The bundle sheath in Zea mays leaves functions as a protective barrier against the toxic effect of lead

Lead is a highly toxic metal. It impairs the metabolism of living organisms. Plants show different sensitivity to the action of this element. One of the plants with relatively high lead tolerance is Zea mays, where even in detached leaves treated with Pb2+ ions, the photosynthesis rate remains very high compared to other plant species. This study set out to determine the mechanism responsible for the high resistance of maize photosynthetic tissue to the toxic effect of this metal. For this purpose, the cut leaves of Z. mays were incubated in Pb(NO3)2 solutions at different concentrations. Regions of lead accumulation in tissues and cells were located using histochemical methods and transmission electron microscopy. The experiments showed a diverse distribution of lead ions in the leaf blade of Z. mays. Most of the accumulated Pb2+ ions were observed in the vascular bundle and the bundle sheath, while minimal traces of metal were transferred to the mesophyll. In Pisum sativum leaves, although Pb(NO3)2 concentration in the solution was two-fold lower, lead accumulated in all the leaf tissues - mainly in the vascular bundle, epidermis, sclerenchyma, and mesophyll. Thus, bundle sheath cells in maize leaves were able to inhibit the flow of Pb2+ ions to the ground tissue. Therefore, the influence of the toxic metal on photosynthesis in mesophyll cells remained minimal. These experiments show that the structure of Z. mays leaf, with a layer of bundle sheath cells (characteristic of C4 plants), contributes to the protecting photosynthetic tissue against the toxic effect of lead.

Comparison of the toxicity and distribution of cadmium and lead in plant cells

The toxicity of heavy metals (Cd, Zn, and Pb) was assessed by in vivo observations of their effect on cytoplasmic streaming in Allium cepa L. bulb scale epidermal cells. On the basis of our results, the order of toxicity of the studied cations is Zn < Pb << Cd. The difference in toxicity between cadmium and lead was found to be very large. When cytoplasmic streaming was assessed, this difference was threefold. When the total content of cadmium and lead (determined by inductively coupled plasma mass spectrometry) was the criterion, the difference in toxicity was 15-fold. Fractionation of the tissue and enzymatic digestion of the cells revealed that the largest proportion of cadmium was located in the cell walls (56%), whereas almost all of the lead (97.6%) was accumulated in an insoluble form. The speciation of water-soluble Pb and Cd fractions is discussed on the basis of analysis by capillary zone electrophoresis interfaced with inductively coupled plasma mass spectrometry of water extracts from epidermal cells. Lead and cadmium appeared to be bound mainly to salts, which explains their toxicity. Cadmium was complexed (detoxified) by organic acids, while thiols were the metal-complexing species for lead. Histidine formed complexes with both cadmium and lead. Ultrastructural analyses showed that lead was encapsulated in small vesicles in the cytoplasm. Fluorescence studies of the endoplasmic reticulum (ER) revealed that it underwent extensive fragmentation under the influence of lead, with numerous ER vesicles appearing in the cells. In other words, the lead deposits in the cytoplasm were contained in vesicles arising from fragmentation of the ER. These observations indicate that epidermal cells have a rapid and effective mechanism for detoxifying lead involving the ER, and this may be one of the mechanisms accounting for the lower toxicity of lead in comparison with cadmium. The suitability of Allium cepa bulb scale epidermal cells for use in ecotoxicological studies is also discussed. Step-by-step directions for this test are given.