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Outdoor PM2.5 air filtration: optimising indoor air quality and energy Cover

Outdoor PM2.5 air filtration: optimising indoor air quality and energy

Open Access
|Apr 2022

Figures & Tables

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Figure 1

World map presenting the investigated cities.

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Figure 2

Dedicated outdoor air system (DOAS) configurations for the three operation scenarios: baseline scenario (DOAS with a baseline filtration), optimum scenario (DOAS with an optimal filter grade) and bypass scenario (DOAS with a baseline filter plus a filter bypass).

Table 1

Filter grades, PM2.5 arrestance efficiencies and pressure drops for a ventilation airflow of 0.944 m3/s (during occupied hours).

FILTER-GRADE EN 779 (CEN 2012)FILTER-GRADE MERVPM2.5 ARRESTANCE EFFICIENCY (%)Δp¯ (Pa)
G4MERV 720%70
M5MERV 825%80
M6MERV 1030%97
F7MERV 1270%150
F8MERV 1480%203
F9MERV 1590%264
HEPAHEPA99.7%450

[i] Note: HEPA = high-efficiency particulate arrestance (filter); MERV = minimum efficiency reporting values.

Table 2

Total PM2.5 arrestance efficiencies and pressure drops for an outdoor air (OA) ventilation airflow of 0.944 m3/s (during occupied hours).

FILTER-GRADE EN 779 (CEN 2012)FILTER-GRADE MERVPM2.5 ARRESTANCE EFFICIENCY (%)Δp¯ (Pa)
M5 + F7MERV 8 + 1277.5%230
F7 + F7MERV 12 + 1291.0%300

[i] Note: MERV = minimum efficiency reporting values.

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Figure 3

Summary of the inputs to and outputs from the simulation engine’s inputs and outputs.

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Figure 4

Representative annual mean outdoor PM2.5 concentrations in the investigated cities.

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Figure 5

Outdoor and indoor PM2.5 concentrations in relation to outdoor air classifications (ODA) (EN 16798-3 2017) and corresponding filter grades for baseline scenario (air filtration according to EN 16798-3).

Note: Box plots indicate the minimum, 1st quartile, mean (black cross), median and 3rd quartile, maximum and outlier values. The cross-cutting red line indicates the threshold for the annual mean concentration (10 μg/m3) imposed by WHO (2006) guidelines.

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Figure 6

Indoor PM2.5 concentration in relation to outdoor air classifications (ODA) (EN 16798-3 2017) and as the result of the three air filtration scenarios.

Note: Box plots indicate the minimum, 1st quartile, mean (black cross), median and 3rd quartile, maximum and outlier values. The cross-cutting red line indicates the threshold for the annual mean concentration (10 μg/m3) imposed by WHO (2006) guidelines.

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Figure 7

Annual energy consumption of the fans to overcome the total pressure drops of the ventilation system as a result of the three different filtration scenarios.

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Figure 8

Change of the annual total fan’s energy consumption for the optimum and bypass scenarios relative to the baseline scenario.

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Figure 9

Map presenting the duration of time in a year when the filter bypass can be used at each investigated city.

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Figure 10

Ratio between average energy savings of the fan and the increase in indoor average PM2.5 levels [(kWh/m2 year)/(μg/m3)] for the optimum and bypass scenarios in each investigated city.

Note: Data in the city of Kampala were partially presented as the ΔE/ΔPM2.5 ratio and cannot be defined for the bypass scenario. The outdoor PM2.5 concentration was never <10 μg/m3, and the bypass was never activated. Hence, both ΔE and ΔPM2.5 were equal to zero.

DOI: https://doi.org/10.5334/bc.153 | Journal eISSN: 2632-6655
Language: English
Submitted on: Sep 10, 2021
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Accepted on: Mar 11, 2022
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Published on: Apr 6, 2022
Published by: Ubiquity Press
In partnership with: Paradigm Publishing Services
Publication frequency: 1 issue per year

© 2022 Evangelos Belias, Dusan Licina, published by Ubiquity Press
This work is licensed under the Creative Commons Attribution 4.0 License.