2007
DOI: 10.1021/es070653g
|View full text |Cite
|
Sign up to set email alerts
|

Daily Variation in Chemical Characteristics of Urban Ultrafine Aerosols and Inference of Their Sources

Abstract: A summer air quality monitoring campaign focusing on daily variation of ultrafine (<180 nm in diameter) particle chemical characteristics was conducted in a typical urban site in Los Angeles during June-July 2006. Ultrafine particles (UFP) were collected weekly for two 3 h periods each day, one to capture the morning commute (06:00-09:00 PDT) (Pacific Daylight Time) and one to investigate photochemically altered particles (13:00-16:00 PDT). Samples were analyzed for ionic compounds, metals, trace elements, ele… Show more

Help me understand this report

Search citation statements

Order By: Relevance

Paper Sections

Select...
2
1
1
1

Citation Types

13
77
2

Year Published

2009
2009
2017
2017

Publication Types

Select...
8
1

Relationship

2
7

Authors

Journals

citations
Cited by 109 publications
(92 citation statements)
references
References 45 publications
13
77
2
Order By: Relevance
“…This site is regarded as a typical urban background site in Los Angeles. In the cooler months of late spring and late fall, a characteristic early morning peak, associated with mostly light-duty gasoline vehicle morning commute, is observed from 05:00-10:00 h. Advancing into summer months, this peak is not as robust and eventually flattens, as higher temperatures during the early mornings increase mixing heights, thus enhancing dispersion, and also lead to possible volatilization of semivolatile organics bound to PM from traffic emissions (Biswas et al, 2007;Ning et al, 2007). However, another peak emerges, which has its crest in early afternoon, and in summer months is associated with the highest diurnal values for PNC.…”
Section: Diurnal and Seasonal Variationsmentioning
confidence: 99%
See 1 more Smart Citation
“…This site is regarded as a typical urban background site in Los Angeles. In the cooler months of late spring and late fall, a characteristic early morning peak, associated with mostly light-duty gasoline vehicle morning commute, is observed from 05:00-10:00 h. Advancing into summer months, this peak is not as robust and eventually flattens, as higher temperatures during the early mornings increase mixing heights, thus enhancing dispersion, and also lead to possible volatilization of semivolatile organics bound to PM from traffic emissions (Biswas et al, 2007;Ning et al, 2007). However, another peak emerges, which has its crest in early afternoon, and in summer months is associated with the highest diurnal values for PNC.…”
Section: Diurnal and Seasonal Variationsmentioning
confidence: 99%
“…Once formed, particles are transformed in the atmosphere, by coagulation and condensation of semivolatile vapors on their surface as they are advected downwind. This long-range transport as well as photochemical particle formation in the atmosphere can lead to increased particle number observations downwind of urban areas (Kim et al, 2002;Fine et al, 2004b;Verma et al, 2009;Ning et al, 2007).…”
Section: Introductionmentioning
confidence: 99%
“…Ning et al 78 studied the diurnal variations of UFPM concentrations and chemical composition at an urban site (downtown Los Angeles, CA) using a MOUDI to collect two 3-hr samples daily (6:00 to 9:00 a.m. and 1:00 to 4:00 p.m.). The UFPM mass concentrations ranged from approximately 3 to 7 g/m…”
Section: ϫ3mentioning
confidence: 99%
“…The PENS-PM 0.1 of 18.1 μg/m 3 was highest during welding, followed by that of 15.3 μg/m 3 during milling and lowest of 10.5 μg/m 3 during polishing. These PM 0.1 levels are considered quite high, given the very small sizes and hence mass of nanoparticles and in comparison to PM 0.1 levels of less than 5 μg/m 3 measured in urban and roadside air (e.g., Geller et al, 2002;Ning et al, 2007).…”
Section: Personal Exposure Levels Of Pm 4 and Pm 01mentioning
confidence: 89%