Industrial Nuisance

Except for siUca and natural abrasives containing free siUca, the abrasive materials used today are classified by NIOSH as nuisance dust materials and have relatively high permissable dust levels (55). The OSHA TWA allowable total dust level for aluminum oxide, siUcon carbide, boron carbide, ceria, and other nuisance dusts is 10 mg/m. SiUca, in contrast, is quite toxic as a respkable dust for cristobaUte [14464-46-1] and tridymite [15468-32-3] the allowable TWA level drops to 0.05 mg/m and the TWA for quartz [14808-60-7] is set at 0.1 mg/m. Any abrasive that contains free siUca in excess of 1% should be treated as a potential health hazard if it is in the form of respkable dust. Dust masks are requked for those exposed to such materials (see Industrial hygene). 

Occupational Safety and Health. OSHA has set no specific limits for sodium and potassium sibcates (88). A pmdent industrial exposure standard could range from the permissible exposure limit (PEL) for inert or nuisance particulates to the PEL for sodium hydroxide, depending on the rate of dissolution and the concentration of airborne material. Material safety data sheets issued by siUcate producers should be consulted for specific handling precautions, recommended personal protective equipment, and other important safety information. 

Short-term inhalation of PVA dust has no known health significance, but can cause discomfort and should be avoided in accordance with industry standards for exposure to nuisance dust. The dust is mildly irritating to the eyes. There are no known dermal effects arising from short-term exposure to either soHd PVA or its aqueous solutions. 

Various sources publish data of permissible vibration levels for employees (usually as a graph of acceleration against frequency). These are designed to avoid injury and cannot be used as a guide to the degree of disturbance caused by vibration. Vibration caused by neighboring industrial premises when received at a residence as vibration (i.e. no noise implications) has been considered a nuisance when it is just perceptible. 

Also, the area under question must be considered. Air-pollution levels on a general industrial estate may be considered acceptable, but those same levels may not be so in a residential area. In one case (Sturgess v. Bridgam (1879)) the judge stated that what would be a nuisance in Belgrave Square would not necessarily be so in Bermondsey . 

This process, according to the manufacturer,54 has been developed in such a way that space requirements are kept to a minimum. A BIOPAQ IC reactor is used as the initial step in the treatment process. The name of this anaerobic reactor is derived from the gas-lift driven internal circulation that is generated within a tall, cylindrical vessel. These reactors have been operational in the paper industry since 1996. The second step in the purification process is a mechanically mixed and aerated tank. The aerating injectors can be cleaned in a simple way without the need to empty the aeration tank. Potential scaling materials are combined into removable fine particles. At the same time, the materials that may cause an odor nuisance are oxidized into odorless components. The process can be completed by a third and a fourth step. The third step focuses on suspended solids recovery and removal. The fourth step is an additional water-softening step with lamella separation and continuous sand filters in order to produce fresh water substitute. The benefits claimed by the manufacturer are as follows54 ... 

For the Industrial setting, the outdoor worker scenario, as mentioned above, represents a worst case. Owing to wind and weather conditions, one assumes that the worker Is exposed to dust only 50% of his approximately 225 workdays. The maximum dust concentration Is the normal nuisance dust TLV (9) of 10 kg/m, breathed by a 70-kg adult at a rate of 12.1 nP" per 8-hour workday (4). A factor of 10 Is Introduced (see equation below) to account for a more robust worker population than the general population. From these assumptions, the calculation Is... 

Copper discharges to the global biosphere are due primarily to human activities, especially mining, smelting, and refining copper and the treatment and recycling of municipal and industrial wastes. Some copper compounds, especially copper sulfate, also contribute to environmental copper burdens because they are widely and intensively used in confined geographic areas to control nuisance species of aquatic plants and invertebrates, diseases of terrestrial crop plants, and ectoparasites of fish and livestock. 

At inlet structures to treatment plants and pumping stations, sewer gases may be emitted to the atmosphere. To avoid odor nuisance, this gas may need treatment. Such methods have been widely used in the mining and coal gas industries to remove hydrogen sulfide from gases (Herrygers et al 2000). 

The various effects of the Toxic Substances Control Act (TSCA) on the metalworking fluids Industry is presented, with emphasis placed on nitrosamine contamination of the fluids. A review of the literature on the effects of various metalworking fluid additives on nitrosamine formation is also presented to aid the industry in dealing with the nuisance of nitrosamine contamination. It is concluded that with increased awareness of nitrosamine contamination as a result of the implementation of TSCA and careful consideration of the factors described in this paper, it may be possible to design and control a nitrosamine-free metalworking fluid. 

So the greatest challenges are in the mobile sector, but the pressure to act is much greater here as well, owing to oil scarcity, pollutants from vehicles, noise nuisance, etc. Compared with stationary applications, the alternative technologies in the mobile sector are also much poorer. This is why fuel-cell vehicles remain a possibility, despite the enormous sectoral changes that accompany this alternative. The question is when will they achieve market penetration One of the main obstacles that will have to be overcome is the attendant position of both the automobile industry and the infrastructure industry concerning the investment. Which one is prepared to... 

While breaking of the carbon-to-phosphorus bond is a nuisance in catalysis with organometallic complexes, the breaking of carbon-to-nitrogen and -to-sulfur bonds is a desired reaction in the oil industry. Hydrodenitrification (HDN) and hydrodesulfurisation (HDS) are carried out on a large scale in order to remove nitrogen and sulfur from the fuel feedstocks. 

The aim of dispersion models is the prediction of atmospheric dilution of pollutants in order to prevent or avoid nuisance. Established dispersion models, designed for the large scale of industrial air pollution have to be modified to the small scale of agricultural pollutions. An experimental setup is described to measure atmospheric dilution of tracer gas under agricultural conditions. The experimental results deliver the data base to identify the parameters of the models, For undisturbed airflow modified Gaussian models are applicable. For the consideration of obstacles more sophisticated models are necessary,... 

In the assessment of odour production and nuisance from industrial processes the techniques are by now reasonably well established, and their accuracy and consistency are in principle known. There are major differences however between say a rendering plant on the one hand and a sewage treatment works on the other. One difference is psychological to many people an odour problem is necessarily concomitant to the existence of a sewage works. There have been instances of a well-operated sewage works built next to a tannery, where the sewage works has been almost universally blamed by irate local residents for a problem to which it has contributed in only a minor way. To this extent, for some people the only way to convince them that there is no odour nuisance would be to shut the works completely, and even then it is known that complaints can continue for some time afterwards. 

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