Academia.eduAcademia.edu

A Study of Air Pollutants During Episodes

AI-generated Abstract

This study investigates air pollution levels in Egypt, focusing on various air pollutants and their health impacts within urban environments. A comprehensive monitoring network has been established to measure pollutant concentrations, evaluate air quality against both local and international standards, and assess the required ventilation for public spaces to ensure healthy air for residents. The findings highlight critical areas of pollution and suggest measures for abatement, while emphasizing the importance of ongoing monitoring and regulatory compliance.

B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 A Study of Air Pollutants During Episodes Bjarne Sivertsen1, Haytham A.Ahmed2, Heba F.Ahmed2, Mai E.Ahmed3 1) Task Manager of Air Quality, EIMP programme, EIMP/EEAA, Maadi, Cairo, Norwegian Institute for Air Research 2) Air Quality Counterpart EIMP programme EEAA, Maadi, Cairo. 3) Ref. Lab. Counterpart EIMP programme EEAA, Maadi, Cairo. (NILU), N-2007 Kjeller, Norway. Abstract During the last few months Egypt was exposed to high levels of Air Pollutants due to several factors. Meteorological conditions combined with emissions of air pollutants gave rise to high concentrations in central part of Cairo. The concentrations of different pollutants varied considerably in space and time.A national Air Quality Network has been established by Egyptian Environmental Affairs Agency (EEAA) in co-operation with Danish International Development Assistance (Danida) to monitor the status of the air environment of Egypt.The Air Quality network consists of 42 stations located in the Greater Cairo area (14 sites), Alexandria (8 sites), Delta and Canal area (10 sites), Upper Egypt (9 sites) and Sinai (1 site).The network design, preparations and installation was carried out by EIMP during the period from 1997 till the end of 1999. The operations, data retrieval, Quality Assurance/Quality Control (QA/QC) as well as calibrations and data reporting are undertaken by two institutes: the Center of Environmental Hazard Mitigation (CEHM) at Cairo University and the Institute of Graduate Studies and Research (IGSR) at Alexandria University.The recorded data occasionally showed high concentrations exceeding the Air Quality Limit values as given by Law No. 4 of Egypt. Suspended particles (given by PM10) is normally the main problem in Egypt. Under normal conditions the concentrations of PM10 is very high in Egypt compared to the Air Quality Limit value. During what so called Air Pollution episodes it may exceed the limit values by more than a factor ten. Other pollutants may exceed the limit values by a factor 2 to 8 during theses episodes.There are several reasons for these cases: • Specific large scale meteorological conditions give rise to strong inversions over Cairo, • High humidity combined with low wind speeds prevail during the inversions situations, • Emissions of air pollutant at the surface coming from open air waste burning, traffic and small enterprises, • Sand storm from desert area around Cairo The concentration levels of different pollutants may vary depending on the type of episode and the variability in source strength. 345 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 1. EIMP Air Quality Monitoring Programme One of the major goals of EEAA is to keep a good level of the Air Environment related to local/international standards. Based on this goal EEAA in co-operation with DANIDA has established Air Quality Monitoring Network consists of 42 measurements sites Delta & Canal Abu Zabel Alex. Shoubra El Kheima Abbassyia Delta Cairo Damiatta Kolaly El-Fayum Port Said Kafr Dawar El-Minya Ras Mohammed Damanhur Kafr El Zayat Giza El Mansura El Mahalla Ismailia Tanta Assyut1,2 10 of Ramadan Cairo 6 of October Nag Hammadi Louxor Edfu Gomhoryia Nasr City Cairo Pyramides Maadi Suez KomOmbo Aswan Egy Cairo Alexandria Abu Keir Tabbin South El Asafra Alex. Regional Shouhada square EEAA/EIMP Air Quality Measurement Sites in Egypt IGSR Gheat El Inab El Max Figure1: The EEAA/EIMP Air Quality Measurement Sites in Egypt. The network has been established to provide an image for the Air Environment for the decision makers and normal people. The network is being operated by Center of Environmental Hazard Mitigation (CEHM) in Greater Cairo, Canal area and Upper Egypt. and by Institute of Graduate Studies and Research (IGSR) in Alexandria and Delta area. CEHM is operating 27 sites and IGSR is operating 15 sites distributed in different no of area description. Distribution of Sites and Area type is presented in Table no.1 rea Type Cairo Alex. Delta& Upper Canal Egypt Industrial 3 3 3 2 Urban 1 1 3 4 Residential 4 2 2 2 Street/Road 3 1 Regional/Backgr. 1 1 Mixed areas 2 2 1 Total 14 8 10 9 346 Sinai 1 1 Total 11 9 10 3 3 5 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 A total of 14 sites are located in Greater Cairo area, 8 sites in Alex., 10 sites in Delta and Canal area, 9 sites in Upper Egypt and 1 site in Sinai. In addition to the above mentioned monitoring and sampling sites, about 20 sites have been selected for undertaking passive sampling for SO2 and NO2 on monthly and quarterly basis. 2. Air Quality Limit values The assessment of the air quality is presently being linked to the air pollution levels and to the populations distribution. To protect the health, the concentrations of selected harmful air pollutants should be limited and related to given ambient air quality standards. Several investigations have been performed by Egyptian Environmental Affairs Agency to estimate the impact to human health from various air pollutants. Air Quality limit values are given in the Executive Regulations of the Environmental Law no. 4 of Egypt (1994). These Air Quality Limit values are presented in Table2. Table 2: Ambient Air Quality Limit values as given by Law no.4 for Egypt (1994) compared to the World Health Organization (WHO) Air Quality guideline values. Pollutant Sulphur Dioxide Nitrogen Dioxide (NO2) Ozone (O3) Carbon monoxide(CO) Black Smoke(BS) Total Suspended Particles(TSP) Particles less than 10µm(PM10) Lead (Pb) Averaging time 1 hour 24 hour Year 1 hour 24 hour Year 1 hour 8 hours 1 hour 8 hours 24 hours Year 24 hours Year 24 hours Year Maximum Limit Value WHO Egypt 500 (10 350 min) 125 150 50 60 200 400 150 40-50 150-200 200 120 120 30000 30000 10000 10000 50 150 60 230 90 70 70 0.5-1 1 Indoor air Closed and semi-closed public places according to the environmental Law should also have adequate ventilation systems appropriate to their sizes and capacities, as well as to the type of activities exercised therein, to ensure the renewal of air, its cleanness and the maintenance of a suitable level of temperature. 347 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 Table no. 3 indicates the quantities of air necessary for ventilating public places to avoid problems in breathing of air : Table (3): Air needed for ventilating of closed and semi-closed places Quantity Of External Air? dm3/min/person 140-280 280-420 420-560 560-850 850-1700 Type of Place and activity Places with high ceiling, banks, lecture halls, places of workshops, large public places, theater, non-smoking rooms Apartments, hairdressers, hotel rooms, rooms with limited smoking Cafeterias, small restaurants, hospital rooms, restaurants, rooms with medium level of smoking Offices , clinics, rooms with high levels of smoking Night clubs or crowded rooms with high levels of smoking ?Without the use of Air Conditioners -Suitable spaces for each person shall not be less than 4.25m3 -Suitable floor area for each person shall not be less than 1.4m2 3.Historical background of Air Pollution in Egypt: 3.1-Sulphur Dioxide Very few representative data have been collected in the past concerning SO2 concentrations in Egypt. A few number of measurements undertaken in 1991/92 indicated that monthly mean level of SO2 in the Cairo atmosphere to be in the range of 100300µg/m³. 120 µg/m 100 80 Residential 60 City Center 40 SubUrban 20 0 Winter Spring Summer Autumn Figure 2: Historical Overview for SO2 concentrations in Cairo. 348 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 Table 3 shows that the annual mean concentrations of SO2 in the measurement stations during 1991/1992 were 40µg/m3 in the suburban area, 55µg/m3 in residential area and 84 µg/m3 in the atmosphere of the city center . Table 3 also shows that the 24-hour concentrations in the air of the urban area may peak to more than 300µg/m³. Table4: Sulphur dioxide concentrations in Cairo City atmosphere 1991/1992 Season Winter Spring Summer Autumn Mean Monthly Max 24 hr Max Residential 44 52 66 56 55 76 120 Cairo city City Center 65 72 112 86 84 127 308 Suburban 38 40 46 35 40 54 86 3.2.Total suspended Matter (TSP) The measured annual TSP levels during 1989 to 1991 of about 500-1100µg/m3 are far in excess of WHO guideline of 60-90µg/m3. Moreover it may be noted that, the maximum 24 hr concentration sometimes peaked to more than 1000µg/m3 in the urban districts. 3.3.Oxides of Nitrogen During 1979, Monthly mean NO2 concentrations in the city center of Cairo were 380µg/m3 in January – March, 400µg/m3 in April – July, and 570-760µg/m3 in AugustDecember.The marked maximum NOx concentrations during May and June are connected with increased traffic. 4.Reasons of Air Pollution Episodes Reasons of Air Pollution Episodes can be divided into two main categories based on the polluting sources into Natural and Man-Made Episodes. An exclusive example for the natural episodes is the episodes which we have faced during the last year (adverse weather conditions with low and variable winds, high humidity and strong temperature inversion at few hundred meters above the surface combined with the usual emissions of Air Pollutants). Sand Storm also is considered as an episode from the above type which is mainly generated from high wind speed covering large open area(may be the western desert). The man-made episodes usually consists of open waste burning with high emissions in the direction of prevailing wind direction with slightly high wind speed. 349 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 sometimes the two reasons combined together to generate intensive episode with relatively high concentrations of air pollutants (mainly black smoke). Three examples were hitting Egypt with high concentration of Air Pollutants will be presented in the following chapter. 12 March Episode: During the day of 12 March Cairo was facing adverse weather conditions with usual emissions causing the concentrations of Air Pollutants to increase in most of the Air Quality Measurement Sites. Weather and Meteorology At that time a low-pressure area was covering large part from Asia driving westerly and south westerly winds to blown on the eastern part of middle east, that is why local wind directions from around south was observed . At night, Temperature inversion was observed at height about 200m over the surface which make the pollutants settled down over the surface. In the morning the wind start to blow from north causing the emissions to come back to Cairo. Wind Direction Abbaseya_wd Wind Direction 360 270 180 90 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 Hour Figure3: Wind direction at Abbassyia station as seen from EIMP measurements. 350 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 Wind speed 5 Shoubra_ws 4.5 Abbaseya_ws 4 3.5 Ws 3 2.5 2 1.5 1 0.5 24 23 22 21 20 19 18 17 16 15 14 13 12 11 9 10 8 7 6 5 4 3 2 1 0 Figure4 : Wind speed at Shoubra and Abbassyia measurement sites Air Pollutants Concentrations SO2 Concentrations Although high concentrations were observed in most of the measurement sites, the concentration did not exceed the Air Quality Limit value of 350 µg/m3 . It is also interesting to observe that high concentrations recorded at Shoubra and Abbassyia which give strong evidence for the wind direction which was blown from around north at the same time. The maximum concentrations observed at Kolaly station was around the rush hours time 12 O’clock which may be due to local sources from diesel buses running around the station Slightly low concentrations were observed in Tabbin station during 12 march 351 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 250 shoubra abbaseya 200 Kolaly 100 50 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 hour Figure5: The recorded SO2 concentrations at Greater Cairo area PM10 Concentrations Thoracic particles have Very high concentrations observed at Kolaly and Tabbin at the rush hours due to the local sources at the two station. The continuous data observed at the two station exceeded the Air Quality Limit value of daily average by factor of 2-3 which was presenting risk for the population health in the City. 450 400 PM10 SO2 Tabbin 150 350 kolaly 300 tabbin 250 200 150 100 50 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 hour Figure6 : The PM10 concentrations at Kolaly and Tabbin stations. 352 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 18 January Episode (High concentration of PM10): The following figures represent the PM10 and meteorological data for Tabbin and Kolaly stations on January 18, 2000. 1400 1000 800 600 400 200 0 Hour 12 10 8 6 4 2 0 Hour 360 Wind direction Wind Direction (Degree) 270 180 90 4:00 2:00 0:00 22:00 20:00 18:00 16:00 14:00 12:00 10:00 08:00 06:00 04:00 02:00 0 00:00 PM10 (ug/m 3 ) 1200 Location og measurement sites and an indication of the average wind direction at day time on 18 January 2000 Time Figure 7: Pm10 and meteorology measured on 18 January 2000: a) Hourly average concentrations of PM10 measured at Tabbin b) Hourly wind speed measured at Tabbin c) Hourly wind direction measured at Tabbin 353 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 PM10 (ug/m 3 ) 1200 Kolaly 1000 800 600 400 200 0 Hour 14 Shoubra 12 10 8 6 4 2 0 Hour Wind Direction (Degree) 360 Wind direction 270 180 90 4:00 2:00 0:00 22:00 20:00 18:00 16:00 14:00 12:00 10:00 08:00 06:00 04:00 02:00 00:00 0 Time Figure 8:PM10 and wind measured on in 18 January 2000 a) Hourly concentration of PM10 measured at Qulaly b) Hourly wind speed measured at Shoubra c) Hourly wind direction measured at Shoubra On 18 January 2000, the wind speed increase from 6 to 12 m/s blowing from around south-south west at Tabbin and Shoubra ElKheima. The PM10 concentration increased from 400 µg/m3 to 1200 µg/m3 in Tabbin and Qulaly between 12:00 and 15:00 indicating that dust may have been transported from the desert areas. For SO2 concentrations: Due to high wind speed blowing around south-south west occurred in 18 January 2000 caused a decrease in SO2 concentration at Kolaly and Abbaseya and an increase in Tabbin station. 354 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 SO2 concentration increased at Tabbin station could be due to the brick factories and lead smelters that are located south of the station. At the others two stations Kolaly and Abasseya the SO2 concentration decrease due to the high wind speed that increase the dispersion of SO2 concentration. 300 Abbasseya SO2 Conc 250 Qualaly Tabbin 200 150 100 50 0 17-Jan 00:00 17-Jan 12:00 18-Jan 00:00 18-Jan 12:00 19-Jan 00:00 Figure 9: SO2 Concentration at Abasseya, Kolaly and Tabbin stations in 18 Jan 2000. 12 Abbasseya 10 Tabbin WS (m/s) 8 6 4 2 0 17-Jan 00:00 17-Jan 12:00 18-Jan 00:00 18-Jan 12:00 19-Jan 00:00 Figure10 : Wind speed measured at Abbaseya and Tabbin station in 18 Jan 2000 355 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 360 Wind Direction 270 180 90 Abbasseya Tabbin 0 17-Jan 00:00 17-Jan 12:00 18-Jan 00:00 18-Jan 12:00 19-Jan 00:00 Figure11 : Wind direction measured at Abasseya and Tabbin station in 18 Jan 2000 23 October 1999 Episode The main reason for the episode experienced by a large part of Cairo, was adverse weather conditions with low and variable winds, high humidity and a strong temperature inversion at a few hundred meters above the surface. The emissions of air pollutants released from a number of different sources near the surface in Cairo area added to a slowly transport of particles emitted from burning in Delta. PM10 Concentrations PM10 concentrations during the episode were extremely high reaching very high levels exceeding the daily Air Quality Limit value given by the Executive regulation of law no. 4 of Egypt by factor of 5 to 10. The smog cloud was consisting of thoracic particles combined with mix of unhealthy air pollutants. PM 10 - During 23 October 1999 1600 1400 PM10 - microgram/ m 3 1200 1000 Tebbin 800 Al Kolaly 600 400 200 23 21 19 17 15 13 11 9 7 5 3 1 0 Day Hours Figure12 : PM10 Concentrations at Tabbin and Kolaly station in Cairo. 356 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 The change of wind direction also from North to South direction can be presented in the Following figure. Direction degree Wind Direction Tebbin 23 October 1999 400 300 200 100 0 0 5 10 Hour 15 20 25 30 Figure13 : Wind direction at Tabbin station 23 October,1999. Wind Speed - m/s Wind Speed during 23 October 1999 8 6 4 2 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 Day hours Tebbin Al Kolaly Figure14: Wind speed at Tabbin and Kolaly station (the first half of the day). SO2 NO2 Levels EIMP readings shows that the concentrations of SO2 and NO2 were slightly low comparing to the concentrations of PM10 recorded by the network. 357 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 The two pollutants did not exceed the Air Quality Limit in the measurement sites. 23 October 99 -SO 2 data SO2 - microgram/m 3 250 200 150 Tebbin -SO2 Al Kolaly- SO2 100 50 22 19 16 13 10 7 4 1 0 day hours Figure15: SO2 data at Tabbin & Kolaly station. The most representative station for the City Center is Fum El Khalig station which is located down town where the area is impacted by local sources in addition to the pollutants coming from north during the prevailing north wind is blown. The concentrations of SO2 and NO2 can be compared to the recorded concentrations on the days before the episode. 200 150 SO2/Fum El K. NO2/Fum El K. 100 50 22 19 16 13 10 7 4 0 1 Conc.- microgram / m3 Fum El Kalig St. one hour data on 23 October 1999 hour Figure16: SO2 and NO2 concentration at Fum El Khalig station. 358 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 22 October 99 at Fum El Kalig St. 200 3 160 Concen.- microgram/m 180 140 120 SO2 100 NO2 80 60 40 20 22 19 16 13 10 7 4 1 0 Hours Figure 17: SO2 and NO2 concentrations at 22 October 99. 21 October at Fum El Kalig St. 180 160 conc -microgram/m 3 140 120 100 SO2 NO2 80 60 40 20 21 17 13 9 5 1 0 hours Figure 18: SO2 and NO2 concentrations at 22 October 99. 359 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 9.Air Pollution Control The process of Air Pollution Control include several preparation steps. The most important of these steps are listed in the following: - Identify sources - Quantifying sources emission inventory - Monitoring of air pollution - Assessing the exposure (impact) situation - Identifying sources – exposure relations Estimating the relative importance of the exposure - of various AP sources - Assessing environmental damage - Investigating control (abatement) options - Performing cost-benefit or cost-effectiveness analysis - Developing a control strategy and an investment plan - Developing institutions/regulations/enforcement - Establishing an Air Quality Information System Assessment Control Surveillance Through the work carried out in the local working groups, a large number of proposed actions and measures has been listed and categorized within the following categories: -Improved fuel quality -Technology improvements -Fuel switching -Traffic management. -Traffic demand management. Each of the proposed actions may be described regarding its effect (benefit), costs, policy instruments, and institutions responsible. The table below gives a summary of the cost-benefit analysis. For all of the selected measures except cleaner fuels in power plants, the calculated benefits are very sustainable. 360 B. Sivertsen et al. / ICEHM2000, Cairo University, Egypt, September, 2000, page 345- 361 Table 5: Benefits and costs of selected abatement measures Abatement Measure Benefits Anti Smoke Belching Campaign Avoided effects 160 deaths Reduced costs mill USD 16-20 Improving diesel quality, vehicles 94 deaths 10-12 Inspection/maintenance, vehicles 310 deaths 30-40 Clean vehicle standards 895 deaths 94-116 • The cost reported in this table is subjected to small increases REFERENCES 1) “ Maximum limits for air pollutants” as given by Annex 5 of the law No. 4 of 1994, law for the Environment, Egypt. 2) Nasralla, M.M.(1994) Air Pollution in Greater Cairo . comparing the health risk in Cairo, Egypt( vol3) Annex G, submitted to USAID/Egypt project 398-0365 (Sep.1994). 3) Sivertsen.B.Air Pollution in Egypt (Nilu O-96613 June 1999) 4) Amin.A.Comparative Environmental Risk Analysis in the Greater Cairo Area Submitted to USAID/Egypt project 398-0365 (SEP.1994). 5) Air Quality Monitoring Systems and Application.(Bjarne Sivertsen) 6) World Health Organization (1987) Air Quality guidelines for Europe. Copenhagen WHO regional publications. European series; No. 23) 361