Activation energies from parallel reaction model

By applying a parallel reaction model the activation energies of different types fuel such as DB, sorghum, LARM, LAPC, HARM, HAPC, and TXL can be determined (as Table 3.5).

3.7 IGNITION

3.9.1 Ignition temperature

TGA analysis can also be used to determine the ignition temperature of a fuel when experiments are performed in an air environment. Each fuel was first analyzed in a nitrogen environment and then analyzed again in an air environment. The TGA traces of the two fuels began similarly, but upon ignition, the fuel would oxidize if air was present. Ignition caused the two TGA traces to

Подпись: Table 3.6. Ignition temperature for various FB samples (Martin, 2006); blend ratio: coal biomass. Particle size: AR 75 45 Fuel Blend ratio AR 75 45 Fuel Blend ratio All temperatures are in degrees Kelvin All temperatures are in degrees Kelvin LAPC 100-0 574 543 566 LARM 100-0 574 543 566 90-10 568 540 536 90-10 561 557 549 70-30 580 562 555 70-30 591 573 544 50-50 572 560 549 50-50 571 565 569 0-100 751 752 742 0-100 755 728 746 HAPC 100-0 574 543 566 HARM 100-0 574 543 566 90-10 603 565 550 90-10 581 567 540 70-30 595 573 556 70-30 565 569 560 50-50 604 594 570 50-50 591 576 562 0-100 733 774 787 0-100 715 757 726

deviate. The temperature at which this deviation occurred was defined as the ignition temperature (Fig. 3.18). For the mass loss traces obtained during testing, ignition is defined as the point at which the difference between the moisture normalized traces begin to deviate by more than 5% of the average value at that point and continue to deviate thereafter (Lawrence, 2007):

Подпись: > 5%

image114

(m%)N2 — (m%)air

(m%)N2 + (m%)air
2

This is best illustrated graphically as in Figure 3.18.

The ignition behavior of the biomass fuels was analyzed with similar independent variables as those used to analyze the activation energy behavior (Table 3.6). Figure 3.18 gives the temperature [K] at which ignition of the fuel sample is said to have occurred according to the definition.

The results show that the fixed carbon content of the fuel, particle size, and coal: FB blend ratio had very little effect on the ignition temperature of the fuel. The fixed carbon content for all the fuels tested is given in Table 3.7.

Table 3.7.

Fixed carbon

comparison

for various FB samples.

Fuel

HAPC

LAPC

HARM

LARM

Coal

FB

present

present

% Fixed carbon as

received basis

100%

0%

25.41

25.41

25.41

25.41

90%

10%

23.21

24.02

23.47

24.08

70%

30%

18.80

21.25

19.59

21.43

50%

50%

14.39

18.47

15.71

18.78

0%

100%

3.36

11.54

6.02

12.16

Table 3.8. Higher heat value of fuels and volatile matter from parent fuel.

HHV-DAF, HHV of VM*

Fuel

Chem. formula

kJ/kg

VM-DAF %

kJ/kg

Ref

Wy coal

CH0.71N0.014

O0.18S0.0014

29805

46.7

26430

Thien etal. (2012)

TX lignite

CH0.68N0.016

O0.19S0.0061

28460

49.4

25650

Thien etal. (2012)

LA PC feedlot biomass (FB)

CH1.28N0.05

O0.53S0.0056

21370

81.9

18130

Arumugam et al. (2009)

LAPCDB

CH1.25N0.047

O0.40S0.0046

21450

78.3

18310

Lawrence et al. (2009)

Litter

biomass, LB

CH1.55N0.091

O0.60S0.0087

19585

82.3

16750

Lawrence et al. (2009)

Mesquite

CH1.3582O0.5779 N0.0122S0.0003

20128

79.82

16933

Chen etal. (2012)

Juniper

CH1.3708O0.5637 N0.0049S0.0001

20584

84.55

18358

Chen et al. 2012)

*Computed from HHVdaf & VMdaf *HHVvm + FCdaf *HVfc where HVfc & 32765 kJ/kg of carbon (Chapter 4, Annamalai and Puri, 2007).

Boie basedHHVVM in kJ/kg ofVM released & [35160 YC + 116225 YH — 11090 YO + 6280 YN + 10465 YSFC * HVfc]/VM], where VM, FC… Yc, Yh. .. are either in mass fractions as received or %.

The type of FB used also had little effect on the ignition behavior of the fuel. The overall average ignition temperature for those fuels, which had coal present, is 566 K with a standard deviation of only 2.9%. The only appreciable difference in ignition point temperature is for those fuels that were pure biomass. For the pure biomass fuels, no matter the particle size, the average ignition temperature is 747 K with a standard deviation of 2.7%, probably due to lower quality of volatiles from biomass fuels.

It can be seen from Table 3.8 that coal volatiles are of high quality compared to volatiles from biomass.