ISSN 1408-7073 RMZ - MATERIALS AND GEOENVIRONMENT PERIODICAL FOR MINING, METALLURGY AND GEOLOGY RMZ - MATERIALI IN GEOOKOLJE REVIJA ZA RUDARSTVO, METALURGIJO IN GEOLOGIJO RMZ-M&G, Vol. 58, No. 3 pp. 241-356 (2011) Ljubljana, September 2011 Historical Rewiev More than 80 years have passed since in 1919 the University Ljubljana in Slovenia was founded. Technical fields were joint in the School of Engineering that included the Geologic and Mining Division while the Metallurgy Division was established in 1939 only. Today the Departments of Geology, Mining and Geotechnology, Materials and Metallurgy are part of the Faculty of Natural Sciences and Engineering, University of Ljubljana. Before War II the members of the Mining Section together with the Association of Yugoslav Mining and Metallurgy Engineers began to publish the summaries of their research and studies in their technical periodical Rudarski zbornik (Mining Proceedings). Three volumes of Rudarski zbornik (1937, 1938 and 1939) were published. The War interrupted the publication and not untill 1952 the first number of the new journal Rudarsko-metalurski zbornik - RMZ (Mining and Metallurgy Quarterly) has been published by the Division of Mining and Metallurgy, University of Ljubljana. Later the journal has been regularly published quarterly by the Departments of Geology, Mining and Geotechnology, Materials and Metallurgy, and the Institute for Mining, Geotechnology and Environment. On the meeting of the Advisory and the Editorial Board on May 22nd 1998 Rudarsko-metalurski zbornik has been renamed into "RMZ - Materials and Geoenvironment (RMZ -Materiali in Geookolje)" or shortly RMZ - M&G. RMZ - M&G is managed by an international advisory and editorial board and is exchanged with other world-known periodicals. All the papers are reviewed by the corresponding professionals and experts. RMZ - M&G is the only scientific and professional periodical in Slovenia, which is published in the same form nearly 50 years. It incorporates the scientific and professional topics in geology, mining, and geotechnology, in materials and in metallurgy. The wide range of topics inside the geosciences are wellcome to be published in the RMZ -Materials and Geoenvironment. Research results in geology, hydrogeology, mining, geotechnology, materials, metallurgy, natural and antropogenic pollution of environment, biogeochemistry are proposed fields of work which the journal will handle. RMZ -M&G is co-issued and co-financed by the Faculty of Natural Sciences and Engineering Ljubljana, and the Institute for Mining, Geotechnology and Environment Ljubljana. In addition it is financially supported also by the Ministry of Higher Education, Science and Technology of Republic of Slovenia. Editor in chief 241 Table of Contents - Kazalo Original Scientific Papers - Izvirni znanstveni članki The effect of defects on tensile strength of the continuous steel casting products Vpliv napak na natezno trdnost kontinuirno ulitih jeklenih proizvodov Gone, M., Lazic, L., Kožuh, S., Kosec, L. An analysis of the quasi-chemical model of a ternary solution: On the counting of pairs Analiza kvazikemičnega modela ternarne raztopine: O štetju parov Chen, J. Finite element solution strategy to analyze heterogeneous structures 259 Strategija analize heterogenih struktur z metodo končnih elementov Lamut, M. 253 273 Tracing coalbed gas dynamics and origin of gases in advancement of the working faces at mining areas Preloge and Pesje, Velenje Basin Spremljanje sestave premogovega plina in izor plinov z napredovanjem čela delovišč na pridobivalnih (rudarskih) območjih jam Preloge in Pesje, Velenjski bazen Kanduč, T., Žula, J. Zavšek, S. Sediment transport and sedimentation in a coastal ecosystem - a case study 289 Sedimentni transport in sedimentacija v priobalnem ekosistemu - zgled študije Purandara, B. K., Venkatesh, B., Choubey, V. K. Integrated remote sensing and GIS approach to groundwater potential assessment in the basement terrain of Ekiti area southwestern Nigeria Povezava daljinskega ugotavljanja in GIS za oceno potenciala podtalnice v kristalinični podlagi območja Ekiti v jugozahodni Nigeriji Talabi, A. O., Tijani, M. N. 303 Preliminary notes - Predhodna objava Influence of the heat treatment and extrusion process on the mechanical 9 and microstructural properties of the AISi1MgMn Alloy Vpliv toplotne obdelave in postopka iztiskanja na mehanske in mikrostrukturne lastnosti zlitine AISi1MgMn Steinacher, M., Dragojevič, V, Smolej, A. Event notes - Novice Petdeset let delovanja Metalurškega instituta "Kemal Kapetanovic" v Zenici 339 Kosec, B., Rimac, M. Author s Index, Vol. 58, No. 3 342 Instructions to Authors 343 Template 351 The effect of defects on tensile strength of the continuous steel casting products Vpliv napak na natezno trdnost kontinuirno ulitih jeklenih proizvodov Mirko Gojic1-*, Ladislav Lazic1, Stjepan Kožuh1, Ladislav Kosec2 University of Zagreb, Faculty of Metallurgy, Aleja narodnih heroja 3, 44103 Sisak, Croatia ^University of Ljubljana, Faculty of Natural Sciences and Engineering, Aškerčeva 12, 1000 Ljubljana, Slovenia Corresponding author. E-mail: gojic@simet.hr Received: May 23, 2011 Accepted: October 6, 2011 Abstract: The goal of this paper is to determine the influence of defects on tensile strength of continuous casting steel products made from low alloy Mn-V steel. The microstructure was determined by optical microscopy and scanning electron microscopy. The composition of non-metallic inclusions were determined by energy dispersive X-ray spectroscopy. The microstructural analysis has shown that there are significant differences between the microstructure near the surface and in the central zone of the round cross-section. It was found that a significant decrease in tensile strength can be correlated the presence of alumina and sulphide inclusions as well as dendritic structure. Povzetek: Namen članka je določiti vpliv napak na natezno trdnost kontinuirno ulitih jeklenih proizvodov, izdelanih iz Mn-V maloogljičnega jekla. Mikrostruktura je bila analizirana z optičnim mikroskopom in vrstičnim elektronskim mikroskopom. Kemična sestava nekovinskih vključkov je bila opredeljena z energijsko disperzijsko spektroskopijo rentgenskih žarkov. Mikrostrukturna analiza je pokazala občutno razliko med mikrostrukturo blizu površine in tisto v centralni coni prečnega prereza. Ugotovili smo, da je občuten padec natezne trdnosti v korelaci-ji s prisotnostjo aluminatnih in sulfidnih nekovinskih vključkov in tudi z dendritsko strukturo. Key words: low alloy steel, solidification, non-metallic inclusions, continuous casting Ključne besede: maloogljično jeklo, strjevanje, nekovinski vključki, kon-tinuirno litje Introduction It is known that continuous casting of steels involves many physical phenomena (fluid flow, heat transfer, solidification etc.).[1-4] The flow of liquid steel inside the strand influences the quality of solidified steel, solidification structure, inclusion distribution and segregation.[5] One of the factors in connecting the quality of steel products is the cleanness of the steel, which refers to the non-metallic inclusion content in the steel. The presence of the defects from the steelmaking process can initiate a local weakness of the steel and its failure during application. Among others, low alloy steels are used commonly for oil country tubular goods (OCTG). The main reasons for this application are excellent hardenability, high strength, good toughness and high resistance to sulphide stress corrosion cracking (SSCC) as a form of hydrogen embrittlement.[6] Since these steels are used under complex loads, their defects (especially non-metallic inclusions) should be strictly controlled to decrease their negative effects.[7] Limitation of non-metallic inclusions and reduction of centreline segregation have a very important role in increas- ing the resistance of low alloy steels to hydrogen induced cracking (HIC) and sulphide stress cracking (SSC). Non-metallic inclusions in steel are originated from deoxidation, reoxidation, segregation and chemical reactions with the refractories.[8, 9] Since mechanical properties and resistance to corrosion are influenced by the presence of defects in the steel, the objective of this paper is to establish the type, size and distribution of non-metallic inclusions and dendritic structure across the cross-section of the continuous casting products, as well as their impact on tensile strength. The obtained results will serve in the subsequent thermal stress analyses, questioning whether the temperature differences, appearing across the cross-section of the products heated in the rotary-hearth furnace, lead to thermal stresses which exceed the tensile strength of the final products and cause stress cracks in the structure. The investigation methodology consists of testing the tensile strength of the specimens taken at different places of cross-section of cast products, as well as examinations of the microstructural features of steel structure and defects on the tested tensile specimens using optical microscope (OM) and scanning electron microscope (SEM) methods, respectively. Materials and methods The cast steels for this investigation were produced in an electric arc furnace. The range of composition of the steel under investigation is given in Table 1. As can be seen, the steel grade corresponds to the low alloy Mn-V steel. The molten steel is continuously cast in the round cross-section with the diameter of 410 mm. Specimens for tensile tests were machined from the round cross-section in accordance with ASTM standards.[10] The specimens were taken from the mid-thickness location in two series all over the cross-section, starting from the surface, across the central zone to the opposite end (Figure 1). In this sequence, the specimens were tested at test temperatures from 100 °C up to 650 °C, with the step of 50 °C. The specimens were elongated to fracture on Zwick 50 kN tensile testing machine. The specimens for metallographic analysis were grinded and polished. After that the specimens were etched by a nital solution consisting of 5 % nitric acid in ethyl alcohol. Metallographic analysis was carried out on both etched and non-etched samples. Microstructural examination was carried out using an optical microscope (OM) and scanning electron microscope (SEM) equipped with energy dispersive X-ray spectrometry (EDX). EDX unit was used for the spot aimed chemical X-ray mi-croanalysis. Fraction of inclusions was determined by quantitative metallogra- Samples 1.1 3.1 2.1 3.2 3.1 4.1 3.4 5,1 3.5 6.1 3.6 7.1 3.7 8,1 3.8 9.1 3.9 10.1 3.10 11.1 3.11 12.1 3.12 2eAB, the solution tends to segregate into A-rich and B-rich regions. A quasi-chemical solution model accounts for the non-random distribution of atoms. It starts with the partition function , which equals the sum of all microstates the system can occupy. Q =Xexp{- where k is the Boltzmann constant and 1/kT is the inverse temperature; E. is the energy level of microstate i. Each microstate has a unique arrangement of atoms. Hence, E is the function of numbers of different pairs and associated interaction energies. Thermodynamic quantities like the Gibbs free energy and the activity of a solute can be deduced from the partition function. An exact solution of the partition function in two dimensions was obtained by onsager.[7] The partition function has not been evaluated exactly for a three dimensional lattice. The system researched in the work by Alex and McLellan contains A, B and c atoms. A and B form a substitutional solution, and may interchange positions on the sites. Whereas c atom occupy sites in the space between the A and B atoms. It is an interstitial solute of the solvent A and B. Figure 1 shows a body-centered cubic (BCC) lattice model. any interstice are designated as Z1 and Z2 respectively. In the BCC structure, Z1 equals 4, and Z 2equals 2 (Figure 3). The number of A, B and c atoms are designated as NA, NB and Nc respectively. The ratio of interstitial sites per lattice atom is p. Therefore the number of empty sites e equals (NA + NB) p -Nc. The pairs of nearest neighbouring atoms are separated by half the lattice parameter a/2 and can be divided into two groups (Figure 2). The number of nearest interstices and the number of nearest lattice atoms to The difficulty Alex and McLellan proposed a set of formulae counting the numbers of the seven kinds of pairs for the construction of a quasi-chemical model. For the first group of pairs, it starts with the number of pairs between atom c and site e, which is simply designated as Z]Xy Then the number of c-c pairs equals the total interstitial pairs con- Figure 1. The ternary system consists of three types of atoms: type A, type B and type c. Atoms A and B form the BCC lattice, and atom c and empty sites e are the octahedral sites in BCC structure. Figure 2. The left shows the pairs between interstices, i.e. c-e, c-c and e-e, and the right shows the pairs between interstice and a main lattice atom, i.e. c-A, c-B, e-A and e-B. Figure 3. Zt is the number of nearest interstices to any interstice. Z2 is the number of main lattice atoms to any interstice. Table 1. Formulae of the number of pairs used in a ternary quasi-chemical model[5] Type of pair Count c-e and e-c Vi c-c (z^-z^yi e-e [Z, (Na + Nb)p - (Z,Nc ~ Z&) ~ 2 Z^J/2 c-A ZA c-B Z2N-Z2X2 e-A ZNa-z2x2 e-B Z2Nb-(Z2N-Z2X2) necting to c, ZxNc, minus those connecting c to e, and then divided by 2 as the same pair is double counted by either c of the pair. The same logic applies to the e-e pairs. For the second group of pairs, first the number of pairs between c and A is designated as Z2^2. Then the number of c-B pairs equals all the pairs connected to c minus the c-A pairs. The formulae of the numbers of e-A and e-B pairs are problematic, which will be discussed below. The list of the formulae of the counting of the pairs used by Alex & McLellan is shown on Table 1. Let us take a closer look at the number of e-A pair and e-B pair. A simple sum of the formulae of e-A and e-B pairs in Table 1 yields the equation for the total number of pairs connecting e to A or B atoms. (ZN - Wl z2(na+np)p-z2n (2) Zna - ZÀl + ZNB = z2 Na+nb) - z2nc (1) However, clearly the two equations are not equal, as equals 3 for a BCC lattice. The solution To solve the problem, a new variable, Z3 is needed. It is the number of nearest interstices to an A atom or a B atom (Figure 4). For both body-centered cubic metal, e.g. ferrite in steel and face-centered cubic metal, e.g. austenite in steel, Z3 equals 6. Equation 1, in principle, should equal the number of all pairs connecting to both c and e, Z2 (NA + NB)fi, minus c-A Figure 4. Z3 is the number of nearest in-and c-B pairs terstices to a lattice atom. Table 2. The comparison of the formulae of e-A and e-B pairs. Type of pair Old count New count e-A ZJV, - z± Z,jV, - z± e-B Z^-iZ^-ZX) The number of e-A pairs equals the total number of pairs connecting A to interstices, Z3Na, minus c-A pairs Z3NA - Z2^2 And the number of e-B pairs equals all the pairs connecting e to lattice atoms, Z2[(Na + NB)fi - Nc], minus e-A pairs WA + Nb)P - NJ - (Z3NA - Z2^2) or + W - Z3NA - ZN - ZA) The new and old formulae are compared in Table 2 Conclusion A careful investigation of the quasi-chemical model of a ternary solid solution proposed by Alex & McLellan[5] has revealed a mistake in two formulae counting the number of pairs. The solution to the flaw proposed in this work will give a new quasi-chemical model of the solid solution, which will produce different functions of thermodynamic properties. It would be interesting to investigate the compatibility of the new quasi-chemical model of the ternary system with the model of a binary system[2] at the limits where NB ^ 0, or the interaction energy eBX ^ eAX, where X represents the interstitial atom in the system. References [1] J. A. Lobo & G. H. Geiger (1976): Thermodynamics and Solubility of Carbon in Ferrite and Ferri-tic Fe-Mo Alloys. Metallurgical Transactions A; 7A:1347. [2] R. B. McLellan & W. W. Dunn (1969): A Quasi-Chemical Treatment of Interstitial Solid Solutions: Its Application to Carbon Austenite. J. Phys. Chem. Solids; 30:2631-2637. [3] L. M. Yu, F. X. Yin & D. H. Ping (2007): Natural Mechanism of the Broadened Snoek Relaxation Profile in Ternary Body-cen-tered-cubic Alloys. Phys. Rev. B; 75(17):174105. [4] M. Grujicic & X. W. Zhou (1993): Monte-carlo Analysis of Short-range Order in Nitrogen-strengthened Fe-Ni-Cr-N Austen-itic Alloys.Materials Science and Engineering A, 169:103-110. [5] K. Alex & R. B. McLellan (1971): A Quasi-Chemical Approach to the Thermodynamics of Ternary Solid Solutions Containing Both Substitutional and Interstitial Solute Atoms. J. Phys. Chem. Solids; 32:449-457. [6] E. A. Guggenheim (1952): Mixtures. Oxford University Press, Oxford. [7] L. Onsager (1944): Crystal Statis- tics. I. A Two-Dimensional Model with an Order-Disorder Transition. Phys. Rev.; 65:117-149. Finite element solution strategy to analyze heterogeneous structures Strategija analize heterogenih struktur z metodo končnih elementov Martin Lamut 1CO Vesolje-SI, Aškerčeva 12, 1000 Ljubljana, Slovenia Corresponding author. E-mail: martin.lamut@space.si * Received: September 19, 2011 Accepted: November 2, 2011 Abstract: In this contribution a general strategy for solving a coupled micro-macro problems is presented which enables analyses of modern heterogeneous materials. It provides an efficient problem solving tool to structures with complex microstructures, used in a demanding structural components. The method uses a nested finite element solution strategy called multilevel finite element approach-ML-FEM. Within the ML-FEM framework one conducts an embedded micro-scale computation in order to obtain quantities required at the macroscopic level. The application of ML-FEM circumvents the need to construct an explicit macroscale constitution formulation, considering increased computational costs. Increased computation is linked to detailed microscopic analysis for which the statistical representative volume element-RVE is needed. RVE will be derived based on the convergence criterion. In this work a general method for calculation of the consistent macroscopic stiffness matrix via sensitivity analysis of a micro level is shown. As an example the proposed method is applied on a simple test specimen under compression consisting microstructures with porosities and stiff inclusions. Povzetek: V tem delu je bila razvita splošna strategija za reševanje vezanih mikro-makro sodobnih heterogenih materialov. Strategija je učinkovito orodje pri reševanju problemov s kompleksno mikrostrukturo, uporabljeno v zahtevnih inženirskih komponentah. Strategija uporablja večnivojski način reševanja problemov, kjer na mikroskopski in makroskopski ravni poteka analiza z metodo končnih elementov (ML-FEM). Pri tej metodi reševanja makroskopska konstitutivna zveza ni več potrebna, saj je le-ta na račun povečanega računskega časa pridobljena z natančno mikroskopsko analizo. Ta je izvedena na statističnem reprezentativnem volumnu (RVE), katerega velikost določimo s konvergenčnim merilom. Metoda je splošen način reševanja makroskopske togostne matrike preko občutljivostne analize mikroskopskega nivoja. Lastnosti metode so bile preizkušene na enostavnem tlačnem preizkusu za porozno mikrostrukturo in mikrostrukturo s togimi vključki. Keywords: Heterogeneous materials, multiscale analysis, macroscopic tangent computation, sensitivity analysis Ključne besede: heterogeni materiali, mikro-makro analize, makroskopska togost, občutljivostna analiza Introduction Heterogeneous materials used in engineering sciences have physical properties that vary throughout their microstructures. Heterogeneities, such as inclusions, pores, fibers and grain boundaries, have a significant impact on the observed macroscopic behavior of multi-phase materials. In engineering some typical examples are metal alloy systems, various composites, porous and cracked structures, polymeric blends and polycrystalline materials. To describe the macroscopic overall characteristics of heterogeneous structures is a vital problem in many engineering applications. The ability to convey information across length scales is essential for a better understanding of the sources of physical behavior observed on higher scales. Using mi- cromechanical models of the microstructural elements, homogenization techniques allow an efficient and correct transfer of microscale information to the macroscale analysis. The fundamental methodology of homogenization is the characterization of the macroscopic behavior of the heterogeneous material by appropriately identifying and testing a statistically representative micromechanical sample. Once an appropriate sample is identified it can be used in the multiscale analysis methodology. The most straightforward way is to use the multilevel finite element method ML-FEM[1-5]. When analyses at both levels are made in the context of FEM, it can be referred to as the FE2 method[6, 7]. The application of ML-FEM circumvents the need to construct an explicit macroscale constitution formulation, though at an increased computational cost. The con- stitutive equations are written only on microscopic scale and homogenisation and localization equations are used to compute the macroscopic strains and stresses knowing the mechanical state at microscopic level. By analyzing the engineering structure, the point of interest is usually localized in the so called critical region, where detailed analyses are needed. So to further increase the efficiency of the computation the structure can be divided into subdomains, critical region and the rest of the structure. In the critical region an embedded ML-FEM computation is conducted, while elsewhere a classical homogenization technique is used. In either case a statistical mi-cromechanical model or representative volume element (RVE) will be needed. The purpose of this contribution is mainly two fold. First, the statistical RVE size will be derived based on convergence criterion of the several parameters being monitored. The second purpose of this work tackles the efficiency of multilevel computation. Since a conventional way of macroscopic tangent computation in a condensation procedure, necessitate the computation of a Shur complement. It inflicts for increasingly complex microstructure higher memory allocation demands that may not be met by today's computers. Therefore, as an alternative, a tangent computation tech- nique based on a sensitivity analysis of a microscopic level will be presented. Methods Numerical RVE size In order to estimate the effective properties of heterogeneous material, most of the micro-macro methods assume the existence of a micromechanical sample that is statistically representative of the microstructural features. The usual approach[8] is to determine a relation between averages, E\ defined through (o)RVE = E*(e)RVE . Here o and e are the stress and strain fields within a statistically representative volume element. The RVE is considered both smaller enough than the macro scale media and bigger enough than the heterogeneities on the micro scale, without introducing non-existing properties (e.g. anisotropy). In this contribution, macroscopically isotropic materials are considered, therefore the two linear elastic constants (bulk and shear moduli) describing the form of E'can be computed using: (1.1) ¡(^RVE-j^RVE V (s')xMv where a' and e' denotes the deviatoric part. Macroscopically isotropic heterogeneous structure is achieved by random particle distribution at the mi-croscale. Therefore, for a given sample size, multiple distributions of particles are possible. In order to capture a statistical measure of the range of responses from different distributions, a simple averaging of three samples per RVE size was used. To model random porous microstructures a matrix containing randomly distributed pores throughout a square L x L was considered. The size of the particles were determined relatively to unit length of the RVE such that 0.1 < 2r < .15. Mechanical properties of the matrix material was K = 167 GPa and G = 77 GPa. In order to determine a suitable RVE size, one must monitor the range of estimates to E" for successively larger samples, shown on Figure 1. The following sequences of particles per sample are used (N): 2, 4, 15 and 32. Relying on the expectation as RVE size increases indefinitely the effective properties of material constants (K, G) will converge towards E\ For numerical simulation of the response a 2D quadrilateral plane strain 2 x2 Gauss rule elements were used. To determine the effective bulk and shear moduli, since the effective response is assumed isotropic, only one test loading is necessary en = 0.01005. In Table 1, the perturbation magnitudes are shown for various quantities as a function of pore number in the sample. Besides convergent material properties, the RVE must be tested upon the influence of the microstructural geometry Figure 1. A series of test samples with increasing size, the volume fraction of particles is fixed at 0.6 %. Table 1. Perturbation magnitudes for shear and bulk moduli as a function of particles number (N). K G N RVE size k32 ~ k v Gn ~GN Kn Gn 2 0.73 0.0 IX 0.018 4 1 0.021 0.023 15 2 0.013 0.013 32 3 0.002 0.005 properties. This can be done by tracking various quantities such as: strain energy function, maximal stresses, averaged stresses in the particles or matrix etc. In this work the maximal effective stress was considered (von Misses). To guarantee the mixed stress fields besides the previously used normal test loading en = 0.01005 the shear loading condition was used e12 = 0.01005 all the rest stays the same as described previously. Figure 2 is showing the convergence of the max. effective stress in the RVE by increasing its size. Based on the tests the statistical RVE size 2 (approximately 15 particles) is chosen. This size is used in all subsequent analysis. The outline of the determination of the RVE size and ef- size Figure 2. Max. effective stress for two loading cases depending upon RVE size Table 2. Perturbation magnitudes of max. oeff for normal and shear load condition as a function of particles number (N). n RVE size fb fs 5 C c02 <*.) s13cch4 August 18, 2010 341 42.2 57.8 0.0 57.8 1.8 -31.0 August 31, 2010 316.4 43.5 56.5 0.0 56.5 -1.1 -37.2 September 22, 2010 307.5 46.1 53.9 0 53.9 -6.6 -29.8 November 30, 2010 152.1 42.3 57.7 0.0 57.7 0.9 -50.0 Working face G2/C, borehole jpk-31/10, mining area Preloge North Date of sampling Distance of the working face ch4 vol. % C02 vol % n2 vol. % CDMI index (%) 5 C co2 (%„) ® Com (%o) August 20, 2010 335.3 45.7 54.3 0.0 54.3 -1.7 -45.5 August 27, 2010 316.4 30.7 69.3 0.0 69.3 -9.1 September 22, 2010 307.5 36.6 63.4 0.0 63.4 -3.9 -60.4 November 30, 2010 152.1 43.3 56.7 0.0 56.7 -0.7 -50.3 Working face -50/B, borehole jpk-22/09, mining area Pesje Date of sampling Distance of the working face ch4 vol. % c02 vol % n2 vol. % CDMI index (%) s ° ^ c02 (%„) 0 Ljchi November 16,2009 December 14, 2009 January 11, 2010 February 22, 2010 February 24, 2010 March 15, 2010 March 22, 2010 267 214 181 79 76 35 26 41.3 19.9 33.1 24.5 28.0 42.1 27.6 58.7 80.1 66.9 75.5 72.0 57.9 72.4 0.0 0.0 0.0 0.0 0.0 0.0 0.0 58.7 80.1 66.9 75.5 72.0 57.9 72.4 2.28 -4.76 -0.70 -2.1 -4.4 -0.1 1.0 -26.9 -44.4 ^42.6 -58.0 -60.6 -48.3 -56.6 Working face -50/B, borehole jpk-23/09, mining area Pesje Date of sampling Distance of the working face ch4 vol. % co2 vol % N2 vol. % cdmi index (%) s c c02 (%„) 5 cch4 (%o) November 16,2009 267 38.7 61.3 0.0 61.3 0.44 -49.4 February 22, 2010 79 24.5 75.5 00 75.5 -2.2 -583 February 24, 2010 76 28.0 72.0 0.0 72.0 -4.4 -60.6 March 8, 2010 48.2 19.2 80.8 00 80.8 -1.3 -54.6 March 15, 2010 35 26.0 740 00 74.0 -2.5 -59.6 with advance of the working face enable migration of methane through lignite seam in surrounding strata or to a surface, while CO2 remains adsorbed in lignite seam. Figures 3 A, B and C show concentrations of CO2 and methane at researched mining areas (Preloge North, Preloge South and Pesje) in advancement of the working face (-120/B, G2/C and -50/B). Generally, at all working faces it was observed that methane migrates faster than CO2 with advance of the working face, therefore the trend of maximum of methane concentration coincides with minimum CO2 concentrations (Figures 3 A, B and C). Tempo- ral changes of coalbed concentrations (CO2 and methane) fluctuate with the rate of advancement of working faces (Figures 3 A, B and C). At the working face -120/B it was observed that at the distance of the working face 92 m (rate of advancement of working face 2.5 m/d) caused highest concentrations in methane and lowest concentration in CO2 (Figure 3 A). At the distance of the working face 45 m (rate of advancement of the working face cca. 2 m/d) the next maximum of CO2 was detected, coinciding with minimum of methane concentrations. After May 13 the rate of working face approaching to borehole jpk-28/10 gradually slowed down (rate of advancement Figure 2. Concentration of CO2 versus concentration of methane in lignite seam in advancement of the working faces (-120/B Preloge South, G2/C Preloge North, -50/B Pesje) of working face cca. 1 m/d) causing lower fluctuations in concentration of CO2 and methane. At the working face G2/C no trends of increasing/decreasing of CO2 and methane concentrations are observed, probably due to constant approaching of the working face with average rate 1.9 m/d to the boreholes jpk-30/10 and jpk-31/10 (Figure 3 B). The rate of advancement of the working face -50/B was from 0.9 m/d to 2.4 m/d. Maximum methane and minimum methane concentrations were traced within borehole jpk-22/09 at the distance of the working face 35 m (rate of advancement of working face cca. 2.2 m/d) (Figure 3 C). Approaching of the working face also influence on stress situation at working face (Figure 4). During excavation of lignite secondary fissures are generated due to rearrangement of primary stress conditions, enabling releasing of coalbed gas preserved in pores of coalbed reservoir. These stress conditions are presented in Figure 4 modified after William (1999). Results of changing of stresses were investigated by three axis cells build in lignite structure. The research revealed that at the distance of 120 m from the working face vertical stresses start to increase. At the distance of 80 m from the working face shearing and collapsing of lignite structure occur; vertical stresses continue to increase while horizontal and transverse stresses decrease. At the distance of the working face 30-50 m from three axis cell vertical stresses are so high that the lignite structure collapse (Zavsek, 1990). Research of temporal variations of concentrations (CO2 and methane) within borehole 780H IV at working face -80c similar trends as at working faces -120/B, G2/C and-50/B in concentrations of CO2 and methane were observed; at the distance of the working face 177 m and 122 m maximum concentrations of methane were traced and coincide with minimum concentrations of CO2 (Kanduc, 2004). Besides the rate of advancement of the working face concentrations of methane and CO2 measured in lignite seam within boreholes (jpk-28/10, jpk-30/10, jpk-31/10, jpk-22/09 and jpk-23/09) also depends on permeability and porosity of lignite seam. When methane and CO2 reaches strata with high permeability such as fault zones, their concentrations start to increase, therefore also areas with high concentrations of methane and CO2 might be expected. CO2 behaves at certain condition (above its critical temperature 31.1 °C and critical pressure 7.39 MPa, expanding to fill its container like a gas but with a density like that of a liquid) as supercritical fluid (Atkins, 1994), meaning that could be at liquid and gas phases. The conditions of critical temperature and pressure for CO2 are possibly reached at working faces causing its adsorption (liquid phase)/desorption (gas phase). Areas with high CO2 content (CDMI index) might be potentially danger- Figure 3A. Concentration of methane and CO2 versus date of sampling in advancement of the working face -120/B (Preloge South) Figure 3B. Concentration of methane and CO2 versus date of sampling in advancement of the working face G2/C (Preloge North) Figure 3C. Concentration of methane and CO2 versus date of sampling in advancement of the working face -50/B (Pesje) ous for gas outbursts (Clayton, 1998). Anyway, investigation of gas concentrations at each working face should be further related to petrological characteristics of lignite (lithotype type e. g. xylite, detrite), tectonically characteristics (characteristics of fault zones) and geotechnical conditions (pressures, porosity and permeability) to get better insight to coalbed gas migration as well sorption/desorption processes, especially CO2 through lignite. Interpretation of coalbed gases from investigated mining areas of Pesje and Preloge was performed according to previous study of tracing inorganic and organic carbon cycles in different geological media (calcified xylite, carbonate lenses in the lignite seam, lignite and Pliocene, Triassic and Lithotam- nium aquifers) (Kanduc et al., 2010, in review). From the results it was concluded that coalbed gases in the Velenje Basin are mainly microbial (bacterial) origin, while CO2 could be also endogenic. Microbes that generate methane (methanogens) could have either of been deposited with the coal sediments in the geologic past or transported in more recently with active groundwater recharge. To thrive methanogens require an anoxic, aqueous environment with organic carbon substrates and the absence of other free-energy electron acceptors, such as NO3- and SO42-. Fermentative bacteria degrade complex organic matter in coalbeds (e.g. structures of carbohydrates, proteins and lipids that originate in vegetation and sediments) to simpler molecules including acetate (CH3COOH), fatty acids, CO2 and H2 gas. Acetogenic bacteria thrive on fatty acid products to produce acetate, with CO2 and H2 by products (Kotelnikova, 2002). The products of these reactions support a variety of methanogens. Some metha-nogens use an acetate food source to produce CO2 and methane, according to following reactions: ch3cooh ^ ch4 + CO2 Acetate fermentation (2) While other methanogens use the hydrogen gas to reduce CO2: CO2 + 4H2 ^ CH4 + 2H2O CO reduction or HCO3- +4H2 ^ CH4 + 2H2O + OH-CO„ reduction with the 13C isotope and depletion of 12C in generated CO2 (Figure 5). It is known that coalbed lignite strata were formed in the Pliocene in a calm sedimentary environment (Markic & Sachsenhofer, 1997), but the proportion of early stage microbial gas retained in the lignite structure (Smith & Pallaser, 1996) is difficult to estimate. Microbial methane in Velenje basin was generated by microbial reduction and/or by microbial fermentation. Also recent microbial activity (methanogenic and methanotrophic bacteria) might generate microbial (3) (4) We applied diagrams 513CCH4 versus S13CCO2 (Figure 5) to explain the origin of methane and 513CCO2 versus CDMI index (Figure 6) to explain the origin of CO2. 513CCH4 (Figure 4) in the Velenje basin indicate the successive origin of methane: microbial (CO2 reduction) with 513CCH4 values from -40 %o to -50 %, microbial (acetate fermentation) with 513CCH4 less than -50 % and mixed origin between these two (Clayton, 1998). Enrichment with 13C in methane could be also due to microbial oxidation of methane, which results in an enrichment of residual methane Figure 4. Geomechanical conditions and generation of secondary fissures due to longwall method of excavation of lignite, causing a realese of coalbed gases inside of demolished zone (adapted after Williams, 1999) 284 Kanduc, t., žuLA, j., zavšEK, S. Figure 5. Interpretation of the origin of methane in the Velenje basin using S13CCH4 versus S13CCO2 in a lignite seam at boreholes (jpk - 28/10, jpk - 30/10, .jpk - 31/10, jpk - 22/09 and jpk - 23/09) in advancement of the working faces (-120/B, G2/C and -50/B) Figure 6. Interpretation of the origin of CO2 at working faces (-120/B, G2/C in -50/B) using S13CCO2 versus CDMI index in a lignite seam in boreholes (jpk - 28/10, jpk - 30/10, jpk - 31/10, jpk - 22/09 and jpk - 23/09) ahead of the working faces (-120/B, G2/C and -50/B) gas (Kotelnikova, 2002). Methane and CO2 were/are generated by mi-crobial fermentation process while methane was/is generated by CO2 reduction process. CO2 generated by fermentation process is characterized by 513CCO2 similar that organic matter around -25 %o, while microbial reduction process results in an enrichment with the 13C of residual CO2 (Figures 5 and 6). Microbial CO2 reduction is characteristic in mining area Preloge North, while at Preloge South 513CCH4 indicate bacterial origin via fermentation. At mining area Pesje both micro-bial (CO2 reduction and methane fermentation) processes generated methane formation (Figure 5). The origin of CO2 is interesting due to its relation with outbursts in coalmines. High concentrations of carbon dioxide in seam gases in Australian coals occur in regions of igneous activity and associated faulting and this component has been described as being of presumed pneumatolytic origin (Smith & Gould, 1980). In our study CDMI index versus 513CCO2 (Figure 5) was used to explain the origin of CO2 (Kotarba, 2001) and indicate endogenic CO2 (including CO2 originating from carbonates) and CO2 of microbial origin in relation to micro-bial methane (working face Preloge North, jpk-30/10) discussed above. At working face Pesje -50/B (jpk-22/09 and jpk-23/09) 513CCO2 indicate micro- bial and endogenic origin (Figure 6). Typical endogenic values of 513CCO2 are about -7 %o (Kotarba, 2001) and high CDMI index found in our study (at working face Preloge South, jpk-28/10) are probably related to the tectonics of the Šoštanj and Smrekovec faults at the time of formation of the Velenje basin. 513CCO2 derived from carbonates is dependent on 513C of carbonates and the temperature of their degradation. The resulting products are clay minerals and CO2. Supposing that dolomites underwent thermal decomposition and are located below lignite seam along the Šoštanj fault zone values of 513CCO2 from -2 %o to -6 %o might indicate CO2 of thermal decomposition of dolomites (Figure 6). This source of CO2 has similar values as endog-enic CO2 from the fault zones and can not be distinguished with 513CCO2. Also secondary processes should be considered since they might camouflage the origin of gases. Migration of gases as a secondary process caused by reduction of pressure in lignite seam causes enrichment in light 12C isotope in methane and in CO2. During migration of coalbed gases, gases of different origin might be mixed together and complicate interpretation of gas origin. Conclusions Gas outbursts remain for coalminers one of the main problems in the Velenje coalmine, therefore geochemical investigations are one of the important parameters used in case of prediction or prevention gas outbursts. Concentrations of methane and CO2 change in advance of the working face. Areas with high CO2 concentrations accompany with low methane concentrations and could be related with the rate of advancement of the working face. The rate of advancement of the working face is one of the crucial parameters influencing on gas composition at working faces. Concentrations and stable isotope studies of coalbed gases at working faces allow the possible interpretation of the origin of coalbed gas in the Velenje basin. Considering also the results of previous studies, it can be concluded that coalbed CO2 from investigated working faces is endogenic and bacterial origin. Methane is microbial origin (formed through microbial fermentation and/or CO2 reduction). Secondary processes like migration, adsorption/ desorption and mixing of gases of different origin during excavation complicate the interpretation of gas origin and were neglected in interpretation of the origin of coalbed gases. Examination of the origin of nitrogen (at loca- tions with excess of nitrogen) in coal-bed gases from Velenje Basin needs further research. Acknowledgements This study was conducted in the framework of project Z1-2052 funded by the Slovenian Research Agency (ARRS) and the Velenje Coalmine d.d. The authors are also grateful to Mr. Tedej Zagoricnik, Mr. Robert Lah and Mr. Stojan Zigon for technical support, assistance in the field sampling and laboratory analyses. Sincere thanks to Dr. Jennifer Mcintosh for improving the English of the manuscript. References Aravena, R., Harrison, S. M., Barker, J. F., Abercrombie, H. & Rudolph, D. (2003): Origin of methane in the Elk Valley coalfield, southeastern British Columbia, Canada. Chem. Geol.; Vol. 195, pp. 219227. Atkins, P. W. (1994): Physical Chemistry, fifth ed. Oxford Univ. Press, Oxford, pp. 1031. Clayton, J. L. (1998): Geochemistry of coalbed gas - A review. Inter J. Coal Geol.; Vol. 35, pp. 159-173. Coplen, T. B. (1996): New guidenices for reporting stable hydrogen, carbon and oxygen isotopes ratio data. Geochim. Cosmochim. Acta; Vol. 60, pp. 390-3360. Flores, R. M. (1998): Coalbed methane: From hazard to resource. Inter. J. Coal Geol.; Vol. 35, pp. 3-26. Kanduc, T. 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Sediment transport and sedimentation in a coastal ecosystem - a case study Sedimentni transport in sedimentacija v priobalnem ekosistemu - zgled študije B. K. Purandara1, B. Venkatesh1 & v. K. choubey2 1 Regional Center, National Institute of Hydrology, Hanuman Nagar, Belgaum - 590 001 Karnataka, India 2NIH, Roorkee - 2447667, Uttarakhand, India Corresponding author. E-mail: purandarabk@yahoo.com Received: August 27, 2011 Accepted: November 2, 2011 Abstract: The determination and interpretation of particle grain-size has a fundamental role in hydraulics, geomorphology and sedimentology. The study of textural parameters of the sediments is of paramount utility in differentiating various depositional environments. The present study is carried out along the Central Kerala coast. Grain-size data have been collected from various sources. Apart from collected data, few representative surface sediment samples from the downstream of important rivers like Pamba, Manimala, Muvattupuzha, Minachil and Periyar which debauches into Vembanad lake have been collected. Surface and suspended sediment samples were also collected from the Vembanad lake area where the rivers join the lake and the adjacent nearshore area. Beach sediments were also collected from the selected locations. The study revealed a systematic change in grain-size pattern from moving from one environment to another. Coastal waters showed significant quantities of suspended sediment which resulted in the formation of mud banks (wave dampening). It is also observed that the accumulation of finer sediments aid in protecting the coast during southwest monsoon season. A socio-economic survey has been conducted in the study area to know the importance and significance of the rare coastal phenomena known as mud banks. Mud banks acts as a treasure house for fishes. Izvleček: Določanje in interpretacija zrnavosti ima bistveno vlogo v hidravliki, geomorfologiji in sedimentologiji. Preučevanje strukturnih značilnosti sedimentov je izjemno pomembno pri razločevanju različnih sedimentacijskih okolij. To študijo so opravili ob obali osrednje Ke-rale (Indija). Podatke o zrnavosti so zbrali iz različnih virov. Razen tega so vzeli nekaj značilnih površinskih vzorcev naplavin iz spodnjega teka pomembnejših rek, ki se izlivajo v jezero Vembanad, kot so Pamba, Manimala, Muvattupuzha, Minachil in Periyar. Površinski in suspendirani sediment so vzorčili pri izlivu rek na območju jezera Vembanad in v okolici. Nadalje so vzorčili tudi obalni sediment v izbranih točkah. Študija je razkrila sistematično spreminjanje zrnavosti na prehodih od enega okolja do drugega. Ugotovili so, da priobalne vode vsebujejo znatne količine suspendiranega sedimenta, kar vodi do nastanka blatnih usedlin ("wave dampening"). Opazili so tudi, da kopičenje zelo drobnozrnatih usedlin pripomore k varovanju obale v obdobjih jugozahodnega monsuna. Na preučevanem območju so opravili tudi družbeno-ekonomsko raziskavo za oceno pomembnosti redkega obalnega pojava, znanega kot blatni nasipi. Blatni nasipi so prava zakladnica za ribe. Key words: grain-size, lake, suspended sediments, mud bank, nearshore, beach Ključne besede: zrnavost, jezero, suspendirane usedline, blatni nasip, priobalno okolje, obala Introduction The various processes involved in the movement of water and its relationship to depositional patterns have attracted the scientists and engineers from various fields. Tides, freshwater outflow, and waves cause complicated water movement which transport, fractionate and modify the properties of particulate matter in coastal regions. These area differ geomorphologically, but have the common feature that suspended mat- ter is carried back and forth, deposited, and eroded many times before it finally settles, either permanently or for a long period. Although the problem of the source of the sediments is often very complex, the process of sorting and grain size selection usually establishes an equilibrium between the bottom, suspended matter and the water. Sediment granulometry have been studied using grain-size statistics. Review of this work has been given by (Folk & Ward, 1957; Folk, 1966; Friedman, 1961, 1967; Veerayya et al. 1975; Rawlison,1984; Purandara, 1993; Pathani,1997; Kumar et al, 2000; Ganesan, 2004; Sanil et al., 2006; Purandara, 2008). Kerala coast is one of the most dynamic and distinctive areas with variety of natural resources and facilities and there has always been a zone of hectic human activity. In the coastal areas, numerous problems such as devastation of natural habits due to erosion, pollution, siltation, over population, salt water intrusion, flooding etc are encountered. This part of the coastal area is known for highest density of population in the world. The present study is an attempt to understand the distribution pattern of sediments in rivers, lake, beach and adjoining shelf. The study has been conducted along the central Kerala coast, between Azhikode in the north to Pur-akkad in the south (south of Alleppey). This stretch of coastal land is important for their unique formation of Mud banks'. Mud banks are natural smooth water anchorages formed at particular locations along the Kerala coast during the southwest monsoon season. It extends outwards up to a distance of 3-4 km from the shore. These are semicircular in shape, with their northern and southern edges defined by two crescen- tic lines of breakers running outwards to the sea. The formation of mud banks play a major role in moulding the socio-economic set up of the coastal people by providing a stable fishing ground during the monsoon season. Mud banks affect the coastal processes by damping the waves in the following ways: • traps the littoral material transported from the updrift side thereby preventing its downcoast movement, • causes refraction of waves on its sides, (iii) protects the beach in particular from erosion. Study area Geologically, the study area is covered by the Tertiary and Recent sediments which rests directly upon the Archaean crystalline complex consisting of khon-dalites, leptynites, charnockites and mica hornblende gneisses. The entire wetland ecosystem comprises of four major rivers that debouches into the Vembanad lake which fringes the coastal tract with an outlet to sea. The sediments brought by the rivers first settles in the lake and then it filters out to the sea through the estuary. The estuarine region presents a stable marine condition for major part of the year. During the monsoon period temporary halo-cline formed with fresh to brackish wa- 0 76-0 * 30' 77-0' 30' Figure 1. Study Area map with sediment sampling locations ter condition exists at the surface, and marine condition continues to prevail at the bottom. The estuarine region is highly productive and the underlying sediments are correspondingly rich in organic matter content. The coastal sedimentary basins of the Kerala form the eastern margin of a bigger basin extending westward over the continental shelf. In the nearshore, gradients are 20 m/km to 80 m/km. The sediments present in the Kerala coastal basin include primarily Miocene sediments overlain by a thin section of Quarternary sediments. Present study has been carried out along the Central Kerala coast (Figure 1) to understand the distribution pattern of sediments. Surficial sediments from the rivers (downstream areas of Pamba, Manimala, Minachil, Muvattupuzha and Periyar) Vemband lake, mud banks and shelf were collected and sedimento-logical analysis were carried out. Methodology Field Investigations Sediment samples were collected from the downstream region of the rivers Pamba, Manimala, Minachil, Muvattupuzha and Periyar (up to 30 km) were collected from the mid-stream channel at an interval of about 2 km to 10 km to the point of origin of the rivers. Sediment samples were collected during pre-monsoon and post-monsoon season. Samples were collected from the beach, mud bank and non-mud bank areas of the continental shelf. Surficial sediments were collected by using van Veen grab and water sampling for suspended sediments and salinity determinations were carried out by using HiTech water bottles at different depths. Laboratory Investigations Textural analysis Textural analysis include both sieve and pipette analysis. Samples collected from the Vembanad lake and mud bank region was subjected to combined sieve and pipette analysis. For pipette analysis known quantities of dried sediments were dispersed overnight in a solution of sodium hexametaphosphate. The silt and clay fractions were separated by sieving the dispersed sediments through 230 pm mesh sieve. The coarse fractions remained in the sieve were dried and analysed. Statistical parameters like mean, standard deviation, skewness and kurtosis were determined by the method suggested by Folk & Ward (1957). Results and discussion The size analysis of the sediments collected from various rivers, namely, Pamba, Minachil, Muvattupuzha and Periyar reveal that the downstream sediments are very fine in size and the upstream sediments are medium to coarse grained. This is clear from the polymodal nature of the sediments in the upstream. The decreasing tendency of grain-size with distance has been attributed to various hydraulic processes associated with the sediment movement which mainly depends on the travel distance. However, the present investigations reveal that the distribution of sediment varies widely, particularly in the downstream regions as shown in figures 2a, 2b & 2c. The variation is more pronounced in the river Pamba where there is a sudden change of grain size at a distance of 22 km from the river mouth. This is attributed to the change in river pattern and also due to the confluence of Puthan ar which supplies comparatively finer sediments to the main stream by depositing the coarser sediments in the meandering course. It can also be explained on the basis of irregular mixing up of the estua-rine and nearshore sediments. The mixing up process is influenced by the tidal currents, waves and coastal currents which push the sediment towards the estuarine region and from there it reaches the river mouth and vice versa. 294 Purandara, v. K., Yenkatesh, B. & chqubey, Y K. 16,00 mean —•—Standard Deviation -Skewness Figure 2a. Plots showing variation of Grain size parameters (Phi mean size, Standard deviation and Skewness) with Distance (upstream to downstream) along the river Pamba 14,00 -4,00 -1-1-1-1-1-1-1-1-1-1-1-1-1-1-1-1-1-1-1-1-1-1-1—1-1-1— UULJLJLJOLJLJLJLJOLJ(_iULJ(_)UOOUUl_)UUUUU r> r_ r^ ^ O i*^ rr rj r* t\ r, ,—I rH » .1 4 mean -^—Standard Deviation ' Skewness Figure 2b. Plot showing variation of Grain size parameters (Phi mean size, Standard deviation and Skewness) with Distance (upstream to downstream) along the river Minachil Figure 2c. Plot showing variation of Grain size parameters (Phi mean size, Standard deviation Grain-size analysis (phi mean size, standard deviation and skewness) of the sediments carried out for all the four rivers in the downstream region are poorly sorted to very poorly sorted. The upstream sediments of Pamba, Minachil and Muvattupuzha show almost a constant value and are poorly sorted. The coarseness and poor sorting of the sediments may be due to its high energy conditions, relative proximity of the source area and the influx of the sediments from the tributaries. The poor sorting of the sediments towards Pamba from Muvattupuzha are noted both in the downstream and upstream region. Generally, river sands display better sorting towards downstream due to progressive sorting based on size. Here, instead, in the downstream area, a complex distribution pattern is observed. This may be due to its sharp decrease in the competency of the transporting agent, intensive mixing of sediments in the river mouth and an increase in depth which is observed during the field investigations. The decrease in velocity |s responsible for the sudden deposition of coarser sediments which mixes with the finer sediments. The skewness of the sediments vary between positive to very negative values both in the upstream and downstream region. In general, most of the downstream sediments show a negative skewness or nearly symmetrical distribution. The negative skewness of sediments could be attributed to the addition of material to the coarser terminal, or subtraction of fines from the normal population. This is evident from the observation that the finer sedi- ments are added through bank erosion and the tidal currents carry finer sediments during the flood tides. The CM pattern (Figure 3) of the rivers of Central Kerala, closely resembles the pattern of river Mississippi. From the diagram, it is clear that the majority of the samples fall in region IV of Passega & Byramjee (1969) showing graded suspension with high turbulence. A small percentage of the samples fall in region I showing rolling with high energy environment. This shows that the river sediments are mainly transported either as graded suspension or bottom suspension with minor rolling and uniform suspension (Purandara, 1990). It is also assumed that particles of graded suspension are lifted by bottom turbulence and the sorting of the deposit is due to settling out of a bottom current (Passega & Byramjee, 1969). It is also important to note that the diameter of the coarsest grain of a graded suspension deposit indicates slow bottom currents. Sediments in the deposits having median values lower than 15 pm never Figure 3. CM pattern diagram of selected rivers of central Kerala show proportionality between C and M. They are too fine to be sorted by bottom currents. Hence, the uniform suspension is shown by fine particles of the downstream region where the competency of the river decreases and depth of water increases. Pre-monsoon and 0.31 to 0.98 during post-monsoon. Sorting of the sediments is poorer during post-monsoon and comparatively better sorted during pre-monsoon season. The kurtosis value shows decrease from pre-monsoon to post-monsoon season. The phi mean size of the Vembanad lake sediments varies between 2.5 and 10.55. The average phi mean is 8.21 in the pre-monsoon and 6.4 for the post-monsoon sediments. The standard deviation varies from 1.39 phi to 4.54 phi (pre-monsoon) and 1.95 phi to 3.85 phi (post monsoon). The skewness varies between 0.38 and 0.48 phi during both the seasons. Lake sediments are platykurtic in nature. The kurtosis value ranges from 0.55 to 0.98 during The CM pattern drawn for the pre-monsoon and post-monsoon sediments of Vembanad lake (Figure 4) show that the segment PM is missing during the pre-monsoon and post-monsoon seasons. In the case of pre-monsoon sediments, it contains QR and RS segments. Cluster of very fine sediments are noted due to its constant mean size and percentile values. In the pre-mon-soon season, majority of the sediments are grouped below the coarsest percen- Figure 4. CM pattern diagram of Vembanad lake sediments (a) pre-monsoon; (b) post-monsoon Figure 5. Scatter plot - Phi mean versus Standard deviation Figure 6. Scatter plot- Phi mean versus Skewness tile of 31 pm and the median less than 3 pm. The total sediments in uniform suspension and graded suspension are less. The plot drawn for post-monsoon sediments indicates that the sediments are transported mostly by uniform suspension and graded suspension. The maximum size of the grains transported is 650 pm in size during pre-monsoon and it is 420 pm during post-monsoon. The textural analysis of the beach sands showed that generally, sediments are finer during May and also immediately after the offset of monsoon. The finer size of the sediments may be due to the action of sediments by waves and currents along the beaches at certain places. The formation of mud bank is also significant in depositing the sediments along the coast. Most of the beach sediments are moderately sorted (Figure 5). The range of standard deviation is from moderately sorted to well sorted. Generally, the better sorting of the sediments could be due to the constant action by waves and currents. The skew-ness value of the pre-and post monsoon sediments varies widely. However, majority of the sands are nearly symmetrical in nature. In general, some of the beach sands are positively skewed. The positive skewness in beach sands as in the case of river sands may be because of the infiltration of fines. The micro-environmental delineation of granulometric characteristics of the beach sediments are attempted. The size varies from coarse to very fine sand (Figure 5, 6). It is observed that beach sands relatively finer during May and immediately after the offset of monsoon. Most of the beach sands are moderately sorted and nearly symmetrical. Sediment movement in a coastal environment indicates that the various transport mechanisms remain active and it tend to retain the sediments as far as possible in the nearshore environment. In fact, very limited quantity of sediments brought by rivers and other geological agents passes to offshore. In the first stage, the sediments are filtered through estuary and escape into the nearshore and are mostly accumulated as suspended matter due to settling, scour lag effect and salinity variation. Only coarser denser materials are transported further offshore. This kind of accumulation of fine sediments in the nearshore region lead to the formation of mud banks. Mud banks are smooth water tracts along the study area formed during southwest monsoon season. This zone is relatively calm due to the dampening of the waves. The sediment characteristics of this region shown that the percentage of clay increase from May to August and there is a considerable decrease after September. The sediment with grain size less than 1 pm exceeds more than 50 %. During the south-west monsoon, the overflowing rivers of central Kerala are the major contributors of the sediments through the lake and estuary. These overloaded sediments brought by rivers as suspension and bed load may be filtered through the estuarine mouth and will be transported to the nearshore zone. The transportation of sediments through such a long distance will bring very finer sediments and may remain in suspension due to lower salinity. Due to high concentration of suspended sediments (100 mg/L to 900 mg/L in the surface layer and 120 mg/L to 3600 mg/L in the bottom waters), waves are unable to reach the coast and are dampened completely. This process is very clear from the results which showed that there is a considerable increase in the concentration of suspended sediments from May to August and then a gradual decrease as observed by (Kurup, 1977; Ramachandran & Mal-lik, 1985; Purandara & Dora, 1991). Furthermore, it explains that the accumulation of sediments take place in the low energy environment as the waves cannot reach the shore. This clearly indicates the gradual decrease of grain-size when transported to the sea through rivers and estuary. The confinement of suspended matter within a certain region, combined with movement by tidal and density currents, has an important selective effects on the sediment distribution on the continental shelf. In many areas distributional patterns are closely related to water movements including that of waves. Deeper portions on the shelf are often sufficiently quiet for mud deposition, but the deposits are coarse since no fine grained suspended matter is available. Conversely, muddy deposits may form in rough water if sufficient fine grained materials are supplied. Conclusions In summary, the movement of sediments in coastal sedimentary environments shows that various transport mechanisms are responsible for holding the material within these regions. The study reveal that the accumulation of fine grained sediments and suspension are mainly due to settling, tidal movements and scour lag effects. The size of the particles mainly depends on local conditions and also on the accumulation process but the retention is usually most effective for fine grained matter. Further, it is important to note that the confinement of suspended matter within a certain region, combined with movement by tidal and density currents, has an important selective effect on the grain-size distribution of the deposit. (Postma, 1967) explained similar condition while dealing with estuarine sedimentation. A socio-economic survey was conducted by contacting the farmers in the region and they expressed the view that the formation of mud banks is a boon to them because, the waters in the region is enriched with nutrients and therefore, fishes come closer to the coast during this particular season. Since, offshore movement is restricted during the monsoon season, the availability of fishes in the nearshore region helps them to fetch their livelihood. However, they also opined that, in the recent years the Vembanad lake is facing threat of pollution due to various industries located in and around the lake. The pollutants entering the lake will finally reach to the open sea and may harm the production fishes due to their pollutant. Therefore, it is essential to take control measures while discharging the industrial wastes to lake. Acknowledgement Authors are highly grateful to Sh. R. D. Singh, Director, National Institute of Hydrology, Roorkee for his encouragement. Authors are also grateful to Department of Marine Sciences, Cochin university of Science and Technology for the assistance rendered during the study. References Folk, R. L., Ward, W. C. (1957): Brazos River Bar: A study in the significance of grain-size parameters. Journal of Sedimentary Petrology, Vol. 27, pp. 3-26. Friedman, G. M. (1961). Distinction between Dune, Beach and River sands from their textural characteristics. Journal of Sedimentary Petrology, Vol. 31, pp. 514-529. friedman, G. M. (1967). Dynamic processes and statistical parameters compared for size frequency distribution of beach and river sands. J. Sediment. Petrol., Vol. 37, pp. 327-354. Ganesan, P. (2004): Delineation of high tide line and seasonal beach profiling at Kalbadevi bay, Maharashtra, central west coast of India. Technical report: NI0/TR-8/2004. Kumar, S. V., Kumar, K. A., Anand, N. M. (2000): Characteristics of waves off Goa, West coast of India. Journal of Coastal Research, V. 16(3), pp. 782-789. Kumar, S. V., Pathak, K. C., Pednekar, P., Raju, N. S. N., Gowthaman, R. (2006): Coastal processes along the Indian Coastline. Current Science, Vol. 91(4), pp. 530-536. Kurup, P. G. (1977): Stduies on Physica aspects of mud banks along the Kerala coast, Mahasagar- Bull. National Institute of Oceanography, 2(3), 25-31. Passega, R., (1957 Texture as characteristic of clastic deposition.Bull. Am. Assoc. Petrol. Geologists, Vol. 41(9), pp. 1952-1984. Passega, R., Byramjee, R. (1969): Grain size image of clastic deposits. Sed-imentology. Vol.13, pp. 233-252. Postma, H. (1967): Sediment transport and sedimentation in estuaries (ed by G. H. Lauff). American Associ- 302 Purandara, V. K., Venkatesh, B. & Choubey, V K. ation for Advancement of Science, pp.158-179. Pathani, R. A. (1997): Significance of grain-size analysis to differentiate microenvironment from Malvan beach, Maharshtra. Journal Geol. Assn. Res. Centre, Vol. 5(1), pp. 20-28. Purandara, B. K., Unnikrishnan, V. P., Gupta, C. S., Dora, Y. L., (1987): Textural and mineralogical studies from Fort-cochin to Chellanam, Kerala. Journal Geological Society of India, Vol. 30, pp. 524-530. Purandara, B. K. (1990): Provenance, Sedimentation and Geochemistry of the modern sediments of mud banks off the central Kerala coast, India. Ph. D. Thesis, Cochin University of Science & Technology. Purandara, B. K., Dora, Y. L. (1991): Textural variations of Narakkal and Saudi Mud banks, west coast of India. Journal of Indian Association of Sedimentologists, Vol. 10, pp. 1-11. Purandara, B. K. (1993): Texture and Mineralogy of Periyar river(southwest coast of India) sediments. IJMS, 22:78-80. Purandara, B. K. (2008): Sediment Observations in Muvattupuzha, Kerala, Southwest India. Proceedings (Abstract volume) National Seminar on Konkan Coast DEED, pp. 74-81. Ramachandran, K. K. & Mallik, T. K. (1985): Mud banks off Kerala Coast- A State of the Art report. State Committee on Science, Technology and Environment, Govt. of Kerala. Rawlison, S. E. (1984): Environments of deposition, Palaeo-currents, and provenance of Tertiary deposits Kachemaka Bay, Kenai Peninsula, Alaska, Sedimentary Geology, 38, pp.421-442. Samsuddin, M., Suchindan, G. K., (1987): Beach erosion and accretion in relation to seasonal longshore current variation in the Northern Kerala coast, India. Journal of Coastal Research, Vol. 3(1), pp. 55-62. Samsuddin, M. (1986): Textural differentiation of the foreshore and breaker zone sediments on the northern Kerala coast, India. Sedimentary Geology, Vol. 46, pp.135-145. Unnikrishnan, V. P. (1987): Texture, Mineralogy and Provenance of the beach sands of south Kerala. Ph. D thesis. Cochin University of Science and Technology (unpublished). Veerayya, M., Varadachari, V. V. R. (1975): Depositional environments of coastal sediments of Ca-langute, Goa. Sedimentary Geology, Vol. 14, pp. 63-74. Integrated remote sensing and GIS approach to groundwater potential assessment in the basement terrain of Ekiti area southwestern Nigeria Povezava daljinskega ugotavljanja in GIS za oceno potenciala podtalnice v kristalinični podlagi območja Ekiti v jugozahodni Nigeriji Abel o. Talabi1, * & Moshood N. Tijani2 'University of Ado-Ekiti, Faculty of Science, Department of Geology, Ado-Ekiti, Nigeria 2University of Ibadan, Faculty of Science, Geology Department, Ibadan, Nigeria *Corresponding author. E-mail: soar_abel@yahoo.com Received: March 15, 2011 Accepted: September 6, 2011 Abstract: Occurrence of groundwater in the Basement Complex terrain of Ekiti area, southwestern Nigeria is controlled by secondary porosities developed through weathering and fracturing of the crystalline bedrocks. Here, the aquifers are characteristically discontinuous (localized) warranting assessment of the ground-water potential of the area to serve as a guide for groundwater exploration. Remote sensing (RS) and Geographical Information System (GIS) have been useful in assessing, monitoring and conserving groundwater occurrence. Hence, this paper presents the integrated approach of RS and GIS to groundwater potential zonation in the study area. Thematic maps of geology, geomor-phology, lineament, slope, drainage and drainage density were prepared and integrated using ArcGIS 9.1 software to produce the groundwater potential map of the study area. The GIS evaluation produced a groundwater potential map in which the study area was categorized into zones; very good, good-moderately good and poor. Furthermore, superimposition of the groundwa- ter yield data from the study area on the groundwater potential map revealed that there are more number of high-yield wells in the favourable zones (very good to good-moderately good) indicated by the GIS approach. This study highlights that the groundwater potential map would apart from its role as exploration guide be useful for the development of sustainable ground-water scheme in the area. Izvleček: Navzočnost podtalnice v stari podlagi območja Ekiti v jugozahodni Nigeriji je odvisna od sekundarne poroznosti, ki je posledica preperelosti in razpokanosti kristaliničnih kamnin. Značilno za vodonosnike v njih je, da so nepovezani (lokalizirani) in je zato mogoče podatke o potencialu podtalnice v njih uporabiti kot vodilo za njeno sledenje. Daljinsko ugotavljanje (RS) in geografski informacijski sistem (GIS) sta uporabni orodji za ocenjevanje, spremljanje in varstvo podtalnice. V članku je opisana povezana uporaba RS in GIS za zoniranje potenciala podtalnice na raziskovanem ozemlju. Izdelane tematske karte geologije, geomorfologije, lineamentov, nagiba reliefa, površinskih vodnih tokov in njihove gostote so združili s programsko opremo ArcGIS 9.1 v karto potenciala podtalnice raziskovanega ozemlja. Na tej karti, izdelani z uporabo GIS, je ozemlje razdeljeno na območja dobrega, dobrega do zmerno dobrega in slabega potenciala. Ob prekritju karte izdatnosti podtalnice na raziskovanem ozemlju s karto njenega potenciala se je dalje izkazalo, da so visoko izdatni vodnjaki številnejši v ugodnih območjih (z zelo dobrim in dobrim-zmerno dobrim potencialom), kakor so bili določeni z metodologijo GIS. Iz raziskave izhaja, da je karto potenciala podtalnice mogoče uporabiti ne le kot vodilo pri sledenju, vendar tudi za trajnostno gospodarjenje s podtalnico na danem ozemlju. Key words: Remote sensing, GIS, groundwater potential zonation, Ekiti area, Basement Complex, thematic maps, high yield wells. Ključne besede: daljinsko ugotavljanje, GIS, zonalnost vodnega potenciala, območje Ekiti, kristalinična podlaga, tematske karte, vodnjaki visoke izdatnosti Introduction Water is an important constituent of all forms of life and is required in sufficient quantity and acceptable quality to meet the ever increasing demand for various domestic, agricultural and industrial processing operations. This requirement is hardly fulfilled because 97.5 % of the world global water is saline existing in the ocean, 69.5 % of the remaining 2.5 % world global water that is fresh is locked up in glaciers/permafrost while 30.1 % and 0.4 % of it represent groundwater and surface/atmospheric water respectively (http://ga.water.usgs. gov/edu/waterdistribution.html). Surface water on the one hand is prone to seasonal fluctuations and contamination through anthropogenic activities while groundwater on the other hand is more in quantity, readily available as it exists in virtually all geologic formations and is naturally protected from direct contamination by surface anthropogenic activities. In the basement terrain of Ekiti area, south western Nigeria, availability of surface water is seasonal; during the relatively dry period of November to February each year, shallow groundwater in form of hand-dug wells and boreholes remain the only source of water supply as most streams and rivers are dried up. However, the occurrence and movement of groundwater in this crystalline bedrock setting depend on the degree of weathering and extent of fracturing of the rocks (Oloruniwo & Ülorunfemi, 1987). The highlighted scenario warrants a detailed investigation of the groundwater potential characteristics of the area so that an exploration guide as well as sustainable groundwater management strategy can be developed. Groundwater prospect in an area is controlled by many factors such as geology, geomorphology, drainage, slope, depth of weathering, presence of fractures, surface water bodies, canals and irrigated fields amongst others (Jain, 1998). Slope for example is one of the factors that control the rate of infiltration of rainwater into the subsurface and could therefore be used as an index of groundwater potential evaluation. In the gentle slope area the runoff is slow allowing more time for rainwater to percolate, whereas high slope area facilitate high runoff allowing less residence time for rainwater hence comparatively less infiltration. In one way or the other, each of the listed factors contributes to groundwater occurrence. These factors can be interpreted or analyzed with GIS using RS data. Burrough (1986) defined a GIS ''as a powerful set of tools for collecting, storing, retrieving at will, transforming and displaying spatial data from the real world for a particular set of purpose''. GIS thus enables a wide range of map analysis operations to be undertaken in support of groundwater potential zonation of an area. Several conventional methods exist for the exploration and preparation of groundwater potential map of an area. These methods include; geological, geophysical and hydrogeological. However, RS amongst these methods is considered to be more favourable as it is less expensive and applicable even in inaccessible areas. It is a rapid and cost effective tool in producing valuable data in geology and geomorphology. In classifying groundwater potential zones, visual integration of data generated from remote sensing is feasible but cumbersome. However, with the advent of GIS technologies, the mapping of groundwater potential zones within each geological unit has become easy. Gustafsson (1993) used GIS for the analysis of lineament data derived from SPOT imagery for groundwater potential mapping in a semi-arid area in south eastern Botswana. Also, Jain (1998) demonstrated the use of hydro geomor-phological map by using Indian Remote Sensing Satellite Linear Imaging Self-Scanning II geocoded data on 1 : 50 000 scale along with the topographic maps to indicate the groundwater potential zones in qualitative terms (i.e., good to very good, moderate to good and poor). Previous research efforts in the study area have been directed at locating and developing potable groundwater using geophysical and geological techniques. Such studies, including the work of Re-boucas & Cavalcante (1989), classified the basement terrains aquifers into three; the weathered basement aquifer, the basement detrital overburden aquifer and the fractured rock aquifer. Also, Oyinloye & Ademilua (2005) examined the nature of aquifer in the crystalline Basement rocks of Ado-Ekiti, Igede-Ekiti and Igbara-odo areas, southwestern Nigeria and concluded that aquifers occurred both in the regolith and fractured basement rocks of the area. The highlighted previous ground-water investigations concentrated on identifying fracture zones and areas with thick overburden employing geophysical and geological techniques as pathfinders to groundwater availabity. However, basic knowledge of ground-water location, its potential in terms of quantity and availability can provide basis for more rational planning. Therefore, the present study assessed the groundwater potentials of the study area using integrated RS and GIS approach. Study area The study area (Figure 1) lies between latitudes 7015'-805' N and longitudes 4044'-5045' E and fall within the Basement Complex setting of southwestern Nigeria. It covers area extent of about 6 353 km2. The study area enjoys tropical climate with two distinct seasons; rainy and dry seasons covering (April to October) and (November to March) respectively. The annual temperature range is between 25 oC and 30 oC while the annual rainfall is 1 500 mm. The study area is drained by many streams and rivers most of which dry off at the pick of the dry season usually between January and February causing supply of water for domestic and agricultural purposes to depend heavily on groundwater system. Groundwater supply in the area is mainly from shallow hand dug wells and limited boreholes. Two major aquiferous units (weathered and fractured layers) have been identified as source of supply to the wells and boreholes (Ademilua & Olorunfemi, 2000). The topography is generally undulating with most area lying above 250 m above sea level. The landscape is characterized by old plains, broken steep sided outcrops of dome shaped Inselbergs that may occur singularly or in ridges. Such outcrops exist mainly in form of rugged hills at Ado-Ekiti (central part of study area) and Ikere-Ekiti in the southern part of the study area. Geology of study area Geologically, the study area is underlain by Precambrian crystalline rocks mostly of igneous-metamorphic origin with iso-topic ages greater than 300 Ma to 450 Ma (Matheis, 1987). Prominent rock units include porphyritic granite, fine-medium grained granite, granite gneiss, schist/quartz schist, migmatites and char-nockite. The gneisses and migmatite are intimately associated such that they are hardly distinguishable on the field. The gneisses and the migmatite rock units are ubiquitous and form the bulk of the rocks in the study area. In some places, these rocks display characteristic feature of banding of varying width (Figure 2). Migmatite is a mixed rock composed of a gneissic host and intruded by the granitic and pegmatitic rocks. It covers over 50 % of the whole study area (Figure 3). Figure 2. Migmatite rock outcrop along a road cut (Iworoko-Ifaki) in the study area. 8W00 00"N 7°45'00 00"N 7s 30*00 00"N Legend I I Se: Basic schist & calc-gneiss I I OGd: Biotite & biotite-hornblende granudiorite I | ch: Chamockite □ OGp: Coarse porpliyritic biotite& biotite-homblende granite □ e: Epidiorite I I OGf: Fine-medium grained biotite & biotite-muscovite granite I I OGe: Medium-coarse grained biotite granite I—| Su: Pelitic schist, undifferentiated; icluding layered granite-gneiss in the southeast CU Q: Quartzite □ Eq: Quartz-schist & quartzite I lOGu: Undifferentiatrd older granite; granitized gneiss with porphyroblastic gneiss & some migmatite □ M: Variably migmatized. undifferentiated biotite & _biotite-h omblende-gneis s with intercalated ampliibolite_ Figure 3. Geology Map of the Study Area. The quartzite occurs as relatively minor concordant layers within the gneiss-migmatite units. On account of high content of late crystallised mineral and consequently resistance to weathering/ erosion, the quartzite tends to stand out as prominent hills and ridges within the study area. The granitic units occur as intrusive bodies of various dimensions in the pre-existing basement rocks i.e. the gneiss-migmatite units and the schist/ quartz schist bedrock. The granitic units consisting of a suite of porphy-ritic and non-porphyritic granite rocks as well as medium to coarse grained textural varieties are widely distributed in the study area especially the central and south- eastern part. One striking feature of the granitic unit is the occurrence as picturesque inselbergs (prominent hills) rising sharply above their surrounding plains. In some places, charnockite, a bluish-green rock, is found associated with the granitic units. The charnockite features prominently at Ikere and Ado towns in the study area. Methodology System integration, which involves the integration of computer software (AutoCAD 2000, Cad overlay R.14 and ArcGIS 9.1) and hardware, im- agery processing, information extraction and analysis formed the basic methodology of this work. System integration involves the use of computer hardware (equipment), software, data and personnel as well as other accessories such as digitizer and scanner at building capable expert system to extract geo-referenced information from the acquired satellite imagery. The processing flow chart of the methodology used in this study is presented in Figure 4. The first step in system integration is to identify data need, conceptualize how it would be captured and display in a GIS platform. The data required and used for this study were identified and their sources verified. The data sources include the Geological Survey Department of Nigeria, Abuja, National Institute of Figure 4. GIS in groundwater potential assessment Remote sensing, Bukuru, Jos, Nigeria and Federal Ministry of Solid Mineral Resources, Abuja, Nigeria. Data acquisition, Conversion and Information extraction and converted to GIS supported Ge-oTIFFs raster format. These were subsequently exported into ArcGIS 9.1 software for further processing which include editing of both spatial and tabular data on a continuous and interactive basis. The relevant data acquired which include existing analogue maps, charts, plans and records are presented in Table 1. Consequently, assembling and detail data structuring were also carried out before the compilation and digital conversion for logical data structure. The data as highlighted in Table 1 conformed to the National Geospatial Data Infrastructure (NGDI) - an initiative for co-sharing information in a Geoinformation-based economy. Subsequently, the analogue spatial and attribute data acquired were captured, rasterized, georeferenced and manipulated in CAD software (CAD Overlay R14) As part of the follow up activities, the information required were extracted using supervised, unsupervised and ground truthing approach plus existing data and information. To classify the image into unique characters comprising of pixels with similar spectral characteristics, unique clusters which represent one or more features according to some statistically determined criteria, were also employed. Subsequently, fieldwork was embarked upon to validate GIS processed information. Where outcrops were not visible, the slope and drainage were used to validate the results. Table 1. Relevant spatial data, information extracted and data sources for the research Spatial Data Attribute Data Source Land sat Imagery Digital Elevation Modeling/ Terrain/Geology National Institute of Remote Sensing, Bukuru, Jos, Nigeria NigerSat-1 Imagery Digital Elevation Modeling/ Terrain/Drainage National Institute of Remote Sensing, Bukuru, Jos, Nigeria Mineral Maps of Nigeria Metadata Geological Survey Department of Nigeria, Abuja, Nigeria Aero Magnetic Map of Southwestern Nigeria Lineation Ministry of Solid Mineral Resources, Abuja, Nigeria Integration of data Consequently, each of the thematic maps in raster format was assigned suitable weightage factor (Table 2) based on previous works of researchers such as Srinivasa Rao & Jugran (2003), Krishnamurthy et al. (1996), Saraf & Choudhary (1998) and Par-asad et al. (2008). Each of the thematic maps such as geology, geomorphology, drainage density, lineament and slope provides certain clue in respect of the occurrence of groundwater. To unify these information, there is the need for integration of the data with appropriate factor. Though, it is possible to superimpose the information manually, however, it is time consuming and may be proned to errors. Therefore, the information were integrated through the application of GIS. Various thematic maps were reclassified on the basis Table 2. Weightage assigned to various thematic maps based on prospective contribution of input factors to groundwater occurrence (Srinivasa Rao & Jugran, 2003). Feature Classification Weightage Geology Migmatites Charnockite Granite gneiss Granite Quartzite/quartzite schist 1 1 2 2 3 Geomorphology Hilly area Lowland area 1 3 Extreme steep slope (76.30) 1 Very steep slope (35.20) 1 Steep slope (30.810) 1 Slope Moderate-steep slope (22.130) 1 Moderate slope (9.210) 1 Gentle slope (8.40) 2 Very gentle slope (4.570) 3 Lowland/Nearly Level (0.250) 4 Lineaments Present 3 Absent 1 Low density/coarse texture 4 Drainage density Medium density/medium texture High density/fine texture 2 1 Very high density/very fine texture 1 Drainage density Low density/coarse texture Medium density/medium texture High density/fine texture Very high density/very fine texture 4 2 1 1 of weightage assigned and processed using the ''Raster Calculator'' function of Spatial Analysist Extension of ArcGIS 9.1 for integration.The procedure adopt simple arithmetical model to integrate the various thematic maps by averaging of the weightage to produce a final groundwater potential map of the study area. Finally, to validate or authenticate the evaluation method, existing borehole yield data were cor- related with the various groundwater potential zones in the study area. Results and discussion Results of the integrated approach of RS and GIS to delineate groundwater potential zones in hard rock terrain of Ekiti area are presented in form of thematic maps (Figures 3, 5 & 7-10). Figure 5. Lineament map of the study area. The final groundwater potential map in which the study area were zoned into three categories (Very good, good-moderately good & poor) is represented in Figure 11. Furthermore, Figure 12 represents a typical weathered overburden soil in charnockite bed rock terrain at Ikere in the southern partof the study area while graphical evaluation of the highlighted zones with well depths and yield data are presented in Figures 13 and 14 respectively. Lineaments The study area is criss-crossed with lineaments characterized by dominant NW-SE and NE-SW directions while a few numbers of the lineaments also trend E-W (Figure 5) this strongly agree with result of the directional analysis presented in rose diagram (Figure 6). Lineaments cut across the entire bedrock units of the whole area. Futher evaluation revealed that migmatite has low lineament density with 0.02 km-2 com- Length Frequency Figure 6. Rose Diagram pare to quartzite, granite and charnock-ite with density range from 0.05 km-2 to 0.13 km-2. These lineament density revealed existence of more lineaments on the granitic /charnockitic rocks which might be as a result of transpressive forces exhibited during intrusion of the rocks into the parent migmatite/meta-sedimentary rocks. However, the linea- ments in the low lying part of the study area are of significant interest with respect to groundwater occurrence because the lineaments on migmatite are mostly on the hilly and high slope areas with little or no overburden which are regarded as less significant due to possible high runoff rather than favouring vertical groudwater infiltration. Figure 7. Drainage Map of the Study Area Drainage Usually, drainage patterns are said to be reflections of surface and subsurface formations while drainage density is proportional to surface run-off due to the fact that the more the drainage den- sity, the higher the runoff. (Parasad et al, 2008). Hence, the drainage density characterizes the runoff in an area as the volume of relative water that was unable to penetrate into the subsurface. In addition, drainage density do give >^)0E 5°i0E 5°20E 5°30E 5;-l0E Figure 8. Drainage Density Map of the Study Area indications of closing or otherwise of stream/river channels which inturn will depend on the nature and degree of weathering of the surface and subsurface lithologic units. Low drainage density therefore enhances the chance of recharge and contributes positively to groundwater availability if other groundwater occurrence conditions are favourable. In this study thematic map extracted from the topographic map shows dendritic pattern (Figure 7) while the drainage density map presented in Figure 8 reflects the infiltration characteristics with high drainage density indicating low-infiltration and the low drainage density high infiltration respectively. Most of the drainage originates from the quartzite ridge and granitic/charnockitic hills with dense drainage pattern. The lowland part of the study area that are characterized mainly by diverse rock units (por-phyritic granite, fine-medium grained granite, granite gneiss and migmatite) presents low density an indication of favourable condition for vertical infiltration of runoff from surrounding hills and thus enhancing grounwater oc-currence.This observation signify that groundwater occurrence in the lowland part of the study area is not only controlled by rock formations but other factors like topography and weathering as weathering products from the surrounding hills pile up to form overburden thickness aquifer while during igneous rocks intrusion fractures fa- vourable for vertical infiltration were developed and thus additionally support groundwater occurrence. Slope/Geomorphology Results of slope and geomorphology thematic maps produced from integrated RS and GIS as presented in Figures 9 and 10 respectively revealed eight slope categories ranging from extreme slope to lowland and two main geo-morphic units; hilly area and lowland area. Geomorphology is a reflection of the various landform and structural features of an area. Such landform and structural features are useful in categorizing groundwater occurrence. Generally, field observation revealed that the lowland areas are covered by thick weathered material representing alluvium matrials from the hilly areas (Figure 12). The weathered overburden revealed three principal horizons designated A, B and C. The "A" horizon is dark brown to redish lateritised soil, littered with some plant residues which implies organic soil form. The "B" horizon is subdivided into three distinct sub-units but all the three units are generally finer in texture compared to "A" horizon and of a lighter brown. The first two subunits of "B" horizon constitute the vadoze zone where active leaching and vertical of infiltration water occurs.The third sub-unit of the horizon constitute the phreatic zone representing the aquiferous layer.Soil horizon "C" is grey to white in col- our due mainly to absence or substantial reduction of weathering activities and represents fresh parent rock which may or may not be fractured. However, when the parent rock is fractured, it compliments the overburden thickness in terms of groundwater occurrence. The hilly areas comprise of gentle sloping surfaces with transported sediments lying between hills and plains. Additionally, the hilly areas are also characterized by presence of residual hills occuppying over 64 % of the study area (Figure 11). The ground- water prospect in this zone is poor. for rainwater infitration, whereas ex- Further evaluation with respect to the tremly steep slope area facilitate high slope characteristics of the study area runoff allowing less residence time for revealed that gentle slope are indica- rainwater hence, comparatively less in- tive of slow runoff allowing more time filtration. Extreme slope to moderately 5WE 5°10E 5°20E 5°J0E Figure 10. Geomorphology Map of the Study Area steep slope occupy over 50 % of the Synthesis and Groundwater poten- study area and groundwater prospect tial map of the study area in this area is poor in agreement with The integration of the thematic maps the earlier observation infereed from resulted in the production of ground- geomorphologic thematic map. water potential map of the study area 5 WE 5°10E 5*2 0E 5°30E 5S40E Â& N y^r L^JCS v. es /v 1 , J ,, , I S rSr \ W ft i A 'N / \ / * r^jH yL^J/fi A ' v jr Ax 1 V J1 ÏÏ- f A / , sS\ 1 .J — iiT V r ' UjL J ■ * \7" * / p Ï V L.jl i T ID Nu 1 Groundwater Potential Classification & Area of Cov erage Leaeiid Verv eood 1JZ41.64km Ekiti settlement Good ^lo.ôotnr Fault Moderated good 358JSkm* Road Poor 3,759S3km: Lineament S^OON 7°50N r40N 7°20N Figure 11. Groundwater Potential Map of the Study Area (Figure 11). As shown in the map, the area that has very good potential for groundwater is situated in the south eastern part covering about 21.15 % of the study area. The good to moderately good potential area covers only 6.12 % while the greatest portion of the area about 64.04 % belongs to poor groundwater potential zone. The poor groundwater potential zone on the one hand is characterized majorly by migmatite and migmatite gneiss with quartzite/ quartz-schist and charnockite consti- tuting the minority rock units while on the other hand, the very good and good to moderately good groundwater potential zones are covered majorly by granitic and charnockitic rocks with migmatite and quartzite constituting minority rock units. The various rock units cut across the different groundwater potential zones. However, the migmatite rocks that cover greater parts of poor groundwater potential zone are less fractured and in most cases covered with shallow overburden SOIL HORIZONS A -Top soil Vadose zoneh • - -Light brownish silty soil B - Greyish clay soil -SaproHte Phreatic zone- * - Zone of fractured and/or unfractured parent rock cigSi; ; 3§i£ I C - Parent rock Figure 12. Showing weathered overburden soil in a typical charnockite bed rock terrain at Ikere Well depth (m) ■ V. Good ■ Good-tnoderately good ■ Poor Figure 13. Frequency distribution of well depth with respect to groundwater potential zones. Figure 14. Frequency distribution of well yield with respect to groundwater potential zones thickness when compared to the granitic and charnockitic rocks that form the major rock units of the very good and good to moderately good potential zones. Obviously, weathering, thickness of overburden mateerial as well as fracture system in the various ground-water potential zones are major factors controlling groundwater occurrence in the study area and these factors are more favoured in the very good and good to moderately good groundwater potential zones compared to the poor groundwater potential zones. Result validation In order to validate the classification of Lagos, Nigeria were collected and evaluated. The data revealed that boreholes in the study area can be categorized into high (>100 m3/d), moderate (50100 m3/d) and low yield (<50 m3/d). In additipon, the depth range varies from 21.3 m to 92 m while the yield range between 8.64 m3/d to 354.24 m3/d (Table 3). The data also revealed that 46 % of wells within granitic terrain are of high yield (>100 m3/d) while 21 % of well in both migmatite and charnock-itic also exhibited high yield compared to 12 % of the quartzite terrain. These are characteristics of very good to good groundwater potential zones which is consistent with the trend of the GIS- the study area into different groundwa- based potential zones. However, mig- ter potential zones (i.e. very good, good matite, charnockite, granite and quartz- to moderately good and poor), bohole ite bedrocks are characterized by 63 %, yield data of existing wells from Be- 16 %, 13 % and 3 % of the low yield nin/Owena River Basin Development (<50 m3/d) wells respectively which Authority (BRBDA), Ikere-Ekiti, and are typical of poor groundwater poten- Federal Ministry of Water Resources, tial zones in the study area. Table 3. Summary of Borehole completion records in Ekiti Basement area S/NO Location BHD/m SWL/m Yield (m3/d) GWZ Bedrock 1 Ogbesse 45 4.1 86.4 Very good migmatite 2 Ikere (Ogoga palace) 53 8.9 103.68 Very good granite 3 Ikere(Benin/Owena office) 40 3.9 103.68 Very good charnockite 4 Emure(Owode) 35 1 103.68 Very good granite gneiss 5 Emure(Awopegba house) 30 5.7 69.12 Very good granite gneiss 6 Ise(oraye) 45 4.8 103.68 Very good migmatite 7 Orun 40 4.5 69.12 Very good migmatite 8 Ado(Bolorunduro) 36 3.9 86.4 Very good charnockite 9 Ado(Italaoro) 10 Igede 11 Temidire 12 Ilumoba 13 Ago-Aduloju 14 Bolorunduro 15 Ado-Com. School 16 Aro Camp-Ikere 17 ESGSC-Ikere 18 Ado grammar school 29 Ogbese 20 Itawure 21 Ikoro 22 Egbewa 23 Owode 24 Ilupo 25 Imesi 26 Ijero-Ekiti 27 Aramoko-Ekiti 28 Ogotun-Ekiti 29 Iloro-Temidire 30 Soso 31 Itawure 32 Ado-Ekiti 33 Ifaki 34 Ijero(palace) 35 Ipoti 36 Epe 37 Are 38 Iworoko 39 Ipoti 40 Erinjiyan 41 Igede-Ekiti 30 3.3 86.4 35 8 69.12 43.8 6 131.33 45 7 354.24 29.6 2.7 129.6 31.3 3.2 30.24 40 6.8 132.19 42 3.2 54.43 68 18 203.04 51.4 7.2 25.92 48.6 1.5 283.39 37 2 103.68 60 9 112.32 50 21 103.68 43 2.1 175.39 26 4 103.68 46.6 8 114.05 80 8.1 304.99 48 14.61 160.70 92 2 129.6 38 9.1 95.04 31.4 8.7 98.49 21.3 5.7 95.04 74 2.7 191.81 40 18 69.12 50 6 69.12 50 1.7 53.57 31 12 69.12 40 4.6 34.56 42 5 43.2 50 11.8 51.84 40 10 43.2 72 1.3 114.91 Very good granite Very good granite Very good granite Very good migmatite very good chamockite very good chamockite Very good granite Very good chamockite Very good chamockite Very good granite Very good migmatite Good quartzite Good migmatite Good migmatite Good granite gneiss Good granite gneiss Good quartz-schist Good. quartz-schist Good granite gneiss Good granite Good granite Good granite Good quartzite Good granite Poor migmatite Poor quartz-schist Poor migmatite Poor migmatite Poor migmatite Poor migmatite Poor migmatite Poor quartzite Poor granite 42 Orin farm settlement 60 12.4 8.64 poor charnockite 43 Aba Igbira 37.8 13.9 17.28 poor migmatite 44 MGHS Ifaki 59 1 86.4 poor migmatite 45 Ofale community 50 11 11.23 poor migmatite 46 Ipao CHC 25.5 2.9 21.6 poor migmatite 47 Eda-Ile 54.7 12.3 31.10 poor migmatite 48 Ilasa 46.6 6.2 27.65 poor migmatite 49 Kajola 30 7.2 17.28 poor migmatite 50 Ipole Iloro 43.5 9.2 11.23 poor migmatite 51 Ipoti-Ekiti 72 13.97 95.90 poor granite 52 Igede-Ekiti 72 1.33 114.91 Poor granite 53 Otun-Ekiti 72 3.89 102.81 poor migmatite 54 Ilawe-Ekiti 89 NN 86.4 poor granite 55 Usi-Ekiti 80 10.63 64.8 poor charnockite 56 Iyin-Ekiti 72 9.15 26.78 poor granite 57 Ilogbo-Ekiti 70 4.85 44.06 poor migmatite 58 Iworoko-Ekiti 78 3.5 120.09 poor migmatite 59 Ire-Ekiti 74 12.8 28.512 poor migmatite 60 Ijan-Ekiti 70 1.9 40.61 poor charnockite 61 Igogo-Ekiti 46 1.33 40.61 poor migmatite 62 Usi-Ekiti 80 10.63 64.8 poor migmatite 63 Ajebandele 41.5 3 17.28 poor migmatite 64 Ikogosi 42 14.4 103.68 poor quarzite 65 Irare Fulani 46.1 NN 36.29 poor migmatite 66 Irare community 48.4 6.1 8.64 poor migmatite 67 Ogunnire School 29 8.5 8.64 poor charnockite 68 Obalatan 50.6 4.5 8.64 poor charnockite 69 EKSC Ayede 23.4 2.1 21.6 poor migmatite Source: Federal Ministry of Water Resources, Lagos, Nigeria and Benin/Owena River Basin Development Authority, Ikere- Ekiti, Nigeria NN: Not known BHD: Borehole depth SWL: Static water level GWZ: Groundwater zones Further evaluations revealed low correlation (r = 0.37) between well yield and well depth suggesting that well yield depends on aquifer characteristics such as porosity, permeability and fracture system rather than depth. This is consistent with the frequency distribution of well depth with respect to groundwater potential zones (Figure 13) revealed that well yield is not controlled by depth due to the fact that wells with depth >40 m are more represented in the poor groundwater potential zone. This is a clear indication of the localized nature of weathered basement aquifer in the study area. Nonetheless, the frequency diagram of well yield distribution (Figures 14) support the early observation because wells with low yield (<50 m3/d) are predominant in the poor groundwa-ter potential zone and minimal in the good to moderately good groundwater potential zone. Thus the frequency of occurrence of high yielding wells decreases from very good groundwater potential zone to poor groundwater potential zone in agreement with the GIS evaluation of the groundwater potential of the study area. Further evidence to support this observation is the fact that the shallowest well with depth of 21.3 m located on quartzite has a yield of 95.04 m3/d well with depth of 89.0 m on a granite bedrock has a yield of 86.4 m3/d. This scenario is an indication of the tendency of the unqualified local driller to drill deeper in the hard granitic and migma-tite bedrocks with the hope of intersecting fractures at deeper depth. The is an indication of lack of adequate knowledge of the hydrogeological settings by these local unqualified drillers as the assumption is not always applicable in such Basement bedrock setting hence the need to use professionally trained drillers in the drilling exercise not only reduce cost but also to ensure sustainable groundwater exploitation. Summary and conclusions This study provides an integrated RS/ GIS approach to groundwater potential zonation in Ekiti Basement terrain to serve as a guide for groundwater exploration and development in the study area. As part of the study approach, thematic maps were prepared and susequently integrated using Arc GIS 9.1 software to produce groundwater potential map of the study area. The groundwater potential assessment revealed; 1) That the very good groundwater potential zones are located mainly in the south-eastern part of the study area with an area extent of 1 241.64 km2 representing 21.15 % coverage. Also, the good to moderately good groundwater potential zones are concentrated in the north- eastern and south-western parts of the study area. These zones have an area extent of 868.97 km2 representing 6.12 % coverage. However, the poor groundwater potential zone with an area extent of 3 759.83 km2 represents 64.04 % coverage and is variably located in the remaining portions of the study area. 2) That the very good potential groundwater zone is undelain mostltly by granitic/ charnockitic rocks while the good to moderately good groundwater potential zone is covered by quartzite/quartz-schist, granite and charnockitic rocks. The poor groundwater potential zone, however, are underlain by predominantly by migmatite/ migmatite gneiss bedrock with few charnock-ite and granitic rock units. 3) That fractures on the migmatite bedrocks are poorly developed with thin overburden thickness accounting for the poor groundwater occurrence in this terrain. However, the relatively moderate to thick weathered overburden units characterized the quartzite and granitic bedrocks where greater proportion of high yield (>100 m3/d) are located. 4) That yield is not controlled by well depth as wells with depth >40 m are more represented in the poor groundwater potential zone compared to very good and good to moderately good groundwater potential zones. This is a clear indi- cation of the localized nature of weathered basement aquifer in the study area. 5) That superimposition of existing groundwater yield data on the deciphered groundwater potential zones revealed more frequent occurrence of high to medium yield wells in the favourable groundwater potential zones which support the result of integrated GIS thematic maps. In summary the overall asssessment as presented in this study highlight that mapping of groundwater potential using integrated RS/GIS approach could be an effective means of charcateriza-tion of groundwater potential zones as well as serving as a usuful tool and guide in groundwaer exploration and development in the study area. However, further geophysical investigation to determine the aquifer characteristics and the overburden thickness of various groundwater potential zones highlighted is recommended to compliment the present study. References Ademilua, O. L. & Olorunfemi, M. O. (2000): Geoelectric/Geology estimation of the groundwater potential of the Basement Complex area of Ekiti and Ondo States, Nigeria. Journal of Techno science. Vol. 4, pp. 4-20. Burrough, P. A. (1986): Principles of Geographical Information Systems for Land Resource aassessment. Clarendon Press, Oxford, U. K. Gustafsson, P. (1993): High Resolution Satellite Data and GIS as a Tool for Assessment of the Groundwater Potential of a Semi-Arid Area. Proceedings of the Ninth Thematic Conference on Geologic Remote sensing. Vol. 1, pp. 609-619. Gustafsson, P. (1994): Spot satellite data for exploration of fractured aquifers in a semi-arid area in south eastern Botswana. Applied Hydrogeology J. Vol. 2, pp. 9-18. Jain, P. K. (1998): Remote sensing techniques to locate ground water potential zones in upper Urmil River basin, district Chatarpur-central India. J Ind Soc Remote Sens. Vol. 26, No. 3, pp. 135-47. Krishnamurthy, J. N., Venkatesa, K., Jayaraman, V. & Manivel, M. (1996): An approach to demarcate ground water potential zones through remote sensing and geographical information system. Int J Remote Sens. Vol. 17, pp. 1867-1884. Matheis, G. (1987): Nigeria Rare Metal Pegmatites and their lithologic framework. Geol. Journ. Vol. 22, pp. 271291. Oloruniwo, M. A. & Olorunfemi, M. O. (1987): Geophysical i n v e s - tigation for groundwater in Precam-brian terrains: a case study from Ikare. Southwestern Nigeria. Journal of African Earth Sciences. Vol. 6, No. 6, pp.787-796. Oyinloye, A. O. & Ademilua, O. L. (2005): The nature of aquifer in the crystalline basement rocks of Ado-Ekiti, Igede-Ekiti and Igbara-Odo areas, southwest- ern Nigeria. Pak. J. sci. Ind. Res. Vol. 48, No. 3, pp. 154-161. Prasad, R. K., Mondal, N. C., Banerjee, Pallavi, Nandakumar, M. V. & Rao, N. Subba (2006): Groundwater potential index in a crystalline terrain using remote sensing data. Environmental Geology. Vol. 50, pp. 1067-1076. Prasad, R. K., Mondal, N. C., Banerjee, Pallavi, Nandakumar, M. V. & Singh, V. S. (2008): Deciphering potential groundwater zone in hard rock through the application of GIS. Environ. Geol. Vol. 55, pp. 467-475. Reboucas, A. C. & Cavalcante, I. N. (1989). Hydrogeology of crystalline rocks in Brazil. In groundwater exploration and development in crystalline basement aquifers. (Proceedings, Zimbabwe, 15-24 June, 1987, vol.1 sessions 1-5), Commonwealth Science Council, Pall Mall, London: 103-126. Saraf, A. & Choudhary, P. R. (1998): Integrated remote sensing and GIS for ground water exploration and identification of artificial recharge site. Int J Remotes sense. Vol. 19, pp.18251841. Singh, V. S. (2008): Deciphering potential groundwater zone in hard rock through the application of GIS. Environ Geol. Vol. 55, pp. 467-475. Srinivasa, Rao Y. & Jugran, K. D. (2003): Delineation of groundwater potential zones and zones of groundwater quality suitable for domestic purposes using remote sensing and GIS Hydrogeol. Sci. J. Vol. 48, pp. 821-833. USGS - General Interest Publication "Groundwater" - retrieved from http://pubs.usgs.gov/edu/waterdistri-bution.html. Influence of the heat treatment and extrusion process on the mechanical and microstructural properties of the AISi1MgMn Alloy Vpliv toplotne obdelave in postopka iztiskanja na mehanske in mikrostrukturne lastnosti zlitine AISi1MgMn Matej Steinacher1, Vukašin Dragojevic2 & Anton Smolej1 University of Ljubljana, Faculty of Natural Science and Engineering, Department for Materials and Metallurgy, Aškerčeva 12, Ljubljana, Slovenia 2Impol, Aluminium Industry, Slovenska Bistrica, Slovenia corresponding author. E-mail: matej.steinacher@omm.ntf.uni-lj.si Received: August 17, 2011 Accepted: November 2, 2011 Abstract: The paper describes the influence of homogenization temperatures (480 °C/5 h and 560 °C/6 h), methods of cooling rate after homogenization annealing and various extrusion processes (conventional extrusion K, press-quenching PQ, billet quenching BQ) upon the microstructural and mechanical properties of AlSilMgMn (AA6082) alloy at industrial producing conditions. The mechanical properties of extruded rods from homogenized billets at 560 °C/6 h are higher after the extrusion processes PQ and BQ than the mechanical properties of the rods from homogenized billets at lower temperature. The rods, produced by process K, have higher tensile stress and yield stress in comparison to processes PQ and BQ. The reason is the distribution of Mg2Si phase during the homogenization annealing and subsequent BQ and PQ treatment of the alloy. Povzetek: Članek opisuje vpliv homogenizacijskega žarenja (480 °C/5 h in 560 °C/6 h), način ohlajanja po homogenizacijskem žarenju in različne postopke iztiskanja (navadno iztiskanje K, gašenje na iztiskalnici PQ in gašenje okroglic BQ) na mikrostrukturne in mehanske lastnosti zlitine AlSilMgMn (AA6082), ki je bila izdelana in predelana v industrijskih razmerah. Mehanske lastnosti palic iz drogov, homoge-niziranih pri 560 °C/6 h in iztiskanih po postopkih PQ in BQ, so viš- Preliminary notes je kot mehanske lastnosti palic iz drogov, homogeniziranih pri nižji temperaturi. Palice, ki so bile izdelane po tehnologiji K, imajo višje mehanske lastnosti v primerjavi s postopkoma PQ in BQ. Vzrok je porazdelitev faze Mg2Si med homogenizacijskim žarenjem in nadaljnjo BQ- in PQ-obdelavo zlitine. Key words: AISi1MgMn alloy, homogenization, extrusion Ključne besede: zlitina AlSi1MgMn, homogenizacija, iztiskanje Introduction Investigated AlSilMgMn alloy belongs to the AA6xxx (AlMgSi) series of aluminium alloys, where magnesium and silicon are the principal alloying elements. The commercial alloys of this type contain the mass fractions 0.5 % to 1.5 % of Si and 0.5 % to 1.5 % of Mg and are used in great quantities and they are universal aluminium alloys which can be extruded into sections, rods and tubes. Their characteristics are high workability, strength properties, corrosion resistance and machinability. Their mechanical and technological properties depend on the chemical composition and heat treatment of castings i. e. cast blanks and extruded pieces.[1, 2] Heat treatment of castings consists of the homogenization annealing where principal factors are temperature and time of annealing, and the cooling rate of material to the ambient temperature. The way of cooling influences the precipitation of those alloying elements which are in solid solution during the homogenization annealing. The size and the distribution of secondary precipitates influence the stress required for deformation, extrusion rate, surface quality, and mechanical properties of extruded pieces. Optimal properties of semiproducts depend also on the reheating of homogenized castings to the temperature of the extrusion process.[2] The influence of the cooling after the homogenization on the extrusion rate was widely investigated, but findings were often controversial.13-81 It is known that Mg2Si precipitates have to be fine and uniformly distributed in the matrix.[8] The conventional extrusion process of the alloy includes the homogeniza-tion annealing of as-cast billets, cooling from the annealing temperature by air fans (H) or by water sprays (HP), heating to the forming temperature, extrusion, separated solution treatment in the salt bath, quenching, and artificial aging.[9] Recently, the development of the extrusion of the 6xxx series alloys combined different technological processes. The processes of separated solution annealing and quenching were replaced by the press-quenching process (PQ). This process contains extrusion and quenching on the extrusion press. Due to its reduced number of operations and efficiency of working heat, this process has great economic and ecological advantages. The billet quenching process (BQ) is an upgrade of extrusion process PQ and includes the technological processes of preheating above the solvus temperature and cooling billets with water sprays to the forming temperature. At the preheating of billets above the solvus temperature, the Mg2Si phase dissolves in the solid solution. During cooling of billets with water sprays to the forming temperature, the Mg2Si phase does not precipitate and so all the Mg and Si remain in the solid solution. The extrusion process BQ includes the following technological processes the homogenization annealing of as-cast billets, cooling from the annealing temperature by air fans or by water sprays, preheating of billets above the solvus temperature, cooling with water sprays to the forming temperature, extrusion, quenching on the extrusion press and artificial aging. The new extrusion process BQ was first used for extrusion of Al-Cu alloys.[10, 11] The present paper describes the influence of the homogenization annealing and the modified billet-quenching process (BQ process) on the microstructual and mechanical properties of the AISi1MgMn alloy. The BQ process includes the preheating of billets before extrusion above the solvus temperature with subsequent water cooling to the forming temperature. The comparison of BQ process was made at various forming temperatures and extrusion rates with the extrusion processes K and PQ. Experimental procedure The tested alloy was semicontinuously casted with HotTop-AirSlip system into billets with diameter of 228 mm, Table 1. The billets were in the first example homogenization annealed 5 h at 480 °C and in the second example 6 h at 560 °C in the gas furnace at industrial conditions. Cooling after the completed annealing was achieved by two cooling rates: =116.6 °C/min (water sprays, HP) and =200 °C/h (air fans, H). Then the billets were cut, tested with X-ray and extruded (20 MN direct press machine) into rods (diameter 20 mm) at various extrusion processes (K, PQ and BQ), Figure 1. At the extrusion process BQ, the billets were preheated above the solvus temperature and cooled with water sprays to the forming temperature. Preheating time of the billets above the solvus temperature was 6 min and cooling times were 4 s, 8 Table 1. Chemical composition of investigated alloy (w/%) Si Fe Cu Mn Mg Cr Zn Ti Pb Bi Al 0.8599 0.2022 0.0236 0.4778 0.6911 0.0547 0.0220 0.0286 0.0032 0.0019 rest Figure 1. Scheme of the extrusion processes a) conventional, K (1-ho-mogenization, 2-cooling, 3-reheating, 4-extrusion, 5-cooling, 6-solution treatment, 7-quenching and 8-artifical aging), b) press-quenching, PQ (1-homogenization, 2-cooling, 3-reheating, 4-extrusion, 5-quenching and 6-artifical aging) and c) billet-quenching, BQ (1-homogenization, 2-cooling, 3-preheating above the solvus temperature, 4-cooling to the forming temperature, 5-extrusion, 6-quenching and 7-artificial aging) s, 12 s and 16 s. After the quenching on the extrusion press, the rods were artificially aged for 16 h at 150 °C. Mechanical properties were tested by Zwick Z 400 tensile testing machine and Brinell hardness number by Zwick ZHU250. Microstructures were analyzed by JEOL JSM-5610 scanning electron microscope and Leica MEF4M optical microscope. Results and discussion Mechanical properties At extrusion process K, the rods exceed mechanical properties specified by EN standard to heat treatment T6, because the extrusion process K is similar to the heat treatment T6, Table 2. The rods from the homogenized billets at the temperature of 480 °C/5 h have higher values of Rm and rp0 2 for 2 %, same values of HB and lower values a5 for 7 % than the rods from the homogenized billets at the temperature of 560 °C/6 h, Figure 2. At extrusion process PQ, the rods from the homogenized billets at the temperature of 480 °C/5 h, have lower values of r for 3 %, HB for 2 %, A, for 12 % m 5 5 5 and higher values of Rp0 2 for 3 % than the rods from the homogenized billets at the temperature of 560 °C/6 h, Figure 2. At extrusion process BQ, the rods from the homogenized billets at the temperature 480 °C/5 h, have lower values of r for 6 %, r n for 2 %, A, for 8 % and m 5 p0.2 5 5 hb for 2 %, than the rods from the homogenized billets at the temperature of 560 °C/6 h. The extruded temperatures of billets after cooling do not have significant effect on the mechanical properties, Figure 2. The rods, extruded with process K, have higher values of Rm for 5 %, Rp0 2 for 13 % and lower values of a5 and HB for 8 % then the rods extruded with process PQ and BQ. The impact of homogenization annealing on the mechanical properties is very questionable at the extrusion process K, because process K contains of separated soluble annealing in salt bath and quenching in water. During the separated soluble annealing in salt bath at the temperature of 525 °C the whole Mg2Si phase dissolves in the solid solution. Therefore the rods have higher Table 2. Prescribed mechanical properties of the alloy AlSilMgMn after the heat treatment T6[12] Rm/(N mm-2) Rpo.2/(N mm-2) HB a5/% min. 310 min. 260 85 8 BQ (4 s) BQ (S s) Extrusion process BQMs) BQ (8 s) Extrusion process BQU2s) BQ(I6s) C) d) Figure 2. Mechanical properties of the extruded rods at different extrusion processes a) tensile strength, R HB and d) elongation, A b) yield stress, Rp02, c) Brinell hardness, Alx(FeMn)ySiz V -MgiSi 20kW X5S0 50M.T, WTF O MM LJ ti t T W Ak(FeMn)ySiz |v V \ ' < I r \ / . K-i < j M <} 20k