Dissertations / Theses on the topic 'Sorption/desorption'

Master of Science
Department of Agronomy
Nathan O. Nelson
Phosphorus (P) is an essential nutrient in crop production, but P inputs to surface waters have resulted in impairments such as eutrophication and algae blooms. Non-point sources such as agricultural fields are a main contributor of P. Kansas, being a high agricultural dependent state, has frequent fresh water body impairments. Multiple erosion and transport processes contribute to P loss. While P loss from sheet and rill erosion has been studied extensively, P loss from ephemeral gully erosion is largely unknown. The objective of this study is to understand the effects ephemeral gullies have on the transport and transformation of P. Three fields in McPherson County with well-defined ephemeral gullies were studied. Soil samples were taken in field locations that are effected by ephemeral gullies at the 0 to 2, 2 to 5, 5 to 15, and 15 to 30 cm depths. Samples were analyzed for total P, anion exchange phosphorus (AEP) (labile P), ammonium-oxalate extractable Fe, Al, and P (Fe[subscript]ox, Al[subscript]ox, P[subscript]ox), Mehlich 3 extractable Fe, Al, Ca, and P (Fe[subscript]M3, Al[subscript]M3, Ca[subscript]M3, P[subscript]M3), equilibrium phosphorus concentration at zero net sorption (EPC[subscript]0), 1:1 soil to water pH, and texture. Soil testing showed that P quantities tend to be much higher in surface soils eroded by sheet and rill erosion and lower in subsoil soil that is eroded by ephemeral gullies. The quantity of sorptive elements such as Fe and Al, were not significantly different throughout the tested area except in areas of changing soil texture. EPC[subscript]0 testing showed it was likely that P desorbs from the surface erosion of sheet and rill and is adsorbing onto the subsoil eroded from ephemeral gullies. Sediment eroded by ephemeral gullies has a P buffering capacity greater than the sediment eroded by sheet and rill, and a small quantity of ephemeral gully subsoil will have a large effect on the dissolved P concentration of runoff. Sediment, total P loss and expected dissolved P in runoff was surveyed and modeled for two of the fields. Ephemeral gullies contributed to a majority of sediment and total P loss. The addition of ephemeral gully sediment to the erosional mix of sheet and rill sediment caused the dissolved P concentration to decrease from 0.0204 to 0.0034 mg L[superscript]-1 in one field and from 0.0136 to 0.0126 mg L[superscript]-1 in another. The results of this study show that best management practices (BMPs) such as grass waterways could cause the losses of total P to decrease as much as 2 to 12 times in fields with ephemeral gullies. However, reducing ephemeral gully erosion will likely increase dissolved P concentrations up to 600% more in runoff. Therefore, BMPs need to be combined to fully control P loss from agricultural fields.

A series of twelve laboratory column experiments were conducted to determine equilibrium partitioning coefficients (K ) and kinetic rate coefficients for sorption of four hydrophobic pollutants on a low organic carbon natural soil. K 's for trichloroethene (ICE), tetrachloroethene (PCE), 1,1,1-trichloroethane (TCA), and 1,1,2,2-tetrachloroethane (PCA), were 0.17, 0.44, 0.06, and 0.05, respectively; about as expected based on empirical carbon-based partitioning equations found in the literature. Tailing of the breakthrough curves could be accounted for with a two-site non-equilibrium solute transport model. Rates were fast compared to pore water velocities normally encountered in an alluvial aquifer, but kinetic effects were observed at pore water velocities likely to be encountered during pumping, such as for site cleanup. Desorption was faster than adsorption, with forward rates of about 10⁻⁴ to 10⁻⁵ s⁻¹ and reverse rates about 10⁻³ to 10⁻⁴ s⁻¹. The two-site model indicated that slower sites constituted roughly half the total number of sites.

In natural systems, the solution concentration and hence, potential bioavailability of trace metals is primarily controlled by adsorption-desorption reactions at the mineral-water interface. While many studies have been conducted to understand the adsorption of trace metals to soil minerals, less is known about long-term adsorption/desorption processes. In this study, we examined the influence of mixing and sorption period on the desorption of lead from goethite. Lead sorption was rapid and essentially complete in 1 h, with no change in the quantity of lead adsorbed over the 6 month sorption period. Desorption of lead was slower than the adsorption reaction and was best modeled by two first order equations. At all sorption densities, the desorption of lead followed the order Short-term (24 h) > Long-term non-stirred (6 months) > Long-term stirred (6 months). However, statistical analysis indicated that these differences were not statistically significant. Furthermore, the desorption rate coefficients were very similar for all the experiments indicating that there was no significant residence time effect in this study. However, a sample from a previous study that was allowed to age 5 years and then analyzed by the desorption procedure did have statistically significant differences between the long-term (5 years) and the short-term (5 months). These results suggest that longer adsorption periods, perhaps a number of years, may be necessary to determine if residence time effects are an artifact of the experimental conditions or truly the length of the adsorption period.
Master of Science

A series of bench-scale experiments was carried out to determine the rate and efficiency with which benzene and p-xylene, components of gasoline, could be removed from an unsaturated soil by air stripping. Glass columns, 30 cm in length, were packed with soil and wetted to volumetric moisture contents of 10 and 18 percent. Air saturated with one of the volatile organic compounds (VOCs) was used to load the column. Clean air was used to strip the contaminant from the soil. Benzene and p-xylene concentrations in the soil water and air were reduced four orders of magnitude after a few hours (2-8) of stripping. Benzene was removed faster than p-xylene. Air flow was the rate-limiting step early in the stripping, however slow desorption from the soil became rate-limiting as the stripping progressed. As moisture content increased the rate of removal of both contaminants decreased.

Táto práca sa zameriava problematiku interakcie ibuprofénu s pôdnym systémom. Popísané sú jeho základné vlastnosti, správanie a faktory ovplyvňujúce toto správanie. Vo všeobecnosti najvplyvnejšími faktormi je prítomnosť pôdnej organickej hmoty v pôde a pH. Ibuprofén patrí do skupiny nesteroidných protizápalových liečiv. Patrí medzi ľahko dostupné a vysoko konzumované liečivá. Toto prispieva k jeho narastajúcemu transportu a kontaminácii životného prostredia. Jeho prítomnosť v životnom prostredí môže pôsobiť negatívne na živé organizmy. V experimentálnej časti bol preskúmaný vplyv pôdnej organickej hmoty a pH na sorpciu a desorpciu ibuprofénu. Použité boli tri pôdy získané z odlišných regiónov Českej republiky. V rámci procesu sorpcie a desorpcie boli použité koncentrácie v rozmedzí 1 až 10 mg/l. Vplyv pH na sorpciu a desorpciu bol preskúmaný použitím koncentrácie ibuprofénu 10 mg/l a Britton-Robinsonovho pufru s pH 3, 7 a 10. Detekcia ibuprofénu v jednotlivých vzorkách bola uskutočnená pomocou UV-VIS spektrometrie a kvapalinovej chromatografie s hmotnostne spektrometrickou detekciou.

Polyethylene pipes and epoxy or polyurethane linings are increasingly used in drinking water infrastructure. As a recent introduction to the water industry, there are still many unknowns about how polymers will behave in the distribution system specifically relating to sorption and desorption of chemical contaminants. This study is in response to a spill of 4-methylcyclohexane methanol (MCHM) that occurred in January 2014 contaminating the drinking water of nine counties in West Virginia. This study investigated sorption and desorption of the odorous chemical MCHM into polymer drinking water infrastructure and granular activated carbon (GAC). Experiments for sorption of non-polar toluene and polar 1-butanol were conducted as a comparison for MCHM sorption. Additionally, a brief odor analysis was done on the ability of activated carbon to remove odor from contaminated water and on leaching of MCHM from pipe material into clean water. The results show that MCHM diffusion and solubility in polyethylene pipe materials is low. Solubility in polyethylene ranged from 0.003-0.008 g/cm3 and was more similar to the polar contaminant n-butanol than the non-polar contaminant toluene. Desorption experiments indicated that MCHM sorbed to polyethylene diffused back into water at levels that produced odor. MCHM diffused very quickly into epoxy; its solubility was similar to polyethylene pipe. MCHM caused the polyurethane lining to swell and deform. Granular activated carbon effectively sorbed MCHM to below its odor threshold. The sorption properties of MCHM indicate the potential for contamination of infrastructure and the desorption indicates subsequent recontamination of drinking water.
Master of Science

Dans le contexte des futurs stockages des matières nucléaires en couches géologiques profondes, le transfert desélénium 79 des eaux de nappes vers la biosphère, par le biais de l'irrigation, est un des scenarii envisagés parl'ANDRA. Le sol servirait alors d'interface entre la géosphère et la biosphère.Le modèle actuellement utilisé pour évaluer la mobilité de nombreux éléments dans le sol repose sur une représentationsimple de leur distribution entre la quantité adsorbée sur le sol et la quantité restante en solution (modèleKd), considérée comme instantanée, réversible et linéaire avec la concentration de contamination. Ce modèleprésente des lacunes vis-à-vis du sélénium puisque ce dernier peut être présent sous différents états redoxqui contrôlent sa mobilité et dont les cinétiques de transformation entre ces états sont peu connues (Se(-II), Se(0),Se(IV) et Se(VI)).Dans le but d'améliorer les prédictions faites sur la mobilité du sélénium dans un sol, le séléniate (Se(VI)), qui estla forme la plus mobile, a été utilisé pour étudier ses interactions vis-à-vis de deux sols différents (sol B et sol R).Un modèle cinétique, alternatif au modèle Kd, a été développé pour décrire l'évolution des stocks de Se(VI) ensolution, en considérant une fraction de sélénium associée au sol de façon réversible (potentiellement mobile) etune fraction stabilisée sur le sol (fixée pseudo-irréversiblement). Ce modèle intègre des cinétiques de stabilisationbiotique et abiotique sur le sol, et une cinétique de réduction en solution.Afin d'acquérir les paramètres des modèles, des expériences en batchs et en réacteurs à flux ouvert avecl'utilisation de sacs à dialyse ont été réalisées. L'acquisition des paramètres a permis de confronter les modèlescinétiques et Kd dans différents scenarii réalistes de contamination (chronique ou séquentielle) d'un sol de surfacepar du 79Se(VI).De plus, les mécanismes de sorption du Se(VI) au sein des deux sols ont été évalués en batch avec l'ajout de compétiteursspécifiques vis-à-vis de certains sites pouvant sorber ce dernier (acides humiques et carbonates de calcium).Ceci a été complété avec l'étude de la sorption du Se(VI) sur des phases pures commerciales (silice, hydroxyded'aluminium, goethite, bentonite, carbonate de calcium et acides humiques) ou extraites d'un sol (substanceshumiques), pour différentes concentrations en Se(VI) (10-8, 10-6 et/ou 10-3 mol/L), de l'impact de l'ajout dephases pures réactives, dans les sols, sur la sorption du Se(VI).Il a été montré que le Se(VI) était sorbé sous la forme de complexes de sphères externes (CSE) au sein du sol Rpour des concentrations inférieures à 10-6 mol/L, tandis que dans le sol B, la majorité était sorbée sous la formesde complexes de sphère internes (CSI). La formation de CSE étant réversible et instantanée, l'utilisation du modèleKd était donc suffisante pour décrire la sorption du Se(VI) au sein du sol R, dans les expériences en réacteursà flux ouvert.A contrario, pour le sol B, il a été montré que le modèle Kd, contrairement au modèle cinétique, présentait deslacunes pour décrire la sorption pseudo-irréversible du Se(VI), engendrée par la formation de CSI.Il a été montré que les mécanismes biotiques étaient majoritaires au sein du sol B, en raison de l'apport de nutrimentspour les microorganismes, par l'utilisation de sacs à dialyse en cellulose régénérée. Cependant les mécanismesabiotiques ont aussi eu lieux au sein du sol B.14/256Les études sur les phases pures ont montré que seuls l'hydroxyde d'aluminium (pH 5,2 et 8) et la goethite (pH 5,2)pouvaient sorber le Se(VI) respectivement de manière pseudo-irréversible et réversible (pour [Se(VI)] < 10-6mol/L).Enfin, il a été montré que l'ajout de certaines phases pures (goethite et hydroxyde d'aluminium) au sein des deuxsols, pouvait entrainer une augmentation ou une diminution de la sorption du Se(VI) par rapport à celle attendue(additivité réactionnelle). Les interactions solide/solide directes et/ou indirectes, (la plus connue étant le coating)peuvent être à l'origine de la difficulté d'évaluation, de manière générique, de la sorption du Se(VI) au sein dusol, connaissant seulement sa composition élémentaire.

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.

Master of Science
Department of Civil Engineering
Alok Bhandari
In the upper Midwest, subsurface tile drainage water is a major contributor of nitrate (NO[subscript]3–N) coming from fertilizers and animal manure. Movement of NO[subscript]3-N through tile drainage into streams is a major concern as it can cause eutrophication and hypoxia conditions, as in the Gulf of Mexico. Denitrifying bioreactors is one of the pollution control strategies to treat contaminated tile drainage water. These bioreactors require four conditions which are: 1) organic carbon source, 2) anaerobic conditions, 3) denitrifying bacteria and 4) influent NO[subscript]3-N. This research focuses on investigating fate of veterinary antibiotics in woodchips commonly used in in-situ reactors. Tylosin (TYL) and sulfamethazine (SMZ) are two veterinary antibiotics which are most commonly used in the United States and can be found in tile water after manure is land applied. Partition coefficients of TYL and SMZ on wood were determined by sorption experiments using fresh woodchips and woodchips from an in situ reactor. It was concluded that the woodchips were an effective means to sorb the veterinary antibiotics leached into the tile water after application of animal manure. Linear partition coefficients were calculated and phase distribution relationships were established for both the chemicals. The fresh woodchips gave inconclusive data but predictions could be made by the information determined in the experiments using woodchips from a ten year old woodchip bioreactor. Desorption was also studied and the likelihood of desorption was predicted using the Apparent Hysteresis Index. Overall, it was found that the old woodchips allowed for quick sorption of both antibiotics. It was also found that SMZ had reversible sorption on old woodchips. Thus, it was concluded that the woodchip bioreactor would not be effective for removal of veterinary antibiotics from tile drainage. More research is required for the fate of TYL and to confirm the conclusion.

A distinção de doses dos herbicidas residuais encontradas nas recomendações oficiais para a agricultura está normalmente baseada nas classes texturais dos solos (arenosa, média e argilosa), que são distinguidas pelos teores de argila na camada superficial de solo. No entanto, a disponibilidade dos herbicidas residuais na solução do solo é função do processo de sorção, que é determinado principalmente pelas variações percentuais dos atributos do solo: teor de argila, matéria orgânica e capacidade de troca catiônica (CTC). Portanto, a recomendação de doses dos herbicidas residuais pelas classes texturais do solo pode não ser adequada. Sendo assim, foi desenvolvida a presente pesquisa com o objetivo de avaliar o comportamento sortivo dos herbicidas residuais diuron e hexazinone em função de atributos de quatro tipos de solos de texturas contrastantes, e assim verificar a correlação destes atributos com a disponibilidade dos herbicidas para as plantas. As amostras de solo foram coletadas em quatro áreas de produção de cana-de-açúcar do Estado de São Paulo, e apresentaram variações consideráveis no conteúdo de argila (6 a 67%), areia (22 a 93%), capacidade de troca catiônica (CTC) (58,7 a 152,8 mmolc dm-3) e carbono orgânico (C.O.) (13,95 a 19,19 g.kg-1). Foi utilizado o método batch com herbicida radiomarcado (14C), utilizando-se 2,0 g de solo para o herbicida diuron e 4,0 g para o herbicida hexazinone, e como substância extratora dos herbicidas o CaCl2 em volume de 8,0 mL. Cinco concentrações de cada herbicida foram utilizadas, sendo para o diuron: 0,19; 0,42; 0,84; 1,68 e 3,34 mg.L-1 e para o hexazinone: 0,12; 0,22; 0,66; 2,17 e 6,03 mg.L-1. Os resultados permitiram concluir que o solo arenoso estudado apresentou baixa capacidade de adsorção e intensa dessorção de diuron, no entanto para os solos argilosos o processo de sorção e retenção de diuron foi intenso. Houve uma correlação positiva entre a sorção de diuron com os teores de matéria orgânica e argila. Os valores de Kd para o diuron foram maiores nos solos com maior teor de C.O. (g kg-1) e argila (%); sendo que de maneira geral, a sorção do diuron foi mais relacionada com o teor de C.O. do solo, que com a argila. Os valores de Kd, Koc e Kf(sor) do herbicida hexazinone foram maiores nos solos com maior teor de C.O. (g kg-1) e argila (%). O processo de dessorção do herbicida hexazinone foi intenso para todos os solos estudados, sendo que os valores de Kf(des) foram maiores que seus respectivos Kf(sor), indicando que o processo de dessorção envolve mecanismos com menor energia de ligação que a sorção. As recomendações de doses dos herbicidas diuron e hexazinone deveriam levar em consideração outros atributos do solo, além da textura como normalmente é utilizado na prática.
The distinction of the recommendation rates of the residual herbicide found in the official recommendations for agriculture is normally based on three soil texture classes (sandy, medium and clayey), which are distinguished by the clay content in the soil top layer. However, the availability of the residual herbicides in the soil solution is function of the of the sorption process, which is determined mainly by the percent variations of the soil clay and organic matter content, and cationic exchange capacity (CEC). Therefore, the rate recommendations of residual herbicides by textural classes might not be adequate. Therefore, it was developed this research with the objective of evaluating the sorptive behavior of the herbicides diuron and hexazinone function of the four types of soil attributes of contrasting textural properties, and then verify the correlation of the soil attributes with the availability of these herbicides to plants. The soil samples were collected in four sugarcane production areas of São Paulo State, Brazil, presenting considerable variations in the content of clay (6 to 67%), sand (22 to 93%), cationic exchange capacity (CEC) (58.7 to 152.8 mmolc dm3) and organic carbon (O.C.) (13.95 to 19.19 g.kg-1). It was used the batch method with the radio labeled (14C) herbicide, using 2.0 g of soil for the herbicide diuron, and 4.0 g of soil for the herbicide hexazinone, and as herbicide extractor substance the CaCl2 in volume of 8.0 mL. Five concentrations of each herbicide were used, being for the diuron 0.19; 0.42; 0.84; 1.68 and 3.34 mg.L-1 and for hexazinone: 0.12; 0.22; 0.66; 2.17 and 6.03 mg.L-1. The sandy soil studied presented low sorption capacity and intense desorption of diuron, however, for clayey soils the sorption and retention process of diuron was more intense. The Kd values for diuron were higher in soils with higher content of O.C (g kg-1) and clay (%), so in general, the sorption of diuron was more correlated to the O.C. content of the soil, than to the clay content. The values of Kd, Koc, and Kf(sor) of the herbicide hexazinone were higher for the soils with higher content of O.C (g kg-1) and clay (%). The process of desorption of the herbicide hexazinone was intense for all the studied soils; the values of Kf(des) were higher than the respective Kf(sor), indicating that the process of desorption involves mechanisms with higher energy of linkage, than the sorption. The recommendations of herbicide rates of diuron and hexazinone to sugarcane should take into account other soil attributes, besides the texture each is normally used in the suggestions of the herbicide rates.

Svenska Aerogel AB has developed the material Quartzene® which is of the typeprecipitated silica and contains calcium - magnesium silicate ((Ca, Mg) SiO3). Thematerial is used for molecular filtration of contaminated air. Qartzene™, which is inpellet form, is porous and has a high internal surface which is a requirement for themolecular filtration. With the use of various impregnations, filtration can affect thedesired outcome. As an example Quartzene® can be impregnated with Potassiumhydroxide and clear the air of Sulfur dioxide, SO2 (Svenska Aerogel AB, n.d).Svenska Aerogel AB has developed Quartzene® further and new areas of application hasarosee, one of these areas is how the material function within dehumidification. Thepurpose of this study is to research and analyze how different impregnation salts effecthow Quartzene® function in terms of moisture absorption and moisture desorption.Quartzene® is a hygroscopic material, which is a material that easily absorbs and exudatesmoisture from the air. Materials with high porosity absorb moisture by adsorption andcapillary condensation. A hygroscopic material strives for equilibrium with ambientenvironment which is illustrated in a sorption curve where moisture absorption is set inrelation to relative humidity. In this study the jar method is used to measure moistureabsorption, this is shown with the use of sorption curves. The jar method uses saturatesalt solutions to create environments whit a set relative humidity. Quartzene® – pellets areplaced in jars and weighed at regular intervals to determine the moisture absorption.The results of this study indicate that impregnations affect the way that Quartzene®function in terms of moisture absorption and moisture desorption. Some of theimpregnations affect the material to absorb more moisture than Quartzene® that has notbeen impregnated, while others affect the material to absorb less moisture. The resultsalso show that sodium – based impregnation gives similar results as Quartzene® that hasnot been impregnated.

Increasing concern about the pollution of environment by inorganic and organic chemicals arising from naturally occurring ecological events and industrial processes has created a need for the search of new techniques in the removal of these contaminants. One of the natural material that can be used in such processes is clay. Clay minerals have large surface areas and high cation exchange capacities which enables them to be modified by cationic surfactants. The material prepared, often called as &
#8216
organoclay&
#8217
, can be used to remove hydrophobic organic and anionic contaminants from polluted water. Among the anionic contaminants, oxyanions such as nitrate, chromate are detrimental to human life and environment even at µ
g/L- mg/L levels. Application of organoclays for their removal from polluted water appears as one of the practical and rather cheap solution. In this study, a local clay from Ankara-Kalecik (Hanç
ili Bentonite) was modified by hexadecyltrimethylammonium bromide (HDTMA-Br) to a level of twice of its cation exchange capacity. This process alters the negatively charged surface of the clay into a positively charged one, providing sites for the removal of anionic contaminants. In this study, the degree of HDTMA+ uptake by the clay within a period of eight hours is found to be 97% of the initial amount added. In desorption studies it was revealed that only about 1% of the sorbed HTDMA+ was leached in a seven days of water-organoclay interaction revealing a rather stable organoclay structure in aqeous media. Sorption experiments with nitrate, borate, and chromate solutions were performed in order to determine the anion sorption capacity of the organoclays prepared. It turns out that while untreated clay has insignificant capacity, the modified clay can remove considerable amount of nitrate and chromate ions from aqeous solutions. While the nitrate sorption was increased about eleven fold, change in chromate sorption was reached to a level of twenty fold compared to that of the untreated clay. Sorption data for nitrate and chromate are both well described by the Langmuir isotherms. No significant change was observed in case of borate-organoclay interaction. Desorption of nitrate and chromate ions from organoclay surface were also investigated. Sorption of these oxyanions were found to be almost irreversible in aqeous media. The results imply that a properly prepared organoclay can be used for the removal of oxyanions, such as nitrate and chromate from polluted water systems.

O objetivo deste trabalho foi avaliar o método de fluxo em colunas de solo e o método “batch” na determinação da sorção de imazaquin; avaliar a cinética de sorção e dessorção do imazaquin em solos através do método “batch” e; determinar a sorção dependente do tempo do diuron e sua interação com o tamanho dos agregados do solo. Na primeira parte foi avaliada a sorção e a mobilidade do imazaquin em solos com diferentes características químicas, físicas e mineralógicas utilizando as técnicas de deslocamento miscível e “batch”. Com os dados de lixiviação do imazaquin utilizou-se um modelo matemático bicontínuo que considera a sorção sob condições de não-equilíbrio. O modelo forneceu alguns parâmetros de sorção e transporte do imazaquin através da coluna. No método “batch” os dados experimentais foram ajustados à equação de Freundlich, que também forneceu parâmetros de sorção. Na segunda parte foram estudadas a sorção e dessorção do imazaquin em solos com diferentes características químicas e mineralógicas através do uso de isotermas e estudos de cinética e assim quantificar a histerese no processo de sorção-dessorção. Para todos estes ensaios foi utilizado o método “batch”, com os dados das isotermas de sorção e dessorção sendo ajustados pela equação de Freundlich. Os dados de cinética foram ajustados pela equação de Elovich. No terceira e última parte foi avaliada a sorção do diuron em função do tempo de incubação e do tamanho do agregado do solo, assim como a interação destes dois fatores. Em períodos pré-determinados, amostras de solo incubadas com o diuron foram extraídas e oxidadas, obtendo-se as frações em equilíbrio com a solução, sorvida e resíduo-ligado. Com relação aos resultados, o imazaquin apresentou baixa sorção e alta mobilidade em coluna para todos os solos estudados, principalmente o mais arenoso. A curva de eluição do imazaquin ajustou-se ao modelo matemático que considera a sorção ocorrendo sob condição de não-equilíbrio. O método do deslocamento miscível apresentou os menores valores de Kd para o imazaquin, comparado ao método “batch”, sendo atribuída esta diferença ao não-equilíbrio no processo de sorção durante o transporte do imazaquin na coluna. No estudo de sorção/dessorção do imazaquin constatou-se que os coeficientes de sorção do imazaquin foram baixos para todos os solos, com a menor sorção sendo observada no solo RQ que apresenta baixos teores de argila e carbono orgânico do solo. Os coeficientes de dessorção do imazaquin foram maiores que seus coeficientes de sorção, demonstrando ocorrer histerese na dessorção. A histerese foi observada em todos os solos. A sorção do imazaquin ocorreu em duas fases, sendo que a segunda fase, mais lenta, é influenciada por processos difusivos. No estudo de incubação do diuron, houve correlação negativa entre o diuron extraído em solução de CaCl2 e o conteúdo de carbono orgânico no solo. Não foi observada interação entre o tempo de incubação e o tamanho dos agregados, evidenciando que a sorção dependente do tempo, neste caso, não está relacionada à estrutura do solo. A fração sorvida de diuron aumentou com o tempo de incubação, indicando que o processo de sorção é dependente do tempo.
The aim of this study was to evaluate the column flow and batch methods in the measurement of the imazaquin sorption: to evaluate de sorption kinetic and desorption of the imazaquin in soil by batch method and; to evaluate the time-dependent sorption of the diuron and the interaction with the aggregate size of the soil. In the first part it was evaluated the imazaquin mobility and sorption in soils with different mineralogical, physical and chemical characteristics. The imazaquin breakthrough curves were fitted by a mathematical model that considers the nonequilibrium sorption. The model provided sorption and transport parameters. In the batch method the experimental data were fitted to Freudlinch equation, which provided also the sorption parameters. In the second part were studied the imazaquin sorption/desorption in soils with with different mineralogical, physical and chemical characteristics. It was carried out by batch method and kinetics studies, which allowed quantifying the hysteresis in the sorption-desorption process. The experimental data were fitted to the Elovich equation. In the third and last part it was evaluated the time dependent sorption of the diuron and the influence of the aging and aggregate size. Samples of aged soil were extracted and combusted in pre-determined periods. It was obtained the equilibrium, sorbed and bound-residue fractions. Regarding the results, the imazaquin showed low sorption and high mobility in columns for the three soils, mainly the sandy soil. The imazaquin breakthrough curve fitted to the mathematical model that considers the nonequilibrium sorption. The miscible displacement method showed the lower values of the Kd than the batch method. This result was attributed to the nonequilibrium sorption during the imazaquin transport through the column. In the sorption/desorption study it was observed that the imazaquin sorption coefficients were low for the three soils. The RQ soil showed the lowest Kd value. This soil presented the lower clay and organic carbon content. The imazaquin desorption coefficients were higher than the sorption coefficients, evidencing that occurred hysteresis in the process. The imazaquin sorption occurred in two phases. The second phase, which is slower, seems to be influenced by diffusive processes. In the aging experiment it was noted negative correlation between extracted diuron in CaCl2 solution and organic carbon content. It was not observed interaction between the incubation period and aggregate size, demonstrating that the time dependent sorption, in this case, is not related to the soil structure. The sorbed fraction of the diuron increased during the aging, indicating that the sorption process is time dependent.

U okviru ovog istraživanja ispitani su: 1. Optimalni uslovi  zaeksperimente biodegradacije policikličnih aromatičnih ugljovodonika sa istim irazličitim brojem prstenova; 2. Uticaj struture  i matriksa na biodegradacijupolicikličnih aromatičnih ugljovodonika sa istim brojem prstenova; 3.Fitotoksičnost biljaka  (testovi klijavosti i usvajanje policikličnih aromatičnihugljovodonika); 4. Procena  potencijalne  biodostupne frakcije primenomrazličitih hemijskih sorbenata (HPCD, βCD  i  MCD, XAD4 i TenaxTA)  i 5.Korelacija dobijenih rezultata  testovima biodegradacije, testovima klijavosti,testovima fitotoksičnosti i rezultata dobijenih iz eksperimenta procenebiodostupnosti hemijskim testovima.  Rezultati su pokazali da se  optimalniuslovi za biodegradaciju  postižu dodatkom mineralnih medijuma, inokuluma isurfaktanata.  Posmatrajući uticaj sadržaja gline i organske materije i strukturemolekula,  najveći stepen biorazgradnje ima fluoranten, što je u skladu sanjegovim fizičko-hemijskim osobinama, dok se sadržaj pirena i krizena nijemogao jasno korelirati sa sadržajem organske materije i gline.  Što se tičetestova fitotoksičnosti,  sva semena su proklijala, što govori u prilog tome  damešavina ovih kontaminanata  pri ispitivanim koncentracijama  nije inhibiralaklijanje biljaka.  Testovi usvojivosti ispitivanih PAH-ova su pokazali da jenajmanji procenat usvojivosti semenom dobijen za benzo(a)piren, što se možeobjasniti njegovom kompleksnijom strukturom. Hemijskim testovima zaprocenu biodostupnosti je sa druge strane pokazano da se desorpcija u prisustvuMCD, XAD4 smole i Tenaxa može koristiti kao jednostavna metoda za procenupotencijalne biodostupne  frakcije organskih jedinjenja u sistemima sediment  -voda.
The aim of this study was to investigate: 1. The optimal conditions for the biodegradation of polycyclic aromatic hydrocarbons with the same and different numbers of rings; 2. The impact of structure and matrix biodegradation of polycyclic aromatic hydrocarbons with the same number of rings; 3. Phytotoxicity (germination tests and polycyclic aromatic hydrocarbon uptake); 4. The means for assessing the bioavailable fractions using various chemical sorbents (HPCD, βCD, MCD, XAD4 and  TenaxTA) and 5. The correlation between the results of the biodegradation tests, germination tests, phytotoxicity tests and the results obtained from the experiments in the assessment of bioavailability and chemical tests. The results showed that the optimal conditions for biodegradation are achieved by the addition of mineral media, inoculum and surfactants. When considering the effect of the contents of clay and organic matter and the structure of the molecules, the highest degree of biodegradation was observed with fluoranthene,  which is in line with its physico-chemical properties. The concentrations of pyrene and chrysene were not clearly correlated with the organic matter and clay contents. During thephytotoxicity tests, all seeds sprouted, which speaks in favor of a mixture of these contaminants not inhibiting the germination of the plants. Tests for the uptake of the investigated PAHs showed that the lowest percentage seed uptake was for benzo(a)pyrene, which is explained by its more complex structure. Chemical tests for evaluating bioavailability have shown that desorption in the presence of MCD, XAD4 and Tenax resins can be used as a simple method for the evaluation of a potential bioavailable fraction of organic compounds in water-sediment systems.

L'épandage des boues d'épuration est un mode de valorisation à la fois écologique et économique pour autant que l'on maitrise leur qualité et notamment la concentration des métaux lourds mobilisables. Le cuivre est une molécule très répandue, naturelle dans l'environnement, largement utilisée dans l'industrie et l'agriculture. En conséquence, les quantités de cuivre dans l'environnement ont augmenté, de sorte que ce dernier a été choisi dans cette étude comme représentant de la pollution anthropique pour évaluer sa mobilité en fonction de la qualité des boues épandues et des sols. 9 boues classiques et 2 sols (Sol d’herbe (de France) et sol de riz (du Vietnam)) ont été étudiés ainsi que des boues granulaires. Une méthodologie est proposée pour évaluer l'effet de la boue et de l'origine du sol sur la capacité de lessivage du cuivre lors de l'épandage des boues pour les activités agricoles. Les essais de désorption dans les colonnes de sol amendé par des boues ont montré que: a) quelle que soit l'origine du sol amendé, les boues de lit de roseaux (LR), séchées (BCD), centrifugées (BC) ont présenté une libération de Cu inférieure à 2% tandis que les boues de filtre-presse (BFP), digérées (BD), épaissies (BE) et calcaires (BCh) ont amélioré la disponibilité de Cu dans le sol; b) La lixiviation du cuivre dans le sol d’herbe (du France) amendé par des boues granulaires était supérieure à celle mesurée pour les échantillons classiquesde boues; c) Dans le sol de riz (de Vietnam), l'épandage des boues granulaires a limité la désorption de cuivre par rapport aux échantillons de boue (BCh), de filtre-presse (BFP), digérée (BD) ou centrifugée (BC). Quatre mécanismes sont proposés pour expliquer le devenir du Cu dans les sols: 1) le contrôle; 2) le groupe de Cp1, Cp2, BC, LR and BCD; 3) le groupe de BCh, BD, BE, BFP et 4) le groupe de boue granulaire. Il est constaté que pour le sol de riz contenant une faible teneur en matière organique, l'application de boues granulaires ou d'autres types de boue tels que les boues compostées ou séchées peut non seulement augmenter la teneur en éléments nutritifs, mais aussi réduire la capacité de lixiviation du cuivre
The spreading of sewage sludge is both ecological and economical in sofar as their quality is controlled and in particular the low level of the heavy metals available. Copper is a very common substance, naturally occurring in the environment, widely used in industry and agriculture. As a result, quantities of copper in the environment have increased, so it has been selected in this study as representing human-induced pollution to assess its mobility in relation to the quality of sludge and soil. 9 different sludges and 2 soils (grass soil from France and paddy soil from Vietnam) were studied as well as granular sludge. A methodology was developed to evaluate the effect of sludge and soil origin on copper leaching ability during sludge application for agricultural activities. Desorption tests in soil-amended sludge columns showed that: a) Whateverthe origin of soil, the centri-dried (BCD), centrifuged (BC), reed-bed (LR) sludges presented a Cu release lower than 2% while filter-pressed (BFP), digested (BD), thickened (BE) and limed (BCh) sludge amended soils increased Cu availability in soil; b) the copper leaching of granular sludge amended grass soil was higher than those measured for conventional sludge samples; c) in paddy soil, landspreading of granular sludge limited the Cu desorption compared to limed (BCh), filter-press (BFP), digested (BD) and centrifuged (BC) sludge samples. Four mechanisms groups are proposed to explain the fate of Cu in soils: 1) the control; 2) the group of Cp1, Cp2, BC, LR and BCD; 3) the group of BCh BD BE and BFP, and 4) the group of granular sludge. It is found that paddy soil containing low organic matter, application of granular sludge orother types such as composted or dried sludge can not only increase the nutrient content but also reduce the leaching capacity of copper

The sorption/desorption behaviour of n-hexane in high molarmass linear polyethylene (PE) and branched PEs with 0.39 and5.09 hexyl branches per 100 main chain C atoms andcrystallinities between 4 and 82% at 298 K has been studied.Crystal core contents determined by Raman spectroscopy werealways lower than those determined by density measurements. Then-hexane solubilities in the copolymers depended in anon-linear manner on the content of penetrable polymercomponent and were lower for homogeneous copolymers than forheterogeneous copolymers at the same contents of penetrablecomponent. The solubility of hexane in the linear PE sampleswas proportional to the volume fraction of the penetrablepolymer and the solubility was low in comparison with that ofthe branched PE of the same crystallinity. TheCohen-Turnbull-Fujita (CTF) free volume theory was capable ofdescribing the desorption process in the PEs studied. Theconcentration dependence of the thermodynamic diffusivitypredicted by the CTF free volume theory was confirmed by thedata obtained by the differential method, and the differencesbetween the results obtained by the integral and differentialmethods were within the margins of experimental error. Thedependence of the fractional free volume of the penetrablephases on the phase composition suggests that mass transporttakes place from the liquid-like component to the interfacialcomponent and that the penetrant molecules are trapped at theinterfacial sites. The linear PE samples showed a physicallyrealistic trend with a decrease in the geometrical impedancefactor (t) with decreasing degree of crystallinity, whereas theopposite trend was obtained for the copolymers. The decrease int with increasing crystallinity in the copolymers may beexplained by the presence of wide crystal lamellae in the lowcrystallinity samples.

A novel melt-extrusion method was used to createcircumferential chain orientation in pipes of crosslinked PE.The microstructure of the pipes was characterized usingdifferential scanning calorimetry (DSC), density measurements,X-ray diffraction, infrared dichroism and contractionmeasurements. The mechanical properties were assessed byuniaxial tensile tests. The maximum degree of circumferentialorientation was obtained at the inner wall of the orientedpipe. The oriented pipe material exhibited a 5-15% higherdegree of crystallinity and a greater crystal thickness thanconventionally crosslinked pipe. The circumferential and axialmoduli of the oriented, crosslinked pipe were greater than thecorresponding moduli of the non-oriented crosslinked pipe.

Blends of single-site materials of linear PE andethyl-branched PE were prepared using solution- and melt-mixingmethods. The thermal properties of the blends were studied byDSC and results obtained by the two mixing methods werecompared. Data obtained for heats of melting andcrystallization, melting and crystallization peak temperaturesand melting and crystallization temperature profiles wereessentially the same for the samples obtained by the two mixingmethods. The heat associated with the high temperature meltingpeak of the blend samples obtained by both preparation methodsafter crystallization at 398 K was higher than that of thelinear polyethylene included in the blends, suggesting that apart of the branched polyethylene crystallized at 398 K.

Key words:n-Hexane diffusion, polyethylene, free volume,solubility, sorption, desorption, mechanical properties,orientation, thermal properties, blend.

Cette thèse porte sur le comportement d’un composé prioritaire au titre de la Directive Cadre sur l’Eau au niveau européen : le tributylétain (TBT) et ses métabolites (dibutylétain (DBT) et monobutylétain (MBT)). On s’intéresse plus particulièrement aux eaux usées domestiques lors de leur transit dans deux stations d’épuration par lagunage naturel (STEP), traitement adapté aux effluents provenant des zones faiblement urbanisées. Ce travail de thèse vient combler le manque de résultats scientifiques sur (1) le niveau des concentrations en butylétains dans les effluents domestiques des zones peu urbanisées en entrée des stations par lagunage et en sortie après traitement ; (2) l’efficacité du traitement par lagunage à éliminer les butylétains ; (3)l’identification des processus qui contrôlent le devenir de ces éléments au cours du traitement.Les butylétains sont mesurés dans les matrices particulaires, dissoutes et dans les boues, par couplage GC-ICP-MS, dans toutes les étapes du traitement par lagunage de deux communes rurales du département de l’Hérault (34,France) : Gigean (6000 eq-hab.) et Montbazin (4500 eq-hab.). On montre que les trois espèces butylées sont systématiquement présentes dans tous les échantillons prélevés sur les deux STEP. Les butylétains arrivent principalement sous forme particulaire dans les eaux brutes en entrée des stations. Au cours du traitement, les processus de sorption sur les particules en suspension et la décantation de ces dernières au fond de chaque bassin sont les principaux facteurs permettant l’élimination des butylétains. Les premiers bassins anaérobies, de grande profondeur et de long temps de séjour, permettent l’élimination de plus de 60% à Gigean (93% à Montbazin) des butylétains. Les boues de fond de chaque bassin montrent des concentrations élevées en butylétains. La remise en suspension des butylétains est notée dans les derniers bassins de finition, peu profonds, ce qui peut être due à la re-stratification thermique. En sortie de station, malgré les abattements importants, des concentrations non négligeables en butylétains (12 à 228 et 1.8 à 15 ng(Sn).L-1 respectivement pour Montbazin et Gigean) sont rejetées dans le milieu récepteur. Des expériences de sorption basées sur la mise en contact de butylétains avec des boues de fond de bassin diluées ont été effectuées selon plusieurs approches expérimentales. On a ainsi montré que (1) la distribution des espèces MBT, DBT, TBT, entre les phases solide et liquide, est variable d’un test à l’autre selon les conditions opératoires ; (2) l’affinité entre les butylétains et la boue est importante, quelle que soit sa provenance. 98% des butylétains se retrouvent dans la phase solide, du fait de leur hydrophobicité. Le coefficient de distribution Kd entre le TBT et les boues est plus élevé que celui obtenu pour d’autres type de phases solides (75000 L.kg- 1) ; (3) le processus de sorption est rapide. De plus des processus de sorption, désorption et déalkylation du TBT, expliquant les variations des concentrations en MBT et DBT dans la phase solide ont été identifiés. La désorption du TBT est rapide. Il se dégrade dans la phase liquide en DBT dont une partie se transforme en MBT. La sorption du MBT sur les boues a été systématiquement mesurée. Le phénomène de sorption n’est donc pas complètement réversible au cours du temps. Ces résultats contribuent à expliquer les dysfonctionnements observés dans les stations de traitement par lagunage, par exemple lors d’apports directs d’eau de pluie.Cette thèse démontre la présence systématique des butylétains dans les stations d’épuration par lagunage naturel. Les données acquises in-situ couplées à des essais en laboratoire permettent de comprendre le comportement de ces composés lors de ce traitement : la fraction solide joue un rôle clé dans les processus de sorption-désorption-(bio)dégradation des butylétains
This thesis deals with the behavior of a priority compound on the basis of the framework Directive on water at European level: tributyltin (TBT) ) and its metabolites (dibutyltin (DBT) and monobutyltin (MBT)). The study is focused on two waste stabilization pond treatment plants (WSP), which is an appropriate treatment to domestic effluents from sparsely urbanized areas.This thesis comes to fill the lack of scientific results on (1) the level of butyltin concentrations in domestic effluents from sparsely urbanized areas, in the input of the WSP and the output after treatment; (2) the efficiency of butyltins elimination by the WSP treatment; (3) the identification of the processes that control the fate of these elements during the treatment.Butyltins are measured in particulate and dissolved matrices and in sludge, by GC-ICP-MS, in all stages of the treatment by lagooning of two villages of the Department of Hérault (34, France): Gigean (6000 p.e.) and Montbazin (4500 p.e.).It is shown that the three butyltin species are consistently present in all samples taken from the two WSP. Butyltins arrive primarily in particulate form in the raw water. During treatment, the processes of sorption onto particulate matter and the settling of the latter at the bottom of each basin are the main factors for the elimination of butyltins. The first anaerobic ponds, characterized by deep depth and long residence times, allow the elimination of more than 60% Gigean (93% at Montbazin) of butyltins. Bottom sludge of each basin show high butyltins concentrations. The resuspension of butyltins is noted in the last maturation ponds, characterized by shallow depth, which may be due to re-thermal stratification. At the outlet, despite significant butyltin removal, concentrations in butyltins remain high (12 to 228 and 1.8 to 15 ng (Sn). L-1, respectively for Montbazin and Gigean).Laboratory batch experiments were conducted to study sorption processes following several experimental protocols. It was thus shown that: (1) the distribution of the butyltin species between solid and liquid phases is different from one test to another according to the operating conditions; (2) the affinity between butyltins and bottom sludge is important, regardless of its provenance. 98% of the butyltins are found in the solid phase, due to their hydrophobicity. The TBT sludge-water partition coefficient is higher than that obtained for other type of solid phases (75000 L.kg-1); (3) the process of sorption is fast.Moreover processes of sorption, desorption and dealkylation of TBT, explaining changes in concentrations of MBT and DBT in the solid phase were identified. Desorption of TBT is fast. It degrades in the liquid phase in DBT which part turns into MBT. The sorption of MBT on sludge has been systematically measured. Therefore, the sorption phenomenon is not completely reversible over time. These results help to explain the dysfunctions observed in WSP, for example after direct inputs of rainwater.This thesis shows the systematic presence of butyltin in waste stabilization pond treatment plants. In-situ data coupled with laboratory tests allow to understand the behaviour of these compounds during this treatment: the solid fraction plays a key role in the processes of sorption-desorption-(bio) degradation of butyltins

Sr-90 and Cs-137 are two key fission products that are important in a number of radioactive waste or contamination clean-up scenarios. This thesis investigates the sorptiondesorption behaviour of these two radionuclides with a number of sorbents relevant to one of the legacy waste storage ponds on the Sellafield site. Sorption-desorption studies were undertaken on brucite (Mg(OH)2), UO2 and UO3 powders to represent components of the fine particulate sludge that has accumulated on the bottom of the pond, resulting from corrosion of the Magnox fuel elements. Brucite was found not to have a significant interaction with Sr-90 or Cs-137. However, organic molecules in the form of humic acid and Pseudanabaena catenata cyanobacterial growth supernatant were both found to enhance sorption interactions of Sr-90 with brucite. The effect of humic acid was pH dependent and appeared to control both sorption and desorption behaviour at pH 11.5. Uranium oxides had the most significant effect on controlling Sr-90 and Cs-137 sorption-desorption behaviour. In this work X-Ray Absorption Spectroscopy (XAS) showed that 90Sr sorbed strongly to both uranium oxides as a bidentate inner-sphere complex. Humic acid did not appear to alter the interaction of Sr-90 with UO2. For Cs-137 there was a significant, reversible interaction with both oxides, although the interaction was far stronger with UO3. Successful detection of stable Sr and Cs isotopes on uranium oxides was achieved with Laser Induced Breakdown Spectroscopy (LIBS).

Prirodna organska materija zemljišta/sedimenata predstavlja glavnu oblastza sorpciju hidrofobnih organskih jedinjenja, a njene osobine utiču na stepenretencije i konsekventnu (bio)dostupnost organskih jedinjenja. Da bi se procenioekotoksikološki rizik zagađenih zemljišta/sedimenata po okolinu, dizajniralaodgovarajuća strategija remedijacije ili predvidela sudbina i transport organskihpolutanata u zagađenim zonama, neophodno je razumevanje mehanizma sorpcije idesorpcije na nivou mehanizma uspostavljenih veza. U radu je izvršeno ispitivanjesorpcije i desorpcije odabranih hidrofobnih organskih polutanata, pentahlorbenzenai lindana, na sekvencijalno ekstrahovanim huminskim kiselinama i huminima izjednog uzorka sedimenta u cilju pronalaženja veze između strukturnihkarakteristika izolovanih huminskih kiselina i humina i sorpcionih i desorpcionihparametara. Afinitet za sorpciju, nelinearnost izotermi i prividna sorpciono-desorpciona histereza korelirani su  sa osobinama sorbenata dobijenim izelementarne i FTIR spektroskopske analize. Predloženo je da je mehanizamsorpcije na huminskim kiselinama rezultat odigravanja raspodele i specifičneadsorpcije, pri čemu se pri nižim koncentracijama pentahlorbenzena i lindana prvopopune sorpciona mesta u kondenzovanoj aromatičnoj oblasti, a tek potom privišim koncentracijama sorpciona mesta u amorfnim alifatičnim oblastima.Sveukupno viši koeficijenti nelinearnosti dobijeni za sorpciju pentahlorbenzena na huminskim kiselinama u odnosu na nelinearnost sorpcionih izotermi lindana, ukazuju na to da u ukupnoj sorpciji pentahlorbenzena veći značaj ima mehanizam raspodele i smeštanje molekula pentahlorbenzena u hidrofobne šupljine huminskih kiselina, u odnosu na specifičnu adsorpciju. Ovi zaključci su potvrđeni rezultatima spektroskopskih istraživanja interakcija  odabranih organskih jedinjenja i N-metilformamida. Predloženi mehanizam sorpcije ne može objasniti sorpciju pentahlorbenzena i lindana na uzorcima humina, većje pretpostavljeno da nelinearna sorpcija za uzorke humina može biti rezultat ostvarivanja površinskih interakcija, a visoki afinitet za sorpciju rezultat je raspodele organskih jedinjenja u amorfnim alifatičnim oblastima koje pružaju odlično okruženje za sorpciju.U cilju daljeg proučavanja mehanizma sorpcije, izvršeno je ispitivanje kinetikedesorpcije tri odabrana hidrofobna organskajedinjenja, pentahlorbenzena, lindana ipentahloranilina, posredstvom  čvrstog adsorbenta, XAD-4 makroporoznejonoizmenjivačke smole. Na osnovu rezultata dobijenih za uzorak sedimenta ifrakciju < 125 µm za dva ravnotežna vremena (15 i 90 dana) i za sva odabranaorganska jedinjenja može se zaključiti da se za procenu potencijalne (bio)dostupnefrakcije organskih jedinjenja može koristiti jednostavna desorpcija u prisustvuXAD-4 makroporozne jonoizmenjivačke smole i to na dva načina: (1) ekstrakcijomsedimenta tokom 24 časa, kada frakcija koja se desorbuje odgovara frakcijijedinjenja koja se nalazi u brzo-desorbujućem domenu organske materije, ili (2)ekstrakcijom tokom 6 časova, kada frakcija koja se desorbuje odgovara polovinione frakcije jedinjenja koja se nalazi u brzo-desorbujućem domenu organskematerije.
Natural organic matter of soil/sediment make the main region for sorption of hydrophobic organic compounds, ant its properties influence the degree of retention and, consequently, (bio)availability of organic compounds. In order to assess the ecotoxicological risks of contaminated soils/sediments to the environment and design the appropriate remediation strategy or predict the fate and transport of organic pollutants in contaminated zones, it is necessary to understand the mechanisms of sorption/desorption at the level of the mechanism of established bonds. Study of the sorption and desorption of selected hydrophobic organic pollutants, pentachlorobenzene and lindane, on sequentially extracted humic acids and humins from a single sediment sample with the aim of finding the relationship between the structural characteristics of the isolated humic acids and humin and sorption and desorption parameters. Sorption affinity, nonlinearity of isotherms, and apparent sorption-desorption hysteresis were correlated to the sorbent characteristics obtained from elemental analysis and FTIR spectroscopic data. The proposed sorption mechanism on humic acids assumes that at low concentrations of pentachlorobenzene and lindane the sorption sites in the condensed aromatic region are occupied first, and then, at their higher concentrations, the sorption sites in the amorphous and aliphatic regions. Generally higher nonlinearity coefficient obtained for the sorption of pentachlorobenzene on  umic acids compared with the nonlinearity of sorption isotherms for lindane, indicate that in the overall sorption of pentachlorobenzene of higher significance is the  echanism of distribution and insertion of pentachlorobenzene molecule into hydrophobic dips of humic acids, compared to specific adsorption. These conclusions were confirmed with the results of spectroscopic investigation of  intermolecular interaction of chosen organic compounds and N-methylformamide.Since suggested sorption mechanism could not explain sorption of  pentachlorobenzene and lindane onto humin samples, it is supposed that the nonlinearity can be a result of surface interactions, while the high sorption affinity is result of distribution of organic compounds in the amorphous aliphatic regions that offer an excellent environment for sorption.With the aim of further insight into the sorption mechanism, investigation of desorption kinetics of three chosen hydrophobic organic compounds, pentachlorobenzene, lindane and pentachloroaniline, in the presence of  soild adsorbent XAD-4 macroporous ion-exchange resin was performed. On the basis of the results obtained for sediment sample and fraction < 125 µm at two equilibrium times (15 and 90 days) and for all selected organic compounds, it can be concluded that the assessment of the potential (bio)avialable fraction of organic compounds may be obtained by using simple method of desorption in the presence of XAD-4 macroporous ion-exchange resin, performed in two ways: (1) by sediment extraction during 24 hours, when the desorbing fraction corresponds to the fraction of  he compound that is found in the fast-desorbing domain of organic matter, or (2) by 6-hour extraction, when the desorbing fraction corresponds to one half of the fraction appearing in the fast-desorbing domain of the organic matter.

Ce travail visait à évaluer le transport d’hydrocarbures aromatiques polycycliques (HAP) et de métaux dans des sols multi pollués, en s’intéressant plus particulièrement au couplage transport-réaction dans la zone non saturée du sol, selon deux axes de travail. En premier lieu, puisque de nombreux sites industriels sont multi pollués, nous avons choisi d’étudier l’influence des métaux sur la sorption des HAP et vice versa en système modèle. Nous avons montré que lors d’une pollution simultanée par du fluoranthène et du zinc, ce dernier est beaucoup moins retenu que lorsqu’il est présent seul et peut donc migrer plus facilement vers la nappe phréatique. Le plomb, quant à lui, est plus fortement retenu en présence de fluoranthène. En revanche, l’effet des métaux sur la rétention du fluoranthène est plus limité. En second lieu, nous avons évalué le transport des HAP et des métaux dans une terre d’une ancienne cokerie lorraine à plusieurs échelles : en colonne de laboratoire en conditions saturées et non saturées ainsi qu’en lysimètre de terrain, afin d’évaluer le pouvoir prédictif des sytèmes de laboratoire. Nous avons montré que les expériences en colonne de laboratoire surestiment la sortie des HAP telle qu’elle a lieu sur le terrain. En revanche, la sortie des métaux est bien prédite par de telles expériences. Mais le lysimètre ne peut pas être utilisé lors d’études de risque puisqu’il demande des durées d’expériences de plusieurs années afin d’avoir une vue globale des phénomènes qui s’y produisent. C’est pourquoi nous avons conçu un système original au laboratoire, capable d’évaluer leur transport conformément à ce qui se passe sur le terrain
PAHs and heavy metals are major soil pollutants and most of former industrial soils are co-polluted by both types of compounds. The aim of this work was to assess their transport in polluted soils under saturated and unsaturated flow conditions. This study was carried out by two approaches. First, heavy metal influence on PAH sorption and vice versa was studied with a “model” system. We showed that when the soil was simultaneously contaminated with fluoranthene and zinc, zinc retention was lower than when it was alone in the soil. As a consequence zinc would be expected to migrate more easily to the water table in co-polluted soils. Lead was more strongly retained in the presence of fluoranthene. But heavy metal influence on fluoranthene sorption was of minor importance. Then, PAH and heavy metal transport in a former coking plant soil was evaluated at the laboratory scale, under saturated and unsaturated flow conditions, by means of column experiments, and at the lysimeter scale under natural atmospheric conditions. The goal of these experiments was to compare PAH and heavy metal migration in a field-like situation with results obtained in the laboratory and to determine the appropriate experimental device for risk assessment studies. We showed that column experiments may overestimate PAH migration at the field scale. However heavy metal leaching was in accordance with what was expected from lysimeter experiments. But such experiments are rather time consuming and quite expensive, and as a consequence not adapted for risk assessment studies. Therefore we designed an original laboratory set up able to represent PAH and heavy metal migration at the field scale

Ce travail vise à étudier le couplage entre écoulement et interactions physico-chimiques dans les sols, dans différentes conditions de saturation en eau, afin d’améliorer la prédiction du devenir des polluants. Il s’agit de comprendre en quoi le taux de saturation du milieu affecte la réactivité du sol vis-à-vis des polluants, et d’évaluer le pouvoir prédictif du transport de solutés réactifs étudié en milieu saturé sur la réactivité en conditions non saturées. Différents processus sont considérés : l’échange de cations calcium-zinc sur un milieu poreux modèle (sable-kaolinite), la sorption et désorption d’un composé organique sur une terre non contaminée, le transport de polluants prioritaires tels que les HAP sur une terre de friche industrielle. Dans chaque cas, des expériences en colonne de laboratoire ont été conduites en conditions d’écoulement saturé et non saturé permanent, permettant tout d’abord la caractérisation de l’hydrodynamique, puis l’étude du couplage avec la réactivité. Les courbes de percée obtenues ont été ensuite modélisées avec des codes tels que CXTFIT. On a montré l’influence de la teneur en eau du milieu sur le transport réactif, variable suivant le type de réaction considéré, la structure des milieux jouant également un rôle important. L’échange d’ions sur le milieu modèle n’est globalement pas affecté par la teneur en eau, dans une gamme proche de la saturation. En revanche, une plus forte sorption et une plus faible mobilisation des polluants organiques ont été observées en conditions non saturées. Le transport réactif de ces composés ne peut donc pas être prédit en conditions non saturées à partir de mesures en milieu saturé, qui peuvent surestimer le transport
The aim of this work was to study the link between water flow and physical and chemical interactions in soils under variably water flow conditions, in order to improve the prediction of contaminants fate. It deals with understanding how the porous media water content can modify soil reactivity towards contaminants, and assessing the possibility to predict reactivity under unsaturated conditions with reactive solute transport studied in saturated porous media. Various processes were considered: cations exchange calcium-zinc on a model porous media (sand-kaolinite), sorption and desorption of an organic compound on a non polluted soil, transport of priority contaminants such as PAHs on an industrial contaminated soil. In each case, experiments were carried out with soil columns at the laboratory scale under saturated and unsaturated steady-state flow conditions, in order to characterize at first hydrodynamics and then to study the link with reactivity. Modeling of the breakthrough curves was then performed with codes such as CXTFIT. We showed an influence of porous media water content on reactive transport which was different as a function of the interaction. Porous media structure must also be taken into account. Ions exchange on a model porous media was not globally modified by the water content varying in a range close to saturation. On the contrary, higher sorption and lower migration of organic contaminants were observed under unsaturated conditions. Reactive transport of these compounds cannot therefore be predicted under unsaturated conditions with tests performed on saturated porous media which may overestimate transport

La réduction de la consommation énergétique dans le secteur de bâtiments présente aujourd’hui une priorité primordiale dans les politiques des pays industrialisés. En France, le secteur du bâtiment consomme environ 43 % de l’énergie finale et contribue pour près d’un quart aux émissions nationales de gaz à effet de serre [ADEME]. Il se positionne comme un acteur clé pour parvenir à résoudre les inquiétants défis environnementaux auxquels nous devons faire face. Face à ces véritables défis, l’augmentation des niveaux d’exigence des réglementations thermiques s’est poursuivie et intensifiée pendant les 40 dernières années, jusqu’à la naissance de la réglementation thermique 2012, qui a permis de construire des bâtiments basse consommation (BBC) qui équivaut à 50 kWh/m².an. Cette nouvelle réglementation plus exigeante constitue une incitation forte à l'innovation des matériaux, produits et systèmes d'enveloppe. Dans ces conditions, l’amélioration des performances hygrothermiques des matériaux de construction aura des retombées économiques et environnementales conséquentes. C’est dans ce contexte que ce travail a été mené. Il vise à étudier et à améliorer les performances des produits de l’entreprise Briqueteries du Nord (BdN). Il est réparti sur deux axes principaux : le premier consiste à l’étude de l’inertie thermique et du pouvoir hygroscopique des briques en terre crue. Le second axe vise à élaborer des solutions possibles concernant l’amélioration de la résistance thermique des briques en terre cuite. Ce travail de recherche a été réalisé au laboratoire de l’Ecole Centrale de Lille avec une étroite collaboration avec l’université d’Artois et l’entreprise (BdN)
Nowadays, the reduction of energy consumption in buildings industry represents a major issue in industrialized countries’ policies. In France, the building sector consumes about 43% of final energy and accounts for nearly a quarter of the national emissions of greenhouse gas emissions [ADEME]. It is considered as a key factor to overcome the environmental challenges we have to face.In front of these significant challenges, the thermal regulations requirements were seriously intensified during the last 40 years until the notification of the thermal regulation 2012. This latter enable the construction of low energy buildings (BBC) whose consumption is equivalent to 50 kWh/m² per year on average. This new regulation provides a strong incentive for innovation of materials, products and envelope systems. Under these conditions, improving hygrothermal performance of building materials will allow a substantial economic and environmental benefits. This work was conducted in this context. It aims to study and improve the performance of the company Briqueteries du Nord (BdN) products. It is divided in two main axis: the first consists on studying the thermal inertia and hygroscopic capacity of unfired clay bricks. However, the second axis aims to develop possible solutions for improving the thermal resistance of fired clay bricks. This research was conducted in the laboratory of the Ecole Centrale de Lille with close collaboration with the University of Artois and the BdN company

Magnesium (Mg) thin films with various thicknesses ranging from 50 to 1000 nm capped with nominally 20 nm Palladium (Pd) were prepared by a thermal evaporation unit. A total of 25 glass substrates were used in each experiment. The unit had a rotatable macro shutter, rectangular in shape, rotation axes opposite to the Mg source, which allowed controlled exposure of the substrates. Thin films of 50, 100, 150, 200, 300, 400, 500, 600, 800 nm and 1000 nm were produced in a single experiment. Hydrogenation and dehydrogenation of the films were examined using a gas loading chamber which allowed in-situ resistance measurement. Samples were hydrogenated isochronally up to 453 K with a heating rate of 1.5 K/min. Samples cooled to room temperature were subjected to dehydrogenation test. The chamber was taken under vacuum (~10-2 mbar) and the sample was heated up to 453 K at a rate of 1.5 K/min. The results showed that the hydrogenation and dehydrogenation temperatures correlate with the film thickness, thinner films reacting with hydrogen at low temperatures. While 200 nm thin film hydrogenated at 420 K and desorbed it at 423 K, 50 nm thin film hydrogenated at room temperature and desorbed it at 405 K. Thicker films needed higher temperatures to react with hydrogen. It is concluded that films thinner than 200 nm react fully with hydrogen
while a considerable portion of the thicker films remain unreacted. Significance of this is discussed with reference to the design of hydrogen storage systems based on thin films or nanoparticles.

For this dissertation I studied phosphorus (P) sorption dynamics in the shallow groundwater of the southern Everglades. In particular, I examined how the ambient water type governs soluble reactive P (SRP) availability through adsorption/desorption reactions with the aquifer matrix. Chapter 2 investigated how P sorption dynamics of the mangrove root zone sediment are affected by high bicarbonate brackish groundwater compared to both fresh groundwater and saltwater. The results from chapter 2 show that the sediment exhibited exceptionally low sorption efficiency in the high bicarbonate brackish water, which would allow ambient water SRP concentration to be maintained at a higher level. Chapter 3 is a detailed analysis of how P sorption dynamics in two bedrock samples are affected by incremental increases in saltwater content in a freshwater-saltwater transition zone. The results of chapter 3 indicate that a sorption edge occurs at 3 mM Cl- concentration. In water exceeding this Cl- concentration, SRP would be expected to desorb from the bedrock due to a sharp decrease in sorption efficiency between the freshwater saltwater. These results suggest that SRP is active in the ion exchange front of saltwater intrusion, with a rapid increase in SRP availability expected at the leading edge of saltwater intrusion. A landward incursion of 3 mM Cl- concentration water would be expected to raise ambient SRP concentration along the affected aquifer zone, in turn increasing SRP availability in the ecosystem where the transitional waters discharge to the surface. Chapter 4 investigates the kinetics SRP release accompanying saltwater intrusion using a column of carbonate aquifer solids and alternating inflow between fresh groundwater and saltwater. The results show an immediate and high magnitude increase in SRP concentration when saltwater flows into the column. The combined results of this dissertation show that, in the southern Everglades and possibly other carbonate coastlines as well, water type strongly controls P sorption behavior of the sediment and bedrock, and may have a direct influence on the local ecology through increased P availability. A fundamental understanding of the abiotic exchange mechanisms between SRP and the aquifer solids can aid in the successful management and protection of this unique and important ecosystem.

Cette étude a pour objet de comparer les propriétés acoustiques, mécaniques et hygrothermiques de différents biocomposites destinée à l’isolation des bâtiments à base de granulats issus de co-produits végétaux et d’un liant à base d’argile. Nous avons d’abord analysé les matières premières afin d’obtenir d’une part la masse volumique et les propriétés thermiques et hydriques des granulats végétaux et les caractéristiques minéralogiques et gravimétriques de la terre crue sélectionnée d’autre part. L’évolution de la conductivité thermique des mélanges terre:granulats végétaux a été étudiée à différents taux d’humidité et différentes masses volumiques. D’un point de vue hydrique, les capacités de sorption/désorption de ces matériaux ont été mesurées en régime statique de même que la capacité de tampon hydrique simulant un régime dynamique. L’un des principaux intérêts de cette étude est de confirmer qu’une large gamme de co-produits végétaux produits à l’échelle locale pourrait être utilisée en tant que granulats pour l’élaboration de bétons végétaux
The purpose of this study was to compare hygrothermal acoustical and mechanical properties ot different materials based on vegetal aggregates and clay in order to characterize the performances of different biocomposites to provide building insulation solutions with a view to valorizing agricultural waste. We first analyzed the raw materials in order to get the density, thermal and hydric properties of the vegetal aggregates in one hand and the mineralogy and gravimetric data of the selected crude earth in the other hand. Thermal behavior of earth:vegetal aggregates mixes have been investigated at different humidity rates and different density ranges. Additionally, hydric properties have been measured to produce sorption and desorption curves and moisture buffer values (MBV) in one hand and capillarity of both aggregates and biocomposites on the other hand. One of the main interests of this study is to confirm that a wide range of locally produced vegetal byproducts could be used as - bioaggregates for concretes. Local biomaterials industries could therefore emerge depending on the locally available resources at country scale

The interaction of arsenite (As(III)) and arsenate (As(V)) with magnetite nanoparticles has been studied to evaluate the environmental impact of magnetite nanoparticles and possible beneficial use of these nanoparticles in water treatment. The effects of particle size (20--300 nm) and pH on the sorption/desorption of AS(III) and As(V) on magnetite nanoparticles were examined. On a surface area basis, it was found that large and nanometer scale magnetite particles had similar maximum As(III)/As(V) sorption capacities. However, the sorption of As(III) to magnetite showed the same Langmuir sorption slope for the nanometer scale particles as for the large particles, while the sorption of As(V) to magnetite showed a larger Langmuir sorption slope for the nanometer scale particles than for the large crystals. The particle size effect on sorption is constant over a pH range of 4.8 to 8. Sorption of As(V) was found to be greater at lower pH, while sorption of As(III) was not pH sensitive. The sorption data of both As(III) and As(V) have been modeled with the Diffuse Double Layer model. Stronger desorption hysteresis was observed for both As(III) and As(V) sorption to nanometer scale magnetite particles than that to large magnetite particles, which indicates that the decrease of particle size may increase the affinity of sorption. The experimental results showed that magnetite nanoparticles are potentially a very effective sorbent for arsenic removal in water treatment.

碩士
高雄師範大學
生物科技系
98
The high fuel price triggered awareness among many countries of their vulnerability to oil shortages. The dwindling fossil fuel sources and the creasing dependency on imported crude oil have led to a major interest in expanding the use of bioenergy in many countries. Therefore, Taiwan is promoting the use of E3 (gasoline with addition of 3% ethanol) and B1 (diesel fuel with addition of 1% biodiesel) in 2007 and 2008, respectively. Consequently, a thorough understanding of the environment fate of potential biofuels additives (i.e., ethanol, biodiesel) and the influence that these compounds may have on the fate of other fuel constituents should be obtained before biofuels widely utilized. In this study, batch and column experiments were designed to simulate potential spills of biofuels in the subsurface environment and to evaluate the sorption behavior of hydrophobic organic compounds (HOCs) of biofuels in soils. This study provides fast estimation of contamination potential of target compounds (i.e., monoaromatic and polyaromatic hydrocarbons), and possibly other organic contaminants in various types of soil. The extent and reversibility of sorption of major components from biofuels onto major soils and groundwater was determined. The results showed that when the proportion of ethanol in gasoline increased, the easier desorption of pollutants to water occurred, which is obvious when ethanol content exceeds 25%. However, if more biodiesel was added to diesel fuel, sorption of HOCs increased. In addition, when content of soil organic carbon was increased, desorption of target compounds was decreased. The empirical relationship between Koc and water solubility (S), Koc and octanol-water partition coefficient (Kow) were established as the follings: logKoc = 0.6212 logKow+0.7919 logKoc = 0.4172 logS + 3.5475 This study will provide a basis to predict fate and transport of HOCs due to spills of biofuels. The spill scenarios generated may assist the assessment of biofuel contaminated sites.

碩士
國立中央大學
應用地質研究所
101
Geological sequestration of CO2 into depleted oil reservoir, saline aquifer or unmineable coal seam is now being actively investigated for the purpose of reducing greenhouse gas in the atmosphere. Understanding the physical, chemical, and thermodynamic phenomena occurred with CO2 injection is very important in making a reliable prediction of sequestration. This study examined the feasibility of carbon dioxide sequestration into unmineable coal seams in Taiwan. A total of 20 Miocene-aged coal samples from Western Foothill Belt, NW Taiwan, were collected. The stratigraphy include Mushan, Shihti, and Nanchuang Formation from bottom up. Proximate and petrographic analyses include maceral composition and vitrinite reflectance were also measured. Carbon dioxide adsorption isotherms were analyzed at 35℃ and up to 800 psi, by using a gravimetric ad/desorption apparatus. Isotherms were then fitted with a modified Langmuir Isotherm model by using Langmuir Pressure and Langmuir Volume so the model can be applied to supercritical conditions. According to the result of adsorption experiment, the pressure and temperature were quite significant. The gas storage capacity of CO2 was about 250~500 scf/ton at pressure up to 800 psi. Comparing the results of adsorption capacity with Proximate and Petrographic analyses, the Langmuir Volume shows a strong positive correlation with fixed carbon and vitrinite content. Furthermore, Adsorption capacity is closely related to micropores which were also rank and maceral dependent. It is noticed that the observed coal pore structures were affected by rank, and thus exhibit different diffusion rate. Finally, images under SEM were evaluated to understand the pathways of gas sorption.The filling mineral matter (mostly clay) will lead to the decrease of gas sorption.

碩士
逢甲大學
環境工程與科學所
91
During the outbreak of foot-and-mouth disease in pigs in 1997, the corpses of ill pigs were buried. To study whether the residual viruses on corpses have penetrated and polluted the ground water, a simulation model can be used to study the transport of bacteriophage in soil. The main object of this study was to establish a model that exhibited transport of bacteriophage in soil, especially the effect of inactivation and desorption on bacteriophage transportation were taken into consideration. Several parameters were obtained from batch experiments, and based on the equations used in the adsorption of phages to soil, the parameters of adsorption, desorption and inactivation were the key factors affected the reaction between bacteriophage and Ottawa sand. The results from batch experiments showed that the adsorption equilibrium time of bacteriophages and Ottawa sands was 60 minutes. To ensure the consistency of unit measurement, the concentration of free bacteriophage ( ) and the concentration of bacteriophages adsorbed to sand ( ) were multiplied with, and , solid-liquid conversion coefficients. The results from batch experiments were used along with Taylor’s expansion to obtain the adsorption coefficient, =2.23 10-11 and the amount of saturated adsorptive bacteriophage on Ottawa sand, = 4.3 107 PFU/g. In addition, two functions were obtained from batch experiment, that was the and varied with the concentration of bacteriophage (C), and . Finally, simulation was performed on the bacteriophage transport model. The soil condition, such as velocity ( ) and diffusion coefficient ( ) were especially examined. The pressure of Ottawa sand in soil column (pressure factor ) was then taken into consideration to modify the model and verify the relationship between the effluent of bacteriophage from the soil column as well as the validity of simulation model.

博士
國立臺灣大學
環境工程學研究所
100
Antibiotic were used widespread to protect humans and animals from illness and infection, throughout the world. The parent compound or their metabolites will be excreted by human beings and enter waste water treatment plants (WWTPs) through sewer system. To date, little has been quantified for the interactions, biodegradation and sorption, of sulfonamide antibiotics with activated sludge. Hence, three frequently occurring sulfonamide antibiotics including sulfamethoxazole (SMX), sulfadimethoxine (SDM), and sulfamonomethoxine (SMM) were selected to study sorption/desorption and biodegradation of antibiotics by the activated sludge process. Our objectives were to determine the distribution of sulfonamides in the aqueous and solid phases, the concentration changes of the compounds in both phases over time, and the sorption and biodegradation mechanisms contributed by the activated sludge for removal of the compounds. The distribution of antibiotics in municipal sewage sludge was also investigated in this research. The results of distribution of antibiotics in WWTPs activated and digested sludge showed the concentrations of penicillins in sewage sludge samples were found to be well below the limit of quantification (LOQ). This may be perhaps due penicillins prefer to hydrolyze in the water and are degraded to different products. Average concentrations of sulfamethoxazole, sulfamethazine, sulfamonomethoxine, sulfadimethoxine, erythromycin-H2O, tylosin, tetracycline, oxytetracycline and chlortetracycline in sewage sludge ranged between 2.56 and 56.6 μg/kg of dry weight. Experimental results in the presence of activated sludge with and without being subjected to NaN3 biocide showed that the antibiotic compounds were removed via sorption and biodegradation by the activated sludge, though biodegradation was inhibited in the first 12 h possibly due to competitive inhibition of xenobiotic oxidation by readily biodegradable substances. The affinity of sulfonamides to sterilized sludge was in the order of SDM>SMM>SMX. The sulfonamides existed predominantly as anions at the study pH of 6.8, which resulted in a low level of adsorption to the activated sludge. The adsorption/desorption isotherms were of a linear form, as well described by the Freundlich isotherm with the n value approximating unity. The linear distribution coefficients (Kd) were determined from batch equilibrium experiments with values of 28.6 ± 1.9, 55.7 ± 2.2, and 110.0 ± 4.6 mL/g for SMX, SMM, and SDM, respectively. SMX, SMM, and SDM desorb reversibly from the activated sludge leaving behind on the solids 0.9%, 1.6%, and 5.2% of the original sorption dose of 100 µg/L. In addition to apply biocide, an ultrasonic solvent extraction method was employed to quantify and delineate biosorption and biodegradation of three sulfonamide antibiotics in this work. All sulfonamides were removed completely over 11 – 13 d. Sorptive equilibrium was established well within the first few hours, followed by a lag period of 1-3 days before biodegradation was to deplete the antibiotic compounds linearly in the ensuing 10 days. Apparent zeroth-order rate constants were obtained by regression analysis of measured aqueous concentration vs. time profiles to a kinetic model accounting for sorption and biodegradation; they were 8.1, 7.9, and 7.7 µg/L/d for SDM, SMX, and SMM, respectively, at activated sludge concentration of 2.56 g/L. The results obtained in this study illustrate: 1. the sorbed antibiotics can be introduced into the environment if no further treatments were employed to remove them from the biomass; 2. the existence of antibiotics in municipal sewage sludge and the importance of concern about distribution of antibiotics in the environment when sewage sludge is reutilized in land application; 3. the measured kinetics implied that with typical hydraulic retention time (e.g. 6 h) provided by WWTP the removal of sulfonamide compounds from the wastewater during the activated sludge process would approximate 2 µg/L.

碩士
萬能科技大學
工程科技研究所
96
This study investigates the surface properties of clay particles and colloids of kaolinite, montmorillonite and ri-hsing bentonite. Moreover, the sorption/desorption of Cs+ and Sr2+ on the above three kinds of colloid in artificial buffered aqueous solutions were conducted to understand the fate of radioactive cations in the subsurface environment. The results show that the variation extents of specific surface area and cation exchange capacity depend on the kinds of clay particles and colloids. The sorption sites of montmorillonite colloid can be divided into two categories: sites of high energy that are effective sites for low cation concentration and sites of low energy that are only effective under high cation concentration. The fractions of the two kinds of sites vary with different pH conditions. When log [Cs+] or log [Sr2+] ranges among -3.5 to -1.5 mmol/L, the values of partition coefficient remain constant, which contributes to the bases of prediction for the Cs+ and Sr2+ sorption in subsurface environment. The sorbed Cs+ and Sr2+ could not completely desorb from colloids. X-ray defraction spectrums show that the sizes of clay lattice changed after sorption, which is worthy to investigate. The separation with centrifuge in this study was not satisfactorily to evaluate the rapid sorption rates.