| Literature DB >> 34221243 |
Samuele Marinello1, Maria Angela Butturi2, Rita Gamberini1,2.
Abstract
The health emergency linked to the spread of COVID-19 has led to important reduction in industrial and logistics activities, as well as to a drastic changes in citizens' behaviors and habits. The restrictions on working activities, journeys and relationships imposed by the lockdown have had important consequences, including for environmental quality. This review aims to provide a structured and critical evaluation of the recent scientific bibliography that analyzed and described the impact of lockdown on human activities and on air quality. The results indicate an important effect of the lockdown during the first few months of 2020 on air pollution levels, compared to previous periods. The concentrations of particulate matter, nitrogen dioxide, sulfur dioxide and carbon monoxide have decreased. Tropospheric ozone, on the other hand, has significantly increased. These results are important indicators that can become decision drivers for future policies and strategies in industrial and logistics activities (including the mobility sector) aimed at their environmental sustainability. The scenario imposed by COVID-19 has supported the understanding of the link between the reduction of polluting emissions and the state of air quality and will be able to support strategic choices for the future sustainable growth of the industrial and logistics sector.Entities:
Keywords: COVID‐19; COVID‐19 conseguences; air quality; atmospheric pollutants; environmental impact; lockdown
Year: 2021 PMID: 34221243 PMCID: PMC8237064 DOI: 10.1002/ep.13672
Source DB: PubMed Journal: Environ Prog Sustain Energy ISSN: 1944-7442 Impact factor: 2.824
FIGURE 1Emissions of the main air pollutants by sector group in the EEA‐33 [Colour figure can be viewed at wileyonlinelibrary.com]
Research and selection protocol
| A Database | ||||
|---|---|---|---|---|
| A1. | ScienceDirect | |||
| A2. | Scopus | |||
| B Search criteria | ||||
| B1. | Journal | All | ||
| B2. | Year | All | ||
| B3. | Article type | All | ||
| B4. | Date of search | 10th November 2020 | ||
| C Keywords for papers identification | ||||
| Group A | Group B | |||
| COVID‐19 | Air pollution | |||
| Lockdown | Air quality | |||
| SARS‐CoV‐2 | AND | Environmental impact | ||
| NO2 | ||||
| PM10 | ||||
| D Steps for material selection | ||||
| D1. | Duplicate removal | |||
| D2. | Keywords and highlights assessment | |||
| D3. | Application of inclusion criteria on the content of the text | |||
| D3.1 | Treats the air quality of specific areas | OR | ||
| D3.2 | Assess the effect of COVID‐19 | OR | ||
| D3.3 | It evaluate the results quantitatively | |||
| D4. | Full text assessment | |||
| E Other paper sources | ||||
| E1. | From informal approach | |||
| E2. | From browsing method | |||
| F Descriptive analysis | ||||
| Year | ||||
| Journal | ||||
| Country type | ||||
| Research paper | ||||
| Review | ||||
| Others | ||||
| G Case studies analysis | ||||
| Location of the case studies | Location of the case studies | |||
| Impact of lockdown on logistics and industrial/economic activities | Impact of lockdown on logistics and industrial/economic activities | |||
Characterization of case studies
| AMERICAS | ||
|---|---|---|
| Continent or country | USA |
|
| Canada |
| |
| Colombia |
| |
| Argentina |
| |
| Region | California |
|
| Some US states |
| |
| Ontario region |
| |
| City | New York |
|
| Los Angeles |
| |
| Somerville |
| |
| Mexico city |
| |
| Rio de Janeiro |
| |
| Sao Paulo |
| |
| Bogotá |
| |
| Medellín |
| |
| Quito |
| |
| Lima |
| |
| 12 Ecuadorian cities |
| |
| ASIA AND OCEANIA | ||
| Continent or country | Asia |
|
| India |
| |
| China |
| |
| Japan |
| |
| Korea |
| |
| Bangladesh |
| |
| Australia |
| |
| Region | YRD region |
|
| Beijing‐Tianjin‐Hebei region |
| |
| Regions of India |
| |
| Hat Yai region |
| |
| City | Shanghai |
|
| Beijing |
| |
| Wuhan |
| |
| Guangzhou |
| |
| Shijiazhuang |
| |
| Hangzhou |
| |
| Some Chinese cities |
| |
| Seoul |
| |
| Daegu |
| |
| Tokyo |
| |
| Hong Kong |
| |
| New Delhi |
| |
| Mumbai |
| |
| Chennai |
| |
| Ghaziabad |
| |
| Chandigarh |
| |
| Ahmedabad |
| |
| Gujarat |
| |
| Kolkata |
| |
| Some Indian cities |
| |
| Dubai |
| |
| Tehran |
| |
| Baghdad |
| |
| Kathmandu |
| |
| Almaty |
| |
| Chittagong |
| |
| Dhaka city |
| |
| EUROPE | ||
| Continent or country | Europe |
|
| Spain |
| |
| Italy |
| |
| France |
| |
| Germany |
| |
| UK |
| |
| Region | Lombardy region |
|
| Veneto region |
| |
| Emilia‐Romagna region |
| |
| City | London |
|
| Paris |
| |
| Barcelona |
| |
| Madrid |
| |
| Zaragoza |
| |
| Valencia |
| |
| 11 Spanish cities |
| |
| Berlin |
| |
| Düsseldorf |
| |
| Moscow |
| |
| Graz |
| |
| Milan |
| |
| Rome |
| |
| Turin |
| |
| Florence |
| |
| Padova |
| |
| Pisa |
| |
| Lucca |
| |
| Brescia |
| |
| Palermo |
| |
| 5 Polish cities |
| |
| Istanbul |
| |
| Athens |
| |
| Nice |
| |
| AFRICA | ||
| Continent or country | Egypt |
|
| City | Salé City |
|
| Johannesburg |
| |
| INTERNATIONAL | ||
| Various international cities |
| |
FIGURE 2Spatial coverage of the case studies available in literature [Colour figure can be viewed at wileyonlinelibrary.com]
FIGURE 3Consequences of the lockdown on logistic and industrial activities [Colour figure can be viewed at wileyonlinelibrary.com]
Results from case studies: pollutants analyzed by each study [Color table can be viewed at wileyonlinelibrary.com]
| Reference | Pollutant | ||||||
|---|---|---|---|---|---|---|---|
| PM10 | PM2.5 | NO2 | SO2 | CO | O3 | Others | |
|
| X | X | X | ||||
|
| X | X | X | ||||
|
| X | −65% | |||||
|
| X | X | −36% | X | X | X | |
|
| −13% / ‐86% | ||||||
|
| X | X | NO, NOx | ||||
|
| X | X | X | X | X | X | |
|
| −43% | −31% | −18% | −10% | Factor of 1.5–2 | ||
|
| |||||||
|
| X | −25% | |||||
|
| −12% | ||||||
|
| X | −8% | X | X | +14% | ||
|
| X | X | |||||
|
| X | ||||||
|
| X | X | X | ||||
|
| X | X | X | X | X | ||
|
| X | X | X | ||||
|
| X | ||||||
|
| X | X | X | X | X | ||
|
| −49% | −37% | |||||
|
| −31% | −39% | |||||
|
| −29% | −50% | X | X | |||
|
| X | X | X | X | X | X | NOx, Benzene |
|
| −2% / ‐70% | ||||||
|
| X | ||||||
|
| X | X | X | X | X | ||
|
| X | X | X | X | |||
|
| −45% | −46% | −61% | ||||
|
| −44% | −40% | −60% | ||||
|
| X | ||||||
|
| −9% / ‐21% | −11% / ‐26% | −10% / ‐19% | X | |||
|
| X | X | −12% / ‐60% | X | X | ||
|
| X | X | |||||
|
| −19% / ‐83% | −71% | −4% | HCHO | |||
|
| X | ||||||
|
| −60% | −60% | −40% | −40% | |||
|
| −30% | −17% | |||||
|
| −35% | −35% | |||||
|
| −10% | −17% | −16% | ||||
|
| −15% | −8% | −6% | +13% | |||
|
| X | ||||||
|
| −90% | ||||||
|
| X | X | X | X | X | X | |
|
| Ultrafine particle | ||||||
|
| −40% | −43% | +7% | ||||
|
| −35% | −45% | −20% | X | −17% | X | |
|
| −31% | −32% | −64% | −20% | −31% | ||
|
| X | −12% | |||||
|
| −21% | −35% | X | −49% | +15% | BTEX | |
|
| X | X | −45% | ||||
|
| −10% / ‐54% | ||||||
|
| −55% | −49% | −60% | −19% | |||
|
| X | X | Aerosol | ||||
|
| X | X | |||||
|
| −32% | −45% | −20% | ||||
|
| X | ||||||
|
| −30% | −60% | −20% | −42% | NO, NOx, CO2, OC, EC | ||
|
| −14% / ‐20% | −7% / ‐16% | −23% / ‐37% | −2% / ‐20% | −7% / ‐11% | +10% / +27% | |
|
| −19% | −16% | −25% | ||||
|
| X | X | X | X | |||
|
| −14% | −41% | +34% | ||||
|
| −50% | −50% | X | X | NH3 | ||
|
| X | X | −57% | X | −30% | NO, NH3 | |
|
| X | X | X | X | X | X | |
|
| −32% | −40% | −13% | X | X | ||
|
| X | X | X | X | |||
|
| −36% | −28% | X | X | X | X | NO, NOx, NH3, VOCs |
|
| −30% | ||||||
|
| −50% | ||||||
|
| X | −54% | −65% | +30% | NO | ||
|
| X | X | −20% | X | X | X | |
|
| X | X | X | X | X | ||
|
| −55% | X | |||||
|
| −50% | −50% | −50% | ||||
|
| −13% | ||||||
|
| X | X | X | ||||
|
| X | X | |||||
|
| X | X | X | ||||
|
| X | X | X | ||||
|
| −50% | ||||||
|
| −26% | −20% | −17% | −9% | −10% | ||
|
| −12% | ||||||
|
| X | X | −50% | +20% | NO, NOx | ||
|
| −10% | −50% | NO, NOx | ||||
|
| X | X | X | ||||
|
| X | X | X | X | |||
|
| −50% | ||||||
|
| X | X | |||||
|
| −40% | −44% | −51% | −21% | |||
|
| X | X | −30% / ‐84% | X | X | +16% / +58% | |
|
| X | −36% | X | X | |||
|
| X | X | X | X | X | ||
|
| −50% | ||||||
|
| −8% / ‐42% | −8% / ‐42% | −56% | +17 / +36% | NO | ||
|
| X | X | NMVOC | ||||
|
| X | X | X | X | X | X | |
|
| X | X | X | X | X | X | |
|
| −12% | X | |||||
|
| −23% | −21% | −33% | ||||
|
| −33% | −41% | −50% | −16% | +149% | ||
|
| X | −50% | X | +50% | BC | ||
|
| X | X | X | X | X | X | |
|
| −85% | ||||||
|
| −45% | −50% | −51% | ||||
|
| X | X | X | X | X | X | |
|
| X | ||||||
|
| X | X | |||||
|
| −33% | −21% | −38% | −20% | |||
|
| −14% / ‐38% | ||||||
|
| −33% | −29% | −17% | NO, NOx | |||
|
| −50% | −50% | −65% | ||||
|
| −58% | −47% | −83% | −11% | −30% | +125% | |
|
| −29% | −68% | −48% | −38% | |||
|
| X | X | |||||
|
| X | X | |||||
|
| −30% | −37% | −52% | −29% | −33% | X | |
|
| X | X | |||||
|
| X | X | X | X | X | ||
|
| X | ||||||
|
| X | X | |||||
|
| X | X | |||||
Note: Concentration values worsened during lockdown were indicated in red, unchanged values in yellow and decreasing values in green and, when available, the relative percentage values.
FIGURE 4Variation in pollutant concentrations [Colour figure can be viewed at wileyonlinelibrary.com]