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Factors, environmental

Environmental factors such as temperature, light, and humidity also influence the toxicity of pollutants. [Pg.160]

Temperature also affects the response of vegetation to air pollution. Generally, plant sensitivity to oxidants increases with increasing temperature up to 30°C. Soybeans are more sensitive to ozone when grown at 28°C than at 20°C, regardless of exposure temperature or ozone doses (Dunning et al. 1974). The response of pinto bean to a 20 and 28°C growth temperature was found to [Pg.160]

The environmental factors that are considered by the methodology to affect the performance of new pavement are the subgrade swelling and frost heave. Either of these factors, or both, can lead to a significant loss of serviceability or ride quality during the analysis period. [Pg.547]

This loss is expressed in terms of the PSI index. The swelling loss, APSIjw, or the frost heave loss, APSIpn, can be quantified using relevant serviceability models and calculation procedures given in the methodology (AASHTO 1993). [Pg.547]

However, there is little scientific evidence that support the claims of environmental damage caused by plastic bags and such issues need to be settled through the judicial system, where scientific evidence supporting such claims would be necessary. A report by the British Environmental Agency is especially important for the outcome of such cases, as this report states that a single-use polyethylene bag has a lower carbon footprint than alternative paper or reusable bags [28]. [Pg.42]

Many of the metabolic changes described above are changes in energy metabolism, and energy metabolism in uninjured animals is in turn influenced by environmental conditions, in particular, temperature, humidity, and wind velocity. Furthermore, environmental conditions may themselves act as noxious stimuli as in sunburn or frostbite. We have already mentioned some examples of the interaction of environment, specifically environmental temperature, in the body s response to injury, and a more detailed account follows. [Pg.26]

In the U.K. in 1992, 3.5 million tonnes of sulphur dioxide were emitted into the atmosphere. Combustion of fossil fuels in electricity generating power stations produced 69% of the emitted sulphur dioxide. Much of this sulphur dioxide is oxidized in the atmosphere, e.g. by ozone, eventually to produce sulphuric acid or sulphates. [Pg.236]

Sulphuric acid is one of the main constituents of acid rain. Concern over the effects on the environment of acid rain is shown by action taken in the European Community (EC). The EC Large Combustion Plants Directive 88/609 takes 1980 emissions as a baseline and requires reductions in emissions from existing plants of capacity greater than 50 megawatts thermal of 20% by the end of 1993, 40% by 1998 and 60% by 2003  [Pg.236]

This focuses the spotlight on the sulphur content of fuels since the combustion of fuels which contain sulphur in any form will result in the formation of the stable combustion product which is sulphur dioxide. [Pg.236]

The use of FGD and other methods of control of emissions of sulphur dioxide add to the cost of generating electricity especially from coal and this helps to explain the switch-over to the use of natural gas, particularly for the generation of electricity. In the U.K. from 1960 to 1993 the proportion of electricity supplied by natural gas increased from 0.6% to 9.9%.  [Pg.237]

Temperature and moisture level affect the stability of PLA [49-51]. The effects of these two parameters on PLA barrier properties are discussed separately below. [Pg.161]

Both Auras et al. [54] and Shogren [37] observed a decrease in the water vapor permeability of PLA with increasing temperature. Auras et al. [54] also smdied the effect of the temperature on the permeation of O2 in PLA. In this study, PLA films containing different L-lactide content (94% and 98%) were exposed to 5, 23, and 40°C PET films were used for comparison. A significant increase in the value of P for O2 with increasing temperature was observed for both types of PLA. The values of P for O2 increased by approximately 10% with each temperature step PET films showed a similar behavior. Lehermeier et al. [12] earlier reported that O2 permeability in 100% linear PLA with an l d ratio of 96 4 was temperature dependent (y = 276.43e , where y and x are permeation and 1/T, respectively). [Pg.161]

2 Moisture Moisture sorption is a factor that can limit the use of polymers. Water absorbed from the atmosphere can swell, plasticize, or react with the polymer chains. Changes in the interactions between atoms within a polymer [Pg.161]

FIGURE 123 Oxygen diffusion coefficient of PLA film containing 98% L-lactide as a function of water activity (reproduced from Ref. 54 with permission from Wiley-VCH Verlag GmbH Co. KGaA). [Pg.161]

Bracken stands could be expected to provide cover to support large populations of herbivorous mammals that might, by selective grazing behavior, be responsible for a paucity of individual plants within the stands. To estimate the number of mammals, live traps were set in open grasslands, on the edge of the bracken stands, and within the stands. More animals were captured within the bracken, and thus a series of experiments were performed to determine if animals were having an effect on plants. [Pg.186]

The above experiments, analyses, and bioassays give an idea of the many factors that must be excluded to establish a hypothesis of allelopathy. In the second part of their study, Gleissman and Muller proceeded to make the case. [Pg.186]

A series of eight experiments were performed that established the source of toxic compounds in the dominant plant (bracken) differential susceptibility of associated species to toxic effects the probable route of the toxins into the soil toxicity in the natural and toxin-modified soils and reversal of the phenomenon by removal of the toxic source. A brief summary follows. [Pg.186]

To ascertain whether or not osmotic effects of extracts were responsible for the inhibitory activity, manitol solutions were made up to osmotic concentrations slightly in excess of frond extracts. Osmotic concentrations were shown to be in part responsible for some of the bioassay inhibition observed, but a significant component was due to organic inhibition. [Pg.187]

To test for differential effects on different species, extracts of fronds collected before rains were made by soaking them for 2 h in distilled water. Variation in effects on herb species were observed (1) the species most abundant within bracken stands was the most tolerant, (2) the rodent-excluded species was somewhat tolerant, and (3) several species least frequently encountered inside bracken stands were the most susceptible. [Pg.187]

It is not uncommon that bacteria do not develop weU even when aU the mentioned parameters are optimal since the composition of wine is very complex. From a nutritional point of view, essential elements such as carbon, nitrogen, vitamins, and metal sources are appropriately represented in the wine. Pentoses and hexoses present after AF, in concentrations of about sevraal hundred mg/1, are sufficient to produce the necessary biomass to carry out the MLF In addition, the bacteria glycosidases and peptidases hydrolyze numerous glycosylated and peptide molecules into sugars and amino acids, which they then use. By contrast, grape molecules, such as some phenohc compounds, may be toxic but they may have positive effects as has also been demonstrated (Theobald et al. 2008 Cairpos et al. 2009). [Pg.237]

The phase which is stable at the lowest temperatures is generally that with the greatest binding energy, because the entropy term rS is small. However, as the temperature increases, another phase with higher entropy due to uncertainty of positional or electronic [Pg.161]

Thus the influence of the entropy term in the expression for the free energy of a phase can be clearly understood with regard to positional and spin disorder, as well as melting, but understanding the factors that contribute to the enthalpy is a much more difficult part of accounting for phase and structural stability. [Pg.163]

Pressure alters the relative dispositions of the free-energy-composition surfaces in an analogous manner to temperature, so that the type of phase changes occurring under the influence of pressure are similar to those that take place under the influence of temperature (Volume 5, Chapter 9). [Pg.163]


Unprotected steel corrodes at a rate which is generally assumed to be 0.1 to 0.2mm per annum. Factors that influence the actual rate of corrosion include the maintenance program applied by the owner - particularly preservation of protective coatings, efficiency of cathodic protection systems in ballast tanks, corrosive properties of the cargo carried and environmental factors such as temperature and humidity. Under extreme conditions it has been known for the annual rate of corrosion on unprotected steel exposed on both surfaces to approach 1mm. [Pg.1048]

Table VIII. The compounds selected are as typical as possible, but it must be remembered that there are many environmental factors that produce changes in the location of the absorption bands. These displacements are usually of the order of a few mp., but in some cases they are so great as to move the absorption band into a completely different region of the spectrum. Table VIII. The compounds selected are as typical as possible, but it must be remembered that there are many environmental factors that produce changes in the location of the absorption bands. These displacements are usually of the order of a few mp., but in some cases they are so great as to move the absorption band into a completely different region of the spectrum.
In many cases an optimized method may produce excellent results in the laboratory developing the method, but poor results in other laboratories. This is not surprising since a method is often optimized by a single analyst under an ideal set of conditions, in which the sources of reagents, equipment, and instrumentation remain the same for each trial. The procedure might also be influenced by environmental factors, such as the temperature or relative humidity in the laboratory, whose levels are not specified in the procedure and which may differ between laboratories. Finally, when optimizing a method the analyst usually takes particular care to perform the analysis in exactly the same way during every trial. [Pg.684]

The fully extended molecular length is not representative of the spatial extension that a molecule actually displays. The latter is sensitive to environmental factors, however, so the extended length is convenient for our present purposes to provide an idea of the spatial size of polymer molecules. [Pg.5]

Environmental factors such as temperature, humidity, moisture, and Electromagnetic Interference (EMI) or Radio Frequency Interference (RFI) can affect performance if insufficient care is exercised in designing the scale... [Pg.327]

Temperature and Humidity. Temperature is probably the easiest environmental factor to control. The main concern is that the temperature remains constant to prevent the thermal expansions and contractions that are particularly dangerous to composite objects. Another factor regarding temperature is the inverse relation to relative humidity under conditions of constant absolute humidity, such as exist in closed areas. High extremes in temperature are especially undesirable, as they increase reaction rates. Areas in which objects are exhibited and stored must be accessible thus a reasonable temperature setting is generally recommended to be about 21°C. [Pg.428]

Aflatoxki B (1) is of greatest occurrence ki nature, followed by G, B2, and G2. Water content of medium, temperature, pH, and tight are among those environmental factors that affect aflatoxki production. [Pg.480]

The specific design most appropriate for biomass, waste combustion, and energy recovery depends on the kiads, amounts, and characteristics of the feed the ultimate energy form desired, eg, heat, steam, electric the relationship of the system to other units ia the plant, iadependent or iategrated whether recycling or co-combustion is practiced the disposal method for residues and environmental factors. [Pg.21]

Climate and Environmental Factors. The biomass species selected for energy appHcations and the climate must be compatible to faciUtate operation of fuel farms. The three primary climatic parameters that have the most influence on the productivity of an iadigenous or transplanted species are iasolation, rainfall, and temperature. Natural fluctuations ia these factors remove them from human control, but the information compiled over the years ia meteorological records and from agricultural practice suppHes a valuable data bank from which to develop biomass energy appHcations. Ambient carbon dioxide concentration and the availabiHty of nutrients are also important factors ia biomass production. [Pg.30]

Environmental Factors. The control, recovery, and disposal of mercury-bearing waste products are as important to the mercurials industry as the manufacturing process. The difficulties involved in removing mercury from waste-product streams and the problems of recovery or disposal have resulted in a substantial reduction in the number of manufacturers of mercury compounds as well as in the variety of mercury compounds being manufactured. Moreover, the manufacturing process used for a mercury compound may not necessarily be the most efficient or economical. Rather, the choice may depend on the nature of the by-products, the toxic hazard of the process, and the ease of recovery of the mercury from the waste-product stream. [Pg.116]

Health, Safety, and Environmental Factors. Sulfur dioxide has only a moderate acute toxicity (183). The lowest pubHshed human lethal concentration is 1000 ppm for 10 months. The lowest pubHshed human toxic concentration by inhalation is 3 ppm for 5 days or 12 ppm for 1 hour. The lowest pubHshed human lethal concentration is 3000 ppm for 5 months. In solution (as sulfurous acid), the lowest pubHshed toxic dose is 500 flg/kg causing gastrointestinal disturbances. Considerable data is available by other modes of exposure and to other species NIOSH standards are a time-weighted average of 2 ppm and a short-term exposure limit of 5 ppm (183). [Pg.147]

The final composition of stream water is the product of the weathering reactions and related processes outlined above. However, the chemical processes are influenced and controlled by an intricate combination of environmental factors that are characteristic for each drainage system. Therefore, the composition of the bedrock in an area and the residual material left at the surface as soil and subsoil exert a strong influence on the chemical composition of mnoff from the area. The reactions of water with this material are the ultimate geological control and are the source of soluble weathering products. [Pg.198]

The primary appHcation for barrier polymers is food and beverage packaging. Barrier polymers protect food from environmental factors that could compromise both taste and shelf life. They also help retain desirable flavors and aroma. Barrier polymers are also used for packaging medical products, agricultural products, cosmetics, and electronic components and in moldings, pipe, and tubing. [Pg.501]


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