978 resultados para 13200-065
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Vesienhoidon EU:n laajuisena tavoitteena on pohjavesien hyvä kemiallinen ja määrällinen tila vuoteen 2015. Pintavesien osalta tavoitteena on hyvän ekologisen tilan saavuttaminen. Vesienhoito on osa koko Euroopan laajuista, vesipolitiikan puitedirektiiviin pohjautuvaa työtä. Tavoitteiden täyttämiseksi on Kaakkois-Suomen alueen pohjavesille laadittu toimenpideohjelma. Lisäksi alueelle on laadittu kaksi pintavesien hoidon toimenpideohjelmaa, joista toinen kattaa Vuoksen ja toinen Kymijoen-Suomenlahden vesienhoitoalueen. Kaakkois-Suomen vesienhoidon pohjavesien toimenpideohjelmaan vuosille 2010–2015 on koottu tiedot pohjavettä heikentävistä toiminnoista, riskipohjavesialueista ja selvityskohteista sekä pohjavesien määrällisestä ja kemiallisesta tilasta. Toimenpideohjelmassa esitetään myös tärkeimmät toimenpiteet, joiden avulla pohjavesien määrällinen ja kemiallinen hyvä tila pyritään saavuttamaan ja ylläpitämään vuoteen 2015 mennessä. Kaakkois-Suomen alueella merkittävimmät pohjavettä vaarantavat ja muuttavat toiminnot ovat asutus ja maankäyttö, liikenne, pilaantuneet maa-alueet sekä teollisuus ja yritystoiminta. Myös maa-ainesten otolla, maa- ja metsätaloudella sekä vedenotolla ja tekopohjaveden muodostamisella voi olla pohjaveden laatua heikentäviä vaikutuksia. Pohjavesien määrällinen tila on kaikilla Kaakkois-Suomen pohjavesialueilla hyvä. Kemiallisen hyvän tilan saavuttaminen ja sen ylläpitäminen vaativat toimenpiteitä, joista tärkeimpiä ovat riskitoimintojen ohjaaminen pohjavesialueiden ulkopuolelle, pohjavesien suojelusuunnitelmat, pilaantuneiden maa-alueiden tutkimukset ja kunnostukset sekä tiealueiden pohjavesisuojausten rakentaminen. Pohjavesien hyvää kemiallista tilaa ei saavuteta kaikilla pohjavesialueilla vuoteen 2015 mennessä, vaikka esitetyt toimenpiteet toteutettaisiin. Toimenpideohjelma tarkistetaan kuuden vuoden välein, jolloin arvioidaan uudestaan pohjavesien tila ja toimet pohjavesien hyvän tilan saavuttamiseksi.
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Após várias décadas de busca de alternativas para controle do arroz-vermelho, desenvolveram-se genótipos de arroz tolerantes a herbicida do grupo químico das imidazolinonas, o qual controla eficientemente esta planta daninha no Sistema Clearfield. O experimento teve como objetivo avaliar: a eficiência do controle de arroz-vermelho com a mistura formulada dos herbicidas imazethapyr (75 g L-1) + imazapic (25 g L-1) (produto comercial Only®); o residual do herbicida no solo através dos danos causados ao azevém e arroz não-tolerante; e a taxa de ocorrência de cruzamento natural entre o arroz-vermelho e o arroz cultivado. O delineamento experimental foi de blocos ao acaso, com três tratamentos e doze repetições. Para determinar o fluxo gênico entre o arroz tolerante a imidazolinonas e o arroz-vermelho, foram coletadas e analisadas as panículas de arroz-vermelho não-controladas. O efeito residual do herbicida em culturas não-tolerantes foi verificado através de coleta de fitomassa de azevém e do estande inicial do cultivar de arroz não-tolerante semeado no ano seguinte. O herbicida testado controlou eficientemente o arroz-vermelho e a fitotoxicidade inicial não reduziu a produtividade do cultivar tolerante. O estande inicial do cultivar IRGA 417 foi afetado pelo residual do herbicida no solo. Os resultados mostraram também que ocorre cruzamento natural entre o arroz-vermelho e o arroz cultivado, e a taxa obtida no experimento foi de 0,065%.
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Correlations of measures of percentages of white coat color, five measures of production and two measures of reproduction were obtained from 4293 first lactation Holsteins from eight Florida dairy farms. Percentages of white coat color were analyzed as recorded and transformed by an extension of Box-Cox procedures. Statistical analyses were by derivative-free restricted maximum likelihood (DFREML) with an animal model. Phenotypic and genetic correlations of white percentage (not transformed) were with milk yield, 0.047 and 0.097; fat yield, 0.002 and 0.004; fat percentage, -0.047 and -0.090; protein yield, 0.024 and 0.048; protein percentage, -0.070 and -0.116; days open, -0.012 and -0.065; and calving interval, -0.007 and -0.029. Changes in magnitude of correlations were very small for all variables except days open. Genetic and phenotypic correlations of transformed values with days open were -0.027 and -0.140. Modest positive correlated responses would be expected for white coat color percentage following direct selection for milk, fat, and protein yields, but selection for fat and protein percentages, days open, or calving interval would lead to small decreases.
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Injection of an Ascaris suum extract (Asc) affects both the humoral and cellular immune responses to unrelated antigens when it is co-administered with these antigens. In the present study we evaluated the effect of Asc on macrophage activation in the early phase of Mycobacterium bovis BCG (Pasteur strain TMCC 1173) infection in C57Bl/6 mice. C57Bl/6 mice were injected intraperitoneally (ip) with 0.1 mg BCG (BCG group) or BCG plus 1 mg Asc (BCG + Asc group). The peritoneal exudates were obtained at 2, 7 and 14 days after infection. The numbers of IFN-g-secreting cells were assessed by the ELISPOT assay. Nitric oxide (NO) production was measured by the Griess method and by the evaluation of NADPH diaphorase activity in the peritoneal exudates. The administration of Asc extract increased NADPH diaphorase activity (2 days: control = 0, BCG = 7%, BCG + Asc = 13%, and Asc = 4%; 7 days: control = 4, BCG = 13%, BCG + Asc = 21%, and Asc = 4.5%) and TNF-a levels (mean ± SD; 2 days: control = 0, BCG = 169 ± 13, BCG + Asc = 202 ± 37, and Asc = 0; 7 days: control = 0, BCG = 545 ± 15.5, BCG + Asc = 2206 ± 160.6, and Asc = 126 ± 26; 14 days: control = 10 ± 1.45, BCG = 9 ± 1.15, BCG + Asc = 126 ± 18, and Asc = 880 ± 47.67 pg/ml) in the early phase of BCG infection. Low levels of NO production were detected at 2 and 7 days after BCG infection, increasing at 14 days (mean ± SD; 2 days: control = 0, BCG = 3.7 ± 1.59, BCG + Asc = 0.82 ± 0.005, Asc = 0.48 ± 0.33; 7 days: control = 0, BCG = 2.78 ± 1.54, BCG + Asc = 3.07 ± 1.05, Asc = 0; 14 days: control = 0, BCG = 9.05 ± 0.53, BCG + Asc = 9.61 ± 0.81, Asc = 10.5 ± 0.2 (2 x 106) cells/ml). Furthermore, we also observed that Asc co-injection induced a decrease of BCG-colony-forming units (CFU) in the spleens of BCG-infected mice during the first week of infection (mean ± SD; 2 days: BCG = 1.13 ± 0.07 and BCG + Asc = 0.798 ± 0.305; 7 days: BCG = 1.375 ± 0.194 and BCG + Asc = 0.548 ± 0.0226; 14 days: BCG = 0.473 ± 0.184 and BCG + Asc = 0.675 ± 0.065 (x 102) CFU). The present data suggest that Asc induces the enhancement of the immune response in the early phase of BCG infection.
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Den här publikationen går in på hur fånggrödorna minskar kväveurlakningen och hur de lämpar sig för odling i praktiken. I första delen behandlar vi fånggrödornas möjligheter att minska urlakningen av kväve på en vetenskaplig forskningsgrund och i andra delen går vi in på jordbrukarnas erfarenheter av fånggrödor gårdsvis. Forskningen och de gårdsvisa försöken visar att fånggrödorna hindrar kväveurlakningen. Fånggrödorna har också en gynnsam verkan på markstrukturen och den minskar erosionen och mängden ogräs i växtligheten. Publikationen är avsedd att vara till hjälp för de jordbrukare som planerar att börja odla fånggrödor. Denna guide ingår i det material som producerats inom TEHO Plus-projektet för jordbrukare och rådgivare. Den kompletterar Gårdens miljöhandbok, som också sammanställts inom projektet.
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Cancer cachexia induces host protein wastage but the mechanisms are poorly understood. Branched-chain amino acids play a regulatory role in the modulation of both protein synthesis and degradation in host tissues. Leucine, an important amino acid in skeletal muscle, is higher oxidized in tumor-bearing animals. A leucine-supplemented diet was used to analyze the effects of Walker 256 tumor growth on body composition in young weanling Wistar rats divided into two main dietary groups: normal diet (N, 18% protein) and leucine-rich diet (L, 15% protein plus 3% leucine), which were further subdivided into control (N or L) or tumor-bearing (W or LW) subgroups. After 12 days, the animals were sacrificed and their carcass analyzed. The tumor-bearing groups showed a decrease in body weight and fat content. Lean carcass mass was lower in the W and LW groups (W = 19.9 ± 0.6, LW = 23.1 ± 1.0 g vs N = 29.4 ± 1.3, L = 28.1 ± 1.9 g, P < 0.05). Tumor weight was similar in both tumor-bearing groups fed either diet. Western blot analysis showed that myosin protein content in gastrocnemius muscle was reduced in tumor-bearing animals (W = 0.234 ± 0.033 vs LW = 0.598 ± 0.036, N = 0.623 ± 0.062, L = 0.697 ± 0.065 arbitrary intensity, P < 0.05). Despite accelerated tumor growth, LW animals exhibited a smaller reduction in lean carcass mass and muscle myosin maintenance, suggesting that excess leucine in the diet could counteract, at least in part, the high host protein wasting in weanling tumor-bearing rats.
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We have shown that the free cholesterol (FC) and the cholesteryl ester (CE) moieties of a nanoemulsion with lipidic structure resembling low-density lipoproteins show distinct metabolic fate in subjects and that this may be related to the presence of dyslipidemia and atherosclerosis. The question was raised whether induction of hyperlipidemia and atherosclerosis in rabbits would affect the metabolic behavior of the two cholesterol forms. Male New Zealand rabbits aged 4-5 months were allocated to a control group (N = 17) fed regular chow and to a 1% cholesterol-fed group (N = 13) during a 2-month period. Subsequently, the nanoemulsion labeled with ³H-FC and 14C-CE was injected intravenously for the determination of plasma kinetics and tissue uptake of the radioactive labels. In controls, FC and CE had similar plasma kinetics (fractional clearance rate, FCR = 0.234 ± 0.056 and 0.170 ± 0.038 h-1, respectively; P = 0.065). In cholesterol-fed rabbits, the clearance of both labels was delayed and, as a remarkable feature, FC-FCR (0.089 ± 0.033 h-1) was considerably greater than CE-FCR (0.046 ± 0.010 h-1; P = 0.026). In the liver, the major nanoemulsion uptake site, uptake of the labels was similar in control animals (FC = 0.2256 ± 0.1475 and CE = 0.2135 ± 0.1580%/g) but in cholesterol-fed animals FC uptake (0.0890 ± 0.0319%/g) was greater than CE uptake (0.0595 ± 0.0207%/g; P < 0.05). Therefore, whereas in controls, FC and CE have similar metabolism, the induction of dyslipidemia and atherosclerosis resulted in dissociation of the two forms of cholesterol.
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O presente trabalho avaliou a disponibilidade do ferro do feijão comum e os efeitos de suas interações com ácido ascórbico e cistina em comparação a disponibilidade deste metal em carne bovina. Para a determinação do teor de ferro e diálise de ferro in vitro, foram realizadas análises químicas nas amostras de carne bovina (C), feijão comum (F), feijão comum com ácido ascórbico (FA), feijão comum com cistina (FCI) e feijão comum com ácido ascórbico e cistina (FACI). Em F foram determinados taninos, ácido fítico e ácido oxálico. Em F foi encontrado 0,065 g de tanino/100 g; 8,03 mg de ácido fítico/g e 7,12 mg de ácido oxálico/g. A quantidade de ferro variou de 9,64 mg/100 g a 10,37 mg/100 g. A amostra FCI e FA apresentaram os menores teores de ferro. A quantidade de ferro encontrada na amostra C foi de 10,37 mg/100 g. A porcentagem de ferro dialisável variou de 17,33% a 24,31%. As amostras de carne bovina apresentaram a maior porcentagem de ferro dialisável, seguida por FACI. A menor porcentagem de ferro dialisável foi observada nas amostras F e FCI. Portanto, pode-se concluir que a adição simultânea de ácido ascórbico e cistina, tornou o ferro presente no feijão mais biodisponível, equiparando-o ao da carne bovina.
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Três linhagens genética suína A, B e C comercializadas no Brasil, foram submetidas ao insensibilizador elétrico manual (Karl Schermer 220-230/250 volts, 45-60 Hz e 1,4 - 1,5 A) e ao sistema gasoso coletivo (COMBI-BUTINA 90% CO2) . A insensibilização elétrica proporcionou níveis mais elevados de salpicamento nas regiões do coxão mole (0,477 e 0,26, p < 0,01), paleta/cranial (0,154 e 0,039, p < 0,05), paleta/central (0,261 e 0,052, p < 0,001), paleta/caudal (0,180 e 0,030, p < 0,01), lombo/central (0,185 e 0,065, p < 0,01), lombo/caudal (0,06 e 0,207, p < 0,01) e lombo/lateral externa (0,061 e 0,013, p < 0,05), assim como salpicamento mais difuso nas regiões do coxão-mole (0,461 e 0,279, p < 0,05), paleta/cranial (0,154 e 0,039, p < 0,01), paleta/central (0,231 e 0,039, p < 0,001) e paleta/caudal (0,185 e 0,026, p < 0,001). O sistema elétrico também proporcionou maiores índices de escoriações da pele nas regiões da paleta (1,098 e 0,795, p < 0,001), corpo (1,04 e 0,948, p < 0,05) e pernil (0,84 e 0,68, p < 0,001), assim como elevados índices de reflexo palpebral (11,57%) comparativamente ao gasoso (2,86%), de um total de 426 suínos. Pequenos índices de fraturas ósseas e contusões musculares em animais de ambos os sistemas foram observados.
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O Sistema Nacional de Transplantes (SNT) Brasileiro coordena e regulamenta o, provavelmente, maior programa de transplantes públicos do mundo. Desde o seu estabelecimento, em 1997, o número de transplantes renais aumentou de 920 (5,8 pmp), em 1988, para 4.630 (24,1 pmp), em 2010. Esse crescimento foi primariamente devido ao aumento no número de doadores efetivos (de 1,8 pmp em 1998 para 9,3 pmp em 2010), com aumento correspondente no número de rins transplantados de doadores falecidos (3,8 pmp em 1999 versus 9,9 pmp em 2010). O número de rins transplantados com órgãos de doadores vivos não aumentou significativamente, 1.065 (6,7 pmp), em 1998, para 1.641 (8,6 pmp), em 2010, tanto em consequência do melhor desempenho do programa de doadores falecidos, como talvez também devido a mais restrita regulamentação, permitindo apenas doação entre doadores vivos relacionados. De 2000 a 2009, a idade média dos doadores vivos aumentou de 40 para 45 anos, e a dos doadores falecidos, de 33 para 41 anos, com eventos cerebrovasculares sendo responsáveis por 50% dos episódios de óbito atualmente. Existem disparidades geográficas evidentes nos desempenhos entre as 5 regiões nacionais. Enquanto o estado de São Paulo ocupa a primeira posição em doação e captação de órgãos (22,5 pmp), alguns estados da região Norte apresentam pequena ou nenhuma atividade de transplante. Essas disparidades estão diretamente relacionadas à densidade populacional regional, ao produto interno bruto e ao número de médicos com treinamento em transplante. A avaliação inicial de desfechos clínicos robustos não indica diferenças nas sobrevidas do enxerto em comparação com as observadas nos EUA e na Europa. A etnia e o tempo em diálise, mas não o tipo de imunossupressão, apresentam influência decisiva nos desfechos medidos. A regulamentação nacional da pesquisa clínica foi implementada a partir de 1996, permitindo a participação de centros brasileiros em numerosos estudos clínicos nacionais e internacionais para o desenvolvimento de regimes imunossupressores. Acompanhando o desafio de atenuar as disparidades regionais no acesso ao transplante, o sistema pode ser aperfeiçoado pela criação de um registro nacional para receptores de transplante e de doadores vivos de rins e também pela promoção de estudos clínicos e experimentais voltados a melhor compreender a resposta imune relacionada ao transplante em nossa população.
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1920/10/07 (Numéro 13200).
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Relationships between surface sediment diatom assemblages and lake trophic status were studied in 50 Canadian Precambrian Shield lakes in the Muskoka-Haliburton and southern Ontario regions. The purpose of this study was to develop mathematical regression models to infer lake trophic status from diatom assemblage data. To achieve this goal, however, additional investigations dealing with the evaluation of lake trophic status and the autecological features of key diatom species were carried out. Because a unifying index and classification for lake trophic status was not available, a new multiple index was developed in this study, by the computation of the physical, chemical and biological data from 85 south Ontario lakes. By using the new trophic parameter, the lake trophic level (TL) was determined: TL = 1.37 In[1 +(TP x Chl-a / SD)], where, TP=total phosphorus, Chl-a=chlorophyll-a and SD=Secchi depth. The boundaries between 7 lake trophic categories (Ultra-oligotrophic lakes: 0-0.24; Oligotrophic lakes: 0.241-1.8; Oligomesotrophic lakes: 1.813.0; Mesotrophic lakes: 3.01-4.20; Mesoeutrophic lakes: 4.21-5.4; Eutrophic lakes: 5.41-10 and Hyper-eutrophic lakes: above 10) were established. The new trophic parameter was more convenient for management of water quality, communication to the public and comparison with other lake trophic status indices than many of the previously published indices because the TL index attempts to Increase understanding of the characteristics of lakes and their comprehensive trophic states. It is more reasonable and clear for a unifying determination of true trophic states of lakes. Diatom specIes autecology analysis was central to this thesis. However, the autecological relationship of diatom species and lake trophic status had not previously been well documented. Based on the investigation of the diatom composition and variety of species abundance in 30 study lakes, the distribution optima of diatom species were determined. These determinations were based on a quantitative method called "weighted average" (Charles 1985). On this basis, the diatom species were classified into five trophic categories (oligotrophic, oligomesotrophic, mesotrophic, mesoeutrophic and eutrophic species groups). The resulting diatom trophic status autecological features were used in the regressIon analysis between diatom assemblages and lake trophic status. When the TL trophic level values of the 30 lakes were regressed against their fi ve corresponding diatom trophic groups, the two mathematical equations for expressing the assumed linear relationship between the diatom assemblages composition were determined by (1) uSIng a single regression technique: Trophic level of lake (TL) = 2.643 - 7.575 log (Index D) (r = 0.88 r2 = 0.77 P = 0.0001; n = 30) Where, Index D = (0% + OM% + M%)/(E% + ME% + M%); 4 (2) uSIng a' multiple regressIon technique: TL=4.285-0.076 0%- 0.055 OM% - 0.026 M% + 0.033 ME% + 0.065 E% (r=0.89, r2=0.792, P=O.OOOl, n=30) There was a significant correlation between measured and diatom inferred trophic levels both by single and multiple regressIon methods (P < 0.0001, n=20), when both models were applied to another 20 test lakes. Their correlation coefficients (r2 ) were also statistically significant (r2 >0.68, n=20). As such, the two transfer function models between diatoms and lake trophic status were validated. The two models obtained as noted above were developed using one group of lakes and then tested using an entirely different group of lakes. This study indicated that diatom assemblages are sensitive to lake trophic status. As indicators of lake trophic status, diatoms are especially useful in situations where no local trophic information is available and in studies of the paleotrophic history of lakes. Diatom autecological information was used to develop a theory assessing water quality and lake trophic status.
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Fermi patches in quasi-two dimensional charge density waves (CDW) have not described the connection to superconductivity (SC) according to theory adequately at this point in time. The connection between CDW and SC in the quasi-two dimensional material CuxTiSe2 is an interesting one which might reveal mechanisms in unconventional superconductors. A previous Brock graduate student grew crystals of CuxTiSe2. The precise doping of the samples was not known. In order to determine the doping parameter x in CuxTiSe2, a sensitive resistivity measurement system was necessary. A new resistivity measurement system was designed and implemented utilizing an Infrared Labs HDL-10 He3 cryostat. By comparing with data from the literature, doping of two samples was investigated using the new measurement system and a Quantum Design Magnetic Property Measurement System (MPMS). Methods for determining the doping revealed that the old resistivity system would not be able to determine the CDW transition temperature of highly doped samples or doping for elongated samples due to electronic noise. Doping in one sample was found to be between x=0.06 and x=0.065. Values of doping in the second sample had a discrepancy but could be explained by incorrect sample orientation.