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JAEA-Review-2010-065.pdf:15.99MB - 日本原子力研究開発機構

JAEA-Review-2010-065.pdf:15.99MB - 日本原子力研究開発機構

JAEA-Review-2010-065.pdf:15.99MB - 日本原子力研究開発機構

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3-48<br />

Visualization of 107 Cd Accumulation<br />

in Oilseed Rape Plants Treated with Glutathione<br />

S. Nakamura a) , N. Suzui b) , S. Ito b) , N. Kawachi b) , N. S. Ishioka b) ,<br />

H. Rai a) , H. Hattori a) , M. Chino a) and S. Fujimaki b)<br />

a) Faculty of Bioresource Sciences, Akita Prefectural University,<br />

b) Radiation-Applied Biology Division, QuBS, <strong>JAEA</strong><br />

Cadmium (Cd) is one of toxic heavy metals. Cd<br />

accumulation in human bodies leads to serious health<br />

problems. Cd accumulates in human bodies mainly<br />

through consumption of agricultural products. It is<br />

necessary to reduce Cd accumulation in agricultural<br />

products in order to inhibit Cd accumulation in human<br />

bodies. However, critical technologies to reduce Cd<br />

accumulation in agricultural products have not yet been<br />

realized. To realize these technologies, it is needed to<br />

understand mechanisms of Cd long-distance transport and<br />

Cd accumulation in higher plants. However, these<br />

mechanisms are not well understood so far. Glutathione<br />

(GSH) is a major low molecular weight thiol tripeptide,<br />

consisting of cysteine, glutamic acid, and glycine. GSH is<br />

involved in many aspects of metabolism in plants. In our<br />

previous work, GSH concentration in the phloem sap<br />

collected from oilseed rape plants increased by Cd<br />

1)<br />

treatment . These results suggested that GSH might be<br />

playing important roles in controlling Cd long-distance<br />

transport and accumulation in plants. In this work, we<br />

investigated effects of GSH to Cd long-distance transport<br />

and accumulation by using positron emitting tracer imaging<br />

system (PETIS). PETIS is a planner imaging system. We<br />

can obtain serial images of distribution of positron emitting<br />

2)<br />

molecules in the plant body non-invasively . We already<br />

have succeeded in visualizing Cd absorption, transport and<br />

3)<br />

accumulation in rice plants by using PETIS .<br />

107<br />

Cd (half-life: 6.5 h) was used as positron-emitting<br />

radioactive tracer in our PETIS experiments. 107 Cd was<br />

produced by bombarding silver plate with an energetic<br />

proton beam delivered from AVF cyclotron at TIARA<br />

(Takasaki Ion Accelerators for Advanced Radiation<br />

Application). Produced 107 Cd was purified, following the<br />

4) 107<br />

method of Ishioka et al . Purified Cd was used for<br />

PETIS experiments. Oilseed rape plants (Brassica napus)<br />

were grown hydroponically in a growth chamber where the<br />

plant growth conditions were controlled completely for two<br />

weeks after sowing. PETIS experiments were also<br />

performed in the growth chamber under controlled growth<br />

conditions. After setting two week old oilseed rape plants<br />

in the chamber, PETIS experiments were started by adding<br />

purified 107 Cd in the nutrient solutions which were including<br />

GSH. In these experiments, 10 M Cd was added to<br />

hydroponic solutions as a carrier. Time-series images of<br />

the 107 Cd distribution were obtained every four minute for<br />

36 h. After PETIS experiments, 107 Cd accumulation in the<br />

plant body of oilseed rape plants were investigated<br />

<strong>JAEA</strong>-<strong>Review</strong> <strong>2010</strong>-065<br />

- 104 -<br />

thoroughly by using an imaging instrument (BAS-1500;<br />

Fujifilm, Tokyo, Japan).<br />

We succeeded to obtain fine serial images of Cd transport<br />

and accumulation in oilseed rape plants (data not shown).<br />

We also succeeded to obtain images of 107 Cd accumulation<br />

in these plants by using an imaging instrument (Fig. 1).<br />

107 Cd signals were observed in the shoot and root of oilseed<br />

rape plants. In the shoot, Cd accumulation was inhibited<br />

by GSH treatment (Fig. 1A and 1B). However, we could<br />

not see any difference in the Cd accumulation in the root of<br />

oilseed rape plants (Fig. 1C and 1D). Further research<br />

enables us to understand effects of GSH on Cd long-distance<br />

transport and accumulation in oilseed rape plants.<br />

References<br />

1) S. Nakamura et al., Sulfur Transport and Assimilation in<br />

Plants in the Post Genomic Era (2005) 229-232.<br />

2) S. Fujimaki, ITE Let. (2007) 8, C1-C10.<br />

3) S. Fujimaki et al., Plant Physiol. 152 (<strong>2010</strong>) 1796-1806.<br />

4) N. S. Ishioka et al., <strong>JAEA</strong> Takasaki Ann. Rep. 2005<br />

(2006) 162.<br />

A. B.<br />

C. D.<br />

Fig. 1 107 Cd accumulation in the plant body of oilseed<br />

rape plants. These images were obtained by using<br />

an imaging instrument (BAS-1500). A; Shoot of<br />

oilseed rape plant (Control), B; Shoot of oilseed rape<br />

plant (GSH treated), C; Root of oilseed rape plant<br />

(Control), D; Root of oilseed rape plant (GSH<br />

treated).

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