Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2022 Oct 8;19(19):12898.
doi: 10.3390/ijerph191912898.

Spatially Resolved Distribution, Sources, Exposure Levels, and Health Risks of Heavy Metals in <63 μm Size-Fractionated Road Dust from Lucknow City, North India

Vidhu Gupta  1 , Lalita Bisht  1 , Ajay Kumar Arya  2 , Ajay Pratap Singh  2 , Sneha Gautam  3
Affiliations

Spatially Resolved Distribution, Sources, Exposure Levels, and Health Risks of Heavy Metals in <63 μm Size-Fractionated Road Dust from Lucknow City, North India

Vidhu Gupta et al. Int J Environ Res Public Health. .

Abstract

In the present study, a total of 64 road dust samples were collected from five different functional areas (residential, commercial, parks, high-traffic, and industrial) in urban Lucknow to assess the accumulation, distribution, and health risk of heavy metals (HMs) (i.e., Fe, Mn, Zn, Cu, Pb, Cd, As, Cr and Ni). Acid digestion methods were used to analyze HMs, followed by inductively coupled plasma-mass spectrometry (ICPMS). The ascending frequency of HMs was Cd < As < Ni < Cr < Pb < Cu < Zn < Mn < Fe for all different functional areas. Almost all HMs exceed the limits of Indian natural soil background values (INSB) across all functional areas. The pollution assessment results reveal that the urban road dust of Lucknow is highly enriched with Zn and Pb, causing deterioration of dust quality. The spatial distribution of HMs shows that road dust found in the central and southwestern zones of the Lucknow urban area are more contaminated than in other areas. The ecological risk assessment demonstrates that Cd was the highest risk contributor, followed by Pb, Zn and Cu. The result of the health risk assessment i.e., the cumulative hazard index (HI) and the cumulative lifetime cancer risk (LCR), reveal that children (mean HIchildren = 1.26, LCRchildren = 0.000187) are more vulnerable to HM exposure than adults (HIadults = 0.14, LCRadults = 0.0000804). For carcinogenic and non-carcinogenic risk, ingestion appears to be the major pathway of HM exposure in both age groups. It is alarming that all studied four carcinogenic HMs were found in concentrations higher than 1 × 10-6 (the permissible limit for humans). This indicates slight chances of developing cancer for both age groups in all functional areas.

Keywords: health risk assessment; heavy metals; pollution assessment; potential ecological risk; road dust; spatial distribution.

PubMed Disclaimer

Conflict of interest statement

The authors declare that they have no known competing financial or non-financial interest to disclose.

Figures

Figure 1
Figure 1
Map of the study area and sampling locations.
Figure 2
Figure 2
Pollution indexes (PIs) and integrated pollution indexes (IPI) of HMs in the dust of Lucknow over different functional areas.
Figure 3
Figure 3
Geo-accumulation index (Igeo) of HMs in the road dust of Lucknow over different functional areas.
Figure 4
Figure 4
(a–i) Spatial distribution of HMs in the road dust of Lucknow over different functional areas.
Figure 4
Figure 4
(a–i) Spatial distribution of HMs in the road dust of Lucknow over different functional areas.
Figure 5
Figure 5
(a) Ecological risk factors (Er) of individual HMs in different functional areas; (b) relative percentage contributions of heavy metals to the potential ecological risk index (PER) in Lucknow; (c) box plot of potential ecological risk (PER). The box plot is outlined by the 25th and 75th percentile values, whiskers indicate the 10th and 90th percentile values, and dots show the 5th and 95th percentile outliers. The solid black line within the box corresponds to the 50th percentile value (or the median).
See this image and copyright information in PMC

References

    1. Rajaram B.S., Suryawanshi P.V., Bhanarkar A.D., Rao C.V.C. Heavy metal contamination in road dust in Delhi city, India. Environ. Earth Sci. 2014;72:3929–3938. doi: 10.1007/s12665-014-3281-y. - DOI
    1. Zhao N., Lu X., Chao S., Xu X. Multivariate statistical analysis of heavy metals in less than 100 μm particles of street dust from Xining, China. Environ. Earth Sci. 2015;73:2319–2327. doi: 10.1007/s12665-014-3578-x. - DOI
    1. Bisht L., Gupta V., Singh A., Gautam A.S., Gautam S. Heavy metal concentration and its distribution analysis in urban road dust: A case study from most populated city of Indian state of Uttarakhand. Spat. Spatiotemporal Epidemiol. 2022;40:100470. doi: 10.1016/j.sste.2021.100470. - DOI - PubMed
    1. Gupta V., Bisht L., Deep A., Gautam S. Spatial distribution, pollution levels, and risk assessment of potentially toxic metals in road dust from major tourist city, Dehradun, Uttarakhand, India. Stochastic Environ. Res. Risk Assess. :2022. doi: 10.1007/s00477-022-02207-0. in press . - DOI
    1. Roy S., Gupta S.K., Prakash J., Habib G., Baudh K., Nasr M. Ecological and human health risk assessment of heavy metal contamination in road dust in the National Capital Territory (NCT) of Delhi, India. Environ. Sci. Pollut. Res. 2019;26:30413–30425. doi: 10.1007/s11356-019-06216-5. - DOI - PubMed