AIR QUALITY DURING HAZE EPISODES
During the 1990s, five separate haze episodes (1990, 1991, 1994, 1997 and 1998) occurred in Southeast Asia. Although not a new phenomenon, as haze in the area dates back to at least the early 1980s and even 1960s (Rindam, 1995), the increasing frequency is of great concern. Figure 1 depicts estimated PM10 levels in Sarawak for the period of 1978 to 1997. The haze episodes of 1991, 1994 and 1997 are clearly evidenced by the increases in PM10. This figure is based upon PM10 estimated from visibility. A quantitative relationship exists between visibility and the amount of particles in the air, though it is confounded by moisture. An equation for predicting the amount of PM10 in the atmosphere can be developed by using this association (Brook, 1998). Data on visibility, humidity and PM10 at stations in Sarawak, Malaysia were used to determine a linear equation for PM10 (Brook, 1998). Potential sources of error in these estimates are that the correction factors were not derived for particles from vegetation fires, and the subjective nature of visibility measurements. Nonetheless, the equation is useful for identifying peak PM10 concentrations. All of the haze episodes discussed are the result of biomass burning.
Many of the air quality concentrations reported in the literature for haze episodes are based on measurements of total particulate. In order to standardise the data, TPM, SPM and TSP are converted to PM10. The ratio of PM10 to total particulate varies depending on the stage of combustion, but the United States Environmental Protection Agency estimates that 92.8% of particulates from agricultural burning are less than 10 µm (
Environmental Assessment pm_vol1.htm). Also, Ward (1990) suggests that up to 95% of particulate matter is less than 2.5 µm. Therefore, we assume that 90% of total particulate matter is smaller than 10 µm and use this to convert all measured TPM, TSP and SPM values to estimated PM10 concentrations. Original measurement values are reported in parentheses.
1990
For a period of two weeks during 1990, haze affected areas of peninsular Malaysia resulting in reduced visibility and an increase in particulate concentrations. The episode began around the middle of August and lasted until the end of that month. A sudden decrease in visibility occurred on 21 August, with values as low as 1 km over the central states of peninsular Malaysia (Tussin, 1995). Levels of particulates increased starting from 15 August. Peak 24-hour values of PM10 were equivalent to 426 µg/m3 (TSP=473.8 µg/m3) in Petaling Jaya (Tussin, 1995) and 464 µg/m3 (TSP=516 µg/m3) in the Klang Valley (Rindam, 1995). These quantities were up to four times the mean levels measured during non-haze periods (Tussin, 1995).
1991
Two separate haze episodes occurred in Malaysia during 1991. The first, which will not be discussed further, took place in June as the result of the injection of ash from the volcanic eruption of Mt Pinatubo (Tussin, 1995; Hassan et al, 1995). The second, at the end of September and lasting through most of October, was more severe and was the result of biomass burning from forest fires (Tussin, 1995). The latter episode included two phases separated by a rainy period: from September 27 until October 11, and a less severe event from 22 to 31 October (Tussin, 1995; Hassan et al, 1995). The impact of the haze was most evident in Malaysia (Hassan et al, 1995). Locations in western Borneo reported visibility of less than 2 km after 2 October (Tussin, 1995). Days of low visibility corresponded to high concentrations of particulate matter (Hassan et al, 1995). 24-hour PM10 values in Kuala Lampur, Malaysia ranged from 102 µg/m3 to 254 µg/m3 (SPM=113 µg/m3 to 282 µg/m3) for the first period of 4 to 11 October and 95 µg/m3 to 153 µg/m3 (SPM=105 to 170 µg/m3) for 23 to 30 October (Hassan et al, 1995). These values were significantly higher, up to three times the normal mean (Tussin, 1995), than those for the rest of the month (Hassan et al, 1995). In Petaling Jaya, peak 24-hour averages were 445 µg/m3 (SPM=494.5 µg/m3) on 30 September and 441 µg/m3 (SPM=489.8 µg/m3) on 8 October (Tussin, 1995).
1994
After two years of relatively haze-free air quality in 1992 and 1993, fires in 1994 brought haze again to the Singapore-Malaysia-Indonesia region (Nichol, 1997). The area affected by the smoke spanned approximately 3 million square kilometers (Nichol, 1997). The haze lasted from August to October in Indonesia, Malaysia (Hassan et al, 1995), Brunei (Radojevic and Hassan, 1999) and Singapore (Chia et al, 1995; Nichol, 1997). Most of the available information comes from Malaysia. Visibility was reduced to 1 km in Malaysia with a minimum of 0.3 km in Petaling Jaya, as compared to 30 km under normal conditions (Rindam, 1995). Some measurements also suggest that the haze in 1994 was worse than in previous years in Malaysia (Rindam, 1995). The highest 24-hour average PM10 reading reported in Petaling Jaya was 410 µg/m3 (TSP=454.5 µg/m3) on 30 September (Tussin, 1995), while in Kuala Lampur, PM10 reached 409 µg/m3 on 5 October (Hassan et al, 1995). In Singapore, 24-hour average PM10 concentrations peaked above 250 µg/m3 (PSI>150) on 13 and 27 September and 29 October (Nichol, 1997). Concentrations of other particulate constituents such as sulphur, potassium, titanium, vanadium, manganese, nickel, arsenic and lead were 3-6 times higher than average during the haze period in late October (Orlic et al, 1997). The forest fires, though, did not have a significant influence on the levels of PAHs in Singapore (Chee et al, 1997).
1997
The 1997 fires in Indonesia drew worldwide attention as the haze impacted Malaysia, Singapore, southern Thailand and the Philippines and lasted from June through until November. As early as the beginning of May, air quality began to deteriorate in Singapore (Nichol, 1998). 24-hour average concentrations in Singapore peaked at approximately 230 µg/m3 (PSI=140) on 19 and 29 September (Nichol, 1998). These particulate levels in Singapore were not any more severe than those associated with the 1994 forest fires (Nichol, 1998). In Sarawak, however, 24-hour average PM10 peaked as high as 930 µg/m3 on 23 September (Nichol, 1998), which represents a value more than 15 times the normal levels (Brauer and Hashim-Hisham, 1998). Due to the location of fires and direction of the wind, Sumatra and Kalimantan in Indonesia were the most severely affected areas (Pinto et al., 1998). Daily averaged concentrations of PM10 reached as high as 3546 µg/m3 (TPM=3940 µg/m3) in Sumatra at the end of September (Heil, 1998). The concentrations were even higher in Kalimantan, on the island of Borneo, with a 24-hour maximum of 3645 µg/m3 (TPM=4050 µg/m3) (Heil, 1998). Even at the beginning of November in Palembang when the air quality was improving, daily PM10 and PM2.5 still exceeded the US NAAQS (Pinto et al., 1998). Aircraft measurements performed during this episode indicated that the smoke plume reached an altitude of 4 km and included high concentrations of O3, NOx and CO along with aerosols. In the lower layer of the plume, visibility was less than 500m (Tsutsumi et al, 1999).
1998
With the persistence of the El Niño that started in 1997 and an abnormally short wet season (Levine et al, 1999), forest fires raged again in 1998 and resulted in another, more localized, haze event (Radojevic and Hassan, 1999). In this case, the episode was most acute on Borneo and particularly in Brunei. The haze first emerged on 1 February and remained until 30 April, with especially severe conditions at the beginning of April. Daily average concentrations in the capital, Bandar Seri Begawan, reached nearly 450 µg/m3 and the 24 hour guideline for PM10 of 70 µg/m3 was exceeded 54 times during the period of 1 February to 30 April (Radojevic and Hassan, 1999). The "warning stage," which is associated with a PSI value of 300 (24-hour average PM10 concentrations of 420 µg/m3), was exceeded on 15 April (Radojevic and Hassan, 1999). During the 1998 episode in Brunei, PM10 was the only significant pollutant contributing to the haze (Radojevic and Hassan, 1999). Other gaseous pollutants such as SO2, O3 and NO2 were within acceptable limits, and only the 8 hr guideline for CO was exceeded on several occasions (Radojevic and Hassan, 1999). In Miri, Sarawak, Malaysia, 24-hour average PM10 concentrations rose above 600 µg/m3 (API=649) on March 30 (WHO, 1998).