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First published online October 29, 2004; 10.1104/pp.104.044503 Plant Physiology 136:3814-3823 (2004) © 2004 American Society of Plant Biologists Identification of Thlaspi caerulescens Genes That May Be Involved in Heavy Metal Hyperaccumulation and Tolerance. Characterization of a Novel Heavy Metal Transporting ATPase1United States Plant, Soil and Nutrition Laboratory, United States Department of Agriculture, Agricultural Research Service, Cornell University, Ithaca, New York 14853
Thlaspi caerulescens is a heavy metal hyperaccumulator plant species that is able to accumulate extremely high levels of zinc (Zn) and cadmium (Cd) in its shoots (30,000 µg g–1 Zn and 10,000 µg g–1 Cd), and has been the subject of intense research as a model plant to gain a better understanding of the mechanisms of heavy metal hyperaccumulation and tolerance and as a source of genes for developing plant species better suited for the phytoremediation of metal-contaminated soils. In this study, we report on the results of a yeast (Saccharomyces cerevisae) complementation screen aimed at identifying candidate heavy metal tolerance genes in T. caerulescens. A number of Thlaspi genes that conferred Cd tolerance to yeast were identified, including possible metal-binding ligands from the metallothionein gene family, and a P-type ATPase that is a member of the P1B subfamily of purported heavy metal-translocating ATPases. A detailed characterization of the Thlaspi heavy metal ATPase, TcHMA4, demonstrated that it mediates yeast metal tolerance via active efflux of a number of different heavy metals (Cd, Zn, lead [Pb], and copper [Cu]) out of the cell. However, in T. caerulescens, based on differences in tissue-specific and metal-responsive expression of this transporter compared with its homolog in Arabidopsis (Arabidopsis thaliana), we suggest that it may not be involved in metal tolerance. Instead, we hypothesize that it may play a role in xylem loading of metals and thus could be a key player in the hyperaccumulation phenotype expressed in T. caerulescens. Additionally, evidence is presented showing that the C terminus of the TcHMA4 protein, which contains numerous possible heavy metal-binding His and Cys repeats residues, participates in heavy metal binding. When partial peptides from this C-terminal domain were expressed in yeast, they conferred an extremely high level of Cd tolerance and Cd hyperaccumulation. The possibilities for enhancing the metal tolerance and phytoremediation potential of higher plants via expression of these metal-binding peptides are also discussed.
There are a small number of terrestrial plant species that not only can tolerate high levels of toxic heavy metals in the soil but also can accumulate those metals to unusually high levels in their shoot biomass. These fascinating plant species, first coined hyperaccumulators by Brooks et al. (1977)  , are loosely categorized as plants that can accumulate metals in the shoot from 100- to 1,000-fold higher than normal, nonaccumulator plants (McGrath et al., 2002). Hyperaccumulating plant species have been identified for a number of heavy metals, including nickel (Ni), zinc (Zn), and cadmium (Cd), as well as for the metalloids selenium and arsenic. Probably the best known metal hyperaccumulator is Thlaspi caerulescens, a member of the Brassica family that has been the object of interest in the plant biology community for over a century, based on its ability to colonize calamine and serpentine soils containing naturally elevated levels of heavy metals such as Zn, Cd, Ni, and cobalt (Co). Certain ecotypes of T. caerulescens can accumulate Zn and Cd to extremely high levels in the shoot, with Zn reaching levels as high as 30,000 µg g–1 (Brown et al., 1995) and shoot Cd concentrations of 10,000 µg g–1 (Lombi et al., 2000). By comparison, shoot Zn concentrations in Zn-sufficient nonaccumulator plants are around 100 µg g–1, with 30 µg g–1 adequate and 300 to 500 µg g–1 toxic (Mengel and Kirkby, 1987); foliar Cd levels above 1 to 10 µg g–1 are usually toxic. The growing awareness by the plant biology community regarding metal hyperaccumulating plants has, in part, spurred the considerable recent interest and research activity into phytoremediation as a "green" technology for the clean up of heavy metal-contaminated soils. A number of laboratories around the world are studying metal hyperaccumulators, such as T. caerulescens, as model plant systems to gain a better understanding of the mechanisms of heavy metal hyperaccumulation and tolerance, as well as a potential source of genes for developing high biomass plant species that are better suited for phytoremediation of metal-contaminated soils.
Our laboratory has been studying the physiology and molecular biology of heavy metal hyperaccumulation in T. caerulescens and has previously shown that altered metal ion transport plays an important role in the hyperaccumulation phenotype in this plant species (Lasat et al., 1996
This study focused on the identification of candidate heavy metal tolerance genes from T. caerulescens via a yeast (Saccharomyces cerevisae)-functional complementation screen. A number of Thlaspi genes that conferred Cd tolerance to yeast were identified, including possible metal-binding ligands from the metallothionein gene family, and a P-type ATPase that is a member of the P1B subfamily of purported heavy metal-translocating ATPases (Axelsen and Palmgren, 1998
Complementation Screening of Candidate Metal Tolerance Genes from T. caerulescens Preliminary studies determined that when 90 µM Cd was included in solid modified synthetic dextrose (SD) media (see "Materials and Methods"), both the wild-type DY1457 yeast strain as well as DY1457 transformed with the empty pFL61 vector were unable to grow. Thus, this Cd level was used to select for Cd-tolerant transformants. Yeast cells were transformed with a T. caerulescens cDNA library constructed in the yeast expression vector, pFL61, and 35 yeast colonies were identified that were able to grow on this restrictive level of Cd. Yeast from each colony was grown up and replated on the same high Cd media to verify the Cd-tolerant phenotype. Subsequently, the plasmids bearing the T. caerulescens cDNA inserts were isolated, and the Thlaspi cDNAs were subjected to restriction digest analysis and DNA sequencing. Based on this analysis, seven unique Thlaspi genes were identified that conferred Cd tolerance to wild-type yeast. As depicted in Table I, which lists the identity of each of these putative metal tolerance genes, two had a close resemblance to metallothionein genes previously identified in Arabidopsis and Brassica juncea. Four of the other genes either had an unknown function based on DNA and protein sequence comparisons, or could play roles in processes such as photosynthesis, protein synthesis, or signal transduction. The final gene on the list in Table I was represented by two different length partial cDNA clones (423 and 1,152 bp in length) that had a strong similarity to the Arabidopsis heavy metal-transporting ATPase, AtHMA4. RACE-PCR techniques using the GeneRacer kit (Invitrogen Life Technologies, Carlsbad, CA) were employed to clone the full-length TcHMA4 cDNA from T. caerulescens. This technique targets only the 5' end-capped mRNA, and thus allows for the cloning of only the full-length cDNA. Because of the possible importance of heavy metal ATPases to metal hyperaccumulation and tolerance in T. caerulescens, our subsequent research focused on a detailed characterization of TcHMA4.
Both nucleotide and amino acid sequence comparisons between TcHMA4 and similar sequences from other organisms indicated that it is a member of the P-type ATPase superfamily and, more specifically, the P1B subfamily of ATPases that are purported to transport heavy metals. As mentioned above, the Arabidopsis P-type ATPase that it is most similar to is AtHMA4, which was recently shown to possibly be involved in Cd export and tolerance (Mills et al., 2003 ). The deduced amino acid sequence for TcHMA4 and its alignment with AtHMA4 are shown in Figure 1. The full-length TcHMA4 open reading frame is 3,561 bp in length and encodes a polypeptide of 1,186 amino acids. TcHMA4 is 71% identical to AtHMA4 and contains many of the same predicted motifs found in AtHMA4 and other heavy metal ATPases, including eight predicted membrane-spanning domains, and a large C-terminal tail that harbors a number of putative heavy metal-binding domains (see Fig. 1). These include a His repeat consisting of nine His residues, a number of Cys pairs, and multiple single His residues.
Expression of TcHMA4 in Yeast Confers Heavy Metal Tolerance When wild-type yeast is transformed with the full-length TcHMA4, a significant level of Cd tolerance is conferred. As shown in Figure 2, growth of both the wild-type yeast expressing the empty pFL61 vector, and the untransformed wild-type strain (not shown) are strongly inhibited by inclusion of 75 and 90 µM Cd in solid SD media, while expression of TcHMA4 in yeast allows a significant increase in growth on both levels of Cd and also promotes growth compared with wild-type yeast on Cd concentrations as high as 120 µM (data not shown).
Heavy Metal Accumulation in Wild-Type and TcHMA4-Transformed Yeast A plant transporter can confer metal tolerance when expressed in yeast either via mediating metal exclusion due to efflux across the plasma membrane or by sequestering the metal in an endomembrane compartment. The first scenario should result in reduced metal accumulation in yeast, while the second should cause enhanced metal accumulation. Thus, metal accumulation experiments were conducted with wild-type yeast expressing empty pFL61 and TcHMA4-transformed yeast; these experiments involved incubating both yeast genotypes in liquid SD media supplemented with either 20 µM CdCl2 or 10 µM PbCl2, ZnCl2, or CuCl2 and harvesting yeast cells after 30 and 70 min of metal accumulation. As shown in Figure 3, expression of TcHMA4 in yeast resulted in a large decrease in both Cd (Fig. 3A) and Pb (Fig. 3B) accumulation. After both 30 and 70 min of metal accumulation, TcHMA4-transformed cells accumulated approximately 70% less Cd and 50% less Pb. TcHMA4-transformed cells also accumulated less Zn and Cu than wild-type cells (data not shown). These findings are consistent with TcHMA4 operating at the yeast plasma membrane to pump metals out of the cell and having the ability to transport a number of different essential micronutrients and heavy metals.
Quantitation of 109Cd Efflux and Influx In order to more conclusively determine if TcHMA4 is functioning to pump metals across the yeast plasma membrane and out of the cell, 109Cd flux techniques were used to quantify Cd influx and efflux in control and TcHMA4-transformed yeast. As depicted in Figure 4, short-term 109Cd uptake experiments showed that there were no differences in Cd influx in control versus TcHMA4-transformed cells. However, when both yeast genotypes were loaded with 109Cd and allowed to efflux radiotracer into identical, unlabeled solution, the TcHMA4-transformed cells maintained a 3.5-fold higher rate of Cd efflux than did control cells not expressing the Thlaspi ATPase. These results further support the hypothesis that TcHMA4 is a metal efflux transporter operating at the plasma membrane. It is interesting to note than in these cells, the rates of Cd influx were 2- to 6-fold larger than Cd efflux, indicating that a net Cd uptake was occurring, which presumably is associated with rapidly growing and dividing cells in the mid-log phase of growth.
Tissue-Specific Expression of TcHMA4 in T. caerulescens The expression of TcHMA4 in different plant tissues and in response to changes in plant mineral nutrient and heavy metal status were investigated via northern analysis in T. caerulescens seedlings. For this northern analysis, we used a 1,500-bp probe from the C-terminal region of TcHMA4 to avoid cross-hybridization with other HMAs (heavy metal associated). The C-terminal sequence is the most divergent region for the HMA subfamily of transporters. Southern analysis using this same 1,500-bp probe with T. caerulescens genomic DNA under the same stringency conditions used for the northern blots yielded results consistent with hybridization to a single copy of TcHMA4 in the genome (data not shown). These results suggest that the northern-analysis data are not complicated by hybridization of TcHMA4 to other members of the TcHMA subfamily.
As depicted in Figure 5, TcHMA4 is expressed strongly in roots, and we also found a very low level of expression in aboveground plant tissues and organs (data not shown). This finding suggests that TcHMA4 is primarily a root-associated metal transporter. With regards to the relationship of TcHMA4 expression and plant Zn status, both Zn deficiency as well as exposure of plants to high Zn levels induced a significant increase in TcHMA4 transcript abundance (Fig. 5). Furthermore, when plants were challenged with high levels of Cd in the nutrient solution, this also induced a strong increase in TcHMA4 expression (Fig. 5). This response to increasing plant Cd status in T. caerulescens is quite different than what has been reported for its homolog in Arabidopsis, where it has been shown that root expression of AtHMA4 is down-regulated by plant exposure to Cd (Mills et al., 2003
Analysis of Partial TcHMA4 Clones As described above for the initial yeast complementation screen for Thlaspi Cd tolerance genes, two different partial TcHMA4 clones conferred a significant degree of Cd tolerance when expressed in yeast. These two clones encode peptides predicted to be 384 and 141 amino acids in length that encompass most (for the 384-amino acid peptide) or a portion (for the 141-amino acid peptide) of the large C-terminal cytoplasmic tail of TcHMA4 that harbors a number of putative heavy metal-binding domains (Fig. 6). These domains include a number of Cys pairs, a His-9 repeat, and numerous single His residues. As neither of these peptides contain any predicted membrane-spanning domains, it is clear that they are not functioning as metal transporters. Thus, the possibility that they confer heavy metal tolerance in yeast by acting as metal-binding peptide ligands in the yeast cytoplasm was investigated. As shown in Figure 7, both the 141- and 341-amino acid peptides conferred a very high degree of Cd tolerance, resulting in significant yeast growth even in solid media supplemented with 200 µM CdCl2. Thus these peptides confer a considerably higher degree of tolerance than does the full TcHMA4 protein, as yeast expressing the full TcHMA4 protein would not grow on media containing Cd at concentrations higher than 120 µM. It is interesting to note that the longer TcHMA4 peptide confers a greater degree of Cd tolerance than does the shorter, 141-amino acid peptide (see Fig. 7). The longer peptide contains both the His-9 concatamer as well as the numerous Cys pairs and single His residues, while the shorter peptide lacks the His-9 repeat. Thus, it might be expected that the longer peptide, which covers most of the C-terminus cytoplasmic tail with its numerous potentially metal-binding amino acids, might have a greater capacity to bind Cd and afford a greater degree of metal detoxification in the cytoplasm. It should also be pointed out that the His concatamer as well as the vicinal Cys residues also can effectively interact with other micronutrients and heavy metals; therefore, it is also possible in the full-length ATPase that this region of the peptide could also be involved in the binding and/or sensing of a range of metals in addition to Cd, including Zn, Co, and Ni.
It can be predicted for a heavy metal tolerance mechanism, based on the production of a metal-binding ligand, that this tolerance mechanism would be associated with a larger cellular metal accumulation compared with wild-type yeast cells. As shown in Figure 8, this is what occurs; yeast cells transformed with the partial clones exhibit a 4- to 6-fold greater Cd accumulation than wild-type yeast expressing the empty pFL61 vector after 1 h of accumulation. Furthermore, Cd accumulation in yeast cells expressing the longer peptide was always greater than in yeast cells expressing the shorter peptide at all three time points where Cd accumulation was measured (Fig. 8). Again, this correlates nicely with the differing degree of Cd tolerance conferred by these two clones and with the relative metal-binding capacity of these two peptides as predicted from their amino acid sequences. It is interesting to note that the net Cd accumulation in yeast expressing these partial peptides was approximately 10-fold higher than the rates of Cd accumulation in yeast expressing the full-length transporter. This is consistent with Cd tolerance via the partial clones associated with increased symplasmic binding and accumulation of Cd, while for the full length transporter, tolerance is conferred by the pumping of the absorbed metal back out of the cell, which would result in a lower rate of net accumulation.
In this study, we identified a number of genes that may be involved in the mechanisms of metal tolerance and hyperaccumulation in the heavy metal hyperaccumulating plant species, T. caerulescens (Table I). Some of the genes, such as those encoding metallothioneins and heavy metal ATPases, have previously been suggested to play a role in metal tolerance (see, for example, Clemens, 2001 ; Cobbett and Goldsbrough, 2002). However, for most of the other genes in Table I, it is more difficult to ascribe a function in metal tolerance mechanisms based on sequence similarity to previously characterized genes. In should be noted that, because the yeast complementation screen used in this study will identify genes that can confer tolerance at the single-cell level, it is possible that some of these genes may not participate in metal tolerance in T. caerulescens, particularly if more complex metal tolerance mechanisms based on the operation and interplay of multiple cell types, tissues, and/or organs is functioning in Thlaspi.
From the yeast complementation screen, we identified a P1B-type heavy metal ATPase that is 71% identical on a protein level to the Arabidopsis heavy metal ATPase, AtHMA4 (Mills et al., 2003 TcHMA4 shares many of the conserved motifs found in other P1B-type ATPases, including eight putative membrane-spanning domains, and conserved CPx (amino acids 357–359) and HP (amino acids 441–442) motifs. Also, TcHMA4 shares certain unique structural features with its Arabidopsis homolog, in that both AtHMA4 and TcHMA4 have a long polar C-terminus region that is predicted to reside in the cytoplasm and contains numerous metal-binding amino acids, including a long (9-amino acid) His stretch at the very end of the C terminus, 13 Cys pairs, and a large number of single His residues (Figs. 1 and 6) and might be expected to participate in the binding of a number of heavy metals, although an involvement of this putative metal-binding region in transport has not been demonstrated. As shown in Figure 2, expression of TcHMA4 in wild-type yeast conferred a significant increase in heavy metal (Cd) tolerance. Metal tolerance at the single cell level can be achieved in a number of different ways. These include: (1) metal efflux, where the metal is first transported into the cell and then actively pumped back out via the action of an efflux transporter; (2) true tolerance, where the synthesis of metal-binding ligands bind and detoxify the metal in the cytoplasm; and (3) internal sequestration, where an endomembrane-localized metal transporter sequesters the metal in an internal cellular compartment (e.g. the vacuole). Yeast accumulation experiments indicated that expression of TcHMA4 in yeast resulted in reduced metal accumulation, and that this occurred rapidly, within minutes. Furthermore, TcHMA4 can mediate this reduced accumulation for a number of heavy metals and micronutrients, including Cd and Pb (Fig. 3) as well as Zn and Cu (data not shown). This TcHMA4-mediated reduction in metal accumulation is consistent with the TcHMA4 functioning to mediate metal efflux across the yeast plasma membrane. This possibility was investigated in more detail using 109Cd radiotracer flux techniques, and these experiments clearly showed that TcHMA4 was associated with metal efflux out of the cell (Fig. 4). Thus, it is quite likely that in yeast and plants, TcHMA4 operates as a plasma membrane-localized metal ATPase to pump Cd and possibly other heavy metals and micronutrients across the plasma membrane and out of the cell.
Heavy metal hyperaccumulation in T. caerulescens is associated with several traits, including: (1) the ability to tolerate high levels of metals both in the soil and within the plant; (2) an enhanced ability to absorb metals from the soil; (3) the ability to efficiently and rapidly translocate the absorbed metals from the root to the shoot; and (4) the ability to store very high levels of the metals in leaf epidermal cells (Lasat et al., 1996
When one examines the metal transport and gene expression data for TcHMA4 presented here in comparison with recently published expression data for AtHMA4 in Arabidopsis, the findings lead us to speculate about an intriguing scenario regarding the role of TcHMA4 in metal hyperaccumulation in Thlaspi. In Arabidopsis, it has been reported that the homolog of TcHMA4 is expressed throughout the plant, with somewhat stronger expression in roots than in other plant organs and tissues (Mills et al., 2003
During our initial yeast screen for heavy metal tolerance genes, the two heavy metal ATPase clones that conferred Cd tolerance in wild-type yeast were not the full-length ATPase, but instead were partial TcHMA4 clones. As seen in Figure 6, these two clones are 141 and 384 amino acids in length and both are from the C-terminal region of the TcHMA4 protein, which is predicted to reside in the cytoplasm and contains numerous His and Cys residues that have high affinities for heavy metals. From their predicted amino acid sequence, it is clear that the partial clones lack any membrane-spanning domains and are too small to function as a metal transporter. The only explanation for the increased Cd tolerance conferred by these partial clones is that they are functioning as Cd-binding ligands in the yeast cytoplasm. Our yeast metal tolerance and accumulation experiments with these partial clones verified this hypothesis, as expression of both clones conferred a high degree of Cd tolerance (considerably greater than the Cd tolerance associated with the full-length TcHMA4) and Cd hyperaccumulation (4- to 6-fold increase in yeast Cd accumulation after 1 h). The longer 384-amino acid clone harbors both the long, His-9 concatamer as well as the numerous Cys pairs and single His residues of the TcHMA4 C terminus, while the shorter 141-amino acid peptide lacks the poly-His tail as well as several of the Cys-Cys repeats. There was a clear correlation between the number of metal-binding motifs and the degree of metal tolerance and accumulation conferred by the two peptides, with the longer peptide conferring significantly higher Cd tolerance and Cd hyperaccumulation in yeast.
It has previously been suggested that the Cys dipeptides and His-rich domains in heavy metal ATPases may be involved in heavy metal-binding (Solioz and Vulpe, 1996
Plant Growth Conditions Thlaspi caerulescens (ecotype Prayon) seedlings were grown on a modified Johnson's solution that had a macronutrient composition of 1.2 mM KNO3, 0.8 mM Ca(NO3)2, 0.2 mM NH4H2PO4, and 0.2 mM MgSO4 and a micronutrient composition of 50 µM KCl, 12.5 µM H3BO4, 1 µM MnSO4, 1 µM ZnSO4, 0.5 µM CuSO4, 0.1 µM Na2MoO4, 0.1 µM NiSO4, and 7.5 µM Fe-EDDHA (N,N'-ethylenediamine-di(O-hydroxyphenylacetic acid)). The solution was buffered at a pH of 5.5 with 1 mM MES (2-[N-morpholino]-ethanesulfonic acid) buffer. Thlaspi seeds were placed in a drop of 0.7% (w/v) low-temperature gelling agarose on nylon mesh circles (1-mm mesh openings), which, in turn, were positioned on a coarser mesh support sealed to the bottom of black plastic cups. The cups and seeds were fitted into holes cut into black plastic lids covering 5-L black plastic pots. Seedlings were grown in a growth chamber at 25/15°C (light:dark, 16:8 h) under a light intensity of 300 µmol photons m–2 s–1 for 2 weeks, and then seedlings were transferred into identical growth containers containing modified Johnson's solution supplemented with specific concentrations of Zn (0, 1, 5, or 100 µM) or Cd (10 or 100 µM). Tissue samples were harvested after 20 d growth in the Zn- and Cd-supplemented medium.
The wild-type yeast strain DY1457 (MATa ade6 can1 his3 trp1 ura3) was transformed either with the empty yeast expression vector pFL61 (Minet et al., 1992
A cDNA library was constructed with combined polyA+ RNA from roots and shoots of T. caerulescens seedlings grown on both Zn-deficient and Zn-replete nutrient solution. The cDNA was synthesized using the Superscript Choice System (Life Technologies/Gibco-BRL, Cleveland), then ligated using BstXI/EcoRI adapters into the bifunctional yeast/Escherichia coli expression plasmid vector pFL61 (Pence et al., 2000
Wild-type DY1457 yeast strain containing the empty pFL61 vector and TcHMA4-transformed yeast were grown on liquid SD medium. At the mid-log phase of growth, the metal accumulation experiment was initiated by adding either CdCl2 or PbCl2 to a final concentration of 20 or 10 µM, respectively. After 5, 30, and 70 min of metal accumulation, aliquots of yeast cells were taken, centrifuged at 10,000g for 2 min to separate yeast cells from the metal-containing media, washed once with 5 mM CaCl2 to desorb Cd2+ or Pb2+ from the yeast cell walls, and then centrifuged again at 10,000g for 2 min. The heavy metal content of the yeast cell pellet was analyzed using an inductively coupled, plasma trace analyzer emission spectrometer (Model ICAP 61E, Thermo-Jarrell Ash, Waltham, MA). The same procedure was carried out when determining Cd accumulation in yeast transformed with the partial TcHMA4 clones, except that Cd accumulation was determined after 1, 3, and 5 h of yeast Cd accumulation. All the metal accumulation values are the average ± the SE determined from four replicate experiments.
Radiotracer (109Cd) flux methodologies were used to determine Cd2+ influx and efflux in control and transformed yeast cells (transformed with either full-length or partial TcHMA4 clones). For the Cd2+ influx experiments, the pFL61- and TcHMA4-transformed yeast were grown on liquid SD medium until they reached the mid-log phase of growth. At this time, the Cd2+ influx experiment was initiated by adding 109CdCl2 to a final [Cd] of 10 µM. Yeast was sampled at 30 s (which was an approximation of Cd bound to cell walls), 3, 5, 10, and 15 min. The yeast aliquots for each time point were transferred into 1.5 mL plastic microfuge tubes containing a 200-µL silicon oil/dinonyl phthalate pad on top of 2 µL of 40% perchloric acid. Tubes were centrifuged at 7,000g for 1 min to separate the yeast from the radiolabeled uptake solution, and the supernatant was removed. The microfuge tube with the remaining cell pellet was placed in a scintillation vial and the amount of 109Cd accumulation determined using a Perkin Elmer WIZARD 3 1480 Automatic Gamma Counter (Perkin Elmer Applied Biosystems, Foster City, CA). The amount of 109Cd associated with yeast cells after 30 s was determined in preliminary experiments to be a measure primarily of Cd associated with the yeast cell wall, and this value was subtracted from each time point to obtain a measure of Cd accumulation in the yeast cell symplasm. Preliminary experiments determined that Cd2+ accumulation was linear between 30 s and 15 min, and these values were used to calculate Cd2+ influx values. For the Cd efflux experiments, the control and TcHMA4-transformed yeast cells were grown on liquid SD medium and again, at the mid-log phase of growth, 109CdCl2 was added to a final concentration of 10 µM. The yeast cells were allowed to accumulate 109Cd2+ for 90 min, centrifuged at 7,000g for 2 min, washed briefly in 5 mM CaCl2, and then centrifuged again. The washed yeast cells were then transferred to liquid SD medium containing nonradioactive CdCl2 (10 µM) to initiate the Cd efflux, and yeast aliquots were sampled at 30, 60, 90, and 120 min. The yeast cells were treated as described above for the influx experiments to determine the amount of 109Cd appearing in the efflux solution, and Cd efflux was calculated based on the rate of arrival of 109Cd into the efflux solution. We also found in separate experiments that the same rates of Cd efflux were obtained when the efflux was calculated based on the rate of disappearance of 109Cd from yeast cells. All of the Cd influx and efflux values are the average ± the SE determined from four replicate experiments.
To determine the relative Cd tolerance of control and TcHMA4-transformed cells (transformed with either full or partial clones), the different yeast genotypes were grown on regular liquid SD medium until they achieved an optical density (OD) of 1.0. At this point, the cells were harvested and serial dilutions were made to achieve ODs of 0.1, 0.01, and 0.001. SD plates were made containing the appropriate concentration of CdCl2, and a 20-µL aliquot for each cell dilution was spotted on to the plates, as described by Lee et al. (2003)
T. caerulescens plants were grown in modified Johnson's nutrient solution as described above that was supplemented with different Zn2+ and Cd2+ concentrations. Total RNA was isolated from roots and shoots, denaturated, separated with denaturating agarose gel electrophoresis, and transferred to a nylon membrane (Hybond N+; Amersham Pharmacia; Piscataway, NJ). Probes were labeled with [ Upon request, all novel materials described in this publication will be made available in a timely manner for noncommercial research purposes, subject to the requisite permission from any third-party owners of all or parts of the material. Obtaining any permissions will be the responsibility of the requestor. Sequence data from this article have been deposited with the EMBL/GenBank data libraries under accession numbers AY486001, AY486002, AY486003, AY486006, AY486008, and AY486009. Received April 11, 2004; returned for revision May 7, 2004; accepted May 18, 2004.
1 This work was supported by the National Science Foundation (grant no. IBN–0129844) and a National Research Initiative Competitive Grant from the U.S. Department of Agriculture (grant no. 2002–35100–12487 to L.V.K.).  Article, publication date, and citation information can be found at www.plantphysiol.org/cgi/doi/10.1104/pp.104.044503. * Corresponding author; e-mail lvk1{at}cornell.edu; fax 607–255–2459.
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ABSTRACT
RESULTS
-32P]dCTP by random hexamer primers and hybridized to the membrane overnight. Next, 20 µg of RNA was loaded in each line and equal loading was ensured by ethidium bromide staining of ribosomal subunits. Following hybridization at 65°C, the nylon membranes were washed twice for 15 min at 65°C in a low-stringency wash solution (2x SSC, 0.1% SDS). Each northern experiment was repeated at least twice. 
