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Lead-only particles

The vast majority of the total particle population was due to lead only particles originating from the bullet in the case of the RNL (round nosed lead) ammunition whereas the JHP (jacketed hollow point) ammunition produced a much smaller proportion of lead only particles because the base and side of the bullet are enclosed in the jacket, with the only exposed lead at the nose of the bullet.175 This partly explains the much larger particle population experienced with unjacketed bullets. [Pg.129]

Numerous lead, antimony particles were detected accompanied by copper, zinc particles, iron particles, and lead-only particles. The lead, antimony copper, zinc and lead-only particles, probably originated from the bullets and the iron particles probably originated from the car bodywork. No unique FDR particles or other FDR particle types were detected. [Pg.163]

If we consider a shear flow of a diluted suspension of noninteracting particles, then substitution of spheres by particles of ellipsoidal form leads only to a variation of... [Pg.88]

In Section 2, factors that could lead to particle assembly and secretion into the supernatant were discussed. At this point a deeper analysis of the factors affecting cell infection will be made. Optimisation of the production process should take into account virus-cell interactions, and more specifically viral attachment and internalisation into the cell. The impact of chemical modifications of the medium in baculovirus attachment-internalisation has not been carefully studied. It is widely known for example, that serum increases the infec-tivity of baculovirus. These reviewers have had one case where we were only able to succeed in infecting Sf9 cells adapted to growth in serum-free media [52], with a baculovirus produced by Sf9 cells (not adapted to grow in serum-free media), after adding serum to the culture (authors unpublished observations). However, since serum is not desirable for use in industrial production, its utilisation should be avoided as much as possible. [Pg.193]

Note For convenience the elements lead, antimony, and barium are referred to as the primary elements in FDR particles. Thus, a single primary element particle would be termed lead only, antimony only, or barium only but it could have, and typically does have, other elements present in the particle from the list of permitted additional accompanying elements. [Pg.139]

From casework statistics the unique particles (those containing the combination lead, antimony and barium, and those containing antimony and barium) occur in the ratio 7 3, respectively. Approximate percentages for indicative particles are lead-only 55% lead, antimony 20% lead, barium 8% antimony-only 7% barium, calcium, silicon 5% barium-only 5%. Table 19.3 gives an indication of the levels of the primary elements in each particle type. Table 19.4 gives an indication of the levels of accompanying elements in each particle type and is the basis for note b in Table 19.5, Particle Classification Scheme. [Pg.151]

The majority of the lead-only, antimony-only, and lead, antimony particles that were spherical would be classified as indicative of FDR. However, they were accompanied by particles whose morphology was inconsistent, and only a limited range of particle types were present. No unique FDR particles were detected. [Pg.157]

Criteria pollutants are air pollutants emitted from numerous or diverse stationary or mobile sources for which National Ambient Air Quality Standards have been set to protect human health and public welfare. The original list of criteria pollutants, adopted in 1971, consisted of carbon monoxide, total suspended particulate matter, sulfur dioxide, photochemical oxidants, hydrocarbons, and nitrogen oxides. Lead was added to the list in 1976, ozone replaced photochemical oxidants in 1979, and hydrocarbons were dropped in 1983. Total suspended particulate matter was revised in 1987 to include only particles with an equivalent aerodynamic particle diameter of less than or equal to 10 micrometers (PM10). A separate standard for particles with an equivalent aerodynamic particle diameter of less than or equal to 2.5 micrometers (PM25) was adopted in 1997. [Pg.81]

A key feature of Vajda s work, which differs from the experiments by Heiz and Anderson, is that reactivity is probed at realistic (atmospheric) pressures and temperatures associated with technical catalysts as opposed to UHV conditions. Although in many cases the reaction chemistry under UHV conditions can be extended to ambient conditions, additional processes that may affect cluster stability are only observed under real catalytic conditions. For example, the ripening of clusters, likely to be slow or nonexistent in the molecular beam experiments of Heiz and Anderson, could be significant at atmospheric pressures and lead to particle growth. [Pg.359]

All of the promise of the future technology based on nanometer-scale inorganic solids relies on the production of nanoparticles of controlled size, shape and crystal structure, and further ultimately requires that these nanoparticles be rationally linked to make a working device. Enormous progress has been made in the synthesis of inorganic nanospheres routinely, at present, control over the diameter of nanoparticles leads to particle size distributions that are within 10% of the mean diameter, and frequently within 5%. Only since the mid-1990s and later have there been good synthetic methods to make nanoparticles of controllable size and shape (other than spheres) [3, 20, 22]. [Pg.286]

With the batch reactors used in the fine-chemical industry, the rate of the catalytic reaction is generally not decisively important. The number of catalyst particles per unit volume of the liquid to be treated is one of the experimental factors determining the apparent activity of the catalyst. Because the size of the catalyst particles usually affects the apparent activity of the catalyst only, the size is not critical, provided the particles are no smaller than ca 3 pm. When the size of the particles is below this, separation of the catalyst from the reaction product(s) is difficult, and with still smaller sizes even impossible. The requirement to avoid particles smaller than ca 3 pm imposes fairly severe requirements on the mechanical strength of catalyst particles employed in slurry-phase reactors. When the catalyst particles are liable to attrition, which leads to particles smaller than 3 pm, it is difficult to purify the reaction product(s) completely from the catalyst. Especially with fine-chemicals to be used in the food or pharmaceutical industry, contamination of the reaction product with the catalyst is usually not acceptable. Either mechanically strong catalyst particles must therefore be employed with slurry-phase catalysts or the reactor must be adapted to minimize attrition. With a bubble-column reactor the attrition of suspended catalyst particles is much smaller than with a reactor equipped with a stirrer that vigorously agitates the suspension. [Pg.17]


See other pages where Lead-only particles is mentioned: [Pg.147]    [Pg.148]    [Pg.205]    [Pg.147]    [Pg.148]    [Pg.205]    [Pg.5]    [Pg.260]    [Pg.82]    [Pg.431]    [Pg.262]    [Pg.174]    [Pg.1049]    [Pg.451]    [Pg.51]    [Pg.490]    [Pg.1]    [Pg.702]    [Pg.143]    [Pg.52]    [Pg.64]    [Pg.681]    [Pg.685]    [Pg.210]    [Pg.490]    [Pg.143]    [Pg.213]    [Pg.117]    [Pg.156]    [Pg.132]    [Pg.146]    [Pg.681]    [Pg.13]    [Pg.49]    [Pg.536]    [Pg.367]    [Pg.432]    [Pg.71]    [Pg.158]    [Pg.81]    [Pg.36]   


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Lead particles

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