What is the difference between residual and pollutant




















Having eliminated this dominated strategy, determine whether Asahi and Kirin now. At the end of 5 years, the compactor will be replaced by another identical compactor Cynthia hopes to be so lucky. Assuming that the City will own and operate a landfill f. What is the expected cost in Year 1 if the firm has projected that the machinery cost wil. Assume you work five days a week and time spent riding on a bus or driving a c. To evaluate the two projects, you decide to use the company's weighted average cost of capital WACC for the less risky project 12 percent and the WACC plus two points 1.

Suppose firm 1 has a constant marginal cost of 10 while firm 2 has a constant marginal c. A firm is planning to manufacture a new product. As the selling price is increased, the quantity that can be sold decreases. We ensure premium quality solution document along with free turntin report! Sign In Sign Up. Already have an account? Get multiple benefits of using own account! Despite major achievements in improving air quality, the number of smog days has been increasing in many areas during the past years.

Exposure to air pollution has been associated with cancer or numerous health problems, including decrease in lung functions, neurological damage, miscarriages, birth defects and increase in respiratory symptoms. Even short-term exposure to particle pollution is associated with cardiac arrhythmia, heart attacks and premature death. Recent studies have linked air pollution and lung cancer, and it has been suggested that the efffects of air pollution on the reduction of life expectancy are not uniformly distributed, but depend on factors such as education and antioxidant vitamin status.

This implies that life expectancy could be reduced more in disadvantaged populations that are often disproportionately represented in neighborhoods near industrial sites.

EPA to promulgate and implement technology based standards on emissions of nearly hazardous air pollutants. These emission limits were to reflect the "maximum achievable control technology" MACT for categories of source and were adopted by the year The use of MACT relies on the engineering judgment about the amount of the reduction in emission.

The U. EPA establishes emission limits as a percent reduction or a concentration limit that the regulated source must achieve. This strategy worked better than the risk-based approach to implement hazardous air pollutant standards that was used between and The result of risk-based standards was inefficient and ineffective, and the U.

EPA listed only eight pollutants and regulated only seven air pollutant standards. Implementing MACT standards has resulted in a significant reduction of toxic air emissions. However, the emission reductions that have been achieved as a result of the MACT program may not be sufficient to protect the public health and the environment. An assessment of the residual risk of toxic air emissions from MACT-regulated sources is needed to determine whether further controls are needed.

For many source categories, this assessment may be challenging since it must encompass concerns of the people regularly exposed to toxic air pollutants, the data gap and the concerns in the model uncertainty, complexity of the assessment and economic concerns of the industries. It is suggested that Anaerolineaceae , Cyanobacteria , Acidobacteria , and Nitrosomonadaceae were associated with the residual pollutant removal.

This study proposed a promising low-cost system that has remarkable implications for the quality of the treated effluent. Mahmod, S. Potential utilisation of dark-fermented palm oil mill effluent in continuous production of biomethane by self-granulated mixed culture. Gan, P. Econometric study on Malaysias palm oil position in the world market to Energy Rev.

Article Google Scholar. Abdullah, N. The oil palm wastes in malaysia. Chan, Y. Madaki, Y. Google Scholar. Rupani, P. Review of current palm oil mill effluent POME treatment methods: Vermicomposting as a sustainable practice.

World Appl. CAS Google Scholar. Singh, R. Composting of waste from palm oil mill: A sustainable waste management practice. Ibrahim, I. Reduction of residual pollutants from biologically treated palm oil mill effluent final discharge by steam activated bioadsorbent from oil palm biomass. Othman, M. Treatment of effluents from palm oil mill process to achieve river water quality for reuse as recycled water in a zero emission system.

Greipsson, S. Lone, M. Phytoremediation of heavy metal polluted soils and water: Progresses and perspectives. Zhejiang Univ. B 9 , — Wu, H. A review on the sustainability of constructed wetlands for wastewater treatment: Design and operation.

Chen, Y. Effects of plant biomass on nitrogen transformation in subsurface-batch constructed wetlands: A stable isotope and mass balance assessment. Water Res. Klomjek, P. Swine wastewater treatment using vertical subsurface flow constructed wetland planted with Napier grass. Kaseva, M. Performance of a sub-surface flow constructed wetland in polishing pre-treated wastewater—A tropical case study.

Zhang, D. Application of constructed wetlands for wastewater treatment in tropical and subtropical regions — Lin, Y. Performance and microbial community in hybrid anaerobic baffled reactor-constructed wetland for nitrobenzene wastewater.

Al-baldawi, I. Preliminary test of hydrocarbon exposure on Azolla pinnata in phytoremediation process. Energy Biotechnol. Fernandes, J. Microbial community dynamics associated with veterinary antibiotics removal in constructed wetlands microcosms.

Weber, K. Microbiology in treatment wetlands. Sust Sanit Pr. Ibekwe, A. Bacterial community composition and structure in an Urban River impacted by different pollutant sources. Total Environ. Lloyd, J. Stimulation of microbial sulphate reduction in a constructed wetland: Microbiological and geochemical analysis.

Coban, O. Nitrogen transforming community in a horizontal subsurface-flow constructed wetland. Zhang, X. Simultaneous improvement of waste gas purification and nitrogen removal using a novel aerated vertical flow constructed wetland. Zhou, X. Truu, J. Phytoremediation and plant-assisted bioremediation in soil and treatment wetlands: A review. Open Biotechnol. Vymazal, J. Constructed wetlands for wastewater treatment in the Czech Republic the first 5 years experience. Water Sci. Book Google Scholar.

Su, J. A strain of Pseudomonas sp. Kalyani, D. Jayashree, R. Biodegradation capability of bacterial species isolated from oil contaminated soil. Abdirahman Elmi, H. Waste Resour. Sonune, N. Bioremediation potential of bacterial isolates for municipal wastewater treatment. World Environ. Dhulap, V. Removal of pollutants from sewage through constructed wetland using Pennisetum purpureium.

Mohammed, R. Treatment and decolorization of biologically treated palm oil mill effluent POME using banana peel as novel biosorbent. Grismer, M. Plants in constructed wetlands help to treat agricultural processing wastewater. Masbough, A. The effectiveness of constructed wetland for treatment of woodwaste leachate. Kang, W. Assessment of low concentration wastewater treatment operations with dewatered alum sludge-based sequencing batch constructed wetland system.

Sikora, F. Ammonium removal in constructed wetlands with recirculating subsurface flow: Removal rates and mechanisms. Ogheneruemu, A. Assessing and modelling the efficacy of Lemna paucicostata for the phytoremediation of petroleum hydrocarbons in crude oil-contaminated wetlands.

Canfield, D. Science , — Ge, Z. Natural pyrite to enhance simultaneous long-term nitrogen and phosphorus removal in constructed wetland: Three years of pilot study. Efficiency of constructed wetland systems cultivated with black oats treatment of domestic sewage. Acta Sci. Wang, Y. The inhibition and adaptability of four wetland plant species to high concentration of ammonia wastewater and nitrogen removal efficiency in constructed wetlands. A novel aerated surface flow constructed wetland using exhaust gas from biological wastewater treatment: Performance and mechanisms.

Tilak, A. Evaluating wastewater treatment efficiency of two field scale subsurface flow constructed wetlands. Zhang, J. Enhancement of surface flow constructed wetlands performance at low temperature through seasonal plant collocation.

Muhrizal, S. Changes in iron-poor acid sulfate soil upon submergence. Geoderma , — Jadia, C. Phytotoxicity and remediation of heavy metals by fibrous root grass sorghum. Currie, H. Silica in plants: Biological, biochemical and chemical studies. Effect of silicon on plant growth and crop yield.

Plant Sci. Anamika, S. Phytoremediation of cadmium, lead and zinc by Brassica juncea L. Czern and Coss. Prinzenberg, A. Relationships between growth, growth response to nutrient supply, and ion content using a recombinant inbred line population in Arabidopsis. Plant Physiol.

Osman, N. The effect of palm oil mill effluent final discharge on the characteristics of Pennisetum purpureum. Ping, Y. The soil bacterial and fungal diversity were determined by the stoichiometric ratios of litter inputs: Evidence from a constructed wetland.



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