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Environ Eng Res > Volume 23(2); 2017 > Article
Al-Taani, Howari, Nazzal, and Yousef: Seasonal impact to air qualities in industrial areas of the Arabian Gulf region


Air quality conditions and pollution status have been evaluated in the industrial area between Sharjah and Ajman border in UAE. Daily concentrations of O3, CO, NO2, SO2, PM2.5, PM10, Total Volatile Organic Compounds (TVOC) and Total Suspended Particulate (TSP) have been monitored from Sept. 2015 to April 2016. The monthly average concentrations of O3, CO, NO2, SO2, TVOC were within the UAE ambient air quality standards during the survey period. However, PM10 and TSP levels exceeded the recommended limits in Sept. 2015, Oct. 2015 and March 2016. Temporal variations in air quality parameters showed highest levels in March 2016 for PM2.5, PM10, NO2, TVOC and TSP, whereas O3, SO2 and CO showed relatively low values in this month. PM2.5 levels in ambient air were above the EPA guideline of 35 μg/m3 in all months. PM2.5 was the critical ambient air pollutant with Index for Pollutant (Ip) values varying from 103–209, indicating Air Quality Index categories of unhealthy for sensitive groups (62.5%) to unhealthy (25%) to very unhealthy (12.5%). The Ip average values of PM2.5 decreased from Sept. 2015 to reach lowest value in Dec. 2015 before increasing gradually, peaking in March 2016. These results suggest the potential health risks associated with PM2.5 is low in winter, where the prevailing meteorological conditions of lower temperatures, higher humidity, higher wind speed reduced particulate matter. The results revealed the industrial area is impacted by anthropogenic and natural sources of particulate matter.

1. Introduction

Short- and long-term exposure to ambient air pollution has been associated with several adverse health effects, particularly among sensitive groups [110]. Air pollution has also become a leading cause of death in the world and has imposed a heavy burden on government’s health care budgets [11].
Atmospheric pollutants can directly or indirectly affect ecosystems, reduce visibility, cause property damage and harm to the human. They may undergo changes in their compositions between their emission and their detection. In addition to its local effects, the impacts of air pollution are extended to a global scale, where climate change and global warming are likely to aggravate food shortages, alter water resources and damage the infrastructure in certain countries (rising sea-levels and extreme weather). Thousands of chemicals emitted into the air are considered air pollutants. The WHO has identified particulate matter (PM), nitrogen dioxide (NO2), carbon monoxide (CO), sulfur dioxide (SO2) and ozone (O3) as the pollutants with greatest public health importance. The United States National Ambient Air Quality Standard designates all of the above plus airborne lead as criteria pollutants.
CO, NOx, and part of Volatile Organic Compounds (VOCs) are largely traffic-related emissions, whereas O3 and NO2 are secondary pollutants photochemically formed from precursors [12, 13]. SO2 is primarily originated from power plants and heavy industry. The ground-level O3 formation also depends the concentrations of NOx, VOCs, and their VOCs:NOx ratios [14]. The NO2, a major O3 precursor [15, 16] is related to anthropogenic combustion emissions. It is subject to atmospheric oxidation to form nitrate aerosol, which effects PM10 levels [17]. VOCs are oxidized to form CO [18]. The SO2 may contribute to photo-formation of O3 with the NOx and VOCs under the intense insulation [19, 20]. Therefore, the photochemistry of the NO–NO2–O3 system in ambient air is locally controlled by the reactions with CO and many VOCs and even SO2 [13, 20].
United Arab Emirates (UAE) is one of the fastest growing countries. The recent economic and industrial development in UAE has substantially impacted the air quality and increased the severity of air pollution. This requires frequent inspection and monitoring program of the levels of pollutants in ambient air to reduce emissions and define environmentally friendly economic growth plans.
The industrial area between Sharjah and Ajman, is becoming one of the cornerstones of the UAE industrial development. In response to the growing public concern and to communicate the health significance of air pollution to the public, the authority is developing an air quality monitoring and control center. The measurements are used to determine the human exposure to pollutants and assess trends of atmospheric pollution. In addition, this air quality monitoring network provides data to decision makers in a timely manner to determine whether these industrial facilities maintain compliance with national ambient air quality requirements.
This work is intended to characterize the ambient levels of air pollution in the industrial area between Sharjah and Ajman, UAE. This is likely to provide best available evidence in supporting public health policy decision making and support emission strategy development and to activate emergency control procedures that prevent or alleviate air pollution episodes.

2. Materials and Methods

2.1. Description of Study Area

The industrial area between Sharjah and Ajman in UAE (Fig. 1), has a unique geographic location with a multi-access to neighboring and global countries through land, sea and air. It is fast becoming one of the cornerstones of the UAE industrial development. The management body of the industrial area has published the “Engineering, Environmental, Health and Safety Regulations” which specifies its Engineering Policy and Health, Safety & Environment (HSE) Policy and expects its investors to partner with them in their objective of promoting good HSE performance which will ensure long term success of the businesses. These regulations urge the investors to accord prime significance to HSE performance with business performance. To provide air pollution data to its decision makers and investors in a timely manner, it has developed an air quality monitoring network that has both mobile and fixed monitoring stations, as well as the state of art sensors technology. The recorded measurements are used to determine the human exposure to pollutants and can be combined with trace/background monitoring as well as stack monitoring to assess an organization’s contribution to pollution, and the effect is usually compared to natural levels.
The UAE Federal Environment Agency and several international regulatory bodies (ex.: EPA, WHO, etc.) identified six major air pollutants called “criteria pollutants” (Table 2). These air pollutants are particulate matter (PM10), SO2, NO2, O3, CO and lead (Pb). Fine particulate matter (PM2.5) was later added as an additional criteria pollutant. In addition, VOCs are regulated as a criteria pollutant because they are precursors to O3.
UAE is part of prevailing arid climate, with mild winter season that lasts from November through March. The hot and humid summer season extends from April through September. In the industrial area the strong winds are generally from the N-NNW to S-SSE direction, wind rose diagram is presented in Fig. 2. The average daily temperatures varied between 17.0°C (occurring mainly in winter) and 31.8°C during 2015 with a maximum temperature of around 40°C (in summertime). The average maximum relative humidity is around 87%. The highest rainfall during winter seasons can reach up to 79 mm.

2.2. Air Quality Monitoring Stations

Five monitoring stations were used to measure the ambient air quality in the industrial area (Fig. 1). The airpointer and ecotech air quality sensors were used to monitor airborne pollutants. Ecotech sensors were configured and fixed to be stationary and airpointers as mobile stations (model numbers and manufacturing countries are tabulated in Table 1). The daily baseline ambient air quality was investigated through monitoring concentrations of PM2.5, PM10, Total Suspended Particulate (TSP), SO2, NO2, CO, Total VOCs and O3. Those parameters were measured daily from Sept. 2015 to April 2016.
A 24-h sample was taken from midnight to midnight, at frequency interval, to ensure full coverage for 7 d a week using airpointers and for 30 (or 31) d using ecotech analyzers. Data required for comparison to the National Center of Meteorology & Seismology have specific completeness requirements. These completeness requirements generally start from completeness at hourly and 24-h concentration values. The VOC was collected using MiniRAE 3000. Its Photoionization Detector’s (PID) extended range of 0 to 15,000 ppm makes it an ideal instrument for applications from industrial hygiene, for leak and HazMat detection.

2.3. Air Quality Index (AQI)

The EPA has a standardized AQI calculation methodology for the key air pollutants. The following equation represents the model using linear interpolation for single pollutants. Using the Eq. (1) with the aid of the EPA values of breakpoints [21] and the pollutant concentration data, the Index for Pollutant (Ip) is calculated. The highest Ip value represents the daily AQI.
where Ip is the index for pollutant, p; Cp is the concentration of pollutant, p; CH is the breakpoint that is greater than or equal to Cp; CL is the breakpoint that is less than or equal to Cp; IH is AQI value corresponding to CH; and IL is AQI value corresponding to CL.

3. Results and Discussion

3.1. Air Quality Conditions

The statistical analysis of the monthly average concentrations of O3, CO, NO2, SO2, PM2.5, PM10, TSP and TVOC are tabulated in Table 3. The concentrations of O3, CO, NO2, SO2 comply with the maximum allowable limits of the national air quality standards (Table 2 and Table 3). The monthly average concentrations of PM10 exceeded the recommended standard limit of 150 μg/m3 in Sept. 2015, Oct. of 2015 and in March 2016, with highest values were observed in the latter month. Exceptionally high concentrations of PM10 during the episode of dust storm were due to transport from local and regional deserts.
The ambient air levels of PM2.5 were above the EPA (2015) [21] guidelines of 35 μg/m3 in all months, with slightly above the limit values observed in Nov. and Dec. of 2015 (Table 2 and Table 3). The TSP showed monthly average values that exceeded the maximum allowable limit in Sept. 2015, Oct. 2015 and March 2016, though there have been some events with elevated daily levels exceeding the allowable standards, in the remaining months.
TVOC showed lower monthly average levels compared with the national standards limit of 20 mg/m3. Relatively higher levels of TVOC were measured from Feb. 2016 through April 2016 and lowest values observed in Dec. 2015 (corresponding to periods of lower use of fossil fuel and industrial activities).
The VOCs are precursors of O3. Under appropriate ambient conditions, VOCs and NOx are photochemically reacted to form smog. Smog is composed of O3 and particles, among others. Therefore, the VOCs levels are decreased as they are converted to O3, during which higher O3 values are observed. However, when the weather conditions are not favorable, ambient air VOCs show higher values whereas O3 levels remain at lower levels. Unlike other place, for example [17], which showed peak in O3 levels in springtime (March, April and May) compared to the summer (June, July and August) due to the summertime monsoon and clouds. In addition, [17] found that the lowest O3 level was observed in the winter due to the low photolysis.
The kinetics associated with VOC → CO → CO2 reaction during combustion, is explained by a composite behavior [22]. At early stage of combustion, VOCs produce CO (VOCs levels are reduced whereas CO increases). As the reaction continues, both are reduced while CO2 consistently increases [22, 23]. In addition, CO can form from atmospheric oxidation of VOCs [18], where the concentrations of VOCs decreased as they were converted to CO.
As mentioned earlier, the CO, NOx, and part of VOCs are largely traffic-related emissions, whereas O3 and NO2 are secondary pollutants photochemically formed from precursors [12, 13]. SO2 is primarily originated from power plants and heavy industry.
It is noteworthy to mention that due to the prevailing arid to hyper-arid climate of the UAE, it experiences high temperatures throughout the year, except in winter, where the average temperature drops to about 17ºC (and rarely deceases below to 6ºC). Air-conditioning is required almost year-round except in winter. Electricity consumption for air-conditioning is high (reaching, for examples, over 51% of the annual electricity consumption in residential area). In addition, industries in UAE require no heating considering the arid climate (hot temperatures with high relative humidity). The industrial demand of energy for cooling is at low levels during winter. Therefore, the overall energy consumption decreases considerably in wintertime, with reduced levels of TVOCs emissions.

3.2. Critical Ambient Air Pollutants

The critical pollutant is identified as the pollutant with the highest Ip value of the six ambient air pollutant, which also represents the daily AQI category [21]. The Ip and AQI values were calculated based on a 24-h average for SO2, PM10, and PM2.5, and they were calculated based on peak 8-h running average for O3 and CO. The Ip and AQI values for NO2 were calculated based on one-hour average as per standard procedure [24].
Air quality monitoring data were collected for each of the five monitoring stations for 30 (or 31) d (NO2 and SO2 data were unavailable for April 2016). These data were used to identify the dominant AQI values in the industrial area. The calculated Ip values for CO ranged from 3–8 with a mean value of 5.29 representing good to moderate AQI category. However, O3 showed Ip values varying between 4 and 25 with an average of 17.25 corresponding to good AQI class. Similarly, the Ip values for NO2 and SO2 ranged from 16–44 (with a men value of 27.29) and from 1–4 (with a men value of 2.67), respectively, corresponding to good AQI category.
Except for March 2016, the monthly average of Ip values for PM2.5 were consistently higher than that for PM10 (from 77–116). This indicates that PM2.5 was the critical ambient air pollutant that can cause potential health impacts during the study period and that the air quality categories were determined by AQI values for PM2.5 parameters.
PM2.5 showed Ip values varying from 103–209 with an average of 141. These values indicate AQI categories of unhealthy for sensitive groups (62.5%) to unhealthy (25%) to very unhealthy (12.5%). The Ip average values of PM2.5 tended to decrease from Sept. 2015 to reach lowest value in Dec. 2015 before increasing back gradually, peaking in March 2016. These results suggest that the potential health risks related to PM2.5 concentrations is low in winter. This is probably attributed to the prevailing meteorological conditions of lower temperatures, higher humidity and higher wind speed, and more rainy days helped the dissipation of PM and provided relatively better and homogenous ambient air quality [25].
The temporal variations in ambient air quality parameters are presented in Fig. 3 with highest levels were observed in March 2016 for PM2.5, PM10, NO2, TVOC and TSP. In contrast, O3, SO2 and CO tended to show relatively low values in March 2016.
These higher values of particulate matter represent the end of winter and beginning of spring season with frequent dust events. In addition, these are likely related to increased rate of industrial activities following the winter season with subsequent increased use of fossil fuel.

3.3. PM2.5/PM10 Ratio

The PM2.5/PM10 ratio, presented in Fig. 4, has been used to assess the aerosol sources and types [26]. The high ratios generally indicate the dominance of anthropogenic aerosols whereas the low ratios indicate prevailing dust aerosols. Anthropogenic sources produce more fine particles (traffic emissions or burning activities), whereas natural sources (windblown or road dust) contribute higher quantities of coarse particles resulting in a lower ration [2731].
The relative high average ratios of PM2.5/PM10 observed during the study period suggest significance contribution of fine particles and that the atmospheric particles are related to anthropogenic sources (industrial activities and heavy traffic). The highest PM2.5/PM10 ratio coincided with the high concentrations of CO and O3 (Fig. 3 and Fig. 4) indicating predominant emissions from anthropogenic sources.
[27] reported lower ratio in residential area compared to urban area. Also, [32] indicated that PM2.5 is dominant within immediate proximity to industrial area.
Combustion sources (traffic, biomass burning and industrial processes) emit more fine particles, whereas mechanical processes (crushing, gridding and construction activities) contribute to coarse fraction of PM [33].
Monthly variations in PM2.5/PM10 ratio were also apparent. There has been generally a slight decrease in the ratio from Sept. 2015 through Jan 2016, before relatively an abrupt increase in PM2.5/PM10 ratio was observed in the following months (except for March 2016).
The lowest average ratio observed for March 2016 (Fig. 4) compared to other months suggests that during this month the area has experienced dust storms and that they were potentially the dominant source of particulate matter. [27] reported that coarse particles from dust storm contribute significantly to PM10. However, higher levels of TVOC recorded during March 2016 (Fig. 3) indicate that anthropogenic sources, from burning fossil fuel, were common. These results suggest that industrial area was impacted by both sources of aerosols, with prevailing anthropogenic sources from Nov. 2015 through Jan. 2016 and in March 2016.
In addition to combustion sources (traffic, fossil fuel burning and industrial processes) which emit more fine particles and increase the ratio, the increasing trend after Jan. 2016 (except for March 2016) may be attributed to the meteorological conditions. High wind velocity, rainfall and relative humidity during this period (winter season) reduce large particle emissions leading to increase in the PM2.5/PM10.

4. Conclusions

Five monitoring stations (fixed and stationary) were used to measure the daily baseline ambient air quality in the industrial area between Sharjah and Ajman border in UAE. PM2.5, PM10, TSP, SO2, NO2, CO, TVOCs and O3 were measured from Sept. 2015 to April 2016. The monthly average concentrations of air parameters were within the UAE ambient air quality standards during the survey period, except for PM10 and TSP in Sept. 2015, Oct. 2015 and March 2016. PM2.5 was the critical pollutant with index values indicating AQI categories of unhealthy for sensitive groups (62.5%) to unhealthy (25%) to very unhealthy (12.5%). The results revealed the industrial area is impacted by anthropogenic and natural sources of PM. However, in such a fast growing industrial area surrounded by desert region, it is likely that PM exceeds the acceptable limits due to frequent dust events. These monitoring data can help the management authority to communicate information to investors and public about the current status of ambient air quality and advise for further precautionary measures to maintain healthy air quality conditions.


1. Barrett S, Graddy KFreedom, growth, and the environment. Environ Dev Econ. 2000;5:433–456.

2. Analitis A, Katsouyanni K, Dimakopoulou K, et alShort-term effects of ambient particles on cardiovascular and respiratory mortality. Epidemiology. 2006;17:230–233.
crossref pmid

3. Burnett RT, Cakmak S, Brook JR, Krewski DThe role of particulate size and chemistry in the association between summertime ambient air pollution and hospitalization for cardiorespiratory diseases. Environ Health Perspect. 1997;105:614–620.
crossref pmid pmc

4. Goldberg MS, Burnett RT, Bailar JC, et alThe association between daily mortality and ambient air particle pollution in Montreal, Quebec. 2. Cause-specific mortality. Environ Res. 2001;86:26–36.
crossref pmid

5. Burnett RT, Cakmak S, Raizenne ME, et alThe association between ambient carbon monoxide levels and daily mortality in Toronto, Canada. J Air Waste Manag Assoc. 1998;48:689–700.
crossref pmid

6. Goldberg MS, Giannetti N, Burnett RT, Mayo NE, Valois MF, Brophy JMA panel study in congestive heart failure to estimate the short-term effects from personal factors and environmental conditions on oxygen saturation and pulse rate. Occup Environ Med. 2008;65:659–666.
crossref pmid

7. Ostro B, Broadwin R, Green S, Feng WY, Lipsett MFine particulate air pollution and mortality in nine California counties: Results from CALFINE. Environ Health Perspect. 2006;114:29–33.
crossref pmid

8. Zanobetti A, Schwartz JThe effect of fine and coarse particulate air pollution on mortality: A national analysis. Environ Health Perspect. 2009;117:898
crossref pmid pmc

9. Lelieveld J, Evans JS, Fnais M, Giannadaki D, Pozzer AThe contribution of outdoor air pollution sources to pre-mature mortality on a global scale. Nature. 2015;525:367–371.
crossref pmid pdf

10. Burnett RT, Pope CA, Ezzati M, et alAn integrated risk function for estimating the global burden of disease attributable to ambient fine particulate matter exposure. Environ Health Perspect. 2014;122:397–403.
crossref pmid pmc

11. World Bank. Cost of pollution in China: Economic estimates of physical damages. Rural Development, Natural Resources and Environment Management Unit; Washington D.C.: 2007.

12. Kuttler W, Strassburger AAir quality measurements in urban green areas – A case study. Atmos Environ. 1999;33:4101–4108.

13. Masiol M, Agostinelli C, Formenton G, Tarabotti E, Pavoni BThirteen years of air pollution hourly monitoring in a large city: Potential sources, trends, cycles and effects of car-free days. Sci Total Eviron. 2014;494/495:84–96.

14. Nevers NDAir Pollution Control Engineering. 2nd edMcGraw-Hill Companies, Inc.; New York: 2000. p. 571–573.

15. Gilge S, Plass-Duelmer C, Fricke W, et alOzone, carbon monoxide and nitrogen oxides time series at four alpine GAW mountain stations in central Europe. Atmos Chem Phys. 2010;10:12295–12316.
crossref pdf

16. Lamsal L, Martin R, van Donkelaar A, et alIndirect validation of tropospheric nitrogen dioxide retrieved from the OMI satellite instrument: Insight into the seasonal variation of nitrogen oxides at northern midlatitudes. J Geophys Res Atmos. 2010;115:D05302
crossref pdf

17. Yoo JM, Jeong MJ, Kim D, et alSpatiotemporal variations of air pollutants (O3, NO2, SO2, CO, PM10, and VOCs) with land-use types. Atmos Chem Phys. 2015;15:10857–10885.
crossref pdf

18. Wang Y, McElroy MB, Munger JW, et alVariations of O3 and CO in summertime at a rural site near Beijing. Atmos Chem Phys. 2008;8:6355–6363.
crossref pdf

19. Klemm O, Stockwell WR, Schlager H, Krautstrunk MNOx or VOC limitation in East German ozone plumes? J Atmos Chem. 2000;25:1–18.

20. Derwent R, Jenkin M, Saunders S, et alPhotochemical ozone formation in north west Europe and its control. Atmos Environ. 2003;7:1983–1991.

21. EPA (United States Environmental Protection Agency). Technical assistance document for reporting of daily air quality—the air quality index (AQI). EPA-454/B-09-001. U.S. Environmental Protection Agency; North Carolina: 2009.

22. Liu DHF, Lipták BGAir pollution. Boca Raton: Lewis Publishers; 2000.

23. Al-Momani T, Al-Taani AA, Al-Nasser A, El-Radaideh NAn assessment of automobile emissions in Irbid, Northwest Jordan. Electron J Appl Stat Anal. 2011;4:91–102.

24. EPA (U.S. Environmental Protection Agency). 2015. National Ambient Air Quality Standards (NAAQS). Available from: https://www.epa.gov/criteria-air-pollutants/naaqs-table

25. Jassim MS, Coskune GAssessment of spatial variations of particulate matter (PM10 and PM2.5) in Bahrain identified by air quality index (AQI). Arab J Geosci. 2017;10:19
crossref pdf

26. Sugimoto N, Shimizu A, Matsui I, Nishikawa MA method for estimating the fraction of mineral dust in particulate matter using PM2.5-to-PM10 ratios. Particuology. 2016;28:114–120.

27. Zakey AS, Abdel-Wahab MM, Pettersson JBC, Gatari MJ, Hallquist MSeasonal and spatial variation of atmospheric particulate matter in a developing megacity, the Greater Cairo, Egypt. Atmosfera. 2008;21:171–189.

28. Querol X, Alastuey A, Rodriguez S, et alPM10 and PM2.5 source apportionment in the Barcelona Metropolitan area, Catalonia, Spain. Atmos Environ. 2001;35:6407–6419.

29. Kulshrestha A, Satsangi PG, Masih J, Taneja AMetal concentration of PM2.5 and PM10 particles and seasonal variations in urban and rural environment of Agra, India. Sci Total Environ. 2009;407:6196–6204.
crossref pmid

30. Spindler G, Gruner A, Muller K, et alLong-term size segregated particle (PM10, PM2.5, PM1) characterization study at Melpitz-influence of air mass inflow, weather conditions and season. J Atmos Chem. 2013;70:165–195.

31. Al-Taani AA, Rashdan M, Khashashneh SAtmospheric dry deposition of mineral dust to the Gulf of Aqaba, Red Sea: Rate and trace elements. Mar Pollut Bul. 2015;92:252–258.

32. Ehrlich C, Noll G, Kalkoff WD, Baumbach G, Dreiseidler APM10, PM2.5 and PM1.0 – Emissions from industrial plants – Results from measurement programmes in Germany. Atmos Environ. 2007;41:6236–6254.

33. Mukherjee A, Agrawal MWorld air particulate matter: Sources, distribution and health effects. Environ Chem Lett. 2017;15:283–309.
crossref pdf

Fig. 1
Location map of the industrial area between Sharjah and Ajman border, UAE, and the locations of air quality monitoring stations.
Fig. 2
Wind rose diagram showing the prevailing wind directions and speed at the industrial area during the study period.
Fig. 3
Ambient air quality parameter from Sept. 2015 to April 2016.
Fig. 4
Monthly average PM2.5/PM10 ratios.
Table 1
Model Numbers and Manufacturing Countries of Ecotech Sensor and Analyzers Used for Ambient Air Quality Monitoring
S. No. Parameter Model offered Make
1 SO2 Serinus 50 Ecotech, Australia
2 O3 Serinus 10 Ecotech, Australia
3 NOx Serinus 40 Ecotech, Australia
4 CO Serinus 30 Ecotech, Australia
5 BTEX(Benzene, Toluene, Ethylbenzene & xylene) Airmo VOC BTEX GC866 Chromatotec, France
6 PM10 BAM 1000 (PM10) Metone, USA
7 PM2.5 BAM 1100 (PM2.5) Metone, USA
8 TSP BAM 1000 (PM10) Metone, USA
Table 2
The UAE Ambient Air Quality Standards
Substance Max allowable limits (μg/m3) Average time
SO2 350 1 h
150 24 h
60 1 y
CO 30 (mg/m3) 1 h
10 (mg/m3) 8 h
NO2 400 1 h
150 24 h
O3 200 1 h
120 8 h
TSP 230 24 h
90 1 y
PM10 150 24 h
Pb 1 1 y
Table 3
Summary Statistics of Ambient Air Quality from Sept. 2015 to April 2016

μg/m3 mg/m3 μg/m3 μg/m3 μg/m3 μg/m3 μg/m3 mg/m3
Sept. 2015
Mean 17.89 0.38 24.44 2.03 74.07 185.7 270.18 0.15
SD 7.03 0.13 6.81 0.2 86.79 100.99 112.37 0.12
Min 0.53 0.18 6.98 1.7 33.96 79.8 96.55 0
Max 33.55 0.65 38.85 2.46 524.15 585.58 550.59 0.44
Count 30 30 30 30 30 30 30 30

Oct. 2015
Mean 18.33 0.4 24.55 0 57.82 159.09 240.84 0.12
SD 4.99 0.08 5.79 0 46.01 44.63 161.8 0.05
Min 10.16 0.25 12.53 0 20.24 63.56 75.8 0
Max 31.66 0.58 36.68 0 277.69 238.89 856 0.14
Count 31 31 31 31 31 31 31 31

Nov. 2015
Mean 24.67 0.43 17.88 1.09 36.94 139.35 191.84 0.19
SD 9.02 0.13 14.54 0.68 12.36 62.46 84.31 0.083
Min 10.49 0.21 0.35 0.07 12.479 71.57 100.17 0.10
Max 40.7 0.70 42.57 2.04 64.47 378.97 501.05 0.50
Count 30 30 30 30 30 30 30 30

Dec. 2015
Mean 19.56 0.49 28.33 1.62 36.29 117.90 157.53 0.003
SD 7.64 0.17 9.21 0.92 11.70 38.61 52.67 0.01
Min 9.44 0.23 8.30 0.65 5.3 26.31 71.37 0
Max 37.98 0.978 40.46 3.33 65.22 202.52 303.98 0.08
Count 31 31 31 31 31 31 31 31

Jan. 2016
Mean 22.18 0.77 28.00 3.13 44.06 151.94 174.54 0.12
SD 8.11 1.12 10.75 1.19 16.98 48.04 57.63 0.13
Min 9.66 0.218 4.62 1.07 13.35 48.87 61.71 0
Max 45.79 6.66 44.10 5.83 77.38 256.45 292.48 0.29
Count 31 31 31 31 31 31 31 31

Feb. 2016
Mean 17.69 0.54 35.21 3.06 50.98 108.83 186.05 2.06
SD 12.05 0.12 9.00 0.92 15.11 35.22 79.66 1.18
Min 0.638 0.32 7.83 1.742 24.66 26.31 74.53 0
Max 48.14 0.78 51.48 5.02 86.60 201.72 417.46 2.77
Count 28 28 28 28 28 28 28 28

March 2016
Mean 4.62 0.45 47.08 2.56 158.49 831.7 283.46 3.74
SD 5.47 0.1 8.61 1.19 297.18 320.73 248.65 0.78
Min 0.72 0.28 21.13 −0.77 21.1 72.58 83.32 2.16
Max 20.1 0.66 62.22 5.35 985 985 985 5.14
Count 31 31 31 31 31 31 31 31

April 2016
Mean 27.48 0.66 - - 50.98 108.83 186.05 2.88
SD 11.25 0.27 - - 15.12 35.22 79.66 0.94
Min 8.66 0.06 - - 24.66 26.31 74.53 2.06
Max 49.48 1.03 - - 86.6 201.72 417.46 7.25
Count 30 30 - - 30 30 30 30
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