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Pyrolysis continued system

The authors had already conducted the laboratory scale study and the preliminary pilot plant study, and proposed that "drying-pyrolysis process" (pyrolysis followed by indirect steam drying of dewatered sludge cake) (Fig,-i) could be one of the most economical and feasible alternatives for conventional incineration process. The authors have further conducted the feasibility study on a continuous system of "drying-pyrolysis process to evaluate the performance of the process in pilot scale, and to demonstrate its effectiveness as a thermal processing of sewage sludge. This paper presents the results of this pilot plant study. [Pg.488]

For continuous pyrolysis, only metal reactors (steel or nickel alloys) are used and PTFE is fed into the reactor with a screw feeder. The gaseous products are either collected using a scaled up cold trap, or fed directly into other processes [5,13], Continuous systems suffer from a drawback in that it is very difficult to maintain a pressure seal at the PTFE inlet, resulting in the inclusion of air in the reactor atmosphere, which induces PTFE combustion rather than pyrolysis and produces a mixture of mostly undesired products, such as CF4, C02 and CF2O. [Pg.83]

Particle size is less important in HTC, particularly when batch systems are being used however HTL and HTG rely on pumping slurries and employ continuous systems. The influence of particle size on HTC has not been fully investigated however it is likely to have considerable effects on the carbonization process. If particle sizes are too large, the inside of biomass particles are not fully contacted with water, and heat transfer is faster than mass transfer, leading to pyrolysis reactions rather than dehydration and decarboxylation. [Pg.522]

BioTherm A System for Continuous Quality, Fast Pyrolysis BioOil, Dynamotive Energy Systems Corporation, 4th Biomass Conference of the Americas, Oakland, California, September 1, 1999... [Pg.157]

Sulfates are precipitated as BaS04, and then reduced with carbon at 1,000°C to produce CO2 and CO. The CO is either measured directly or converted to CO2 by electrical discharge between platinum electrodes (LonginelU and Craig 1967). Total pyrolysis by continuous flow methods has made the analysis of sulfate oxygen more precise and less time-consuming than the off-line methods. Bao and Thiemens (2000) have used a C02-laser fluorination system to liberate oxygen from barium sulfate. [Pg.60]

In the present review the ring systems containing one heteroatom are considered first, except for P-lactams which are given a special section at the end. Interest in azetidines continues to be stimulated by the discovery of the potentially useful trinitro derivative. The requirements for the stereoselective synthesis of substituted oxetane are being explored and derivatives of aluminium are useful in the stereoselective routes to oxetanones. The preparation and subsequent pyrolysis of oxetanones is suggested as an alternative to the Wittig route to olefins. Stereoselective routes to thietanes and thietane 1 -oxides are mentioned. [Pg.66]

Figure 5. Schematic diagram showing the effect of changing the volume fraction of second phase on the apparent viscosity at a fixed rate of shear of a two-phase emulsion. The different dotted lines refer to different viscosities of the pure phases A and B, The solid line suggests the viscosity that may be displayed by a system in which both the viscosities of the pure phases and the relative proportions of phases are changing continuously, as in a pyrolysis run. Figure 5. Schematic diagram showing the effect of changing the volume fraction of second phase on the apparent viscosity at a fixed rate of shear of a two-phase emulsion. The different dotted lines refer to different viscosities of the pure phases A and B, The solid line suggests the viscosity that may be displayed by a system in which both the viscosities of the pure phases and the relative proportions of phases are changing continuously, as in a pyrolysis run.
The work on ethane indicates quite strikingly that the same saying applies to pyrolysis. Our present understanding of pyrolysis reactions, which is not inconsiderable, has for the most part derived, and will continue to derive, from the studies of the thermodynamic and kinetic properties of individual free radicals observed in very carefully selected model systems. [Pg.363]

Many of these reactions have been studied before in the section on NaOa and so will not be discussed again here. In excess NO, the rate becomes nearly first-order over most of the decomposition with a rate constant which is itself a function of the total pressure. NO2 is an inhibitor for the decomposition, and in consequence the reaction in the absence of added NO shows a steady fall in apparent first-order rate constant with continuing decomposition. In this respect the nitrates and nitrites all seem to have in common the feature that the pyrolysis products inhibit the rate of decomposition. Tliis is to be expected in systems decomposing via radical mechanisms when the products of the reaction include such efficient radical traps as NO and NO2. It is unfortunate that quantitative data on these systems are at present so sparse and in many cases disparate. This is to be expected for systems that are so complex and show such sensitivity to surface reactions. The free radical chemistry of these systems is, however, a very interesting and important one, and efforts to elucidate it will eventually turn out to be quite rewarding. [Pg.424]

In this section we discuss the process flow diagram for the pyrolysis of waste plastics. This is required to be a compact process that can be controlled in a stable and continuous way, because of movement of the high-viscosity material for each unit system in the process. This material can block the flow line and make difficult the continuous control of unit process. [Pg.133]


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