SOLVENT DE-ASHING FROM HEAVY PRODUCT OF BROWN-COAL LIQUEFACTION USINGTOLUENE - 2 - CONCENTRATION AND SEPARATION OF ASH WITH A CONTINUOUS DE-ASHING SYSTEM

Citation
O. Okuma et al., SOLVENT DE-ASHING FROM HEAVY PRODUCT OF BROWN-COAL LIQUEFACTION USINGTOLUENE - 2 - CONCENTRATION AND SEPARATION OF ASH WITH A CONTINUOUS DE-ASHING SYSTEM, Fuel processing technology, 56(3), 1998, pp. 229-241
Citations number
20
Categorie Soggetti
Engineering, Chemical","Energy & Fuels","Chemistry Applied
Journal title
ISSN journal
03783820
Volume
56
Issue
3
Year of publication
1998
Pages
229 - 241
Database
ISI
SICI code
0378-3820(1998)56:3<229:SDFHPO>2.0.ZU;2-3
Abstract
The brown coal liquefaction (BCL) process is a two-stage liquefaction (hydrogenation) process developed for Victorian brown coal in Australi a. The BCL process has a solvent de-ashing step to remove the ash and heavy preasphaltenes from the heavy liquefaction product (vacuum resid ue) derived from the coal in primary hydrogenation and named CLB (coal liquid bottom). This solvent de-ashing step uses toluene or coal-deri ved naphtha as a de-ashing solvent (DAS). After dissolving the CLB int o the solvent (CLB/solvent ratio, 1/8-1/4, w/w) under high temperature (200-290 degrees C) and high pressure (4-5 MPa), insoluble solid part icles which consist of ash and heavy preasphaltenes are settled by gra vity and separated from the solution as an ash-concentrated slurry. Th e ash-concentrated slurry and the de-ashed solution are withdrawn from the settler as an underflow and overflow, respectively. The de-ashed heavy product is recovered from the solution by eliminating the solven t and is further hydrogenated in secondary hydrogenation. The authors have reported on the solubility of CLB in toluene and the settling vel ocity (V) of the boundary of ash content in the settler under de-ashin g conditions. This paper discusses the effects of de-ashing conditions on ash concentration in the settler bottom and the operating conditio ns of a continuous de-ashing system. The ash content in underflow (C-U F, kg/kg or wt.%) at the settler bottom was found to increase with tem perature and to decrease with the rate (flux) of downward flow (underf low). The maximum C-UF, Z, is expressed by the equation: Z = B-CLB(FL/ 0.35)(-0.32)(T/527)(4.26), where B-CLB, FL and T are the characteristi c parameters of organic CLB (kg/kg or wt.%), flux of underflow in the settler (kg/m(2) s) and temperature (K), respectively. B-CLB is also e xpressed by using the analytical results of organic insolubles in the CLB under de-ashing conditions. Finally, stable operating conditions o f a continuous de-ashing system are confirmed to be determined as the following qualifications: /V-u/ < /V/, W-UF > W-SA/C-UF and Z > C-UF, where /V-u/, /V/, W-SA and W-UF are the upward velocity of the solutio n in the settler (mm/s), settling velocity of the ash boundary (mm/s) in the settler, flow rate of ash in the feed slurry (kg/h) and flow ra te of underflow (kg/h). respectively. Under these qualified conditions , the 50 t/d pilot plant constructed in Australia was operated under s table conditions for 3700 h using toluene as a DAS. (C) 1998 Elsevier Science B.V. All rights reserved.