Levels of lead in urban soils from selected cities in a central region of the Philippines.
OBJECTIVE
Lead (Pb) is a naturally occurring element that poses environmental hazards when present at elevated concentration. It is being released into the environment because of industrial uses and from the combustion of fossil fuels. Hence, Pb is ubiquitous throughout global ecosystems. The existence of potentially harmful concentrations of Pb in the environment must be given full attention. Emissions from vehicles are major source of environmental contamination by Pb. Thus, it becomes imperative that concentrations of Pb and other hazardous materials in the environment not only in the Philippines, but elsewhere in the world be adequately examined in order that development of regulations and standards to minimize risk associated with these materials in urban areas is continued. The objectives of this study were: (1) to determine the levels of Pb in soil from selected urbanized cities in central region of the Philippines; (2) to identify areas with soil Pb concentration values that exceed estimated natural concentrations and allowable limits; and (3) to determine the possible sources that contribute to elevated soil Pb concentration (if any) in the study area.


METHODS
This study was limited to the determination of Pb levels in soils of selected urbanized cities located in central region in the Philippines, namely: Site 1--Tarlac City in Tarlac; Site 2--Cabanatuan City in Nueva Ecija; Site 3--Malolos City in Bulacan; Site 4--San Fernando City in Pampanga; Site 5--Balanga City in Bataan; and Site 6--Olongapo City in Zambales. Soil samples were collected from areas along major thoroughfares regularly traversed by tricycles, passenger jeepneys, cars, vans, trucks, buses, and other motor vehicles. Soil samples were collected from five sampling sites in each of the study areas. Samples from the selected sampling sites were obtained approximately 2 to 3 meters from the road. Analysis of the soil samples for Pb content was conducted using an atomic absorption spectrophotometer. This study was conducted from 2003 to 2004. Since this study assumed that vehicular emission is the major source of Pb contamination in urban soil, other information which the researchers deemed to have bearing on the study were obtained such as relative quantity of each gasoline type disposed of in each city within a given period and volume of traffic in each sampling site. A survey questionnaire for gasoline station managers was prepared to determine the relative quantity of each fuel type (diesel, regular gasoline, premium gasoline, and unleaded gasoline) disposed of or sold within a given period in each study area.


CONCLUSIONS
Analysis of soil samples for Pb content showed the presence of Pb in all the soil samples collected from the 30 sampling sites in the six cities at varying concentrations ranging from 1.5 to 251 mg kg(-1). Elevated levels of Pb in soil (i.e. greater than 25 mg kg(-1) Pb) were detected in five out of the six cities investigated. Site 4 recorded the highest Pb concentration (73.9 +/- 94.4 mg kg(-1)), followed by Site 6 (56.3 +/- 17.1 mg kg(-1)), Site 3 (52.0 +/- 33.1 mg kg(-1)), Site 5 (39.3 +/- 19.0 mg kg(-1)), and Site 2 (38.4 +/- 33.2 mg kg(-1)). Soil Pb concentration in Site 1 (16.8 +/- 12.2 mg kg(-1)) was found to be within the estimated natural concentration range of 5 to 25 mg kg(-1). Site 1 registered the least Pb concentration. Nonetheless, the average Pb concentration in the soil samples from the six cities studied were all found to be below the maximum tolerable limit according to World Health Organization (WHO) standards. The high Pb concentration in Site 4 may be attributed mainly to vehicular emission. Although Site 4 only ranked 3rd in total volume of vehicles, it has the greatest number of Type B and Type C vehicles combined. Included in these categories are diesel trucks, buses, and jeepneys which are considered the largest contributors of TSP (total suspended particles) and PM10 (particulate matter less than 10 microns) emissions.


CONCLUSIONS
Only one (San Juan in Site 4) of the thirty sampling sites recorded a Pb concentration beyond the WHO permissible limit of 100 mg kg(-1). San Juan in Site 4 had a Pb concentration of >250 mg kg(-1). On the average, elevated Pb concentration was evident in the soil samples from San Fernando, Olongapo, Malolos, Balanga, and Cabanatuan. The average soil Pb concentrations in these cities exceeded the maximum estimated natural soil Pb concentration of 25 mg kg(-1). Average soil Pb concentration in Site 1 (16.8 mg kg(-1)) was well within the estimated natural concentration range of 5 to 25 mg kg(-1). Data gathered from the study areas showed that elevated levels of Pb in soil were due primarily to vehicular emissions and partly to igneous activity.


CONCLUSIONS
The findings of this study presented a preliminary survey on the extent of Pb contamination of soils in urban cities in central region of Philippines Island. With this kind of information on hand, government should develop a comprehensive environmental management strategy to address vehicular air pollution in urban areas, which shows as one of the most pressing environmental problems in the country. Basic to this is the continuous monitoring of Pb levels and other pollutants in air, soil, and water. Further studies should be conducted to monitor soil Pb levels in the six cities studied particularly in areas with elevated Pb concentration. The potential for harm from Pb exposure cannot be understated. Of particular concern are children who are more predisposed to Pb toxicity than adults. Phytoremediation of Pb-contaminated sites is strongly recommended to reduce Pb concentration in soil. Several studies have confirmed that plants are capable of absorbing extra Pb from soil and that some plants, grass species in particular, and can naturally absorb far more Pb than others.
Ona
Louella F
LF
Tarlac State University, Tarlac City, Philippines.
Alberto
Annie Melinda P
AM
Prudente
Jacqueline A
JA
Sigua
Gilbert C
GC
D002947:Cities; D007854:Lead / Q000032:analysis*; D010679:Philippines; D012989:Soil Pollutants / Q000032:analysis*; D013054:Spectrophotometry, Atomic; D001335:Vehicle Emissions / Q000032:analysis*
D012989:Soil Pollutants; D001335:Vehicle Emissions; D007854:Lead