Airborne microplastics (AMPs) have been reported in indoor and outdoor air in high-income countries and are expected to be a significant contributor to daily microplastic (MP) exposure for human beings. To date, there are only a handful of studies in lower-middle-income countries. In this study, AMPs from 5000 to 50 μm were sampled across selected areas of Sri Lanka using an active sampling technique. Suspected AMPs were further characterized using Fourier transform infrared spectroscopy. MP concentrations were higher indoors compared to outdoor air (0.13−0.93, compared to 0.00−0.23 particles/m 3 , respectively). The types of indoor MPs were related to indoor-generating sources, and the occupant's lifestyles. The highest outdoor MP abundance was found near an industrial zone, followed by urban and inland locations in high-density areas. The dominant size range of MPs was 100−300 μm, and the only shapes observed indoors and outdoors were fibers (98%) and fragments. Polyethylene terephthalate was the most prominent MP type, followed by polyester, indicating that textile fibers could be the major source of these AMPs. This study provides the first report on AMPs in Sri Lanka. Considering population growth and industrialization, further research should evaluate possible trends and health risks upon inhalation.
The hypothesis having excessive fluoride and hardness levels in ground water in combination is said to have been associated with the onset of CKDu. Provision of good quality drinking water devoid of fluoride and hardness to levels less than nephrotoxic levels would be considered of paramount importance. In this respect, several types of water filters have been introduced to CKDu affected areas of which RO units are the most popular filters. Hence, this research aims at investigating the effectiveness of domestic RO units in removing fluoride and hardness levels reported in CKDu affected areas under different climatic conditions for a period covering dry and wet seasons. Two monsoons and the 2 nd inter monsoon were simulated in the laboratory and the removal of fluoride and hardness by the RO unit were evaluated according to the drinking water guidelines.Northeast monsoon was subdivided into extreme wet and wet to dry periods. Hardness and fluoride concentrations in the raw water during above periods were 110 ppm and 578 ppm and fluoride concentrations were 0.52 ppm and 2.93 ppm respectively. In the above periods hardness values obtained in the permeate were 12 ppm and 24 ppm and the fluoride was completely removed during extreme wet period and 0.15 ppm fluoride was observed in wet to dry period. In the 2 nd inter monsoon, hardness and fluoride concentrations in raw water were 1032 ppm and 7 ppm respectively and in the permeate 40 ppm hardness and 0.39 ppm of fluoride were observed. All the above fluoride and hardness values in the permeate do not comply with the required drinking water guidelines. Southwest monsoon was subdivided in to three periods namely extreme dry, dry and dry to wet. In extreme dry period hardness and fluoride in raw water were 1230 ppm and 15.5 ppm respectively. In the permeate hardness concentration varied from 48 ppm-184 ppm and fluoride concentrations varied from 0.19 ppm-1.67 ppm. At the latter stage both the fluoride and hardness values have exceeded the required drinking water guideline values. This happen when all the adsorption sites of the filter unit get saturated with the increase of the raw water concentration and then excess amount of water constituents will pass through the RO membrane. Flow rate was dropped from 0.24 litres/min to 0.03 liters/min during these periods implying that the membrane of the unit has started to get clogged. As the performance of the RO unit depends on the initial constituent's concentration in the raw water, according to this study people can use RO unit for a period of 6 months without getting clogged.
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