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Thursday, September 3, 2020
What was the Cartoonists View of the verdict passed on Nelson Mandela Essays
What was the Cartoonists View of the decision passed on Nelson Mandela Essays What was the Cartoonists View of the decision passed on Nelson Mandela Essay What was the Cartoonists View of the decision passed on Nelson Mandela Essay In December 1963 Nelson Mandela was attempted in the Rivonia Trial. The Trial went on until June 1964 where he was detained forever barely abstaining from being condemned to death with seven others including Walter Sisulu, the pioneer of the ANC. Mandela was gone after for enrolling individuals for preparing and guerrilla fighting with the end goal of brutal unrest, when the police assaulted the MKs central station and discovered connections among Mandela and the ongoing attacks on power stations. The indictment requested that they should all be hanged however the measure of global intrigue constrained the appointed authority to pass life detainment on them all. The captures figured out how to separate the MK and the ANC inside South Africa. In Source G the visual artist, a man named Illingworth, has delineated Nelson Mandela being secured by one finger with a police officer a court judge and Verwoerd the most impressive Nationalist gathering Leader remaining close to him. Illingworth is attempting to state that the framework isn't holding him down. This is on the grounds that in the source Mandelas face is portrayed as irate and like the men secures him are having no impact on him. It might likewise be that he is attempting to state that the administration imagine that they have felled a goliath however they are having no impact. This is on the grounds that the characters remaining close to Mandela are little contrasted with him and from their perspective it looks like they have triumphed over Mandela. The Judge remaining close to Mandela is holding a record that says Mandela Judgment. It is suggested that the courts and government believe that they are successful over Mandela. When this source was distributed Nelson Mandela and the ANC had sorted out many bomb assaults on power stations and petroleum treatment facilities. They were attempting to make South Africa ungovernable by interruption by these assaults. Illingworth is stating that the legislature have not halted Mandela however just blocked him. I state this on the grounds that the police officer in the source is secures one of his fingers and this doesnt appear to concern Mandela in the source since it is just one finger. Another manner by which this could be deciphered is that the figure of Mandela speaks to the entire of the Black Community against politically-sanctioned racial segregation. In the event that the finger is deciphered to speak to Mandela it passes on the message that you can hold down one man however would never keep down the entire Black Community. Hendrik Verwoerd is in the animation since he is one of the pioneers of the NP and when that the source was distributed he was one of the primary impacts behind the Nationalist Party, in the animation he is holding his head high and is grinning giving the feeling that he is glad and pleased that Nelson Mandela has been cut down. Mandela is likewise envisioned as youthful and solid in the picture and this is to give the message that the young people of the ANC is the future and that Mandela and the ANC are solid and will stand up to. Illingworth would have thought this since he was British and the occasions in South Africa didn't just speak to the South Africans yet to individuals everywhere throughout the World since occasions, for example, the Sharpeville Massacre and the manner in which the ANC were battling against politically-sanctioned racial segregation was something that would be placed everywhere throughout the news in different nations. In 1976 there were numerous enemy of politically-sanctioned racial segregation shows in London since individuals realized what was happening. There was additionally a developing populace who were joining the ANC and numerous individuals who in spite of the fact that didn't join the ANC shared a large number of its thoughts against politically-sanctioned racial segregation so Illingworth was attempting to state that the NP believe that they have accomplished more than they really have. He likely likewise understood that he could start mischief in England since this is the place the Source was printed and could get individuals to understand that the ANC was the correct way to decide for the South Africans. He presumably believed that in the event that there was sufficient outside help, at that point the NP would be compelled to transform it arrangements. In 1973 the OAU (Organization of African Unity) was shaped and given a solid restriction to politically-sanctioned racial segregation this was significant in light of the fact that after so much concealment the dark network was at long last attempting to fight back and this is one of the focuses in the animation. That despite the fact that Mandela has been cut down the dark network is as yet solid and there is as yet a solid resistance towards politically-sanctioned racial segregation. Another motivation behind why the sketch artist may have held this view is on the grounds that he has seen what has occurred in different nations, for example, those that have had their freedom and were presently finding real success. The illustrator may likewise be criticizing the NP since South Africa had as of late left the Common Wealth which gave them worldwide standing. He might be calling attention to that under the NP South Africa isn't progressing admirably and on the off chance that under the ANC, at that point it will turn out to be better. In end Illingworths perspective on the decision is that despite the fact that Mandela has been placed in jail the ANC and the Black Community can not be held down. He thinks this since he is a British supporter of politically-sanctioned racial segregation and needs to see the finish of racial separation in South Africa. Illingworths see is that Nelson Mandela ought not be in jail however that it doesn't have a lot of effect on the grounds that the restriction is so solid against the legislature that regardless of whether Mandela is in jail they can even now do the opposition without him. Through the Source he is attempting to state that the administration believe that they have squashed their resistance by capturing and attempting Mandela yet Illingworth most likely idea this was false and that the Black Community and the restriction to politically-sanctioned racial segregation would at present go on despite the fact that Mandela was not there to sort out it.
Saturday, August 22, 2020
Application for a Job as an Advertiser Essay Example | Topics and Well Written Essays - 1750 words
Application for a Job as an Advertiser - Essay Example Above all my scholarly certifications are an elaboration to guarantee my comments. Similarly as explained in my certifications, I have shown to be in a profound touch with both oral and composed language. Next, after an interior entry level position with my learning foundation, I am persuaded that I have amassed satisfactory relational abilities. This comes after I was granted on merit for commendable execution, by the data and interchanges innovation office. A lot to impact my profession, I have aced a receptive way to deal with handling ordinary issues, this has attracted inventiveness me particularly as well as furnished me with the capacity of advancement. Given the idea of exercises the calling involves, I am constrained to stretch out my ability to adaptability. I canââ¬â¢t deny that I am frequently tested with extraordinary working conditions. Nonetheless, I have frequently than not exhibited great adapting abilities; with the goal that I ensure accomplishment in that which is anticipated from me. Regardless, everybody needs direction in any field. By and by, I donââ¬â¢t have faith in void ways but instead issue-based goals; I am a man of activity. To a minor degree, I have frequently undermined my relational abilities. For example, when I emphatically accept on my stand I am constantly crashed into making it progressively harsh in this manner depicting inflexibility. Anyway much I might be correct, this ought to never be a piece of polished methodology. Luckily, I am cheerful that after a progression of serious courses and introduction to the activity showcase, I will without a doubt be in a place of most extreme polished skill. My Curriculum Vitae and Attachment Letter. POST APPLIED FOR: 1. Individual Details SURNAME Bull INITIALS J. B. Changeless Address and Postcode: P.O BOX, 2298-764 Westminster, K-4 Street, Dapard Address for correspondence (if unique): N/A Telephone No(s) Home: 11123647 Work: 111240032 Email Address Onomtpoei@hotmal.con Mobi le: 0766224365 Are we ready to get in touch with you at work? By Phone: Yes/No= Yes By Email: Yes/No=Yes no Do you hold a present full vehicle driving permit? Indeed/No= No 2.
Friday, August 21, 2020
All Money, All the Time essays
All Money, All the Time expositions In Richard Brookhisers article All Junk, All the Time, Brookhiser investigates components of awesome music which will never show signs of change on the grounds that as he states it is so natural to do alright (Brookhiser 607). He guarantees that mainstream society exciting music, or pop, is substandard compared to the melodic executions of old style, jazz, and show tunes. In spite of these unrivaled types of music, awesome music requires no ability, it utilizes dull verses to play to audience members with second rate keenness, or more all there is pain free income to be made. Brookhisers perspective may seem haughty or unselfish, yet as a general rule his announcement is reality. This kind of ironical editorial has existed for ages and will for some more. His case that drumming is simple and can be faked mirrors Voltairian discourse of long past. He contends that the guitar is certifiably not a refined instrument and in help offers that this instrument doesn't require long periods of preparing and isn't utilized as educational program in college melodic examinations. Grungy instruments bring forth foul music, which generates grungy moving. This thought inspires murmurs of alleviation from men around the globe. All things considered, who has the opportunity to take move exercises? Rock darlings can do alright by rotating set up, knocking and pounding. Come move, its simple! Maybe Transcontinental Records CEO, Lou Pearlman, emphasizes the most deplorable offense of the popular music industry. As indicated by Jim Slotek of the Toronto Sun Pearlman is, to put it plainly, the person who made The Backstreet Boys and Nsync in a zeppelin holder in Orlando, Fla., and watched his brilliant thoughts create more than $2 billion in deals (Slotek 1). Since his production of the two most gainful cutout boybands Pearlmans boyband plant has, working together with ABC, started take a shot at the following huge thing to hit shouting adolescents all over, O-Town. This m ... <!
Friday, June 19, 2020
Hydraulic Conductivity Soil
Hydraulic Conductivity Soil Chapter 1 Introduction Hydraulic conductivity or permeability of a soil is one important soil properties used in geotechnical engineering. It can be seen from the difficulty in measuring accurate and reliable values of hydraulic conductivity. Hydraulic conductivity of soil is basically the capacity of water to let water to pass through the pores or voids in the soil. There are many methods developed in order to measure the hydraulic conductivity of soil; both laboratory and in-situ field methods. Some of the common laboratory methods are the constant-head test and falling head test. On the other hand, the common in-situ field methods are pumping well test, borehole tests (e.g. slug test, variable head test), infiltrometer tests and using porous probes (BAT permeameter). All these in-situ field test methods were used to measure the hydraulic conductivity of subsoil for both saturated and unsaturated media. One other in-situ field measurement method that has been introduced is the Two-Stage Borehole (TSB) test, also known as the Boutwell permeameter test. This testing method is commonly used to test a low hydraulic conductivity soil such as compacted clay liner used in landfill barrier system or covers used at waste disposal facilities, for canal and reservoir liners, for seepage blankets, and for amended soil liners. The advantage of using this method is that it can be used to measure both the vertical and horizontal hydraulic conductivity values of soil, kv and kh respectively. One other advantages of using this method is that it can be used to measure the rate of infiltration of water or other fluid into a large mass of soil which can represent the tested site. However, the application of the TSB/Boutwell permeameter test for natural soil or other soils having a higher permeability value has been limited. This report will discuss the theory behind the TSB/Boutwell permeameter test and the application of this method on natural soil. The methodology of this test will also be included in this report. In addition to the standard TSB setup, this report will also discuss the modification made to the standard TSB test which can be easily and quickly installed in shallow boreholes for subsequent testing. The methodology and results from the modified setup will also be included. The results from both the standard and modified setup will then be compared. Objectives The objectives of this project is summarised into four stages. In the first stage, the objective is to measure the hydraulic conductivity of the soil using the standard TSB/Boutwell permeameter setup. The second stage involves the modification of the standard TSB/Boutwell Permeameter setup. The aim is to obtain a simple installation setup which can be easily and quickly installed in shallow boreholes for subsequent testing. In the third stage, the objective is to test the modified TSB/Boutwell Permeameter test in the field. This is done by carrying out a series of tests in varied subsurface media at the assigned site location. The results from both the standard and modified TSB/Boutwell Permeameter test will be compared. The last stage of the project consists of particle size analysis of the soil obtained from site. The results from the two setups will again be compared to the hydraulic conductivity values obtained from the derivation of the Particle Size Distribution curves. The tasks that are done in this project include: The review of TSB/Boutwell Permeameter methodology Developing the modify TSB/Boutwell Permeameter Completion of field tests using the TSB/Boutwell Permeameter Collection of soil samples and subsequent particle size analysis Chapter 2 Literature Review 2.1 Soil Water Soils are consists of separate solid particles. The pore spaces between the solid particles are all interconnected which mean that water is free to flow through these interconnected pore spaces (Whitlow, 2001). The water will flow from a higher pore pressure point to a lower pore pressure point. The pressure of the pore water is measure relatively to the atmospheric pressure. The level in which the pressure is zero (i.e. atmospheric) is defined as the water table (Craig, 2004). The soil above the water table is assumed to be unsaturated and the soil below the water table is assumed to be fully saturated. The level of water table changes in relation with climate conditions and can also be affected by any constructional operations (Craig, 2004). It is usual to express a pressure as a pressure head or head which is measured in metres of water when considering water flow problems. According to Bernoullis equation, the total head at a point in flowing water can be given by the sum of three head components; pressure head (u/ÃŽà ³w), velocity head (v2/2g) and elevation head (Z). This relationship is illustrated in the equation below: (Equation 1) where; h = total head u = pressure v = velocity g = acceleration due to gravity ÃŽà ³w = unit weight of water Z = elevation head However, since the seepage velocities in the soil are so small due to the high resistance to flow offered by the granular structure of the soil, the velocity head is often omitted from the equation (Whitlow, 2001). The total head at any point is then can be adequately represented by: (Equation 2) In saturated conditions, the one-dimensional water flow in soil is governed by the Darcys Law, which states that the velocity of the groundwater flow is proportional to the hydraulic gradient: (Equation 3) where; v = velocity of groundwater flow = flow/area (q/A) k = coefficient of permeability or hydraulic conductivity (constant) i = hydraulic gradient = head/length (h/L) The empirical validity of Darcys Law depends heavily on the hydraulic conductivity, k, which must be carefully determined so that it can represent the soil mass (Azizi, 2000). The different practical methods that can be used to measure the hydraulic conductivity will be discussed in Section 2.3. It is important to study the flow of water through porous media in soil mechanics. This is necessary for the estimation of underground seepage under various conditions, for investigation of problems involving the pumping of water for underground constructions, and for making stability analyses of retaining structures that are subjected to seepage forces (Das, 2006). Hydraulic Conductivity (Coefficient of Permeability) Hydraulic conductivity, k, of a soil is the capacity of the soil to allow water to pass through it. The value of hydraulic conductivity is often used to measure the resistance of a soil to water flow. Hydraulic conductivity has units of length divided by time. The most common unit used of measurement is meter per second (m/s). Although hydraulic conductivity has the same unit as those to describe velocity, it is not a measure of velocity (Coduto, 1999). Importance of Hydraulic Conductivity Hydraulic conductivity is a very important parameter in geotechnical engineering or in determining the widespread of contamination. This can be seen in the difficulties in measuring it. This is because hydraulic conductivity can varies from one point in a soil to another, even with small changes in the soil characteristics. It is also, as mentioned in the previous section, influenced by the viscosity and unit weight of the fluid flowing through the soil. Hydraulic conductivity is also dependent to the direction of flow which means that the vertical hydraulic conductivity would not be the same as the horizontal hydraulic conductivity. This condition of the soil is said to be anisotropic. Studies that have been made indicate that the value of vertical hydraulic conductivity (Kv) of a soil is usually higher than the horizontal hydraulic conductivity (Kh) in one or two order of magnitude (Chen, 2000). Some applications in which information on hydraulic conductivity is very important are in modelling the groundwater flow and transportation of contaminants in the soil. Hydraulic conductivity data of a soil is also important for designing drainage of an area and in the construction of earth dam and levee. In addition, it is very important in tackling most of the geotechnical problems such as seepage losses, settlement calculations, and stability analyses (Odong, 2007). Factors Affecting Hydraulic Conductivity The hydraulic conductivity of a soil depends on many factors. The main factor that affecting the value of hydraulic conductivity is the average size of the pores between particles in the soil, which in turn is related to the distribution of particle sizes, particle shape and roughness, pore continuity, and soil structure (Craig,2004). In general; the bigger the average size of the pores, the higher the value of hydraulic conductivity is. The value of hydraulic conductivity of a soil that has a presence of small percentages of fines will be significantly lower than the same soil without fines. In the other hand, the presence of fissures in clay will result in a much higher value of hydraulic conductivity compared to that of unfissured clay (Craig, 2004). The range of the hydraulic conductivity value is very large. Table 1 below illustrates the range of hydraulic conductivity which differs from one soil type to another which is mainly due to the different average size of the pores between the soil particles. Table 1 Range of hydraulic conductivity values (m/s) with different soil type (Whitlow, 2001) 102 101 1 10-1 Clean gravels Very good drainage 10-2 10-3 10-4 Clean sands Gravel-sand mixtures 10-5 10-6 Very fine sands Silts and silty sands Fissured and weathered clays Good drainage Poor drainage 10-7 10-8 10-9 Clay silts (20% clay) Unfissured clays Practically impervious The hydraulic conductivity is also dependent to viscosity and density of water in which both are affected by temperature. It is therefore conclude that the value of hydraulic conductivity will then be affected by changes in temperature. Theoretically, it can be shown that for laminar flow and saturated soil condition the relationship between temperature and hydraulic conductivity: (Equation 4) Where; ÃŽà ³w= unit weight of water ÃŽà · = viscosity of water K = absolute coefficient (units m2). This value is dependent on the characteristic of the soil skeleton. Since most of the laboratory graduations were standardised at 20C, the value of hydraulic conductivity at this temperature is taken as 100% (Craig, 2004). Other value of hydraulic conductivity at 10C and 0C are 77% and 56% respectively (Craig, 2004). Hydraulic Conductivity Tests Most of the tests for measuring hydraulic conductivity measured one average value of hydraulic conductivity. However, some tests measured both the vertical and horizontal hydraulic conductivity values to obtained more accurate estimation. There are numbers of experiments and test that can be done to measure the hydraulic conductivity of a soil. These tests to measure the hydraulic conductivity can be done both in the laboratory and in the field. The following sections will briefly discussed the most common laboratory and in-situ tests practiced today to measure the hydraulic conductivity of a soil. Although with all the various tests developed to measured the hydraulic conductivity, there are uncertainties arise on how the soils that being tested represent the whole soil condition at the site of interest. It is therefore a good practice to perform different tests and comparing the results obtained. Laboratory Permeability Tests One problem with laboratory tests is that the samples collected do not adequately represent the detailed conditions of the soil, e.g. fissures, joints or other characteristics in the site of interest. Even with carefully conducted tests and good sampling techniques, it is impossible to obtain a very accurate result. The results typically have a precision of about 50% or more (Coduto, 1999). It is therefore important to take this into consideration if any construction activities or contamination remediation operations to be perform at the site of interest. Constant Head Permeability Test The constant head test is used to measure the hydraulic conductivity of more permeable soils such as gravels and sands which have a hydraulic conductivity value of 10-4 m/s (Whitlow, 2001). The equipments used for this test is called a constant head permeameter. A schematic illustration of this equipment is shown in Figure 2.1. The constant head permeameter was developed base on the basic idea of Darcys Law (Equation 3). The soil sample is contained in a cylinder of cross-sectional area A. Continuous water supply is let to flow from a tank to the sample to maintain a constant head. The water that flow through the sample is collected in a collection jar or container and the discharge through the sample is measured by calculating the volume of the water in the collection container over a period of time t. h Figure 2.1 Schematic diagram of Constant Head Permeameter (www.geology.sdsu.edu) The hydraulic conductivity, k of the tested soil is then calculated by: From equation 3: (Equation 5) Where; Q = the discharge through the sample (m3/s) L = the length of the sample (m) A = cross-section of the sample (m2) h = hydraulic head (m) The above diagram shows a simple setup of the constant-head permeameter. Other setup is also available which make use a pair of standpipes to measure the pore pressure and potential at two points. This is illustrated in Figure 2.2 below. Although both the setups are different, it makes used of the same concepts; Darcys Law. Figure 2.2 Alternative setup of Constant Head Permeameter (Whitlow, 2001) Falling Head Permeability Test The falling head test is used to measure the hydraulic conductivity of less permeable soils such as fine sands, silt and clay. The water flow resistance in these types of soil are very high which unable to measure accurate measurements of hydraulic conductivity if used with constant head permeameter. Undisturbed samples are required to perform laboratory test to measure the hydraulic conductivity of a soil. However, a small degree of disturbance of the sample is accepted as it is very hard to obtain a perfect undisturbed sample. An undisturbed sample can be obtained usually using a U100 sample tube or a core-cutter tube (Whitlow, 2001).The schematic illustration of the falling head test setup is shown in Figure 2.3. Figure 2.3 Laboratory setup of falling head test (Whitlow, 2001) The sample is place in a cylinder container with a wire mesh and gravel filter at both end of the cylinder. The base of the cylinder is left to stand in a water reservoir fitted with a constant level overflow. At the other end, which is the top of the cylinder, it is connected to a glass standpipe of known diameter (Whitlow, 2001). These standpipes are then filled with de-aired water and it is allow to flow through the soil sample. The height of the water in the standpipe is measured at several time intervals. The test is then repeated using standpipes of different diameters. It is a good practice to take note of the initial and final unit weight and water content of the sample to get additional information about the properties of the sample (Whitlow, 2001). The hydraulic conductivity of the sample is then calculated from the results obtained from the tests. The Darcys Law concept is still used in determining the hydraulic conductivity. The derivation of the hydraulic conductivity for the falling head test is done as follow (Whitlow, 2001). Deriving from Equation 3: With reference to Figure 2.3, if the level of the water in the standpipe fall dh in a time of dt the flow, q will be and the hydraulic gradient, i Therefore; (Equation 6) Where; a = cross-sectional area of the standpipe A = cross-sectional area of the sample When equation 6 is rearranged and integrated, the final equation to calculate the hydraulic conductivity is given as (Equation 7) Particle Size Analysis Particle size analysis is commonly used to classify the physical properties of the soil being tested. This testing method is used for both soil science and engineering purposes (Keller and Gee, 2006). In context of engineering purposes, it is commonly used to define the particle size distributions of the soil. The data obtained from the particle size distributions can then be used to estimate the pore-size classes needed in calculating the hydraulic properties of the soil such as hydraulic conductivity (Keller and Gee, 2006). There are various methods of measuring particle size analysis. Traditional methods include sieving, hydrometer and pipette. Other new techniques are also been developed; one example is laser-diffraction techniques (Eshel et al, 2004). However, particle size analysis is dependent on the technique used for defining the particle size distribution. It is therefore a common practice to do more than one method to define the particle size distribution (Keller and Gee, 2006). The results from all the different methods can then be compared to obtain more representative result. For the traditional particle size analysis methods, two separate procedures are used in order to obtain wider range of particles sizes (Head, 1980). The two procedures are sieving and sedimentation procedures (hydrometer or pipette method). Sieving is used to categorise large particle such as gravel and coarse sand. The particles can be separated into different size ranges using a series of standard sieves. For the finer particles such as silt and clay, sedimentation procedure is used (Head, 1980). Once the particle size distribution is defined from the particle size analysis, the hydraulic conductivity of the tested soil can then be estimated using a number of established empirical equations. However, the applicability of the above equations depends on the type of soil that is being tested. The following paragraphs summarised several empirical equations from previous studies (Odong, 2007). Hazens equation: (Equation 8) Kozeny-Carmans equation: (Equation 9) Breyers equation: (Equation 10) Slitchers equation: (Equation 11) Where; g = acceleration due to gravity v = kinematic viscosity n = porosity of the soil d10 = grain size in which 10% the sample is finer than The estimation of the hydraulic conductivity from these equations required information on the kinematic viscosity v and porosity n of the soil. The kinematic viscosity can be calculated by: (Equation 12) Where; = dynamic viscosity ÃŽà ¡ = density of water The porosity n can be calculated using the empirical relationship below: (Equation 13) Where U is the coefficient of grain uniformity and is given by: (Equation 14) The values of d60and d10 can be obtained from the particle size distribution. d60and d10 represent the grain size for which 60% and 10% of the sample respectively is finer than. In-situ Field Permeability Tests Due to the problems associated with reliability and laboratory tests, as mention in Section 2.3.1, field methods of measuring the hydraulic conductivity should be used to obtain more accurate and reliable measurements. In the field test, the soil disturbances is kept to a minimum level and they usually involves the testing of larger, more representative samples. Although, in term of cost and time, field measurement method is more expensive, it will as well provide more reliable measurement of hydraulic conductivity when dealing with a wide range of soil macro-structural characteristics. Other more economic option of field measurement can also be done. Such example is by performing borehole test, provided the pumping observation sequences are carefully planned and controlled (Whitlow, 2001). Well Pumping Tests This method is more suitable if used to measure hydraulic conductivity in homogenous coarse soil strata (Craig, 2004). The procedure involves the measurement of water that is being pumped out of a well at a constant rate, then observing the effect of these pumping activities to the drawdown of the groundwater level at other wells. The diameter of the well is normally at least 300mm and penetrates to the bottom of the stratum under test (Craig, 2004). The pumping rate and the groundwater levels in two or more monitoring wells are then recorded. The analysis of the results depends whether the aquifer is confined or unconfined. Well pumping test in a confined aquifer In confined aquifer the permeable stratum is squeezed in between two impermeable layers. This is illustrated in Figure 2.4 below. To perform the test, the pumping rate must not be too high to reduce the level in the pumping well below the top of the aquifer. The interface between the top aquifer and the overlying impermeable stratum therefore forms the top stream line (Whitlow, 2001). Figure 2.4 Pumping test in confined aquifer (Azizi, 2000) Figure 2.4 illustrates the arrangement of the pumping well and two other monitoring wells. Two assumptions were made at this point; the piezometric surface is above the upper surface of the aquifer and the hydraulic gradient is constant at a given radius (Whitlow, 2001). In steady state condition, the hydraulic gradient through an elemental cylinder with radius r from the well centres estimated as follow: where; dr = thickness h = height The area in which the water flow, A: where; D = the thickness of the aquifer Substituting the area A into the Darcys Law (Equation 4) will give; Hence: And therefore the hydraulic conductivity is: (Equation 15) In the case that the piezometric level is above ground level, where the water level inside the well inserted into the confined aquifer rises above the ground level, this scenario is called Artesian conditions (Azizi, 2000). This is illustrated in Figure 2.5. Figure 2.5 Artesian conditions (Azizi, 2000) Well pumping test in unconfined aquifer An unconfined aquifer is a free-draining surface layer that allows water to flow through the surface. The permeable stratum is not overlain by an impermeable layer. The piezometric surface is therefore in the same level of the water table. This is illustrated in Figure 2.6 below. The surface layer permeability is very high, thus allowing the water table to fluctuate up and down easily. Figure 2.6 Pumping test in an unconfined aquifer (Whitlow, 2001) Under steady state pumping conditions, the hydraulic gradient i at a given radius is assumed to be constant in a homogenous media. Homogenous unit is where the properties at any location are the same. For instance, sandstone has grain size distribution, porosity and thickness variation within a very small limit (Fetter, 2001). With reference to the arrangement of pumping well and two monitoring wells in Figure 2.6 above, the hydraulic conductivity can be determine by: Deriving from Equation 3: where; Hydraulic gradient i is And area through which the water flow, Then, Thus, hydraulic conductivity for an unconfined aquifer (after integrating the above equation) is (Equation 16) Borehole Permeameter Tests There are many borehole tests developed to determine the hydraulic conductivity of a soil. The most common in-situ borehole tests are as follow: Slug test Two-stage borehole test/ Boutwell Permeameter Variable head test In-situ constant head test Slug test is one of the cheapest in-situ field methods to determine the hydraulic conductivity of a soil. The procedure of this test involves the rapid adding or removing a slug or water into a monitoring well. The slug can be of anything that can displace the volume of the water in the well, e.g. water, plastic tubing capped at both ends, and other material of known volume and can fit into the monitoring well. The rate of rise and fall of the groundwater level is then observed until it reaches an equilibrium state. In a variable head test, a slug is introduced into the monitoring well by either adding in a measured volume of water into the well or other materials mentioned earlier. The rate of water level fall is then measured in time. This is called falling head test. The water can also be removed out from the well by using a bailer or a pump. The rate of water level rise is then measured with time. This is called a rising head test. Depending on the properties of the aquifer and the soil, and the size of the slug used the water can either returns to its original water level before the test quickly or very slowly. For instance, if the porosity of the soil is high then the water level will returns very quickly to its original water level before the test is done. There is also the constant head test. In this test the water level or head is maintained throughout the test at a given level. This is done by adjusting and measuring the flow rate of the water at intervals from start to the end of the test (Whitlow, 2001). The constant head test is said to give more accurate results, provided the water pressure is controlled so that it would not cause fracturing or other disturbance to the soil (Whitlow, 2001). There are several assumptions made for this test: The soil is homogenous, isotropic, uniformly soaked Infinite boundaries Soil does not swell when wetted The expressions use to calculate the hydraulic conductivity for the above tests depend on whether the stratum is unconfined or unconfined, the position of the bottom of the casing within the stratum and details of the drainage face in the soil (Craig, 2004). The horizontal hydraulic conductivity is tend to be measured if the soil is anisotropic with respect to permeability and if the borehole extends below the bottom of the casing. On the other hand, the vertical hydraulic conductivity is often measured if the casing penetrates below soil level in the bottom of the borehole (Craig, 2004). The following expressions are all recommended in BS 5930 to calculate the hydraulic conductivity (Whitlow, 2001). For variable head test: (Equation 17) Or, (Equation 18) For constant head test: Hvorslevs time lag analysis (Equation 19) Gibsons root-time method (Equation 20) where; A = cross-sectional area of the standpipe or borehole casing F = and intake factor dependent on conditions at the bottom of the borehole. The value for F can be obtained from Figure 6 of BS 5930 (BS 5930, 1999). T = basic time lag. Figure 7 and 8 of BS 5930 (BS 5930, 1999). H1, H2 = variable heads measured at elapsed times of t1 and t2 respectively Hc = constant head q = rate of inflow = steady state of inflow, obtained from Figure 10 of BS 5930 (BS 5930, 1999). Two-Stage Borehole (TSB) test/ Boutwell Permeameter This project involves the use of this measurement technique. It is one of the borehole permeability tests and can be used in both saturated and unsaturated region. This method is first developed by Professor Gordon P. Boutwell as a relatively quick and simple way to calculate the effectiveness of compacted soil liner construction techniques (www.erosioncontrol.com). This test method may also be utilised for compacted fills or natural deposits, above or below the water table. TSB test or Boutwell permeameter is usually used to measured the hydraulic conductivity for a low permeability media such as natural clay liner used in landfill barrier system or other material with hydraulic conductivity value less than or equal to 110-5 m/s (ASTM, 1999). This test method involves two-stage falling head test using infiltrometer installed inside the ground. The infiltrometer is basically a standpipe used to measure the fall in the water level in the borehole as the water dissipated into the soil. In both stages of the TSB test, the rate of flow in which water flow into the soil through a sealed, cased borehole is measured usually using a standpipe in a falling-head test procedure. In stage 1 of the TSB test, the bottom of the casing is in the same level with the bottom of the borehole. The casing will prevent the water to dissipate horizontally. This will ensure the maximum effect of the vertical hydraulic conductivity KV. In stage 2 of the TSB test, the borehole is extended below the bottom of the casing. This will make the water to dissipate both vertically and horizontally. Both the vertical and horizontal hydraulic conductivity values, KV and KH respectively, can be calculated. The setup for TSB is illustrated in Figure 2.7 below. The value obtained from this test is only the limiting hydraulic conductivity values K1 and K2. The actual value of KV and KH are then calculated from these limiting values. (a) (b) Figure 2.7 Setup for two-stage borehole test (a) Stage 1 (b) Stage 2 This method covers field measurement of limiting values for both vertical and horizontal hydraulic conductivities of porous materials the two-stage cased borehole technique. These limiting hydraulic conductivity values are the maximum possible value for the vertical direction and the minimum possible value for the horizontal direction (ASTM, 1999). The methodology of this method will be further discussed in the following chapter. Chapter 3 Methodology 3.1 Introduction This chapter will discuss the methodology and equipments used to perform both the standard and modified setup of the TSB /Boutwell Permeameter test. This chapter will also discuss the methodology of the laboratory test for the particle size analysis. The site background on which the tests are done will also be included in this chapter. The results from both the standard and modified TSB/Boutwell tests will then be compared to that of the results obtained from the soil particle size analysis. 3.2 Site background and condition The tests were performed at the Quad of the David Kier Building, Queens University Belfast. The site can be access from the Stranmillis Road or the Malone Road. Figure 3.1 below shows the satellite image of the site. Figure 3.1 Satellite image of the site (Google Map) With reference to Figure 3.1, the site is found to be sloping downward. The site is surrounded by the David Kier building. There are three big trees grew within the quad. There is a big excavation done in the site during its construction in 1962. The soil at the site might consist of man-made fill. However, the soil below 1 or 2 metre might represent the natural soil of the site. 3.3 Field test of the standard TSB/Boutwell Permeameter test 3.3.1 Theory As mention earlier in the literature review, the TSB test or Boutwell Permeameter was used to measure the limiting values of the vertical and horizontal hydraulic conductivity. For the case of the vertical direction, the maximum possible value is taken. On the other hand, the minimum possible value is taken for the horizontal direction. Both the two stages in the TSB test involve the measurement of the flow rate of water flow into the soil through a sealed, cased borehole. Grout was usually used for sealing the borehole and the casing used is commonly a plastic PVC pipe. In Stage 1 the casing extended to the bottom of the borehole to prevent the water dissipates into the soil horizontally. Water will only flow into the soil through the bottom of the borehole. This will enable for the measurement of the maximum effect of the vertical hydraulic conductivity (Kv). In Stage 2 of the TSB test, the length of the borehole is extended. The length of the extended borehole depends on the diameter (D) of the casing (see Figure 2.7b). Standard values that were usually used are 1.0D, 1.5D and 2.0D (Daniel, 1989). Water will now be able to flow into the soil through the side wall and bottom of the borehole. This will enable the measurement of the maximum effects of both Kv and Kh hydraulic conductivity. The standard TSB/Boutwell Permeameter test method that was done in this project will be slightly different from the standard test method in the ATM International: Designation D6391-99. More of this will be discuss in sub-section 3.4.3. However, note must be taken that the direct results obtained from the field test are not the actual value of Kv and Kh. It is only the measurement of the limiting values of K1 and K2. The actual values of Kv and Kh are then calculated from these limiting values. 3.3.2 Equipments This section will list down the equipments used during the whole TSB test. Below are all the equipments. Hand auger used to drill the borehole. Reamer used to ream the bottom of the borehole to a level plane. Borehole casing consists of watertight plastic PVC tubing. The bottom end of the casing is not capped. Dip meter to measure the head in the standpipe manually. It has a sensor at the very end of it. This sensor will detect any presence of water in the borehole. Stopwatch to measure the time taken for any fall in head in the borehole. Readable to 1 second. Datalogger This will automatically measures the heads in the borehole. 3.3.3 Procedure 3.3.3.1 Borehole and casing setup This is the most important steps in the whole procedure. Extra care must be taken to when doing this stage. The borehole is first drilled using the hand auger. The drilling procedure must be done in the direction perpendicular to the ground surface. This is to ensure that the borehole will not be drill at an angle to the ground surface. No drilling fluid was used during the drilling. The diameter of the drilled borehole was 7cm. The bottom of the borehole is then ream and smoothed using a flat auger. The bottom of the borehole must be smooth and flat to ensure proper measurement during the test. The casing is then inserted into the borehole after the borehole preparation was done. The casing used was 5.5cm in diameter. The casing was set parallel to the axis of the borehole and centered by hand. The depth from the top and the bottom of the casing was then measured. The casing is extended 5cm above the ground surface .The borehole is then sealed using a mixture of bentonite and water. The bentonite mixture extended 2-3cm to the ground surface. Extra attention was given to make sure no bentonite spill into the casing. The bentonite was then let to dry (hydration period). The hydration period take approximately atleast 12 hours. The top of the casing was covered to prevent any rainfall, surface runoff or other debris to enter the borehole. In the ASTM International, a flow system and a standpipe should be installed on top of the borehole casing. However, in this project both the flow system and standpipe will not be used. Usually the TSB/Boutwell Permeameter test was conducted to measure the hydraulic conductivity of compacted clay liner which has a very low hydraulic conductivity value. This means that water will flow very slowly into the soil. Since there will only be a very small changes of water level in the borehole for testing a compacted clay liner over a period of one hour, the standpipe will be very useful to measure this difference of water level. However, this will not heavily affect the results of the test. 3.3.3.2 Stage 1 At the start of the test, sock should be inserted into the bottom of the borehole. The purpose of the sock is to protect the soil at the bottom of the casing from disturbance when water is introduced into the casing (ASTM, 1999). However, due to the unavailability of this item, the sock was not used during the whole project. Water is then introduced into the casing slowly to prevent any damage to the soil exposed at the bottom of the casing. The borehole was filled with water until the water level is just above the ground level. This is to check whether the borehole seal is working properly. If there is water flowing out through the seal, this mean that the seal is not working properly. In this case the sealing procedure should be repeated. There are two ways how the rates of water flow into the soil can be measured; (i) manually using a dipmeter and a stopwatch and, (ii) automatically using a datalogger. The measuring procedure is similar to that is apply for falling-head test. For taking the manual reading, the initial water level was first measured using the dipmeter. Record this reading and mark it as time zero. This is when the test is started. Measurements of the water level in the casing were then taken at a given time interval (e.g. for every 5 minutes). In the case of taking the reading automatically, datalogger was used. The datalogger was first set using a computer. The datalogger has the ability to calculate the water depth in the borehole by measuring the atmospheric pressure in the borehole. It also can also measure the water temperature in the borehole. Once the test is terminated, the data in the datalogger is downloaded into a computer. Since the test was conducted on natural soil, the flow of water into the soil is expected to be higher than the test conducted on compacted clay liner. This will mean that water level in the borehole will drop quickly. The test will be terminated once the water in the borehole fully infiltrate into the soil. The data collected from this test is then use to calculate the vertical limiting conductivity (K1) of the soil. The following Hvorslevs equation is used to calculate the value of K1 (Daniel, 1989). With reference to Figure 2.7(a) K1 is calculated as follow: (Equation 21) where; d= the diameter of the standpipe D = the diameter of the borehole casing t1 = time at the start of the test t2 = time at the end of the test H1 = head at the start of the test H2 = head at the end of the test Note must be taken that since the standpipe is not used during the setup, the value of d will then be equal to the value of D. The values of log K1 is then plotted against log time. 3.3.3.3 Stage 2 The Stage 2 of this test can be perform when the Stage 1 have been done. Make sure the water in the borehole from Stage 1 has fully infiltrated into the soil. The borehole is then extended to the specified depth using a smaller diameter hand-auger. The length of the extended borehole (L) depends on the geometry factor to be used. Values that are commonly used are 1.0D, 1.5D and 2.0D; where D is the diameter of the borehole casing (Daniel, 1989). In this project, the default length of the extended borehole used is 1.5D. Water was then introduced into the borehole. The Stage 2 test is then started. It is of the same procedure as the test made in Stage 1 where the rate of water flow into the soil in the borehole is measured with respect to time. As in Stage 1, the test will be terminated once the water in the borehole fully infiltrate into the soil. With reference to Figure 2.7(b), the horizontal limiting conductivity, K2 can then be calculated using the following Hvorslevs equation (Daniel, 1989): (Equation 22) where; As in Stage 1, since no standpipe is used during the setup, the value of d will be equal to the value of D. The values of log K2 is then plotted against log time. 3.4 Field test of the modified TSB test / Boutwell Permeameter 3.4.1 Theory The basic idea of the modified TSB test/Boutwell permeameter setup was to obtain a more simple installation setup which can be easily and quickly installed in shallow boreholes for subsequent testing. The standard TSB test/Boutwell permeameter setup, although proven was effective in measuring the hydraulic conductivity of the tested soil, is considered to be of much works. This is mainly because the person who is doing the test have to drill the same borehole twice; once during the Stage 1 and once during the Stage 2. The modified setup of the TSB test/Boutwell permeameter suggested in this report involved only involved a single drilling procedure. The detail setup procedure will be discussed in section 3.5.3. 3.4.2 Equipments All the equipments used for the modified setup was similar to the standard setup. The only different equipment used in the modified setup was the borehole casing. In the standard setup, only one plastic PVC tubing (not capped both ends) was used. In the modified setup, two plastic PVC tubing (not capped both ends) of different diameter sizes were used. The diameter of the bigger pipe and smaller pipe is 5.0cm and 4.5cm respectively. Both the tubes are connected together in a way that it can be adjusted to two different lengths by sliding the smaller size diameter tube into the larger size diameter tube. The connection between the two pipes is ensured to be watertight so that water will not leak through the pipe during the testing stage. An O-Ring (Figure 3.2) was used for this purpose. The O-Ring is inserted in between the bigger size pipe and the smaller size pipe. Figure 3.2 Different sizes of O-Ring (supaseal.co.uk) 3.4.3 Procedures 3.4.3.1 Borehole and casing setup The drilling borehole and casing setup procedure in the modified setup was very similar to the standard setup. The drilling procedure must be done in the direction perpendicular to the ground surface. No drilling fluid was used during the drilling. In the modified setup, the borehole was drilled to a much deeper depth compare to the standard setup. The bottom of the borehole is then ream and smoothed using a flat auger. The bottom of the borehole must be smooth and flat to ensure proper measurement during the test. The modified casing is then inserted into the borehole after the borehole preparation was done. The casing was set parallel to the axis of the borehole and centered by hand. The maximum length of the modified casing is used. The depth from the top and the bottom of the casing is then measured. For the modified TSB/Boutwell permeameter setup, two sealing methods are used. From the bottom of the larger pipe to half of its length, a geo-synthetic clay liner is used. For the remaining half of the larger pipe length a mixture of bentonite powder and water is used. This is illustrated in Figure 3.3 below. Before inserting the bentonite into the borehole, the geo-synthetic liner must first be wetted. Once inserted the bentonite is then let to dry. The hydration period take atleast 12 hours. The top of the casing is covered to prevent any rainfall, surface runoff or other debris to enter the borehole. Figure 3.3 Schematic illustration of Stage 1 of the modified TSB/Boutwell Permeameter test setup Bentonite Geo-synthetic clay liner 4.5cm Ãâââ¬Å¾ pipe 5.0cm Ãâââ¬Å¾ pipe 3.4.3.2 Stage 1 Figure 3.3 is a schematic illustration of the Stage 1 of the modified TSB/Boutwell Permeameter test setup. Water is first introduced into the casing slowly to prevent any damage to the soil exposed at the bottom of the casing. Once the water inside the casing is almost full, the water depth is noted. This is the initial water depth. The Stage 1 can now be started. The idea of measuring the rate in which the water level in the casing dropped is still the same as in the standard TSB/Boutwell permeameter test setup. A datalogger is used to measure the water depth in the borehole. The test is terminated once the water in the casing fully infiltrated into the soil. The data from the datalogger is then used to calculate the vertical limiting conductivity, K1 of the soil using Equation 21. The values of log K1 is then plotted against log time. 3.4.3.3 Stage 2 In stage 2 of the standard setup, the borehole is extended using the hand auger. However, in the modified setup instead of drilling the borehole, the smaller diameter tube is raised up by sliding it upward for approximately 1.5 times the diameter of the larger pipe. Since the diameter of the smaller pipe is 5.0cm, therefore the length L will be approximately 7.5cm. The smaller pipe is then slide 7.5cm upward. This will then creates a similar scenario as in the Stage 2 of the standard setup with the extension of the borehole. Figure 3.4 illustrates the Stage 2 of the modified TSB/Boutwell permeameter test setup. Figure 3.4 Schematic illustration of Stage 2 of the modified TSB/Boutwell Permeameter test setup 1.5 x 5.0cm à ¢Ã¢â¬ °Ãâ 7.5cm Geo-synthetic clay liner Bentonite 5.0cm diameter pipe 4.5cm diameter pipe Water is then introduced slowly into the casing. The initial water depth inside the casing is noted. It is the same procedure as the test made in Stage 1 where the measurement of the rate of water level dropped in the casing with respect to time is recorded. The only different factor was that both the horizontal and the vertical hydraulic conductivity will take effect. The Stage 2 test is terminated once the water has fully infiltrated into the soil. The data from the datalogger is then used to calculate the horizontal limiting conductivity, K2 of the soil using Equation 22. The values of log K2 is then plotted against log time. 3.5 Calculating horizontal and vertical hydraulic conductivity The horizontal and vertical hydraulic conductivity, Kh and Kv respectively, of the tested soil can be calculated from the limiting hydraulic conductivity values of K1 and K2. However, the anisotropy condition of soil must first be taken into account when calculating Kv and Kh by relating the ratio K2/K1 to the degree of anisotropy, m. A value of m must first be selected, where m is defined as follow: (Equation 23) The corresponding value of K2/K1 is then calculated by using the following equation: (Equation 24) Values of K2/K1 are plotted against values of m and L/D and are shown in Figure 3.5 (Daniel, 1989). The value of m that corresponds to the actual K2/K1 value can be determined from this graph. Once the value of m is obtained, the values of Kh and Kv can then be calculated using the following expressions: (Equation 25) (Equation 26) Figure 3.5 3.6 Particle Size Analysis 3.6.1 Theory Particle size analysis, as mention earlier, is the common method practiced to classify the physical properties of the tested soil. There is a very wide range of particle sizes that can be encountered in soil. The main purpose of performing the particle sieve analysis is to define the particle size distributions of the soil. In addition, a number of engineering properties such as permeability, frost, susceptibility and compressibility are related directly or indirectly to particle size characteristics (Whitlow, 2001). There are many ways in which soil analysis can be done. However, the most common and cheapest method is using the sieve analysis. In the case of coarse soil, where the fine particles have been removed or were absent, a dry sieve analysis is done. Here a representative amount of soil sample is passed through a series of standard size sieves arranged in descending order. The weight of soil retained on each individual sieve is determined and the cumulative percentage of the sub-sample weight passing each sieve is calculated. In the case of the soil sample contains fine particles, a wet sieving is first carried out to remove these. Sedimentation test using hydrometer can be done to further classify the particle size distribution in the fine particle fraction. 3.6.2 Equipments Listed below are all the equipments used during the particle sieve analysis. Hydrometer test: Hydrometer Water bath Weighing machine 63ÃŽà ¼m sieve 1000ml measuring cylinder Conical flask Stopwatch Dry sieve analysis: Series of different sizes sieve Weighing machine readable to 0.1g Automatic shaker 3.6.3 Procedures 3.6.3.1 Hydrometer test There are several steps required to be done first before actually doing the hydrometer test. The sample is first dried oven at 105-110C for a day. Once the sample is dried, take a mass of the dried sample and record the mass. The weight sample is then mixed with 100ml of sodium hexametaphosphate solution. This solution can be prepared by dissolving 33g of sodium hexametaphosphate and 7g of anhydrous sodium carbonate in distilled water to make 1L of the solution (BS 1377-2, 1990). The purpose of mixing the sample and the solution is to break down the bonding between the different types of soil in a sample. The amount of sample to be mix with the solution depends on the type of the soil. For sandy soil a mass of 100g of the sample is appropriate. For silty and clayey soil, a mass of 50g and 30g respectively are adequate (BS 1377-2, 1990). Once the sample is mixed with the solution, it is left for another day. The next step is to wet sieve the sample through a standard 63ÃŽà ¼m sieve. The sample is put into a 1000ml measuring cylinder through a 63ÃŽà ¼m sieve. The particles that passed through the 63ÃŽà ¼m sieve will be retained in the cylinder. A conical flask is used to ensure all the particles passing through the 63ÃŽà ¼m sieve will be retained in the cylinder. Water is then added into the cylinder until it reaches the 1000ml graduation mark. The cylinder is then put into the water bath and left for a day. This is to ensure no temperature variation for testing multiple samples. The particles that are retained in the 63ÃŽà ¼m sieve will be oven dried again for a day at 105-110C and will be subjected to dry sieve analysis. Before starting the hydrometer test, the sample in the cylinder is shocks thoroughly making sure no particles are left settling on the bottom of the cylinder. After shaking the cylinder, immediately put the cylinder back into the water bath. At the same instant start the stopwatch and the test is started. Put the hydrometer into the cylinder and record the hydrometer reading at the upper rim of the meniscus. Readings are taken at 0.5min, 1 min, 2min, 4min, 8min, 15min, 30min, 1hr, 2hrs, 4hrs, 8hrs and 24hrs after the start of the test. 3.6.3.2 Dry sieve analysis For the particles that are retained at the 63ÃŽà ¼m sieve during the wet sieve, it is subjected to dry sieve analysis. The particles are first weight after they are dried oven. Record the mass of the retained particles. The particles are then passed through a series of standard size sieve arranged in descending order. For this test sieves of size 5mm, 3.35mm, 2.36mm, 1.18mm, 0.6mm, 0.425mm, 0.3mm, 0.212mm, 0.15mm, 0.063mm and 0.00mm are used. The particles inside the series of sieve are then shock for about 10-15mins using an automatic shaker. Record the mass of the particles that is retained on each sieve. The data from both the hydrometer test and the dry sieve analysis are then used to define the particle size distribution of the sample. 3.6.4 Calculating hydraulic conductivity The hydraulic conductivity of the soil can be calculated once the particle size distribution is defined. From the particle size distribution, take the sizes of the particle that correspond to d10 and d60. These two values are then put into Equation 14 to calculate the coefficient of grain uniformity U. The porosity n of the soil can be calculated by empirical relationship with U (Equation 13). For the purpose of comparison, different empirical equations are used to calculate the hydraulic conductivity of the tested soil. Below are all the empirical equations used: Hazens equation (Equation 8) Kozeny-Carmans equation (Equation 9) Breyers equation (Equation 10) Slitchers equation (Equation 11) The values of n, d10 and kinematic viscosity v are inserted into the above empirical equations to calculate the hydraulic conductivity of the tested soil. Chapter 4 Results 4.1 Borehole locations A total of 6 boreholes are installed during the project; three boreholes using the standard TSB/Boutwell permeameter setup and three boreholes using the modified setup. For the standard setup, the boreholes are numbered BH1, BH2 and BH5. For the modified setup, the boreholes are numbered as BH3, BH4 and BH6. The locations of each borehole are shown in Figure 4.1 below. The red circles indicate the borehole with the standard setup whereas the yellow triangles indicate the boreholes with modified setup. The results from all the tests; both from field and laboratory test will be included in the following sub section. BH1 BH5 BH4 BH6 BH2 BH3 Figure 4.1 Locations of the boreholes (Google Map) 4.2 General description of the soil The maximum depth of the borehole used in the test is 1.5m. For the first 0.4m depth, the soil consists of dark brown colour soil. For the remaining of the depth to 1.5m, the soil is reddish-brown in colour predominantly sand and silt. This is as expected for man-made fill since sand is one of the most abundance soils in the on the Earth. This is common for all the boreholes on the site. Small gravels are found occasionally at different depth in all the boreholes. The average soil description of all the boreholes is shown in Figure 4.2 below. Figure 4.2 Average soil description of the site 0.4m 1.3 m 1.5 m Top soil. Dark brown in colour. Consist mainly of sand and some small gravel. Reddish-brown soil. Mixture of sand and silt. Silty sand. Reddish-brown soil. Silty sand with a very little amount of clay. 4.3 Standard TSB test/Boutwell Permeameter All the results from the field and laboratory results for the standard TSB/Boutwell permeameter test will be presented in this sub-section. Refer to Appendix for the full data on the result for both field and laboratory tests. For the field TSB/Boutwell permeameter test, all the measurements were taken automatically using the datalogger.. 4.3.1 Field test The summary of all the results done with the standard setup, obtained from the field test, is given in Table 2. More detailed results from the field test is given in the following sub-section. Table 2 Summary of the field standard TSB/Boutwell permeameter test BH Test Average K1 (m/s) Average K2 (m/s) m Kh (m/s) Kv (m/s) 1 1 1.35 x 10-6 5.78 x 10-7 2 7.60 x 10-7 6.67 x 10-7 3 6.02 x 10-7 0.705 4.8 x 10-7 9.66 x10-7 2 1 9.55 x 10-6 2.42 x 10-6 2 5.06 x 10-6 2.29 x 10-6 3 5.90 x 10-6 2.53 x 10-6 4 1 2.27 x 10-7 2.27 x 10-6 2 5.97 x 10-6 2.55 x 10-6 3 5.16 x 10-6 2.29 x 10-6 4.3.1.1 Stage 1 The result of Stage 1 for all the three boreholes with the standard TSB/Boutwell permeameter setup is shown in the following figure. Figure 4.3 shows the value of log K1 (m/s) plotted against time (min) for; (a) BH1, (b) BH2 and (c) BH4. One similar pattern can be seen when comparing the all the tests within one borehole with the other borehole; the result for Test 1 for each borehole is either lesser or higher than the result for Test 2 and 3 by approximately by half to one order of magnitude. However, the result for Test 2 and 3 for the three boreholes indicate a similar pattern. The values of K1, with respect to time, for both Test 2 and 3 in each borehole are approximately the same. In BH1, the duration of the test for Test 1 is much less compared to Test 2 and Test 3. However, the pattern of the three graphs indicates a similar trend. The average K1 value for BH1 was determine using the data range from t=80 to t=120 minutes for Test 1 and from t=150 to t=200 minutes for Test 2 and 3. In BH2, for the first 20 minutes, all the three tests show a similar pattern. This is shown in Figure 4.3(b). However, in Test 1, the K1 values start to increase after t=20 minutes. For Test 2 and 3, the K1 values only start to increase after t=80 minutes. The average K1 value for BH2 was determine using the data range from t=40 to t=100 minutes for Test 1 and from t=40 to t=130 minutes for Test 2 and 3. In BH4 (Figure 4.3(a)), there is a very large difference between the graphs of Test 1 and both Test 2 and 3. The graphs for Test 2 nd 3 are almost identical. The average K1 value for BH2 was determine using the data range from t=20 to t=35 minutes for Test 1 and from t=30 to t=55 minutes for both Test 2 and 3. 4.3.1.2 Stage 2 The result from Stage 2 of the standard TSB/Boutwell permeameter test is shown in Figure below. In Stage 2, the graphs for all the tests within one borehole show a similar pattern. For BH1 only two tests were conducted. Three tests were conducted for both BH2 and BH4. In BH1, both the graphs of Test 1 and 2 indicate a similar pattern. This is shown in Figure 4.4(a). There is a sharp drop of K2 value at the start of Test 2. However, the values of K2 for both tests are increasing from the start of the tests towards the end. The average K2 value for BH1 was determine using the data range from t=150 to t=225 minutes. (a) BH1 (b) BH2 (c) BH4 Figure 4.3 Standard TSB/Boutwell permeameter: log K1 against time (a) BH1 (b) BH2 (c) BH4 Figure 4.4 Standard TSB/Boutwell permeameter: log K2 against time (a) BH1 (b) BH2 (c) BH4 (a) BH1 (b) BH2 (c) BH4 Figure 4.4(b) show the results for BH2. Three tests were conducted. For the first 70 minutes of the tests, the values of K2 for all the three tests were decreasing. The values of K2 then start increasing after that time until it reach approximately the 120 minutes time. The K2values than start to decrease again after that. This can be seen for all the three tests. The average K2 value for all the three tests in BH2 was determine using the data range from t=50 to t=80 minutes. Three tests were also conducted in BH4. As can be seen in Figure 4.4(c), the graph patterns for the three tests are almost the same. However, in Test 3, there is a sharp fall of K2 value between t=60 and t=70 minutes. The average K2 value for all the three tests in BH4 was determine using the data range from t=20 to t=60 minutes. 4.3.1.3 Calculation of m, Kh and Kv From the average value of K1and K2, the value of degree of anisotropy (m) is calculated using Equation 24. Once the value of m is calculated, the value of Khand Kv using Equation 25 and 26 respectively. Table 3 below shows the values of m, Kh and Kv obtained from BH1, BH2 and BH4.
Monday, May 18, 2020
Ap World Dbq 2004 - 772 Words
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Wednesday, May 6, 2020
John Wayne Gacy s Life - 1267 Words
John Wayne Gacy was born to a typical Chicago blue collar couple. His father was a World War I veteran who worked as a machinist and his mother was a homemaker. He was the only son of the three children born into the Gacy family. As an adolescent Gacy did not possess the typical attributes of the ââ¬Å"popular crowdâ⬠. He was over-weight, and un-athletic and what some would describe as ââ¬Å"A Mamas Boyâ⬠. Though he tried, Gacy could not cultivate much of a positive relationship with his father who is said to have been a physically and verbally abusive alcoholic. As with many sexual sadists who go on to become serial killers, Gacy claimed that he was molested as a child by a family friend. As Gacy got older the verbal abuse from his father continued. Eventually Gacy fled to Nevada where he worked as a funeral attendant. One night Gacy climbed into the coffin of a teenage boy and proceeded to embrace the corpse. Gacy expressed that he was so shocked by his actions that he returned to the home of his father afterwards. Gacy eventually went on to become a successful business man, married, moved to Iowa and had two children, finally earning the acknowledgement he had craved from his father as an adolescent. Gacy made advances at many of his male teenage employees during this time, perhaps foreshadowing his later victimology. Gacys criminal double life truly began at the end of the summer of 1967. Gacy successfully sexually assaulted many youths using tactics such as blackmail, trickery,Show MoreRelatedJohn Stanley Gacy, A Engineer And World War I Veteran1231 Words à |à 5 PagesMarion Elaine Robinson, a pharmacist, and John Stanley Gacy, a mechanic and World War I veteran, were married on January 7, 1939. On March 17, 1942, the couple gave birth to their second child, and only son, John Wayne Gacy in Edgewater Hospital, Chicago Illinois. Gacy was reportedly born with a congenital heart defect, an enlarged heart. John Sr. suffered with severe alcoholism, believed to stem from his military service in World War I. As a toddler, Gacy watched his father physically abuse his motherRead MoreIdentifiable Criminal Behavior : Modus Operandi And Signature964 Words à |à 4 PagesOperandi and Signature when committing and completing their criminal act. Letââ¬â¢s take a look into the infamous serial killer case of ââ¬Å"John Wayne Gacyâ⬠(the killer clown) and make a determination to what his (MO) was. Surly one would automatically assume that John Wayne Gacy (MO) was the use of a clown custom this is not the case at all. The name the killer clown came from Gacy passion for dress up in a clown custom to entertain children at celebratory events this was not his primary Modus Operandi thisRead MoreEssay On The Killer Gangster1676 Words à |à 7 PagesIntroduction: Criminal Case Facts John Wayne Gacy, also known as ââ¬Å"the Killer Clown,â⬠was 36 years old and living in Des Plaines, Illinois when he was apprehended by police in 1978. By then, Gacy had murdered 33 young men and boys. He was originally arrested on a drug charge, when further investigation of his home, due to the connection that he had to several missing young men, revealed to investigators the horrible contents of the crawlspace underneath his home (Crime Stories, 1999). He was thenRead MoreBiography of John Wayne Gacy Essay1482 Words à |à 6 PagesBiography of John Wayne Gacy One of the most horrendous serial killers in modern history would have to be John Wayne Gacy, Jr. He was the second of three children and born in 1942. He lived in Chicago and attended catholic schools, and wasnt a very popular boy in school. Gacy seemed to live a very normal childhood, with exception to his relationship with his father, and series of accidents that effected him. No one could have known what the future held for John, not even his father. When Gacy was elevenRead MoreA Brief Biography of John Wayne Gacy1417 Words à |à 6 PagesJohn Wayne Gacy was a business man a family man and a man who everyone depended on, but he was responsible for over 33 killings of young boys. Gacyââ¬â¢s early childhood might be a big factor of why he would do such things since he was abused mentally and physically. But after he removed himself from the bad situations and left home, Gacy made his own decision to start killing and raping young boys. John Wayne Gacy was born on March 17, 1942. Gacy had an alcoholic father that would torture him mentallyRead More They Call Him Mr. Gacy Essay2347 Words à |à 10 Pagesanalyses of the life and deeds of American serial killer John Wayne Gacy, who is thought to have sexually assaulted and murdered 32 boys between 1976 and his arrest in December 1978 (Cahill, 1978; Gacy, 1989). This profile of Gacy compiles a birth-to-death chronology of events and activities that may lend insight to the personality of a habitual liar, model citizen, and serial murderer. Born to Marion Elaine Robinson Gacy and John Hanely Gacy on St. Patricks Day in 1942, John Wayne Gacy was the secondRead MoreSerial Killers: Are They Born Or Made?. There Are Multiple1230 Words à |à 5 Pagessee other people suffer. As this brain abnormality in most cases of psychopathic criminals is not abruptly acquired, there is a good reason to think that it s grounded in the psychopath s DNA. This would be an example of how genetics can take control of their chaotic ways. According to former chief of the FBI s Elite Serial Crime Unit, John Douglas, ââ¬Å"There are 25 to 50 active serial killers in the United States at any given moment. Today. Right nowâ⬠(Moss). Those numbers may seem small since thereRead MoreSerial Killers Essay985 Words à |à 4 Pagesis, John Wayne Gacy, During Gacys late teens, he had some trouble with his father, although relations with his mother and sisters were very strong. John Wayne Gacy, Sr., was an abusive alcoholic who physically abused his wife and verbally assaulted his children. Although John Sr. was an unpleasant individual, young Gacy deeply loved his father and wanted desperately to gain his devotion and attention. However, his father would drink himself stupid and physically and verbally abuse young Gacy. HeRead MoreBiography Of John Wayne Gacy Doesn t Be An Ordinary Family1006 Words à |à 5 Pagesended up being a successful business person, due to his flair towards sales. Gacy also played the role of a responsible community member, throwing barbecues for his neighbors and dressing up as a clown. To cheer up sick children in the hospital. So what triggered his desire to kill? Could it be the fact that he adored a father that was a violent alcoholic, who didnââ¬â¢t appreciate to be around people, used to beat young Gacy and call him names? Or can it be due to his numerous failures of going up onRead MoreSerial Murders Are Not Indigenous, Nor Are They A New Phenomenon1157 Words à |à 5 Pagesmotive besides personal gratification for the killer (Johnston). Ambiguous repetitive murders are often the hardest cases to solve and murder analysts continue to search for explanations of these actions. Crime analyst William Anderson states that it s believed that a variety of biological and social factors correlate to such heinous acts (Anderson). Key traits that are common among serial killers include: social patterns, negative childhood experiences, and neurological abnormalities. Neurological
Digital Transformations in Management of Cyber â⬠Free Samples
Question: Discuss about the Digital Transformations in Management of Cyber. Answer: Introduction: The rapid growth of population has resulted in the advent of many new latest and innovative machines, which has revolutionized the business of the companies and organizations. This is in terms of the need for upgrading the standard and quality of the existing business services. However, with the advent of new machines, there hasnt been recruitment and selection of the personnel (Park et al. 2013). Even if the recruitment and selection process has been executed, the hired candidates are not provided with the necessary trainings regarding the efficient and judicious utilizations of the machines. Herein, the profession of system engineering and its diversification is nullified. These aspects have delayed the completion of the important projects, staining the stability in the relationship between the company and their stakeholders and shareholders. This hostile relationship has added vulnerability in the market position of companies and organizations (Haimes 2015). Moreover, this situati on has affected the mindset of the stakeholders and shareholders. As a matter of specification, possession of inadequate skills by the employees has compelled the managers to encounter situations like inability to complete the allocated tasks within the stipulated deadlines, indulging in scandalous situations among others. These situations stain the reputation of the company. Herein, the role of the managers is questioned in terms of regulating the performance of the employees. This interrogative tone contradicts the usual conventions of the managerial roles in terms of understanding the customers and clients prior to the execution of the business activities (Chang 2016). When it comes to the management of the technological usage of the employees, lackadaisical attitude contradicts the designation of the managers. One of the major concerns, due to the possession of inadequate technological skills is the loss of trust, loyalty and dependence over the managers and the senior officers for the employees. This has resulted in the difference of opinions, conflicts, discriminations and harassments. More specifically, lack of adequate technological skills has escalated the cyber crimes, which has compelled the companies and organizations to lose important official data. Along with this, unwanted emails and invitations have aggravated the complexities of the companies in terms of maintaining the privacy, security and safety of the customers profile. These have compelled the company personnel to receive large amount of complaints from the clients (Kerzner 2013). In view of the cyber crimes, the lack of adequate technological skills is very dangerous in terms of the future of the companies and organizations. Theoretical approach to cyber crimes When a problem occurs, it needs to be viewed from different angles for achieving effective solutions. Herein lay the appropriateness of four levels of thinking pyramid. Countering this, thinking is one of the major elements of the behavioral science applied by the individuals. In view of this connotation, there are six levels of thinking- knowledge, comprehension, application, analysis, synthesis and evaluation (Buede and Miller 2016). Optimizing the levels, the six levels can be contracted into four levels- events, patterns, system structures and mental models. Thinking the cyber crimes as a problem reflects the consciousness of the personnel towards the safety, security and privacy of the customers. On the contrary, not thinking as a problem aggravates the complexities of the personnel in terms of ensuring the wellbeing of the customers. Both of these aspects thinking and not thinking are behavioral tendencies exposed by the humans towards the issues, which they encounter in their lives (Wasson 2015). Possessing adequate knowledge about the problems of cyber crimes is also an aspect of behavior in case of the company personnel. Lagging behind the others in terms of the harmful effects of cyber crimes attaches negative connotation to the behavior of the personnel. This negativity results in difficulty in terms of gathering effective solutions for the technological issues and challenges. Herein the thought of transformations in business is a mere and distant hope. On the other hand, conducting open forums and discussions assists the personnel to gather many solutions for the encountered problems (Kerzner 2013). In this, lack of adequate knowledge about the problems the clients are facing due to the cyber crimes proves fatal for the maintaining the efficiency within the marketing activities. Collecting various solutions enhances the perspectives of the company personnel, which is assistance in terms of analyzing the exposed performance. Attaching evaluation within this is an extension in the analysis, which brings the major drawbacks to the forefront. Synthesis aligns with the approach of the personnel towards the conclusion regarding mitigating the intensity of the cyber crimes. Delving deep into the aspect, synthesis can be considered as the product of the evaluation and analysis (Chang 2016). Viewing it from other perspective, evaluation and analysis of the issues, which the contemporary brands are encountering enriches the preconceived knowledge of the personnel towards cyber crimes. Herein lay the appropriateness of market research and survey, which makes the company aware of the steps necessary for solving the problem. Maintaining consistency in the execution of market survey and research would enable the company personnel to comprehend solutions to the clients in terms of mitigating the intensity of the harmful effects, which have resulted due to the cyber crimes (Morse, Babcock and Murthy 2014). Emerging successful in this task upgrades the personality of the personnel, especially the managers in terms of regulating the performance of the employees. Pondering upon the contracted levels, the first level is the events. Here, adequate knowledge, skills and expertise is needed to identify the potential issues, which has stalled the productivity of the companies and organizations. This identification makes the solution process easier; saving a lot of time, which if devoted to the execution of the other tasks would systematize the business activities. The second level is the patters. This can be related with the stage of application, where the personnel need to enhance their clarity in terms of the most appropriate solution towards the problem of cyber crime (Bahr 2014). This application would make the personnel aware of the pattern of solutions, which possess flexibility towards solving the problem of cyber crimes in an efficient and effective manner. Application of the gathered solutions makes the personnel aware of the systems, which are needed for safeguarding the clients from the dangers of cyber crimes. Creating concrete structures for overcoming the challenges of cyber crime supports the personnel as to whether they are progressing on the right track. Planning in this direction is of utmost importance in terms of assessing the proposed activities in comparison to the identified and the specified requirements. Clarity in these aspects leads the personnel towards the selection of the models, which would alter the predicament of the companies and organizations from the crisis phase (Peppard and Ward 2016). There are various models, which possess the flexibility to uplift the standards of the companies and organizations from the crisis of cyber crimes. Typical example in this direction is the Application Threat Modelling. Here, one of the major components is the study of the cyber crime attack surface. The model is viewed as a circular issue, where there are different phases of mitigating the intensity of the cyber crimes. The first phase is to analysis the attacks inflicted upon the company. This is done through the means of identifying the sources of attacks and their intensity. The second phase is the consideration of the use and misuse cases registered. This enhances the clarity of the personnel towards the intensity of the hazards, which the clients had to encounter. The third phase of this model is to analyze the type of the attack (Haimes 2015). Here ratings are used, which helps in determining the type of solution needed for the restoration of the lost justice and respect of the clients. The next phase initiates the security analysis. Architectural plans or DFDs are constructed by the personnel prior to the initiation of the business activities. The draft of these plans is sent to the higher authorities for their approval in terms of the undertaken steps till this phase. The written approval is preserved by the personnel in order to avert the indulgence into illegal activities (Park et al. 2013). As a sequential stage, the solution selected is designed for the understanding of the personnel and the clients. After gaining the approval of the stakeholders and shareholders, the personnel move on to the application of risk mitigation strategies. Here templates and checklists are used for solving the issues in an efficient and effective manner. The next stage is to indulge in partnerships with the government officials in terms of gaining awareness of the legislative standards. Violation or gaps in this direction attaches negativity in the business operations. After receiving the standards, the source of these standards are codified and sent to the managers and the directors so that no third party gets to know the secret code (Galliers and Leidner 2014). The transmission is thoroughly monitored by the officials until it reaches to the receiver. Herein lay the appropriateness of penetration testing, which helps the personnel to assess the avenues, which are opened before them in ter ms of ensuring the safety and security of the clients. After all these, cyber crime intelligence phase comes, where the personnel think of producing artificial intelligence tools, which would scan the presence of malfunctions, virus and hacker intervention. Recommendations to mitigate the problem of cyber crime The proposed business model possesses enough flexibility to mitigate the crisis of cyber crime. However, certain recommendations would alter the plight of the companies and organizations from the crisis phase. One of the most important recommendations is the adoption of efficient security software (Buede and Miller 2016). Typical example in this direction is Quick Heal. For this, market research would be an efficient option. Search engine optimization within this would take the personnel directly to the needed information. Along with this, provision of training to the employees regarding the efficient and judicious use of latest technological machines would enhance their preconceived skills, expertise and knowledge. Including the various dynamics of the different machines would enhance the clarity of the employees regarding their operations. Increasing the frequency of these training sessions would help the employees to have an easy grasp over the digital issues and their impact on the business services. Hiring IT experts would bring to the forefront the presence of malfunctions, virus attacks and the hacker interventions. Within this, frequency is of utmost importance in terms of averting the risks of possessing defective machines, which stall the productivity and efficiency of the business activities at the time of emergencies (Galliers and Leidner 2014). Frequent evaluation of the revenue generated and their sources would make the personnel aware of the major drawbacks. Spontaneity in modification of these drawbacks would upgrade the standard and quality of the business, especially the ones carried out online. This spontaneity would pave the way of foreign market penetration for the companies and organizations. This penetration, in turn, would result in the advent of technological advancement in the workplace (Wasson 2015). This can be achieved only the companies and organizations abide by the IT legislations such as Computer Misuse Act and Data Protection Act (1998) among others. References Bahr, N.J., 2014.System safety engineering and risk assessment: a practical approach. CRC Press. Buede, D.M. and Miller, W.D., 2016.The engineering design of systems: models and methods. John Wiley Sons. Chang, J.F., 2016.Business process management systems: strategy and implementation. CRC Press. Galliers, R.D. and Leidner, D.E. eds., 2014.Strategic information management: challenges and strategies in managing information systems. Routledge. Haimes, Y.Y., 2015.Risk modeling, assessment, and management. John Wiley Sons. Kerzner, H., 2013.Project management: a systems approach to planning, scheduling, and controlling. John Wiley Sons. Morse, L.C., Babcock, D.L. and Murthy, M., 2014.Managing engineering and technology. Pearson. Park, J., Seager, T.P., Rao, P.S.C., Convertino, M. and Linkov, I., 2013. Integrating risk and resilience approaches to catastrophe management in engineering systems.Risk Analysis,33(3), pp.356-367. Peppard, J. and Ward, J., 2016.The strategic management of information systems: Building a digital strategy. John Wiley Sons. Wasson, C.S., 2015.System engineering analysis, design, and development: Concepts, principles, and practices. John Wiley Sons.
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