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  • About
  • The Global ETD Search service is a free service for researchers to find electronic theses and dissertations. This service is provided by the Networked Digital Library of Theses and Dissertations.
    Our metadata is collected from universities around the world. If you manage a university/consortium/country archive and want to be added, details can be found on the NDLTD website.
101

Suspension firing of residue/coal mixtures : NOx formation and control

Zamani, Hossein Sadeghi January 2011 (has links)
Typescript (photocopy). / Digitized by Kansas Correctional Industries
102

Pesticides and produce : risk perceptions of extension clientele

Love, Margaret L. 30 August 1993 (has links)
While there is growing public concern over the safety of the food supply, few studies have contrasted varying perceptions of pesticide risk. This study assessed and contrasted perceptions of three groups of Oregon State University Extension Service clientele (home food preservers, Master Gardener volunteers, commercial growers) and factors influencing these perceptions. The impact of the pesticide risk perceptions on purchasing decisions and pesticide application practices was assessed. Two questionnaires were developed: one for home food preservers/Master Gardener volunteers and one for commercial growers. One hundred twenty-seven questionnaires were completed by a convenience sample of home food preservers (85% adjusted return rate) and 155 questionnaires were completed by randomly selected Oregon State University Master Gardener volunteers (81% adjusted return rate). A shortened version of the questionnaire was completed by 124 participants at the annual meeting of Willamette Valley Processed Vegetable Growers. Home preservers were 84% female (mean age=49 ± 14 years), volunteers were 50% female/50% male (mean age=56 ±14 years), and commercial growers were 95% male (mean age=42 ± 11 years). Three different measures of pesticide risk perceptions were used to test six hypotheses: Respondents rated 1) "eating foods produced using pesticides" as high, low, or no risk, and agreed/disagreed (on Likert scales) whether 2) "chemical residues remaining on produce are a major health concern," and 3) "children are at a greater risk for illness from pesticides than adults." Produce selection decisions, pesticide application practices, life stages, gender, media awareness, and knowledge of agricultural production techniques and practices were also assessed to determine their relationship with risk perceptions. Perceptions of risk varied among the three groups. Fifty-five percent of preservers rated "eating foods produced using pesticides" as a "high" risk compared to 34% of volunteers and 2% of growers. Thirty-four percent of preservers strongly agreed that "chemical residues remaining on produce are a major health concern" compared to 25% of volunteers and 7% of growers. Forty-six percent of preservers strongly agreed that "children are at a greater risk of illness from pesticides than adults" compared to 42% of volunteers. Fifty-two percent of growers strongly/ somewhat agreed that children are at no greater risk. Gender was significantly associated with respondents' perceptions. Eighty-nine percent of preservers rating the risk of "eating food produced using pesticides" as "high" were female as were 65% of volunteers. Female volunteers moderately agreed that "chemical residues remaining on produce are a major health concern" compared to males who tended to neither agree nor disagree. The presence of children living in the home was significantly related to the volunteers' perceptions that chemicals are a major health concern and that children are at greater risk. Preservers and growers' results indicated there were no significant differences. Awareness of pesticide reports in the media was measured by recall of four media events. Media awareness was significantly associated with preservers' perceptions that eating foods produced with pesticides was "high" risk and that children are at a greater risk for illness because of pesticide residues. There was no media association for either volunteers or growers. Influence of risk perceptions on produce purchase decisions was measured with a series of questions about past, present, and future purchases. Results indicated that volunteers' pesticide risk perceptions were significantly related to more produce selection decisions than were home food preservers. The risk perception measure that "chemical residues remaining on produce are a major health concern" was most significantly associated with purchase decisions for both preservers and volunteers. For preservers and volunteers there were significant relationships between all three measures of pesticide risk perceptions and three of the twelve purchase decisions tested. Those who perceived a higher risk were 1) more willing to pay a higher price for certified residue free produce, 2) more concerned about pesticide residues when buying imported produce, and 3) intended to purchase produce grown without synthetic pesticides even if it costs more. Knowledge of agricultural practices was measured by a set of five questions. Mean scores ranged from 0.9 ± 0.9 for preservers to 1.6 ± 1.0 for volunteers out of a possible 5.0. Volunteers' with higher scores were significantly more likely to agree that chemicals are a major health concern and that children are at a greater risk of illness from pesticide residues. No significant associations were seen for preservers. Pesticide application practices were significantly related to pesticide risk perceptions. Preservers and volunteers who generally perceived the risks as "high" reported not using pesticides. Preservers reporting changes in application practices moderately agreed chemical residues are a major health concern while volunteers' reporting changes in application practices strongly agreed that children are at higher risk than adults. Growers tended to disagree that pesticides are a major health concern and they were less concerned that children are at a greater risk from pesticides. The study concluded that the home food preservers and Master Gardener volunteers perceived the risks associated with pesticides and produce as much higher than commercial vegetable growers. This difference in perceptions is reflected in some of their produce selection decisions and pesticide application practices. Children living at home, gender, media awareness, and knowledge of agricultural practices were associated with the pesticide risk perceptions of these Extension clientele. Results suggest that educational programming to increase knowledge about pesticide usage in agricultural production is warranted. There is also a need to foster better communications among groups with differing points of views about pesticide residue risks. / Graduation date: 1994
103

Site Directed Mutagenesis of Dienelactone Hydrolase

Al-Khatib, Haifa Yousef 08 1900 (has links)
The clcD gene encoding dienelactone hydrolase (DLH) is part of the clc gene cluster for the utilization of the B-ketoadipate pathway intermediate chlorocatechol. The roles that individual amino acids residues play in catalysis and binding of the enzyme were investigated. Using PCR a 1.9 kbp clcD fragment was amplified and subcloned yielding a 821 bp BamHi to ZscoRI subclone in the plasmid pUC19.
104

Biomass utilization for energy purposes in Kenya : Fuel characteristics and thermochemical properties

García López, Natxo January 2016 (has links)
Around forty percent of the world´s population, mostly inhabitants of countries with developing economies, rely on the traditional usage of biomass for energy purposes. The major negative consequences are environmental and health effects. Additionally, the most remarkable social consequence is rural poverty which is directly linked to lack of access to electricity. This places the questions related to biomass utilization for energy production at the core of global welfare. The present work was performed as a part of a larger research project funded by Formas and which involves Swedish and Kenyan partners. The aim of this study was to gather basic knowledge about the characteristics of relevant biomass from sub-Saharan Africa, more specifically from Kenya. Eight different types of biomass, including agroforestry trees, agricultural residues, and water hyacinth, were evaluated according to fuel characteristics and thermochemical properties. Ultimate and proximate analyses of the collected biomass were carried out, in addition to heating values analyses. Moreover, the biomass was pelletized and a thermogravimetric analysis was performed in a single pellet reactor.  Finally, the composition of the residual ashes was determined. The results show that there was a large variation in the fuel characteristics and thermochemical behaviour of the studied agricultural residues and water hyacinth biomass types, whereas agroforestry trees had rather similar properties and thermochemical behaviour when combusted at the same temperature. In addition, results from the ash composition analyses showed large differences among the studied biomass types, which can be used to better predict and solve problems related to the combustion of these biomass types.
105

Dragagem, transporte e disposição final de sedimento de leito de rio - estudo de caso: Calha do Rio Tietê - Fase II. / Dredging, transport and final disposition of the river bed sediments - case study: Rio Tietê\'s Gutter - Phase II.

Lima, Lilian Rouse da Silva 04 July 2008 (has links)
As obras de Ampliação da Calha do Rio Tietê fazem parte de medidas estruturais que visaram ao aumento da capacidade de vazão para o controle das enchentes na RMSP. A regularidade da capacidade de vazão dependerá, dentre outras ações, de dragagens de manutenção e retirada do material dragado, cuja destinação é bastante problemática. O objetivo deste trabalho é a elaboração de um estudo sobre o processo de dragagem, transporte e disposição final de material de leito de rio por meio da apresentação do processo adotado no estudo de caso: Ampliação da Calha do Rio Tietê Fase II. Para esse fim, são abordados os principais aspectos técnicos, ambientais, sociais e econômicos relativos às obras do estudo de caso, dando ênfase à gestão do sedimento dragado, que busca estar em consonância com as normas e diretrizes legais vigentes. São finalmente enunciadas as principais recomendações e conclusões que devem ser aplicadas na gestão do sedimento dragado do Rio Tietê. / The works of Enlargement of Rio Tietê\'s Gutter (Waterway) are part of structural measures that objective increase the flow capacity for inundation control in RMSP (Metropolitan Region of São Paulo). The regularity of the flow capacity will depend, among other actions, of maintenance dredgings and retreating of dredged material, whose destination is plenty of problem. The aim of this work is the elaboration of a study about the dredging process, transport and final disposition of the river bed sediment through the presentation of the process adopted in the case study: Enlargement of Rio Tietê\'s Gutter Phase II. For that purpose, the main technical, environmental, social and economical aspects related to the works of the case study are discussed, giving emphasis in the administration of the dredged sediment, that seek fitting to the in course norms and legal guidelines. Finally, the main recommendations and conclusions that should be applied in the administration of Rio Tietê\'s dredged sediment are examined.
106

Painéis de madeira aglomerada produzidos com resíduos de serragem e poliestireno expandido para aplicações na construção civil / Particleboards produced with residues of sawdust from sawmill and expanded polystyrene to the application in construction

Lacombe, Jane Eliza de Almeida 03 December 2015 (has links)
As placas de madeira aglomerada, amplamente empregadas para fabricação de móveis, estão consolidadas no mercado, mas merecem especial atenção devido ao seu alto custo quanto aos adesivos empregados e principalmente à vulnerabilidade à umidade se caso entre em contato com a mesma. Diante os fatos, este trabalho apresenta uma nova alternativa de adesivo, empregado por meio de aparas de isopor (EPS), largamente encontrados como resíduos, e o mesmo, ao envolver as partículas de madeira, material também empregado para a fabricação dos painéis, o torna apto para emprego em ambientes ligados diretamente à umidade, sejam eles internos ou externos à edificação. Com isso, o presente trabalho apresenta a elaboração e a proposta de utilização de um novo produto em forma de painel de madeira, produzido com serragem residual de serrarias, como partículas, e EPS (isopor) dissolvido, como adesivo, que possam ser empregados também na construção civil. Assim, foram produzidos painéis com quatro espécies de resíduos de madeira: pinus, eucalipto, teca e peroba. De cada uma das amostras, foram confeccionados dez painéis para a avaliação das características física, mecânica e outros ensaios. Dos resultados de caracterização física, pode-se concluir que os painéis estão conforme padrões exigidos pela norma brasileira NBR 14.810-2 - \"Chapas de madeira aglomerada\" da ABNT (2006b), e, devido aos baixos valores de inchamento, são adequados à utilização em ambientes úmidos e/ou externos. Dos resultados de caracterização mecânica, os painéis apresentaram bons resultados quanto à ligação interna e compressão, indicando ser promissor o uso de isopor como adesivo bem como sua utilização atrelada a painéis de fechamento. Entretanto, como os resultados de flexão estática não foram satisfatórios, prova-se que tais painéis não podem ser solicitados estruturalmente. Quanto aos outros ensaios realizados, todos os resultados foram favoráveis e, se utilizados conforme especificações técnicas, tornam-se coerentes para empregos em edificação. Como resultado, observou-se que os painéis podem ser produzidos e utilizados no mercado da construção civil, certificando que o produto pode ser empregado de forma segura, desde que sejam conhecidas suas funções, tempo de uso e manutenções necessárias. Desta forma, pretende-se contribuir para a produção e a análise de novos materiais que possam colaborar com a melhoria ambiental. / The particleboards, which are widely employed to manufacturing furniture, are established in the market, but they deserve a special attention due to their high cost considering the adhesives used on them and, paramountly, due to their vulnerability to humidity if on contact with their own parts. Facing the facts, this work presents a new alternative adhesive, applied with Styrofoam trims (EPS), usually found as residues, it may be used for involving the particles of wood, which are also used for manufacturing of the panels, and it makes it suitable for the use in environments directly related to humidity, whether it is internal or external to the building. Therewith, this work introduce the explanation and the proposition of the use of a new product in the shape of wood panel, produced with residual sawdust from sawmills, as particles and the EPS (Styrofoam) dissolved as an adhesive, which might also be used in construction. So, panels have been produced with four kinds of residual wood: pine, eucalyptus, teak and peroba. From each one of the samples, it has been manufactured ten boards for the evaluation of the physical and mechanical characteristics and other tests. From the results of physical description, it may be concluded the panels are in conformity with the requirements of the Brazilian standard NBR 14810-2 - \"Particleboards\" from ABNT (2006b), and due to low swelling values are appropriate to use it in humid and or outdoor environments. The results of mechanical description, the panels have shown satisfying results as for the internal connection and compression, indicating it is promising the use of Styrofoam as an adhesive and also its use in cable management panels. However, since the results of the static bending were not sufficient, it is proved such panels cannot be ordered, structurally. As for the other tests, all the results were positive and if they were used according to the technical specifications, they would become consistent for the application in construction. As a result, it was observed the panels might be produced and used in the market of construction, confirming the product may be applied safely as long as their functions are recognized, useful life, and required maintenance. In this way, it is intended to contribute to the production and analysis of new materials which may collaborate to improvement of the environment.
107

An analytical method for the determination of a dialkyl dimethyl quaternary ammonium chloride in beef liver tissue

Schmidt, Robert Charles January 2011 (has links)
Digitized by Kansas Correctional Industries
108

Dragagem, transporte e disposição final de sedimento de leito de rio - estudo de caso: Calha do Rio Tietê - Fase II. / Dredging, transport and final disposition of the river bed sediments - case study: Rio Tietê\'s Gutter - Phase II.

Lilian Rouse da Silva Lima 04 July 2008 (has links)
As obras de Ampliação da Calha do Rio Tietê fazem parte de medidas estruturais que visaram ao aumento da capacidade de vazão para o controle das enchentes na RMSP. A regularidade da capacidade de vazão dependerá, dentre outras ações, de dragagens de manutenção e retirada do material dragado, cuja destinação é bastante problemática. O objetivo deste trabalho é a elaboração de um estudo sobre o processo de dragagem, transporte e disposição final de material de leito de rio por meio da apresentação do processo adotado no estudo de caso: Ampliação da Calha do Rio Tietê Fase II. Para esse fim, são abordados os principais aspectos técnicos, ambientais, sociais e econômicos relativos às obras do estudo de caso, dando ênfase à gestão do sedimento dragado, que busca estar em consonância com as normas e diretrizes legais vigentes. São finalmente enunciadas as principais recomendações e conclusões que devem ser aplicadas na gestão do sedimento dragado do Rio Tietê. / The works of Enlargement of Rio Tietê\'s Gutter (Waterway) are part of structural measures that objective increase the flow capacity for inundation control in RMSP (Metropolitan Region of São Paulo). The regularity of the flow capacity will depend, among other actions, of maintenance dredgings and retreating of dredged material, whose destination is plenty of problem. The aim of this work is the elaboration of a study about the dredging process, transport and final disposition of the river bed sediment through the presentation of the process adopted in the case study: Enlargement of Rio Tietê\'s Gutter Phase II. For that purpose, the main technical, environmental, social and economical aspects related to the works of the case study are discussed, giving emphasis in the administration of the dredged sediment, that seek fitting to the in course norms and legal guidelines. Finally, the main recommendations and conclusions that should be applied in the administration of Rio Tietê\'s dredged sediment are examined.
109

Comportamento ambiental e bioatividade sobre plantas daninhas de herbicidas residuais aplicados sobre a palha de cana-de-açúcar em diferentes condições hídricas do solo / Behaviour and environmental bioactivityon weeds of herbicides residualapplied on sugarcane residues in different soil with water conditions

Paulo Vinícius da Silva 30 May 2018 (has links)
Herbicidas aplicados nos sistemas de cana-de-açúcar, diretamente no solo ou sobre palha, ficam disponíveis a fenômenos de transporte, retenção e transformação. Nesse contexto, o objetivo desse trabalho foiavaliar a lixiviação e sorção de herbicidas residuais em solos com diferentes características físicoquímicas e em palha de cana-de-açúcar. Para tal, foram realizados quatro experimentos. O primeiro relativo à lixiviação, através da metodologia de bioensaios, seguindo o esquema fatorial 8 x 2 x 2, em delineamento inteiramente casualizado, com quatro repetições, sendo oito profundidades do perfil do solo, dois períodos de seca (0 e 30 dias após a aplicação dos tratamentos - DAT) e duas quantidades de palha, esse fatorial foi adotado de forma individual para os herbicidas amicarbazone (1225 g i.a. ha-1 ); imazapic (147 g i.a ha- 1 ), sulfentrazone (800 g i.a ha-1 ) e tebuthiuron (900 g i.a ha-1 ). Os herbicidas foram aplicados no topo de colunas de solo montadas em tubos de PVC com 0 e 10 t ha-1 de palha, esses tratamentos foram submetidos aos três diferentes períodos de seca (0 e 30 DATs), ao final dessas épocas foi realizada uma simulação de chuva de 30 mm e realizada a semeadura de Cucumis sativus (planta bioindicadora), as avaliações de fitoxicidade foram efetuadas aos 7, 10 e 15 dias após a emergencia - DAE, aos 15 DAE foramrealizadas as avaliações de massa seca e altura da parte aérea das plantas. O segundo experimento consistiu na determinação de coeficientes de adsorção e dessorção (Kd e Koc) em 15 solos com diferentes características físico-químicas, para os herbicidas indaziflam, imazapic e amicarbazone. Foi utilizada a metodologia de herbicidas rádio marcados com C14, aplicou-se cinco diferentes concentrações dos herbicidas frios (0,125, 0,25, 0,50, 0,75 e 1,00 ppm), associados aos diferentes solos e herbicidas rádio marcados nas concentrações de 0,24 KBq de indaziflam, 0,26 KBq de imazapic ou 0,20 KBq de amicarbazone, de forma individual em cada unidade experimental. A concentração dos herbicidas rádio marcados presentes no sobrenadante foi determinada por espectroscopia de cintilação líquida (LSS) e por diferença entre a quantidade inicialmente aplicada e a presente na solução do solo, determinando-se adsorção. Através do mesmo processo também foi avaliada a dessorção dos herbicidas em quatro dias de análise. O terceiro experimento avaliou a adsorção de indaziflam, imazapic e amicarbazone em palha de cana-de-açúcar. Um estudo típico e equilíbrio em lotes foi conduzido para determinar adsorção e dessorção em diferentes concentrações dos herbicidas. A palha de cana-de-açúcar (0,27 g) foi combinada com três concentrações dos herbicidas (0,125, 0,5 e 1 ppm) mais os herbicidas radiomarcados nas seguintes quantidades: 0,24 KBq de indaziflam, 0,26 KBq imazapic e 0,20 KBq de amicarbazone. Após o estabelecimento do equilíbrio que foi de 24 horas para os três herbicidas, foi determinada a quantidade de herbicida adsorvida na palha de cana-de-açucar. Após a analise da adsorção, a solução presente nas unidades experimentais foi descartada e reposta por uma solução de cloreto de cálcio, e a dessorção foi então analisada após 24 horas, durante o período de um dia para amicarbazone, cinco dias para indaziflam, e não foi realizada analise de dessorção para o herbicida imazapic.Um quarto experimento, abordou a intercepção de herbicidas pela palha de cana-de-açúcar mediante a simulação de chuvas em diferentes precipitações (3, 6, 12 e 24 mm). Os herbicidas foram aplicados em duas quantidades de palha de cana-de-açúcar, as quais foram espalhadas de forma uniforme sobre uma tela de aço inoxidável (5 t ha-1 e 10 t ha-1), em seguida, essa tela foi colocada sobre um recipiente de vidro. As simulações de chuva ocorreram aos 0 horas, 24 horas e sete dias após a aplicação dos tratamentos. Para o herbicida amicarbazone aos 0 DAT sem palha, a lixiviação do herbicida amicarbazone foi notada ate os 25 cm, sendo os efeitos fitotoxicos mais expressivos observados nos primeiros 15 cm, já nas aplicações de 30 DAT, nos tratamentos com palha e sem palha a lixiviação foi notada até os 10 cm, com maior fitotoxicidade nos primeiros 5 cm. Na lixiviação tebuthiuron e imazapic e sulfentrazone a permanência do produto sobre a palha de cana-de-açúcar durante 30 DAT tornou a lixiviação desses herbicidas menor. Para o herbicida sulfentrazone a presença de palha imapctou de maneira mais expressiva na lixiviação desse herbicida que o perido de seca. Para imazapic e amicarbazone, os valores de Kd foram baixos devido à sua alta solubilidade em água; no entanto, a adsorção de imazapic foi fortemente influenciada pelo pH do solo, e para amicarbazone a adsorção e dessorção foi influenciada pela matéria orgânica e pH dos solos. Para indaziflam, Kd foi correlacionado negativamente com o teor de argila, mas foi positivamente correlacionado com a matéria orgânica. A adsorção de indaziflam foi superior a 80% em todas as concentrações, enquanto que a adsorção imazapic foi inferior a 7% em todas as concentrações. A adsorção de amicarbazone foi inferior a 20% em todas as concentrações. A dessorção de indaziflam foi de 30%, 28,5% e 27,5% a 0,125, 0,5 e 1 ppm, respectivamente, após 5 dias. A dessorção máxima para amicarbazone foi observada a 1 ppm com 11%. Para o indaziflam, após um período de sete dias após a aplicação dos herbicidas sobre a palha de cana-de-açúcar simulou-se uma precipitação de 24 mm resultando na remoção de apenas 25% do herbicida interceptado. Para o herbicida imazapic a palha de cana-de-açúcar não apresentou uma barreira de expressiva para interceptação desse produto. Dessa forma, as características dos herbicidas, como a solubilidade em água e Kow, podem ser utilizadas para determinar a sua dinâmica em sistemas de produção de cana-de-açúcar, sendo que os atributos lixiviação, sorção em palha e em solo, podem direcionar a uma predileção do comportamento agronômico e destino ambiental de herbicidas residuais. Dessa forma, pode-se concluir que a presença de palha na superfície do solo atrelada aos diferentes períodos de seca pode afetar a mobilidade desses herbicidas no ambiente. Conclui-se que as cracteristicas físico-quimicas dos herbicidas associadas com os atributos do solo podem direcionar a dinâmica de adsorção e dessorção dos herbicidas. As características dos herbicidas, como a solubilidade em água e Kow, podem ser utilizadas para determinar a dificuldade de remoção dos herbicidas em palha de cana-de-açucar. / Herbicides applied to sugar cane systems, directly on the soils our by residues, are available to transport, retention and transformation phenomenon. In this context, the objective of this work was to evaluate the leaching and sorption of residual herbicides in soils with different physicochemical characteristics and in sugarcane residues. Four experiments were carried out. The first, was based on the bioassay methodology, followed the 8 x 2 x 2 factorial scheme, in a completely randomized design, with four replications, eight depths of the soil profile, two dry periods (0 and 30 days after application of the treatments (DAT) and two quantities of residues, this factorial was adopted individually for the herbicides amicarbazone (1225 g ia ha-1); imazapic (147 g i.a ha-1), sulfentrazone (800 g i.a ha-1) and tebuthiuron (900 g i.a ha-1). The herbicides were applied to the top of soil columns mounted in PVC tubes with 0 and 10 t ha-1 of straw, these treatments were submitted to the three different periods of dry (0 and 30 DATs), at the end of those times a 30 mm rainfall simulation and Cucumis sativus sowing (bioindicator plant), phytotoxicity (7, 10 and 15 DAE), dry mass and shoot height were evaluated. It was noted that the greatest phytotoxicity of the herbicide amicarbazone was in the 0-5 cm layer. And that periods of drought and straw decreased the mobility of this herbicide in the columns. In leaching tebuthiuron, imazapic and sulfentrazone the permanence of the product on the sugarcane straw during 30 DAT made the leaching of this herbicide minor. Thus, it can be concluded that the presence of straw on the soil surface coupled to the different periods of drought can affect the mobility of these herbicides in the environment. The second experiment consisted in the determination of coeficivity of adosorption and desorption (Kd and Koc) in 16 soils with different physicochemical characteristics, for the herbicides indaziflam, imazapic and amicarbazone. The C14- labeled radio-herbicide methodology was used to apply five different concentrations of the cold herbicides (0.125, 0.25, 0.50, 0.75 and 1.00 ppm), associated with the different soils and herbicides radio -marked at the concentrations of 0.24 KBq of indaziflam, 0.26 KBq of imazapic or 0.20 KBq of amicarbazone, individually in each experimental unit. The concentration of radiolabelled herbicides present in the supernatant was determined by liquid scintillation spectroscopy (LSS) and by difference between the amount initially applied and the present in the soil solution, determining adsorption. Through the same process the herbicide desorption was also evaluated in four days of analysis For imazapic and amicarbazone, Kd values were low due to their high solubility in water; however, the adsorption of imazapic was strongly influenced by the pH of the soil, and for amicarbazone the adsorption and desorption was influenced by the organic matter and pH of the soils. For indaziflam, Kd was negatively correlated with clay content but was positively correlated with organic matter. The third experiment evaluated the adsorption of indaziflam, imazapic and amicarbazone in sugarcane straw. A typical study and batch equilibrium was conducted to determine adsorption and desorption at different concentrations of the herbicides. Sugarcane residues (0.27 g) was combined with three concentrations of the herbicides (0.125, 0.5 and 1 ppm) plus 0.24 KBq of indaziflam, 0.26 KBq imazapic or 0.20 KBq of labeled amicarbazone radio. The adsorption of indaziflam, imazapic and amicarbazone was evaluated 24, 48 and 120 hours, respectively, after the contact of sugarcane residues. Indaziflam adsorption was greater than 80% at all concentrations, while imazapic adsorption was below 7% at all concentrations. The adsorption of amicarbazone was less than 20% at all concentrations. Indaziflam desorption was 30%, 28.5% and 27.5% at 0.125, 0.5 and 1 ppm, respectively, after 5 days. Maximum desorption for amicarbazone was observed at 1 ppm with 11%. The desorption for imazapic was not determined due to the low initial adsorption. A fourth experiment, addressed the interception of herbicides by sugarcane straw through simulated rainfall in various amounts of precipitation (3, 6, 12 and 24 mm). Two amounts of sugarcane straw were uniformly spread over a stainless steel screen (5 t ha-1 and 10 t ha-1), then the screen was placed on a Pyrex® pan. The rain simulations occurred at 0 hr, 24 hrs and seven days after the treatments were applied. For indaziflam, a period of seven days after application of the herbicides on the sugarcane straw was simulated a precipitation of 24 mm resulting in the removal of only 25% of the adsorbed herbicide. For the herbicide imazapic the sugarcane straw did not present an expressive barrier to interception of this product. Thus, the characteristics of the herbicides, such as water solubility and Kow, can be used to determine their dynamics in sugarcane production systems, and the leaching, straw sorption and soil attributes can a predilection for agronomic behavior and environmental fate of residual herbicides.
110

Comportamento ambiental e bioatividade sobre plantas daninhas de herbicidas residuais aplicados sobre a palha de cana-de-açúcar em diferentes condições hídricas do solo / Behaviour and environmental bioactivityon weeds of herbicides residualapplied on sugarcane residues in different soil with water conditions

Silva, Paulo Vinícius da 30 May 2018 (has links)
Herbicidas aplicados nos sistemas de cana-de-açúcar, diretamente no solo ou sobre palha, ficam disponíveis a fenômenos de transporte, retenção e transformação. Nesse contexto, o objetivo desse trabalho foiavaliar a lixiviação e sorção de herbicidas residuais em solos com diferentes características físicoquímicas e em palha de cana-de-açúcar. Para tal, foram realizados quatro experimentos. O primeiro relativo à lixiviação, através da metodologia de bioensaios, seguindo o esquema fatorial 8 x 2 x 2, em delineamento inteiramente casualizado, com quatro repetições, sendo oito profundidades do perfil do solo, dois períodos de seca (0 e 30 dias após a aplicação dos tratamentos - DAT) e duas quantidades de palha, esse fatorial foi adotado de forma individual para os herbicidas amicarbazone (1225 g i.a. ha-1 ); imazapic (147 g i.a ha- 1 ), sulfentrazone (800 g i.a ha-1 ) e tebuthiuron (900 g i.a ha-1 ). Os herbicidas foram aplicados no topo de colunas de solo montadas em tubos de PVC com 0 e 10 t ha-1 de palha, esses tratamentos foram submetidos aos três diferentes períodos de seca (0 e 30 DATs), ao final dessas épocas foi realizada uma simulação de chuva de 30 mm e realizada a semeadura de Cucumis sativus (planta bioindicadora), as avaliações de fitoxicidade foram efetuadas aos 7, 10 e 15 dias após a emergencia - DAE, aos 15 DAE foramrealizadas as avaliações de massa seca e altura da parte aérea das plantas. O segundo experimento consistiu na determinação de coeficientes de adsorção e dessorção (Kd e Koc) em 15 solos com diferentes características físico-químicas, para os herbicidas indaziflam, imazapic e amicarbazone. Foi utilizada a metodologia de herbicidas rádio marcados com C14, aplicou-se cinco diferentes concentrações dos herbicidas frios (0,125, 0,25, 0,50, 0,75 e 1,00 ppm), associados aos diferentes solos e herbicidas rádio marcados nas concentrações de 0,24 KBq de indaziflam, 0,26 KBq de imazapic ou 0,20 KBq de amicarbazone, de forma individual em cada unidade experimental. A concentração dos herbicidas rádio marcados presentes no sobrenadante foi determinada por espectroscopia de cintilação líquida (LSS) e por diferença entre a quantidade inicialmente aplicada e a presente na solução do solo, determinando-se adsorção. Através do mesmo processo também foi avaliada a dessorção dos herbicidas em quatro dias de análise. O terceiro experimento avaliou a adsorção de indaziflam, imazapic e amicarbazone em palha de cana-de-açúcar. Um estudo típico e equilíbrio em lotes foi conduzido para determinar adsorção e dessorção em diferentes concentrações dos herbicidas. A palha de cana-de-açúcar (0,27 g) foi combinada com três concentrações dos herbicidas (0,125, 0,5 e 1 ppm) mais os herbicidas radiomarcados nas seguintes quantidades: 0,24 KBq de indaziflam, 0,26 KBq imazapic e 0,20 KBq de amicarbazone. Após o estabelecimento do equilíbrio que foi de 24 horas para os três herbicidas, foi determinada a quantidade de herbicida adsorvida na palha de cana-de-açucar. Após a analise da adsorção, a solução presente nas unidades experimentais foi descartada e reposta por uma solução de cloreto de cálcio, e a dessorção foi então analisada após 24 horas, durante o período de um dia para amicarbazone, cinco dias para indaziflam, e não foi realizada analise de dessorção para o herbicida imazapic.Um quarto experimento, abordou a intercepção de herbicidas pela palha de cana-de-açúcar mediante a simulação de chuvas em diferentes precipitações (3, 6, 12 e 24 mm). Os herbicidas foram aplicados em duas quantidades de palha de cana-de-açúcar, as quais foram espalhadas de forma uniforme sobre uma tela de aço inoxidável (5 t ha-1 e 10 t ha-1), em seguida, essa tela foi colocada sobre um recipiente de vidro. As simulações de chuva ocorreram aos 0 horas, 24 horas e sete dias após a aplicação dos tratamentos. Para o herbicida amicarbazone aos 0 DAT sem palha, a lixiviação do herbicida amicarbazone foi notada ate os 25 cm, sendo os efeitos fitotoxicos mais expressivos observados nos primeiros 15 cm, já nas aplicações de 30 DAT, nos tratamentos com palha e sem palha a lixiviação foi notada até os 10 cm, com maior fitotoxicidade nos primeiros 5 cm. Na lixiviação tebuthiuron e imazapic e sulfentrazone a permanência do produto sobre a palha de cana-de-açúcar durante 30 DAT tornou a lixiviação desses herbicidas menor. Para o herbicida sulfentrazone a presença de palha imapctou de maneira mais expressiva na lixiviação desse herbicida que o perido de seca. Para imazapic e amicarbazone, os valores de Kd foram baixos devido à sua alta solubilidade em água; no entanto, a adsorção de imazapic foi fortemente influenciada pelo pH do solo, e para amicarbazone a adsorção e dessorção foi influenciada pela matéria orgânica e pH dos solos. Para indaziflam, Kd foi correlacionado negativamente com o teor de argila, mas foi positivamente correlacionado com a matéria orgânica. A adsorção de indaziflam foi superior a 80% em todas as concentrações, enquanto que a adsorção imazapic foi inferior a 7% em todas as concentrações. A adsorção de amicarbazone foi inferior a 20% em todas as concentrações. A dessorção de indaziflam foi de 30%, 28,5% e 27,5% a 0,125, 0,5 e 1 ppm, respectivamente, após 5 dias. A dessorção máxima para amicarbazone foi observada a 1 ppm com 11%. Para o indaziflam, após um período de sete dias após a aplicação dos herbicidas sobre a palha de cana-de-açúcar simulou-se uma precipitação de 24 mm resultando na remoção de apenas 25% do herbicida interceptado. Para o herbicida imazapic a palha de cana-de-açúcar não apresentou uma barreira de expressiva para interceptação desse produto. Dessa forma, as características dos herbicidas, como a solubilidade em água e Kow, podem ser utilizadas para determinar a sua dinâmica em sistemas de produção de cana-de-açúcar, sendo que os atributos lixiviação, sorção em palha e em solo, podem direcionar a uma predileção do comportamento agronômico e destino ambiental de herbicidas residuais. Dessa forma, pode-se concluir que a presença de palha na superfície do solo atrelada aos diferentes períodos de seca pode afetar a mobilidade desses herbicidas no ambiente. Conclui-se que as cracteristicas físico-quimicas dos herbicidas associadas com os atributos do solo podem direcionar a dinâmica de adsorção e dessorção dos herbicidas. As características dos herbicidas, como a solubilidade em água e Kow, podem ser utilizadas para determinar a dificuldade de remoção dos herbicidas em palha de cana-de-açucar. / Herbicides applied to sugar cane systems, directly on the soils our by residues, are available to transport, retention and transformation phenomenon. In this context, the objective of this work was to evaluate the leaching and sorption of residual herbicides in soils with different physicochemical characteristics and in sugarcane residues. Four experiments were carried out. The first, was based on the bioassay methodology, followed the 8 x 2 x 2 factorial scheme, in a completely randomized design, with four replications, eight depths of the soil profile, two dry periods (0 and 30 days after application of the treatments (DAT) and two quantities of residues, this factorial was adopted individually for the herbicides amicarbazone (1225 g ia ha-1); imazapic (147 g i.a ha-1), sulfentrazone (800 g i.a ha-1) and tebuthiuron (900 g i.a ha-1). The herbicides were applied to the top of soil columns mounted in PVC tubes with 0 and 10 t ha-1 of straw, these treatments were submitted to the three different periods of dry (0 and 30 DATs), at the end of those times a 30 mm rainfall simulation and Cucumis sativus sowing (bioindicator plant), phytotoxicity (7, 10 and 15 DAE), dry mass and shoot height were evaluated. It was noted that the greatest phytotoxicity of the herbicide amicarbazone was in the 0-5 cm layer. And that periods of drought and straw decreased the mobility of this herbicide in the columns. In leaching tebuthiuron, imazapic and sulfentrazone the permanence of the product on the sugarcane straw during 30 DAT made the leaching of this herbicide minor. Thus, it can be concluded that the presence of straw on the soil surface coupled to the different periods of drought can affect the mobility of these herbicides in the environment. The second experiment consisted in the determination of coeficivity of adosorption and desorption (Kd and Koc) in 16 soils with different physicochemical characteristics, for the herbicides indaziflam, imazapic and amicarbazone. The C14- labeled radio-herbicide methodology was used to apply five different concentrations of the cold herbicides (0.125, 0.25, 0.50, 0.75 and 1.00 ppm), associated with the different soils and herbicides radio -marked at the concentrations of 0.24 KBq of indaziflam, 0.26 KBq of imazapic or 0.20 KBq of amicarbazone, individually in each experimental unit. The concentration of radiolabelled herbicides present in the supernatant was determined by liquid scintillation spectroscopy (LSS) and by difference between the amount initially applied and the present in the soil solution, determining adsorption. Through the same process the herbicide desorption was also evaluated in four days of analysis For imazapic and amicarbazone, Kd values were low due to their high solubility in water; however, the adsorption of imazapic was strongly influenced by the pH of the soil, and for amicarbazone the adsorption and desorption was influenced by the organic matter and pH of the soils. For indaziflam, Kd was negatively correlated with clay content but was positively correlated with organic matter. The third experiment evaluated the adsorption of indaziflam, imazapic and amicarbazone in sugarcane straw. A typical study and batch equilibrium was conducted to determine adsorption and desorption at different concentrations of the herbicides. Sugarcane residues (0.27 g) was combined with three concentrations of the herbicides (0.125, 0.5 and 1 ppm) plus 0.24 KBq of indaziflam, 0.26 KBq imazapic or 0.20 KBq of labeled amicarbazone radio. The adsorption of indaziflam, imazapic and amicarbazone was evaluated 24, 48 and 120 hours, respectively, after the contact of sugarcane residues. Indaziflam adsorption was greater than 80% at all concentrations, while imazapic adsorption was below 7% at all concentrations. The adsorption of amicarbazone was less than 20% at all concentrations. Indaziflam desorption was 30%, 28.5% and 27.5% at 0.125, 0.5 and 1 ppm, respectively, after 5 days. Maximum desorption for amicarbazone was observed at 1 ppm with 11%. The desorption for imazapic was not determined due to the low initial adsorption. A fourth experiment, addressed the interception of herbicides by sugarcane straw through simulated rainfall in various amounts of precipitation (3, 6, 12 and 24 mm). Two amounts of sugarcane straw were uniformly spread over a stainless steel screen (5 t ha-1 and 10 t ha-1), then the screen was placed on a Pyrex® pan. The rain simulations occurred at 0 hr, 24 hrs and seven days after the treatments were applied. For indaziflam, a period of seven days after application of the herbicides on the sugarcane straw was simulated a precipitation of 24 mm resulting in the removal of only 25% of the adsorbed herbicide. For the herbicide imazapic the sugarcane straw did not present an expressive barrier to interception of this product. Thus, the characteristics of the herbicides, such as water solubility and Kow, can be used to determine their dynamics in sugarcane production systems, and the leaching, straw sorption and soil attributes can a predilection for agronomic behavior and environmental fate of residual herbicides.

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