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Surveys assessment data

Nevertheless, to estimate human exposure to PAEs measuring the chemicals in foodstuffs, collecting survey/questionnaire data on personal hfestyle and food consumption are not very satisfactory because there are other sources which contributed to the overall human exposure to PAEs (e.g., dermal ccaitact and envircaimental media). Because of that, since the late 1990s many studies have been conducted with the target to prove that the urinary concentration of PAE metabohtes could be used as biomarkers to estimate dose in risk human assessment of PAEs. [Pg.322]

Army. 1986. Literature survey and data base assessment Microbial fate of diesel fuel and fog oils. Project no. 3E162720A835. Frederick, MD U.S. Army Bioengineering Research and Development Laboratory, Fort Detrick. Document no. PC A03/MFA01. [Pg.165]

Data are thus considered to be any information that contributes to, or is relevant to, a particular exposure assessment.3 The term encompasses not just numerical values or estimates, but also information provided in other forms, such as default values adopted for regulatory purposes, theory developed from first principles or basic science, computer programs, surveys, demographic data, census information, graphs, mathematical formulae, subjective expert judgements and descriptive summaries. More detail on the diversity of information that contributes to exposure assessment may be found in the other IPCS risk assessment documents, shown in Figure 1 (IPCS, 2000, 2004, 2005 Part 1 of this document). [Pg.145]

This brief review has shown that there are some differences in the way dietary risk assessment is practiced between the US and the EU. Many of the differences have to do in the types of input data that are available, or in some of the methods used to collect the data. Regarding the food consun tion data, the US surveys use a dietary recall method, whereas the UK approach is a diary method that weighs and measures the amount of food consumed. In the US, data are collected for two non-consecutive days, whereas in the UK surveys, data are collected for either 4 or 7 consecutive days. The US survey is conducted as an integrated whole and includes all segments of the population. In contrast, the UK surveys are conducted for specific population groups. Finally, the US survey collects data at the household level, whereas the UK survey targets demographic characteristics, based upon census information. [Pg.367]

Based on dietary assessment data for energy and fat (Food Surveys Research Group, 2005), SBO accounts for about 12% of calories in the average American diet. Given the contribution of SBO to the diet, this chapter discusses the health effects of SBO and its constituent fatty acid profile, as well as soy protein and its bioactive components. [Pg.732]

United States Geologic Survey (USGS) (2000). World Assessment Summary Remaining Reserves. U.S. Geological Survey Digital Data Series 60. [Pg.73]

Despite the great data and information that are now available as a result of the Hospital SOPS database, one big deficit has been in our understanding of what hospitals are doing between their patient safety culture survey assessments. What initiatives are hospitals implementing How successful are those initiatives in improving patient safety culture and, ultimately, patient safety ... [Pg.275]

Distribution of Carbon. Estimation of the amount of biomass carbon on the earth s surface is a problem in global statistical analysis. Although reasonable projections have been made using the best available data, maps, surveys, and a host of assumptions, the vaHdity of the results is impossible to support with hard data because of the nature of the problem. Nevertheless, such analyses must be performed to assess the feasibiHty of biomass energy systems and the gross types of biomass available for energy appHcations. [Pg.9]

A proper assessment of the costs and benefits associated with standardization depends on having suitable baseline data with which to make a comparison. Several surveys have shown typical doUat returns for the investment in standardization in the range of 5 1—8 1 with occasional claims made for a ratio as high as 50 1. [Pg.21]

Similarly, contaminant concentrations in rivers or streams can be roughly assessed based on rate of contaminant introduction and dilution volumes. Estuary or impoundment concentration regimes are highly dependent on the transport mechanisms enumerated. Contaminants may be localized and remain concentrated or may disperse rapidly and become diluted to insignificant levels. The conservative approach is to conduct a more in-depth assessment and use model results or survey data as a basis for determining contaminant concentration levels. [Pg.235]

OSHA does not specify how the survey data is to be organized or analyzed. Employers should be able to verify that they have conducted an appropriate hazard assessment to identify the level of PPE required to protect the employee from any recognized hazards. The key here is recognized hazards. [Pg.126]

The assessment of exposure brings together all the data and compares the results of this integration with the chosen OEL. It begins with an initial appraisal and continues with a basic survey and then a detailed one until it is confirmed either that exposure exceeds the limit value or that it is sufficiently below that limit. [Pg.370]

Finally, for situations in which it is not clear that exposure is and will continue to be below the limit values, a detailed survey with a measurement strategy is required. The methods used are based mostly on instruments for sampling the environment in order to obtain reliable measurements of workplace air concentrations. In general, the measurement strategy must consider the most efficient use of resources for the purpose of obtaining quantitative data on exposures by having a clear idea of what the data will be used for or whether it meets the specified need. For example, if the data pertain to peak exposures, these peaks have to be assessed according to the STEL requirements, if any. [Pg.370]

The risk inventory or risk evaluation is die ne. t part of die hazard survey. It is not practical to expect the plan to cover every potential accident. When die hazards liave been evaluated, die plan should be focused on die most significant ones. This risk assessment stage requires die technical expertise of many people to compare die pieces of data and detennine die relevance of each. Among die important factors to be considered in performing die risk evaluation are die following ... [Pg.87]

Existing conditions What is the existing spatial, civil, structural and access conditions within the facility Typically, the following data should either be accessed from existing records and design requirements defined by the support function assessment or acquired by new site survey/investigations ... [Pg.53]

Complete data collection should be carried out weekly. Since changes in the unit are continuous, regular surveys permit distinction among the effects of feedstock, catalyst, and operating conditions. An accurate assessment of a cat cracker operation requires reliable plant data. A reasonable weight balance should have a 98% to 102% closure. [Pg.140]

Rickert, D.A. Hines, W.G. McKenzie, S.W. Project Development and Data Programs for Assessing the Quality of the Willamette River, Oregon. Geological Survey Circular 715-C. US6S, Reston, VA, 1976 1-31. [Pg.284]

In this phase of the risk assessment, the validity and reliability of conclusions and advice to risk managers depend on the quality, reliability, and relevance of available exposure data. Therefore it is necessary to (1) critically review the facts from food composition tables and the reasons for differences reported by and within countries, (2) consider the way foods are categorized and thus made comparable (or not) in food consumption surveys, and (3) explore how to refine assessments as more information becomes available. ... [Pg.569]

Generation of data on the nutrient content of agricultural products and foods forms the basis for estimating nutrient intakes of populations via dietary surveys, nutritional labelling for consumer protection, nutrition education for consumer food choice, home and institution menu planning and food purchase, and for research in nutrient requirements and metabolism, toxicant chemical composition is used to assess effects of farm management practices, crop culture, and food processing on chemical content and implications for human health. [Pg.210]

J.D. Martin, Quality of Pesticide Data for Environmental Water Samples Collected for the National Water-Quality Assessment Program, 1992-96, and Examples of the Use of Quality-control Information in Water-quality Assessments. US Geological Survey, Washington, DC (1999). Also available on the World Wide Web http //ca.water.usgs. gov/pnsp/rep/qcsuiumary/, accessed August 2002. [Pg.622]

W.W. Lapham, F.D. Wilde, and M. T. Koterba, Ground-Water Data-Collection Protocols and Procedures for the National Water-Quality Assessment Program Selection, Installation, and Documentation of Wells and Collection of Related Data, Open-File Report 95-398, US Geological Survey, Reston, VA (1995). [Pg.816]

Robison WL, Noshkin VE, Conrado CL, et al. 1997a. The northern Marshall Island radiological survey Data and dose assessment. Health Phys 73(l) 37-48. [Pg.257]


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See also in sourсe #XX -- [ Pg.6 , Pg.7 ]




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