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71.
R.H. Kummler B. Cho G. Roginski R. Sinha A. Greenberg 《Journal of the Air & Waste Management Association (1995)》2013,63(7):720-723
The RAM model provided by the U.S. EPA has been applied to the metropolitan Detroit area for SO2 concentrations and is compared to concentrations predicted by a numerical model and to field data obtained by the 14 station air sampling network maintained by the Wayne County Air Pollution Control Division. Great care was taken to develop the emission inventory. Based upon examination of the temporal and spatial correspondence of the respective model predictions and observed concentrations, the correlation coefficients for the 24-hour averaged data, the correlation coefficients for over 700 3-hour averaged observations, and the cumulative frequency distributions of the model output and observations, it is concluded that the numerical model provides a superior predictive tool to evaluate cause and effect relations, but that the RAM model, at far lower cost, predicts the correct magnitude of the worst events. Hence RAM might well be used in the Detroit Area for statistically based regulatory decisions. 相似文献
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Major variations in lipid composition exist within the fatty melon tissue of the Atlantic bottlenosed dolphin Tursiops truncatus. Topographical lipid analyses indicate a central inner melon core surrounded by distinctive outer melon, under melon, and blubber tissues. Acoustical considerations suggest that this melon-lipid topography may aid in collimation of the ultrasonic pulses used by the dolphin for echolocation. 相似文献
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Matulich Scott C. Mittelhammer Ron C. Greenberg Joshua A. 《Journal of Environmental Economics and Management》1995,28(3)
Commercial fisheries industry structure often suggests exvessel price formation occurs in the context of a competitive harvesting sector and an oligopsonistic processing sector. However, industry conduct leading to a determination of exvessel price can be notably at odds with this inference. This paper presents empirical evidence that the conduct of at least one such fishery, the Alaska king crab industry, may emulate bilateral monopoly. Exvessel price determination is consistent with an implicit formula price contract in which fishers behave as monopolists through bargaining associations, while processors behave as countervailing monopsonists, even in the absence of explicit collusion. Both sectors appear to behave in a manner consistent with joint expected profit maximization, with profit shares apportioned via the implicit formula price contract. This price formation process simplifies empirical analysis of the bilateral monopoly conduct by avoiding complicated game theoretic/bargaining models. 相似文献
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J. L. Cheney J. Chehaske S. Greenberg 《Journal of the Air & Waste Management Association (1995)》2013,63(6):588-591
Two techniques were used to measure primary sulfuric acid and sulfate emissions from two small package boilers burning nominal 0.3% sulfur fuels, one with 11 ppm vanadium and one with 4.3 ppm vanadium. Several of the particulate fractions from both sampling methods were analyzed for sulfuric acid using a selective solvent determination (SSD) procedure. The sulfuric acid present on the filters accounted for a minimum of 11% of the particulate emission rates. The observed conversion of sulfur dioxide to primary sulfate or primary sulfuric acid is reduced considerably when sulfate ion detected in an isopropanol impinger is attributed to sulfur dioxide conversion in the solution rather than to primary sulfuric acid. An additional reduction occurs when the method of calculating the conversion is based solely on sulfur weight. This study gives a fourfold reduction in percent conversion when compared to a similar study conducted earlier. Suggestions are offered for improvements in measurement methods and for a consistent technique for calculating sulfur conversion. 相似文献
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Because management is driven largely by financial concerns, determining the cost of environmental quality is a critical step in developing an environmental TQM program for which management will actively demonstrate commitment and support. Costs of environmental quality can be grouped into three categories: failure, prevention, and appraisal. The total cost of environmental quality can be used as a benchmark to monitor the level of environmental quality and to justify the redirection of resources. 相似文献
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