No description available.

Per- and polyfluoroalkyl substances (PFAS) are synthetic compounds that have beenaround since 1940. They can be used in a variety of products such as fire-fighting foam,food packaging and cosmetic products. Many PFAS have potential toxic effects on bothhumans and animals which poses a problem due to their wide distribution and persistency.Another problem concerns the remediation of PFAS, where the substances ends upcirculating between the different disposal types (landfills, wastewater treatment andincineration). Active methods are therefore needed to remove or retain the contaminants.Some examples of these remediation technologies can be biomaterials, organoclays andmore advanced methods such as activated carbon and ion exchange. The more advancedbeing suited for remediation of drinking water. In this study, the sorption efficiency oftwo pine bark fractions has been studied and also compared to the efficiency of activatedcarbon. The evaluation was done for both target analysis (PFAS-11) and non-specificanalysis of extractable organofluorine (EOF) compounds in contaminated water from ahazardous waste management facility. The two pine bark fractions indicated similarsorption efficiencies, for both the PFAS-11 and the EOF compounds. The sorptionefficiency ranged from 10% up to 75% for perfluorinated sulfonic acids (PFSA) and frombelow zero up to 40% for perfluorinated carboxylic acids (PFCA). A general pattern canbe seen, the sorption efficiency increases with increasing length of the PFAS chain. Theactivated carbon had a higher sorption efficiency, where the majority of PFAS had anaverage sorption of 100%. In comparison, the PFAS-11 and total EOF analysis displayedhigh concentrations of unidentified EOF compounds. These compounds indicated anegative sorption, which might imply that non-targeted PFAS or other fluorinated organic compounds desorb from the bark. Therefore, the pine bark might be suitable as a roughremediation of long-chain PFAS (≥8C), but further studies on the sorption of unidentifiedfluorinated organic compounds are of interest.Keywords:

No description available.

We examined the effects of periodic nitrogen (N) and phosphorus (P) fertilizer applications on the O horizon and mineral soil in loblolly pine (Pinus taeda L.) plantations over a 12-year period. To accomplish this, we used 9 experimental sites located across the south, which were grouped using the CRIFF Classification System. Group 1—CRIFF A, B (poorly-drained Ultisols); group 2—CRIFF C, D, G (sandy Spodosols and Entisols); and group 3—CRIFF E, F (well-drained Ultisols). Fertilization rates were 135, 202, and 269 kg N ha-1 at 4 years application frequency. This resulted in a cumulative N application rate of 540, 808, and 1076 kg ha-1. P was added at 10% of the N rate. Fertilization increased the mass, N content, and P content of the O horizon in all soil groups. Fertilization did not impact mineral soil N. No significant increases in total N trends were observed to a depth of 1 m. Likewise, total inorganic N (NH4+ + NO3-) was not affected by fertilization. These results suggest that N fertilization will have little effect on long-term soil N availability regardless of soil types. In contrast, fertilization increased extractable P in soil CRIFF groups 1, 2, and 3 by 26, 60, and 4 kg P ha-1 respectively suggesting potential for long-term soil P availability and site quality improvement. However, the low extractable P in soil group 3 implies additional fertilization with P for the next rotation for sites included into this soil group. / Master of Science

Introdução: Polifenóis não-extraíveis (NEPPs) são uma fração de polifenóis que não são extraídos da forma convencional por estarem associados à parede celular de produtos de origem vegetal. Um corpo crescente de estudos tem evidenciado seus potenciais efeitos benéficos, especialmente associados à saúde intestinal e interações com a microbiota. O guaraná (Paullinia cupana), fruto típico da biota amazônica, é conhecidamente rico em polifenóis da família dos flavanóis, mas ainda existe uma lacuna a respeito da fração de polifenóis não-extraíveis em sua composição. Objetivo: Caracterizar a fração de polifenóis não-extraíveis quanto a sua composição química, e avaliar sua potencial capacidade de inibição enzimática. Métodos: O guaraná em pó foi submetido a extração aquo-orgânica para obtenção da fração extraível, e o resíduo proveniente dessa extração foi submetido a hidrólise ácida e hidrólise básica para obtenção dos NEPPs. A capacidade redutora total (CRT) foi quantificada pelo método de Folin-Ciocalteu. A quantificação de taninos condensados foi realizada pelo método de Porter. A determinação do perfil de fenólicos foi realizada por HPLC-ECD e LC-MS para as frações extraíveis e hidrolisáveis, e MALDi-TOF/TOF para a fração condensada. Os testes enzimáticos foram realizados com base na cinética de estado estacionário. Os testes estatísticos foram realizados utilizando softwares Excel e SPSS. Resultados: O perfil de fenólicos para a fração extraível consiste na presença de catequina e epicatequina como componentes majoritários, com 5,45 ± 0,15 e 5,95 ± 0,22 mg/g de guaraná em pó (base seca), respectivamente, além de proantocianidinas B1 e B2 e trímero de tipo A. Já o perfil fenólico da fração não-extraível contém uma mistura complexa de monômeros como catequina, leucoantocianidina, cianidina e delfinidina. A fração NEPP também contém dímeros, trímeros, tetrâmeros e pentâmeros de flavanóis, tanto de tipo A quanto de tipo B, com alta variabilidade de grau de hidroxilação. O ensaio enzimático com α-glicosidase resultou em valores de IC50 de 9,504 e 1,624 µg EAG/mL para a fração extraível e a não-extraível, respectivamente. O modo de inibição para ambas as frações foi classificado como misto, com valores de Ki e K\'i de 0,403 e 1,735 µg/mL para a fração extraível e 0,287 e 0,847 µg/mL para a fração não-extraível. Conclusões: A fração de polifenóis não-extraíveis possui composição variada e complexa quando comparada a fração extraível, e possui potencial de inibição de α-glicosidase que deve ser explorado de maneira mais aprofundada, uma vez que tal potencial é de interesse para o controle de doenças crônicas como o diabetes tipo 2. / Introduction: Non-extractable polyphenols (NEPPs) are a portion of polyphenols that cannot be extracted in the conventional way due to being associated with the cell wall of products of plant origin. A growing number of studies have been showing its potential beneficial effects, especially in relation to gut health and microbiota interactions. The guarana (Paullinia cupana), a fruit native of the Amazon rainforest, is known to be rich in polyphenols from the flavanol family, but there is still a gap about non-extractable polyphenols in its composition. Objective: Characterize the non-extractable polyphenol portion in relation to its chemical composition and evaluate its enzymatic inhibition capacity. Methods: The extractable fraction was obtained by aqueous-organic extraction, and the residue from this extraction was treated with acid and alkaline hydrolysis to obtain the NEPPs. The total reducing capacity (TRC) was quantified by the Folin-Ciocalteu method. The quantification of condensed tannins was performed with the Porter method. The phenolic profile was determined by HPLC-ECD and LC-MS for the extractable and hydrolysable fractions, and MALDi-TOF/TOF for the condensed fraction. The enzymatic assay was carried out using steady-state kinetics. The statistical tests were performed using Excel and SPSS. Results: The phenolic profile of the extractable fraction consists of catechin and epicatechin as major components with 5,45 ± 0,15 and 5,95 ± 0,22 mg/g guarana powder (dry weight), respectively, besides B1 and B2 proanthocyanidins and type A trimer. The phenolic profile of the non-extractable fraction contains a complex mixture of monomers like catechin, leucoanthocyanidin, cyanidin, and delphinidin. The NEPP fraction also contains type A and type B dimers, trimers, tetramers, and pentamers of flavanols, with high variability of the degree of hydroxylation. The α-glucosidase enzymatic assay had IC50 values of 9,504 and 1,624 Introduction: Non-extractable polyphenols (NEPPs) are a portion of polyphenols that cannot be extracted in the conventional way due to being associated with the cell wall of products of plant origin. A growing number of studies have been showing its potential beneficial effects, especially in relation to gut health and microbiota interactions. The guarana (Paullinia cupana), a fruit native of the Amazon rainforest, is known to be rich in polyphenols from the flavanol family, but there is still a gap about non-extractable polyphenols in its composition. Objective: Characterize the non-extractable polyphenol portion in relation to its chemical composition and evaluate its enzymatic inhibition capacity. Methods: The extractable fraction was obtained by aqueous-organic extraction, and the residue from this extraction was treated with acid and alkaline hydrolysis to obtain the NEPPs. The total reducing capacity (TRC) was quantified by the Folin-Ciocalteu method. The quantification of condensed tannins was performed with the Porter method. The phenolic profile was determined by HPLC-ECD and LC-MS for the extractable and hydrolysable fractions, and MALDi-TOF/TOF for the condensed fraction. The enzymatic assay was carried out using steady-state kinetics. The statistical tests were performed using Excel and SPSS. Results: The phenolic profile of the extractable fraction consists of catechin and epicatechin as major components with 5,45 ± 0,15 and 5,95 ± 0,22 mg/g guarana powder (dry weight), respectively, besides B1 and B2 proanthocyanidins and type A trimer. The phenolic profile of the non-extractable fraction contains a complex mixture of monomers like catechin, leucoanthocyanidin, cyanidin, and delphinidin. The NEPP fraction also contains type A and type B dimers, trimers, tetramers, and pentamers of flavanols, with high variability of the degree of hydroxylation. The α-glucosidase enzymatic assay had IC50 values of 9,504 and 1,624 Introduction: Non-extractable polyphenols (NEPPs) are a portion of polyphenols that cannot be extracted in the conventional way due to being associated with the cell wall of products of plant origin. A growing number of studies have been showing its potential beneficial effects, especially in relation to gut health and microbiota interactions. The guarana (Paullinia cupana), a fruit native of the Amazon rainforest, is known to be rich in polyphenols from the flavanol family, but there is still a gap about non-extractable polyphenols in its composition. Objective: Characterize the non-extractable polyphenol portion in relation to its chemical composition and evaluate its enzymatic inhibition capacity. Methods: The extractable fraction was obtained by aqueous-organic extraction, and the residue from this extraction was treated with acid and alkaline hydrolysis to obtain the NEPPs. The total reducing capacity (TRC) was quantified by the Folin-Ciocalteu method. The quantification of condensed tannins was performed with the Porter method. The phenolic profile was determined by HPLC-ECD and LC-MS for the extractable and hydrolysable fractions, and MALDi-TOF/TOF for the condensed fraction. The enzymatic assay was carried out using steady-state kinetics. The statistical tests were performed using Excel and SPSS. Results: The phenolic profile of the extractable fraction consists of catechin and epicatechin as major components with 5,45 ± 0,15 and 5,95 ± 0,22 mg/g guarana powder (dry weight), respectively, besides B1 and B2 proanthocyanidins and type A trimer. The phenolic profile of the non-extractable fraction contains a complex mixture of monomers like catechin, leucoanthocyanidin, cyanidin, and delphinidin. The NEPP fraction also contains type A and type B dimers, trimers, tetramers, and pentamers of flavanols, with high variability of the degree of hydroxylation. The α-glucosidase enzymatic assay had IC50 values of 9,504 and 1,624 µg GAE/mL for the extractable and non-extractable fraction, respectively. The mode of inhibition was classified as mixed for both fractions, with Ki and K\'i values of 0,403 and 1,735 µg/mL for the extractable fraction and 0,287 and 0,847 µg/mL for the non-extractable fraction. Conclusions: The non-extractable polyphenols fraction has a varied and complex composition when compared to the extractable fraction, and it has a α-glucosidase inhibition potential that must be explored in a more detailed fashion since said potential is of interest for the control of chronic diseases such as type 2 diabetes. g GAE/mL for the extractable and non-extractable fraction, respectively. The mode of inhibition was classified as mixed for both fractions, with Ki and K\'i values of 0,403 and 1,735 µg/mL for the extractable fraction and 0,287 and 0,847 µg/mL for the non-extractable fraction. Conclusions: The non-extractable polyphenols fraction has a varied and complex composition when compared to the extractable fraction, and it has a α-glucosidase inhibition potential that must be explored in a more detailed fashion since said potential is of interest for the control of chronic diseases such as type 2 diabetes. g GAE/mL for the extractable and non-extractable fraction, respectively. The mode of inhibition was classified as mixed for both fractions, with Ki and K\'i values of 0,403 and 1,735 µg/mL for the extractable fraction and 0,287 and 0,847 µg/mL for the non-extractable fraction. Conclusions: The non-extractable polyphenols fraction has a varied and complex composition when compared to the extractable fraction, and it has a α-glucosidase inhibition potential that must be explored in a more detailed fashion since said potential is of interest for the control of chronic diseases such as type 2 diabetes.

Per- and polyfluoroalkyl substances (PFAS) have been manufactured and used in differentapplications for several decades, including food packaging materials. During the last 20 yearsthese compounds have been acknowledged as hazardous for humans and the environment, anddifferent regulations on PFAS have been established on both national and international levels.Companies started to phase-out long-chain PFAS, including both PFOA and PFOS, around 20years ago. Since PFAS are persistent, this cause concerns both for our health and theenvironment, as well as possible PFAS contamination in new products due to the recycling ofmaterials. The aim of this study was to find an effective method to extract PFAS from differentfood packaging materials; analyze the samples for their extractable organofluorine (EOF)content using combustion ion chromatography; as well as analyze targeted PFAS in the samplesusing ultra-high performance liquid chromatography tandem mass spectrometry. The findingsof this study suggest that none of the selected samples had EOF contents above the Danishindicator value of 20 mg/kg dw TOF set to determine whether PFAS has been intentionallyadded to a material, and that only two samples exceeded the limit of detection for EOF. Atakeaway bowl made out of 100% sugarcane contained the highest EOF content while the outerpackaging of a cereal box contained the second highest EOF. Both PFOA and PFOS, alongwith other long-chain PFAS were detected in a majority of the samples. The lowest total PFASconcentrations when analyzing for targeted PFAS was detected in the sugarcane take awaybowl. The highest total PFAS concentration was detected in an egg carton, followed by theouter packaging of a cereal box (same as above) and the outer box of a waffle mix. The targetedPFAS was detected in almost all samples, with PFNA and 6:2 diPAP being the most frequentlydetected PFAS. PFCAs, PFSAs, FTSAs, FOSAAs and PAPs were detected in a majority of thesamples. The highest concentrations were measured for diSAmPAP in a majority of thesamples. Mass balance calculations of the sugarcane bowl showed that the targeted PFAS onlyaccounted for 0.04% of the extractable organofluorine content. In conclusion, none of thesamples displayed EOF contents higher than the Danish indicator value, suggesting that noneof the samples were intentionally treated with PFAS. However, targeted PFAS analysis of thesesamples showed that they still contain PFAS, that could be further recycled along with therecycling of paper and board food packaging materials. Considering the persistence of PFASand that these compounds can remain in the recycling chain, with the risk of also being releasedinto the environment, it is of importance that PFAS is not introduced in any of the stages in apaper or board containers life cycle.

A diversidade microbiana é geralmente considerada por seu papel nos principais processos do ecossistema, tais como a decomposição da matéria orgânica e ciclos biogeoquímicos. No entanto, informações sobre o impacto da diversidade em funções menores, como degradação de xenobióticos são escassas. Nós estudamos a partir da abordagem da \'diluição para extinção\', o papel da diversidade sobre a capacidade da comunidade microbiana em degradar o fungicida clorotalonil (organoclorado). Também estudamos o comportamento da comunidade bacteriana após aplicação do pesticida no solo com e sem biochar. A diversidade microbiana do solo natural foi alterada artificialmente por diluição, constituindo um gradiente de diversidade (SN > 10-1 > 10-3 > 10-6), seguido pela inoculação em amostras de solo estéril e posterior reestruturação (15 dias). Após a reestruturação da comunidade, as amostras foram manejadas com biochar (1% m/m) e tratadas com a dose de campo do CHT. O comportamento da comunidade bacteriana foi estudo por PCR-DGGE e qPCR do gene 16S rDNA através de um experimento com molécula fria (não radiomarcada). Enquanto a capacidade de degradação do CHT foi estudada por radiorespirometria (14C-CHT). Inicialmente, a comunidade de bactérias foi influenciada pelo gradiente de diversidade obtido por diluição. A separação dos grupos bacterianos se mostrou bastante similar nos três primeiros períodos pré-aplicação do CHT (SN > 10-1 - 10-3 > 10-6), enquanto que no período de 15 dias, a dinâmica de grupos foi alterada (SN > 10-1 > 10-3 - 10-6). O fungicida e o biochar não exerceram efeitos na comunidade bacteriana no tempo zero (imediatamente após a aplicação), a modificação no perfil da comunidade foi atribuído à diluição. Nos períodos de 21 e 42 dias, o perfil comunidade bacteriana apresentou forte modificação. Os grupos bacterianos se mostraram mais dispersos quando considerado somente o CHT. Embora, a análise de ANOSIM indicou não haver diferença nas amostras com e sem biochar, sugerindo que o clorotalonil foi quem mais contribuiu na dispersão dos grupos bacterianos. No período de 42 d, a comunidade apresentou resposta positiva, sendo observado aumentos no número de bandas e no índice de Shannon em todos tratamentos. Isto possivelmente, devido a menor concentração do fungicida disponível na solução do solo, diminuindo assim, os efeitos deletérios sobre a comunidade. Os dados de qPCR não apresentaram alteração no número de copias do gene 16S rDNA em todos os tratamentos. A remoção da diversidade impactou fortemente a capacidade da comunidade bacteriana de degradar o clorotalonil. Apesar da capacidade de degradar não ter sido perdida, a mínima alteração na diversidade promoveu elevada redução na taxa de mineralização do CHT. A dissipação do CHT se mostrou rápida (D50 < 1 dia) em todos os tratamentos, além disso, a formação de 14C-resíduos não extraíveis foi constituiu um dos principais mecanismos de dissipação do CHT. A partir da degradação do fungicida, foram detectados três metabólitos. Conclui-se que a modificação por diluição da diversidade bacteriana promoveu impacto negativo na mineralização do clorotalonil. E que a formação de resíduos não extraíveis consistiu no principal mecanismo de dissipação do CHT em ambos solos. / Microbial diversity is generally considered for his role in key ecosystem processes, such as decomposition of organic matter and biogeochemical cycles. However, information about the impact of diversity on minor functions, such as degradation of xenobiotics is scant. We study from the approach of \'dilution to extinction\', the role of diversity on the capacity of microbial community to degrade the chlorothalonil (organochlorine). We also studied the behavior of bacterial community after applying the pesticide in the soil with and without biochar. Microbial diversity of the soil natural (control) was artificially altered by dilution, forming a gradient of diversity (SN > 10-1 > 10-3 > 10-6), followed by inoculation in sterile soil samples and subsequent restructuring (15 days). After of the community restructuring, the samples were handled with biochar (1% w/w) and treated with the chlorothalonil field dose. The behavior of the bacterial community was studied by PCR-DGGE and qPCR of the 16S rDNA gene through an experiment with cold molecule (no radiolabeled). While the CHT degradation capacity was studied by radiorespirometry (14C-CHT). Initially, the community of bacteria was influenced by the diversity gradient obtained by dilution. The separation of bacterial groups showed very similar in the first three pre-application periods of the CHT (SN > 10-1 - 10-3 > 10-6). While in the period of 15 days, the group dynamic has changed (SN > 10-1 > 10-3 e 10-6). During periods of 21 and 42 days, the profile bacterial community showed strong modification. The bacterial groups were more dispersed when only considered the CHT. Although, the ANOSIM analysis indicated no difference in samples with and without biochar, suggesting that chlorothalonil who has contributed the most in the dispersion of bacterial groups. In the period of 42 days, the community presented a positive response, being observed increases in the number of bands and Shannon-Weiner index in all treatments. This possibly due to less concentration of fungicide available in soil solution, thus reducing, the deleterious effects on the community. The qPCR dates showed no change in the number of copies of the 16S rDNA gene in all treatments. The removal of microbial strongly impacted the ability of the bacterial community to degrading chlorothalonil. Despite the ability to degrade not having been lost, the minimum change in diversity promoted high reduction in the rate of mineralization CHT. The dissipation of the CHT showed quick (D50 < 1 d) in all treatments, in addition, the formation of non-extractable 14C-residues was one of the main mechanisms of dissipation of the CHT. From the degradation of chlorothalonil, three metabolites were detected. We conclude that modification by dilution of the bacterial diversity had a negative impact on the mineralization of chlorothalonil. And the formation of non-extractable residues consisted in the main CHT dissipation mechanism in both soils.

A diversidade microbiana é geralmente considerada por seu papel nos principais processos do ecossistema, tais como a decomposição da matéria orgânica e ciclos biogeoquímicos. No entanto, informações sobre o impacto da diversidade em funções menores, como degradação de xenobióticos são escassas. Nós estudamos a partir da abordagem da \'diluição para extinção\', o papel da diversidade sobre a capacidade da comunidade microbiana em degradar o fungicida clorotalonil (organoclorado). Também estudamos o comportamento da comunidade bacteriana após aplicação do pesticida no solo com e sem biochar. A diversidade microbiana do solo natural foi alterada artificialmente por diluição, constituindo um gradiente de diversidade (SN > 10-1 > 10-3 > 10-6), seguido pela inoculação em amostras de solo estéril e posterior reestruturação (15 dias). Após a reestruturação da comunidade, as amostras foram manejadas com biochar (1% m/m) e tratadas com a dose de campo do CHT. O comportamento da comunidade bacteriana foi estudo por PCR-DGGE e qPCR do gene 16S rDNA através de um experimento com molécula fria (não radiomarcada). Enquanto a capacidade de degradação do CHT foi estudada por radiorespirometria (14C-CHT). Inicialmente, a comunidade de bactérias foi influenciada pelo gradiente de diversidade obtido por diluição. A separação dos grupos bacterianos se mostrou bastante similar nos três primeiros períodos pré-aplicação do CHT (SN > 10-1 - 10-3 > 10-6), enquanto que no período de 15 dias, a dinâmica de grupos foi alterada (SN > 10-1 > 10-3 - 10-6). O fungicida e o biochar não exerceram efeitos na comunidade bacteriana no tempo zero (imediatamente após a aplicação), a modificação no perfil da comunidade foi atribuído à diluição. Nos períodos de 21 e 42 dias, o perfil comunidade bacteriana apresentou forte modificação. Os grupos bacterianos se mostraram mais dispersos quando considerado somente o CHT. Embora, a análise de ANOSIM indicou não haver diferença nas amostras com e sem biochar, sugerindo que o clorotalonil foi quem mais contribuiu na dispersão dos grupos bacterianos. No período de 42 d, a comunidade apresentou resposta positiva, sendo observado aumentos no número de bandas e no índice de Shannon em todos tratamentos. Isto possivelmente, devido a menor concentração do fungicida disponível na solução do solo, diminuindo assim, os efeitos deletérios sobre a comunidade. Os dados de qPCR não apresentaram alteração no número de copias do gene 16S rDNA em todos os tratamentos. A remoção da diversidade impactou fortemente a capacidade da comunidade bacteriana de degradar o clorotalonil. Apesar da capacidade de degradar não ter sido perdida, a mínima alteração na diversidade promoveu elevada redução na taxa de mineralização do CHT. A dissipação do CHT se mostrou rápida (D50 < 1 dia) em todos os tratamentos, além disso, a formação de 14C-resíduos não extraíveis foi constituiu um dos principais mecanismos de dissipação do CHT. A partir da degradação do fungicida, foram detectados três metabólitos. Conclui-se que a modificação por diluição da diversidade bacteriana promoveu impacto negativo na mineralização do clorotalonil. E que a formação de resíduos não extraíveis consistiu no principal mecanismo de dissipação do CHT em ambos solos. / Microbial diversity is generally considered for his role in key ecosystem processes, such as decomposition of organic matter and biogeochemical cycles. However, information about the impact of diversity on minor functions, such as degradation of xenobiotics is scant. We study from the approach of \'dilution to extinction\', the role of diversity on the capacity of microbial community to degrade the chlorothalonil (organochlorine). We also studied the behavior of bacterial community after applying the pesticide in the soil with and without biochar. Microbial diversity of the soil natural (control) was artificially altered by dilution, forming a gradient of diversity (SN > 10-1 > 10-3 > 10-6), followed by inoculation in sterile soil samples and subsequent restructuring (15 days). After of the community restructuring, the samples were handled with biochar (1% w/w) and treated with the chlorothalonil field dose. The behavior of the bacterial community was studied by PCR-DGGE and qPCR of the 16S rDNA gene through an experiment with cold molecule (no radiolabeled). While the CHT degradation capacity was studied by radiorespirometry (14C-CHT). Initially, the community of bacteria was influenced by the diversity gradient obtained by dilution. The separation of bacterial groups showed very similar in the first three pre-application periods of the CHT (SN > 10-1 - 10-3 > 10-6). While in the period of 15 days, the group dynamic has changed (SN > 10-1 > 10-3 e 10-6). During periods of 21 and 42 days, the profile bacterial community showed strong modification. The bacterial groups were more dispersed when only considered the CHT. Although, the ANOSIM analysis indicated no difference in samples with and without biochar, suggesting that chlorothalonil who has contributed the most in the dispersion of bacterial groups. In the period of 42 days, the community presented a positive response, being observed increases in the number of bands and Shannon-Weiner index in all treatments. This possibly due to less concentration of fungicide available in soil solution, thus reducing, the deleterious effects on the community. The qPCR dates showed no change in the number of copies of the 16S rDNA gene in all treatments. The removal of microbial strongly impacted the ability of the bacterial community to degrading chlorothalonil. Despite the ability to degrade not having been lost, the minimum change in diversity promoted high reduction in the rate of mineralization CHT. The dissipation of the CHT showed quick (D50 < 1 d) in all treatments, in addition, the formation of non-extractable 14C-residues was one of the main mechanisms of dissipation of the CHT. From the degradation of chlorothalonil, three metabolites were detected. We conclude that modification by dilution of the bacterial diversity had a negative impact on the mineralization of chlorothalonil. And the formation of non-extractable residues consisted in the main CHT dissipation mechanism in both soils.

Dans la dernière décennie, plusieurs hectares de terre agricole ont été convertis à la culture intensive sur courtes rotations (CICR) de saules dans le sud du Québec (Canada). Peu d’études ont été réalisées afin de déterminer comment se comporte la dynamique du carbone organique (Corg) dans le sol suivant cette conversion. Nous avons donc comparé la quantité du Corg et de deux pools labiles de carbone (carbone extractible à l’eau chaude et les sucres aminés) entre des CICR en phase initiale d’établissement (1-2 ans) et des parcelles appariées représentant le système de culture qui prévalait avant la transformation en culture de saules (culture fourragère) et d’autres cultures d’intérêt. La même chose a été faite pour une CICR en exploitation (depuis 9 ans) à un autre site. La quantité de Corg du sol n’était pas différente entre les CICR et les parcelles sous culture fourragère. Une plus haute concentration de sucres aminés dans le Corg total des CICR en établissement, par rapport aux autres parcelles sur le même site, permet de soupçonner que les perturbations liées à l’établissement ne mènent pas à une minéralisation accrue du Corg à court terme. La proportion de sucres aminés fongiques, qui diminue théoriquement lors de perturbations, était aussi plus élevée sous la plus jeune culture. Sous la CICR de neuf ans, le Corg était redistribué dans le profil vertical et les pools labiles étaient de plus petite taille (à une profondeur de 20-40 cm) comparativement à une parcelle témoin. La conversion d’une culture fourragère en plantation de saules en CICR n’a pas mené à la formation d’un puits de carbone. L’étude laisse entrevoir qu’un tel puits pourrait être créé si la conversion se faisait à partir d’un aménagement impliquant la culture en rotation de plantes annuelles et des labours. / Over the last ten years, many hectares of short-rotation willow coppice (SRWC) have been established on abandoned agricultural lands in southern Quebec (Canada). However, few studies were conducted to determine if these changes from a conventional crop to SRWC of willows would affect the soil carbon dynamic. A preliminary paired-site study was conducted to assess the impact of this land-use conversion on soil carbon stocks and dynamics shortly after they were established (1-year and 2-year) at one site and after multiple rotations (9-year) at another site. Apart from the total soil organic carbon pool, two labile carbon pools were investigated: the hot-water extractable carbon (HWC) pool and the amino sugars (AS) pool. Willow establishment and exploitation for nine years did not bring any changes in total organic carbon compared to an abandoned hay culture. The mature SRWC displayed a redistribution of TSOC in the vertical soil profile. We also measured a higher proportion of AS, compared to other plots on the same site, in total organic carbon under the 1-year-old SRWC; especially the proportion in AS of fungi origin that theorically decrease with perturbation intensity. Proportion of AS was also elevated under 2-year-old SRWC. A possible interpretation is that establishment-linked perturbations did not shift carbon dynamic toward an increased mineralization. The mature willow plantation exhibited depletion of HWC and the more labile amino sugar (muramic acid) in the deeper soil layer (20-40cm). This case study shows that conversion from an abandoned hay culture to a SRWC did not create a carbon sink. It was also found that the 9- year old willow plantation contained higher TSOC and had better soil quality than an adjacent short-term no-till crop rotation culture.

Master of Science / Department of Agronomy / Ganga M. Hettiarachchi / Phosphorus (P) management in reduced tillage systems has been a great concern for farmers. Conclusive results for benefits of deep banding of P fertilizers for plant yield in reduced tillage system are still lacking. Knowledge of the dominant solid P species present in soil following application of P fertilizers and linking that to potential P availability would help us to design better P management practices. The objectives of this research were to understand the influence of placement (broadcast- vs. deep band-P or deep placed-P), fertilizer source (granular- versus liquid-P), and time on reaction products of P. Greenhouse and field based experiments were conducted to study P behavior in soils. Soil pH, resin extractable P, total P, and speciation of P were determined at different distances from the point of fertilizer application at 5 weeks (greenhouse and field) and 6 months (field) after P application (at rate 75 kg/ha) to a soil system that was under long-term reduced tillage. X-ray absorption near edge structure spectroscopy technique was used to speciate reaction products of fertilizer P in the soil. The reaction products of P formed upon addition of P fertilizers to soils were found to be influenced by soil pH, P placement methods, and P sources. Acidic pH (below~5.8) tended to favor formation of Fe-P and Al-P like forms whereas slightly acidic near neutral pH soils favored formation of Ca-P like forms. Scanning electron microscope with energy dispersive X-ray analysis of applied fertilizer granules at 5-wk showed enrichment of Al, Fe and Ca in granule- indicating these elements begin to react with applied P even before granules dissolve completely. The availability of an applied P fertilizer was found to be enhanced as a result of the deep banding as compared to the surface broadcasting or deep placed methods. Deep banded liquid MAP was found to be in more adsorbed P like forms and resulted greater resin extractable P both at 5 wk and 6 month after application. Deep banding of liquid MAP would most likely result both agronomically and environmentally efficient solution for no-till farmers.