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).