Introduction: Air pollution is an emerging global concern, especially in the Western Pacific and South-East Asia regions; smoke-belching and emissions from vehicles on the road are associated with air pollution. In the Philippines, the Clean Air Act of 1999 was passed to address the growing concern for poor air quality to cover mobile sources such as vehicles. Objective: This study aimed to come up with a descriptive analysis of emissions of vehicles as this has an impact on air pollution and road-environmental safety. Methodology: This study analyzed a secondary database of vehicle emissions violation cases from the Land Transportation Organization (LTO) office in Region 11, the Philippines. The study was retrospective in nature and involved a review of traffic violation cases. The data were encoded and analyzed using the SPSS ver. 23 software program. Results: Two hundred eighty-two vehicle emission standard violations were recorded by the Land Transportation Office (LTO) from 2018 to 2019. Most cases were from 2018 (72.7%), with January (30.9%) recorded the highest number of unsafe vehicle emission standard violation cases. Of the apprehended drivers, the majority (88.3%) were of the driving professional license category. All the drivers (100.0%) were caught due to the violation of smoke-belching (V16). In comparison, a small proportion was also seen as cases of driving without a valid driver’s license or conductor’s permit (1.8%) and failure to carry driver’s license/OR/CR (0.8%). All the violators were caught on daytime working and rush hours, between 6:00 am and 5:00 pm. More than half of the apprehended drivers’ vehicles (55.3%) were classified as for hire, while the remaining (41.8%) were classified as private vehicles. The majority (99.3%) of the vehicles did not pass the first emissions standards. Meanwhile, the most common vehicles caught for unsafe emissions were UV vehicles (n = 239). The vehicles caught for dangerous emissions were more than ten years old, with one-third (35.9%) of the vehicles were between 10 to 19 years old. The mean years of use or age of the vehicle were 15.724 ± 8.553 years. Opacity results for the first emission testing were 6.691 ± 2.404, while the Average Light Absorption (ALA) coefficient for the second emissions testing was 1.102 ± 0.577. Conclusion This study provided an overview of unsafe vehicle emissions within an urban city and suggested a need for more robust monitoring of vehicle emissions within safe limits. Vehicles that do not meet safety standards should not be allowed on the road, and disposal of old inefficient running vehicles may be beneficial in reducing dangerous air pollution.
Vehicle Emissions ; Air Pollution

No abstract available.
Animals ; Inflammation* ; Mice* ; Vehicle Emissions*

Humans ; Vehicle Emissions/toxicity* ; Asthma ; Lung

BACKGROUND: The aim of this study was to estimate the number of workers exposed to diesel engine exhaust (DEE) by industry and year in the Republic of Korea. METHOD: The estimates of workers potentially exposed to DEE in the Republic of Korea were calculated by industry on the basis of the carcinogen exposure (CAREX) surveillance system. The data on the labor force employed in DEE exposure industries were obtained from the Census on Establishments conducted by the Korea National Statistical Office from 1993 to 2013. The mean values of prevalence rates adopted by EU15 countries were used as the primary exposure prevalence rates. We also investigated the exposure prevalence rates and exposure characteristics of DEE in 359 workplaces representing 11 industries. RESULTS: The total number of workers exposed to DEE were estimated as 270,014 in 1993 and 417,034 in 2013 (2.2% of the total labor force). As of 2013, the industry categorized as “Land transport” showed the highest number of workers exposed to DEE with 174,359, followed by “Personal and household services” with 70,298, “Construction” with 45,555, “Wholesale and retail trade and restaurants and hotels” with 44,005, and “Sanitation and similar services” with 12,584. These five industries, with more than 10,000 workers exposed to DEE, accounted for 83% of the total DEE-exposed workers. Comparing primary prevalence rates used for preliminary estimation among 49 industries, “Metal ore mining” had the highest rate at 52.6%, followed by “Other mining” with 50.0%, and “Land transport” with 23.6%. CONCLUSION: The DEE prevalence rates we surveyed (1.3–19.8%) were higher than the primary prevalence rates. The most common emission sources of DEE were diesel engine vehicles such as forklifts, trucks, and vans. Our estimated numbers of workers exposed to DEE can be used to identify industries with workers requiring protection from potential exposure to DEE in the Republic of Korea.
Censuses ; Employment ; Family Characteristics ; Korea* ; Methods ; Motor Vehicles ; Prevalence ; Republic of Korea ; Restaurants ; Vehicle Emissions*

Diesel exhaust particles (DEP) contain elemental carbon, organic compounds including Polyaromatic hydrocarbons (PAHs), metals, and other trace compounds. Diesel exhaust is complex mixture of thousands of chemicals. Over forty air contaminants are recognized as toxicants, such as carcinogens. Most diesel exhaust particles have aerodynamic diameters falling within a range of 0.1 to 0.25 microm. DEP was classified as a definite human carcinogen (group 1) by the International Agency for Research on Cancer at 2012 based on recently sufficient epidemiological evidence for lung cancer. Significant decreases in DEP and other diesel exhaust constituents will not be evident immediately, and outworn diesel car having longer mileage still threatens health of people in spite of recent remarkable development in diesel engine technology. Policy change in South Korea, such as introduction of diesel taxi, may raise health risk of air pollution in metropolitan area with these limitations of diesel engine. To protect people against DEP in South Korea, progressive strategies are needed, including disallowance of diesel taxi, more strict regulation of diesel engine emission, obligatory diesel particulate filter attachment in outworn diesel car, and close monitoring about health effects of DEP.
Air Pollution ; Carbon ; Carcinogens ; Humans ; Hydrocarbons ; International Agencies ; Korea ; Lung Neoplasms ; Metals ; Vehicle Emissions

OBJECTIVEThe present work aims to investigate the effects of subacute exposure to diesel exhaust particles (DEP) on reproductive function in female mice.

METHODSA total of 168 ICR (Institute of Cancer Research) mice were randomly divided into four groups by numeration table method, including the low (B), middle (C), high (D) dose DEP exposure groups and the control group (A). Each group consisted of 42 mice. Mice were inoculated with 30 µl DEP suspension at 0.8 (B), 3.0 (C), 12.0 (D) µg/µl, respectively, or the same volume of phosphate-buffered saline (A) on pharynx posterior wall per triduum for 4 times. The body weight and ovary weight were tested and ovary weight/body weight ratios were calculated. Rates of survival, germinal vesicle breakdown, extrusion of the first polar body, in-vitro fertilization and quantity of mitochondrial DNA for the oocytes were investigated. Ultrastructural changes of the oocytes were observed.

RESULTSThe ovary weight/body weight ratios were (15.4 ± 7.3) × 10(-5), (14.1 ± 6.8) × 10(-5), (8.2 ± 0.7) × 10(-5) and (7.2 ± 2.5) × 10(-5) in groups A, B, C and D (F = 3.841, P < 0.05). In groups A, B, C and D at 48 h post-insemination, rates of oocyte survival were 64.3%, 56.8%, 39.5% and 32.9% (χ(2) = 21.575, P < 0.05), rates of extrusion of the first polar body were 75.5%, 65.3%, 37.0% and 27.1% (χ(2) = 52.772, P < 0.05), rates of 2-cell embryos were 27.9%, 39.1%, 17.6% and 12.5% (χ(2) = 20.148, P < 0.05), and rates of embryos over 2 cells were 45.3%, 32.2%, 12.5% and 13.9% (χ(2) = 32.135, P < 0.05), respectively, and were significantly lower in groups C and D compared with group A (P < 0.05). Logarithmic values of mitochondrial DNA copy numbers were 6.54 ± 0.13, 6.48 ± 0.09, 5.57 ± 0.15 and 5.41 ± 0.07 in groups A, B, C and D, respectively, and were significantly lower in groups C and D compared with group A or B (F = 89.241, P < 0.05). A number of mitochondria of the oocytes exhibited tremendous tumescence and vacuolization in groups C and D, which was contrast to a roughly normal appearance in groups A and B.

CONCLUSIONSDEP is noxious to murine female reproduction. Subacute exposure to DEP injures the ovary and oocyte resulting in compromised ovarian function and fertilizability of the oocyte.

Animals ; Female ; Mice ; Mice, Inbred ICR ; Oocytes ; drug effects ; Ovary ; cytology ; drug effects ; Vehicle Emissions ; toxicity

Measurements of the magnetic properties and total contents of Cu, Cd, Pb and Fe in 30 automobile emission particulate samples indicated the presence of magnetic particles in them. The values of frequency dependent susceptibility (chi(fd)) showed the absence of superparamagnetic (SP) grains in the samples. The IRM(20 mT) (isothermal remanent magnetization at 20 mT) being linearly proportional to SIRM (saturation isothermal remanent magnetization) (R(2)=0.901), suggested that ferrimagnetic minerals were responsible for the magnetic properties of automobile emission particulates. The average contents of Cu, Cd, Pb and Fe in automobile emission particulates were 95.83, 22.14, 30.58 and 34727.31 mg/kg, respectively. Significant positive correlations exist between the magnetic parameters and the contents of Pb, Cu and Fe. The magnetic parameters of automobile emission particulates reflecting concentration of magnetic particles increased linearly with increase of Pb and Cu content, showed that the magnetic measurement could be used as a preliminary index for detection of Pb and Cu pollution.
Algorithms ; Environmental Monitoring ; methods ; Feasibility Studies ; Magnetics ; Metals, Heavy ; analysis ; chemistry ; Statistics as Topic ; Vehicle Emissions ; analysis

Benzene ; adverse effects ; analysis ; chemistry ; Catalysis ; Humans ; Occupational Exposure ; Risk Assessment ; Vehicle Emissions ; analysis ; Workplace

OBJECTIVETo study source apportionment of atmospheric PM10 (particle matter ≤ 10 µm in aerodynamic diameter) and PM2.5 (particle matter ≤ 2.5 µm in aerodynamic diameter) in Beijing,Urumqi and Qingdao, China.

METHODSThe atmospheric particle samples of PM10 and PM2.5 collected from Beijing between May 17th and June 18th, 2005, from Urumqi between April 20th and June 1st, 2006 and from Qingdao between April 4th and May 15th, 2005, were detected to trace the source apportionment by factor analysis and enrichment factor methods.

RESULTSIn Beijing, the source apportionment results derived from factor analysis model for PM10 were construction dust and soil sand dust (contributing rate of variance at 45.35%), industry dust, coal-combusted smoke and vehicle emissions (contributing rate at 31.83%), and biomass burning dust (13.57%). The main pollution element was Pb, while the content (median (minimum value-maximum value)was 0.216 (0.040-0.795) µg/m(3)) . As for PM2.5, the sources were construction dust and soil sand dust (38.86%), industry dust, coal-combusted smoke and vehicle emissions (25.73%), biomass burning dust (13.10%) and burning oil dust (11.92%). The main pollution element was Zn (0.365(0.126-0.808) µg/m(3)).In Urumqi, source apportionment results for PM10 were soil sand dust and coal-combusted dust(49.75%), industry dust, vehicle emissions and secondary particles dust (30.65%). The main characteristic pollution element was Cd (0.463(0.033-1.351) ng/m(3)). As for PM2.5, the sources were soil sand dust and coal-combusted dust (43.26%), secondary particles dust (22.29%), industry dust and vehicle emissions (20.50%). The main characteristic pollution element was As (14.599 (1.696-36.741) µg/m(3)).In Qingdao, source apportionment results for PM10 were construction dust (30.91%), vehicle emissions and industry dust (29.65%) and secondary particles dust (28.99%). The main characteristic pollution element was Pb (64.071 (5.846-346.831) µg/m(3)). As for PM2.5, the sources were secondary particles dust, industry dust and vehicle emissions (49.82%) and construction dust (33.71%). The main characteristic pollution element was Pb(57.340 (5.004-241.559) µg/m(3)).Enrichment factors of Zn, Pb, As and Cd in PM2.5 were higher than those in PM10 both in Beijing and Urumqi.

CONCLUSIONThe major sources of the atmospheric particles PM10 and PM2.5 in Beijing were cement dust from construction sites and sand dust from soil; while the major sources of those in Urumqi were pollution by smoke and sand dust from burning coal. The major sources of the atmospheric particles PM10 in Qingdao were cement dust from construction sites; however, the major sources of PM2.5 there were secondary particles dust, industry dust and vehicle emissions. According to our study, the heavy metal elements were likely to gather in PM2.5.

Air Pollutants ; analysis ; China ; Cities ; Dust ; analysis ; Environmental Monitoring ; methods ; Particle Size ; Seasons ; Vehicle Emissions ; analysis

Exposure to traffic-related air pollutants(TRAP)has been implicated in airway allergic diseases.Recent findings include epidemiologic and mechanistic studies that shed new light on the impact of TRAP on allergic rhinitis(AR)and the biology underlying this impact.These studies have found that oxidative stress induced by TRAP could affect the axis of epithelial cell-dendritic cell-T cell towards a T-helper 2 immune response,which is the major mechanism between TRAP and AR.Further,epigenetics and microRNA might be involved in this process.Our review will summarize the most recent findings in each of these areas.
Air Pollutants ; toxicity ; Air Pollution ; Humans ; Oxidative Stress ; Rhinitis, Allergic ; etiology ; Vehicle Emissions ; toxicity