This thesis presents a series of theorems along with proofs to establish a theory of congruences.

Residues of picloram in four varieties of potatoes, given pre-emergence treatments with picloram at 2 oz per acre and picloram at 2 oz + linuron at 24 oz per acre were determined by electron capture gas chromatography. Average residue levels of 3.9 and 2.7 ppb (fresh weight) were obtained for the picloram and picloram + linuron treatments. This difference was significant at the 1% level. Tuber injury, ranging from formation of corky tissues on the surface to splitting, was observed with the picloram treatments. No such injury was observed with the picloram + linuron treatments. Yields were noticeably higher in the picloram + linuron treatments. The reduced picloram residues could thus be associated with the diluting effect of higher yields which resulted from the addition of linuron. A similar experiment using four varieties of carrots given either pre-emergence or post-emergence treatments with picloram at ½ and 2 oz per acre respectively gave no detectable picloram residues. Using ¹⁴C carboxyl labeled picloram this finding was further investigated and it was shown that picloram was absorbed by the foliage and roots and translocated throughout the whole plant. The leaves accumulated four times more radioactivity than the taproots. The radioactivity in the leaves and taproots was in the form of the parent picloram molecule. The picloram present in the taproot was located mainly in the xylem. A study of the stability of picloram, its potassium salt and its methyl ester under short wave ultraviolet light (253.7 nm) revealed that all three compounds were degraded into several photoproducts. The methyl ester was the least stable, being 85% degraded after one hour exposure. Picloram and its potassium salt were more stable, each being 50% decomposed after one hour exposure. Partial polymerization of all three compounds may also have taken place. / Land and Food Systems, Faculty of / Graduate

No description available.

No / Gas chromatography-mass spectrometry (GC-MS) and bulk carbon isotope determinations have been performed on samples ('cemented organic residues', charcoal, sediment and fire-cracked rock) excavated from twelve slab-lined pits from various locations in Arctic Norway to test the premise that these archaeological features were used for the extraction of oil from the blubber of marine mammals, such as seal, whale and walrus. A wide range of lipid compound classes were detected especially in the cemented organic residues and in the charcoal samples. The presence of long-chain unsaturated and isoprenoid fatty acids together with oxidation and thermal alteration products of unsaturated acids such as dicarboxylic acids, dihydroxyfatty acids and ω-(o-alkylphenyl)alkanoic acids suggests that these features were used for marine oil extraction at elevated temperatures. Notably the location of the hydroxyl groups in the dihydroxyfatty acids provides a record of the positional isomer of the precursor fatty acid and allows confirmation that 11-docosenoic (cetoleic) acid, the most abundant C22:1 isomer in marine oil, was a major component of the original lipid. Further information was provided by the presence of long-chain fatty acyl moieties in surviving triacylglycerols and the presence of cholesterol. A fungal metabolite, mycose (trehalose), was found in all samples apart from a fire-cracked rock and points to microbiological activity in the pits. Bulk isotope analysis conducted on the 'cemented organic residues' is consistent with modern reference samples of blubber and oil from seal and whale. These data provide clear analytical evidence of the function of slab-lined pits in the archaeological record and suggest widespread exploitation of marine mammals for producing oil for heating, lighting and myriad other uses in the past.

No description available.

by Pui-nin Lee. / Thesis submitted in: August 1997. / Thesis (M.Phil.)--Chinese University of Hong Kong, 1998. / Includes bibliographical references (leaves 141-148). / Abstract also in Chinese. / List of Abbreviations --- p.I / List of Tables --- p.II / List of Figures --- p.III / Chapter Chapter 1 --- Introduction --- p.1 / Chapter 1.1 --- Sugar cane --- p.1 / Chapter 1.2 --- Mushroom: Pleurotus pulmonarius --- p.5 / Chapter 1.2.1 --- Fruiting bodies --- p.5 / Chapter 1.2.2 --- Life cycle of the mushroom --- p.6 / Chapter 1.2.3 --- Cultivation --- p.7 / Chapter 1.2.4 --- Nutrition --- p.8 / Chapter 1.2.5 --- Cardiovascular and Renal effects --- p.9 / Chapter 1.2.6 --- Dietary fiber --- p.10 / Chapter 1.2.6.1 --- Physical properties of dietary fiber --- p.10 / Chapter 1.2.6.2 --- Physiological actions --- p.11 / Chapter 1.3 --- Food colorants --- p.13 / Chapter 1.4 --- Quality of food products --- p.14 / Chapter 1.4.1 --- Toxicity studies --- p.15 / Chapter 1.4.2 --- Stability --- p.16 / Chapter 1.4.3 --- Sensory evaluation --- p.18 / Chapter 1.5 --- Secondary metabolism --- p.20 / Chapter 1.6 --- Monascus --- p.24 / Chapter 1.6.1 --- Monascus products --- p.25 / Chapter 1.6.2 --- Monascus products as a functional food --- p.27 / Chapter 1.6.3 --- Monascus pigments --- p.27 / Chapter 1.6.4 --- Factors affect Monascus pigment production --- p.31 / Chapter 1.7 --- Purposes of study --- p.37 / Chapter Chapter 2 --- Materials and Methods --- p.38 / Chapter 2.1 --- Micro-organisms --- p.38 / Chapter 2.2 --- Maintenance of culture --- p.38 / Chapter 2.3 --- Waste Culture medium for production of pigments --- p.38 / Chapter 2.4 --- Chemical analysis of sugar cane residue broth (SCRB) --- p.39 / Chapter 2.5 --- Preparation of inoculum --- p.40 / Chapter 2.6 --- Batch culture for pigment production --- p.41 / Chapter 2.7 --- Fermentor culture for pigment production --- p.44 / Chapter 2.8 --- Cultivation of oyster mushroom --- p.46 / Chapter 2.9 --- Purification and characterization of Monascus pigments --- p.49 / Chapter 2.9.1 --- Extracellular pigments --- p.49 / Chapter 2.9.2 --- Intracellular pigments --- p.50 / Chapter 2.10 --- Toxicity test --- p.56 / Chapter 2.11 --- Sensory evaluation --- p.61 / Chapter 2.12 --- Statistical analysis --- p.62 / Chapter Chapter 3 --- Results --- p.62 / Chapter 3.1 --- Extracellular pigment of screening test --- p.63 / Chapter 3.2 --- Batch culture for pigment production by Monascus purpureus --- p.69 / Chapter 3.2.1 --- Consumption of glucose --- p.69 / Chapter 3.2.2 --- Consumption of sucrose --- p.59 / Chapter 3.2.3 --- Biomass production --- p.69 / Chapter 3.2.4 --- Residual protein content --- p.73 / Chapter 3.2.5 --- pH value of the fermented medium --- p.73 / Chapter 3.2.6 --- Production of crude extracellular pigments --- p.73 / Chapter 3.2.7 --- Production of crude intracellualr pigments --- p.75 / Chapter 3.2.8 --- Total crude pigment yield --- p.75 / Chapter 3.3 --- Fermentor --- p.77 / Chapter 3.3.1 --- "Pigmentation of control group, treatment A and B" --- p.77 / Chapter 3.3.2 --- Nutrition of the biomass from control group and treatment B of fermentor products --- p.80 / Chapter 3.4 --- Production of oyster mushroom --- p.80 / Chapter 3.4.1 --- Biological efficiency of mushroom --- p.80 / Chapter 3.4.2 --- Amino acid profile and total amino acid content of the fruitbidies --- p.87 / Chapter 3.4.3 --- Total dietary fiber content --- p.87 / Chapter 3.4.4 --- "The contents of carbon, hydrogen and nitrogen" --- p.91 / Chapter 3.4.5 --- Sensory evaluation of the mushroom --- p.91 / Chapter 3.5 --- Toxicity --- p.91 / Chapter 3.5.1 --- Acute toxicity --- p.91 / Chapter 3.5.1.1 --- Body weight --- p.95 / Chapter 3.5.1.2 --- Food consumption --- p.95 / Chapter 3.5.2 --- Subacute toxicity --- p.99 / Chapter 3.5.2.1 --- Food consumption --- p.99 / Chapter 3.5.2.2 --- Body weight --- p.99 / Chapter 3.5.2.3 --- The organ weight to body weight ratios --- p.99 / Chapter 3.5.2.4 --- The glutamate-pyruvate transaminase (GPT) and glutamate- oxaloacetate transaminase (GOT) level in blood serum --- p.103 / Chapter 3.6 --- Analysis of Monascus pigments from fermentor system by HPLC and spectrophotometry --- p.108 / Chapter 3.6.1 --- Extracellular pigment from control group --- p.108 / Chapter 3.6.2 --- Extracellular pigment from the group supplemented with 1 % MSG --- p.108 / Chapter 3.6.3 --- Intracellular pigment --- p.111 / Chapter 3.6.3.1 --- Standard of intracellular pigments (conventional pigments) --- p.111 / Chapter 3.6.4 --- Intracellular pigments extracted from SCRB group --- p.111 / Chapter 3.6.5 --- Intracellular pigment extracted from SCRB with 1 % MSG --- p.115 / Chapter 3.7 --- Qualitative and quantitative of the extracellular and intracellular pigments --- p.118 / Chapter 3.8 --- Detection of citrinin by HPLC --- p.123 / Chapter Chapter 4 --- Discussion --- p.128 / Chapter 4.1 --- Screening test --- p.128 / Chapter 4.1.1 --- Batch culture system --- p.128 / Chapter 4.2 --- Toxicity test of crude extracellular pigment --- p.129 / Chapter 4.2.1 --- Acute toxicity --- p.129 / Chapter 4.2.2 --- Subacute toxicity test --- p.130 / Chapter 4.2.3 --- Organ to body weight ratios and cytotoxicity --- p.131 / Chapter 4.3 --- The two new water soluble pigment --- p.132 / Chapter 4.4 --- Extraction and purification of Monascus pigments from fermentor system --- p.133 / Chapter 4.4.1 --- Qualitative and quantitative of the intracellular and extracellular pigments --- p.133 / Chapter 4.5 --- Nephrotoxic-citrinin --- p.134 / Chapter 4.6 --- Oyster mushroom cultivation --- p.135 / Chapter 4.6.1 --- Fruiting yield (biological efficiency) --- p.136 / Chapter 4.6.2 --- Amino acid content --- p.136 / Chapter 4.6.3 --- Total dietary fiber content --- p.137 / Conclusion --- p.139 / References --- p.141 / Appendix

O crescimento desordenado, o consumo desenfreado e as constantes alterações climáticas são aspectos que não podem mais ser desconsiderados, assim como o consequente acúmulo de resíduos, advindos destas características em boa parte do mundo. A capacidade da Administração Pública em regulamentar e fiscalizar as atividades poluidoras tem sido e será, cada vez mais, um grande desafio. Por isso, o presente trabalho se incumbiu de uma análise comparada entre as normas e práticas brasileira e portuguesa, considerando Portugal como Estado-Membro da União Europeia. O resultado foi a identificação de uma série de necessidades de adequação na regulamentação, controle e, principalmente, no processo fiscalizatório brasileiro. / The disorganized development, the unrolled consumption and the constant climate changes are aspects that cannot be ignored nowadays, such as the residue accumulation resulted from those characteristics all over the world. The capacity of the State to regulate and control the polluted activities has been and will be, even more, a great challenge. The following work proposed to realize a compared analysis between the Brazilian and Portuguese standards and practices, considering Portugal as a Member-State in European Union. The result was an identification of a series of needs in the regulation and control, mainly, in the Brazilian control process.

Call number: LD2668 .T4 1946 C3 / Master of Science

The background of this work is to suggest ways to take care of branches and tops of trees that today are left out in the north of Sweden after logging because it has to low value to be worth transporting. A solution to this is to place small chemical factories in the sparsely populated areas in the inland of Norrland that can take care of the forest residues and break it into valuable chemicals directly in the forest an then transport it to a market. The aim of this work was to find out if it´s a good idea to invest in these small chemical factories in the north of Sweden. This study has been carried out using literature study and interviews of key people. The largest part of the result comes from the interviews. The results of this study show that the small chemical factory is a good idea. Forest residues contains many valuable substances that should be greater used today. The results section of the report describes various factor that are crucial for the small chemical factory and these are: the products that can be produced, what technology that is suitable, if there is an market, who should be taking care of the factory and how the inland endurance will be affected. The conclusions that can be drawn from the study is that the small chemical factory should produce high-grade-sary chemicals directed at the chemical market. It may also be noted that there is existing technology that can be used in the factories, what has been done in the laboratories today can be implemented in the factory. The market will obviously depend on which product that will be produces, but finding a suitable market should not be impossible. The inland endurance will be positively impacted, among other things, the social endurance is enhances when these small chemical factories creates job opportunities in the inland and it can lead to decreasing the emigration.

In this work we apply the Adomian decomposition method to an orientation aggregation problem modelling the time distribution of filaments. We find analytical solutions under certain specific criteria and programmatically implement the Adomian method to two variants of the orientation aggregation model. We extend the utility of the Adomian decomposition method beyond its original capability to enable it to converge to more than one solution of a nonlinear problem and further to be used as a corrector in path following bifurcation problems.