Bücher: „Effect of spray paints“

1

Haynie, Fred H. Atmospheric acid deposition damage to paints. Research Triangle Park, N.C: U.S. Environmental Protection Agency, Atmospheric Sciences Research Laboratory, 1985.

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2

Piedrahita, O. Prevention of salt-spray injury to fruit and ornamental trees. [Toronto]: Ontario Ministry of Transportation, Research and Development Branch, 1987.

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3

Bottomley, D. M. Aircraft evacuations: The effect of a cabin water spray system upon evacuation rates and behaviour. Cheltenham: Civil Aviation Authority, 1993.

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4

Chong, Calvin. Salt spray injury study: Efficacy of film-forming chemicals for protecting roadside trees. [Toronto]: Environment Ontario, Air Resources Branch, 1989.

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5

DeFrank, Joseph. Risk to nontarget tomatoes from ethephon aerial spray drift. [Honolulu, Hawaii]: HITAHR, College of Tropical Agriculture and Human Resources, University of Hawaii, 1988.

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6

Tonon, Renata V. Spray drying of açai (Euterpe oleracea Mart) juice: Effect of process variables and type of carrier agent on product's quality and stability. New York, N.Y: Nova Science Publishers, 2011.

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7

German, E. R. Effect of spray irrigation of treated wastewater on water quality of the surficial aquifer system, Reedy Creek Improvement District, central Florida. Tallahassee, Fla: U.S. Geological Survey, 1990.

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8

West, Richard J. Ground spray applications of Virtuss, a nuclear polyhedrosis virus, against white-marked tussock moth larvae at Bottom Brook, Newfoundland in 1986. St. John's: Newfoundland Forestry Centre, 1987.

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9

Branch, Canada Dept of Fisheries and Oceans Science. Acetylcholinesterase enzyme activity in fish sampled after the 1985 Newfoundland forest spray program for eastern hemlock looper using fenitrothion. St. John's, Nfld: Science Branch, Dept. of Fisheries and Oceans, 1987.

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10

Miller, Robert A. Characterization and durability testing of plasma-sprayed zirconia-yttria and hafnia-yttria thermal barrier coatings. Part II. Effect of spray parameters on the performance of several hafnia-yttria and zirconia-yttria coatings. Cleveland, Ohio: Lewis Research Center, 1993.

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11

Miller, Robert A. Characterization and durability testing of plasma-sprayed zirconia-yttria and hafnia-yttria thermal barrier coatings. Part 1-Effect of spray parameters on the performance of several lots of partially stabilized zirconia-yttria powder. Cleveland, Ohio: Lewis Research Center, 1993.

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12

Atomizing-gas temperature effect on cryogenic spray dropsize. [Washington, DC: National Aeronautics and Space Administration, 1993.

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13

Atomizing-gas temperature effect on cryogenic spray dropsize. [Washington, DC: National Aeronautics and Space Administration, 1993.

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14

United States. National Aeronautics and Space Administration., Hrsg. Effect of vaporization on cryogenic spray dropsize measurement. [Washington, DC: National Aeronautics and Space Administration, 1992.

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15

Atomizing-gas temperature effect on cryogenic spray dropsize. [Washington, DC: National Aeronautics and Space Administration, 1993.

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16

Atomizing-gas temperature effect on cryogenic spray dropsize. [Washington, DC: National Aeronautics and Space Administration, 1993.

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17

Spray measurements of aerothermodynamic effect on disintegrating liquid jets. [Washington, DC]: National Aeronautics and Space Administration, 1991.

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18

King, Wayne O. Glyphosate activity as affected by spray drop size and leaf coverage. 1988.

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19

Qiao, Yueming Mike. Effect of gravity and surfactant on spray cooling of hot surfaces. 1996.

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20

Characterization of the inlet combustion air in NIST's reference spray combustion facility: Effect of vane angle and Reynolds number. Gaithersburg, MD: U.S. Dept. of Commerce, Technology Administration, National Institute of Standards and Technology, 2000.

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21

Rao, Charagundla S., Presser Gary und National Institute of Standards and Technology (U.S.), Hrsg. Characterization of the inlet combustion air in NIST's reference spray combustion facility: Effect of vane angle and Reynolds number. Gaithersburg, MD: U.S. Dept. of Commerce, Technology Administration, National Institute of Standards and Technology, 2000.

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22

Rao, Charagundla S., Presser Gary und National Institute of Standards and Technology (U.S.), Hrsg. Characterization of the inlet combustion air in NIST's reference spray combustion facility: Effect of vane angle and Reynolds number. Gaithersburg, MD: U.S. Dept. of Commerce, Technology Administration, National Institute of Standards and Technology, 2000.

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23

C, Smith Alex, Hrsg. The Effect of ventilation on the water spray pattern of automatic sprinkler heads. Washington, D.C: U.S. Dept. of the Interior, Bureau of Mines, 1993.

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24

United States. National Aeronautics and Space Administration., Hrsg. Structure of a swirl-stabilized combusting spray. Washington, DC: American Institute of Aeronautics and Astronautics, Inc., 1995.

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25

United States. National Aeronautics and Space Administration., Hrsg. Structure of a swirl-stabilized combusting spray. Washington, DC: American Institute of Aeronautics and Astronautics, Inc., 1995.

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26

Structure of a swirl-stabilized combusting spray. [Washington, DC]: National Aeronautics and Space Administration, 1994.

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27

United States. National Aeronautics and Space Administration., Hrsg. Structure of a swirl-stabilized combusting spray. [Washington, DC]: National Aeronautics and Space Administration, 1994.

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28

Structure of a swirl-stabilized combusting spray. [Washington, DC]: National Aeronautics and Space Administration, 1994.

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29

United States. National Aeronautics and Space Administration., Hrsg. Structure of a swirl-stabilized combusting spray. Washington, DC: American Institute of Aeronautics and Astronautics, Inc., 1995.

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30

United States. National Aeronautics and Space Administration., Hrsg. Structure of a swirl-stabilized combusting spray. Washington, DC: American Institute of Aeronautics and Astronautics, Inc., 1995.

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31

United States. National Aeronautics and Space Administration., Hrsg. Structure of a swirl-stabilized combusting spray. [Washington, DC]: National Aeronautics and Space Administration, 1994.

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32

P, Bennett Kevin, California Environmental Protection Agency. Dept. of Pesticide Regulation. Environmental Monitoring and Pest Management Branch. und California Environmental Protection Agency. Environmental Hazards Assessment Program, Hrsg. Occurrence of aquatic toxicity and dormant-spray pesticide detections in the San Joaquin River Watershed, winter 1996-97. Sacramento, Calif: State of California, Environmental Protection Agency, Dept. of Pesticide Regulation, Environmental Monitoring and Pest Management Branch, 1998.

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33

Guelich, Kurt Robert. Effect of calcium, gibberellic acid, spray adjuvants, and hydrophobic agents on cracking, firmness, and other quality parameters of bing sweet cherries. 1985.

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34

P, Gardner Robert, United States. Office of Aviation Medicine. und Civil Aeromedical Institute, Hrsg. Effect of an airplane cabin water spray system on human thermal behavior: A theoretical study using a 25-node model of thermoregulation. Washington, D.C: U.S. Dept. of Transportation, Federal Aviation Administration, Office of Aviation Medicine, 1998.

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35

Al-Meshal, Mohammed A. S. Physicochemical and tableting properties of crystallised and spray-dried phenylbutazone containing polymeric additives: Effect of polymeric additives (hydroxypropyl methylcellulose and a polyoxyethylene-poloxypropylene glycol) on the crystalline structure, physicochemical properties and tableting behaviour of crystallised and spray-dried phenylbutazone powders. Bradford, 1985.

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36

Zolfaghari, Fatemah. An investigation into drying conditions for liquorice root extracts: The effect of Changes in temperature and pHon the constituents of Iranian liquorice root extracts on spray-and freeze-drying. Bradford, 1986.

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37

Lipworth, Wendy. Pharmaceuticals, Money, and the Health Care Organizational Field. Herausgegeben von Ewan Ferlie, Kathleen Montgomery und Anne Reff Pedersen. Oxford University Press, 2016. http://dx.doi.org/10.1093/oxfordhb/9780198705109.013.24.

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Annotation:

Using an institutional theory framework, this chapter discusses the place of the pharmaceutical industry within the health care organizational field, and the wide-ranging effects the industry has on the other organizations in the field. It then provides a snapshot of the discourse that has emerged about the pharmaceutical industry, and about commercialization and marketization of the health care more generally. This paints a picture of deep ambivalence toward the pharmaceutical industry, both within and between stakeholder groups. The chapter ends with an effort to explain this ambivalence as the effect of competing institutional logics. This, in turn, points to some suggestions as to how the pharmaceutical industry might be better accommodated within the health care organizational field, without losing sight of the need for ongoing critique of industry behavior.

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38

Cameron, Bob. Illumination and Decoration of Flat Surfaces. CSIRO Publishing, 2009. http://dx.doi.org/10.1071/9780643097124.

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It must be appreciated that no building surface is perfectly flat and that the best that can be expected is the appearance of flatness. Unfortunately, this appearance can easily be destroyed by the effect of glancing light, whether natural or artificial. Illumination and Decoration of Flat Surfaces shows the effect of different light sources on a variety of lining materials and paints so that best results can be achieved. Different types of building surfaces are investigated, including set plaster, fibrous plaster, hardboard and gypsum board with gloss and semi-gloss paint applied. This full-colour edition also discusses new building materials such as cement sheet, polystyrene and various composite panels, as well as new building practices, low embodied energy materials and higher energy efficiency of buildings. Illumination and Decoration of Flat Surfaces is a must-have for people involved in the building industry, both commercial and residential.

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39

Trollope, Anthony. Phineas Finn. Herausgegeben von Simon Dentith. Oxford University Press, 2011. http://dx.doi.org/10.1093/owc/9780199581436.001.0001.

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‘To become a member of the British Parliament!… He almost thought that he could die happy.’ Phineas Finn, the handsome Irishman, is equally successful at scaling the political ladder and gaining the affection of influential women. As he makes his precarious way in parliament he discovers how far principles must be sacrificed to the common cause, and how essential money is to political progress. Set during the turbulent passage of the second Reform Act of 1867, the novel paints a vivid picture of the compromises and tactics of daily political life. Loss of independence is felt just as keenly by Lady Laura and Violet Effingham, whose choice of marriage partner will determine their future freedom as much as their happiness. With politics and the personal so closely entwined, Phineas faces an act of conscience that will have a profound effect on his life. The second novel in Trollope’s Palliser series, Phineas Finn’s engaging plot embraces matters as diverse as reform, the position of women, the Irish question, and the conflict between integrity and ambition.

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40

Frew, Anthony. Air pollution. Herausgegeben von Patrick Davey und David Sprigings. Oxford University Press, 2018. http://dx.doi.org/10.1093/med/9780199568741.003.0341.

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Annotation:

Any public debate about air pollution starts with the premise that air pollution cannot be good for you, so we should have less of it. However, it is much more difficult to determine how much is dangerous, and even more difficult to decide how much we are willing to pay for improvements in measured air pollution. Recent UK estimates suggest that fine particulate pollution causes about 6500 deaths per year, although it is not clear how many years of life are lost as a result. Some deaths may just be brought forward by a few days or weeks, while others may be truly premature. Globally, household pollution from cooking fuels may cause up to two million premature deaths per year in the developing world. The hazards of black smoke air pollution have been known since antiquity. The first descriptions of deaths caused by air pollution are those recorded after the eruption of Vesuvius in ad 79. In modern times, the infamous smogs of the early twentieth century in Belgium and London were clearly shown to trigger deaths in people with chronic bronchitis and heart disease. In mechanistic terms, black smoke and sulphur dioxide generated from industrial processes and domestic coal burning cause airway inflammation, exacerbation of chronic bronchitis, and consequent heart failure. Epidemiological analysis has confirmed that the deaths included both those who were likely to have died soon anyway and those who might well have survived for months or years if the pollution event had not occurred. Clean air legislation has dramatically reduced the levels of these traditional pollutants in the West, although these pollutants are still important in China, and smoke from solid cooking fuel continues to take a heavy toll amongst women in less developed parts of the world. New forms of air pollution have emerged, principally due to the increase in motor vehicle traffic since the 1950s. The combination of fine particulates and ground-level ozone causes ‘summer smogs’ which intensify over cities during summer periods of high barometric pressure. In Los Angeles and Mexico City, ozone concentrations commonly reach levels which are associated with adverse respiratory effects in normal and asthmatic subjects. Ozone directly affects the airways, causing reduced inspiratory capacity. This effect is more marked in patients with asthma and is clinically important, since epidemiological studies have found linear associations between ozone concentrations and admission rates for asthma and related respiratory diseases. Ozone induces an acute neutrophilic inflammatory response in both human and animal airways, together with release of chemokines (e.g. interleukin 8 and growth-related oncogene-alpha). Nitrogen oxides have less direct effect on human airways, but they increase the response to allergen challenge in patients with atopic asthma. Nitrogen oxide exposure also increases the risk of becoming ill after exposure to influenza. Alveolar macrophages are less able to inactivate influenza viruses and this leads to an increased probability of infection after experimental exposure to influenza. In the last two decades, major concerns have been raised about the effects of fine particulates. An association between fine particulate levels and cardiovascular and respiratory mortality and morbidity was first reported in 1993 and has since been confirmed in several other countries. Globally, about 90% of airborne particles are formed naturally, from sea spray, dust storms, volcanoes, and burning grass and forests. Human activity accounts for about 10% of aerosols (in terms of mass). This comes from transport, power stations, and various industrial processes. Diesel exhaust is the principal source of fine particulate pollution in Europe, while sea spray is the principal source in California, and agricultural activity is a major contributor in inland areas of the US. Dust storms are important sources in the Sahara, the Middle East, and parts of China. The mechanism of adverse health effects remains unclear but, unlike the case for ozone and nitrogen oxides, there is no safe threshold for the health effects of particulates. Since the 1990s, tax measures aimed at reducing greenhouse gas emissions have led to a rapid rise in the proportion of new cars with diesel engines. In the UK, this rose from 4% in 1990 to one-third of new cars in 2004 while, in France, over half of new vehicles have diesel engines. Diesel exhaust particles may increase the risk of sensitization to airborne allergens and cause airways inflammation both in vitro and in vivo. Extensive epidemiological work has confirmed that there is an association between increased exposure to environmental fine particulates and death from cardiovascular causes. Various mechanisms have been proposed: cardiac rhythm disturbance seems the most likely at present. It has also been proposed that high numbers of ultrafine particles may cause alveolar inflammation which then exacerbates preexisting cardiac and pulmonary disease. In support of this hypothesis, the metal content of ultrafine particles induces oxidative stress when alveolar macrophages are exposed to particles in vitro. While this is a plausible mechanism, in epidemiological studies it is difficult to separate the effects of ultrafine particles from those of other traffic-related pollutants.

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