Sample Paper - Manuscript Preparation


16 
J. mt. area res., Vol. 2, 2017 

   

       Journal of Mountain Area Research 
            

 

 

DETERMINATION OF DIVERSE ENVIRONMENTAL POLLUTION LEVEL FROM 

SELECTED AREAS OF RAWALPINDI, PAKISTAN 
 

S. Pervez1,*, M. S. Siddique1, H. Y. Abdullah1, A. Zahra2, N. K. khanzada1, H. Fareed1, G. Hasnain1 

 

1. Institute of Environmental Sciences and Engineering, National University of Sciences and Technology (IESE, NUST), Islamabad 

2. School of Natural Sciences, National University of Sciences and Technology (SNS, NUST), Islamabad

 

 

ABSTRACT 

Anthropogenic contaminants arising from both stationary (power plants, industries and 

residential heating) and mobile sources (road traffic) can harm ambient air quality in urban areas. 

Depending upon their physical state, these pollutants are classified as liquid and vapor phases 

and are subsequently transported to the Earth’s surface through dry and wet deposition. After the 

deposition of these pollutants onto the surface of earth various health effects caused by these 

pollutants occurred like cardiovascular diseases and hypertension. In this study four different 

locations/sites were selected from the Rawalpindi city depending upon the population, traffic 

rush and industries to examine the noise level, concentration of carbon dioxide and heavy metals. 

Air sampler was used for the collection of air sample to analyze the heavy metal concentration, 

Quest electronic sound meter for measuring sound level and SIBATA for CO2 measurement. The 

study findings revealed that noise level was higher at all selected locations as described by WHO 

limit (70 dB) being highest at Industrial area due to heavy machinery and lowest at green area. 

Concentration of all four heavy metals were high as compared with the prescribed limits. CO2 

level reaches up to 300 ppm because of coal consumption during the winter season. The threshold 

values of all these selected parameters well above the prescribed limits defined by the authorities 

so to combat with this situation we should move towards more energy efficient fuels, proper 

maintenance of vehicles and machineries, traffic management and installation of noise barriers 

in industries as well as installation of catalytic convertors in vehicles to stop further air pollution. 

 

KEYWORDS:  Climate change, Heavy metals, CO2, Noise, Rawalpindi 

 

*Corresponding author: (Email: saim3035@gmail.com) 

 

 

1. INTRODUCTION 

Pakistan is bestowed with a great 

diversity of landscape, climate, seasons, 

ecosystems, etc. The landscape ranges from 

snowcapped peaks in the Himalayan Range 

in the north to Arabian Sea coastline in the 

south, from agriculture ranges in the plains to 

hot dry deserts in Sindh and Baluchistan. This 

diversity has given rise to a variety of living 

organisms including flora, fauna, animals, 

birds, insects, etc. which provide economic 

Vol. 2, 2017 

http://journal.kiu.edu.pk/index.php/JMAR 

Full length article 

mailto:saim3035@gmail.com


 

 
 

Pervez et al., J. mt. area res. 02 (2017) 16-22 

17 
J. mt. area res., Vol. 2, 2017 

benefits and services to human society as 

well as ecological, recreational, cultural and 

aesthetic values.  

However, this diversity provided by the 

nature has not been exempted by the 

human greed for development, has been to 

a large extent exploiting the variety of 

resources provided by the nature. Although 

Pakistan contributes only 0.8 percent in the 

global greenhouse gas emissions and is 

ranked 135th in global GHG per capita 

emissions, still the countries biodiversity is 

prone to adverse impacts of climate change 

and the country has been rated as one of 

the most vulnerable nations to the adverse 

effects of climate change.  

Sources of air pollution are: (1) Natural 

(2) manufactured. Natural sources includes 

wind storms, volcanic ash and gases, pollens 

and gases or odors from natural 

decomposition while man-made sources of 

air pollution are: industries and vehicles (El-

Mubarak et al., 2014). The main pollutants 

from all these sources are carbon dioxide 

(CO2), methane (CH4), hydrocarbons and 

particulate matter. Two different types of air 

pollutants are present, Primary and 

secondary pollutant. Primary pollutants are 

those that occurs in a harmful concentration, 

added directly to the air by natural events or 

human activities while secondary pollutants 

are formed in atmosphere when a primary 

pollutant reacts with the normal air 

components or with other air pollutants. [1]. 

Effects of all these man-made or natural 

atmospheric pollutants are very adverse like 

severe respiratory problems such as asthma, 

chronic bronchitis, and degraded lung 

function and at last but not least respiratory 

failure  [2, 3].  

So, it is necessary to combat with all 

these types of pollutants and with the 

sources, that a healthier environment could 

achieve and climate change not affect at 

all. The aim of the present study is to analyze 

and characterize the ambient air of 

Rawalpindi city for the quantitative 

assessment of heavy metals, noise level and 

carbon dioxide emissions from 

anthropogenic sources and examine the 

current level of compliance with 

environmental regulations. 

 

2. MATERIALS AND METHODS 

The present study deals with the 

characterization and analysis of ambient air 

of Rawalpindi city. For this analysis, four 

different locations based upon populations 

and industrial density were selected. Bahria 

town was selected as residential area while 

commercial market selected as a 

commercial area. Murree road is one of the 

congested and busy road of Rawalpindi city 

and also industries lies on the side of the road 

hence it was selected as industrial area 

whereas Ayub Park selected as green area. 

Air samples were collected from December 

to February. 

A brief methodology followed during the 

project was: 

1. Selection of the area 

2. Visiting the sites 

3. Taking the readings of noise and CO2  

4. Collecting the air samples 

5. Obtaining the heavy metals 

measurements using the AAS. 

6. Comparing the values with standards 

The analysis of different parameters 

measured were performed using standard 



 

 

 

Pervez et al., J. mt. area res. 02 (2017) 16-22 

18 
J. mt. area res., Vol. 2, 2017 

methods by APHA (American Public Health 

Association) 2010 as reference. 

 

 

 

Figure 1.  Selection of the areas 

 

2.1.  Measurement of Noise Level 

For noise measurement the standard 

method was used as described in the 

literature. Instrument that was used named 

as Quest electronic sound meter (model 211 

fs). First of all turn on the meter, select 100 dB 

range position then switch on the calibrator 

and check battery level indicator, carefully 

insert the meter microphone into the 

calibrator coupler. If reading is off slightly, 

insert a small screwdriver in the small hole on 

the bottom of the meter. Now change the 

selector switch to 110 dB position on the 

meter and note the needle should drop to 

the zero position on the meter dial. Meter is 

now calibrated and ready for use. Allow the 

needle to stabilize and record the 

measurement. (APHA, 2010) 

 
Figure 2. Quest electronic sound meter 

2.2. Measurement of Carbon Dioxide (CO2) 

CO2 in air was monitored using 

combustion Gas Analyzer (US). The CO2 

value was monitored and average was 

calculated. The sound level was monitored 

with the help of a portable sound meter. The 

equipment was mounted on a tripod stand 

with a microphone 1.5 m above the ground 

level. The data was continuously monitored 

and average values were calculated. 

(APHA, 2010) 

 

Figure 3.  SIBATA CO2 meter 

 

2.3. Air Samples for Heavy Metals  

   Determination 

Pall flex quartz fiber filter was used for air 

sampling which was preheated at 550 0C for 

1 hour. It was then mounted on an air 

sampler for 2 hours and air flow was kept at 

1m3/min. After sampling, the paper was 

stored in aluminum foil and stored in freezer 

till analysis. Heavy metals were determined 

by chemically digesting filter paper and the 

resulting solution analyzed using AAS (atomic 

absorption spectrometer) [4]. 

 



 

 
 

Pervez et al., J. mt. area res. 02 (2017) 16-22 

19 
J. mt. area res., Vol. 2, 2017 

3. RESULTS AND DISCUSSION 

Results and discussion were made 

according to the survey of the selected 

areas and after the calculation of the 

desired pollutant level. 

 

3.1. Noise Level at Selected Sites of Study  

    Area 

The noise level determined using the 

sound meter at all the selected locations and 

found it to be that at location of Ayub Park 

which is declared as green area has the 

minimum level of 78dB while the residential 

area and commercial area both have the 

same value of noise level i.e. 90dB although 

commercial area has more average value 

which is because of excessive vehicle horn 

and heavy traffic jam [5]. The value of sound 

was higher at industrial area i.e. 80-90dB 

because of heavy machinery working and 

industrial plants. The noise level at all the 

selected locations was greater than the 

prescribed limits given by world health 

organization (WHO). Chronic exposure of this 

loud noise level cause problems like 

cardiovascular and hypertension [6]. 

 

Figure 4. Average of Noise level (dB)  

 

 

 

3.2. Carbon Dioxide Concentration at  

    Selected Locations 

Because of anthropogenic activities, 

CO2 concentration was up to 300ppm. Max 

average value was observed at Bahria town 

i.e. 238 ppm while minimum average value 

was noted at commercial market. Murree 

road and Ayub Park had the average values 

of 214 and 207 ppm respectively. 

Astonishingly the area expected to have 

minimum pollution levels i.e. residential area 

of Ayub Park had maximum average values 

observed. This was probably winds blowing 

that took high concentrations of CO2 from 

congested areas like commercial markets to 

residential areas like Bahria town [7]. 

Moreover highest values were observed at 1: 

00 PM and 7: 00 PM because these are the 

peak hours having maximum traffic 

population. Pakistan is one of top 50 

countries in terms of CO2 emissions [8]. 

 

Figure 5. Average of Carbon Dioxide (CO2) 

concentration (ppm) 

 

3.3. Heavy Metals Concentrations 

3.3.1. Lead  

Maximum concentration was observed 

at Bahria town i.e. 149 µg/m3 while minimum 

at Ayub park i.e. 63 µg/m3 .there are two 

main sources of lead, lower quality fuel 

combustion and lead based paints [9]. Both 

of these sources are absent in Ayub park 



 

 

 

Pervez et al., J. mt. area res. 02 (2017) 16-22 

20 
J. mt. area res., Vol. 2, 2017 

that’s why it has minimum concentration 

while in residential area paints and use of fuel 

in generators for electricity purpose are the 

source that’s why it has maximum values. All 

values are exceeding WHO guidelines of 0.5 

µg/m3 which is alarming because lead is very 

harmful for human health mainly damage to 

nervous system even leading to death [10]. 

3.3.2.  Chromium  

Maximum concentration was observed 

at commercial market i.e. 42 µg/m3 while 

minimum at Ayub park. All the values are 

exceeding WHO guidelines for 0.11 µg/m3. 

Chromium is build up in atmosphere when 

there is lack of winds and air congestion. As 

commercial market was congested area so 

there was lack of winds in area which results 

in chromium buildup due to pollution in area. 

When there is good wind it is readily diluted. 

Chromium in air can lead to lung cancer [11]. 

3.3.3. Arsenic 

Maximum value was observed at 

commercial market i.e. 33 µg/m3.Main 

sources of arsenic are fuel combustion and 

metal smelting and aerosols from pesticide. 

Welding shops lead to smelting while 

pesticides are used in parks adding to fuel 

combustion of vehicles. All the values are 

exceeding guidelines of WHO i.e.0.11 µg/m3. 

This should be taken as important concern 

because arsenic is very poisonous for human 

health [12]. 

3.3.4. Iron  

All the values were exceeding the 

standards set by WHO for iron in air i.e. 150 

µg/m3. Highest values were obtained at 

commercial market and Murree road i.e. 376 

and 512 µg/m3 respectively. Sources were 

use of old machinery, dust winds and local 

industrial area [13]. 

3.3.5. Manganese 

Manganese concentration were lowest 

among all the heavy metals detected but it 

was still higher than WHO standards i.e. 0.15 

µg/m3.highest levels were obtained at 

Murree road i.e. 162 µg/m3 and lowest levels 

were detected at Ayub park i.e. 3 µg/m3. 

Sources of manganese are production of 

steel and alloys and burning of fossil fuels 

that’s why it has maximum concentration at 

Murree road. [4]. its chronic exposure can 

cause neurological disorders [14]. 

 

 

Figure 6. Average concentration of heavy 

metals 

4. CONCLUSIONS 

It was observed that almost all the values 

for heavy metals and noise were found to be 

exceeding the WHO guidelines that is very 

alarming situation for the city environment 

and its inhabitants. Poisonous and dangerous 

heavy metals such as Arsenic (peak value: 33 

µg/m3, WHO limit: 0.11 µg/m3), Lead (peak 

value: 149 µg/m3, WHO limit: 0.50 µg/m3) and 

Chromium (peak value: 42 µg/m3, WHO limit: 

0.11 µg/m3) are more than 10 times their 

guideline values. Average Noise levels were 

around 80-90 db whereas safe hearing limit is 



 

 
 

Pervez et al., J. mt. area res. 02 (2017) 16-22 

21 
J. mt. area res., Vol. 2, 2017 

below 85 db. CO2 values (300 ppm) were 

although in bearable limit but it is a 

greenhouse gas so this average amount of 

CO2 may be significant for our global 

temperature rise. 

 

References 

[1] H. Peace, B. Owen, D.W. Raper, Comparison  

of road traffic emission factors and testing by 

comparison of modelled and measured 

ambient air quality data, Sci. Total Environ 

334-335 (2004) 385-395. 

[2] M. Mansha, B. Ghauri, S. Rahman, A. Amman, 

Characterization and source apportionment 

of ambient air particulate matter (PM2.5) in 

Karachi, Sci Total Environ 425 (2012) 176-183. 

[3] C. Y. Yang, Y. S. Chen, C. H. Yang, S. C. Ho, 

Relationship between ambient air pollution 

and hospital admissions for cardiovascular 

diseases in Kaohsiung, Taiwan, J. Toxicol. 

Environ. Health A, 67 (2004) 483-93. 

[4] A. A. Gharaibeh, A.W. El-Rjoob, M.K. Harb, 

Determination of selected heavy metals in air 

samples from the northern part of Jordan, 

Environ. Monit. Assess 60 (2010) 425-429. 

[5] M. Ali, and M. Athar, Impact of transport and 

industrial emissions on the ambient air quality 

of Lahore City, Pakistan, Environ Monit. Assess 

171 (2010) 353-363. 

[6] B. Berglund, T. Lindvall, D.H. Schwela, 

Guidelines for Community Noise, World 

Health Organization (1999). 

[7] S. Rogers, L. Evans, World carbon dioxide 

emissions data by country: China speeds 

ahead of the rest, The Guardian, (2011). 

[8] P. Dalal, D. Chaudhry, V. Shukla, Analysis of 

heavy metals concentration in ambient air 

and in human population of Rohtak, India, J 

Env. Biol 34 (2013) 945-949. 

[9] WHO, Air Quality Guidelines World Health 

Organization, 2nd Edition, (2000). 

[10] Y. M. Coyle, A. T Minahjuddin, L. S. Hynan, J. 

D Minna, An ecological study of the 

association of metal air pollutants with lung 

cancer incidence in Texas, J Thorac. Oncol 7 

(2006) 654-661. 

[11] E. Von Schneidemesser, E. A. Stone, T. A. 

Quraishi, M.M. Shafer, J. J. Schauer, Toxic 

metals in the atmosphere in Lahore, Pakistan, 

Sci Total Environ, 408 (2010) 1640-1648. 

[12] A. H. El-Mubarak, A. I. Rushdi, k. F. Al-Mutlaq, 

A. Y. Bazeyad, S. L Simonich, B. R Simoneit, 

Identification and source apportionment of 

polycyclic aromatic hydrocarbons in 

ambient air particulate matter of Riyadh, 

Saudi Arabia, Environ Sci. Pollut. Res. Int 

21(2014) 558-567. 

[13] R. J. Delfino, J. Wu, T. Tjoa, S. K. Gullesserian, 

B. Nickerson, D.L. Gillen, Asthma morbidity 

and ambient air pollution: effect 

modification by residential traffic-related air 

pollution, Epidemiology 25 (2014) 48-57. 

[14] Y. Gao, E. Y Chan, L. Li, P. W Lau, T. W Wong, 

Chronic effects of ambient air pollution on 

respiratory morbidities among Chinese 

children: a cross-sectional study in Hong 

Kong, BMC Public Health 14 (2014) 105. 

[15] D. Ware, J. Lewis, S. Hopkins, B. Boyer, C. 

Noonan, T. Ward, Sources and perceptions of 

indoor and ambient air pollution in rural 

Alaska, J Community Health 38 (2013) 773-

780. 

[16] G. C. Rhoderick, 2013, The National Institute 

of Standards and Technology ambient level 

methane in air Standard Reference Material 

historical record, Anal Bioanal. Chem, 405 

(2013) 369-375. 

[17] H. H. Kim, C. S. Lee, J. M. Jeon, S. D. Yu, C. W. 

Lee, J. H. Park, D.C  Shin, Y. W Lim, Analysis of 

the association between air pollution and 

allergic diseases exposure from nearby 

sources of ambient air pollution within 



 

 

 

Pervez et al., J. mt. area res. 02 (2017) 16-22 

22 
J. mt. area res., Vol. 2, 2017 

elementary school zones in four Korean cities, 

Environ. Sci. Pollut. Res. Int 20 (2013) 4831-

4846. 

[18] M. J. Strickland, K. M. Gass, G. T. Goldman, J. 

A. Mulholland, Effects of ambient air pollution 

measurement error on health effect 

estimates in time-series studies: A simulation-

based analysis, J Expo. Sci. Environ. Epidemiol 

25 (2013) 160-166. 

[19] S. Kumar, M. K. Verma, and A. K Srivastava, 

ultrafine particles in urban ambient air and 

their health perspectives, Rev. Environ. Health 

28, (2013) 117-128. 

[20] S. M. Garcia, G. Domingues, C. Gomes, A. V. 

Silva, S. M. Almeida, Impact of road traffic 

emissions on ambient air quality in an 

industrialized area, J. Toxicol. Environ. Health 

A 76 (2013)429-439. 

[21] N. E. Latysh, G. A. Wetherbee, Improved 

mapping of National Atmospheric Deposition 

Program wet-deposition in complex terrain 

using PRISM-gridded data sets, Environ. 

Monit. Assess 184 (2012) 913-928. 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

[22] M. E. Fragala, Y. Aleeva, C. Satriano, 

Integration of metal organic chemical vapor 

deposition and wet chemical techniques to 

obtain highly ordered porous ZnO 

nanoplatforms, J. Nanosci. Nanotechnology 

11 (2011) 8180-8184.  

[23] J. P. Schoonmaker, A. H. Trenkle, D. C. Beitz, 

Effect of feeding wet distillers grains on 

performance, marbling deposition, and fatty 

acid content of beef from steers fed low or 

high-forage diets, J. Anim. Sci 88 (2010) 3657-

3665. 

[24] M. Anicic, M. Tomasevic, M. Tasic, S. Rajsic, A. 

Popovic, M.V. Frontasyeva, S. Lierhagen, and 

E. Steinnes, Monitoring of trace element 

atmospheric deposition using dry and wet 

moss bags: Accumulation capacity versus 

exposure time, J Hazard. Mater 171 

(2009)182-188. 

[25] NIOSH, NIOSH Regulations and Guidelines 

(2003). 

[26] R. J. Thompson, G. B. Morgan, L. J. Purdue, 

Analysis of Metallic Air Pollutants, At. Absorpt. 

Newsl. 9 (1970)195. 

[27] B. Mason, Principles of geochemistry, 3th 

edition, John Wiley and Sons, (1966). 

 This work is licensed under a Creative Commons Attribution 4.0 International License. 

http://creativecommons.org/licenses/by/4.0/
http://creativecommons.org/licenses/by/4.0/
http://creativecommons.org/licenses/by/4.0/