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Technical Papers

Determination of activated carbon fiber adsorption capacity for several common organic vapors: applications for respiratory protection

ORCID Icon, ORCID Icon & ORCID Icon
Pages 570-580 | Received 25 Jun 2021, Accepted 15 Sep 2021, Published online: 05 Jan 2022

Figures & data

Table 1. ACF media characteristics

Table 2. Challenge contaminant properties

Figure 1. Simplified experimental set-up.

Figure 1. Simplified experimental set-up.

Figure 2. Plots of 10% toluene breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm toluene.

Figure 2. Plots of 10% toluene breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm toluene.

Figure 3. Plots of 10% toluene breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm toluene.

Figure 3. Plots of 10% toluene breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm toluene.

Figure 4. Plots of 10% toluene breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm toluene.

Figure 4. Plots of 10% toluene breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm toluene.

Figure 5. Plots of 10% MEK breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm methyl ethyl ketone (MEK).

Figure 5. Plots of 10% MEK breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm methyl ethyl ketone (MEK).

Figure 6. Plots of 10% MEK breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm methyl ethyl ketone (MEK).

Figure 6. Plots of 10% MEK breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm methyl ethyl ketone (MEK).

Figure 7. Plots of 10% MEK breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm methyl ethyl ketone (MEK).

Figure 7. Plots of 10% MEK breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm methyl ethyl ketone (MEK).

Figure 8. Plots of 10% hexane breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm hexane.

Figure 8. Plots of 10% hexane breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm hexane.

Figure 9. Plots of 10% hexane breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm hexane.

Figure 9. Plots of 10% hexane breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm hexane.

Figure 10. Plots of 10% hexane breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm hexane.

Figure 10. Plots of 10% hexane breakthrough time in minutes for each ACF media type at successive bed depths. The challenge contaminant was 200 ppm hexane.

Table 3. Results of ACF surface area analysis

Table 4. Breakthrough experiments with 200 ppm Toluene as challenge contaminant

Table 5. Breakthrough experiments with 200 ppm MEK as challenge contaminant

Table 6. Breakthrough experiments with 200 ppm Hexane as challenge contaminant

Table 7. Maximum ACF bed depths and associated bed weights not in exceedance of 40 mm H20 when tested at a 10 cm/s velocity airflow. Also included are extrapolated 10% breakthrough times (Tb 10%) for each maximum bed weight

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