Cellular Compartmentation of Zinc in Leaves of the Hyperaccumulator Thlaspi caerulescens

Cellular compartmentation of Zn in the leaves of the hyperaccumulator Thlaspi caerulescens was investigated using energy-dispersive x-ray microanalysis and single-cell sap extraction. Energy-dispersive x-ray microanalysis of frozen, hydrated leaf tissues showed greatly enhanced Zn accumulation in the epidermis compared with the mesophyll cells. The relative Zn concentration in the epidermal cells correlated linearly with cell length in both young and mature leaves, suggesting that vacuolation of epidermal cells may promote the preferential Zn accumulation. The results from single-cell sap sampling showed that the Zn concentrations in the epidermal vacuolar sap were 5 to 6.5 times higher than those in the mesophyll sap and reached an average of 385 mm in plants with 20,000 μg Zn g⁻¹ dry weight of shoots. Even when the growth medium contained no elevated Zn, preferential Zn accumulation in the epidermal vacuoles was still evident. The concentrations of K, Cl, P, and Ca in the epidermal sap generally decreased with increasing Zn. There was no evidence of association of Zn with either P or S. The present study demonstrates that Zn is sequestered in a soluble form predominantly in the epidermal vacuoles in T. caerulescens leaves and that mesophyll cells are able to tolerate up to at least 60 mm Zn in their sap.Different mechanisms have been proposed to explain the tolerance of plants to toxic heavy metals (Baker and Walker, 1990; Verkleij and Schat, 1990). Some tolerant plant species, the so-called “excluders,” use exclusion mechanisms by which uptake and/or root-to-shoot transport of heavy metals are restricted. Other tolerant plant species are able to cope with elevated concentrations of toxic metals inside of their tissues through production of metal-binding compounds, cellular and subcellular compartmentation, or alterations of metabolism.An extreme strategy for metal tolerance that is in sharp contrast to metal exclusion is “hyperaccumulation,” a term that was originally used by Brooks et al. (1977) to describe plants that can accumulate more than 1,000 μg Ni g⁻¹ dry weight in their aerial parts. Approximately 400 taxa of terrestrial plants have been identified as hyperaccumulators of various heavy metals, with about 300 being Ni hyperaccumulators (Baker and Brooks 1989; Brooks, 1998). Only 16 species of Zn hyperaccumulators, which are defined as being able to accumulate more than 10,000 μg Zn g⁻¹ in the aboveground parts on a dry weight basis in their natural habitat (Brooks, 1998), have been reported. Thlaspi caerulescens J. & C. Presl (Brassicaceae) is the best-known example of a Zn/Cd hyperaccumulator. Under hydroponic culture conditions T. caerulescens can accumulate up to 25,000 to 30,000 μg Zn g⁻¹ dry weight in the shoots without showing any toxicity symptoms or reduction in growth (Brown et al., 1996a; Shen et al., 1997). Recently, there has been a surge of interest in the phenomenon of heavy-metal hyperaccumulation because this property may be exploited in the remediation of heavy-metal-polluted soils through phytoextraction and phytomining (McGrath et al., 1993; Brown et al., 1995b; Robinson et al., 1997).The mechanisms for metal hyperaccumulation are not fully understood, and this is particularly true in the case of the Zn/Cd hyperaccumulators. To cope with the consequence of hyperaccumulation, plants must also be hypertolerant to the heavy metals that accumulate. Recent studies comparing the different populations of T. caerulescens have shown that hyperaccumulation of Zn is a constitutive property, although the traits are probably separate from those for tolerance (Baker et al., 1994; Meerts and Van Isacker, 1997). Compared with the nonaccumulating species, T. caerulescens possesses an enhanced capacity to take up Zn and transport it from roots to shoots (Baker et al., 1994; Brown et al., 1995a; Shen et al., 1997). Lasat et al. (1996) found that roots of T. caerulescens and the nonaccumulator Thlaspi arvense had similar apparent K_m values for Zn²⁺, but that the V_max in the former was 4.5-fold higher than that in the latter species, indicating that the hyperaccumulator T. caerulescens possessed more Zn²⁺-transport sites in the plasma membranes of root cells. Shen et al. (1997) showed that T. caerulescens was much more effective in exporting the Zn that was accumulated previously in roots to the shoots than an intermediate accumulator species, Thlaspi ochrolucum. Organic acids such as malic acid have been suggested to play a key role in shuttling Zn from cytoplasm to vacuoles (Mathys, 1977). However, the low affinity of malate to chelate Zn (stability constant pK = 3.5 at infinite dilution) does not favor this hypothesis. Moreover, high concentrations of malate found in the shoot tissues of T. caerulescens appear to be a constitutive property (Tolrà et al., 1996; Shen et al., 1997).The extraordinary tolerance of hyperaccumulator plants must also involve compartmentation of toxic metals at the cellular and subcellular levels. Vázquez et al. (1992, 1994) studied localization of Zn in the root and leaf tissues of T. caerulescens using EDXMA. They compared two methods of sample preparation and found that Na₂S fixation was not suitable for preventing the loss of metal ions from the samples. Using cryofixation and freeze substitution, they showed that Zn accumulated mainly in the vacuoles as electron-dense deposits. Many vacuoles of leaf-epidermal and subepidermal cells contained globular crystals that were very rich in Zn. However, it is not known whether the Zn-rich, globular crystal deposits occur inside of the leaf vacuoles in vivo or if they are artifacts caused by sample preparation. Also, the technique used by Vázquez et al. (1992, 1994) allows only semiquantitative determination of Zn concentrations.In this study we used two techniques to investigate cellular compartmentation of Zn in the leaves of T. caerulescens. The first utilized EDXMA of frozen, hydrated tissue to survey the distribution patterns of Zn and other elements across different leaf cells. The second method involved sampling sap from single cells using microcapillaries, followed by fully quantitative determination of Zn and other elements using EDXMA.