Condensation coefficient of mercury vapor

1968 ◽  
Vol 24 (2) ◽  
pp. 176-181 ◽  
Author(s):  
M. N. Ivanovskii ◽  
Yu. V. Milovanov ◽  
V. I. Subbotin
1975 ◽  
Vol 97 (1) ◽  
pp. 83-87 ◽  
Author(s):  
U. Narusawa ◽  
G. S. Springer

The condensation coefficient of mercury was determined by measuring the number flux of a mercury vapor beam incident on, and reflected from, a liquid mercury surface. For a clean surface the condensation coefficient was found to be between 0.65 and 1.


1997 ◽  
Author(s):  
N. Finkelstein ◽  
W. Lempert ◽  
R. Miles ◽  
N. Finkelstein ◽  
W. Lempert ◽  
...  

2020 ◽  
Vol 1697 ◽  
pp. 012233
Author(s):  
V S Kurbanismailov ◽  
S A Maiorov ◽  
G B Ragimkhanov ◽  
Z R Khalikova

1965 ◽  
Vol 43 (4) ◽  
pp. 670-675 ◽  
Author(s):  
B. Ahlborn ◽  
A. J. Barnard ◽  
H. D. Campbell

In a pulsed arc with mercury electrodes the average column field strength Eco was measured for different currents I, and the relationship [Formula: see text] was found. The variations of arc current and voltage with time indicate that the anode and cathode fall regions have a combined thickness of 3 × 10−6 cm, and an average field strength of 2 × 106 V/cm. The arc plasma is formed mainly from mercury vapor, rather than from the surrounding gas.


Processes ◽  
2021 ◽  
Vol 9 (6) ◽  
pp. 1026
Author(s):  
Javier Tejera ◽  
Antonio Gascó ◽  
Daphne Hermosilla ◽  
Víctor Alonso-Gomez ◽  
Carlos Negro ◽  
...  

The objective of this trial was to assess the application of UVA-LED technology as an alternative source of irradiation for photo-Fenton processes, aiming to reduce treatment costs and provide a feasible treatment for landfill leachate. An optimized combination of coagulation with ferric chloride followed by photo-Fenton treatment of landfill leachate was optimized. Three different radiation sources were tested, namely, two conventional high-pressure mercury-vapor immersion lamps (100 W and 450 W) and a custom-designed 8 W 365 nm UVA-LED lamp. The proposed treatment combination resulted in very efficient degradation of landfill leachate (COD removal = 90%). The coagulation pre-treatment removed about 70% of the COD and provided the necessary amount of iron for the subsequent photo-Fenton treatment, and it further favored this process by acidifying the solution to an optimum initial pH of 2.8. The 90% removal of color improved the penetration of radiation into the medium and by extension improved treatment efficiency. The faster the Fenton reactions were, as determined by the stoichiometric optimum set-up reaction condition of [H2O2]0/COD0 = 2.125, the better were the treatment results in terms of COD removal and biodegradability enhancement because the chances to scavenge oxidant agents were limited. The 100 W lamp was the least efficient one in terms of final effluent quality and operational cost figures. UVA-LED technology, assessed as the application of an 8 W 365 nm lamp, provided competitive results in terms of COD removal, biodegradability enhancement, and operational costs (35–55%) when compared to the performance of the 450 W conventional lamp.


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