Extended x-ray absorption fine structure measurements were performed on frozen hydrated samples of the cadmium (Cd)/zinc (Zn) hyperaccumulator Thlaspi caerulescens (Ganges ecotype) after 6 months of Zn 2ϩ treatment with and without addition of Cd 2ϩ . Ligands depended on the metal and the function and age of the plant tissue. In mature and senescent leaves, oxygen ligands dominated. This result combined with earlier knowledge about metal compartmentation indicates that the plants prefer to detoxify hyperaccumulated metals by pumping them into vacuoles rather than to synthesize metal specific ligands. In young and mature tissues (leaves, petioles, and stems), a higher percentage of Cd was bound by sulfur (S) ligands (e.g. phytochelatins) than in senescent tissues. This may indicate that young tissues require strong ligands for metal detoxification in addition to the detoxification by sequestration in the epidermal vacuoles. Alternatively, it may reflect the known smaller proportion of epidermal metal sequestration in younger tissues, combined with a constant and high proportion of S ligands in the mesophyll. In stems, a higher proportion of Cd was coordinated by S ligands and of Zn by histidine, compared with leaves of the same age. This may suggest that metals are transported as stable complexes or that the vacuolar oxygen coordination of the metals is, like in leaves, mainly found in the epidermis. The epidermis constitutes a larger percentage of the total volume in leaves than in stems and petioles. Zn-S interaction was never observed, confirming earlier results that S ligands are not involved in Zn resistance of hyperaccumulator plants.Heavy metals such as copper, manganese, nickel (Ni), and zinc (Zn) are well known to be essential microelements for the life of plants, and recently, even cadmium (Cd) was found to act as the active center of a plant enzyme (Lane and Morel, 2000). On the other hand, elevated concentrations of these metals induce inhibition of plant metabolism, leading to various effects depending on the metal applied, the type of affected plant, and the environmental conditions during the stress (for review, see Clijsters and Van Assche, 1985;Fernandes and Henriques, 1991;Baró n et al., 1995; Prasad and Hagemeyer, 1999).Plants developed a number of strategies to resist the toxicity of heavy metals, such as efflux pumps (van Hoof et al., 2001), complexation of heavy metals inside the cell by strong ligands such as phytochelatins (for review, see Cobbett and Goldsbrough, 2002) or His (Krämer et al., 1996), and several more mechanisms (Maeda and Sakaguchi, 1990; Prasad and Hagemeyer, 1999). Plants that actively prevent metal accumulation inside the cells are called excluders. These represent the majority of metal-resistant plants (Baker, 1981). Other resistant plants deal with potentially toxic metals in just the opposite way, i.e. they actively take up metals and accumulate them. The active accumulation in the aboveground parts of hyperaccumulator plants provides a promising approach for both cl...