THE DESIGN AND ANALYSIS OF EXPERIMENTS. By Oscar Kempthorne. New York, John Wiley and Sons, Inc., 1952. 631 pp. $8.50. This book by a teacher of statistics (as well as a consultant for \"experimenters\") is a comprehensive study of the philosophical background for the statistical design of experiment. It is necessary to have some facility with algebraic notation and manipulation to be able to use the volume intelligently. The problems are presented from the theoretical point of view, without such practical examples as would be helpful for those not acquainted with mathematics. The mathematical justification for the techniques is given. As a somewhat advanced treatment of the design and analysis of experiments, this volume will be interesting and helpful for many who approach statistics theoretically as well as practically. With emphasis on the \"why,\" and with description given broadly, the author relates the subject matter to the general theory of statistics and to the general problem of experimental inference. MARGARET J. ROBERTSON

The Design and Analysis of Experiments

Positive ions that are available in soils absorb on grain surfaces. The total sum of cations that can be absorbed bij a soil/sediment at a certain PH is defined by the cation-exchange capacity (CEC, in meq g-1: mol equivalents per gram). The uptake of cations is an important parameter in agriculture and the larger the CEC, the more cations can be absorbed to the soil. The CEC depends highly on the pH of soil and sediments, where the CEC decreases with decreasing PH (increasing acidity). The exchange of ions on sediments occurs commonly fast on geological time scales, but the kinetics of adsorption in natural environments is still poorly understood. The strength of the bonding between the cations and the sediments varies from weak Van der Waals bondings (physical adsorption) to strong chemical bonds. The CEC is widely used for agricultural assessment because it is a measure of general soil fertility as well as an indicator of structural stability because CED is capabel of enhancing development of shrinkage cracks. The list below shows the CEC for different types of minerals. The data indicate that the CEC can vary over 2 orders of magnitude for various types of , minerals and can vary one order of magnitude within one soil type. Cation exchange capacity for different types of sediment (Eisma, 1992; Locher and de Bakker, 1990):

Cation exchange capacity.

Introduction to quality engineering : designing quality into products and processes

Contents: Variety and Quality. Variability loss and tolerance. Determining tolerances. Tolerance design and experimental design. Offline and online quality control. Parameter design and tolerance design: case study. Experimental design for smaller is better characteristics. Experimental design for larger is better characteristics. Bypassing the S/N ratio: spring experiment. Experimental design for dynamic characteristics.

Introduction to quality engineering. designing quality into products a

Use of surfactants for the remediation of contaminated soils: a review.

Landfills are the primary option for waste disposal all over the world. Most of the landfill sites across the world are old and are not engineered to prevent contamination of the underlying soil and groundwater by the toxic leachate. The pollutants from landfill leachate have accumulative and detrimental effect on the ecology and food chains leading to carcinogenic effects, acute toxicity, and genotoxicity among human beings. Management of this highly toxic leachate presents a challenging problem to the regulatory authorities who have set specific regulations regarding maximum limits of contaminants in treated leachate prior to disposal into the environment to ensure minimal environmental impact. There are different stages of leachate management such as monitoring of its formation and flow into the environment, identification of hazards associated with it, and its treatment prior to disposal into the environment. This article focuses on: (i) leachate composition, (ii) plume migration, (iii) contaminant fa...

/pdf/contemporary-environmental-issues-of-landfill-leachate-t1zjypqwqo.pdf

Contemporary Environmental Issues of Landfill Leachate: Assessment and Remedies

Taguchi optimization approach for production of activated carbon from phosphoric acid impregnated palm kernel shell by microwave heating

Acid mine drainage due to weathering of iron sulfide minerals is one of the biggest global environmental issues. However, due to the unique physicochemical properties of natural and synthesized iron sulfides (i.e. pyrite, pyrrhotite, and mackinawite), they can be effectively used for wastewater treatment. These properties, such as ≡SH functional groups as Lewis bases, reducibility of surface Fe and S species, dissolved Fe2+ as a catalyst, and dissolved S2− as an electron donor, are extensively reviewed in this article. The target water pollutants include toxic metals (i.e. lead, mercury, cadmium, and hexavalent chromium) and metalloid (i.e. arsenic), radionuclides (i.e. uranium and selenium), organic contaminants (i.e. chlorinated organic pollutants, benzene and polycyclic aromatic hydrocarbons), and nutrients (i.e. nitrogen and phosphorus). The dominant interaction mechanisms between iron sulfides and these contaminants, and the removal efficiencies are elucidated. This article focuses on the role of iron sulfides as functional materials for wastewater treatment. A recent development of nanostructured pyrrhotite with a high specific surface area for wastewater treatment is also highlighted.

Utilization of iron sulfides for wastewater treatment: a critical review

Guar gum is a widely used ingredient in food processing industry. This work highlights the use of guar gum as a flocculant aid in potable water treatment. Current practice of using synthetic flocculants such as polyacryl-amide has raised controversies of acrylamide residues in water and thereby increasing health risk of the population. The flocculating effect of guar gum on the settling characteristics of flocs in a bench-scale potable water clarification process is presented in this work. Data from two experimental runs, namely, run A (guar gum and primary coagulant) and run B (primary coagulant only), were used to plot settling velocity distribution curves (SVDC). Observation of these curves revealed that guar gum increased the proportion of destabilised colloidal impurities settling above a stated minimum velocity. It was found that guar gum may be used along with alum to reduce raw water turbidity from 26.5 to 1.0. It may be concluded that guar gum can be used as a safer alternative to polyacrylamide in water treatment for drinking or food processing purposes.

Application of guar gum as a flocculant aid in food processing and potable water treatment

https://pure.hw.ac.uk/ws/files/9980590/1_s2.0_S1385894716301310_main.pdf

Bhaskar Sen Gupta

Papers

Contemporary Environmental Issues of Landfill Leachate: Assessment and Remedies

Taguchi optimization approach for production of activated carbon from phosphoric acid impregnated palm kernel shell by microwave heating

Utilization of iron sulfides for wastewater treatment: a critical review

Application of guar gum as a flocculant aid in food processing and potable water treatment

Ammonium-based deep eutectic solvents as novel soil washing agent for lead removal