| Abstract: | Rice (Oryza sativa) is the staple food for over half the world''s population yet may represent a significant dietary source of inorganic arsenic (As), a nonthreshold, class 1 human carcinogen. Rice grain As is dominated by the inorganic species, and the organic species dimethylarsinic acid (DMA). To investigate how As species are unloaded into grain rice, panicles were excised during grain filling and hydroponically pulsed with arsenite, arsenate, glutathione-complexed As, or DMA. Total As concentrations in flag leaf, grain, and husk, were quantified by inductively coupled plasma mass spectroscopy and As speciation in the fresh grain was determined by x-ray absorption near-edge spectroscopy. The roles of phloem and xylem transport were investigated by applying a ± stem-girdling treatment to a second set of panicles, limiting phloem transport to the grain in panicles pulsed with arsenite or DMA. The results demonstrate that DMA is translocated to the rice grain with over an order magnitude greater efficiency than inorganic species and is more mobile than arsenite in both the phloem and the xylem. Phloem transport accounted for 90% of arsenite, and 55% of DMA, transport to the grain. Synchrotron x-ray fluorescence mapping and fluorescence microtomography revealed marked differences in the pattern of As unloading into the grain between DMA and arsenite-challenged grain. Arsenite was retained in the ovular vascular trace and DMA dispersed throughout the external grain parts and into the endosperm. This study also demonstrates that DMA speciation is altered in planta, potentially through complexation with thiols.Paddy rice (Oryza sativa) is particularly effective, compared to other cereals, at accumulating arsenic (As) in shoot and grain (Williams et al., 2007b). Rice is the staple food for over half the world''s population (Fageria, 2007) and rice represents a significant dietary source of inorganic As, a class 1, nonthreshold carcinogen, particularly in Southeast Asia (Meharg et al., 2009). Inorganic As levels in rice grain are problematic even where soil As is at background levels, derived from geogenic sources (Lu et al., 2009; Meharg et al., 2009). However, widespread pollution of paddy soils with As, leading to further elevation of grain As, has occurred in some regions due to base and precious mining (Liao et al., 2005; Zhu et al., 2008), irrigation of paddies with As-elevated groundwaters (e.g. Meharg and Rahman, 2003; Williams et al., 2006), and the use of arsenical pesticides (Williams et al., 2007a). Unlike other cereal grains, paddy rice cultivation is dependent of soils being anaerobic, and it is this anoxia that gives rise to elevated As concentrations in the plant. Anaerobic soil conditions lead to the mobilization of As as arsenite, where under aerobic systems arsenate dominates (Xu et al., 2008). Arsenite is efficiently assimilated by rice roots through silicic acid transport pathway (Ma et al., 2008).Knowledge of As metabolism and partitioning within plants, particularly rice, is still developing rapidly (Zhao et al., 2009). Several studies have now shown that As in rice vegetative tissue and grain is predominantly speciated as inorganic As and the methylated species dimethylarsinic acid (DMA), with variable, though low, levels of monomethyl arsonic acid (MMA; Abedin et al., 2002a; Williams et al., 2005, 2006; Norton et al., 2009). Arsenate is an analog of phosphate and competes with phosphate for rice root uptake (Abedin et al., 2002a) while arsenite is taken up by rice roots via silicic acid transporters (Ma et al., 2008). Abedin et al. (2002b) demonstrated that the methylated species DMA and MMA are also taken up by rice plants although at a much slower rate than inorganic As, with the protonated neutral forms also transported through silicic acid pathway (Li et al., 2009). Arsenate is reduced to arsenite within the rice root (Xu et al., 2008; Zhao et al., 2009), which then enters the xylem via a silicic acid/arsenite effluxer (Ma et al., 2008; Zhao et al., 2009). Arsenite may be detoxified through complexation with thiol-rich peptides including phytochelatins (PCs) and glutathione followed by sequestration into vacuoles (Bleeker et al., 2006; Raab et al., 2007b; Zhao et al., 2009). Raab et al. (2007a) found that while methylated As species are taken up by rice roots much less efficiently than inorganic species, they appear to be translocated within the plant more efficiently. The comparative contributions of xylem and phloem transport, in translocation of As to the grain, are unknown.The main species within rice grain, along with DMA, are inorganic As, particularly arsenite, which may be complexed with thiols (Williams et al., 2005; Lombi et al., 2009). Nutrients are unloaded into the grain from the ovular vascular trace (OVT) into the nucellar tissue and from there are uploaded, via the apoplast into the filial tissue (the aleurone and the endosperm; Krishnan and Dayanandan, 2003). Lombi et al. (2009) recently suggested that this may represent a physiological barrier that As species cross with differential efficiency. However, the transport and unloading of As to/into the grain, which are key processes in terms of human exposure to this contaminant, are far from being fully understood.This study investigated the differential efficiency with which important As species are translocated and unloaded into the rice grain and the comparative contributions of phloem and xylem transport. Rice panicles were excised below the flag leaf node during grain development, 10 DPA, and treated to a hydroponically administered 48-h pulse of arsenite, arsenate, arsenite glutathione, or DMA. Total As concentrations in flag leaf, grain, and husk samples for each treatment were quantified by inductively coupled plasma mass spectroscopy (ICP-MS), and As speciation in the fresh grain was determined by x-ray absorption near-edge spectroscopy (XANES) analysis. To evaluate the contributions of phloem versus xylem transport, a stem-girdling treatment was applied, using steam to destroy phloem cells in a second set of panicles prior to a pulse of either DMA or arsenite. The spatial unloading of As species into the developing grain was examined by synchrotron x-ray fluorescence (XRF) mapping, and fluorescence microtomography for the DMA and arsenite treatments. |
