ATINER s Conference Paper Proceedings Series ECL Athens, 14 December 2017

Similar documents
HUMUS AND TRACE ELEMENTS AS AN INDICATORS OF MATERIAL ERODED FROM CARBONATIC CHERNOZEMS SURFACE

KIRVALIDZE David ( 1 ), KIRVALIDZE Revaz ( 2 ), JACOBASHVILI Izolda ( 3 )

TYPE: ORGANIC NUTRIENTS CODE: BF4 - GRANULE (JAIVIZYME)

Salts and Chlorides Remediation

Immobilizing Arsenic in Contaminated Soil Using Humic Mineral Concentrates


BIOLOGY - CLUTCH CH.37 - SOIL.

INFLUENCE OF HUMUS ACIDS ON MOBILITY AND BIOLOGICAL AVAILABILITY OF IRON, ZINC AND COPPER

Assessing trace elements accumulation/depletion in agricultural Lithuanian soils

Understanding your results Acidity... 3 Aluminium... 3 Base saturation... 3 Boron... 4 Bulk density... 4 Calcium... 4 Cations...

Fixation of P. Figure 4. Illustration of the interaction between the available and unavailable pools of phosphorous in the soil.

Essential Elements. Original research don by Julius von Sachs 1860 using hydroponics

PROFILE DISTRIBUTIONS OF LEAD, ZINC, AND COPPER IN DYSTRIC CAMBISOLS DEVELOPED FROM GRANITE AND GNEISS OF THE SUDETES MOUNTAINS, POLAND

Soils Baseline Report Jay Project Appendix A, Soils Data September 2014 ANNEX V: APPENDIX A SOILS DATA

EXTREME Chelates Macro and Micronutrients

1101 S Winchester Blvd., Ste. G 173 San Jose, CA (408) (408) fax Page 1 of 2

DOMOGRAN 45 ACTIVATING YOUR NUTRIENT POTENTIAL THE NITROGEN-SULFUR FERTILIZER FROM LEUNA

Leaving at 8:30 am Be prepared for a little mud!

AVAILABLE Cd CONTENT OF SALT AFFECTED AND NORMAL SOILS OF HALASTRA KALOHORI AREA

The effect of humic acid and fulvic acid on adsorption-desorption behavior of copper and zinc in the yellow soil

University of Technology and Agriculture, Department of Soil Science and Biochemistry, 6 Bernardyñska St., Bydgoszcz, Poland

Soil organic matter composition, decomposition, mineralization and immobilization

Structural and Zn-binding features of ortho- and pyrophosphate modified soil metal-humus sorbents (Features of P-modified humus sorbents)

Discuss the importance of healthy soils Soil properties, physical, chemical and biological that one can manage for soil health How organics play a

SOIL TESTS & INTERPRETATION

Slide 1. Slide 2. Slide 3

Lecture 32: Soil Phosphorus and Cation Nutrients

Soil Health - Myth Vs Fact

BOTANY AND PLANT GROWTH Lesson 9: PLANT NUTRITION. MACRONUTRIENTS Found in air and water carbon C oxygen hydrogen

INTERNATIONAL SIMPOSIUM 1996

Understanding a Soil Report

Soil Program Recommendation

Soil acidity. Kiyoshi Tsutsuki

Prediction of Selenium Leaching. Stephen Day and Kelly Sexsmith SRK Consulting

UPTAKE OF MAJOR AND TRACE ELEMENTS BY GRASS BIOMASS AFTER AMELIORATION OF DEGRADED SOIL

Distribution of Micronutrients in Soil of Garhi Tehsil, Banswara District of Rajasthan, India

Title: Nutrient Cyclying, Pools, and Transformations. What is the title of this lecture?

COMPOSITION AND NA TUllE OF HUMUS IN TYPICAL ARIDISOLS OF RAJASTHAN

THOMSON & JOSEPH LTD. The Mineral Specialists GRASS SILAGE EARLY SEASON MINERAL PROFILE

HUMIC SUBSTANCES AND THE POTENTIAL TO COUNTER FIGHT DESERTIFICATION

Use of Soil and Tissue Testing for Sustainable Crop Nutrient Programs

IRON. AGRITOPIC August INTRODUCTION 2. IRON IN THE SOIL

Pushkarov Institute of Soil Science and Agroecology, Shosse Bankia 7, Sofia 1080, Bulgaria, Fax (359) (2)

Chelated and regulated release of all essential nutrients, not just nitrogen

Vetiver for Mine Tail Re-vegetation of Mofu Mountain in Nanjing of China

Mir M. Seyedbagheri, Ph.D. Professor/Soil Agronomist 1

FOLIAR NUTRITION, BIOSTIMULANTS, SPECIALTY CHEMICALS, SURFACTANTS, ADYUVANTS, WETTING AGENTS, AND SOIL AMENDMENT TECNOLOGY

BIONOBEL S FERTIGRENA S (2 MgO) FERTIGRENA S (2 Mg0) FERTIGRENA S (2 Mg0)

Humic Substan. Humic Substances. The Real Dirt On. by Ryan Zadow. and require that only humic acid be used on labels. This creates

Soil Organic Matter. Unit 2. Forms of Soil Organic Matter: OM OC x (assumes 30% C) (1.72 typically used as a conversion factor)

Zinc Deficiency in Soil of Rajasthan and its Management

A reliable, practical and easy-to-use Determination of Soil Conductivity and Salt Content with TRIME Probes

Chapter 05 Mineral Nutrition

This list reports certain measurements made from 1965 to These samples are devoted to a special study of organic matter in soils.

ABSTRACT. Keywords: Added Zn, Significant increase, Exchangeable Zn, Aerobic and Anaerobic Condition INTRODUCTION

Bioavailability of Low Dose Plant Derived Minerals and Amino Acids, ph BALM (ph balanced, Bio Available Living Minerals)

SOILS AND PLANT NUTRITION

Ground Sampling Standards

Trace metals in the ocean Lecture January 23, 2006

ENGLISH TRANSLATION: Gas kov, A. Yu., Sabchenkov, M. F., Yushkov, N. N. The Bratskiy State University and the Irkutsk State Medical University

Boron fertilizers: use, mobility in soils and uptake by plants

Soil Morphology and Chemistry

Overview. Managing Soil Fertility in Organic Systems. Fertilizer Analyses? Fertilizer Analyses? What Soil Amendments Can Be Used?

Analysis. Methods of. of Soils, Plants, Waters, Fertilisers & Organic Manures. Edited by HLS Tandon

TSADILAS Christos, SAMARAS Vasilios, SIMONIS Asterios, SETATOU Helen

Dynamics of potassium fractions in a calcareous Vertic Haplustepts under AICRP-LTFE soils

Effect of salinity on Cd and Zn availability

An innovative remediation for metal polluted soils combined chemical and phytostabilisation

Soil Fertility and Nutrient Management. Hailin Zhang. Department of Plant and Soil Sciences

Soil Prescription - Sample 1

Potential of Potassium Supply in Locally Available Soil Amendments for Use in Coconut Plantations

The uptake of nutrients occurs at both the roots and the leaves.

Lead Influence on the Main Properties of Bradyrhizobium Japonicum

INTERMEDIATE 1 1 Food and Diet. These elements are present in compounds - not as free elements.

COMPLETION REPORT. 2. Location : AICRP WM Dept. of Agronomy Agricultural College & Research Institute Madurai Tamil Nadu, India

CHESWORTH, W.*, GARCÍA-RODEJA E.**, MARTÍNEZ CORTIZAS A.**, MACIAS F.**

EFFECT OF SOIL SALINITY ON VETIVER GROWTH. Paul Truong The Vetiver Network International and Veticon Consulting Brisbane, Australia November 2012

Nutrient Use Strategies for Coconut Based Cropping System in Onattukara Sandy Tract, Kerala

An Asian Journal of Soil Science Vol. 6 No. 1 (June, 2011) : 11-16

Understanding Your Soil Report. Michael Cook 2018

Geol Supplementary Notes 463-RWR-6,7 GEOL RWR-6 ORGANIC COMPOSITION OF PETROLEUM COMPOSITION OF LIVING ORGANISMS

NUTRIENT AND HEAVY METAL CONTENTS OF HOG MANURE - EFFECT ON SOIL QUALITY AND PRODUCTIVITY

Effect of organics and inorganic phosphorus on inorganic P-fractions in soil of soy bean (Glycine max L.) crop

Microbial Enhanced Fish Fertilizer Supplement with Vitamins and Nutrients for Plant Health

The Mineral Specialists

Soil Composition. Air

Greenhouse Horticulture

RELIABILITY OF SOIL AND PLANT ANALYSES FOR MAKING NUTRIENT RECOMMENDATIONS

Common Salt Ions. Salinity. Soil permeability reflects sodicity problems from sodium concentrations 1/15/2008

BUILDING HEALTHY SOILS AND PLANTS. Summary

Defining Agriculture

Advanced ph management

TECHNIQUES FOR PREDICI'ING

Testing Protocol. Iodine Estimation of Salt

CANADA INSTITUT OCEANOGRAPHIQUE DE ~BEDFORD,~ ~AA INSTITUTE OF OCEANOGRAPHY DARTMOUTH, N. S.

FACTORS AFFECTING WATER QUALITY

Nitrophoska. Cereals, fodder beet, horticulture, maize and vegetables. Precise nutrition for superior plant performance

THE EFFECT OF SEWAGE SLUDGE DOSES ON MANGANESE CONTENT IN THE ECOSYSTEM LUVOSOIL AND FIELD CROPS

S. Ananthacumaraswamy and L. S. K. Hettiarachchi (Tea Research Institute of Sri Lanka, Talawakelle, Sri Lanka)

Tree Nutrition and Fertilization

Transcription:

ATINER s Conference Paper Proceedings Series ECL2017-0029 Athens, 14 December 2017 Influence of Various Factors on the Content of Iodine in the Soils of Western Siberia Galina Konarbaeva and Boris Smolentsev Athens Institute for Education and Research 8 Valaoritou Street, Kolonaki, 10683 Athens, Greece ATINER s conference paper proceedings series are circulated to promote dialogue among academic scholars. All papers of this series have been blind reviewed and accepted for presentation at one of ATINER s annual conferences according to its acceptance policies (http://www.atiner.gr/acceptance). All rights reserved by authors. 1

ATINER s Conference Paper Proceedings Series ECL2017-0029 Athens, 14 December 2017 ISSN: 2529-167X Galina Konarbaeva, Leading Researcher, Institute of Soil Science and Agrochemistry, Siberian Branch of Russian Academy Sciences, Russia Boris Smolentsev, Head, Laboratory of Geography and Soil Genesis, Institute of Soil Science and Agrochemistry, Siberian Branch of Russian Academy Sciences, Russia Influence of Various Factors on the Content of Iodine in the Soils of Western Siberia ABSTRACT Important biological role of iodine is due to the fact that being a part of the hormones thyroxine and triiodothyronine, it regulates the rate of metabolism in living organisms. In this paper we present the results of the study of the content and patterns of distribution of iodine in soils of Western Siberia, which are the link in the chain: the atmosphere-soil-water-plants-animals and people. Soil, due to its accumulative properties, refers to natural objects, concentrating iodine. If we talk about the barriers, where there is concentration of halogen, it is a priority for iodine -biochemical -the accumulation of soil organic matter. Geochemical barrier for iodine exists only in the evaporation conditions. The study of the content and distribution of iodine in different types of soil showed that the accumulation of these halogen most influence their degree of humus content. On the processes of accumulation and migration of iodine in the soil profile is influenced by other physical and chemical properties of soils: size distribution, the reaction of the soil medium, the content of iron and aluminum oxides, as well as the type of water regime and chemical properties of the trace element. We have studied the content of I in the soils of Western Siberia in the direction from north to south. Soils of tundra and forest tundra (typical cryozems and coarse humus cryozems, cryometamorphic cryoturbic cleyzems, entic podsols). These soils are largely characterised by the low concentration of humus that varies from 0.07% to 3.12%, sometimes the absence of distinct humus horizon (podzols) and the excess of fulvic acids. Soils that have low ph are characterised by low level of iodine retention. Contrary results were obtained from soils samples taken in the southern parts of Western Siberian Region. At the sod-podzolic soils, gray forest soils of the iodine content was respectively 1.36-2.36 and 1.44-2.82mg/kg. These soils are well-drained, low on humus content and have low ph. Chernozems (categories zonal soils) are the most iodine-rich soils (min 1.2, max 6.4mg/kg) due to their 2

higher than average level of organic matter. Albic luvisols и haplic kastanozems soils can be attributed to the middle range based on their iodine concentration. Within the intrazonal group of soils, alkali soils are found to have the highest level of iodine content (min-5.6, max-33.2 mg/kg). The solonchak is located in low lying grounds that are often to be found in an iodine-rich environment. The more alkaline (higher ph) a soil is the greater is its iodine concentration. Several smaller halogen found in solonetzes (min-1.8, max-18.7 mg/kg) with a maximum in the illuvial horizon enriched by fine mineral particles, oxides and hydroxides aluminium and iron, volumetric rainfall which ness actively absorb iodine. In stratozemah easily exposed to wind and water erosion, humus content does not exceed 0.5%, which resulted in low levels of iodine 0.12-1.43mg/kg. 3

Important biological role of iodine is due to the fact that, being a part of the hormones of thyroxine and triiodothyronine, it regulates the rate of metabolism in living organisms. Deficiency of the microelement leads to the development of endemic goiter, and its excess - to iododerm - the allergic reaction to contact with excess of iodine. The quantitative content of microelement in the human body is in direct proportion to their concentrations in different components of the environment such as rocks, soils, natural waters and atmospheric air (aerosol chemical elements). Therefore, in this report we present the results of studying the content and distribution of iodine and its forms in soils of Western Siberia. The soils are an important link in the chain: atmosphere-soil-water-plants-animals and people. The study of the content and distribution of iodine in different soil types showed that the highest its accumulation in soils was influenced by humus content (Vinogradov, 1957; Whitehead, 1978; Yamada, Hidekazu et al., 1999). The other physicochemical properties of soils, such as soil reaction, particle size distribution, concentration of oxides iron, aluminum and carbonates, readily soluble salts, type of water regime and chemical properties of itself element are influenced a lesser extent the halogen accumulation. We studied the soils on the territory of Western Siberia in the direction from the north to the south. The soils of the zones of tundra and forest tundra have been studied such as cryometamorphic cryoturbic gleysols, haplic cryosols, coarse humus cryosols and podzolic podburs ashed. The content of iodine in these soils will be negligible because here no preconditions for its significant accumulations. The content of humus in the soils under study ranges from 0.1 to 1.4%. Maximum content of clay fraction does not reach even 20%, so that its ability to fix or adsorb halogen is limited. The reaction medium in these soils is acidic and strongly acidic, so that its contribution to the accumulation of halogen is negative. The reactions (taking place in an acid medium) lead to the formation of free iodine, which subsequently evaporates. It is known that the sorption of iodine is enhanced in the presence of various salts, but in this case there is no question of an enrichment of northern soils by different salts, therefore, the contribution of this factor is also negative. The results are shown in Figure 1. 4

Figure 1. Distribution of Humus, % (1) and Iodine, mg/kg (2) in Soil Profile of the North of the Western Siberia: а Coarse Humus Cryosol, b Gley- Podzolic Soil, c Podzolic Podbur, d Hapliс Cryosol, e Cryometamorphic Gleysol The content of water-soluble iodine varies within the range of 0.002-0.026 mg / kg. This is followed by soil of the northern and middle taiga (gleyic albeluvisols, haplic podsols). They have much in common with the previous soils, for example, low humus content, acidic and weakly acidic medium, periodically washing type of water regime in upper horizons. The iodine content varies in these soils from trace amounts to 1 mg/kg. For comparison, the data are given on zonal soils spread southward such as sod-podzolic, cutanic luvisols, haplic chernozems, luvic chernozems and haplic kastanozems (Figure 2, Table 1), where iodine content is already more significant, especially in chernozems. This fact is due to the high content of humus and clay fraction. Humus acids are markedly predominant among organic compounds. It was established experimentally that the iodine is mainly fixed with humic acids (88%). Only 12% of iodine is accounted for fulvic acids [2] (Table 1). 5

Figure 2. Distribution Humus, % (1) and Iodine, mg/kg (2) in the Soil Profile Western Siberia: a- Haplic Chernozems, b- Luvic Chernozems, c- Cutanic Luvisols, d- Gleyic Albeluvisols, e- Haplic Podsols 6

Table 1. Physiсоchemical Properties of Zonal Soils and their Iodine Content Soil type ph Physical clay Humus Iodine, mg/kg % Total H 2 O soluble. Zonal soils Haplic albeluvisols 4.9-6.5 39.4-54.9 0.1-1.98 0.6-2.20 traces- 0,006 Cutanic luvisols 5.3-7.2 42.0-65.56 0.18-2.54 0.64-3.2 0,015-0,038 Chernozems 6.6-8.3 45.5 65.3 0,41 6.0 1.2-6.72 0,01-0,09 Haplic Kastanozems 6.4-8.2 15.48-33.20 0.14-2.42 traces- 2.60 traces- 0,024 Intrazonal soils Solonetz 7.3-9.7 27.8-57.0 0.12-2.40 2.1-14.3 0.05-0.6 Solonchaks 8.3-10.5 36.0-59.0 0.53-6.93 5.6-33.2 0.08-1.1 Haplic Albeluvisols are least rich in iodine, as they are poor in humus, have an acid reaction of the soil medium and a washing water regime, which intensifies migration and halogen losses. Gray forest (Cutanic Luvisols) and Haplic Kastanozems soils occupy an intermediate position by the degree of saturation with iodine. Higher content of iodine is characteristic for intrazonal soils, such as solonetzes and solonchaks, it is favored by some factors, for example strongly alkaline medium, ph value ranges at a level of 8.5-10. Under these conditions the formation of the most stable anions of iodine takes places, i.e. I and IO 3. The formation of these soils occurs in the lowest places of intermountain depressions which are the final point of local transgression of salts, including iodine salts as well. Halogen content in solonetz is slightly lower than in solonchaks, but at the same time it is significantly higher than in zonal soils. The maximum content of iodine in makes up 19.7 and 35.4 mg/kg in solonetzes and solonchaks respectively. We studied in detail the planosols and fluvisols of Kulunda plain. The main type of water regime of planosols is periodically wash. Low content of organic matter in the humus horizon (2.61-3.28%) and humus-eluvial (0.28-1.31%) and increased its fulvate acids suggest low iodine content in the planosols. It is known that a light-graded soil iodine poorer than heavy-graded soil, due to the fact that less light soils iodine chemically bound to the components of the soil, and more - and the mechanisms associated occlusion. Gross iodine content in the planosols varies from 0.02 to 1.68 mg / kg, the saltsoluble form varies from 0.01 to 0.09 mg / kg. The studing stratozems (Fluvisols) distributed also in the territory of the Kulunda plain. These soils are an unstable link in the landscape of agricultural meadowlands (grasslands and pastures). They are easily exposed to wind and water erosion, and their area transformation can lead to the change of the properties of surrounding areas. Obvious decrease in depth of humus content, as it is characteristic of the zonal soils, was not observed here, whereas there is 7

a very slight layer change in its content throughout the profile. These soils are sandy by texture, physical clay content is less than 10%, clay fraction makes up 4-6%; ph value ranges within the limits of 7.74-9.03. The upper horizons are not saline; the lower ones have slight soda-chloride salinization (Table 2). Table 2. The Content of Total Iodine and its Mobile Forms in Fluvisols Horizon Depth of sampling, Iodine, mg/kg cm см total salt-soluble Water-soluble AJ aq 0-7 0.58 0.013 0.010 D 1 7-21 1.19 0.017 0.016 D 2 21-31 0.74 0.022 0.019 RJ aq1 31-43 0,70 0.027 0.020 D 3 50-60 1.43 0.084 0.048 RJ aq2 70-80 1.96 0.096 0.089 D 4 100-110 0.62 0.029 0.023 RJ aq3 125-140 0.12 0.011 0.008 D 5 140-155 0,21 0.025 0.012 Figure 3. The Distribution of the Electric Conductivity of Aqueous Extract (1), A Water-Soluble Iodine (2) and Salt-Soluble (3) in Fluvisols (Stratozem) Profile 8

Thus studies have shown that the soil of Western Siberia in the direction from north to south are gradually enriched with iodine, the maximum content of which is observed in Solonchaks. The soils with a low content of halogen are found both in the north and in the south of Western Siberia. The gross amount of iodine, according to the criteria proposed by Kowalski in 1972, is estimated as follows: 5 mg / kg - insufficient, 5-40 - normal and more than 40 mg / kg -excess. The amount of water-soluble iodine, according to the criteria proposed by Pokatilov in 1993, is estimated as follows: low 0.011-0.03, decreased 0.03-0.05, optimal 0.05-0.1 mg / kg. So, one can state general considerations about the ecological status of iodine in Western Siberia. Almost all types of zonal soils are depleted of gross iodine, except for chernozems. Solonchaks, solonetses are provided with iodine. There is a clear deficit of water-soluble iodine in many types of soils. Sometimes the content of iodine in plants exceeds the concentration of watersoluble form of halogen. This means that other mobile forms, in particular the soluble form, also participate in plant nutrition. This makes it necessary to further study it, especially since its concentration is higher than the watersoluble form. 9