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Risk assessment shortcomings

The initial risk categorization process and the use of control rating codes are not addressed in MIL-STD-882B and are believed to be unique to the facility system safety effort. [Pg.129]

As discussed in Chapter 4, current risk assessment efforts show some shortcomings. [Pg.129]

As pointed out in Chapter 4, deficiencies in the current risk assessment code systems represent one of the major problems facing the entire system safety effort. [Pg.129]

The quantitative severity and probability scales used in most RAC matrices are very subjective. The top of the severity scale is usually a dollar loss of about 500,000 or a single fatality, even though many hazards are capable of producing hundreds or thousands of fatalities and hundreds of millions of dollars in financial loss in a single accident. [Pg.130]

For all practical purposes, the risk assessment code is the driver in the system. The value of this code prioritizes the fixes and the management or command emphasis given to a particular problem. If these codes are not detailed enough to discriminate between very serious hazards and lesser hazards accurately, they are of little value. [Pg.130]

Pacility/nsfn Mentificalion MILCON Project Number.  [Pg.129]

For each proposed acceptance of a risk (e.g., a less than optimum RAC or CRC) associated with an identified hazard, provide the following  [Pg.129]


At the practical level, an ideal mechanistic biomarker should be simple to use, sensitive, relatively specific, stable, and usable on material that can be obtained by nondestructive sampling (e.g., blood or skin). A tall order, no doubt, and no biomarker yet developed has all of these attributes. However, the judicious use of combinations of biomarkers can overcome the shortcomings of individual assays. The main point to emphasize is that the resources so far invested in the development of biomarker technology for environmental risk assessment has been very small (cf the investment in biomarkers for use in medicine). Knowledge of toxic mechanisms of organic pollutants is already substantial (especially of pesticides), and it grows apace. The scientific basis is already there for technological advance it all comes down to a question of investment. [Pg.324]

The systematic evaluation of substance properties and predictable or actual exposure patterns over the entire life-time of a substance within the scope of risk assessment is as yet a relatively recent instrument, for which harmonised scientific rales were created in the EU for the first time in 1997 in the form of the Technical Guidance Documents (TGD). An essential element in this range of instruments is how to deal with shortcomings in knowledge. Wherever information is missing, standardised worst-case scenarios are conceived taking into account appropriate safety factors . If under these worst-case assumptions a rele-... [Pg.39]

In addition, the reliance on generic scenarios for inadvertent intrusion in classifying waste cannot, by definition, represent site-specific risks. However, this is not a serious shortcoming because such scenarios have been used in establishing subclasses of low-level radioactive waste for disposal in near-surface facilities (NRC, 1982a). Furthermore, as emphasized in this Report, establishment of a risk-based waste classification system using particular exposure scenarios does not obviate the need to perform site-specific risk assessments for the purpose of establishing waste acceptance criteria at each disposal site. [Pg.301]

Up to now, the physico-chemical phenomena were considered in risk assessment (if at all) by applying distribution coefficients (K ) in order to model the distribution of a contaminant between solid and aqueous phases. It follows a discussion of the shortcomings of such a model and how it could be improved. [Pg.81]

Percutaneous absorption studies utilizing rhesus monkeys have one Important single advantage. That is, their skin type and absorption characteristics seem to be similar to humans. This is of utmost concern since the purpose of this study is to simulate the human case. This is not a toxicology study, and it should not be the purpose of this study to estimate a worst case scenario as in a hazard identification study. Thus, in spite of the many shortcomings of the described procedures, monkey percutaneous absorption studies could play an important role in pesticide risk assessments. [Pg.90]

Nontechnical Summary In this paper, the process of risk assessment with compounds which exhibit chronic but not acute toxicity is first reviewed. The remainder of the paper is spent on reviewing the procedure for quantifying absorption through the skin. The test animal used is the rhesus monkey since previously published work has shown this animal to yield data most similar to man. Data are presented on oryzalin for which dermal absorption was less than 2 percent of the applied dose. The problems and shortcomings of the procedure as well as its advantage (similarity to man) are also discussed. [Pg.90]

One of the primary shortcomings of the standard data package with regard to worker/bystander risk assessment as It exists today is the emphasis on the oral route of exposure. Others are the limited data on kinetics of the chemical, lack of attention to determining the effect of the route of exposure on toxicity and the Inability to test combinations of pesticides In a manner which would approximate the type of nilxed exposure that applicators receive. These Issues complicate the risk assessments for applicators, for whom the primary route of exposure Is dermal and generally Is Intermittent. [Pg.438]

The shortcomings pertaining to the estloiatlon of exposure which have been described are very serious, and these Issues will have to be resolved before statistical risk assessment models can be utilized as the basis for regulatory decisions on the registration of pesticides. [Pg.441]

The serious failings and shortcomings in all phases of Statoil s planning can be summarised in three categories compliance with governing documents, management s involvement and lack of risk assessment. [Pg.368]

Predictive QSARs are studies aimed at providing estimates for endpoints and parameters required in environmental hazard and risk assessment. This is a demanding goal, which should be strived for only if the principal shortcomings of the approach are considered, otherwise there is the danger of running into scientifically obscure imponderables. [Pg.8]

Discuss briefly the shortcomings of the risk assessment codes currently in use. [Pg.49]

For example, it has been used with minor modification by at least one U.S. company to meet the European Community risk assessment requirements as set forth in ISO 14121, the Safety of Machinery—Principles for Risk Assessment Standard. As will be illustrated later, this risk-scoring system has major shortcomings. [Pg.175]

Chapter 4 summarizes some basic viewpoints on accident sources and risk assessment in industrial maintenance. A study focused on analysing severe and fatal accidents that had occurred during industrial maintenance in Finland. Additionally, a database of accident insurance institutions was revised to gain an understanding of less serious accidents in industrial maintenance. Some typical risk factors are poor system maintainability, defective task safety planning and shortcomings in customer cooperation. [Pg.4]

The patchwork of laws described above had several shortcomings, among them the limited availability of data for the bulk of chemicals in commerce and the schemes for risk assessment and promulgation of risk management measures [92]. Europa, the official website for the European Union, describes the results of these shortcomings "[T]he previous system often proved itself to be incapable of identifying risks posed by many chemicals and was slow to act when risks were identified" [93]. [Pg.89]


See other pages where Risk assessment shortcomings is mentioned: [Pg.405]    [Pg.405]    [Pg.405]    [Pg.129]    [Pg.129]    [Pg.129]    [Pg.129]    [Pg.405]    [Pg.405]    [Pg.405]    [Pg.129]    [Pg.129]    [Pg.129]    [Pg.129]    [Pg.241]    [Pg.239]    [Pg.162]    [Pg.94]    [Pg.421]    [Pg.263]    [Pg.244]    [Pg.300]    [Pg.480]    [Pg.425]    [Pg.307]    [Pg.341]    [Pg.159]    [Pg.478]    [Pg.478]    [Pg.343]    [Pg.49]    [Pg.369]    [Pg.25]    [Pg.2]    [Pg.346]   
See also in sourсe #XX -- [ Pg.441 ]

See also in sourсe #XX -- [ Pg.129 ]

See also in sourсe #XX -- [ Pg.129 ]




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