Journals / Atmospheric Pollution Research / 2019 / Cilt: 10 - Sayı: 4

Trace elements bound to airborne PM10 in a heavily industrialized site nearby Athens: Seasonal patterns, emission sources, health implications

Pages
1347–1356
DOI
—
🏛️Bibliographic metadata and full text access for this article are provided via DergiPark.
DergiPark Record ↗
✨

AI Summary & Key Takeaways

AI Insight
⚡ TL;DR(Too Long; Didn't Read)

An estimation of the excesslifetime cancer risk due to toxic metals exposure via inhalation, revealed that 2 people out of 30 000 in Elefsisarea are at risk of cancer development.

📌 3 Key Takeaways

🎯
Objective & Hypothesis:Trace elements in PM10 samples were studied at Elefsis city, a heavily industrialized area of Greece.
📊
Key Findings & Data:Seasonalsamplings were carried out from December 2015 to August 2017.
💡
Conclusion & Impact:An estimation of the excesslifetime cancer risk due to toxic metals exposure via inhalation, revealed that 2 people out of 30 000 in Elefsisarea are at risk of cancer development.
🔬Design:Research Article
📍Scope:2015 · 10 samples
⚙️Variables:Domain Parameters

Özet

Trace elements in PM10 samples were studied at Elefsis city, a heavily industrialized area of Greece. Seasonalsamplings were carried out from December 2015 to August 2017. Concentration levels of 18 metal (loid)s weremeasured by Inductively Coupled Plasma – Mass Spectrometry (ICP-MS). Al, Ba and Zn were the most abundantelements with mean concentrations ranging between 1000 and 22 000 ng m−3, Fe and Sr between 100 and1000 ng m−3, while Cr, V, Mn, Pb, Cu, Ni, Ga, Rb were detected in traces (< 50 ng m−3) and As, Co, Cd, Cs andTl in ultratrace concentrations (< 2 ng m−3). PM10, Al, Fe, Zn and Ba showed a seasonal variation, with maximum concentrations prevailing during the cold period of the year. The source apportionment tools employed,comprising use of enrichment factors analysis, wind patterns and correlation analysis, revealed that the industrial zone located at the study area constitutes a significant hotspot in terms of trace elements emission in theair (e.g. Cd, Pb), due to the presence of activities including coal and/or fossil fuel combustion, ferrous and nonferrous production, operation of smelters and municipal solid waste incineration. An estimation of the excesslifetime cancer risk due to toxic metals exposure via inhalation, revealed that 2 people out of 30 000 in Elefsisarea are at risk of cancer development.

🔖

Cite This Article

KOUKOULAKİS, K. G., CHRYSOHOU, E., KANELLOPOULOS, P. G., KARAVOLTSOS, S., KATSOURAS, G., DASSENAKİS, M., NİKOLELİS, D., BAKEAS, E. (2019). Trace elements bound to airborne PM10 in a heavily industrialized site nearby Athens: Seasonal patterns, emission sources, health implications. Atmospheric Pollution Research, Cilt: 10 - Sayı: 4, 1347–1356. https://ajindex.com/articles/351309

References (8)

  1. Albuquerque, M., Coutinho, M., Rodrigues, J., Ginja, J., Borrego, C., 2017. Long-term monitoring of trace metals in PM10 and total gaseous mercury in atmosphere of Porto, Portugal. Atmos. Pollut. Res. 8, 535–544. APTD, 1969. Air Pollution Aspects of Barium and its Compounds. National Air Pollution Control Administration, Maryland, USA. Artíñano, B., Gómez-Moreno, F.J., Díaz, E., Amato, F., Pandolfi, M., Alonso-Blanco, E., Coz, E., García-Alonso, S., Becerril-Valle, M., Querol, X., Alastuey, A., van Drooge, B.L., 2017. Outdoor and indoor particle characterization from a large and uncontrolled combustion of a tire landfill. Sci. Total Environ. 593–594, 543–551.
  2. Boogaard, H., Kos, G.P.A., Weijers, E.P., Janssen, N.A.H., Fischer, P.H., Zee, S., Hartog, J.J., Hoek, G., 2011. Contrast in air pollution components between major streets and background locations: particulate matter mass, black carbon, elemental composition, nitrogen oxide, and ultrafine particle number, Atmos. Environ. Times 45, 650–658.
  3. Cancio, J.L., Castellano, A.V., Hernández, M.C., Bethencourt, R.G., Ortega, E.M., 2008. Metallic species in atmospheric particulate matter in Las Palmas de Gran Canaria. J. Hazard Mater. 160, 521–528.
  4. Chadwick, O.A., Derry, L.A., Bern, C.R., Vitousek, P.M., 2009. Changing sources of strontium to soils and ecosystems across the Hawaiian Islands. Chem. Geol. 267, 64–76.
  5. Chaloulakou, A., Kassomenos, P., Spyrellis, N., Demokritou, Ph, Koutrkis, P., 2002. Measurements of PM10 and PM2.5 particle concentrations in Athens, Greece. Atmos. Environ. Times 37, 649–660.
  6. Costa, C.J., Marques, A.P., Freitas, M.C., Reis, M.A., Oliveira, O.R., 2002. A comparative study for results obtained using biomonitors and PM10 collectors in Sado Estuary. Environ. Pollut. 120, 97–106.
  7. Das, R., Khezri, B., Srivastava, B., Datta, S., Sikdar, P.K., Webster, R.D., Wang, X., 2015. Trace element composition of PM2.5 and PM10 from Kolkata- a heavily polluted Indian metropolis Atmos. Pollut. Res. 6, 742–750. EEA, 2018. Air Quality in Europe-2018
  8. Report, EEA Report No. 12. pp. 88 Copenhagen. EN 12341, 2014. Ambient Air - Standard Gravimetric Measurement Method for the Determination of the PM10 or PM2.5 Mass Concentration of Suspended Particulate Matter. EU, 1999. Directive 1999/30/EC of the European Parliament and of the council of 22 April 1999 relating to limit values for SO2, NO2 and NOx, particulate matter and lead in ambient air. Off. J. Eur. Communities No. L 163, 29.6.1999, 41–60), Brussels. http