Hoek and Brown suggested a method to estimate the strength and deformation modulus parameters of rock masses. The method was then widely used in rock engineering designs. In such designs, the mean values of Hoek and Brown parameters are often used which are not proper values due to the variability of rock mass properties within a great range of values. In such cases, probability analysis of rock mass properties is highly important. The geological strength index is one of the most important parameters in Hoek and Brown equations. Determination of this parameter includes greater uncertainties than determining other parameters. In this paper, based on the results of rock mechanical tests carried out on rock samples of Gol-Gohar iron ore mine, and the required field surveys, the sensitivity of rock mass geomechanical properties on the type of the statistical distribution function of the geological strength index in statistical analysis of these parameters using Monte Carlo simulation method was investigated. The results showed that the sensitivity of Hoek and Brown equations to determine different rock mass geomechanical parameters varies as the type of the statistical distribution function of the geological strength index changes. The sensitivity of geomechanical parameters such as internal friction angle, cohesion, total strength and rock mass modulus on the type of the statistical distribution function of the geological strength index is much less than parameters such as uniaxial compressive strength and tension strength of rock mass. The greatest variations based on changes of the type of the statistical distribution function of the geological strength index are less than 5% for the internal friction angle, cohesion and total strength, less than 10% for the modulus, and less than 25% for the uniaxial compressive strength and tension strength.
Tanks are structures for storing fluids that are made in different sizes, shapes and genera. Today using of tanks for water, petroleum products storage, and industrial wastes, has been developed significantly. The buried rectangular concrete tanks are used for water supply in most cities in our country. Soil-structure interaction is one of the most important issues in seismic behavior of buried tanks. With respects to code 123 that has suggested Mononobe-Okabe equation for dynamic pressure of earthquake excitation, the purpose of this research is to achieve the dynamic pressure of soil during earthquake. The obtained results have been compared to analytical and other experimental researches. Therefore, a series of small-scale experimental tests were conducted using 1g shaking table testing in the laboratory of physical modeling at University of Tehran. The results illustrate that dynamic force and pressure from Mononobe-Okabe and Wood equation are greater than experimental testing results. However Seed-Whitman equation is closer to experimental results.
Lime percentage | Soil type | PI% | PL% | LL% | Sample | Layer |
85.15 | SM | 8.99 | 40.65 | 49.64 | L1 | Upper |
62.16 | SM | 15.49 | 32.12 | 47.61 | L2 | Middle |
88.72 | SM | 15.46 | 27.14 | 42.60 | L3 | Lower |
Standard No. | Test type |
ASTM-D422 (2000) | Soil classification |
ASTM-D4318-87 (2000) | Atterberg limits |
ASTM-D698 (2000) | Standard Compaction |
ASTM-D3080 (2000) | ِDirect shear |
ASTM-D2166-87 (2000) | Uniaxial Compressive Strength |
Layers | Gasoil percentage | Liquid limit (%) | Plasticity limit (%) | Plasticity Index (%) | Maximum dry unit weight (g/cm3) | Optimum water content (%) | Internal friction angle (ɸ) | Cohesion (kPa) | Uniaxial compressive strength (kPa) |
L1 | 0% | 49.64 | 40.65 | 8.99 | 1.65 | 22 | 4.6 | 7.4 | 18.4 |
7% | 54 | 40.13 | 13.87 | 1.87 | 10.5 | 4.04 | 6.6 | 8.7 | |
13% | 55.67 | 43.71 | 11.95 | 1.88 | 8.5 | 3.26 | 3.7 | 7.8 | |
19% | 55 | 40.65 | 14.34 | 1.96 | 3 | 2.3 | 2.75 | 3.5 | |
L2 | 0% | 47.61 | 32.12 | 15.49 | 1.87 | 14 | 6.97 | 6 | 9.6 |
5% | 64 | 40.39 | 23.61 | 2.08 | 9 | 5.73 | 5.5 | 7 | |
10% | 66 | 46.63 | 19.37 | 2.11 | 6 | 5.15 | 4 | 6.1 | |
15% | 68 | 49.09 | 18.91 | 2.14 | 3.5 | 4 | 2 | 1.25 | |
L3 | 0% | 42.6 | 27.14 | 15.46 | 1.62 | 22.3 | 2.6 | 10.7 | 22.6 |
7% | 56 | 39.27 | 16.72 | 1.92 | 9.5 | 2.41 | 8.5 | 10.5 | |
13% | 57.18 | 41.66 | 15.51 | 2.01 | 6 | 2.17 | 7/3 | 7.8 | |
19% | 63 | 42 | 20.99 | 2.03 | 3 | 1.45 | 6.9 | 4.4 |
Layer | Gasoil percentage | Dip of 10◦ | Dip of 20◦ | Dip of 30◦ | Dip of 40◦ |
L1 | 0% | 56.4 | 70.4 | 73.2 | 111.06 |
7% | 149.6 | 178.8 | 248.4 | 202.53 | |
13% | 166.53 | 227.2 | 241.6 | 278.93 | |
19% | 227.86 | 256.66 | 419.86 | 334.66 | |
L2 | 0% | 30.8 | 102.53 | 156.53 | 317.73 |
5% | 58.66 | 142.66 | 151.2 | 324.8 | |
10% | 74.93 | 168.66 | 244.53 | 365.73 | |
15% | 105.73 | 283.73 | 359.86 | 608.13 | |
L3 | 0% | 13.33 | 75.06 | 79.46 | 86.26 |
7% | 55.2 | 98.53 | 78.13 | 81.06 | |
13% | 124.13 | 176.8 | 145.73 | 140.06 | |
19% | 196.4 | 279.46 | 200.93 | 210 |
Acid mine drainage (AMD) as the most important environmental issue in mining sites is considered a significant source of environmental pollution. AMD is typically produced by the oxidation of sulphide minerals, especially pyrite. The present study aims to investigate the acid production potential of the wastes of Mehmandoost coal washing plant located in NE Damghan. For this purpose, mineralogical, geochemical, and statistic tests were carried out on 7 representative coal washing waste samples. The obtained results show that although coal washing wastes are not enriched in Cu and Mn, they are moderately enriched in Ni and Co, significantly enriched in Cr, Sb and Zn, strongly enriched in Cd and As, and extremely enriched in Pb and Mo. The main mineral phases presented in the studied samples include quartz, muscovite, clinochlore, kaolinite, illite, montmorillonite, calcite and pyrite. In most of the studied samples, the pH and electrical conductivity (EC) of the saturated paste is <3 and > 2000 μm/cm, respectively. Moreover, in most samples the Net Neutralization Potential (NNP) is < -20. Also, in most of the samples, the Net Acid Production Potential (NAPP) is positive and the Neutralization Potential ratio (NPR) is < 3. The pH of Net Acid Formation (NAG pH) of these samples is < 4.5 and the ratio of Acid Neutralization Capacity to Maximum Acid Potential Acidity (ANC/MPA) is < 1. According to the results of static tests, there is a possibility of production of acidic drainage by the studied samples, therefore, taking suitable management measures to control acid production in the area is of crucial importance.
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