THIOLS OF CU-TREATED MAIZE PLANTS INOCULATED WITH THE ARBUSCULAR-MYCORRHIZAL FUNGUS GLOMUS INTRARADICES

被引:25
作者
GALLI, U
SCHUEPP, H
BRUNOLD, C
机构
[1] UNIV BERN,INST PFLANZENPHYSIOL,CH-3013 BERN,SWITZERLAND
[2] SWISS FED RES STN,CH-8820 WADENSWIL,SWITZERLAND
关键词
ARBUSCULAR MYCORRHIZAL FUNGUS; CU-BINDING PEPTIDES; GLOMUS INTRARADICES; GLUTATHIONE; MAIZE; PHYTOCHELATINS; ZEA MAYS;
D O I
10.1111/j.1399-3054.1995.tb05308.x
中图分类号
Q94 [植物学];
学科分类号
071001 ;
摘要
Mycorrhizal colonization of roots. fresh weight, content of cysteine, gamma-glutamylcysteine (gamma EC), glutathione (GSH), thiol groups in Cu-binding peptides (CuBP), and the uptake of Cu were measured in roots and shoots of maize (Zea mays L., cv. Honeycomb F-1) grown in quartz sand, with Cu at 0, 4.5, 9, 15 and 30 mu g g(-1) added with or without inoculum of the arbuscular-mycorrhizal fungus (AMF) Glomus intraradices. In control plants (no Cu added) AMF significantly reduced shoot growth, but did not affect root growth. At an external Cu supply of 9 mu g (g quartz sand)(-1) or higher, both mycorrhizal colonization and growth of roots and shoots of mycorrhizal and nonmycorrhizal plants were significantly reduced. With up to 9 mu g Cu g(-1), mycorrhizal colonization increased the content of cysteine, gamma EC and GSH in the roots. However, the amount of thiols in CuBPs was not increased by mycorrhizal colonization in Cu-treated plants and no differences in Cu uptake were detected between non-mycorrhizal and mycorrhizal plants. A CuBP-complex with a relative molecular mass of 7 300 and a SH:Cu ratio of 1.77:1 was separated on a Sephadex G-50 column from both non-inoculated and inoculated roots of Cu-treated plants. HPLC chromatography of the CuBPs of both non-inoculated and inoculated roots resulted in a similar peak pattern, indicating that no additional CuBPs were formed by the fungus. In conclusion, our results do not support the idea that AMF protects maize from Cu-toxicity.
引用
收藏
页码:247 / 253
页数:7
相关论文
共 33 条
[1]  
Bradley R., Burt A.J., Read D.J., Mycorrhizal infection and resistance to heavy metal toxicity in Calluna vulgaris, Nature, 292, pp. 335-337, (1981)
[2]  
Colpaert J.V., van Assche J.A., Zinc toxicity in ectomycorrhizal Pinus sylvestris L, Plant Soil, 143, pp. 201-211, (1992)
[3]  
Dameron C.T., Smith B.R., Winge D.R., Glutathione‐coated cadmium‐sulfide crystallites in Candida glabrata, J. Biol. Chem., 264, pp. 17355-17360, (1989)
[4]  
De Vos C.H.R., Vonk M.J., Vooijs R., Schat H., Glutathione depletion due to Cu‐induced phytochelatin synthesis causes oxidative stress in Silene cucubalus, Plant Physiol., 98, pp. 853-858, (1992)
[5]  
Dixon R.K., Buschena C.A., Response of ectomycorrhizal Pinus banksiana and Picea glauca to heavy metals in soil, Plant Soil, 105, pp. 265-271, (1988)
[6]  
Fairchild M.H., Miller G.L., Vesicular‐arbuscular mycorrhizas and the soil‐disturbance‐induced reduction of nutrient absorption in maize, New Phytologist, 114, pp. 641-650, (1990)
[7]  
Fernandes J.C., Henriques F.S., Biochemical, physiological, and structural effects of excess Cu in plants, The Botanical Review, 57, pp. 246-273, (1991)
[8]  
Fitter A.H., Costs and benefits of mycorrhizas: Implications for functioning under natural conditions, Experientia, 47, pp. 311-400, (1991)
[9]  
Florijn P.J., De Knecht J.A., van Beusichem M.L., Phytochelatin concentrations and binding state of Cd in roots of maize genotypes differing in shoot/root Cd partitioning, J. Plant Physiol., 142, pp. 537-542, (1993)
[10]  
Galli U., Meier M., Brunold C., Effects of cadmium on non‐mycorrhizal and mycorrhizal Norway spruce seedlings [Picea abies (L.) Karst.] and its ectomycorrhizal fungus Laccaria laccara (Scop. ex Fr.) Bk. & Br.: Sulphate reduction, thiols and distribution of the heavy metal, New Phytol., 125, pp. 837-843, (1993)