Abstract

The aim of the study was to determine the plant-available manganese in the soil and to study which factors regulate the plant-available manganese. The material consisted of 193 mineral soils and 17 organogenic soils. Oats (Avena saliva L.), Italian ryegrass (Lolium multiflorum Lam.) and turnip rape (Brassica campestris oleifera L.) were used as the test plants in the pot experiments. A cation exchange resin method was developed for extracting soil manganese. The method enabled both exchangeable and reducible manganese to be determined. Exchangeable manganese comprised the manganese which was freely present in the soil solution in cationic form, and the manganese in cationic form which could be exchanged from the soil. Reducible manganese was the manganese reducible to the oxidation state, Mn2+, by the action of hydroquinone, hydroxylammonium chloride or ascorbic acid. The content of exchangeable manganese in the soil explained 33,7 % of the variation in the manganese content of the first yield of ryegrass. The greater the number of yields harvested, the smaller was the significance of the content of exchangeable manganese in the soil as an independent variable. On the other hand, when the content of reducible manganese in the soil was used as the independent variable, then the greater the number of yields harvested, the better it explained the variation in the manganese content of the yield. The content of manganese reduced by hydroxylammonium chloride explained 68,6 % of the variation in the manganese content of the fourth yield. The contents of exchangeable manganese and manganese reducible by ascorbic acid explained 73,4 % of the variation in the manganese content of the roots. The pH, the organic carbon content and the content of hydroquinone-reducible manganese in the soil explained 67,0 % of the variation in the content of exchangeable manganese in the plough layer of the mineral soils. The content of "total" manganese in the plough layer of the mineral soils explained 27,6 % of the variation in the content of ascorbic acid-reducible manganese. The plant stands increased the content of exchangeable manganese in the soil and decreased the redox potential of the soil in comparison to the incubated soils. The content of exchangeable manganese started to increase when the redox potential of the soil fell below 0,59 V. Adding glucose promoted the reduction of manganese in the soil, reduction appearing to be both biological and non-biological in origin. Soil moisture increased the content of exchangeable manganese when the moisture was higher than the field capacity. Liming decreased the content of exchangeable manganese in the soil more than would have been expected on the basis of the change in pH values. The manganese content and manganese uptake of the crop were also reduced. Adding large amounts of manganese (Mn 51,5 kg/ha*20 cm) did not prevent liming (calcite 14 t/ha*20cm) from reducing the manganese content of the yield.

Highlights

  • It has been known for 60 years already that manganese is an essential nutrient for plants (McHARGUE 1922) and it appears, after boron, to be the most extensively studied of the micronutrients (BRANDENBURG et al 1969)

  • Plants are able to utilize a number of oxides and oxyhydroxides of manganese (LEEPER 1947,JONES and LEEPER 1951 a, 1951 b, HEINTZE 1956, JONES 1957 a, 1957 b, 1957 c)

  • An attempt was made to extract the manganese under conditions corresponding to the pH prevailing in the soil so that no changes would occur in the oxidation state of manganese, and manganese would not be transferred from one fraction to another

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Summary

Introduction

It has been known for 60 years already that manganese is an essential nutrient for plants (McHARGUE 1922) and it appears, after boron, to be the most extensively studied of the micronutrients (BRANDENBURG et al 1969). 640), manganese is, known to be a difficult field of soil chemistry. This is mainly due to the fact that manganese occurs in a number of different oxidation states. Reducible manganese may be converted into compounds which the plants cannot utilize. In this case it may be a question of a reduction in the specific surface area of oxides and oxyhydroxides and an increase in crystallization because oxides which have a large specific area and are weakly crystalline, are the most reactive oxides of manganese (MYRRAY et al 1968, LOGANATHAN and BURAU 1973, LOGANATHAN et al 1977)

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