| Literature DB >> 33907954 |
Ming Han1, Fengxia Yang2, Haifeng Sun2.
Abstract
Fine particulate matter (PM2.5) is one of the major air pollutants. A large number of epidemiological and experimental studies have shown that PM2.5 pollution can cause adverse health consequences, which has attracted more public attention. In order to have a deeper and more structured understanding of the research progress and frontiers on the impact of PM2.5 on health, in this study, we used the bibliometrics software CiteSpace to analyze the relevant literature in this field. The results show that since 2000, the relevant literature has increased steadily, especially in the last 5 years, and the number of publications in China has increased rapidly. The United States has the most publications. The Chinese Academy of Sciences and Professor Joel Schwartz are the most published institution and author, respectively, and many articles have been published in the journal of Environmental Health Perspectives. Over time, studies on the health effects of PM2.5 have gradually deepened. In addition to a more comprehensive study of its harmful effects, the related molecular mechanisms have also been further explored. We believe that countries and regions should strengthen cooperation and jointly solve the harm caused by PM2.5 through the integration of multiple disciplines and fields. In addition, the adverse health consequences and its related mechanisms caused by exposure to ultrafine particle, different chemical components of PM2.5, as well as the intervention of the health effects caused by PM2.5 need to be further studied.Entities:
Keywords: Bibliometric; CiteSpace; Health effect; PM2.5; Research progress; Web of Science
Mesh:
Substances:
Year: 2021 PMID: 33907954 PMCID: PMC8079165 DOI: 10.1007/s11356-021-14086-z
Source DB: PubMed Journal: Environ Sci Pollut Res Int ISSN: 0944-1344 Impact factor: 5.190
Retrieval methods and results
| Search | Query | Results |
|---|---|---|
| #1 | TS = (PM2.5 OR “fine particulate matter” OR “fine particles” OR “ultra-fine particulate” OR “ultrafine particles” OR “nanoparticulate matter” OR “black carbon”) | 58,002 |
| #2 | TS = (toxicity OR damage OR injure OR injury OR destroy OR aggravate OR disease OR morbidity OR mortality OR health OR illness OR risk OR “adverse effect” OR “toxicological effect” OR death OR hospital OR hospitalization OR admission OR emergency OR outpatient) | 10,032,109 |
| #3 | (#1 AND #2) AND language: (English) Refined basis: document type: (ARTICLE OR REVIEW) AND Time Span = 1985–2020 | 19,825 |
The use of double quotation marks can help us find phrases more accurately. If you enter a phrase without quotation marks, the search engine will retrieve all records of the entered word
Parameter elucidation of CiteSpace
| Parameter name | Meaning | |
|---|---|---|
| Set up parameter | Timespan | The time interval of the analyzed literature |
| Slice length | Time slice, that is, the time interval is sliced according to how many years are a period | |
| Top N | Extract the top N data generation network for each time slice | |
| Pruning | The method of network tailoring. In order to make the structural network clearer, we have used the tailoring strategy of Pruning Sliced networks in this article | |
| Result parameter | N | The number of network nodes (different node types have different meanings, for example, reference co-citation analysis means cited references, keyword co-occurrence analysis means keywords, and country cooperation network analysis means countries) |
| E | Number of connections | |
| S (silhouette) | Average contour value, the basis for judging the effect of map drawing. Clustering is generally considered reasonable when S > 0.5, and clustering has high reliability when S > 0.7 | |
| Q (modularity) | Module value, the basis for judging the effect of graph drawing, Q > 0.3, the clustering result is significant when Q > 0.3 | |
Fig. 1Publication outputs and time trend
Fig. 2Global distribution map of publications
Fig. 3The cooperation network of authors
Fig. 4The cooperation network of institutions
Top 10 authors and institutions with the highest frequency in the cooperation network
| Rank | Authors | Frequency | Rank | Institutions | Frequency |
|---|---|---|---|---|---|
| 1 | Joel Schwartz | 209 | 1 | Chinese Academy of Sciences | 906 |
| 2 | Peter Koutrakis | 166 | 2 | Harvard University | 898 |
| 3 | Haidong Kan | 136 | 3 | Peking University | 611 |
| 4 | Gerard Hoek | 134 | 4 | United States Environmental Protection Agency | 589 |
| 5 | Bert Brunekreef | 126 | 5 | University of Washington | 410 |
| 6 | Brent A Coull | 120 | 6 | Tsinghua University | 377 |
| 7 | Michael Brauer | 111 | 7 | University of Chinese Academy of Sciences | 315 |
| 8 | Yang Liu | 101 | 8 | Fudan University | 303 |
| 9 | Ital Kloog | 93 | 9 | Utrecht University | 283 |
| 10 | Aaron Van Donkelaar | 88 | 10 | Emory University | 277 |
Fig. 5The specific research direction of the top three institutions with a high volume of publications
Fig. 6The co-citation network of journals
Top 10 cited journals with the highest frequency in the co-citation network of journals
| Rank | Journal | Frequency | Centrality | Burst | IF (2019) |
|---|---|---|---|---|---|
| 1 | Environmental Health Perspectives | 12,783 | 0.67 | - | 8.341 |
| 2 | Atmospheric Environment | 11,985 | 0.39 | - | 4.039 |
| 3 | Environmental Science & Technology | 10,383 | 0.02 | - | 7.864 |
| 4 | Science of The Total Environment | 9564 | 0.13 | - | 6.551 |
| 5 | Environmental Research | 7225 | 0.07 | - | 5.715 |
| 6 | Journal of The Air& Waste Management Association | 6847 | 0.01 | 13.08 | 2.245 |
| 7 | Lancet | 6069 | 0.02 | - | 60.39 |
| 8 | Environmental Pollution | 5565 | 0 | 522.02 | 6.793 |
| 9 | Epidemiology | 5554 | 0 | - | 5.071 |
| 10 | Environment International | 5275 | 0 | 423.87 | 7.577 |
Fig. 7The co-citation network of references
Top 10 cited references in the co-citation network of references
| Number of citations | Betweenness centrality | Year of publication | Burst strength | Reference | Title of publication | Cluster |
|---|---|---|---|---|---|---|
| 1189 | 0.42 | 2010 | 333.84 | (Brook et al. | Particulate matter air pollution and cardiovascular disease | 1 |
| 840 | 0.25 | 2012 | 144.04 | (Lim et al. | A comparative risk assessment of burden of disease and injury attributable to 67 risk factor and risk factor clusters in 21 regions, 1990-2010: a systematic analysis for the Global Burden of Disease Study 2010 | 0 |
| 793 | 0.11 | 2017 | 307.7 | (Cohen et al. | Estimates and 25-year trends of the global burden of disease attributable to ambient air pollution: an analysis of data from the Global Burden of Diseases Study 2015 | 0 |
| 738 | 0.02 | 2015 | 197.56 | (Lelieveld et al. | The contribution of outdoor air pollution sources to premature mortality on a global scale | 0 |
| 590 | 0.28 | 2006 | 239.31 | (Pope III and Dockery | Health effects of fine particulate air pollution: lines that connect | 1 |
| 564 | 0.12 | 2014 | 106.96 | (Burnett et al. | An integrated risk function for estimating the Global Burden of Disease attributable to ambient fine particulate matter exposure | 0 |
| 469 | 0.08 | 2013 | 64.81 | (Hoek et al. | Long-term air pollution exposure and cardio-respiratory mortality: a review | 0 |
| 463 | 0.12 | 2002 | 223.99 | (Pope et al. | Lung cancer, cardiopulmonary mortality, and long-term exposure to fine particulate air pollution | 1 |
| 438 | 0 | 2005 | 184.46 | (Oberdorster et al. | Nanotoxicology: an emerging discipline evolving from studies of ultrafine particles | 0 |
| 407 | 0.04 | 2014 | 98.5 | (Huang et al. | High secondary aerosol contribution to particulate pollution during haze events in China | 0 |
Journal impact factor data comes from the Journal Citation Reports (JCR) in the Web of Science
Top 10 references with strong centrality in the co-citation network of references
| Betweenness centrality | Number of citations | Year of publication | Burst strength | Reference | Title of publication | Cluster |
|---|---|---|---|---|---|---|
| 0.42 | 1189 | 2010 | 333.84 | (Brook et al. | Particulate matter air pollution and cardiovascular disease | 1 |
| 0.34 | 233 | 2004 | 106.69 | (Brook et al. | Air pollution and cardiovascular disease a statement for healthcare professionals from the expert panel on population and prevention pcience of the American Heart Association | 1 |
| 0.34 | 156 | 1996 | 93.13 | (Schwartz et al. | Is daily mortality associated specifically with fine particles? | 5 |
| 0.34 | 130 | 1997 | 74.16 | (Peters et al. | Respiratory effects are associated with the number of ultrafine particles | 4 |
| 0.31 | 249 | 2000 | 133.2 | (Samet et al. | Fine particulate air pollution and mortality in 20 US Cities, 1987-1994 | 1 |
| 0.28 | 590 | 2006 | 239.31 | (Pope III and Dockery | Health effects of fine particulate air pollution: lines that connect | 1 |
| 0.28 | 196 | 2003 | 93.22 | (Li et al. | Ultrafine particulate pollutants induce oxidative stress and mitochondrial damage | 0 |
| 0.26 | 54 | 1995 | 32.16 | (Oberdorster et al. | Association of particulate air-pollution and acute mortality-involvement of ultrafine particles | 4 |
| 0.25 | 840 | 2012 | 144.04 | (Lim et al. | A comparative risk assessment of burden of disease and injury attributable to 67 risk factor and risk factor clusters in 21 regions, 1990-2010: a systematic analysis for the Global Burden of Disease Study 2010 | 0 |
| 0.24 | 98 | 1994 | 60.15 | (Dockery and Pope | Acute respiratory effects of particulate air-pollution | 3 |
Fig. 8Co-citation cluster diagram of references on “health effects caused by PM2.5,” 1990–2020
Fig. 9Keyword co-occurrence time zone view of the development and evolution of health effects caused by PM2.5, 1990–2020
Information of keyword clusters (2016–2020)
| Cluster ID | Size | Silhouette | Mean (year) | Top terms (log-likelihood ratio, |
|---|---|---|---|---|
| #0 | 26 | 0.925 | 2016 | source apportionment (119.78, 1.0E-4); PAHs (84.12, 1.0E-4); chemical composition (54.96, 1.0E-4); air pollution (52.34, 1.0E-4); health risk (47.88, 1.0E-4); heavy metals (46.68, 1.0E-4) |
| #1 | 23 | 0.672 | 2016 | air quality (119.36, 1.0E-4); COVID-19 (80.55, 1.0E-4); ozone (36.44, 1.0E-4); pollution (28.55, 1.0E-4); inflammation (28.12, 1.0E-4); oxidative stress (28.12, 1.0E-4) |
| #2 | 21 | 0.865 | 2016 | cardiovascular disease (65.59, 1.0E-4); mortality (45.45, 1.0E-4); association (43.69, 1.0E-4); risk (39.85, 1.0E-4); pregnancy (38.94, 1.0E-4); hypertension (36.95, 1.0E-4) |
| #3 | 20 | 0.883 | 2016 | air pollution (92.93, 1.0E-4); particulate matter (31.97, 1.0E-4); asthma (23.15, 1.0E-4); health (22, 1.0E-4); PM2.5 (21.25, 1.0E-4); impact (17.62, 1.0E-4) |
| #4 | 19 | 0.895 | 2016 | oxidative stress (136.76, 1.0E-4); inflammation (104.57, 1.0E-4); nanoparticles (55.49, 1.0E-4); apoptosis (55.49, 1.0E-4); ultrafine particles (53.73, 1.0E-4); toxicity (33.6, 1.0E-4) |
| #5 | 13 | 0.725 | 2016 | indoor air quality (92.82, 1.0E-4); personal exposure (32.98, 1.0E-4); air pollution (32.29, 1.0E-4); outdoor (27.56, 1.0E-4); indoor (25.8, 1.0E-4); mortality |
| #6 | 12 | 0.898 | 2016 | respiratory diseases (23.87, 1.0E-4); short-term exposure (21.02, 1.0E-4); particle size (21.02, 1.0E-4); particulate air pollution (20.47, 1.0E-4); respiratory disease (18.85, 1.0E-4); time-series study |
| #7 | 6 | 0.862 | 2017 | China (48.23, 1.0E-4); particulate matter (22.63, 1.0E-4); haze (21.81, 1.0E-4); public health (14.99, 0.001); emission inventory (13.04, 0.001); urban sustainability |
The top six terms were shown in each cluster
Top 40 keywords with high frequency in keyword co-occurrence analysis (2016–2020)
| Rank | Keyword | Frequency | Centrality | Rank | Keyword | Frequency | Centrality |
|---|---|---|---|---|---|---|---|
| 1 | PM2.5 | 4718 | 0.7 | 21 | PM10 | 734 | 0.05 |
| 2 | air pollution | 4325 | 0.53 | 22 | air quality | 726 | 0.03 |
| 3 | particulate matter | 3304 | 0.09 | 23 | inflammation | 665 | 0.12 |
| 4 | exposure | 2111 | 0.03 | 24 | aerosol | 655 | 0.04 |
| 5 | mortality | 1866 | 0.15 | 25 | quality | 620 | 0.01 |
| 6 | health | 1557 | 0.01 | 26 | cardiovascular disease | 591 | 0.08 |
| 7 | pollution | 1262 | 0.12 | 27 | global burden | 545 | 0.03 |
| 8 | association | 1140 | 0.14 | 28 | pollutant | 544 | 0 |
| 9 | source apportionment | 1052 | 0.34 | 29 | model | 517 | 0.06 |
| 10 | particle | 966 | 0 | 30 | particulate air pollution | 511 | 0.03 |
| 11 | impact | 931 | 0.05 | 31 | ozone | 494 | 0.03 |
| 12 | polycyclic aromatic hydrocarbon | 926 | 0.08 | 32 | ambient air pollution | 491 | 0.08 |
| 13 | emission | 913 | 0.07 | 33 | chemical composition | 470 | 0.01 |
| 14 | ultrafine particle | 873 | 0.18 | 34 | children | 468 | 0.09 |
| 15 | black carbon | 870 | 0.03 | 35 | urban | 460 | 0.04 |
| 16 | oxidative stress | 865 | 0.12 | 36 | asthma | 442 | 0.02 |
| 17 | disease | 840 | 0.06 | 37 | nitrogen dioxide | 434 | 0.05 |
| 18 | risk | 839 | 0.03 | 38 | fine | 429 | 0.03 |
| 19 | long term exposure | 805 | 0.15 | 39 | heavy metal | 405 | 0.09 |
| 20 | China | 771 | 0.08 | 40 | United States | 396 | 0.04 |
Fig. 10A timeline visualization of the keywords co-occurrence network, 2016–2020