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1.
Light absorption by soot or nigrosin dye aerosol particles were measured in the laboratory using a particle soot absorption photometer (PSAP) and a photo-acoustic spectrometer (PAS) to assess the influence of non-absorbing organic aerosol (OA) on the PSAP measurements. For the PSAP, particle light absorption is measured after collection on a filter, whereas for the PAS light absorption is measured while the particles remain suspended in the gas phase. OA was generated from the reaction of α -pinene with ozone. It was observed that the presence of this OA in an external mixture of absorbing aerosol and OA can cause an increase in the light absorption measured by the PSAP, relative to that measured by the PAS, by more than a factor of two. This enhancement in the PSAP absorption was found to increase as the amount of OA increased relative to the absorbing compound. Additionally, experiments where absorbing aerosol was deposited on a PSAP filter prior to addition of OA demonstrated that the non-absorbing OA can actually appear as if it were absorbing, with measured single scattering albedo values as low as 0.92. These results indicate that filter-based measurement techniques may significantly overestimate light absorption by aerosols in the atmosphere under conditions where the organic loading is large, with consequent implications for understanding and calculating the Earth's radiation budget. These laboratory experiments aid in the interpretation of results from a recent field study, discussed in a companion article (Lack et al. 2008 Lack, D. A., Cappa, C. D., Baynard, T., Massoli, P., Covert, D. S., Sierau, B., Bates, T. S., Quinn, P. K., Lovejoy, E. R. and Ravishankara, A. R. 2008. Bias in Filter-Based Aerosol Absorption Measurements Due to Organic Aerosol Loading: Evidence from Ambient Measurements. Aerosol Sci. and Technol., 42: 10331041. [Taylor & Francis Online], [Web of Science ®] [Google Scholar]).  相似文献   

2.

The surface discharge on a dielectric barrier induced by dc pulses was successfully utilized as a stable bipolar ion source for neutralizing submicron aerosol particles where the concentration of positive and negative ions could be adjusted independently (a surface-discharge microplasma aerosol charger: SMAC; Kwon et al., 2005 Kwon, S. B., Sakurai, H., Seto, T. and Kim, Y. J. 2005. Charge Neutralization of Submicron Aerosols Using Surface-Discharge Microplasma. J. Aerosol Sci., in press[CSA] [Google Scholar]). The aim of this study was to determine the charge distribution obtained by the SMAC, which has been qualitatively presented in our previous study, and to investigate the effect of unequal bipolar ion concentration on the charge distribution. For this purpose, we performed quantitative analysis of the charge distribution of monodisperse particles in the size range of 30–200 nm acquired by the SMAC and compared the charge distributions with calculated charge fractions obtained from the diffusion charging theory. The ion parameters were calculated by measuring the ion mobility of positive and negative ions and they were used to obtain the analytic solutions of charge distribution. The charge distributions obtained by the equal or unequal concentration of bipolar ions adjusted by the SMAC showed general agreement with the diffusion charging theory.  相似文献   

3.
Simulations of the sky dome color shifts of a cloudless sky have been performed, assuming three urban-industrial tropospheric aerosol cases. Each of these aerosols is represented by the bimodal lognormal volume distribution (Dubovik et al. 2002 Dubovik, O., Holben, B., Eck, T. F., Smirnov, A., Kaufman, Y. J., King, M. D., Tanré, D. and Slutsker, I. 2002. Variability of Absorption and Optical Properties of Key Aerosol Types Observed in Worldwide Locations. J. Atm. Sci., 59: 590608. [Crossref], [Web of Science ®] [Google Scholar]). A total of ten parameters are used to control the aerosol characteristics. These ten parameters are perturbed and the resulting sky color shifts are estimated. All simulations have been performed relative to the reference cases that represent the time-averaged state of each aerosol case. We have simulated the sensitivity of the theoretical CIE (Commission Internationale de l′ Eclairage) standard human observer to discriminate sky color changes, due to changes of the aerosol control parameters. A Digital color Camera Model (DCM) has also been incorporated in the simulation scheme. The DCM simulates the performance of a camera-colorimeter created specifically to measure sky color. The DCM has been used to investigate whether a color digital camera can replicate the behavior of the CIE standard observer, with respect to sky color shifts. The standard observer is most sensitive to perturbations of the parameters of the aerosol fine mode, which are particles with diameters less than 0.6 μ m. However his sensitivity is highly variable, depending on the parameter varied, on the aerosol case and on the direction of the observation. The DCM was in excellent agreement with the behavior of the CIE standard observer. The camera simulated sky color measurement accuracy was high. The results show that the camera sensitivity in discriminating color differences is much better than that of the observer.  相似文献   

4.
Abstract

We have already fabricated honeycomb-patterned cellulosic films with cellulose I and II polymorphisms as a basal framework in order to create an artificial woody cell wall.[ 1 Nemoto, J., Uraki, Y., Kishimoto, T., Sano, Y., Funada, R., Obata, N., Yabu, H., Tanaka, M. and Shimomura, M. 2005. Production of mesocopically patterned cellulose film. Bioresour. Technol., 96: 19551958.  [Google Scholar] , 2 Uraki, Y., Nemoto, J., Otsuka, H., Tamai, Y., Sugiyama, J., Kishimoto, T., Ubukata, M., Yabu, H., Tanaka, M. and Shimomura, M. 2007. Honeycomb-like architecture produced by living bacteria, Gluconacetobacter xylinus. Carbohydr. Polym., 69: 16. [Crossref], [Web of Science ®] [Google Scholar] ] The adsorption of an isolated lignin, acetic acid lignin (AL), was attempted onto the honeycomb films not only to develop materials further mimicking the cell wall but also to elucidate the mechanical effect of isolated lignin on the tensile strength of the cellulosic architecture. The tensile strengths of honeycomb-patterned cellulosic films were improved by the AL adsorption. Although the cellulosic films without lignin weakened under high moisture content conditions as compared with those under the low content conditions, the lignin-adsorbed cellulosic film maintained significant tensile strength even under the high content conditions. This result suggests that lignin contributes to reinforce the mechanical strength of cellulose framework, in particular high moisture conditions.  相似文献   

5.
Experimental measurements of bipolar diffusion charging efficiency over the range of 15–400 nm are compared for oil droplets, flame generated soot aggregates, and diesel engine exhaust particulate matter to explore possible effects of particle morphology. Charging efficiency is recorded using a tandem differential mobility analyzer (DMA) approach; the first DMA selects a monodisperse aerosol and the second compares the flux of these particles through a neutralizer versus an identical blank housing. Electrostatic precipitation of mobility selected soot particles onto TEM grids provides comparative data on changes in soot particle morphology with mobility diameter. The measurements yield soot charging efficiencies that slightly, but systematically, differ from those of equal mobility diameter oil droplets. Single positive charging of soot climbs to ~ 10% higher than oil droplets at 50 nm and then decreases to 15% lower by 400 nm as the soot develops a progressively more fractal-like structure. Negative charging exhibits the same pattern, except the variations are +15% and –10%, respectively. These trends, as well as those for double and triple charging, fall intermediate between Fuchs predictions and the model of Wen et al. (1984a) Wen, H. Y., Reischl, G. P. and Kasper, G. 1984a. Bipolar Diffusion Charging of Fibrous Aerosol Particles—I. Charging Theory. J. Aerosol Sci., 15: 89101. [Crossref], [Web of Science ®] [Google Scholar] for charging of fibrous particles.  相似文献   

6.

Pulsed airflow cued by the fluorescence spectrum of a particular aerosol can be used to distinguish and deflect particles of biological origin out of an aerosol stream, permitting concentration of these particles for subsequent analysis (Pan et al. 2004 Pan, Y. L., Boutou, V., Bottiger, J. R., Zhang, S. S., Wolf, J. P. and Chang, R. K. 2004. A Puff of Air Sorts Bioaerosols for Pathogen Identification. Aerosol Sci. Technol., 38: 598602. [CROSSREF][CSA][Taylor & Francis Online], [Web of Science ®] [Google Scholar]). However, these high velocity pulses of air have an inherent tendency to scatter particles, confounding efforts to concentrate these deflected particles for analysis. The ability to concentrate large numbers of biological particles into a small area on a collection substrate is particularly important for more species-specific techniques such as Raman and FTIR (Fourier Transform Infra-Red) spectroscopy, which require long integration times due to their weak signal strength. In the present work, a simple method is developed for deflecting and localizing particles after classification by a pulsed airflow. The concept is both modeled and experimentally tested. A specially designed funnel is used to localize the scattered particles onto an area of substrate as small as 1 mm in diameter. Computational fluid dynamics simulations were performed to investigate the interaction of the pulsed airflow with the deflected particles and the localizing funnel, in order to gain insight into design parameters and operating conditions that affect the efficiency of this technique. The results show that the combination of pulsed airflow with a localizing funnel effectively deflects and localizes the concentrated bioaerosol onto a small area of substrate or an opening of a microfluidic cell.  相似文献   

7.
The fjord-region PAH dibenzo[a,l]pyrene (DBP) is considerably more carcinogenic than the bay-region benzo[a]pyrene (BP). This fact can be ascribed to differences in DNA binding efficiency of their ultimate carcinogenic diol epoxide (DEs) intermediates, differences in structural features of the DNA adducts, and differences in DNA adduct recognition and the subsequent lesion removal by nucleotide excision repair (NER). In order to further substantiate previous findings in cell-free human systems (1 Buterin, T., Hess, M. T., Luneva, N., Geacintov, N. E., Amin, S., Kroth, H., Seidel, A. and Naegeli, H. 2000. Unrepaired Fjord Region Polycyclic Aromatic Hydrocarbon-DNA Adducts in Ras Codon 61 Mutational Hot Spots. Cancer Research, 60: 18491856.  [Google Scholar]), cultured cells (2 Luch, A., Kudla, K., Seidel, A., Doehmer, J., Greim, H. and Baird, W. M. 1999. The Level of DNA Modification by (+)-syn-(11S,12R,13S,14R)- and (?)-anti-(11R,12S,13S, 14R)-Dihydrodiol Epoxides of Dibenzo[a,l]pyrene Determined the Effect on the Proteins p53 and p21WAF1 in the Human Mammary Carcinoma Cell Line MCF-7. Carcinogenesis, 20: 859865.  [Google Scholar]), and in rodents (3 Jankowiak, R., Ariese, F., Hewer, A., Luch, A., Zamzow, D., Hughes, N. C., Phillips, D., Seidel, A., Platt, K. L., Oesch, F. and Small, G. J. 1998. Structure, Conformations, and Repair of DNA Adducts from Dibenzo[a,l]pyrene: 32P-Postlabeling and Fluorescence Studies. Chemical Research in Toxicology, 11: 674685.  [Google Scholar]) we have studied DNA adduct formation of anti-DE of DBP [(±)-anti-DBPDE], in A549 human epithelial lung carcinoma cells and monitored the levels of adducts as a function of time. A high-performance liquid chromatography (HPLC) procedure that allows monitoring of all cis- and trans-nucleoside adducts of dA and dG was used. Circular dichroism and UV-spectroscopy have been employed to gain information on adduct structural features. Incubation of cells with 0.1 μM (±)-anti-DBPDE resulted in rapid formation of adducts, followed by a decline. After 6 h of incubation about 20% of the adducts remained. Repeating the experiment with 0.01 μM (±)-anti-DBPDE resulted in a correspondingly lower adduct level initially, but in this case a larger proportion (35%) of the adducts remained after 6 h of incubation. Notably, at this time point, similar amounts of adducts are observed with both (±)-anti-DBPDE concentrations studied. Independent of diol epoxide concentration and incubation time, the dA/dG adducts were constant in number (~2.8). However, within the different adduct categories, the adduct distribution seemed to be time dependent. Although the data are preliminary, a selection with regard to adduct removal seems to have taken place. In comparative experiments with (+)-anti-BPDE, no significant difference in rates of adduct removal was evident. Preliminary results from global gene expression analysis, with focus on genes involved in DNA maintenance and cell cycle checkpoints, demonstrate interesting differences in the stress response elicited in the cells following exposure to the distorted and flexible nonplanar DBPDE or the rigid and planar BPDE molecule. As expected some major common induction events were clearly related to the activation of p53-dependent cell cycle checkpoint. However, distinct clusters of gene expression alterations were detected which mark one or other treatment specifically, indicating a high degree of subtlety in the stress response to closely related DNA adduct forming species.  相似文献   

8.
We describe a general theory of multi-nozzle cascade impactor stages and show how testers of inhaled drug products, such as metered-dose or dry-powder inhalers, can decide, solely from the stage nozzle dimensions, whether any used impactor is satisfactorily operating within its expected aerodynamic performance range. We first account for the realistic shape of particle collection efficiency curves and show that the effective diameter, described by Roberts and Romay (2005) Roberts D. L.Romay F. J.Relationship of Stage Mensuration Data to the Performance of New and Used Cascade ImpactorsJ. Aerosol Med2005184396413[Crossref], [PubMed] [Google Scholar], is sufficiently accurate as the primary indication of the aerodynamic performance.

To ensure that a used impactor is performing in the same aerodynamic range allowed for new impactors, one must also satisfy the other, more secondary factors of cascade impaction aerodynamics, most notably the distance to the collection surface relative to the nozzle diameter. We show what this constraint means in practice for used Next Generation Impactors (NGIs; Marple et al. 2003a Marple V. A.Roberts D. L.Romay F. J.Miller N. C.Truman K. G.Van Oort M.Olsson B.Holroyd M. J.Mitchell J. P.Hochrainer D.Next Generation Pharmaceutical Impactor, Part I: DesignJ. Aerosol Med2003a16283299[Crossref], [PubMed] [Google Scholar], b Marple V. A.Olson B. A.Santhanakrishnan K.Mitchell J. P.Murray S. C.Hudson-Curtis B. L.Next Generation Pharmaceutical Impactor—Part II: Archival CalibrationJ. Aerosol Med2003b16[Crossref], [PubMed] [Google Scholar]; 2004 Marple V. A.Olson B. A.Santhanakrishnan K.Roberts D. L.Mitchell J. P.Hudson-Curtis B. L.Next Generation Pharmaceutical Impactor: A New Impactor for Pharmaceutical Inhaler Testing. Part III. Extension of Archival Calibration to 15 L/minJ. Aerosol Med200417335343[Crossref], [PubMed] [Google Scholar]), and show that partially occluded nozzles are the most likely nozzles to fail this test.

Applying this principle that used impactors should perform in the same aerodynamic range as new impactors, we derive constraints on the nozzle diameters of any used NGI (Table 6, main text). We can partially apply this principle to other common impactors used for inhaler testing, such as the Andersen and the Marple-Miller, but are hindered by the absence of a published acceptable range for the distance to the impaction collection surface and by the limited published information on the shape of their stage collection efficiency curves.  相似文献   

9.
The numerical models for predicting the collection efficiency of particles in the size range of 0.3 ~ 10.0 μm in electrostatic precipitators (ESPs) have been well developed. However, for nanoparticles, or particles with the diameter below 100 nm, the existing models can't predict the collection efficiency very well because the electric field and ion concentration distribution were not simulated, or charging models were not adopted appropriately to calculate particle charges. In this study, a 2-D numerical model was developed to predict the nanoparticle collection efficiency in single-stage wire-in-plate ESPs. Laminar flow field was solved by using the Semi-Implicit Method for Pressure-Linked Equation (SIMPLER Method), while electric field strength and ion concentration distribution were solved based on Poisson and diffusion-convection equations, respectively. The charged particle concentration distribution and the particle collection efficiency were then calculated based on the convection-diffusion equation with particle charging calculated by Fuchs diffusion charging theory. The simulated collection efficiencies of 6–100 nm nanoparticles were compared with the experimental data of Huang and Chen (2002 Huang, S. H. and Chen, C. C. 2002. Ultrafine Aerosol Penetration through Electrostatic Precipitators.. Environ. Sci. Technol., 36: 46254632. [Crossref], [PubMed], [Web of Science ®] [Google Scholar]) for a wire-in-plate dry ESP (aerosol flow rate: 100 L/min, applied voltage: ?15.5 ~ –21.5 kV). Good agreement was obtained. The simulated particle collection efficiencies were further shown to agree with the experimental data obtained in the study for a wire-in-plate wet ESP (Lin et al. 2010 Lin, G. Y., Tsai, C. J., Chen, S. C., Tzu, M. C. and Li, S. N. 2010. An Efficient Single-Stage Wet Electrostatic Precipitator for Fine and Nanosized Particle Control.. Aerosol Sci. Technol, 44: 3845. [Taylor & Francis Online], [Web of Science ®] [Google Scholar]) (aerosol flow rate: 5 L/min, applied voltage: +3.6 ~+4.3 kV) using monodisperse NaCl particles of 10 and 50 nm in diameter. It is expected that the present model can be used to facilitate the design of ESPs for nanoparticle control and electrostatic nanoparticle samplers.  相似文献   

10.
Three primary benefits (advantages) of properly designed and operated ozone laundering systems have been proven in successful commercial installations – microbiological kills/inactivation of all microorganisms found in linens to be laundered; economic cost savings and significant environmental benefits. Each of these benefits of ozone laundering is described and quantified in the Ozone Laundry Handbook by Rice et al. (2009 Rice, R.G., Cardis, D., Daniels, R., Tapp, C., DeBrum, M. and Watt, J. 2009. The Ozone Laundry Handbook, A Comprehensive Guide for the Proper Application of Ozone in the Commercial Laundry Industry, San Luis Obispo, CA, , USA: Published by ClearWater Tech, LLC.  [Google Scholar]). In this paper, two of these benefits, Cost Savings and Significant Environmental Benefits are discussed.  相似文献   

11.
In this study, we show that black carbon (BC) mass concentrations measured by different techniques are consistent and traceable. First, we present the volatilities of 13 organic compounds passed through a heated inlet. These data were used to quantify the interference of organic aerosols on the BC measurement techniques. The masses of the refractory particles that incandesce (m*ref) were used to calibrate BC mass measured by a single-particle soot photometer (SP2), which uses laser-induced incandescence. This calibration was influenced little by refractory organics and agreed well with that of fullerene soot, which indicates the consistency of the standards. We estimated the interference of pyrolyzed refractory organics on the BC measured with a filter-based absorption photometer continuous soot monitoring system (COSMOS) with a heated inlet to be small in Asia. This was also confirmed by the stable mass absorption cross section (MAC) obtained by the high correlations between BC mass concentrations measured by COSMOS (M COSMOS) and those measured by the thermal-optical transmittance method (M TOT) (Kondo et al. 2009 Kondo, Y., Sahu, L., Kuwata, M., Miyazaki, Y., Takegawa, N., Moteki, N., Imaru, J., Han, S., Nakayama, T., Hu, M., Kim, Y. J. and Kita, K. 2009. Stabilization of the Mass Absorption Cross Section of Black Carbon for Filter-Based Absorption Photometry by the Use of a Heated Inlet. Aerosol Sci. Technol., 43: 741756. [Taylor & Francis Online], [Web of Science ®] [Google Scholar]). M COSMOS was also compared with total BC mass concentrations measured with an SP2 (M SP2) in Tokyo in 2009. M COSMOS and M SP2 were highly correlated (r 2= 0.97) and agreed to within about 10% on average. These results demonstrate that M SP2, M COSMOS, and M TOT were nearly identical. Use of the masses of incandescing refractory BC particles for calibration of BC mass concentrations determined by different techniques gave consistent results.  相似文献   

12.

The effect of Brownian diffusive particle trajectory of nanoparticles on the transfer function of the low pressure Differential Mobility Analyzer (LPDMA) was evaluated by a numerical simulation of the Langevin dynamic equation. The results of the simulation were compared with previously reported experimental results (Seto et al. 1997 Seto, T., Nakamoto, T., Okuyama, K., Adachi, M., Kuga, Y. and Takeuchi, K. 1997. Size Distribution Measurement of Nanometer-Sized Aerosol Particles using DMA under Low-Pressure Conditions. J. Aerosol Sci., 28: 193206. [CROSSREF][Crossref] [Google Scholar]; Seol et al. 2000 Seol, K. S., Tsutatani, Y., Camata, R. P., Yabumoto, J., Isomura, S., Okada, Y., Okuyama, K. and Takeuchi, K. 2000. A Differential Mobility Analyzer and A Faraday Cup Electrometer for Operation at 200-930 Pa Pressure. J. Aerosol Sci., 31: 13891395. [CSA][CROSSREF][Crossref] [Google Scholar]) and Stolzenburg's transfer function (1988). As the operational pressure decreased, the peak and FWHM (full width of the transfer function at half of its maximum) values of transfer function, as calculated by numerical simulation, were increased, which was not evident from Stolzenburg's transfer function. In comparison with the experiments of Seto et al., discrepancies in the higher electrical mobility regime than from central mobility were found, which could be caused by the incomplete flow control of their LPDMA. However, the transfer function, as calculated by numerical simulation was in good agreement with experimental results reported by Seol et al., performed with the improved LPDMA at well-controlled operation conditions.  相似文献   

13.
Atmospheric aerosols are one of the least understood components of the climate system and incur adverse health effects on susceptible populations. Organic aerosols can make up as much as 80% of atmospheric aerosols (Lim and Turpin 2002 Lim, H. J. and Turpin, B. J. 2002. Origins of Primary and Secondary Organic Aerosol in Atlanta: Results’ of Time-Resolved Measurements During the Atlanta supersite experiment. Environ. Sci. Technol., 36: 44894496. 10.1021/es0206487[Crossref], [PubMed], [Web of Science ®] [Google Scholar]), and so its quantification and characterization plays an important role in reducing our uncertainty with regards to aerosol impacts on health and climate. As the number of organic molecules in the atmosphere are diverse in number (Hamilton et al. 2004 Hamilton, J. F., Webb, P. J., Lewis, A. C., Hopkins, J. R., Smith, S. and Davy, P. 2004. Partially Oxidised Organic Components in Urban Aerosol using GCXGC-TOF/MS. Atmos. Chem. Phys., 4: 12791290. [Crossref], [Web of Science ®] [Google Scholar]), we advance a functional group representation of organic molecules as measured by Fourier transform infrared spectroscopy (FTIR) to characterize the chemical composition of particle samples. This study describes and evaluates the algorithm introduced by Russell et al. (2009 Russell, L. M., Takahama, S., Liu, S., Hawkins, L. N., Covert, D. S.Quinn, P. K. 2009. Oxygenated Fraction and Mass of Organic Aerosol from Direct Emission and Atmospheric Processing Measured on the R/V Ronald Brown During TEXAQS/GoMACCS 2006. J. Geophys. Res.-Atmos., 114: D00F05 10.1029/2008JD011275[Crossref], [Web of Science ®] [Google Scholar]) for apportionment and quantification of oxygenated (carbonyl and hydroxyl) functional groups from infrared absorption spectra. Molar absorptivities for carbonyl and hydroxyl bonds in carboxylic groups are obtained for several dicarboxylic compounds, and applied to a multifunctional compound and mixture to demonstrate the applicability of this method for more complex samples. Furthermore, functional group abundances of two aldehydic compounds, 2-deoxy-d-ribose and glyceraldehyde, atomized from aqueous solution are in quantitative agreement with number of bonds predicted after transformation of these compounds into diols. The procedure for spectra interpretation and quantitative analysis is described through the context of an algorithm in which contributions of background and analyte absorption to the infrared spectrum are apportioned by the superposition of lineshapes constrained by laboratory measurements.

Copyright 2013 American Association for Aerosol Research  相似文献   

14.
An aerosol dynamics model for dry deposition process is developed based on the moment method. Since it is hard to fully apply the moment method to the widely used dry deposition velocity expressions based on the resistance theory, the dry deposition velocity expression by Raupach et al. (2001) Raupach, M. R., Briggs, P. R., Ahmad, N. and Edge, V. E. 2001. Endosulfan Tansport: II. Modeling airborne Dispersal and Deposition by Spray and Vapor. J. Environ. Qual., 30: 729740. [Crossref], [PubMed], [Web of Science ®] [Google Scholar] is used. Detailed deposition mechanisms such as Brownian diffusion, gravitational settling, and impaction are considered in the expression. To verify the validity of the derived dynamic equation, aerosol dynamics for the dry deposition process is estimated with the expressions of Raupach et al. (2001) Raupach, M. R., Briggs, P. R., Ahmad, N. and Edge, V. E. 2001. Endosulfan Tansport: II. Modeling airborne Dispersal and Deposition by Spray and Vapor. J. Environ. Qual., 30: 729740. [Crossref], [PubMed], [Web of Science ®] [Google Scholar], of Wesely (1989) Wesely, M. L. 1989. Parameterizations of Surface Resistance to Gaseous Dry Deposition in Regional-Scale, Numerical Models. Atmos. Environ., 23: 12931304. [Crossref], [Web of Science ®] [Google Scholar] modified for particles (Seinfeld and Pandis 1998 Seinfeld, J. H. and Pandis, S. N. 1998. Atmospheric Chemistry and Physics, 958996. New York, , USA: Wiley.  [Google Scholar]), in CMAQ, and with constant value used in RAINS-ASIA. Those expressions give different dynamics. Generally, the result for this study is between the result of modified Wesely's expression and CMAQ. When using the modified Wesely's expression with the number of sections being equal or smaller than 10, the resultant size distribution does not give the peak shape accurately.  相似文献   

15.
The influence of humidity on changes to the pressure drop of flat and pleated HEPA filters clogged by polydisperse hygroscopic and non-hygroscopic aerosols has been studied. For flat filters, the results confirm the observations reported by Gupta et al. (1993) Gupta, A., Novick, V. J., Biswas, P. and Monson, P. R. 1993. Effect of Humidity and Particle Hygroscopicity on the Mass Loading Capacity of High Efficiency Particulate Air (HEPA) Filter.. Aerosol Sci. Tech., 19: 94107. [Taylor & Francis Online], [Web of Science ®] [Google Scholar] that with a hygroscopic aerosol at humidity below the deliquescent point, or with a non-hygroscopic aerosol, the particulate specific cake resistance decreases as relative humidity increases. For pleated filters as for flat filters, the results reveal that during the formation of the particulate cake, the increase in relative humidity leads to a decrease in the specific cake resistance. When the reduction in filtration area, specific to pleated filters, becomes large, the presence of humidity accelerates the filling of pleats causing a greater pressure drop for a same aerosol mass loading. With a hygroscopic aerosol at a humidity above its deliquescent point, the change in pressure drop through flat or pleated filters is not linear but characteristic of liquid aerosol filtration. The influence of humidity on the efficiency of pleated filters, measured by a soda fluorescein aerosol, has also been studied. For clean filters, the efficiency decreases with increasing relative humidity above 90%. For filters clogged with solid aerosol, change in efficiency versus collected surface mass reaches a maximum whose value depends on the relative humidity; when the aerosol is liquid, the efficiency decreases throughout the clogging.  相似文献   

16.
Recently a new compact aerosol concentration enrichment system was developed at the University of Southern California, specifically intended to provide particle-laden air at flow rates and pressures suitable for interfacing with on-line continuous aerosol instrumentation for chemical analysis such as mass spectrometers. The re-design and engineering of the miniature Versatile Aerosol Concentration Enrichment System (mVACES) and primarily laboratory-based validation of the individual components and overall system has been previously reported (Geller et al. 2005 Geller, M. D., Biswas, S., Fine, P. M. and Sioutas, C. 2005. A New Compact Aerosol Concentrator for Use in Conjunction with Low Flow-Rate Continuous Aerosol Instrumentation. J. Aerosol Sci., 36: 10061022. [CSA][CROSSREF][Crossref], [Web of Science ®] [Google Scholar]). From September to December 2005, a field performance validation study of the mVACES was conducted in Los Angeles, California at a mixed urban site influenced by both freeway traffic and construction. A variety of continuous and semi-continuous physical and chemical composition measurements were performed to assess the performance of the mVACES compared to accepted methods for validation. Near-ideal performance for aerosol concentration enhancement by the mVACES was observed for mass and number distribution with minimal evidence for distortion of the size distribution. Similarly, near-ideal concentration enhancement factors were observed for both inorganic and organic species suggesting that the mVACES works equally well across the range of externally mixed urban aerosol. The data suggest that aerosol concentration enhancements up to an ideal factor of 20 in a delivered flow on the order of 1.5 liters min–1 are readily achievable in an urban environment for the ambient conditions studied.  相似文献   

17.
This paper describes the usefulness of one-dimensional diffusion-ordered NMR spectroscopy (1D-DOSY) in investigating dynamics and interactions of molecules in solution as well as in analyzing the structure of molecules. We synthesized the three imines, N-benzylidene-4-methylbenzene-Sulfonamide (1 Kondo, K., Kazuta, K., Saitoh, A. and Murakami, Y. 2003. Heterocycles, 59: 97100.  [Google Scholar]), N-(4-chloro-benzylidene)4-methyl-benzene-sulfonamide (2 Horibe, H., Kazuta, K., Kotoku, M., Kondo, K., Okuno, H., Murakami, Y. and Aoyama, T. 2003. Synlett, : 20472051. [Web of Science ®] [Google Scholar]), and N- (4-methoxybenzylidene)-4-methyl-benzene sulfonamide (3 Horibe, H., Fukuda, Y., Kondo, K., Okuno, H., Murakami, Y. and Aoyama, T. 2004. Tetrahedron, 60: 1070110709. [Crossref], [Web of Science ®] [Google Scholar]), and acetophenone (4 Sakamoto, Y., Kondo, K., Tokunaga, M., Kazuta, K., Fujita, H., Murakami, Y. and Aoyama, T. 2004. Heterocycles, 63: 13451357. [Crossref], [Web of Science ®] [Google Scholar]) and its three derivatives, 4-chloroacetophenone (5 Sakamoto, Y., Kondo, K., Onozato, M. and Aoyama, T. 2006. Polycycl. Aromat. Comp., 26: 5968. [Taylor & Francis Online], [Web of Science ®] [Google Scholar]), 4-nitro-acetophenone (6 Kondo, K., Kazuta, K., Fujita, H., Sakamoto, Y. and Murakami, Y. 2002. Tetrahedron, 58: 52095214. [Crossref], [Web of Science ®] [Google Scholar]), and 4-methoxyaceto -phenone (7 Gostam, T., Morean, C., Jutean, A., Guichard, E. and Delsuc, M. A. 2004. Magn. Reson. Chem., 42: 496499.  [Google Scholar]). 1D-DOSY was applied to a mixture of compounds (1 Kondo, K., Kazuta, K., Saitoh, A. and Murakami, Y. 2003. Heterocycles, 59: 97100.  [Google Scholar]), (2 Horibe, H., Kazuta, K., Kotoku, M., Kondo, K., Okuno, H., Murakami, Y. and Aoyama, T. 2003. Synlett, : 20472051. [Web of Science ®] [Google Scholar]), and (3 Horibe, H., Fukuda, Y., Kondo, K., Okuno, H., Murakami, Y. and Aoyama, T. 2004. Tetrahedron, 60: 1070110709. [Crossref], [Web of Science ®] [Google Scholar]) and to a mixture of compounds (4 Sakamoto, Y., Kondo, K., Tokunaga, M., Kazuta, K., Fujita, H., Murakami, Y. and Aoyama, T. 2004. Heterocycles, 63: 13451357. [Crossref], [Web of Science ®] [Google Scholar]), (5 Sakamoto, Y., Kondo, K., Onozato, M. and Aoyama, T. 2006. Polycycl. Aromat. Comp., 26: 5968. [Taylor & Francis Online], [Web of Science ®] [Google Scholar]), (6 Kondo, K., Kazuta, K., Fujita, H., Sakamoto, Y. and Murakami, Y. 2002. Tetrahedron, 58: 52095214. [Crossref], [Web of Science ®] [Google Scholar]), and (7 Gostam, T., Morean, C., Jutean, A., Guichard, E. and Delsuc, M. A. 2004. Magn. Reson. Chem., 42: 496499.  [Google Scholar]). Although 1 H NMR chemical shifts of the molecules in the mixtures resembled one another in the surrounding, we could distinguish signals of the individual molecules in each mixture on the basis of the NMR data and the values of the diffusion coefficient. Also, we could found the correlation of the measured diffusion coefficients and the calculated molecular volumes.  相似文献   

18.
Synthesis of a new class of 1, 3-thiazolidine nucleoside analogs is described. Reaction of 2-amino-2-deoxy-D-glucopyranose hydrochloride 2 with carbon disulfide yielded 5-hydroxy-4-(D-arabino-1, 2, 3, 4-tetrahydroxybutyl)-thiazolidin-2-thione 3, which on acetylation yielded 5-acetoxy-4-(D-arabino-1, 2, 3, 4-tetraacetoxy-butyl)-thiazolidin-2-thione 4. The acetylated sugar 4 reacted with hydrazonoyl chlorides 1a–f, affording the 5-acetoxy-4-(D-arabino-1, 2, 3, 4-tetraacetoxybutyl)-spiro-1 Chen, H., Fan, Y-H., Natarajan, A., Guo, Y., Iyasere, J., Harbinski, F., Luus, L., Christ, W., Aktas, H. and Halperin, J. A. 2004. Bioorg. Med. Chem. Lett., 14: 54015405. [Crossref], [PubMed], [Web of Science ®] [Google Scholar] 3 Nasr, M. N., Gineinah, M. M. and El-Bendary, E. R. 2003. Arch. Pharm., 336: 560566. [Crossref] [Google Scholar]thiazolidine-2,2′ -1 Chen, H., Fan, Y-H., Natarajan, A., Guo, Y., Iyasere, J., Harbinski, F., Luus, L., Christ, W., Aktas, H. and Halperin, J. A. 2004. Bioorg. Med. Chem. Lett., 14: 54015405. [Crossref], [PubMed], [Web of Science ®] [Google Scholar] 3 Nasr, M. N., Gineinah, M. M. and El-Bendary, E. R. 2003. Arch. Pharm., 336: 560566. [Crossref] [Google Scholar] 4 Belleau, B., Brasilli, L., Chan, L. and Zacheri, B. 1993. Cameron J. Bioorg. Med. Chem. Lett., 3: 17231928. [Crossref], [Web of Science ®] [Google Scholar]thiadiazole derivatives 8a–f. The antibacterial activity of the novel 1, 3-thiazolidine-2,2′ -spiro- 1 Chen, H., Fan, Y-H., Natarajan, A., Guo, Y., Iyasere, J., Harbinski, F., Luus, L., Christ, W., Aktas, H. and Halperin, J. A. 2004. Bioorg. Med. Chem. Lett., 14: 54015405. [Crossref], [PubMed], [Web of Science ®] [Google Scholar] 3 Nasr, M. N., Gineinah, M. M. and El-Bendary, E. R. 2003. Arch. Pharm., 336: 560566. [Crossref] [Google Scholar] 4 Belleau, B., Brasilli, L., Chan, L. and Zacheri, B. 1993. Cameron J. Bioorg. Med. Chem. Lett., 3: 17231928. [Crossref], [Web of Science ®] [Google Scholar]thiadiazole nucleoside analogs is highlighted. All compounds with free NH group in the thiazolidine series 8a–f showed significant biological activity against all the standard strains.  相似文献   

19.
It is possible to detach ozone from silica gel under the same temperature and same pressure conditions in which the silica gel adsorbed ozone (Murai et al., 2000 Murai, A. and Tahara, N. Storage Method for Ozone oriented to Power Loads Leveling. 2000 International Ozone Association Pan American Group Conference. Proceedings of, Orlando, Florida, USA Session 9. [Google Scholar], 2001 Murai, A., Tahara, N. and Nakajima, T. 2001. Electric Power Loads Leveling by Ozone Storage. J.Inst.Elec.Install.Engi.Japan, 21: 516522.  [Google Scholar], 2002 Murai, A., Tahara, N. and Nakajima, T. 2002. Ozone Storage Oriented to Power Load Leveling. Ozone Sci. Eng., 23: 171180.  [Google Scholar]). The addition of extra energy is unnecessary. We changed the temperature of the silica gel and measured the differences in the amount of stored ozone. The amount of adsorbed ozone became linear, as determined by the van't Hoff relationship. A computer program was developed to simulate the characteristics of the storage and removal of ozone. The results of the calculation demonstrated these characteristics. This system confirms an inexpensive construction method of storing ozone in a sewage plant. This method is effective for power load leveling.  相似文献   

20.
A non-woven graded metal-fiber filter was characterized for its collection efficiency as a function of particle size at an airflow velocity of 10 m s ?1 . Efficiencies were determined by generating a monodisperse aerosol of polystyrene latex (PSL) spheres and oleic acid liquid particles of measured concentration with and without the filter present. For PSL spheres ≤0.7 μm, the collection efficiencies follow theoretical single-fiber collision efficiency (Ptak and Jaroszczyk 1990 Ptak, T. and Jaroszczyk, T. 1990. “Theoretical-Experimental Aerosol Filtration Model for Fibrous Filters at Intermediate Reynolds Numbers”. In Proceedings 5th World Filtration Congress, 566572. France: Nice.  [Google Scholar]). Above 0.7 μm diameter (Stokes number 0.8), PSL collection efficiency exhibits a general decreasing trend with increasing particle size suggesting particle bounce. Although this trend is consistent with measured single-fiber collection (collision and adhesion) efficiency for Stokes numbers in the range of 0.2 to 22 (Rembor et al. 1999 Rembor, H.-J., Maus, R. and Umhauer, H. 1999. Measurements of Single Fibre Efficiencies at Critical Values of the Stokes Number. Part. Part. Syst. Charact, 16: 5459. [Crossref], [Web of Science ®] [Google Scholar]; Ptak and Jaroszczyk 1990 Ptak, T. and Jaroszczyk, T. 1990. “Theoretical-Experimental Aerosol Filtration Model for Fibrous Filters at Intermediate Reynolds Numbers”. In Proceedings 5th World Filtration Congress, 566572. France: Nice.  [Google Scholar]), the magnitude of the filter efficiency is less. For 1 μm to 4 μm PSL, the average collection efficiency is 0.43 (expanded uncertainty (U) of 0.08, n = 6). In the case of particles having very different surface adhesion, e.g., oleic acid (sticky) aerosol, the collection efficiency for ≥1 μm diameter particles is nearly 1.00. This is in accordance with the theoretical collision efficiency as expected for particles with high adhesion. PSL tests performed on a filter coated with a synthetic-oil (aerosol) deposit (32.9 μg mm ?2 ± 0.4 μg mm ?2 ) improved the collection efficiency for PSL ≥ 0.7 μm to nearly 1.00. Particles that are deposited by interception-inertial impaction at 10 m s ?1 airflow velocity depend on the particle and fiber adhesion properties.  相似文献   

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