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Figure 1.
Table 1.
References [1] D.
Rappaz: Modeling Simul Mater Sci Eng, 1 (1993) p. 4555 [5] M.
[9] Qingyan Xu, Baicheng Liu and Zuojian Liang: Material Sc Forum, Vol 475-479 (2005) p. 3137 [10] J.

The dimension of plates and risers is shown in Table 1.
Fig.1 Configuration of casting design.
Conclusions 1.
References [1] Y.S.
Vol.101, (1993), 479-484

The sintering process adapted in shown in Fig.1.
Compression Test and hardness survey were carried out for various samples and the testing parameters are shown in Table 1.
Table 1 Testing Parameters 1.
The following observations were made: 1.
The comparison of hardness survey on the samples before and after the cryogenic treatment is shown in Table 3. 1.

Results and discussion X-ray Diffraction.Fig.1 shows the XRD patterns of undoped and V-doped TiO2 nanoparticles.
Scherrer equation was Fig.1.
References [1] Murugan A, Samuel Vand Ravi V: Mater.
Lett. 60(2006)479 [2] Z.
Sci. 3 (1997) 1 [11] J.W.

Sim 1, J.M.
Results and Discussion Before mechanical activation, sharp peaks of crystalline CaO, Bi2O3 and TiO2, were observed (Figure 1).
REFERENCES 1.
Sakata, "Grain Orientation Effects on Electrical Properties of Bismuth Layerstructured Ferroelectric Pb(1-x)(NaCe)x/2Bi4Ti4O15 Solid Solution", J.
Soc., 82, 477-479, (1999). 14.

The experimental installment for temperature measurement is presented in Fig.1.
Fig. 1 EMCC apparatus and temperature measurement Equations of heat transfer and FE model.
It is can be clearly seen from Fig.6 (1) that the L zone near the crucible slit is the strongest heating zone.
References [1] T.
Vol. 475-479 (2005), p. 2575 [4] H.Z.

The binary image of the machining surface can be acquired as shown in Fig.1.
The amount of pixel points with 1 was calculated using MATLAB software.
Surface height percentage under bearing area from 5% to 80% is shown in Tab.1.
References [1] L.X.
Vol. 29(2005), P. 479-490

Research on Environment Materials with Variation Rule And Characteristic of Air Pollutants In Nanchang City Xifeng Yan1, a , Jinglan Wang1, b, Youhua Zhou2, c and Feng Liu 1,d 1 Jiangxi science and Technology Normal University, Jiangxi, China, 330013 2 Beijing Geo Environ Engineering Technology, Inc, Beijing, China, 100095 aemail:xifengyan@163.com, bemai:jxncwjl@163.com, cemail: 252014111@qq.com, demail: 82899084@qq.com Keywords: Air pollutants; Correlation analysis; Nanchang.
The air quality have drawn high attention by public due to it special location and the development strategy. 1.
Resource Air pollutants SO2, NO2 andPM10 measurement methods includes: Determination of SO2: Formaldehyde absorption - Pararosaniline spectrophotometry (GB/T 15262-94) Determination of SO2: Formaldehyde absorption - Pararosaniline spectrophotometry (HJ 482-2009) (To substitute GB/T 15262-94 from Nov. 1, 2009) Determination of NO2 : Saltzman (GB/T15436-1995) Determination of NO2: Naphthyl ethylene diamine dihydrochloride spectrophotometric method (HJ 479-2009, To substitute GB/T 15436-1995 from Nov. 1, 2009) Determination of PM10: Determination of the concentration of airborne particulate (HJ 618-2011) (To substitute GB6921-1986 from 2011) According to the monitoring data, the concentration of air pollutants sulfur dioxide, nitrogen dioxide, PM10 10 year (2003-2012) annual statistical data, and reference to the research results of many scholars from 2003 [1], can be pushed forward to 1996, which won the concentration variation of 1996-2012 for up to 17 years of three kinds of
main pollutants, drawing the air pollution interannual variation trend of Nanchang City as shown in Figure 1, the time span, more easy to explain variation.
Acknowledgements This work was financially supported by Jiangxi Science and Technology Agency (20122BBG70080 ) References [1] WU Dan, WANG Shi-gong, SHANG Ke-zheng.

Analysis on Estimation of PM2.5 Emissions on Coal-fired Generating Unit Xiaozheng Han 1, a, Qingqing Wang 2, b 1 Environmental Management College of China, Qinhuangdao, Hebei.066004, China; 2 Qinhuangdao Economic and Technological Development Zone Environmental Protection Agency, Qinhuangdao, Hebei.066004, China.
Industrial pollution sources were the main causes of dust haze pollution, some scholars pointed out that Hebei province was in the middle of industrialization development stage [1], relatively backward industrialization process determines the Hebei in the integration construction must make adjustments.
So we must scientific evaluation of power industry dust haze that make a balance of social development and dust haze reduce. 1.
Tab1: Analysis on estimation of electricity generation and PM2.5 emissions Categories(100 million kWh) Units number Generate electricity (100 million kWh) PM2.5 emission (t) PM2.5 emission per 100 million kWh (t) 0-0.5 68 18.12 9095.11 501.94 0.5-1 27 18.44 6387.04 346.37 1-5 38 80.88 6709.48 82.96 5-10 7 46.39 1376.94 29.68 10-15 30 379.11 8577.95 22.63 15-20 39 676.77 11188.46 16.53 Above 2,000 million kWh 20 651.18 8639.75 13.27 Due to the unit generate electricity data range is larger, in order to facilitate data analysis and expression, the small electricity generation units (0~100 million kWh), use the 0.5 group interval, 1~20 million kWh electric units have adopted the 5 group distance.
Research of Environmental Sciences. 2005,18(5):1-5

Fig. 1 Schematic diagram of the fabrication process of polymer nanotubes.
The wetting process for fabrication of polymer nanotubes is shown in Fig. 1.
Spectrum of PMMA in Fig. 5(a) shows the conjugation C=O stretching absorption (1750 to 1700 cm-1), and C-O stretching absorption( 1150 to 1100 cm-1).
References [1] M.
Chi, Materials Science Forum Vol. 475-479 (2005) p.3919 [3] M.