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Communication

Can We Vacuum Our Air Pollution Problem Using Smog Towers?

by
Sarath Guttikunda
* and
Puja Jawahar
Urban Emissions, New Delhi 110019, India
*
Author to whom correspondence should be addressed.
Atmosphere 2020, 11(9), 922; https://doi.org/10.3390/atmos11090922
Submission received: 29 July 2020 / Revised: 20 August 2020 / Accepted: 28 August 2020 / Published: 29 August 2020
(This article belongs to the Section Air Quality)
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Abstract

:
In November 2019, the Supreme Court of India issued a notification to all the states in the National Capital Region of Delhi to install smog towers for clean air and allocated INR 36 crores (~USD 5.2 million) for a pilot. Can we vacuum our air pollution problem using smog towers? The short answer is “no”. Atmospheric science defines the air pollution problem as (a) a dynamic situation where the air is moving at various speeds with no boundaries and (b) a complex mixture of chemical compounds constantly forming and transforming into other compounds. With no boundaries, it is unscientific to assume that one can trap air, clean it, and release into the same atmosphere simultaneously. In this paper, we outline the basics of atmospheric science to describe why the idea of vacuuming outdoor air pollution is unrealistic, and the long view on air quality management in Indian cities.

1. Introduction

Air pollution is a major health risk worldwide—outdoor PM2.5 (particulate matter) and Ozone pollution accounted for an estimated 3 million and 0.5 million premature deaths, respectively, and household (indoor) air pollution for an additional 1.6 million premature deaths [1]. Corresponding numbers for India are 680,000 for outdoor PM2.5, 145,000 for outdoor ozone, and 480,000 for household pollution. Similar estimates were presented by researchers and scientists from the Indian institutes [2,3,4,5,6]. In all the studies, the very young and the old are particularly vulnerable.
The year 2020 is an aberration in the pollution trends, with the COVID-19 lockdowns and a range of restrictions for all the sectors [7]. Across India, ambient air pollution levels improved as much as 50% compared to the annual trends for the same period in the previous year [8]. A summary of the data from all the cities with at least one continuous air monitoring station is included in the Supplementary Materials. Following the pandemic, epidemiological work on COVID-19 patients suggests that the risk of mortality is higher among the population exposed to chronic PM2.5 and NO2 pollution [9,10].
One key lesson from the COVID-19 lockdowns worldwide, is that air pollution can be reduced locally and globally by reducing the emissions at the sources. This was witnessed in the data from the ground-based monitors worldwide and satellite retrievals over India, China, Italy, and the United States [11,12,13]. The measures enacted during the lockdowns are unprecedented, but the results are evidence that we eventually need to control the emissions at the sources for “clean air”.
While the messages are clear that high air pollution is the leading cause of health impacts and “clean air” is only possible by addressing the emissions at the sources, in November 2019, the Supreme Court of India issued a notification to all the states in the National Capital Region of Delhi (NCR) to install smog towers. These giant filtering systems are being pursued as a control mechanism only in the absence of real action to control the emissions at the sources and the continuing incidence of high air pollution levels in Delhi and other major cities. Examples discussed in the notification for replication are (a) a 100 m high purification tower in Xi’an, China [14] and (b) experimental large vacuum cleaners called Wind Augmentation and Air Purifying Units (WAYU) were deployed in the cities of Delhi, Mumbai, and Bengaluru, with no operational details, and (c) a smaller version of the Xi’an smog tower in Delhi (Figure 1). The latter designs also include “mist makers” to initiate coagulation and induce wet scavenging of the particles. The units installed in Delhi and Mumbai were designed by the National Environmental Engineering Research Institute (NEERI) and Indian Institute of Technology (Mumbai) and inaugurated by the then Minister of Environment [15].
A fundamental question remains, “can we vacuum our air pollution problem using smog towers and mist makers”? The short answer is “no”. The idea of removing what is already in the air is unrealistic, given the dynamic nature of air pollution, which moves and transforms simultaneously. In this paper, we outline the basics of atmospheric science to describe why the idea of vacuuming outdoor air pollution is unscientific, and the long view on air quality management in Indian cities. In India, PM2.5 is considered the main criteria pollutant for environmental compliance and public health, and all of the discussion in this paper is about PM.

2. The Sciences

The definition of atmospheric science can be explained via the three basic sciences—Mathematics, Physics, and Chemistry.

2.1. Mathematics

Mathematics relates to the “quantification” of the problem. In a box model version of a city (Figure 2), the size of the city and the height of the inversion layer will determine the amount of air present at any given instance. The inversion layer is an invisible layer of air, which determines the total volume of air available for horizontal and vertical mixing. This height is determined by prevalent surface temperature, air temperature at the ground and upper layers, humidity levels, and land cover, all varying in time and space. There is seasonality associated with the inversion layer—highest during the summer months and lowest during the winter months. This is a typical trend for most of the inland cities in India [16]. The coastal cities like Chennai and Mumbai experience lesser variation across the seasons due to the constant presence of land–sea breeze.
Pollution (in the units of μg/m3) is defined as mass over volume, where mass is the emission load and volume is the amount of air present. In the summer months, a higher volume of air means more room for lateral and vertical mixing, and vice versa for the winter months. For the same amount of emissions in all the months, concentrations are bound to be higher in the winter months and lower in the summer months. For “clean air” and lower concentrations, the requirement is either higher inversion layer height or lower emissions. It is next to impossible to alter meteorology; however, reducing emissions should be relatively easy.
In the box model, we assumed that emissions remain constant over months. This is not true. Emissions are also seasonal, which in the case of India are higher in the winter months from space heating needs [17] along with a lowering in mixing height, further compounding the air pollution problem. A hypothetical case is illustrated in Table 1 for what could be the changes in the overall pollution when the city size expands, emissions halve or double, or for changes in the meteorological conditions. All the calculations assume a steady state condition. The worst-case scenario is when the emissions double and the mixing height drops to a quarter of the norm, resulting in a 700% increase in the overall pollution. During the winter haze episodes, areas between Punjab, Haryana, and Delhi experience these conditions [18,19]—emissions nearly double compared to summer months with the addition of agricultural residue burning and the onset of winter season requiring more biomass and coal combustion to support space heating, with a simultaneous drop in the surface and air temperatures. Typical day-time mixing layer heights are 1000–2000 m in the summer months and 100–200 m in the winter months. Typical night-time heights are half of this.
Mathematically, for a given set of seasonal patterns in meteorology, especially over the Indo-Gangetic plain, the best option is to cut the emissions at the sources and disperse the emissions to farther distances via better urban planning.

2.2. Physics

Physics relates to the “movement” of the problem. A popular saying is that “pollution knows no boundaries”. The box model assuming closed walls in Figure 2 and Table 1 is good to illustrate the point that emissions are key for any increase and decrease in pollution levels. Simultaneously, meteorology plays an important role in determining how much of those emissions stay in the box, determined by the horizontal wind components (U and V), or how much of those emissions will stay close to the surface, determined by the vertical wind component (W) (Figure 3).
This adds two new dimensions to the air pollution problem: (a) the air is not static over the city—between wind speeds of 1 m/s and 2 m/s, the latter is pushing twice the amount of air through the city boundaries; (b) the air from outside the boundary carries outside emissions, which add to the total emissions inside the city. Similarly, emissions from inside the city will be carried to a city downwind. This is called “long-range transport” of pollution—sometimes this is an exchange of pollution between the cities and sometimes between the states. For example, a city like Delhi is surrounded by satellite cities Gurugram (from the state of Haryana) in the West and Noida (from the state of Uttar Pradesh) in the East. There is constant movement of vehicles between these cities and in a map of urban built-up area, it is difficult to draw a closed box [20]. In this case, depending on the wind direction, emissions from each of these cities are affecting the others downwind.
The effect of long-range transport is also prominent during the seasonal dust storms (May–June) originating from the Middle East or the Thar desert in the state of Rajasthan [21], and agricultural residue burning (April–May and October–November) originating mostly from the states of Punjab and Haryana [22]. In both cases, seasonal wind speeds are high enough to pick up and push the emissions into the higher altitudes, support inter-state transport, and affect the pollution levels downwind. The overall known horizontal advection and vertical mixing schemes are more complex than described in this paper.
Guttikunda et al. (2019) [16] presents an analysis for 20 Indian cities, documenting contributions of emissions inside and outside the city airsheds. On average, 30% of the pollution observed in these cities originates outside the city limits. For cities in North India like Ludhiana, Amritsar, and Chandigarh, the long-range transport contribution is more than 50% on an annual basis.
The movement of the pollution also includes scavenging—dry deposition when the pollutants are in contact with a surface and wet deposition during the rains. The dry deposition rates for various pollutants are determined by the surface roughness, soil moisture content, and wind speeds. Under windy conditions and over dry surfaces, we have lesser deposition of the particulates, and vice versa on the trees with enough moisture on the leaves.

2.3. Chemistry

Chemistry relates to the “composition” of the problem—the critical one of the three sciences, as it links PM2.5, PM10, SO2, NO2, CO and ozone directly to all known health impacts. Of the six pollutants, the most critical is PM2.5, and its chemical composition is different in space and time [23,24]. While the first five pollutants are part of direct emissions, ozone is a secondary compound formed in the atmosphere in the presence of NOx and hydrocarbons.
A sample of PM2.5 can provide information not only on how much pollution there is, but also on the fuel origins of the mass on the filter. Figure 4 presents a summary of the key marker metals, elements, and compounds associated with major sources. There are overlaps between the sources and the ratio of the markers also vary significantly, which allows for statistically apportioning source contributions. These markers range from metals from direct combustion of fuels, like coal and diesel, to contributions from other gases, like SO2 forming sulphate aerosols (in a series of reactions involving ozone and some intermediate radicals), NOx forming nitrate aerosols and hydrocarbons forming secondary organic aerosols (via 500+ known reactions with ozone and intermediate radicals) [25,26]. Ozone is a by-product of these 500+ reactions. Most of the chemical transformation between gases and aerosols takes place during the long-range transport—in other words, a significant portion of the PM2.5 samples collected in the city are there because of the emissions originating outside the city [16]. The secondary nature of the PM2.5 originating from sources not likely within a city boundary, complicates the overall pollution control strategy.

3. Do Smog Towers Work?

For managing outdoor air pollution, the answer is still “no”. Atmospheric science defines the air pollution problem as (a) a dynamic situation where the air is moving at various speeds with no boundaries, and (b) a complex mixture of chemical compounds constantly forming and transforming into other compounds. With no boundaries, it is unscientific to assume that one can trap air, clean it, and release into the same atmosphere simultaneously. Expecting filtering units to provide any noticeable results at the community level is unrealistic. This is illustrated in a back-of-the-envelope calculation for Delhi (Table 2) using two pilots under consideration, (a) T1: a smog tower in Xi’an (China) designed to filter 10 million m3 of air every day; (b) T2: a smaller version of T1 piloted in Delhi’s Lajpat number market in January 2020, with a capacity of 600,000 m3/day.
For these calculations, we considered Delhi’s airshed, including its satellite cities Gurugram, Noida, Greater Noida, Ghaziabad, Faridabad, and Rohtak, covering an area of 7000 sq.km (~84 km × 84 km). Table 3 presents a summary of mixing heights, near surface temperature, and wind speeds for the year 2018. The average wind speed in the domain is 4 m/s (=14.4 km/h) in the summer months and 2 m/s (=7.2 km/h) in the winter months. Similarly, the average mixing heights are 1000 m and 200 m, respectively. This translates to an average exchange of 1,209,600 million m3/h and 120,960 million m3/h of air in the summer and winter months, respectively (city side * speed * mixing height)—this calculation assumes a steady state with constant flow of air and no vertical mixing.
The concept of vacuum cleaning has worked in closed environments. For example, (a) in a closed room, if the doors and windows remain shut, then an air purifier is an efficient way to clean the air [27]. This emulates a box model containing a constant amount of air with limited movement. When purifying the closed room, all the dust is collected on a filter, which requires either cleaning or replacement after some time, and a clean disposal of the dust collected. During high pollution days, the frequency of cleaning and replacement is more (b) at the end of a combustion unit, with flue gas moving at a constant flow rate in one direction, like a power plant boiler with a chimney. The system will include an inlet for polluted air and an outlet for cleaned air. This system is designed to trap emissions at the source, before entering the atmosphere at the top of the chimney. In this case, all the dust (fly ash) from the cyclone bags or electrostatic precipitators or filters also need clean collection and disposal [28]. (c) In a subway tunnel, where the air flow is limited and prone to increased exposure levels, a purifier will induce an artificial air flow, diluting the incoming air, and thus reducing the overall exposure levels. None of these examples present the use of filtering systems to clean the air permanently.
In an outdoor environment, at best these systems are a demonstration of a filtering system with negligible efficiencies (Table 2), whose performance at a power plant, or at any of the end of the pipe applications where the emissions originate, is the most efficient.

4. Taking a Long View on Air Quality Management

The air pollution problem in India is year-round [29,30]. The winter months (November, December, January, and February) are the worst, with stagnant meteorology stifling the lateral and vertical movement of pollution, low temperatures pushing the need for space heating, which is mostly met using biomass [17], and some seasonal emissions from agricultural residue burning [22]. These are in addition to the all-year combustion of petrol, diesel, gas, coal, and waste in the transport, industrial, and domestic sectors, and resuspended from the construction activities and traffic on the roads. The monsoon months (June, July, and August) are the best, with enhanced wet scavenging across the country.
The air pollution problem in India is not limited to the cities. An analysis of annual average PM2.5 concentrations, using a combination of satellite retrievals and global emission inventories for the period of 1998–2018, suggests that 60% of the districts do not meet the national ambient standard of 40 μg/m3 and 98% do not meet the WHO guideline of 10 μg/m3 [31]. Typically, North Indian districts are more adversely affected from chronic air pollution.
The judicial system played a central role in several air pollution decisions in India:
  • In 1998, the Supreme Court ruled to convert public transport buses and para-transit vehicles to run on compressed natural gas (CNG). This was a public interest litigation, which also led to other emission control measures in Delhi [32,33]. CNG conversion was the most successful for the transport sector and, in the early 2000s, the city of Delhi witnessed a reduction in emissions and pollution. However, the scale of replacement has not been replicated in any other Indian city since, and the overall bus fleet composition in Delhi has remained the same irrespective of the growing demand [34].
  • In 2015, three toddlers filed a public interest ligation in the Supreme Court of India, to request a full ban on the sale of fireworks. In an apparent victory for cleaner air, in November 2016, the Court ordered a complete ban on the sale of firecrackers in the NCR. What seemed to be a progressive measure was, however, annulled by a ‘temporary’ ruling, when the ban was lifted with the caveat that the ban will be reinstituted if there is evidence that fireworks are a major pollutant during the festive season.
  • In 2018, the Supreme Court ruled in favour of the introduction of BS-VI standard vehicles nationwide, starting 1 April 2020, instead of the original plan for 2025 under the auto fuel policy.
  • In 2019, the Supreme Court ruled in favour of an immediate ban on the use of pet coke (with high sulphur content) in all industries in the NCR by June 2019.
Time and again, judicial interventions have resulted in putting pressure on the respective agencies to implement long-term measures for long-term benefits.
Non-judicial interventions proposed and implemented for improving air quality and health are:
  • In 2015, the Government of India launched the smart cities program for 100 cities. While air quality was not explicitly mentioned as the environment indicator, the proposed activities were designed to benefit overall air quality. These included a ranking system to evaluate the waste management programs, road cleaning, and street greening in the cities.
  • In December 2016, Delhi proposed the Graded Responsibility Action Plan (GRAP), a series of measures to enforce under poor, very poor, severe and emergency levels of pollution [35]. These decisions are made based on a 48-h running average of the air quality index, calculated using hourly PM2.5 and PM10 levels. This plan is now an example for other cities in the Indo-Gangetic Plain to replicate. A missing link in the program is an independent body with teeth to clamp down on offending polluters across states.
  • The Ministry of Petroleum and Natural Gas took an important first step with the Pradhan Mantri Ujjwala Yojana (PMUY) in 2016, providing liquified petroleum gas (LPG) connections to the poorest households. As of September 2019, the PMUY has connected 80 million beneficiaries by directly transferring subsidies to the bank accounts of women in these households and improving indoor and outdoor health [36]. While the number of connections is on the rise, there are barriers to LPG uptake, which need to be addressed [37].
  • In April 2015, a parliamentary standing committee proposed new emission standards for all the coal-fired thermal power plants. These standards were ratified in December 2015, tightening the standards for PM and introducing standards for SO2, NOx, and mercury for the first time. If implemented in full, these standards are expected to yield a 50% drop in the PM2.5 (primary and secondary) pollution from these plants [38,39]. All the power plants are expected to comply in 2022.
  • Financial support from the Government of India for the Faster Adoption and Manufacturing of Electric Vehicles (FAME) program, made electric vehicles (EVs) a new policy and economic choice for small- and large-scale applications. The program now includes subsides for two-, three-, and four-wheelers and the introduction of EV buses into the public transportation system. The Delhi transport corporation is expected to receive its first 1000 buses in 2021–2022 and the Delhi government is promoting EVs to account for 25% of new registrations by 2024.
In 2019, the Ministry of Environment, Forest and Climate Change (MoEFCC) announced the National Clean Air Programme (NCAP) for 122 non-attainment cities from 20 states and three union territories [40]. Under the NCAP, every city is required to prepare a list of actions necessary to reduce their PM2.5 levels by 20–30%, compared to 2017, by 2024. The authors of [41] present a review of these action plans, summarizing the key action points that all the cities want to implement as: (a) augmenting public transport, (b) eradicating road and construction dust, (c) abolishing open waste burning, (d) promoting clean cooking, (e) implementing industrial emission standards, (f) increasing ambient monitoring capacity, and (g) raising public awareness. While improving ambient monitoring capacity and raising public awareness are short-term activities (with long-term maintenance), all others are part of long-term planning, designed to reduce emissions at the sources.
Following the approval of the 102 NCAP city action plans by MoEFCC, the prevalence of pollution episodes in October–November 2019, and limited action in the cities to counter air pollution, the Supreme Court bench again intervened to demand the installation of smog towers and allocated INR 36 crores (~USD 5.2 million) for the replication of the Xi’an’s smog tower design in Delhi. In August 2020, a memorandum of understanding was signed by the Indian Institute of Technology (Bombay) to design and construct the system. Wasting the judicial power by implementing band aid measures is not only unscientific, but also a waste of limited financial and technical resources. We cannot vacuum our way to “clean air”.

5. Conclusions

The city clean air action plans provide proof that there is enough technical know-how on how much air pollution there is, the key sectors that need attention, the institutional requirements to implement long-term strategies, and the ways in which they can be addressed [40,41]. These action plans need institutional and financial support. At the institutional level, there are three tasks that need immediate attention, where the judiciary can help to move the strategies forward: (1) Personnel and Capacity— CPCB and the state pollution control boards are too understaffed to perform auditory and scientific operations. (2) Monitoring infrastructure—as of June 2020, there are 230 continuous monitoring stations operated and maintained by CPCB in 124 (of 715) districts. More than half of these districts have only one station and 70 monitors are in the vicinity of the NCR, which demonstrates the bias in measuring and managing air pollution outside the big cities like Delhi. To spatially and temporally represent the air pollution problem, India requires at least 4000 continuous air quality monitoring systems (2800 in the urban areas and 1200 in the rural areas). (3) Information support—air quality management requires information on emission loads, source contributions, costs and benefits of interventions, and a way to prioritize actions. The funds allocated by the Supreme Court for temporary interventions like testing smog towers are most useful for implementing these permanent solutions.

Supplementary Materials

The following are available online at https://www.mdpi.com/2073-4433/11/9/922/s1, Table S1: Summary of air quality in 124 cities in India for the periods before and during the 4 COVID-19 lockdowns.

Author Contributions

Conceptualization, writing, and editing—S.G. and P.J.; Methodology, resources, and visualization—S.G. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. GBD. Global Burden of Disease. Available online: https://vizhub.healthdata.org/gbd-compare/ (accessed on 29 July 2020).
  2. Chowdhury, S.; Dey, S. Cause-specific premature death from ambient PM2.5 exposure in India: Estimate adjusted for baseline mortality. Environ. Int. 2016, 91, 283–290. [Google Scholar] [CrossRef] [PubMed]
  3. Ghude, S.D.; Chate, D.M.; Jena, C.; Beig, G.; Kumar, R.; Barth, M.C.; Pfister, G.G.; Fadnavis, S.; Pithani, P. Premature mortality in India due to PM2.5 and ozone exposure. Geophys. Res. Lett. 2016, 43, 4650–4658. [Google Scholar] [CrossRef] [Green Version]
  4. Balakrishnan, K.; Dey, S.; Gupta, T.; Dhaliwal, R.S.; Brauer, M.; Cohen, A.J.; Stanaway, J.D.; Beig, G.; Joshi, T.K.; Aggarwal, A.N.; et al. The impact of air pollution on deaths, disease burden, and life expectancy across the states of India: The Global Burden of Disease Study 2017. Lancet Planet. Health 2019, 3, e26–e39. [Google Scholar] [CrossRef] [Green Version]
  5. Saini, P.; Sharma, M. Cause and Age-specific premature mortality attributable to PM2.5 Exposure: An analysis for Million-Plus Indian cities. Sci. Total Environ. 2020, 710, 135230. [Google Scholar] [CrossRef]
  6. Sahu, S.K.; Sharma, S.; Zhang, H.; Chejarla, V.; Guo, H.; Hu, J.; Ying, Q.; Xing, J.; Kota, S.H. Estimating ground level PM2.5 concentrations and associated health risk in India using satellite based AOD and WRF predicted meteorological parameters. Chemosphere 2020, 255, 126969. [Google Scholar] [CrossRef]
  7. WIRE. India: Why Was Daytime Ozone Pollution Higher During the Lockdowns? Available online: https://science.thewire.in (accessed on 29 July 2020).
  8. CPCB. Impact of Lockdowns 25th March to 15th April on Air Quality. In Central Pollution Control Board, Ministry of Environmental Forests and Climate Change; The Government of India: New Delhi, India, 2020. [Google Scholar]
  9. Adhikari, A.; Yin, J. Short-Term Effects of Ambient Ozone, PM2.5, and Meteorological Factors on COVID-19 Confirmed Cases and Deaths in Queens, New York. Int. J. Environ. Res. Public Health 2020, 17, 4047. [Google Scholar] [CrossRef]
  10. Wu, X.; Nethery, R.C.; Sabath, B.M.; Braun, D.; Dominici, F. Exposure to air pollution and COVID-19 mortality in the United States: A nationwide cross-sectional study. medRxiv 2020. [Google Scholar] [CrossRef] [Green Version]
  11. Berman, J.D.; Ebisu, K. Changes in U.S. air pollution during the COVID-19 pandemic. Sci. Total Environ. 2020, 739, 139864. [Google Scholar] [CrossRef]
  12. Marlier, M.E.; Xing, J.; Zhu, Y.; Wang, S. Impacts of COVID-19 response actions on air quality in China. Environ. Res. Commun. 2020, 2, 075003. [Google Scholar] [CrossRef]
  13. Filippini, T.; Rothman, K.J.; Goffi, A.; Ferrari, F.; Maffeis, G.; Orsini, N.; Vinceti, M. Satellite-detected tropospheric nitrogen dioxide and spread of SARS-CoV-2 infection in Northern Italy. Sci. Total Environ. 2020, 739, 140278. [Google Scholar] [CrossRef]
  14. Cyranoski, D. China tests giant air cleaner to combat smog. Nature 2018, 555, 7695. [Google Scholar] [CrossRef] [PubMed]
  15. DST. DST’s Initiatives Tackle Air Pollution Hazard—Wind Augmentation and Air Purifying Unit (WAYU); Department of Science and Technology, The Government of India: New Delhi, India, 2018.
  16. Guttikunda, S.K.; Nishadh, K.A.; Jawahar, P. Air pollution knowledge assessments (APnA) for 20 Indian cities. Urban. Clim. 2019, 27, 124–141. [Google Scholar] [CrossRef]
  17. Chowdhury, S.; Dey, S.; Guttikunda, S.; Pillarisetti, A.; Smith, K.R.; Di Girolamo, L. Indian annual ambient air quality standard is achievable by completely mitigating emissions from household sources. Proc. Natl. Acad. Sci. USA 2019, 116, 10711–10716. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  18. Liu, T.; Marlier, M.E.; Karambelas, A.; Jain, M.; Singh, S.; Singh, M.K.; Gautam, R.; DeFries, R.S. Missing emissions from post-monsoon agricultural fires in northwestern India: Regional limitations of MODIS burned area and active fire products. Environ. Res. Commun. 2019, 1, 011007. [Google Scholar] [CrossRef]
  19. Saikawa, E.; Panday, A.; Kang, S.; Gautam, R.; Zusman, E.; Cong, Z.; Somanathan, E.; Adhikary, B. Air Pollution in the Hindu Kush Himalaya. In The Hindu Kush Himalaya Assessment: Mountains, Climate Change, Sustainability and People; Wester, P., Mishra, A., Mukherji, A., Shrestha, A.B., Eds.; Springer International Publishing: Cham, Switzerland, 2019; pp. 339–387. [Google Scholar] [CrossRef]
  20. Goel, R.; Guttikunda, S.K. Evolution of on-road vehicle exhaust emissions in Delhi. Atmos. Environ. 2015, 105, 78–90. [Google Scholar] [CrossRef]
  21. Sarkar, S.; Chauhan, A.; Kumar, R.; Singh, R.P. Impact of Deadly Dust Storms (May 2018) on Air Quality, Meteorological, and Atmospheric Parameters Over the Northern Parts of India. GeoHealth 2019, 3, 67–80. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  22. Jethva, H.; Chand, D.; Torres, O.; Gupta, P.; Lyapustin, A.; Patadia, F. Agricultural Burning and Air Quality over Northern India: A Synergistic Analysis using NASA’s A-train Satellite Data and Ground Measurements. Aerosol Air Qual. Res. 2018, 18, 1756–1773. [Google Scholar] [CrossRef] [Green Version]
  23. Pathak, A.K.; Sharma, M.; Nagar, P.K. A framework for PM2.5 constituents-based (including PAHs) emission inventory and source toxicity for priority controls: A case study of Delhi, India. Chemosphere 2020, 255, 126971. [Google Scholar] [CrossRef]
  24. Van Donkelaar, A.; Martin, R.V.; Li, C.; Burnett, R.T. Regional Estimates of Chemical Composition of Fine Particulate Matter Using a Combined Geoscience-Statistical Method with Information from Satellites, Models, and Monitors. Environ. Sci. Technol. 2019, 53, 2595–2611. [Google Scholar] [CrossRef] [Green Version]
  25. SAPRC-18. The SAPRC-18 Atmospheric Chemical Mechanism; University of California: Riverside, CA, USA; Available online: https://intra.engr.ucr.edu/~carter/SAPRC/18/ (accessed on 29 July 2020).
  26. Stockwell, W.R.; Saunders, E.; Goliff, W.S.; Fitzgerald, R.M. A perspective on the development of gas-phase chemical mechanisms for Eulerian air quality models. J. Air Waste Manag. Assoc. 2020, 70, 44–70. [Google Scholar] [CrossRef]
  27. Vyas, S.; Srivastav, N.; Spears, D. An experiment with air purifiers in Delhi during Winter 2015–2016. PLoS ONE 2016, 11, e0167999. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  28. Nihalani, S.; Mishra, Y.; Meeruty, A. Handling and utilisation of fly ash from thermal power plants. In Circular Economy and Fly Ash Management; Springer: Berlin/Heidelberg, Germany, 2020; pp. 1–11. [Google Scholar]
  29. Pant, P.; Lal, R.M.; Guttikunda, S.K.; Russell, A.G.; Nagpure, A.S.; Ramaswami, A.; Peltier, R.E. Monitoring particulate matter in India: Recent trends and future outlook. Air Qual. Atmos. Health 2019, 12, 45–58. [Google Scholar] [CrossRef]
  30. Guttikunda, S.K.; Goel, R.; Pant, P. Nature of air pollution, emission sources, and management in the Indian cities. Atmos. Environ. 2014, 95, 501–510. [Google Scholar] [CrossRef]
  31. Hammer, M.S.; van Donkelaar, A.; Li, C.; Lyapustin, A.; Sayer, A.M.; Hsu, N.C.; Levy, R.C.; Garay, M.J.; Kalashnikova, O.V.; Kahn, R.A.; et al. Global Estimates and Long-Term Trends of Fine Particulate Matter Concentrations (1998–2018). Environ. Sci. Technol. 2020, 54, 7879–7890. [Google Scholar] [CrossRef]
  32. Narain, U.; Bell, R.G. Who changed Delhi’s air? Econ. Political Wkly. 2006, 1584–1588. [Google Scholar] [CrossRef]
  33. Mehta, R. History, Politics, and Technology of CNG-Diesel Bus Switch in Delhi. In Proceedings of the Transportation, Land Use, and Environment Workshop Held in Pune, India; Central Institute of Road Transport: Pune, India, 2001; p. 151. [Google Scholar]
  34. Goel, R.; Guttikunda, S.K. Role of urban growth, technology, and judicial interventions on vehicle exhaust emissions in Delhi for 1991–2014 and 2014–2030 periods. Environ. Dev. 2015, 14, 6–21. [Google Scholar] [CrossRef]
  35. WIRE. How Do We Improve Delhi’s Graded Responsibility Action Plan for Better Air Quality? Available online: https://science.thewire.in (accessed on 10 August 2020).
  36. Pillarisetti, A.; Ghorpade, M.; Madhav, S.; Dhongade, A.; Roy, S.; Balakrishnan, K.; Sankar, S.; Patil, R.; Levine, D.I.; Juvekar, S.; et al. Promoting LPG usage during pregnancy: A pilot study in rural Maharashtra, India. Environ. Int. 2019, 127, 540–549. [Google Scholar] [CrossRef] [PubMed]
  37. Gupta, A.; Vyas, S.; Hathi, P.; Khalid, N.; Srivastav, N.; Spears, D.; Coffey, D. Persistence of Solid Fuel Use in Rural North India. Econ. Political Wkly. 2020, 55, 55. [Google Scholar]
  38. Guttikunda, S.; Jawahar, P.; Goenka, D. Regulating air pollution from coal-fired power plants in India. Econ. Political Wkly. 2015, 50, 62–67. [Google Scholar]
  39. Cropper, M.L.; Guttikunda, S.; Jawahar, P.; Lazri, Z.; Malik, K.; Song, X.-P.; Yao, X. Applying Benefit-Cost Analysis to Air Pollution Control in the Indian Power Sector. J. Benefit Cost Anal. 2018, 10, 185–205. [Google Scholar] [CrossRef] [Green Version]
  40. NCAP. National Clean Air Programme. In Central Pollution Control Board; Ministry of Environmental Forests and Climate Change, The Government of India: New Delhi, India, 2019. [Google Scholar]
  41. Ganguly, T.; Kurinji, L.S.; Guttikunda, S. How robust are urban India’s clean air plans. In An Assessment of 102 Plans; Council on Energy, Environment and Water: New Delhi, India, 2020. [Google Scholar]
Atmosphere 11 00922 g001 550
Figure 1. Examples of ambient filtering systems: (a) a smog tower from Xi’an, China, (Image edited from South China Morning Post), (b) a Wind Augmentation and Air Purifying Unit (WAYU) in Delhi, and (c) a smaller version of Xi’an’s filtering system in Delhi.
Figure 1. Examples of ambient filtering systems: (a) a smog tower from Xi’an, China, (Image edited from South China Morning Post), (b) a Wind Augmentation and Air Purifying Unit (WAYU) in Delhi, and (c) a smaller version of Xi’an’s filtering system in Delhi.
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Figure 2. Depiction of a box model pollution calculation with varying inversion heights (a) for summer months and (b) for winter months.
Figure 2. Depiction of a box model pollution calculation with varying inversion heights (a) for summer months and (b) for winter months.
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Figure 3. Three-dimensional motion of air through a city.
Figure 3. Three-dimensional motion of air through a city.
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Figure 4. Key metal and ion markers of various sources contributing to PM2.5.
Figure 4. Key metal and ion markers of various sources contributing to PM2.5.
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Table
Table 1. A hypothetical pollution calculation for a city using a steady state box model method. W = width of the city; L = length of the city; H = mixing height; E = emissions.
Table 1. A hypothetical pollution calculation for a city using a steady state box model method. W = width of the city; L = length of the city; H = mixing height; E = emissions.
Study and InstitutionWLHEPollution%Change
Base case, all as usual1.01.01.01.01.00%
City size doubles in width and length and no change in the emissions2.02.01.01.00.25−75%
Emission doubles, everything else is the same1.01.01.02.02.0+100%
Mixing height doubles, everything else is the same1.01.02.01.00.5−50%
Mixing height halves, everything else is the same1.01.00.51.02.0+100%
Emission doubles and mixing height halves1.01.00.52.04.0+300%
Emission doubles and mixing height is one quarter1.01.00.252.08.0+700%
Emission halves and everything else is the same1.01.01.00.50.5−50%
Table
Table 2. Outdoor air pollution filtering efficiency of the smog towers in Delhi’s airshed.
Table 2. Outdoor air pollution filtering efficiency of the smog towers in Delhi’s airshed.
VariableDelhi’s AirshedT1: Xi’an Smog TowerT2: Delhi’s 2020 Pilot
Filtering capacity under full implementation (m3/h) 400,00025,000
Average airshed volume (m3/h), calculated using inputs from Table 31,209,600 million in the summer 120,960 million in the winter
Filtering efficiency as the amount of air filtered in one hour 0.000033% in the summer and 0.00033% in the winter0.000002% in the summer and 0.00002% in the winter
Number of towers required at full capacity 3,024,000 units in the summer and 302,400 units in the winter50,000,000 units in the summer and 5,000,000 units in the winter
Unit costThe Supreme Court of India allocated INR 36 crores (~USD 5.2 million) for replication of T1Unknown; reported pilot cost is USD 10 millionINR 700,000 (~USD 10,000) + operations and maintenance
Required capital cost for full implementation in Delhi USD 15,725 billionUSD 500 billion
Required operations and maintenance costs for full implementation in Delhi HIGHHIGH
Table
Table 3. Summary of all day (AD), daytime (DT), and nighttime (NT) averages (± standard deviations) of mixing heights (MH in m), near surface temperature (T in °C), and near surface wind speeds (WS in m/s) by month. Data is extracted from Weather Research Forecasting (WRF) model simulations using the National Centers for Environmental Prediction (NCEP) reanalysis fields for the year 2018.
Table 3. Summary of all day (AD), daytime (DT), and nighttime (NT) averages (± standard deviations) of mixing heights (MH in m), near surface temperature (T in °C), and near surface wind speeds (WS in m/s) by month. Data is extracted from Weather Research Forecasting (WRF) model simulations using the National Centers for Environmental Prediction (NCEP) reanalysis fields for the year 2018.
VariableJanuaryFebruaryMarchAprilMayJuneJulyAugustSeptemberOctoberNovemberDecember
MH–AD298 ± 58516 ± 94926 ± 1981075 ± 2541243 ± 3071054 ± 244573 ± 240505 ± 152462 ± 123501 ± 91350 ± 73286 ± 71
MH–DT557 ± 118974 ± 1871801 ± 3932066 ± 5012377 ± 6401855 ± 485994 ± 450906 ± 269827 ± 239959 ± 184651 ± 129534 ± 140
MH–NT39 ± 857 ± 5651 ± 1884 ± 45109 ± 60254 ± 124153 ± 85104 ± 5897 ± 10543 ± 1350 ± 3338 ± 8
T–DT18.9 ± 1.824.2 ± 2.830.5 ± 2.635.5 ± 2.439.4 ± 2.739.0 ± 3.233.9 ± 2.933.0 ± 2.131.4 ± 2.230.0 ± 1.625.3 ± 1.518.8 ± 2.2
T–NT9.9 ± 1.515.3 ± 2.519.6 ± 1.826.3 ± 2.231.1 ± 1.834.0 ± 2.330.6 ± 2.129.3 ± 1.326.5 ± 1.121.8 ± 1.817.5 ± 1.911.1 ± 2.8
WS–AD2.7 ± 0.72.8 ± 0.93.1 ± 0.63.8 ± 0.83.7 ± 0.94.5 ± 1.23.1 ± 0.72.7 ± 0.72.8 ± 0.92.5 ± 0.52.7 ± 0.72.4 ± 0.6

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Guttikunda, S.; Jawahar, P. Can We Vacuum Our Air Pollution Problem Using Smog Towers? Atmosphere 2020, 11, 922. https://doi.org/10.3390/atmos11090922

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Guttikunda S, Jawahar P. Can We Vacuum Our Air Pollution Problem Using Smog Towers? Atmosphere. 2020; 11(9):922. https://doi.org/10.3390/atmos11090922

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Guttikunda, Sarath, and Puja Jawahar. 2020. "Can We Vacuum Our Air Pollution Problem Using Smog Towers?" Atmosphere 11, no. 9: 922. https://doi.org/10.3390/atmos11090922

APA Style

Guttikunda, S., & Jawahar, P. (2020). Can We Vacuum Our Air Pollution Problem Using Smog Towers? Atmosphere, 11(9), 922. https://doi.org/10.3390/atmos11090922

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