Shear bond strength of four different esthetic brackets.

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Laboratory recommendations for scoring deep molecular responses following treatment for chronic myeloid leukemia.

Treatment of chronic myeloid leukemia (CML) with tyrosine kinase inhibitors has advanced to a stage where many patients achieve very low or undetectable levels of disease. Remarkably, some of these patients remain in sustained remission when treatment is withdrawn, suggesting that they may be at least operationally cured of their disease. Accurate definition of deep molecular responses (MRs) is therefore increasingly important for optimal patient management and comparison of independent data sets. We previously published proposals for broad standardized definitions of MR at different levels of sensitivity. Here we present detailed laboratory recommendations, developed as part of the European Treatment and Outcome Study for CML (EUTOS), to enable testing laboratories to score MR in a reproducible manner for CML patients expressing the most common BCR-ABL1 variants.Leukemia advance online publication, 27 February 2015; doi:10.1038/leu.2015.29.

Statistics of the National soil test database of France

In France, farmers commission about 250,000 soil-testing analyses per year to assist them managing soil fertility. The number and diversity of origin of the samples make these analyses an interesting and original information source regarding cultivated topsoil variability. Moreover, these analyses relate to several parameters strongly influenced by human activity (macronutrient contents, pH...), for which existing cartographic information is not very relevant. Compiling the results of these analyses into a database makes it possible to re-use these data within both a national and temporal framework. A database compilation relating to data collected over the period 1990-2009 has been recently achieved. So far, commercial soil-testing laboratories approved by the Ministry of Agriculture have provided analytical results from more than 2,000,000 samples. After the initial quality control stage, analytical results from more than 1,900,000 samples were available in the database. The anonymity of the landholders seeking soil analyses is perfectly preserved, as the only identifying information stored is the location of the nearest administrative city to the sample site. We present in this dataset a set of statistical parameters of the spatial distributions for several agronomic soil properties. These statistical parameters are calculated for 4 different nested spatial entities (administrative areas: e.g. regions, departments, counties and agricultural areas) and for 4 time periods (1990-1994, 1995-1999, 2000-2004, 2005-2009). Two kinds of agronomic soil properties are available: the firs one correspond to the quantitative variables like the organic carbon content and the second one corresponds to the qualitative variables like the texture class. For each spatial unit and temporal period, we calculated the following statistics stets: the first set is calculated for the quantitative variables and corresponds to the number of samples, the mean, the standard deviation and, the 2-,4-,10-quantiles; the second set is calculated for the qualitative variables and corresponds to the number of samples, the value of the dominant class, the number of samples of the dominant class, the second dominant class, the number of samples of the second dominant class.

E-comparisons: A new approach to round robin tests for environmental noise assessment in transport infrastructures

The increasing importance of pollutant noise has led to the creation of many new noise testing laboratories in recent years. For this reason and due to the legal implications that noise reporting may have, it is necessary to create procedures intended to guarantee the quality of the testing and its results. For instance, the ISO/IEC standard 17025:2005 specifies general requirements for the competence of testing laboratories. In this standard, interlaboratory comparisons are one of the main measures that must be applied to guarantee the quality of laboratories when applying specific methodologies for testing. In the specific case of environmental noise, round robin tests are usually difficult to design, as it is difficult to find scenarios that can be available and controlled while the participants carry out the measurements. Monitoring and controlling the factors that can influence the measurements (source emissions, propagation, background noise…) is not usually affordable, so the most extended solution is to create very effortless scenarios, where most of the factors that can have an influence on the results are excluded (sampling, processing of results, background noise, source detection…) The new approach described in this paper only requires the organizer to make actual measurements (or prepare virtual ones). Applying and interpreting a common reference document (standard, regulation…), the participants must analyze these input data independently to provide the results, which will be compared among the participants. The measurement costs are severely reduced for the participants, there is no need to monitor the scenario conditions, and almost any relevant factor can be included in this methodology

Análise de incerteza de um sistema automatizado para ensaios de aspersores de irrigação

Ensaios de distribuição de água de aspersores são convencionalmente realizados manualmente, requerendo tempo e mão de obra treinada. A automação desses ensaios proporciona redução da demanda por esses recursos e apresenta potencial para minimizar falhas e/ou desvios de procedimento. Atualmente, laboratórios de ensaio e calibração acreditados junto a organismos legais devem apresentar em seus relatórios a incerteza de medição de seus instrumentos e sistemas de medição. Além disso, normas de ensaio e calibração apresentam especificação de incerteza aceitável, como a norma de ensaios de distribuição de água por aspersores, ISO 15886-3 (2012), a qual exige uma incerteza expandida de até 3% em 80% dos coletores. Os objetivos deste trabalho foram desenvolver um sistema automatizado para os ensaios de aspersores em laboratório e realizar a análise de incerteza de medição, para sua quantificação nos resultados de ensaio e para dar suporte ao dimensionamento dos tubos de coleta. O sistema automático foi constituído por um subsistema de gerenciamento, por meio de um aplicativo supervisório, um de pressurização e um de coleta, por meio de módulos eletrônicos microprocessados desenvolvidos. De acordo com instruções do sistema de gerenciamento o sistema de pressurização ajustava a pressão no aspersor por meio do controle da rotação da motobomba, e o sistema de coleta realizava a medição da intensidade de precipitação de água ao longo do raio de alcance do aspersor. A água captada por cada coletor drenava para um tubo de coleta, que estava conectado a uma das válvulas solenoides de um conjunto, onde havia um transmissor de pressão. Cada válvula era acionada individualmente numa sequência para a medição do nível de água em cada tubo de coleta, por meio do transmissor. Por meio das análises realizadas, as menores incertezas foram obtidas para os menores diâmetros de tubo de coleta, sendo que se deve utilizar o menor diâmetro possível. Quanto ao tempo de coleta, houve redução da incerteza de medição ao se aumentar a duração, devendo haver um tempo mínimo para se atingir a incerteza-alvo. Apesar de cada intensidade requer um tempo mínimo para garantir a incerteza, a diferença mínima de nível a ser medida foi a mesma. Portanto, para os ensaios visando atender a incerteza, realizou-se o monitoramento da diferença de nível nos tubos, ou diferença de nível, facilitando a realização do ensaio. Outra condição de ensaio considerou um tempo de coleta para 30 voltas do aspersor, também exigido pela norma ISO 15886-3 (2012). A terceira condição considerou 1 h de coleta, como tradicionalmente realizado. As curvas de distribuição de água obtidas por meio do sistema desenvolvido foram semelhantes às obtidas em ensaios convencionais, para as três situações avaliadas. Para tempos de coleta de 1 h ou 30 voltas do aspersor o sistema automático requereu menos tempo total de ensaio que o ensaio convencional. Entretanto, o sistema desenvolvido demandou mais tempo para atingir a incerteza-alvo, o que é uma limitação, mesmo sendo automatizado. De qualquer forma, o sistema necessitava apenas que um técnico informasse os parâmetros de ensaio e o acionasse, possibilitando que o mesmo alocasse seu tempo em outras atividades.

Description of Risk Reduction Engineering Laboratory test and evaluation facilities.

Mode of access: Internet.

Seasonal skid resistance variations. Interim report.

Pennsylvania Department of Transportation, Bureau of Materials, Testing and Research, Harrisburg

Development of standards and tests for acceptance of traffic signal lenses. Final report.

Federal Highway Administration, Washington, D.C.

Panel evaluation of the NHTSA approach to the 1960-1963 Corvair handling and stability. Final report.

National Highway Traffic Safety Administration, Washington, D.C.

Measurement of hydroplaning potential. Final report.

Pennsylvania Department of Transportation, Bureau of Materials, Testing and Research, Harrisburg

NIST's dollars at work for you : a brief look into the office of administration /

Mode of access: Internet.

Gore area delineation. Final report.

Federal Highway Administration, Washington, D.C.

Relationship of locked wheel friction to that of other test modes. Final report.

Pennsylvania Department of Transportation, Bureau of Materials, Testing and Research, Harrisburg

In-pile loop test for the pebble bed reactor fuel development program : final report /

"Final report to Sanderson and Porter for subcontract no. S-3 under USAEC Prime Contract no. AT(30-1)-2378."

An investigation of the constitution of portland cement and properties of cement components with relations to disintegration of concrete,

At head of title: Civil Engineering Testing Laboratories, Columbia University ...