Emissions Tradeoffs among Alternative Marine Fuels: Total Fuel Cycle Analysis of Residual Oil, Marine Gas Oil, and Marine Diesel Oil

2008 ◽  
Vol 58 (4) ◽  
pp. 538-542 ◽  
Author(s):  
James J. Corbett ◽  
James J. Winebrake
1998 ◽  
Vol 33 (12) ◽  
pp. 848-853
Author(s):  
Sadanao Rikiyasu ◽  
Nobukazu Shimada ◽  
Hajime Yoshida

Fuel ◽  
2021 ◽  
Vol 289 ◽  
pp. 119864
Author(s):  
Yimeng Li ◽  
Peng He ◽  
Zhaofei Li ◽  
Hao Xu ◽  
Jack Jarvis ◽  
...  
Keyword(s):  
Gas Oil ◽  

2009 ◽  
Vol 44 (3) ◽  
pp. 456-462
Author(s):  
Masataka HASHIMOTO ◽  
Tomohisa DAN ◽  
Ichiro ASANO ◽  
Tomohito OTANI

2003 ◽  
Vol 144 (1) ◽  
pp. 83-106 ◽  
Author(s):  
Edward A. Hoffman ◽  
Weston M. Stacey

2008 ◽  
Vol 45 (04) ◽  
pp. 191-193
Author(s):  
Wei Hai-jun ◽  
Wang Guo-you ◽  
Wang Xiao-rui

The purpose of this paper is to study the applicability of thermal processed fuel oil (hereafter called waste plastic disposal, or WPD) of diesel engines using low-quality fuel oil. In the experiment, stability of engine operation and components of exhaust gas, such as NOx and COx, were inspected from basic and applicable points of view. This paper illustrates a new test and result of WPD oil applied to marine diesel engines. In recent years, efforts have to be made to develop an advanced technique for recycling waste plastics in order to use scrapped plastics as fuel for diesel engines. It is very important and necessary for us to cope with the increasing calorific value and to satisfy the growing need of environment protection. The experimental fuel oil is obtained by a mixing of diesel oil, WPD, and water.


2019 ◽  
Vol 396 ◽  
pp. 109-120 ◽  
Author(s):  
Caroline Barbosa Monteiro ◽  
Phelype Haron Oleinik ◽  
Bruno Vasconcellos Lopes ◽  
Thalita Fagundes Leal ◽  
Osmar Olinto Möller Junior ◽  
...  

A modelling system was utilised to simulate the movement and behaviour of oil slicks for two types of hydrocarbons, a diesel and another residual, considering hydrodynamic variations. Susceptible areas to oil touching were found in adjacent regions of two vessel manoeuvring zones, in two types of zones, one in a marine coastal and another in an estuarine environment. The evaporation rates were calculated for an estimate of the mass losses. For the maritime zone, the oil particles reached the vicinity of the beaches in approximately 4 to 8 hours after the beginning of the spill simulations, while for the estuary in approximately 1 hour. For the scenarios with diesel oil, mass losses oscillated between 13 to 16% in the estuarine region, and between 23 and 29% in the marine coastal zones. The evaporation rates for scenarios with residual oil, between 2 and 5%, were considerably lower than for diesel (15 and 22%), especially for spills simulated in the estuarine region, where the oil particles reached the lagoon banks after 1 hour. Mass losses by evaporation were more intense in marine coastal areas than for oil spills simulated in estuarine regions, possibly due to the more intense hydrodynamic conditions and the longer time that the oil needs to reach the coast. The fluctuations of observed environmental conditions justify the need for a robust number of simulations for reducing the uncertainties related to the oceanographic and meteorological variability that affect oil spill movement.


1971 ◽  
Vol 60 (3) ◽  
pp. 399-407
Author(s):  
John B. Davies

One field and four laboratory trials were run to determine the reason for the success of 1–8% malathion in diesel oil in controlling Culicoides furens (Poey) in swamp mud in Jamaica. In the laboratory malathion and marine diesel oil (1:4000) was an effective larvicide for up to two days after application to the mud, but diesel oil alone gave only slight mortality even after six days. Judged by the emergence of adults, diesel oil gave 100% pupal mortality for five days and still showed some effect after four weeks; this effect was not improved by the addition of malathion. In the field, counts of emerging adults showed that diesel oil at 106–5 gal/acre gave 97–8% control of C. furens for up to eight weeks after application. It is concluded that, because of the possibility of pupicidal action, insecticides should be assessed on adult emergence rather than larval mortality.


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