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. 2003 Aug 19;100(17):10118-23.
doi: 10.1073/pnas.1734072100. Epub 2003 Aug 8.

Long-distance root-to-shoot transport of phytochelatins and cadmium in Arabidopsis

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Long-distance root-to-shoot transport of phytochelatins and cadmium in Arabidopsis

Ji-Ming Gong et al. Proc Natl Acad Sci U S A. .

Abstract

Phytochelatin synthases (PCS) mediate cellular heavy-metal resistance in plants, fungi, and worms. However, phytochelatins (PCs) are generally considered to function as intracellular heavy-metal detoxification mechanisms, and whether long-distance transport of PCs occurs during heavy-metal detoxification remains unknown. Here, wheat TaPCS1 cDNA expression was either targeted to Arabidopsis roots with the Arabidopsis alcohol dehydrogenase (Adh) promoter (Adh::TaPCS1/cad1-3) or ectopically expressed with the cauliflower mosaic virus 35S promoter (35S::TaPCS1/cad1-3) in the PC-deficient mutant cad1-3. Adh::TaPCS1/cad1-3 and 35S::TaPCS1/cad1-3 complemented the cadmium, mercury, and arsenic sensitivities of the cad1-3 mutant. Northern blot, RT-PCR, and Western blot analyses showed Adh promoter-driven TaPCS1 expression only in roots and thus demonstrated lack of long-distance TaPCS1 mRNA and protein transport in plants. Fluorescence HPLC analyses showed that under Cd2+ stress, no PCs were detectable in cad1-3. However, in Adh::TaPCS1/cad1-3 plants, PCs were detected in roots and in rosette leaves and stems. Inductively coupled plasma atomic emission spectrometer analyses showed that either root-specific or ectopic expression of TaPCS1 significantly enhanced long-distance Cd2+ transport into stems and rosette leaves. Unexpectedly, transgenic expression of TaPCS1 reduced Cd2+ accumulation in roots compared with cad1-3. The reduced Cd2+ accumulation in roots and enhanced root-to-shoot Cd2+ transport in transgenic plants were abrogated by l-buthionine sulfoximine. The presented findings show that (i) transgenic expression of TaPCS1 suppresses the heavy-metal sensitivity of cad1-3, (ii) PCs can be transported from roots to shoots, and (iii) transgenic expression of the TaPCS1 gene increases long-distance root-to-shoot Cd2+ transport and reduces Cd2+ accumulation in roots.

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Figures

Fig. 1.
Fig. 1.
TaPCS1 mRNA and protein are not translocated from roots to shoots. (A) Northern blots probing AtPCS1 expression in WT (Col-0) (row 1) and TaPCS1 expression using the root promoter in Adh/cad1-3 (Adh::TaPCS1/cad1-3) (row 2) and the ectopic promoter in 35S/cad1-3 (35S::TaPCS1/cad1-3) (row 3). 18S rRNA was used as loading control (row 4). (B) RT-PCR was performed with TaPCS1::myc fusion-specific primers. Actin was used as control. (C) Protein was extracted from stems (S), rosette leaves (L), and roots (R) of WT (Col-0), Adh/cad1-3 (Adh::TaPCS1/cad1-3), and 35S/cad1-3 (35S::TaPCS1/cad1-3) plants. Western blot analyses were performed as described in Materials and Methods. WT protein extracts were used as negative controls.
Fig. 2.
Fig. 2.
TaPCS1 complements Cd2+, Hg2+, and As sensitivity in cad1-3 at seedling stage. For all panels: Upper Left, cad1-3; Upper Right, Adh/cad1-3 (Adh::TaPCS1/cad1-3); Lower Left, 35S/cad1-3 (35S::TaPCS1/cad1-3); and Lower Right, WT (Col-0). Seeds were plated and horizontally germinated on one-quarter-strength Murashige and Skoog medium with no added heavy metals (A), 80 μM KH2AsO4 (B), 10 μM HgCl2 (C), and 40 μM CdCl2 (D). Photographs were taken after 21 days.
Fig. 3.
Fig. 3.
Heavy-metal tolerance in cad1-3 was restored completely or partially by ectopic or root-specific expression of TaPCS1. Four-week-old hydroponically grown cad1-3 mutant, Adh/cad1-3 (Adh::TaPCS1/cad1-3), 35S/cad1-3 (35S::TaPCS1/cad1-3), and WT plants were exposed to 20 μM CdCl2 for 3 days. Phenotypes were assessed for roots and rosette leaves (A) and stems (B and C). (B) Blue arrows show sites sensitive to Cd2+ stress in Adh::TaPCS1/cad1-3.
Fig. 4.
Fig. 4.
PCs can be transported from roots to shoots. Four-week-old plants were exposed to 20 μM CdCl2 for 3 days in hydroponic media, and PCs were extracted from root, leaf (rosette), and stem tissues of cad1-3 (A), WT Col-0 (B), 35S/cad1-3 (35S::TaPCS1/cad1-3)(C), and Adh/cad1-3 (Adh::TaPCS1/cad1-3)(D). PC levels were measured by fluorescence HPLC. (E) Synthesized PC2, PC3, and PC4 (2 μM each) PC standards were measured, and three copies of standard measurements are illustrated for easy comparison to the measured samples. PC2, PC3, and PC4 peaks are indicated by arrows.
Fig. 5.
Fig. 5.
Enhanced long-distance Cd2+ transport and reduced Cd2+ accumulation in roots by transgenic expression of TaPCS1. Four-week-old 35S/cad1-3 (35S::TaPCS1/cad1-3), Adh/cad1-3 (Adh::TaPCS1/cad1-3), WT (WT Col-0), and cad1-3 plants grown in hydroponic solution were exposed to 20 μM CdCl2. Samples were harvested at timed intervals after Cd2+ exposure as indicated. Cd2+ accumulation in stems (A), rosette leaves (B), and roots (C) was determined by ICP-AES. Data show mean values ± SE, n = 6 plants.
Fig. 6.
Fig. 6.
Short-term BSO exposure mimics the effect of AtPCS1 gene disruption in cad1-3 with respect to Cd2+ accumulation in roots and shoots. Four-week-old cad1-3, Adh/cad1-3 (Adh::TaPCS1/cad1-3), 35S/cad1-3 (35S::TaPCS1/cad1-3), and WT plants grown in hydroponic solution were pretreated with 0 mM/1 mM BSO for 12 h; 20 μM CdCl2 was then applied to either the untreated plants (A) or the 1 mM BSO pretreated plants with 0.5 mM BSO for 54 h (B). Cd2+ accumulation in stems (S), rosette leaves (L), and roots (R) was determined by ICP-AES. Data show mean values ± SE, n = 6 and 3 plants in A and B, respectively.

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