Environmental Impact Assessment for Training- myassignmenthelp.com

Question: Discuss about theEnvironmental Impact Assessment for Training Purposes. Answer: Introduction This project involves the development of a multi-seam open cut mine, which will be carried out at Caval Ridge. The project will be carried out by BHP Billiton Mitsubishi Alliance Coal Operation Pty Ltd (BMA) and will include new coal handling and processing infrastructure. Also, the project will utilize types of machinery such as draglines and truck-shovel fleet. BMA will be the primary project management team and will do that on behalf of the client who is Central Queensland Coal Associates Joint Venture (QCQA), which is a partnership between BHP Billiton and Mitsubishi Corp (BM Alliance Coal Operations Pty. Ltd., RPS (Firm). 1900). This project will involve the construction of open cut coal mine, the railing of the coal to terminals; spoil dump construction and construction of water management system. Additionally, the project will involve haul road construction, construction of power supply, rail spur construction and construction of mine industrial area. All these services will be connected to the mining and exportation of the coal. This project is also related to Bowen Basin Coal Growth project, Daunia Mine, Goonyella Riverside mine Expansion, Moranbah Airport, Phased EIS Process among others. Different EIS studies have been taken in relation to the available regulations and approvals in QC. The project looks to enhance the EIS proponents. The EIS also focuses on informing decision makers and other parties about potential environmental issues due to the project (Rocky Mountain Mineral Law Foundation, 2013). In the process, EIS focuses on public views in the planning process. Other general sections of the project include the social monitoring and community consultation. Lastly, the project has acquired the relevant approvals from the proper authorities. Project justification and sustainability Queensland is one of the significant sources of coal in Australia and makes the country a leading exporter. Coal is a significant exporter and contributor to the countrys GDP. In addition, the project will be able to produce high-quality coal, which is in high demand. Job creation is estimated to rise due to this project creating close to 70,000 jobs indirectly and 20,000 directly. Technological advancement in this project can reduce the risks associated with the mining (Queensland Queensland, 2014). Additionally, the BMA project is compatible with the regulations which are outlined in section 1.6. Furthermore, the EIS section can show the numerous benefits which the project is able to offer. These include critical benefits in an economic sense, social and environmental. Also, these sections highlight important costs which are experienced in these sections. In addition, the project can provide critical socio-economical benefits and address the socio-economical issues arising. In eco nomical perspective, the project will add value to the other industries in this location from the current $479 to $599 million. Social class for the residents will rise due to jobs in the area. The mine resource is allocated near an existing peak Downs Mining Lease (ML 1775), and it is included in the long-term development goals. Different studies have been carried to project on the sustainability of the current structure and economic evaluation of this project. This project will not have any impact on the existing projects on coal, gal, and minerals in the area. The project does not have any alternative option, and the country is likely to lose a lot if not implemented. Several mining methods will be performed such as dragline, electric rope shovel, and truck and hydraulic excavators. Air quality Mining activities have adverse effects on quality of air within the mining areas. In this assessment for the Caval Ridge project, the dust from the site was considered as a risk due to the mining and movement activities of the vessels in the mine (BHP Billiton Mitsubishi Alliance RPS (Firm)., 2011). In this area, an evaluation of the source of dust emission and mitigation measures is evaluated. They are analyzed to determine the potential impact to the communities residing in the area. Additionally, the quality of air has a significant impact on area climate and environmental status. In the assessment, the meteorological department is highly involved since it plays a key role in transportation and dispersion of dust from the mining site. In the dispersion of the dust, a key model such as DERM, which is approved by the Calmet/Calpuff modeling packages will be used. In addition, air quality will be maintained according to key standards and legislation available. Control and keeping th e climate according to the current climatic condition described in Section 4.1 of EIS will be prioritized. On the legislative framework, the project will be carried according to the Queensland and Australia laws. The guidelines on the Environmental Protection for Air policy developed in 2008 will be a key guideline in this project. In addition, the dust deposition guidelines will be adopted through the use of DERM protection (Giant Mine Remediation Project , Canada, 2015). The control of the dust will be done to prevent any production of dust to levels considered to be a nuisance. The quality of the pollutants in the air will be measured before they are released from the site. In the air quality management, it is crucial to look at the potential impacts and key mitigation measures which will maintain high-quality air within the mine area. In this project, the air quality impact was assessed through estimation of the emissions from any mining-related activities and mining itself. Dispersion models were used to estimate the potential effects and sensitive receptors (Alderliesten, Konings Niessen, 2004). In order to identify the vulnerable receptors for the locations around the mines, land use of information, aerial photographs, and BMA information will be used. The sensitive receptors are taken to indicate the individual residential locations in the vicinity and Moranbah Township. In addition, the sensitive receptors will be analyzed according to the effects on other land use activities and facilities such as schools, child care centers and health care centers. To help in addressing the receptors, the receivers are grouped according to locations and related to the project. In addition, in the pollutants which are considered, the critical emissions from the projects, which are generated from its activities, are considered. These activities are likely to overburden the movement and coal. In addition, the pollutants can lessen the combustion of diesel fuel from the mobile equipment available on site (Queensland, 2013). The contaminants from dust are considered in terms of TSP, PM10 PM2.5, and dust deposition. Air pollution and diesel combustion are key air pollutants which are found in this project. Some of the emission such as sulphur dioxide, nitrogen dioxide, and volatile organic compounds are released and able to pollute air from diesel combustion of the available mobile vessels on site (Victoria, 2013). Nevertheless, these essential substances are not considered in the emission and effect on quality of air in this project. On the other hand, CO2 and N2O are found in the address of the greenhouse gas assessment from the diesel combustion of the vessel s in this project. There are different areas which can emit the emissions in this project. The mining activities from this project will take place in the Horse and Heyford pits. The sites are likely to produce 5.5 Mtpa production of coal (BHP Billiton Mitsubishi Alliance, 2008). In addition, Peak Downs mine is projected to produce 2.5 Mtpa, which will be loaded to the Southern ROM and then transported by conveyor to the CHPP project for washing and export. In addition, the coal from Southern ROM is included in the total CHPP capacity of 8 Mtpa. These productions will have a high contribution to the emissions in this area. Since the project is not yet operational, the data on emissions of the dust cannot be obtained directly. In order to analyze the emission factors, emission rates were derived from the industry standard emissions that are collated by the NPI and US EPA AP42 emissions and estimates. All these factors are based on the critical measurements of dust emissions on other coal mines in US and Australia (BHP Billiton Mitsubishi Alliance Coal Operations Pty Ltd., Queensland, 2009). In this project, TSP and PM10 are combined to bring out the relevant activity in this project. Additionally, site-specific parameters are used to derive the emissions. Some of these critical parameters include the use of trucks on unpaved roads, draglines, excavators use, shovels, graders, dozers and blasting in mines. Most important, default emission factors were used in this project for the windblown dust, dumping of coal, loading and unloading stockpiles and loading of trains. In addition, the mine equipment scheduling is meant to be flexible to achieve the required production while being able to accommodate the equipment breakdown. Each location in this project was analyzed according to the available parameters (Rao, Raman Singh, 2003). In addition, due to lack of additional information for this site, a conservative assumption of 20% of dust emitted consisted of particles with a diameter less than 2.5 microns. The production data for this project was done for the production year 1 to production year 30. To enhance air quality, different emission control measures are proposed for this project. Modeling during the construction phase such as Horse pit and Heyford Pit will be required to analyze the effects and provide mitigation measures (Mo?lders, 2012). In addition, to control emissions, factors such as total distance traveled by coal, reject and overburden haul trucks will be analyzed. In each site of operation, the estimation of discharge during operation is done. Changing coal production, the location of mining and the amount of overburden are vital measures which are considered in the emissions. References Alderliesten, T., Konings, M., Niessen, W. (January 01, 2004). Simulation of minimally invasive vascular interventions for training purposes. Computer Aided Surgery, 9, 3-15. BHP Billiton Mitsubishi Alliance Coal Operations Pty Ltd., Queensland. (2009). Caval Ridge Coal Mine Project: Environmental impact statement : supplementary report. Brisbane, Qld.: BHP Billiton Mitsubishi Alliance (BMA. BHP Billiton Mitsubishi Alliance. (2008). BMA Bowen basin growth project: Initial advice statement. Brisbane: BHP Billiton Mitsubishi Alliance. BHP Billiton Mitsubishi Alliance., RPS (Firm). (2011). Caval Ridge Mine: Change request 8 : accommodation village condtition changes. Brisbane, Qld.: BMA (BHP Billiton Mitsubishi Alliance. BM Alliance Coal Operations Pty. Ltd., RPS (Firm). (1900). BMA Caval Ridge Mine Project. Brisbane, Qld: BMA (BHP Billiton Mitsubishi Alliance. Giant Mine Remediation Project (Canada),, Canada. (2015). Air quality monitoring update. [Ottawa]: Aboriginal affairs and Northern Development Canada. Mo?lders, N. (2012). Land-use and land-cover changes: Impact on climate and air quality. Dordrecht: Springer. Queensland. (2013). Bowen Basin coal growth project: Caval Ridge Mine : Coordinator-General's change report number 6 - miscellaneous condition amendments. Brisbane, Qld. Queensland Government. Queensland., Queensland. (2014). Bowen basin coal growth project: Caval Ridge Mine : Coordinator-General's change report no.10 : Audit. Brisbane, Qld [Coordinator General]. Rao, G. V., Raman, S., Singh, M. P. (2003). Air Quality. Basel: Birkha?user Basel. Rocky Mountain Mineral Law Foundation. (2013). Air quality issues affecting oil, gas, and mining development in the west. Denver, Colo: The Foundation. Victoria. (2013). Air quality: Latrobe Valley mine fire. [Melbourne] EPA Victoria.