Development and characterization of an exposure generation system to investigate the health effects of particles from fresh and aged traffic emissions

2012 ◽  
Vol 6 (2) ◽  
pp. 419-429 ◽  
Author(s):  
Vasileios Papapostolou ◽  
Joy E. Lawrence ◽  
Stephen T. Ferguson ◽  
Jack M. Wolfson ◽  
Edgar A. Diaz ◽  
...  
2016 ◽  
Vol 851 ◽  
pp. 244-248
Author(s):  
Ya Fei Zhang ◽  
Zhi Yuan Yao ◽  
Bi Cheng Wu

The glass nanopore produced by the physical method has better physical characteristics, higher strength, stronger stability, longer life and other significant features compared with the chemical method. The purpose of this paper is to study DNA sequencing (973 project) to provide experimental basis for preparation of glass capillary 5nm 3D nanochannel In this paper, we design a set of glass capillary tension system which is controlled by laser heating and linear ultrasonic motor and produced successfully the device for the preparation of nanopore below 50 nm. In addition, the use of micro droplet generation system has carried out preliminary characterization of nanopore drawn devices. Seen from the characterization, the nanopore device fabricated can indeed produce a through-hole.


2002 ◽  
Author(s):  
◽  
Kumindra Devrajh Ramsunder

Fusarium species produce toxic mycotoxins that are known to exert adverse health effects in humans and animals. No attempts have been made to establish mycotoxin-producing capabilities of isolates of Fusarium species from bananas exhibiting symptoms of crown rot. Crown rot is one of the most serious post harvest problems in banana and the disease is caused by different fungal species, principally Fusarium species. Banana, which is of great economic significance in growing countries (i.e. Costa Rica, Cameroon, Ecuador) is seriously affected by crown rot and is a major cause of fruit loss


Author(s):  
Morton Lippmann ◽  
Richard B. Schlesinger

This chapter describes the extensive scientific terminology needed to describe the various classes of chemical contaminants as they occur in environmental media (air, water, soil, etc.) and the structural aspects and dynamic mass and energy transfers within and among the atmosphere, hydrosphere, lithosphere, and biosphere. It also introduces: the characteristics of occupational environments; health effects attributable to occupational and environmental exposures; dose response relationships in populations; and how they are affected by anthropogenic (human activity caused) inputs and disruptions.


1999 ◽  
Vol 107 ◽  
pp. 639 ◽  
Author(s):  
Abraham Brouwer ◽  
Matthew P. Longnecker ◽  
Linda S. Birnbaum ◽  
Jim Cogliano ◽  
Paul Kostyniak ◽  
...  
Keyword(s):  
Low Dose ◽  

Author(s):  
Husein Adam Nakhawa ◽  
S.S. Thipse

Today, in the automotive emissions ultrafine and nanoparticles emissions are of very high importance because of their vulnerable effects to environment and human health causing respiratory problems like bronchitis, asthma, cardiovascular disease, and various types of cancers spreading in all age groups in the society leading to premature death [1]. Therefore, characterization of ultrafine and nanoparticles in terms of their size distribution and number concentration for the automobiles operating on various fuels and traffic conditions is of great importance in understanding the phenomenon and the adverse effects. Various research studies carried out at international level show the adverse health effects due to ultrafine particles from C.I. and S.I. engines and hence, there is definite need to examine for the particulate mass, size and number concentration considering social needs [2].Even after very stringent emission norms which were tightened over the years and today down to more than 97% from it’s baseline norms couldn’t show proportionate improvement in the ambient air quality. Climate effects inevitably lead to health effects leading to premature death due to ultrafine particles from the automotive exhaust [1]. Recent WHO report confirmed the vulnerable effect of diesel particles in terms of carcinogenicity and severe health effects of diesel fuel used in automotive sector [3]. European regulations has taken the steps to address this concern by introducing new norms for particle number and PM2.5 as 6 x 1011 and 4.5 mg/km respectively [4]. Investigations carried out on GDI vehicles show substantial ultrafine and nanosize particle emissions and by number, nearly all of the particles emitted by a diesel engine are nanoparticles which are also true for gasoline engines [5]. Like gasoline engines other S.I. engines, even though they look very clean as there is no visible smoke and large particles emitted in their exhaust, it is necessary to investigate them. Very limited research work has been carried out particularly, on CNG engines/ vehicles for their PM and PN levels at national and international level. Characterization of ultrafine and nanoparticles in terms of their size distribution and number concentration for the automobiles operating on various fuels and traffic conditions is of great importance in understanding the phenomenon and their significance.In this context and understanding the social need this research work was carried out to investigate experimentally the significance of CNG and diesel passenger car for it’s contribution to particle number (PN) and PM2.5. This work includes comparative investigation of CNG and diesel passenger cars to characterize the ultrafine and nanoparticle emissions on modified Indian driving cycle. CNG passenger car show large peak of PN emissions during cold starting phase at the beginning of the test cycle which is almost twice that of diesel vehicle but it settles down to lower level as the vehicle gets warmed up. During acceleration and cruising operation on extra urban cycle under heavy load the PN emissions from CNG car are higher in magnitude. For diesel car, urban part of cycle contributes approximately 53% compared to 25% for CNG vehicle and rest 47% and 75% is contributed by extra urban part towards PN emissions.This research paper covers experimental Investigation carried out to compare the behavior of diesel and CNG passenger cars to characterize the particle emissions and to identify the significance of different operating phases viz. idling, acceleration, deceleration and cruising for their contributions to Particle number and size distribution pattern on urban and on extra urban part of the driving cycle.


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