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Informal reports, definition

Incremental investments, 315-329 Index name, 893 subject, 897 Indexes, cosf 163-166 Indirect costs, 210 in capital investments, 160, 167 Inflation, 295 strategy for, 408-413 tax effects on, 410-413 Informal reports, definition of 453- 454 Infringements of patents, 102 Installation costs for equipmenf 171-172 Instrumentation cost of 172-173, 812-814 plant requirements for, 97 Insulation cost of 172 for pipe, 513 Insurance, 262-265 as a cost, 253, 262 cost of 205, 210 Intalox saddles, 688, 690, 694 cost of 710 Interest ... [Pg.903]

All research personnel must search for clues about safety events from many sources, such as information in clinical records at the study sites information in data collection forms (e.g. CRFs, diary cards, quality-of-life forms, psychiatric rating scales, etc.), occurrence of missed and/or unscheduled visits, dropouts and withdrawals use of any concomitant medications/devices and abnormal laboratory data. AEs may also occur simply as a result of study procedures and study participation. Information about definitions of AEs and requirements for reporting AEs must be clearly stated in the protocol and explained to the site staff, who must also be educated in the correct procedure and immediate requirement for reporting any AE suspected to be serious or unexpected as per the regulatory definitions. [Pg.148]

AAML 1994. Management Information Report MIR 3 Computerized Maintenance Management Systemsfor Clinical Engineering. Arlington, VA, Association for the Advancement of Medical Instrumentation. Bauld T.J. 1987. Productivity Standard terminology and definitions. /. Clin. Eng. 12 139. [Pg.809]

Data about derailments exist both in European and national databases, either pubhc or confidential. These belong to a variety of organizations and are presented in a number of formats differing in stiucture, information under which criteria is reported, definition of causes of accidents, etc. The main sources of information for this research included ... [Pg.320]

Consider, for example, the data in Table 4.1 for the mass of a penny. Reporting only the mean is insufficient because it fails to indicate the uncertainty in measuring a penny s mass. Including the standard deviation, or other measure of spread, provides the necessary information about the uncertainty in measuring mass. Nevertheless, the central tendency and spread together do not provide a definitive statement about a penny s true mass. If you are not convinced that this is true, ask yourself how obtaining the mass of an additional penny will change the mean and standard deviation. [Pg.70]

Indicate whether the chemical is manufactured (including imported), processed, or othen/vise used at the facility and the general nature of such activities and uses at the facility during the calendar year. Report activities that take place only at your facility, not activities that take place at other facilities involving your products. You must check all the blocks in this section that apply, tf you are a manufacturer of the chemical, you must check a and/or b, and at least one of c,.ji. e> orf. Refer to the definitions of manufacture," "process," and othenwise use" in the general information section of these instrilctions or section 372.3 of the rule for additional explanations. [Pg.37]

The advantages to using MSDSs for chemical inventories are that MSDSs are publicly available and required by law. There is no extra cost or labour needed to supply them. The limitations to using MSDSs as a source of inventory data are that currently, in the United States, a standardized reporting format is not mandatory. MSDSs are not verified or audited and MSDS information can be incomplete and/or inaccurate. In addition, OSHA s definition of hazard does not include the broader scope of hazard used in green chemistry. Therefore, chemicals that are potential hazards from the green chemistry perspective but are not defined by OSHA as hazards, are not required to be identified on a MSDS. [Pg.278]

The starting point in the single appliance approach is to determine the amount of the target devices that reach China every year. In previous sections data from Zoeteman et al. [1] have been used as a basis for the definition of the global e-waste flow in China. However, for the single appliances approach more specific information on the entering flow of e-waste appliances in China has been found in a report developed by Yang et al. [23]. Therefore, this document has been taken as the basis of the present section. [Pg.327]

Since 1925, The International Commission on Radiation Units and Measurements at Bethesda, Maryland has been publishing reports updating the definitions and units for measurements of various radiation-related quantities. Of these ICRU Reports, special mention may be made of reports no. 19 (1971) [radiation quantities and units], 33 (1980) [radiation quantities and units], 36 (1983) [microdosimetry], 47 (1992) [thermoluminiscent dosimetry], and 51 (1993) [radiation protection dosimetry]. A succinct description of various devices used in dosimetry, such as ionization chambers, chemical and solid-state dosimeters, and personnel (pocket) dosimeters, will be found in Spinks and Woods (1990). In this section, we will only consider some chemical dosimeters in a little detail. For a survey of the field the reader is referred to Kase et at, (1985, 1987), McLaughlin (1982), and to the International Atomic Energy Agency (1977). Of the earlier publications, many useful information can still be gleaned from Hine and Brownell (1956), Holm and Berry (1970), and Shapiro (1972). [Pg.363]

Numerous case reports are available regarding the lethal and nonlethal toxicity of arsine in humans, but definitive exposure concentration or duration data are lacking. Although the case reports are of limited use for quantitative estimates of exposure limits, they do provide qualitative information about the nature of arsine poisoning in humans. Some estimated human toxicity values are available and are summarized in Table 2-3. [Pg.93]

Data on acute exposures of humans to both isomers of dimethylhydrazine are limited to case reports of accidental exposures. Signs and symptoms of exposure include respiratory irritation, pulmonary edema, nausea, vomiting, and neurologic effects. However, definitive exposure data (concentration and duration) were unavailable for these accidents. The limited data in humans suggest that the nonlethal toxic response to acute inhalation of dimethylhydrazine is qualitatively similar to that observed in animals. No information was available regarding lethal responses in humans. In the absence of quantitative data in humans, the use of animal data is considered a credible approach for developing AEGL values. [Pg.175]

The principal observation, which the laboratory scientist should not forget, was that most lifetime assessment of polymers is based on experience from service. Many of the respondents to the survey report examining parts taken from service at the end of life, or those that failed during warranty. Service experience is the principal source of information for the definition of insured lifetimes for polymer components in the construction industry. [Pg.43]

R3 R2 and R2 Ri gauche interactions however, for the same set of substituents, an increase in the steric requirements of either Rj or R3 will influence only one set of vicinal steric interactions (Rj R2 or R3 R2). Some support for these conclusions has been cited (eqs. [6] and [7]). These qualitative arguments may also be relevant to the observed populations of hydrogen- and nonhydrogen-bonded populations of the aldol adducts as well (see Table 1, entries K, L). Unfortunately, little detailed information exists on the solution geometries of these metal chelates. Furthermore, in many studies it is impossible to ascertain whether the aldol condensations between metal enolates and aldehydes were carried out under kinetic or thermodynamic conditions. Consequently, the importance of metal structure and enolate geometry in the definition of product stereochemistry remains ill defined. This is particularly true in the numerous studies reported on the Reformatsky reaction (20) and related variants (21). [Pg.12]

The Reasoner combines evidence from all sources and makes deductions from this evidence. The combination of evidence results in a single "confidence level" for each substructure. These confidence levels designate the degree to which the evidence supports the presence of the substructure in the unknown compound. They range from -100% (substructure definitely absent), through 0% (no information), to +100% (substructure definitely present). The confidence levels are ultimately derived from statistical analysis of representative spectral libraries. Details of the generation and propagation of confidence levels will be described in a separate report.(28)... [Pg.354]

With specially designed reactants, the determination of the product structure can be very informative. Mercury(II)-catalyzed aquations of Co(III) complexes are believed to proceed via a 5-coordinated intermediate (Sec. 4.3.2). The shape of this intermediate is of interest. The Hg +-catalyzed aquation of Co(NH3)4 (NDj)X + in which the ND, and X groups are trans to one another gives substantially rrans-Co(NH3)4(ND3)(H20). This is excellent evidence for a square pyramidal intermediate in the reaction. A trigonal-bipyramidal intermediate would be expected to lead to substantial scrambling of the NDj and NHj groups (Fig. 2.1). The definite but very small amount (2.8 0.4%) of cis product recently reported using NHj instead of NDj attests to the sensitivity of current nmr machines. [Pg.83]

It is difficult to find any definitive information that indicates ozone damage as extensive as that suggested in the mri report. The latter identified cotton, nylon, and rayon as particularly susceptible to ozone. The oxidation of cellulose fibers by ozone was the subject of a study in 1952 that showed that dry cotton was not seriously degraded by ambient ozone. In more recent studies, these conclusions were confirmed. The only information available on fibers other than cotton addressed the effect of ozone on modacrylic, acrylic. Nylon 66, and polyester fabrics.The results indicated minimal effects on these fibers. [Pg.665]


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See also in sourсe #XX -- [ Pg.453 ]




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