No | Name | Rank | Photo | |
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10. | Daw Nu Nu Nge | Assistant Lecturer | nununge@bmwuni.edu.mm | |
11. | Daw Yin Zar Lin Tun | Assistant Lecturer | yinzar@bmwuni.edu.mm | |
12. | Daw Pan Myat Thu | Assistant Lecturer | panmyatthu@bmwuni.edu.mm | |
13. | Daw Thiri Aung | Assistant Lecturer | thiriaung@bmwuni.edu.mm | |
14. | Daw Su Mon Kyaw | Assistant Lecturer | sumonkyaw@bmwuni.edu.mm | |
15. | Daw Yamin Thant | Demonstrator | yaminthant@bmwuni.edu.mm |
No | AUTHOR | Research Name | Abstract | Journal Name, Vol.No, Date | ||
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1 | Dr Su Su Aung Associate Professor | Synthesis of Building Construction Material from Bamboo Leaves Ash | Bamboo usually grow mixed with other forest species and they form the undestroyed biomass in high forests. Bamboo leaves available in significant quantities and problems of disposal in rural areas are utilized as fuel in some regions. When burnt under controlled conditions, the bamboo leaves ash BLA obtained is essentially silica form which possesses highly pozzolanic and suitable for use in lime-pozzolana mixes and as Portland cement replacement material in construction work. Bamboo leaves collected from Thanlyin Township were used as raw material. The optimum condition for incineration temperature is 700 °C for two hours. The yield of bamboo leaves ash obtained at 700 °C is 29.18 %. The semi-quantitative assays of bamboo leaves ash indicated the relative percent composition of the presence of silicon 80.03 %, and other trace elements. Oxides of silicon (74.18%) was measured qualitatively by conventional chemical method..The pozzolanic activity of bamboo leaves ash at different incineration temperature was also determined by reaction with calcium hydroxide. Six blending ratio of bamboo leaves ash and cement, and five mixing of bamboo leaves ash and lime cement were used as experimental designs in testing the quality of blended cement. The mechanical strength such as compressive strength, tensile strength and transverse strength of each blending were measured and the quality evaluated. Mechanical strength of concrete increases with each addition of ash up to 30 %.The ash could possibly be blended up to half amount with ordinary Portland cement for concrete making. OPC blending with 30% BLA becomes affordable for people in rural areas. Adding a bamboo leaves ash, which combines with lime (by weight ratio of 1:1) in the presence of water can be used in strengthening of concrete work like rodent proof rice stores, drains in acidic soils and building construction. | Banmaw University Research Journal, 2018 October,Vol.9 No.1(Pg 56-65) | ||
2 | Dr Su Su Aung Associate Professor | Study on the Mechanical Properties of Chitosan Calcium Aleinate Membrane | The present study involves the preparation of membranes and investigation of the effect of alginate content, calcium ion content and chitosan content on the mechanical properties such as tensile strength, percent elongation at break, tear strength and thickness. From the experimental works, if the amount of alginate content were increased, the tensile strength and % elongation at break were increased. If the amount of calcium ion content were increased, the tensile strength and % elongation at break were also increased. Therefore the amount of alginate content influenced the tensile strength and percent elongation at break.. And also the amount of chitosan content influenced the tensile strength and % elongation at break. | Banmaw University Research Journal, 2019 June,Vol.10 No.1(Pg 130-140) | ||
3 | Dr Su Su Aung Associate Professor | Using of Rice Straw (Oryza Sativa L.) for Better Purposes Fabricating and Evaluating of Physical and Mechanical Properties of Fiberboard | This study investigated the preparation and characterization of rice straw (Oryza Sativa L.) fiberboard. The fiberboards were made by treated rice straw and different amounts adhesives urea-formaldehyde. These were manufactured using urea-formaldehyde adhesive. Fabrications of fiberboards were made by compressing molding method. The physicochemical properties of pre-treated rice straw were investigated. The physicomechanical properties of prepared fiberboards such as bending strength , impact , hardness, water absorption, thickness and density were determined. The prepared rice straw fiberboards (FBr1, FBr2, FBr3 and FBr 4) will also be characterized by modern techniques. Surface morphologies of pre-treated rice straw sample and prepared fiberboards will be analyzed by Microscope. | 1 st Myanmar International Science andCulture Conference 2019 , 2020 May, Vol.1, No.3(Pg 192-197) |
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4 | Dr Su Su Aung Associate Professor | Investigation of Physicochemical Properties on Composted Soil | This research work is concerned with the study on physicochemical properties of composted soil by using farm’s waste such as ( rice husk char and cow dung ). Soil sample was collected from Tharzee Village, Banmaw Township, Kachin State and all the farm’s waste were collected from Namphar Quarter, Banmaw Township Kachin State in December , 2017. The collected soil sample was composted with farm’s wastes in December, 2017 to April, 2018 under aerobic and anaerobic conditions. Some physicochemical properties of different soil samples were determined by instrumental, analytical, and titrimetric methods. Relative abundance of composted soil samples were determined according to the different interval of time by ED XRF analysis. And then the different nutritional values of composted soil samples were also investigated. According to the soil texture analysis, all the soil samples were loam types. By composting with farm’s waste, the pH, bulk density, moisture, humus and organic carbon were obtained the highest values under anaerobic condition during two months. They have no detectable toxic metals (As, Cd, Hg, etc) from all samples. The fertilization activities of composted soil samples were also determined by cultivation of Lettuce plant within two months. | 2 st International Conference on Bioeconomy 2019 , 2020 June, Vol.1, No.1(Pg 140-143) |
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5 | Dr Su Su Aung Associate Professor | Application of Corncob Powder Adsorbent for Removal of Heavy Metal Ions | The present research work is the preparation of corncob powder to be used as the effective sorbents for the removal of heavy metal lead and cadmium. The corncobs were collected from the Shwe Kyi Narr village, Banmaw Township in Kachin State. Thermal activation of corncob powder (80-mesh size) was prepared by heating process of 100◦C at 2 hr. The elemental content of corncob powder was determined by EDXRF analysis. The removal of heavy metal lead and cadmium from aqueous solution on thermal activated corncob powder were carried out by titrimetric method. The effects of sorption parameters (concentration of metal ions solution, contact time and sorbent dose) were investigated. For concentration effect, 100, 200, 300, 400, 500, and 600 mg L1 of each metal ions were used on sorbent dosage 0.50 g at 60 min contact time for shaking at 150 rpm . For contact time method, the initial concentration 300 mg L1 of each metal ions solution and sorbent dosage 0.50 g were used with various content time 15, 30, 45, 60, 75, 90 , 105, 120, and 135 min respectively. For dosage method, the amount of sorbents 0.25 g, 0.50 g, 0.75 g, 1.00 g , 1.25 g, and 1.50 g and initial concentration 300 mg L1 were used at 60 min contact time for shaking at 150 rpm . Sorption isotherm studies corresponded to Langmuir and Freundlich isotherms were used. And then, significant sorption parameters of these isotherms were also evaluated. Based on R2 values the Freundlich isotherm is more favorable and multilayer adsorption is possible. Based on the percent removal results, the sorption capacities of sorbent for the removal of lead are greater than that of cadmium. The kinetics of adsorption could be described using pseudo-first order and pseudo-second order kinetic model. In all cases, the kinetics follows the pseudo-second order rate equation. | Banmaw University Research Journal, 2020 June, Vol.11, No.1(Pg 130-143) | ||
6 | Dr Su Su Aung Associate Professor | A Study on the Biogas Production and Waste Recycling from Anaerobic Digestion of Farm'Wastes | The production of biogas from farm’s wastes such as vegetable wastes and cow dung were studied under anaerobic treatment. The vegetable wastes were collected from Namphar Quarter, Banmaw Township .And then, the cow dung was also collected from Kokkodaw Quarter, Banmaw Township, Kachin State. The production of biogas was carried out due to five different conditions using vegetable wastes and cow dung by means of anaerobic digestion within two months. Consequently, each residue after being produced biogas was converted into natural fertilizers. The fertilization activities of residue samples were investigated by standard methods. | Banmaw University Research Journal, 2020 June, Vol.11, No.2(Pg 126-134) | ||
7 | Dr Su Su Aung Associate Professor | Removal Properties of Heavy Metals from Tube well by Using Rice Husk Ash Alginate composite Beads | This investigation has shown that it is feasible to prepare effective rice husk ash-calcium alginate composite beads by using rice husk ash, sodium alginate and calcium chloride. Rice husk (Zeyar) was collected from Hlegu Township, Yangon Region. Physicochemical properties of rice husk ash were determined. The prepared rice husk ash-calcium alginate beads were used as an sorbent material for the removal of heavy metals such as lead, cadmium and zinc in tube well water (East Dagon Township Area). The effect of sorption parameters such as initial concentration, contact time and adsorbent dosage were investigated. The result indicates that rice husk ash-calcium alginate beads are an effective sorbent for removing heavy metals from tube well water. | University of Magway Research Journal, 2019 December, Vol- IX(Pg 191-199) | ||
8 | Dr Su Su Aung Associate Professor | Preparation and Characterization of Natural Fertilizer from Farm's Waste | Study on the some physicochemical properties of natural fertilizer by using farm’s waste (vegetables waste). All the farm’s waste were collected from Namphar Quarter, Banmaw Township, Kachin State, in the month of December, 2017. The collected samples were mixed December 2017 to April 2018 under aerobic condition S(I) and anaerobic condition S(II) .Some physicochemical properties of prepared natural fertilizers such as moisture, pH, bulk density, organic matter, carbon nitrogen ratio and nutrients content (total N, P and K) were determined by instrumental, analytical, and titrimetric methods. Generally, all the physicochemical properties of prepared natural fertilizer were found to be in the range of moisture 5.797% to 19.555%, pH 7.02 to7.09, bulk density 0.54 gcm-3 to 0.63 gcm-3, organic matter 42.56% to 68.69%, carbon nitrogen ratio 12.01 to21.07 and total nutrients, nitrogen 1.89% to 2.87%, phosphorous 0.04% to 0.878% and potassium 6.00% to 7.56% respectively. The elemental compositions of all samples were analyzed by ED XRF. They have no detectable toxic metals such as Cd, Zn, Hg, etc. And then, the fertilization activities of prepared samples were also determined by cultivation of Lettuce within two months. | Third Myanmar national Conference on Earth Science (MNCES 2019) Yadanabon University , 2019 November (Pg 1468-1472) | ||
9 | Dr Su Su Aung Associate Professor | Removal Properties of Heavy Metals from Tube well by Using Rice Husk Ash Alginate composite Beads | Removal of heavy metals from soil and bio fertilization activity of biochar (biomass): two organic residues rice husks from husker and bamboo leaves have been determined by using contaminated soils. These contaminated soil samples were collected from the Pagaye mining site Sc(I), Pagaye village Sc(II) and Battery service area from Weigyun Sc(III), Dawei township. The three contaminated soil samples and biochar (rice husks and bamboo leaves) were treated under a close atmosphere using plastic housing. Soils were incubated at 27C for three months. Physiochemical properties such as (moisture, pH, texture, organic carbon, humus) of contaminated soils and treated soils were determined and major nutrients contents (total N, available P and available K), exchangeable cations (K+, Ca2+ and Mg2+) were studied by using instrumental and analytical methods. Generally, it was found that moisture, pH, organic carbon and humus were improved in treated soils and nutrients and exchangeable cations: K+ and Ca2+ were also improved. Elemental compositions and heavy metals (Pb and Cd) in these soils were also determined with different interval of times by EDXRF and AAS methods. Both biochars can remove the toxic metals Pb and Cd in all the contaminated soil samples. In addition, it was carried out the comparison of the soil fertility on the contaminated and treated soils were carried out within one month. The soil fertility was also improved in the treated soil samples. | Journal of the Myanmar Academy of Arts and Science, 2020 July, Vol- XVIII,No.1C(Pg 95-105) | ||
10 | Dr Hla Hla Win | Purification and Characterization of Tyrosinase from Straw Mushroom, Volvarielia volvacea ( Bull. Ex Fr.) | Tyrosinase (monophenol, o-diphenol: oxygen oxidoreductase, EC(1.14.18.1) is a copper containing metalloenzyme distributed in a wide range of organisms, including bacteria, fungi, plants, insects, and other animals. It is a key enzyme in the process of melanin biosynthesis from L-tyrosine. In this research, tyrosinase from straw mushroom was isolated and purified by using successive ammonium sulphate precipitation and gel chromatographic (Sephadex G-100) techniques. Tyrosinase oxidized catechol to initially to orange compound benzoquinone that is converted to melanins as major product. The specific activity (relative purity) of the enzyme, increased about four folds from crude extracted to final purification step. The activity of purified tyrosinase was found to be137.50 EU per gram of mushroom. The purity of the enzyme was confirmed by non SDS-PAGE as a single band. By using non SDS-PAGE the molecular weight for tyrosinase was found as 114.815 Dalton. The enzyme properties (effect of enzyme concentrations, pH, temperature, enzyme specificity, reaction time) were determined. The optimum pH and temperature of the tyrosinase enzyme were found to be 7.0 (phosphate buffer) and 37˚C, respectively. The activation energy (Ea) of the tyrosinase-catalysed reaction was determined to be 4.0470 kcal mol-1and Arrhenius constant was 8.8247 x103. The enzyme specificity of the purified tyrosinase enzyme was studied by using various substrates such as catechol, hydroquinone, resorcinol, tyrosine and phenol. It was found that tyrosinase activity of the prepared enzyme mainly related with catechol and tyrosine and some extent to phenol. Therefore, the purified tyrosinase exhibits absolute specificity on catechol, tyrosine and phenol, not for hydroquinone and resorcinol. | Journal of the Myanmar Academy of Arts and Science, 2010 March, Vol.VIII, No.1(Pg 297-309) | ||
11 | Dr Hla Hla Win | Degradation of Phenol by Immobilized Tyrosinase Enzyme | Tyrosinase (EC 1.14.18.1) enzyme was extracted from straw mushroom (Volvariella volvacea) by using ammonium sulphate precipitation method and then chromatographic purification on crude tyrosinase enzyme was carried out using Sephadex G-100 gel. The relative purity of the enzyme (specific activity) increased about four folds from crude extract to final purification step. The immobilization of the purified tyrosinase was carried out by adsorption on alumina using acetone as an immobilization medium. Comparative studies of optimum temperature and optimum pH between the free and immobilized enzyme were carried out. There was no significant difference of optimum pH and temperature between immobilized and free one. The optimum pH and optimum temperature for immobilized and free tyrosinase enzyme were found to be 7.0 and 37oC, respectively. In this paper, phenol degradation catalyzed by immobilized tyrosinase was studied using model phenol solution. At first, wavelength of maximum absorption of phenol solution was investigated and λmax were found at 216 and 269 nm. The standard calibration curve was constructed using standard phenol solution (10, 20, 40, 60, 80 and 100 ppm). The straight line passed the origin and Beer’s law was obeyed. Although enzymatic reaction of dephenolization was relatively fast (51% phenol degradation for 2 hr), polymer precipitation of insoluble brown precipitate was much slower and was noticeable only after 7 hr degradation time. After 24 hr degradation time, 97.75% of phenol was degraded. | Journal of the Myanmar Academy of Arts and Science, 2013 March, Vol.XI, No.1(Pg 357-370) | ||
12 | Dr Hla Hla Win | A study on Antimicrobial Activity of Aloe vera ( L .)Burn. F. Local and Foreign Product | Aloe vera leaf gel is widely used as a traditional folk medicine for the treatment of different infectious diseases. In present study, the antimicrobial potential of different Aloe vera local and foreign products were determined against three gram-positive bacteria (B.subtitis, B.pumilus, and S.aureus), two gram-negative bacteria (E.coli and P.aeruginosa) and two fungi (A.niger and C.albicans).The ager well diffusion method was used to test the antimicrobial activity. The antimicrobial activity of vaseline shower, vaseline lotion, intimate lotion, mira facial foam, natural shampoo, palmolive shampoo and GC juice were tested against the selected strains. The standard chemotherapeutic agent ampicillin (10 μg mL-1) and ketoconazole (100 mg mL-1) were used to serve as control. Natural and palmolive shampoos showed moderate inhibition. The antimicrobial activity of vaseline shower gave the best result activity (15-20 mm) against tested strains (B.subtilis, B.pumilus, S.aureus, E.coli, P.aeruginosa, C.albicans, and A.niger) but the highest inhibition activity was shown against A.niger (24mm) for palmolive shampoo.The antimicrobial activity of GC juice was observed in P.aeruginosa (18 mm). However, the antimicrobial activity of vaseline and intimate lotions and mira facial foam were not shown against all tested strains. Aloe vera leaf gel is widely used as a traditional folk medicine for the treatment of different infectious diseases. In present study, the antimicrobial potential of different Aloe vera local and foreign products were determined against three gram-positive bacteria (B.subtitis, B.pumilus, and S.aureus), two gram-negative bacteria (E.coli and P.aeruginosa) and two fungi (A.niger and C.albicans).The ager well diffusion method was used to test the antimicrobial activity. The antimicrobial activity of vaseline shower, vaseline lotion, intimate lotion, mira facial foam, natural shampoo, palmolive shampoo and GC juice were tested against the selected strains. The standard chemotherapeutic agent ampicillin (10 μg mL-1) and ketoconazole (100 mg mL-1) were used to serve as control. Natural and palmolive shampoos showed moderate inhibition. The antimicrobial activity of vaseline shower gave the best result activity (15-20 mm) against tested strains (B.subtilis, B.pumilus, S.aureus, E.coli, P.aeruginosa, C.albicans, and A.niger) but the highest inhibition activity was shown against A.niger (24mm) for palmolive shampoo.The antimicrobial activity of GC juice was observed in P.aeruginosa (18 mm). However, the antimicrobial activity of vaseline and intimate lotions and mira facial foam were not shown against all tested strains. | Banmaw University Research Journal, 2018 October, Vol.IX(Pg 66-74) | ||
13 | Dr Kyi Kyi San | Preparation, Characterization and Properties of Kaolinite and Fly ash -based Geopolymers | Kaolinite and fly ash-based Geopolymer has been prepared by using different concentrations of NaOH at room temperature. The source materials, kaolinite clay minerals from Kyauktaga and Taungnauk (Kyaukpadaung Township) and fly ash samples from Cement Industries located at Pyin Oo Lwin and Tigyit were collected. The collected samples were also characterized by using SEM, EDXRF and XRD instrumental techniques according to the prescribed procedure. The prepared geopolymer samples were analyzed by conventional methods. The mineralogical and microstructural characteristics of Geopolymeric materials were studied by modern instrumental techniques such as SEM, EDXRF, XRD, FTIR and TG-DTA for explaining the changes in compressive strength of geopolymer samples. Moreover, some mechanical properties of the prepared geopolymers, such as setting time, compressive strength and tensile strength were also determined. Acid resistance test was conducted on prepared geopolymer by using solutions of 10% H2SO4 and 10% HNO3 up to a period of 24 weeks and evaluation of its resistance in terms of surface corrosion and changes in weight at regular intervals. | Journal of the Myanmar Academy of Arts and Science, 2013 March, Vol.XI, No.1(Pg 21-45) | ||
14 | Dr Kyi Kyi San | Immobilization and Removal of Toxic Metal ions by Kaolinite and Fly ash -based Geopolymers | Geopolymers are the synthetic analogues of natural zeolitic materials which are aluminosilicate materials. They can be used in the immobilization of heavy metal contaminants as well as in the structural products. Thus, the aim of this research work is to study the use of kaolinite and fly ash-based geopolymer to immobilize heavy and toxic metals in the application of the removal of toxic metals from contaminated wastewater and the extraction of heavy metals from their leached solutions. The characterization of kaolinite samples from Taungnauk and Kyauktaga and fly ash samples from industries located at Tigyit and Pyin Oo Lwin were carried out by using SEM, XRD, FTIR and TG-DTA instrumental techniques. Moreover, the chemical compositions of the samples were also analyzed by using standard conventional methods. The geopolymer materials were prepared by using different ratios of kaolinite and fly ash with different concentrations of NaOH at room temperature. These geopolymers were analyzed and characterized by modern instrumental techniques. Science research work concerns with the use of geopolymers for immobilization of heavy and toxic metals, the removal of toxic metal ions in wastewater samples from different industries by using prepared geopolymer samples (H1-H4), as well as the leaching properties of Pb, Cd and As loaded geopolymers (H1-H4) from the model solutions were studied. Among the four geopolymer samples, geopolymer sample (H1) was found to be the maximum leaching property (i.e., the immobilization efficiency exceeds 92.9% when Pb2+ ions contained in metal loaded geopolymer (H1). Moreover, the removal percents of Pb2+, Cd2+ and As3+ions from wastewater samples were found to be in the range of 67.5%, 59.5% and 52.5% for Textile Mill (Wundwin), whereas the removal percents of Pb2+ and As3+ions were 65.7% and 49.4% for Battery Industry (Shwe Pyi Thar) by using prepared geopolymer (H1).Thus the process of removal of the toxic metal ions from wastewater sample by kaolinite and fly ash-based geopolymers can be used as an effective alumino-silicate polymeric material in the treatment of industrial influents. | Journal of the Myanmar Academy of Arts and Science, 2014 March, Vol.XII, No.1(Pg 29-47) | ||
15 | Dr Kyi Kyi San | A Study on the Immobilization of Toxic Metal Ions by using Prepared Kaolinite and Fly Ash - based Geopolymers | Geopolymers are the synthetic analogues of natural zeolitic materials which are aluminosilicate materials. They can be used in the immobilization of heavy metal contaminants as well as in the structural products. Thus, the aim of this research work is to study the use of kaolinite and fly ash-based geopolymer to immobilize heavy and toxic metals in application of the removal of toxic metals from contaminated wastewater and the extraction of heavy metals from their leached solutions. The characterization of kaolinite samples from Taungnauk and Kyauktaga and fly ash samples from industries located at Tigyit and Pyin Oo Lwin were carried out by using EDXRF, SEM, XRD, FTIR and TG-DTA instrumental techniques. Moreover, the chemical compositions of the samples were also analyzed by using standard conventional methods. The geopolymer materials were prepared by using different ratios of kaolinite and fly ash with different concentrations of sodium hydroxide at room temperature. These geopolymer samples were analyzed and characterized by conventional methods and modern instrumental techniques such as EDXRF, SEM, XRD, FTIR and TG-DTA. Moreover, some mechanical properties of the prepared geopolymers, such as compressive strength and tensile strength were also carried out. Since this research work concerns with the use of geopolymers for immobilization of heavy and toxic metals, the removal of toxic metal ions in wastewater samples from different industries by using prepared geopolymer samples (H1-H4). Among the four geopolymer samples, geopolymer sample (H1) was found to be the maximum leaching property (i.e., the immobilization efficiency exceeds 92.9% when Pb2+ ions contained in metal loaded geopolymer (H1). Moreover, the removal percents of Pb2+, Cd2+ and As3+ions from wastewater samples were found to be in the range of 67.5%, 59.5% and 52.5% for Textile Mill (Wundwin), whereas the removal percents of Pb2+ and As3+ions were 65.7% and 49.4% for Battery Industry (Shwe Pyi Thar) by using prepared geopolymer (H1). Thus the process of removal of the toxic metal ions from wastewater sample by kaolinite and fly ash-based geopolymers can be used as an effective alumino-silicate polymeric material in the treatment of industrial influents. | Dagon University Research Journal, 2014 December, Vol.6(Pg 107-123) | ||
16 | Dr Kyi Kyi San | Chemical Analysis of Rainwater in Mohyin Township | The present work is concerned with the monthly investigation of physico-chemical characteristics of rainwater from Mohnyin Degree College in Mohnyin Township, Kachin state. The rainwatersamples were collected from rainy season (during the period of June to August, 2015). The physico-chemical properties of rainwater samples such as color, pH, turbidity, conductivity, hardness and alkalinity were investigated. The mineral contents of water samples were determined by Atomic Absorption Spectroscopy (AAS). Most of the methods used in the present investigation are based on standard methods of American Public Health Association and International Standards for Drinking Water of WHO (1968). According to these data, it was found that all values are within the standard levels. So, the quality of rainwater is satisfactory for drinking, domestic and further research work. | Mohnyin Degree Collede Research Journal, 2017 January, Vol.7(Pg 50-65) | ||
17 | Dr Kyi Kyi San | The Use of Moringa oleifera Lamk.( Dant-Da-Lun) Seed Powder as Natural Coagulant for Water Treatment | Myanmar has been facing considerable challenges in the management of the environment due to increasing domestic and foreign investments in the industrial and development sectors. Water pollution and management is one of the main concerns for the development and also environmental management. The present study was carried out to confirm the effectiveness of seed powder extracted from mature-dried Moringa oleifera seeds which are commonly available in most rural communities. The main objective of this work is to evaluate the efficiency of a natural coagulant from Moringa oleifera seeds in treating river water. During this study, surface water samples were collected for treatment by watery extract of air dried powdered Moringa oleifera seeds, resulting in an effective natural coagulant agent for highly turbid and untreated pathogenic water. Various doses of Moringa oleifera seed powdered extract viz. 60, 80 and 100 mg/L were taken and checked for the efficiency dose on raw water. After treatment of seed powder with water samples were analyzed for some physico-chemical parameters like pH, temperature, TDS, DO, hardness and conductivity. All parameters were reduced with increasing dose of 60, 80 and 100 mg/L seed powdered extract. Application of this low cost Moringa oleifera seeds is recommended for eco-friendly, nontoxic, simplified water treatment where rural and peri-urban people living in extreme poverty. | Banmaw University Research Journal, 2020 June, Vol.11, No.1(Pg 144-156) | ||
18 | Dr Kyi Kyi San | Characterization of Prepared Metakaolinite and Rice Husk Ash-based Geopolymer | Geopolymer, an inorganic polymer, is a class of three-dimensionally networked alumino-silicate materials, similar to natural zeolite minerals. Metakaolinite and rice husk ash-based geopolymer has been prepared by using the different concentration of NaOH at 200oC for 4 hours. The source materials, kaolinite clay minerals from Kyauktaga and Taungnauk (Kyaukpadaung Township) and rice husk ash sample from Paddy Grinding Mill, Seik Phyu were collected. The collected samples were also characterized by using EDXRF, SEM, XRD, FT-IR and TG-DTA instrumental techniques according to the catalogue procedure. According to EDXRF analysis, the silica (SiO2) and alumina (Al2O3) contents of Kyauktaga metakaolinite were found to be 57.773% and 35.756%, respectively. The silica (SiO2) content (70.360%) and the alumina (Al2O3) content (23.022%) were found to be in Taungnauk metakaolinite. The mineralogical and microstuctural characteristics of geopolymeric materials were studied by modern instrumental techniques such as EDXRF, SEM, XRD, FT-IR, and TG-DTA. The silica (SiO2) content in geopolymer sample was found to have highest percent (78.145%). Alumina (Al2O3) content was the second highest percent (16.175%) in geopolymer sample by EDXRF analysis. From the thermal analysis data, geopolymer sample was found to be the weight loss (19.452%). | Banmaw University Research Journal, 2020 June,Vol.11, No.2(Pg 135-147) | ||
19 | Daw Myint Myint Than | Study on Sorption Properties of Activated Biosorbents(Fishscale and Seashell) for the Removal of Anionic Surfactant | In this study, waste fishscale and seashell were used as biosorbents for the removal of surfactants from industrial wastewater. These biosorbents were collected from fish market in Pathein Township, Ayeyarwady Region. The selected samples were washed with distilled water for three times and were soaked in 3 % nitric acid for 24 h and then were washed again with distilled water until pH 7 and dried in an oven at 105˚C and were made to powder form. The physiocochemical properties such asmoisture content, bulk density and pH of raw fishscale powder (RFSP) and raw seashell powder (RSSP) were determined by conventional methods and characterized by modern techniques such as EDXRF, SEM, TG-DTA and FTIR analyses. RFSP and RSSP were calcined at various temperatures (400oC to 1000oC) to obtain heat activated fishscale powder 1-7(HAFSP 1-7) and heat activated seashell powder 1-7 (HASSP 1-7). The critical micelle concentration (CMC) of sodium dodecyl sulphate (SDS) were obtained as 7x10-3M, 7x10-3M, 7x10-3M, 4x10-3M, 6x10-3M and 5x10-3 M at pH 1, 2, 3, 4, 5 and 6 respectively. From these results, 7x10-3 M at pH 3 and5x10-3M at pH-6 was selected as optima CMC of SDS. The adsorption properties of different biosorbents (HAFSP-1, 2, 3, 4, 5, 6 and 7) and (HASSP-1, 2, 3, 4, 5, 6 and 7) were compared for the removal of SDS at pH 3and 6. According to these analyses, HAFSP-5 and HASSP-7 were found to be more effective than other samples. Adsorption capacities of HAFSP-5 and HASSP-7 were determined at different contact time and pH by using UV-Vis spectrophotometer at λmax 498nm and 25oC. The optimum contact time was 60 min and pH was 3 and 6 respectively for the removal of SDS solution from the paper industrial wastewater by HAFSP-5 and HASSP-7. The outcome of the present research is the preparation of waste biosorbents for the removal of anionic surfactant from the paper industrial wastewater. | Myanmar Academy of Arts and Science Journal, 2020 June, 2020, Vol. XVIII, No. 1A | ||
20 | Daw Myint Myint Than | Removal of Anionic Surfactant (Sodium Dodecyl Sulphate) from Industrial Wastewater by Using Activated Biosorbents (Fishscale) | In this study, waste fishscale was used as bio-sorbent for the removal of surfactant from industrial wastewater. These bio-sorbent was collected from fish market in Pathein Township, Ayeyawaddy Region. The selected sample was washed with distilled water for three times and was soaked in 3 % nitric acid for 24h and then was washed again with distilled water until pH 7 and dried in an oven at 105C and was made to powder form. RFSP was calcined at various temperatures (400C to 1000C) to obtain heat activated fishscale powder 1-7 (HAFSP 1-7). The adsorption properties of different bio-sorbent (HAFSP-1- 7) were compared for the removal of sodium dodecyl sulphate (SDS) at pH 3. According to these analyses, HAFSP-5 was found to be more effective than other samples. Adsorption capacities of HAFSP-5 were determined at different dosages and initial concentration by using UV-Vis spectrophotometer at λmax 498 nm and 25C. The optimum dosage was 0.1 g and initial concentration was 100 ppm respectively. The outcome of the present research is the preparation of waste bio-sorbent for the removal of anionic surfactant from the industrial wastewater. | 2nd International Conference on Bioeconomy, 2020 | ||
21 | Daw Myint Myint Than | Study on the Adsorption of Surfactant With and Without Electrolytes on Activated Seashell Sorbent | In this study, waste seashell was used as biosorbent for the adsorption of surfactant with and without electrolytes from model aqueous solution at pH 6. Surfactant, sodium dodecyl sulphate (SDS) was used as modifier. The critical micelle concentration (CMC) value of SDS decreases with mixing electrolytes (Na2SO4 and Na3PO4). Therefore, upon addition of Na2SO4and Na3PO4 in SDS, Na3PO4 decreases the CMC value of SDS more than Na2SO4. Adsorption of SDS on HASSP-7 sample by batch operations were conducted with different operation parameters such as dosage of adsorbent and initial concentration of adsorbate. The optimum dosage was 0.1 g and initial concentration was 100 ppm. Sorption of SDS on HASSP-7 was conducted with and without electrolytes. The amount adsorbed of SDS was found more with electrolytes than without electrolytes. Moreover, the amount of SDS adsorption with Na2SO4 was high in comparison with Na3PO4. The outcome of the present research is the surfactant consumption was reduced by adding small amount of electrolytes to the surfactant solutions. It is expected that they can be used in the treatment of paper industrial wastewater containing surfactant (SDS). | Myanmar Academy of Arts and Science Journal, 2020 | ||
22 | Daw Nu Nu Nge | A Study on the Quality of Water from the Hot Spring in Moemauk Township | The water quality of the hot spring which is located in Moemauk Township, Kachine State was studied during cold season. Water samples were collected to analyze some physicochemical components of water in hot spring. The results obtained were compared with the standard level of WHO. This investigation has indicated the extent of water pollution of the hot spring, leading to what actions should be taken to control the quality of water. According to the recorded results, Moemauk Hot Spring is a sulfur spring. The values of BOD and cadmium were found to be slightly above the standard level. | Banmaw University Research Journal, 2016 August, Vol-6 | ||
23 | Daw Nu Nu Nge | Antioxidant Scavenging Activity Assays of Kassod Tree Plant | In this research work, three parts of Kassod Tree plant were selected for the study.The leaf, bark and root of Kassod Tree were collected from Namphar Quarter, Banmaw Township, Kachin State. The collected samples were tested by phytochemical screening. The crude extracts of samples were investigated by two antioxidant activity scavenging methods (metal chelating activity assay and DPPH radical scavenging activity assay) with China 752 N UV-VIS spectrophotometer. The obtained data were compared with respective standard values. The IC50 values of three samples were determined by linear regressive excel programme. | Banmaw University Research Journal, 2019 June, Vol.10, No.2 | ||
24 | Daw Nu Nu Nge | Determination of Total Phenolic, Total Flavonoid Content and Antioxidant Activity of Lemon Plant | The three different parts of Lemon extracts (leaf, bark and root) were analyzed for total phenolic content (TPC), total flavonoid content (TFC) and antioxidant activity. TPC and TFC of Lemon extracts were determined as mg of gallic acid equivalents per gram (mg GAE/g) and mg of catechol equivalents per gram (mg CAE/g) by using their calibration curves. The antioxidant activity was determined by the reducing power assay. This assay based on the electron transfers to oxidative ions or free radicals. Ascorbic acid was used as a standard for the comparison of IC50 values in the reducing power assay. | Banmaw University Research Journal, 2020 June, Vol.11, No.1 |
No | Candidate | Thesis Title | Supervisor | Year | |
---|---|---|---|---|---|
1. | Ma Aye Aye Phyu (2Mah-Chem-2) | A Study on the Physiochemical Properties of Composed Soil | Dr Su Su Aung Professor & Head | 2018 | |
2. | Ma Moe Sandar Oo (2Mah-Chem-3) | A Study on the Physicochemical Properties of Natural fertilizer | Dr Su Su Aung Professor & Head | 2018 | |
3. | Ma Nwe Ni Linn (2Mah-Chem-3) | Preparation of Biogas and Organic Fertilizer from Vegetable Waste and Cow Dung Under Anaerobic Treatment | Dr Su Su Aung Professor & Head | 2019 | |
4. | Ma Tin Tin Aye (2Mah-Chem-7) | Preparation and Characte- rization Fiberboards from Rice Straw | Dr Su Su Aung Professor & Head | 2019 |
1. Classical Literature 2. Modern Literature 3. Literary Theory and Criticism 4. Linguistics 5. Ancient Language 6. Indigenous Languages |
Year | Total |
---|---|
First | 103 |
Second | 90 |
Third | 55 |
Fourth | 60 |
First Year Hons: | 17 |
Second Year Hons: | 19 |
Third Year Hons: | 16 |
Qualify | 10 |
MI | 15 |
MII | 22 |
Total | 407 |
Year | Total |
---|---|
First | 17 |
Second | 19 |
Third | 18 |
Fourth | 15 |
Total | 69 |
Curriculum and Time Table
- First Year
- Second Year
- Third Year
- Fourth Year
- First Year(Hons:)
- Second Year(Hons:)
- Third Year(Hons:)
- Qualifying
- MSc First Year
- MSc Second Year
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | မ 1001 | မြန်မာစာ | 3 | 2 | 2 | |
2. | Eng 1001 | English | 3 | 2 | 2 | |
3. | Chem 1101 | Fundamental Chemistry I | 4 | 3 | 2 | |
4. | Elective | * | 3 | 2 | 2 | |
5. | Course (I) | * | 3 | 2 | 2 | |
6. | Elective | |||||
Course (II) | ||||||
AM- 1001 | Aspects of Myanmar | 3 | 2 | 2 | ||
Total | 19 | 13 | 12 |
Time/ Date | 9:00-10:00 | 10:00-11:00 | 11:00-12:00 | 12:00-1:00 | 1:00-2:00 | 2:00-3:00 | 3:00-4:00 |
---|---|---|---|---|---|---|---|
MON | AM | Myanmar | Math-1001 | Chem-1101 | |||
TUE | AM | Myanmar | Math-1001 | Phys-1001 | AM(Tutorial) | ||
WED | Eng-1001 | Chem-1101 | Phys-1001 | Myanmar(Tutorial) | |||
THUR | Eng-1001 | Chem-1101(Practical) | Phys-1001 (Practical) | ||||
FRI | Eng-1001(Tutorial) | Chem-1101 | Math-1001(Tutorial) |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | မ 1002 | မြန်မာစာ | 3 | 2 | 2 | |
2. | Eng 1002 | English | 3 | 2 | 2 | |
3. | Chem 1102 | Fundamental Chemistry II | 4 | 3 | 2 | |
4. | Elective Course (I) | * | 3 | 2 | 2 | |
5. | Elective Course (II) | * | 3 | 2 | 2 | |
AM 1002 | Aspects of Myanmar | 3 | 2 | 2 | ||
Total | 19 | 13 | 12 |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Eng 2001 | English | 3 | 2 | 2 | |
2. | Chem 2101 | Inorganic Chemistry I | 4 | 3 | 2 | |
3. | Chem 2102 | Physical Chemistry I | 4 | 3 | 2 | |
4. | Chem 2103 | Organic Chemistry I | 4 | 3 | 2 | |
5. | Elective Course (I) | * | 3 | 2 | 2 | |
Elective Course (II) | * | 3 | 2 | 2 | ||
Total | 21 | 15 | 12 |
Time/ Date | 9:00-10:00 | 10:00-11:00 | 11:00-12:00 | 12:00-1:00 | 1:00-2:00 | 2:00-3:00 | 3:00-4:00 | |
---|---|---|---|---|---|---|---|---|
MON | Chem-2104 | Eng-2001 | Chem-2101 | Chem-2101(Practical) | ||||
TUE | Chem-2103 | Eng-2001 | Chem-2105 | Chem-2104 | Chem-2101 | |||
WED | Chem-2102 | Chem-2103(Practical) | Chem-2103 | Chem-2104(Practical) | ||||
THUR | Chem-2101 | Chem-2105(Practical) | Chem-2102 | Eng-2001(Tutorial) | ||||
FRI | Chem-2103 | Chem-2102 (Practical) | Chem-2102 | Chem-2105 |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Eng 2002 | English | 3 | 2 | 2 | |
2. | Chem 2106 | Inorganic Chemistry II | 4 | 3 | 2 | |
3. | Chem 2107 | Physical Chemistry II | 4 | 3 | 2 | |
4. | Chem 2108 | Organic Chemistry II | 4 | 3 | 2 | |
5. | Elective Course (I) | * | 3 | 2 | 2 | |
Elective Course (II) | * | 3 | 2 | 2 | ||
Total | 21 | 15 | 12 |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Eng 3001 | English | 3 | 2 | 2 | |
2. | Chem 3101 | Inorganic Chemistry III | 4 | 3 | 2 | |
3. | Chem 3102 | Physical Chemistry III | 4 | 3 | 2 | |
4. | Chem 3103 | Organic Chemistry III | 4 | 3 | 2 | |
5. | Chem 3104 | Analytical Chemistry I | 4 | 3 | 2 | |
Elective Course | * | 3 | 2 | 2 | ||
Total | 22 | 16 | 12 |
Time/ Date | 9:00-10:00 | 10:00-11:00 | 11:00-12:00 | 12:00-1:00 | 1:00-2:00 | 2:00-3:00 | 3:00-4:00 | |
---|---|---|---|---|---|---|---|---|
MON | Chem-3103 | Chem-3105(Practical) | Chem-3104 | Chem-3105 | ||||
TUE | Chem-3102 | Chem-3104(Practical) | Chem-3105 | Chem-3101 | ||||
WED | Chem-3102 | Chem-3104 | Eng-3001 | Chem-3103 | Chem-3103Practical) | |||
THUR | Chem-3103 | Chem-3101 | Eng-3001 | Chem-3104 | Chem-3102(Practical) | |||
FRI | Chem-3101 (Practical) | Chem-3101 | Chem-3102 | Eng-3001(Tutorial) |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Eng 3002 | English | 3 | 2 | 2 | |
2. | Chem 3107 | Inorganic Chemistry IV | 4 | 3 | 2 | |
3. | Chem 3108 | Physical Chemistry IV | 4 | 3 | 2 | |
4. | Chem 3109 | Organic Chemistry IV | 4 | 3 | 2 | |
5. | Chem 3110 | Analytical Chemistry II | 4 | 3 | 2 | |
Elective Course | * | 3 | 2 | 2 | ||
Total | 22 | 16 | 12 |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Eng 4001 | English | 3 | 2 | 2 | |
2. | Chem 4101 | Inorganic Chemistry V | 4 | 3 | 2 | |
3. | Chem 4102 | Physical Chemistry V | 4 | 3 | 2 | |
4. | Chem 4103 | Organic Chemistry V | 4 | 3 | 2 | |
5. | Chem 4104 | Analytical Chemistry III | 4 | 3 | 2 | |
Elective Course | * | 3 | 2 | 2 | ||
Total | 22 | 16 | 12 |
Time/ Date | 9:00-10:00 | 10:00-11:00 | 11:00-12:00 | 12:00-1:00 | 1:00-2:00 | 2:00-3:00 | 3:00-4:00 | |
---|---|---|---|---|---|---|---|---|
MON | Chem-4106 | Chem-4101 | Eng-4001 | Chem-4103(Practical) | ||||
TUE | Chem-4103 | Chem-4102 | Eng-4001 | Chem-4101 | Eng-4001(Tutorial) | |||
WED | Chem-4103 | Chem-4101(Practical) | Chem-4102 | Chem-4104 | ||||
THUR | Chem-4104 (Practical) | Chem-4106 | Chem-4103 | Chem-4102(Practical) | ||||
FRI | Chem-4102 | Chem-4104 | Chem-4104 | Chem-4101 | Chem-4106(Practical) |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Eng 4002 | English | 3 | 2 | 2 | |
2. | Chem 4107 | Inorganic Chemistry VI | 4 | 3 | 2 | |
3. | Chem 4108 | Physical Chemistry VI | 4 | 3 | 2 | |
4. | Chem 4109 | Organic Chemistry VI | 4 | 3 | 2 | |
5. | Chem 4110 | Analytical Chemistry IV | 4 | 3 | 2 | |
Elective Course | * | 3 | 2 | 2 | ||
Total | 22 | 16 | 12 |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Eng 3001 | English | 3 | 2 | 2 | |
2. | Chem 3201 | Inorganic Chemistry I | 4 | 3 | 2 | |
3. | Chem 3202 | Physical Chemistry I | 4 | 3 | 2 | |
4. | Chem 3203 | Organic Chemistry I | 4 | 3 | 2 | |
5. | Chem 3204 | Analytical Chemistry I | 4 | 3 | 2 | |
Elective Course | * | 3 | 2 | 2 | ||
Total | 22 | 16 | 12 |
Time/ Date | 9:00-10:00 | 10:00-11:00 | 11:00-12:00 | 12:00-1:00 | 1:00-2:00 | 2:00-3:00 | 3:00-4:00 | |
---|---|---|---|---|---|---|---|---|
MON | Chem-3203 | Chem-3205(Practical) | Chem-3204 | Chem-3205 | ||||
TUE | Chem-3202 | Chem-3204(Practical) | Chem-3205 | Chem-3201 | ||||
WED | Chem-3202 | Chem-3204 | Eng-3001 | Chem-3203 | Chem-3203Practical) | |||
THUR | Chem-3203 | Chem-3201 | Eng-3001 | Chem-3204 | Chem-3202(Practical) | |||
FRI | Chem-3201 (Practical) | Chem-3201 | Chem-3202 | Eng-3001(Tutorial) |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Eng 3002 | English | 3 | 2 | 2 | |
2. | Chem 3207 | Inorganic Chemistry II | 4 | 3 | 2 | |
3. | Chem 3208 | Physical Chemistry II | 4 | 3 | 2 | |
4. | Chem 3209 | Organic Chemistry II | 4 | 3 | 2 | |
5. | Chem 3210 | Analytical Chemistry II | 4 | 3 | 2 | |
Elective Course | * | 3 | 2 | 2 | ||
Total | 22 | 16 | 12 |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | English 4001 | English | 3 | 2 | 2 | |
2. | Chem 4201 | Inorganic Chemistry III | 4 | 3 | 2 | |
3. | Chem 4202 | Physical Chemistry III | 4 | 3 | 2 | |
4. | Chem 4203 | Organic Chemistry III | 4 | 3 | 2 | |
5. | Chem 4204 | Analytical Chemistry III | 4 | 3 | 2 | |
Elective Course | * | 3 | 2 | 2 | ||
Total | 22 | 16 | 12 |
Time/ Date | 9:00-10:00 | 10:00-11:00 | 11:00-12:00 | 12:00-1:00 | 1:00-2:00 | 2:00-3:00 | 3:00-4:00 | |
---|---|---|---|---|---|---|---|---|
MON | Chem-4206 | Chem-4201 | Eng-4001 | Chem-4203(Practical) | ||||
TUE | Chem-4203 | Chem-4202 | Eng-4001 | Chem-4201 | Eng-4001(Tutorial) | |||
WED | Chem-4203 | Chem-4101(Practical) | Chem-4202 | Chem-4204 | ||||
THUR | Chem-4204 (Practical) | Chem-4206 | Chem-4203 | Chem-4202(Practical) | ||||
FRI | Chem-4202 | Chem-4204 | Chem-4204 | Chem-4201 | Chem-4206(Practical) |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Eng 4002 | English | 3 | 2 | 2 | |
2. | Chem 4207 | Inorganic Chemistry IV | 4 | 3 | 2 | |
3. | Chem 4208 | Physical Chemistry IV | 4 | 3 | 2 | |
4. | Chem 4209 | Organic Chemistry IV | 4 | 3 | 2 | |
5. | Chem 4210 | Analytical Chemistry IV | 4 | 3 | 2 | |
Elective Course | * | 3 | 2 | 2 | ||
Total | 22 | 16 | 12 |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Chem 5201 | Inorganic Chemistry V | 4 | 3 | 2 | |
2. | Chem 5202 | Physical Chemistry V | 4 | 3 | 2 | |
3. | Chem 5203 | Organic Chemistry V | 4 | 3 | 2 | |
4. | Chem 5204 | Analytical Chemistry V | 4 | 3 | 2 | |
5. | Chem 5205 | Nuclear Chemistry I | 4 | 3 | 2 | |
Chem 5206 | Food and Nutritional Chemistry | 4 | 3 | 2 | ||
Total | 24 | 18 | 12 |
Time/ Date | 9:00-10:00 | 10:00-11:00 | 11:00-12:00 | 12:00-1:00 | 1:00-2:00 | 2:00-3:00 | 3:00-4:00 | |
---|---|---|---|---|---|---|---|---|
MON | Chem-5201 | Chem-5202(Practical) | Chem-5202 | Chem-5203(Practical) | ||||
TUE | Chem-5203 | Chem-5204 | Chem-5205 | Chem-5202 | Chem-5205(Practical) | |||
WED | Chem-5206 | Chem-5203 | Chem-5202 | Chem-5206 | Chem-5204(Practical) | |||
THUR | Chem-5206 (Practical) | Chem-5205 | Chem-5206 | Chem-5205 | Chem-5204 | |||
FRI | Chem-5201 | Chem-5201 | Chem-5204 | Chem-5203 | Chem-5201(Practical) |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Chem 5207 | Inorganic Chemistry VI | 4 | 3 | 2 | |
2. | Chem 5208 | Physical Chemistry VI | 4 | 3 | 2 | |
3. | Chem 5209 | Organic Chemistry VI | 4 | 3 | 2 | |
4. | Chem 5210 | Analytical Chemistry VI | 4 | 3 | 2 | |
5. | Chem 5211 | Nuclear Chemistry II | 4 | 3 | 2 | |
Chem 5212 | Nanochemistry | 4 | 3 | 2 | ||
Total | 24 | 18 | 12 |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Chem 5201 | Inorganic Chemistry V | 4 | 3 | 2 | |
2. | Chem 5202 | Physical Chemistry V | 4 | 3 | 2 | |
3. | Chem 5203 | Organic Chemistry V | 4 | 3 | 2 | |
4. | Chem 5204 | Analytical Chemistry V | 4 | 3 | 2 | |
5. | Chem 5205 | Nuclear Chemistry I | 4 | 3 | 2 | |
Chem 5206 | Food and Nutritional Chemistry | 4 | 3 | 2 | ||
Total | 24 | 18 | 12 |
Time/ Date | 9:00-10:00 | 10:00-11:00 | 11:00-12:00 | 12:00-1:00 | 1:00-2:00 | 2:00-3:00 | 3:00-4:00 | |
---|---|---|---|---|---|---|---|---|
MON | Chem-5201 | Chem-5202(Practical) | Chem-5202 | Chem-5203(Practical) | ||||
TUE | Chem-5203 | Chem-5204 | Chem-5205 | Chem-5202 | Chem-5205(Practical) | |||
WED | Chem-5206 | Chem-5203 | Chem-5202 | Chem-5206 | Chem-5204(Practical) | |||
THUR | Chem-5206 (Practical) | Chem-5205 | Chem-5206 | Chem-5205 | Chem-5204 | |||
FRI | Chem-5201 | Chem-5201 | Chem-5204 | Chem-5203 | Chem-5201(Practical) |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Chem 5207 | Inorganic Chemistry VI | 4 | 3 | 2 | |
2. | Chem 5208 | Physical Chemistry VI | 4 | 3 | 2 | |
3. | Chem 5209 | Organic Chemistry VI | 4 | 3 | 2 | |
4. | Chem 5210 | Analytical Chemistry VI | 4 | 3 | 2 | |
5. | Chem 5211 | Nuclear Chemistry II | 4 | 3 | 2 | |
Chem 5212 | Nanochemistry | 4 | 3 | 2 | ||
Total | 24 | 18 | 12 |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Chem 611 | Inorganic Chemistry | 4 | 4 | 2 | |
2. | Chem 612 | Physical Chemistry | 4 | 4 | 2 | |
3. | Chem 613 | Organic Chemistry | 4 | 4 | 2 | |
4. | Chem 614 | Analytical Chemistry | 4 | 4 | 2 | |
Total | 16 | 16 | 8 |
Time/ Date | 9:00-10:00 | 10:00-11:00 | 11:00-12:00 | 12:00-1:00 | 1:00-2:00 | 2:00-3:00 | 3:00-4:00 | |
---|---|---|---|---|---|---|---|---|
MON | Chem-613 | Chem-612 | Chem-612 | Chem-611 | ||||
TUE | Chem-612 | Chem-613(Practical) | Chem-614 | Chem-613 | ||||
WED | Chem-611 | Chem-614(Practical) | Chem-614 | Chem-612 | ||||
THUR | Chem-613 | Chem-611 | Chem-611 | Chem-612(Practical) | ||||
FRI | Chem-614 | Chem-611(Practical) | Chem-614 | Chem-613 |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Chem 621 | Inorganic Chemistry and Nuclear Chemistry | 4 | 4 | 2 | |
2. | Chem 622 | Physical Chemistry | 4 | 4 | 2 | |
3. | Chem 623 | Organic Chemistry | 4 | 4 | 2 | |
4. | Chem 624 | Analytical Chemistry | 4 | 4 | 2 | |
Total | 16 | 16 | 8 |
No. | Module No | Name of Module | Credit Points | Hours per week | ||
---|---|---|---|---|---|---|
Lecture | Tutorial | |||||
1. | Chem 631 | Inorganic Chemistry and Nuclear Chemistry | 4 | 4 | 2 | |
2. | Chem 632 | Physical Chemistry | 4 | 4 | 2 | |
3. | Chem 633 | Organic Chemistry | 4 | 4 | 2 | |
4. | Chem 634 | Analytical Chemistry | 4 | 4 | 2 | |
Total | 16 | 16 | 8 |
Sample Description
No. | Module No | Name of Module | Credit Points | |
---|---|---|---|---|
1. | Chem 641 | Research Progress Report and Seminar | 8 | |
2. | Chem 642 | Thesis and Viva Voce | 8 | |
Total | 16 |