptoms in rice
The Fe deficiency symptoms are commonly seen in young and emerging leaves because of its immobile nature. Interveinal yellowing and chlorosis of leaves are usually found but turn pale and plant die under severe deficiency situation (Kobayashi and Nishizawa, 2014). The roots may be affected and converted into chimeric and necrotic epidermis (Morrissey and Guerinot, 2009; Giehl et al., 2012; Gruber et al., 2013). Under deficiency of this nutrient, chlorophyll content reduces which decreases
Screening strategies for Fe deficiency and toxicity tolerance in rice
The commonly followed phenotypic screenings for Fe deficiency and toxicity tolerance in rice by researchers are performed in hotspot locations, potted plants and under hydroponic screening approaches. Hotspot screening is the most common screening method in a place where Fe toxicity or deficiency spots or locations exist naturally. The stress symptoms are easily observed in susceptible rice varieties. In pot screening, toxic or deficient soils for Fe ions are supplied in pots for screening of
Breeding for enhancing Fe toxicity tolerance in rice
Various breeding programs were started systematically in African countriessince 1974. Initially, rice varieties were introduced for testing and evaluation in Western African countries. Few good varieties were released from this program. Suakoko 8, a variety released for Liberia, become very popular and till date is being used as national check for Fe toxicity tolerance. Another introduced variety ROK 24 was released for Sierra Leone. These introduced varieties were good for Fe toxicity
Conclusion
Many genes/QTLs responsible for Fe-uptake from rhizosphere, transport from roots to shoots and other plant parts and their regulation are now known. Those reported genes/QTLs for the stress tolerance are still not properly validated and utilized in the breeding programs. Additionally, more genes/QTLs contributing towards high phenotypic variance to these stresses tolerance need to be identified. Hence, efforts are needed for inclusion of modern techniques like genome editing, genome
Author contributions
SKP conceived the idea for preparation of the manuscript and outlined the content. SKP, EP, SP, AP, HP helped in writing of the manuscript. SKP, EP, LB, SRD, HP revised the manuscript.
Funding
No funding involved in this article.
Declaration of Competing Interest
The authors declare that the review article was submitted without any commercial or economic interest that could be construed as a potential conflict of interest.
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Authors contributed equally.