Regulatory mechanisms for the oil and gas industry in a developing world setting

oil and gas industry
oil and gas industry

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Regulatory mechanisms for the oil and gas industry in a developing world setting

Introduction

As today’s society is organized, oil plays a critical and immense role. Petroleum products represent a lot more than just a major energy source that mankind uses. Other than being a vital source of energy, oil serves as feedstock for a number of consumer goods, and it therefore plays a pertinent and increasing role in the lives of people (Mariano & Rovere, 2012). Conversely, the oil and gas industry holds a significant potential of hazards for the environment and it might impact the environment at dissimilar levels including soil, water and atmosphere, and subsequently every living being on earth.

In this context, pollution is the most dangerous and extensive consequence of the activities of the gas/oil industry (Buchsbaum, 2013; Mariano & Rovere, 2012). This essay critically examines the regulatory mechanisms for the gas and oil industry within the context of the developing world. The essay does so by presenting theoretical, legal framework and environmental policies employed by developing countries in managing the impacts of the gas and oil industry.

The essay will particularly explore the regulatory mechanisms in the following oil-producing developing countries located in the Middle East, Asia, Africa, and South America: Venezuela, Peru, Colombia, Trinidad and Tobago, Algeria, Yemen, Philippines, Cambodia, and Sudan. Others are Papua New Guinea, Kazakhstan, Thailand, Afghanistan, Mauritania, Angola, and the Democratic Republic of Congo.

This essay will also examine the efficacy of the regulatory mechanisms in the aforementioned oil producing developing nations. This will help to determine whether or not the regulatory mechanism has actually been effective in preventing companies in the oil and gas industry from contaminating the environment in their operations.

The paper may determine that in some oil-producing developing nations, there are regulatory mechanisms but their enforcement is weak. This poor implementation of regulatory mechanisms could be due to a number of reasons such as lack of monetary and human resources required to ensure effective environmental governance, as well as corruption (Ingelson & Nwapi, 2014). In the countries with weak environmental laws, this essay provides a number of recommendations to ensure strict enforcement of environment laws for environmental protection in oil-producing developing nations.

Environmental impact of oil and gas industry

Pollution is linked to almost every activity throughout every phase of the production of gas/oil from exploratory activities to refining. Exploration of oil brings about many environmental problems such as the environmental degradation and economic loss due to gas flaring; soil contamination as a result of oil leaks and spill; and increased deforestation (Perunović & Vidić-Perunovié, 2012).

Gas emissions, waste waters, aerosols, and solid waste produced throughout drilling, production, refining and shipping amount to more than 810 dissimilar chemicals, amongst which prevail petroleum and oil products. The other impacts on the environment include contamination of the ground water, poorer quality of water, acid rain, and the intensification of the greenhouse effect (Klare, 2014). Additionally, the gas/oil industry might contribute to the loss of biodiversity and the destruction of ecosystems, which might be unique (Mariano & Rovere, 2012).   

In any nation around the world, particularly developing nations, the discovery of natural resource could be the start of economic growth in that nation. If managed well, the wealth derived from that natural resource can promote sustained economic development within that nation. Duncan (2013) noted that the exploration and exploitation of natural resources usually comes with a number of challenges, the major one being the industry’s negative environmental impact.

It is notable that the environmental impact of the gas and oil industry could be very disastrous to the country, that it necessitates a properly designed policy for managing controlling, and monitoring the industry’s negative impact on the environment (Ingelson & Nwapi, 2014). In many developing countries such as Mauritania, Cambodia, Kazakhstan, Colombia, Algeria, Nigeria, Trinidad and Tobago, Argentina, Peru, Angola, Venezuela, and Ghana among others, the gas and oil industry is marred by various environmental challenges (Tan, Faundez & Ong, 2015).

The environmental challenges are even considered a significant national concern since most of these developing nations have actually not performed well in terms of managing environmental problems brought about by the oil and gas industry (Vining, 2012).

The regulatory mechanisms in developing countries

The aim of environmental regulations in the natural gas and oil industry is basically to develop the framework in which regulatory programmes ensure that safeguarding of the environment is given greatest consideration as regards the development of gas and oil resources (Duncan, 2013). The goals of gas and oil regulation are to: present an effective and efficient framework for facilitating development and exploration of the nation’s oil/gas resources; reduce or eliminate risks to public safety and health and the environment and ensure proper resource management; and provide certainty and clarity to license holders with regard to the regulator’s requirements (Anejionu et al., 2015).

There are many developing nations that are producers or potential producers of oil and gas. These are illustrated in the table below:

Sub-Saharan AfricaThe Caribbean and South AmericaEurope and AsiaNorth Africa and Middle East
NigeriaMexicoPapua New GuineaYemen
Sao Tome and PrincipeVenezuelaThailandSyria
AngolaColombiaChinaEgypt
MauritaniaPeruPhilippinesAlgeria
Democratic Republic of CongoArgentinaAzerbaijan 
GabonEquadorKazakhstan 
CameroonTrinidad and TobagoAfghanistan 
SudanBrazilCambodia 
Ghana Indonesia 

In most of these developing nations, there is in place an adequately appropriate, though mostly theoretical, legal framework and environmental policy that is used to manage the impacts of the gas and oil industry (Tan, Faundez & Ong, 2015). On the whole, the regulatory system principles that have been adopted already in many developing nations are for the most part transposed onto the national legislation of these countries.

Put simply, most developing nations that produce oil have developed, in theory, a regulatory and legal framework consistent with the ones in place for the benchmark nations (Tan, Faundez & Ong, 2015). Most of these nations have established a dedicated institution whose purpose is to manage the social and environmental impacts of gas and oil industry; in most cases, this is usually a ministry for environment.

The regulatory, legal, and contractual frameworks in oil producing developing nations are as described below: environmental governance objectives – in these countries, the legal system is mainly reliant upon incentives or penalties to accomplish its environmental objectives. Constitutional rights and obligations – in oil producing developing countries, there are constitutional obligations and rights which specifically address ownership of natural resources, address the status of indigenous communities, sustain and protect the environment, and protect the health of people (The World Bank, 2011).

Environmental policy for the oil and gas industry – in the oil producing developing nations,

(i) specific laws have been put in place which establish policy for the development of this industry. Relevant regulations have also been duly enacted which give direction to executing the policy.

(ii) There are environmental laws which set policy for addressing environmental issues which arise from the exploration and development of oil and gas. There are a number of regulations duly passed providing direction for execution of policy (The World Bank, 2011).

(iii) Within the context of gas and oil industry development, oil producing developing countries have a set of laws which establish policy regarding use of water; emissions and effluents into the water, into the atmosphere, and onto land; noise; pollution; abandonment and decommissioning; and waste management including the management of hazardous wastes (The World Bank, 2011).

In addition, appropriate regulations have been duly enacted which give direction to the execution of the policies and have quantitative standards.      

Production-sharing agreement/host government agreement

(i) in the oil producing developing countries, there is a particular host government agreement which clearly spells out the contractual obligations and rights of the host government that arise out of a gas and oil development. In addition, this specific agreement directly addresses the host government’s related environmental obligations and rights (The World Bank, 2011).

(ii) In these oil producing developing countries, there is a particular production-sharing agreement which spells out the contractual obligations and rights of the proponents of a gas and oil development. Moreover, this production-sharing agreement addresses the proponents’ related environmental obligations and rights (The World Bank, 2011). International agreements and obligations

(i) most national governments of the oil producing developing countries have included international law rights as well as obligations in their legal system which addresses the environmental issues that arise out of gas and oil industry development.

(ii) The governments of these developing nations have established policy for addressing possible environmental impacts which affect adjacent nations by means of consultation or notification.

(iii) For transnational firms that operate in the gas and oil industry in these nations, the companies are required to comply with the corporate policies developed due to the jurisdictional requirements followed within its country of origin (The World Bank, 2011).

Environmental disputes

(i) in these nations, there is actually an important access to a quasi-judicial commission or board as well as access to a national court system for every stakeholder to a functioning judiciary for ultimate, independent adjudication of disputes and determination of remedies that arise out of the environmental implications of the gas and oil industry development.

(ii) These countries also have laws which identify and establish public hearings or appeals process for projects that are complex and/or controversial.

(iii) Members of the public have access to the legal system and the court to get remedies for environmental nonconformity (The World Bank, 2011).

Protected areas, parks, and other restrictions on gas and oil activities – in many oil producing developing nations, the development of gas and oil is inadmissible within protected areas and parks. Before the bidding process, there are clearly identified restrictions which apply (The World Bank, 2011).

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Many developing nations have in place regulations and laws on the environment that seek to regulate the activities of companies in the oil and gas industry to minimize the negative impact of their activities on the environment (Abdalla, Siti-Nabiha & Shahbudin, 2013). There are oil/gas drilling and production regulations that restrict oil/gas companies operating in the developing country from using land within 50 yards of any public road, reservoir, dam or building; establish that oil/gas companies should take appropriate measures to prevent pollution of water, and to stop it if it happens; and prohibit oil and gas companies, without rightful permission, from cutting down of trees in the developing country’s forest reserves (Abdalla, Siti-Nabiha & Shahbudin, 2013).

Furthermore, many oil-producing developing nations have in place petroleum refining regulations which require the manager of an oil refinery to take the reasonable measures in preventing and controlling environmental pollution, and which stipulate how infringement of the regulation would be punishable, for instance through imprisonment or fine (Anifowose et al., 2014).

Oil-producing developing nations have also put in place regulations that set down the necessary precautions that any oil and gas company in the production, loading, transportation as well as storage of petroleum products is required by law to take in order to prevent pollution on the environment (Laurent, 2015). There are also relevant regulations concerned with the control and licensing of oil and gas refining activities. Such regulations prohibit unlicensed refining of hydrocarbon oils and petroleum products in locations outside an oil refinery, and require hydrocarbon oil refineries in the oil-producing developing country to maintain pollution prevention facilities (Aldhous, 2012).

In addition, these countries have in place regulations that seek to prevent the discharge of hydrocarbon oil and petroleum products from ships. Such regulations prohibit ships of oil and gas companies in the oil-producing developing country from discharging oil into shorelines or territorial waters (Abdalla, Siti-Nabiha & Shahbudin, 2013). These regulations have also made it an offence for companies that transport petroleum products to discharge any oil on the waters of the developing nation.

Oil and gas companies are required to install antipollution equipment in their ships (Atsegbua, 2012). The laws actually make such discharge punishable with a heavy fine and require the oil/gas company to keep records of incidences of oil discharge into the country’s shorelines or territorial waters. The oil-producing developing nations in which oil/gas is extracted offshore have in place relevant laws for oil pollution prevention offshore (Laurent, 2015). All discharges of oil from gas/oil offshore installations need to be controlled in a careful manner in order to reduce marine environment contamination and the contamination of the living resources which the marine environment supports (Farrington, 2014). 

Many oil producing developing nations also have some type of Environmental Impact Assessment (EIA) process which has been included in their regulatory and legal framework. Nonetheless, the emphasis of the process is largely directed towards regulatory approval of gas and oil projects and not towards developing a life-cycle approach for reducing social and environmental impacts all through the life of the whole project (Duncan, 2013).

Environmental Impact Assessment is essentially a legal procedure wherein the oil and gas company is required to present environmental information to a consenting body so that the information could be utilized to make better informed decisions. In addition, EIA entails publication and public disclosure/comment or consultation. Visser and Larderel (2012) reported that this information is often presented in an Environmental Impact Assessment Report.

There are a number of goals of an Environmental Impact Assessment. An EIA is a tool for identifying possible environmental impacts of a proposed project, assessing how important or significant these environmental impacts are and propose suitable mitigation, monitoring and management measures for preventing or reducing impacts to levels that are good enough (Visser & Larderel, 2012).

Environmental Impact Assessment is also a tool and process that aids decision-making. The information collected during an Environmental Impact Assessment could feedback into project design. Outcomes of Environmental Impact Assessment are usually utilized in managing subsequent stages of project design, construction, as well as operation (Visser & Larderel, 2012).

As dictated by best practice, the full extent of the Environmental Impact Assessment process in some oil-producing developing nations has yet to be executed. What lacks in particular is adequate and systematic participation of local stakeholders and the public, access to baseline social and environmental information within the affected areas, comprehensive examination of project alternatives, as well as consideration of cumulative and regional impacts further than the project level (Visser & Larderel, 2012).

In most of these nations, project follow-up and environmental monitoring are seen as part of the Environmental Impact Assessment framework regulatory enforced. Even so, actual enforcement practices is usually insufficient, there is inadequate environmental monitoring, and monitoring data are either not divulged or they are not made extensively accessible to the affected stakeholders and the public (The World Bank, 2011). Furthermore, many oil producing developing nations have inadequate – at times completely absent – enforcement and control mechanisms in the post-Environmental Impact Assessment approval stage.

Although a lot of oil-producing developing nations claim that risk management procedures and regulatory enforcement mechanisms for gas and oil activities are included into the regulatory framework, actual enforcement of Environmental Impact Assessment approval conditions and regulatory limits on-the-ground is not happening systematically and effectively (The World Bank, 2011).        

Regulations and policies to reduce environmental impact of pit-wastewater: some oil-producing developing countries such as Brazil, Venezuela, Mexico, Colombia and Thailand have in place appropriate regulations aimed at reducing the environmental impact of pit-wastewater which include wastewater and sludge that is generated through drilling activities (Mariano & Rovere, 2012). Oil and gas companies are required to install pit-wastewater processing systems.

To avoid affecting local environments, these companies are expected to return pit-wastewater – wastewater that treatment facilities emit and production water attendant to gas and oil – underground, and treat pit-wastewater with the use of microorganisms and discharge the treated water into the ocean (Perunović & Vidić-Perunovié, 2012). Companies are also required to design and install their facilities and establish operating manuals basing upon their risk assessment in order to prevent contamination as a result of crude oil and pit-wastewater leaks (Anomohanran, 2012).

Gas and oil companies are also required to establish an operating structure under which they monitor the operations of their facility with the use of twenty-four hour patrols and remote systems. This ensures that even in case of an accident, any leakages could be reduced (Mohamed & Al-Thukair, 2013)

Regulations and policies to prevent air pollution: in a number of oil-producing developing nations including Argentina and Thailand and Egypt, there are laws that require oil and gas companies to avoid air pollution as much as possible. Emissions from combustion equipment utilized in production sites such as gas engines and boilers are required to be below the regulation standard limits for concentrations of nitrous oxide and dust (Managi et al., 2012).

Critique of the impact and application of the regulatory framework in oil-producing developing nations 

Even though these developing nations have a regulatory framework, the efficacy of the regulatory frameworks is compromised by the lack of an adequately organized administrative structure which facilitates effective regulatory conformity and enforcement. Furthermore, the other factor that compromises the effectiveness of regulations is the lack of monetary and human resources required to ensure effective environmental governance.

In the oil producing developing nations, the institutions that are responsible for environmental management generally have inadequate or little resources – information systems, technology, training, personnel, and budget – to properly execute their strategies and perform their regulatory mandate (The World Bank, 2011).

Although the governance structure and frameworks are in existence in oil producing developing countries, the execution of governance in an effective and efficient environmental management system for gas and oil activities is not well established. As such, efforts are required for strengthening the technical and administrative capabilities of governments in such countries so as to improve the environmental governance of the gas and oil industry (Duncan, 2013).    

Nowadays, environmental concerns are not regularly taken into account in plans for offshore gas and oil exploration and development. Depending on the oil producing nation where they are working, most oil and gas corporations also operate to different social and environmental standards. In some oil producing developing nations, this implies that even the most fundamental requirements are not met (Tan, Faundez & Ong, 2015).

Decommissioning of infrastructure is also a key issue and is rarely taken into account during planning and control. The life of a lot of oil exploration wells is limited; some wells with as short as just 1 – 3 months, though their construction often has long-term impacts. If planning for decommissioning is taken into consideration in the process of design, then environmental disruption will be decreased (Vining, 2012). All in all, thanks to weak environmental laws in many oil producing developing countries, many oil and gas companies continue to cause irreparable damage to the environment through their gas and oil exploration and development activities.

What the governments need to do to strengthen their regulatory framework

Governments of these nations need to establish stringent laws and regulations and take drastic actions against any oil and gas company that violates such laws and regulations not only through paying of fines (Anejionu et al., 2015). Firms that violate the established laws/regulations have to be fined very exorbitantly to serve as a deterrent against other oil and gas companies that plan on deliberately and carelessly polluting the environment during their gas/oil exploration and development in developing nations.   

Conclusion

In conclusion, most developing nations that produce oil have developed, on paper, a regulatory and legal framework similar to the ones established in the benchmark nations. Many oil-producing developing countries have established a dedicated institution whose main purpose is to manage the environmental impacts of gas and oil industry. Although oil-producing emerging economies have a regulatory framework in place, the efficacy of the regulatory frameworks is compromised by the lack of a properly organized administrative structure that actually facilitates effective regulatory conformity and enforcement.

References

Abdalla, Y. A., Siti-Nabiha, A. K., & Shahbudin, A. (2013). Examining the regulatory frameworks for the oil and gas industry in Sudan. Journal Of Environmental Assessment Policy & Management, 15(1), -1. doi:10.1142/S1464333213500063

Aldhous, P. (2012). Drilling into the unknown. New Scientist, 213(2849), 8-10.

Anifowose, B., Lawler, D., Horst, D., & Chapman, L. (2014). Evaluating interdiction of oil pipelines at river crossings using Environmental Impact Assessments. Area, 46(1), 4-17. doi:10.1111/area.12065

Atsegbua, L. A. (2012). The Nigerian Oil and Gas Industry Content Development Act 2010: an examination of its regulatory framework. OPEC Energy Review, 36(4), 479-494. doi:10.1111/j.1753-0237.2012.00225.x

Buchsbaum, L. (2013). Oil & gas and agriculture look for common ground on water and environmental issues. Coloradobiz, 40(8), 34.

Duncan, C. (2013). Mediation in the oil and gas industry: Taking the best for the future. Dispute Resolution Journal, 68(4), 71-85.

Farrington, J. W. (2014). Oil Pollution in the Marine Environment II: Fates and Effects of Oil Spills. Environment, 56(4), 16-31. doi:10.1080/00139157.2014.922382

Hamso, B. (2015). New drive to end routine flaring. Energy Policy, 34(7): 21-27

Ingelson, A., & Nwapi, C. (2014). Environmental impact assessment process for oil, gas and mining projects in Nigeria: A critical analysis. LEAD Journal (Law, Environment & Development Journal), 10(1), 1-22.

Klare, M. T. (2014). Petro-machismo. Nation, 298(12), 30-32.

Laurent, G. (2015). A New Regulatory Paradigm for Over-the-Counter Oil Forward Contracts. Economic Affairs, 35(2), 299-305. doi:10.1111/ecaf.1212.

Managi, S., Opaluch, J. J., Di, J., & Grigalunas, T. A. (2012). Environmental Regulations and Technological Change in the Offshore Oil and Gas Industry. Land Economics, 81(2), 303-319.

Mariano, J., & Rovere, E. L. (2012). Environmental impacts of the oil industry. Encyclopaedia of Life Support Systems. (EOLSS).

Mohamed, L., & Al-Thukair, A. A. (2013). Environmental Assessments in the Oil and Gas Industry. Water, Air & Soil Pollution: Focus, 9(1/2), 99-105. doi:10.1007/s11267-008-9190-x

Perunović, Z., & Vidić-Perunovié, J. (2012). Environmental Regulation and Innovation Dynamics in the Oil Tanker Industry. California Management Review, 55(1), 130-148.

Senze, M., Kowalska-Góralska, M., Pokorny, P., Dobicki, W., & Polechoński, R. (2015). Accumulation of Heavy Metals in Bottom Sediments of Baltic Sea Catchment Rivers Affected by Operations of Petroleum and Natural Gas Mines in Western Pomerania, Poland. Polish Journal Of Environmental Studies, 24(5), 2167-2175. doi:10.15244/pjoes/40273

Tan, C., Faundez, J., & Ong, D. M. (2015). Regulating environmental responsibility for the multinational oil industry: Continuing challenges for international law. International Journal Of Law In Context, 11(2), 153-173. doi:10.1017/S1744552315000051

The World Bank. (2011). Environmental governance in oil-producing developing countries. Extractive Industries for Development Series, 17(6): 1-48

Vining, S. K. (2012). Improve emissions monitoring. Hydrocarbon Processing, 77(1), 79.

Visser, J. P., & Larderel, J. A. (2012). Environmental management in oil and gas exploration and production: An overview of issues and management approaches. American Journal of Scientific and Industrial Research, 3(8): 65-77

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Solar Heating Engineering Project Dissertation

Solar Heating
Solar Heating

Solar Heating

Design and development of low cost solar thermal systems for domestic use

Background Information

Current trends in energy supply and use are patently unsustainable – economically, environmentally and socially. Without decisive action, energy-related emissions of carbon dioxide (CO2) will more than double by 2050 and increased oil demand will heighten concerns over the security of supplies. We can and must change our current path, but this will take an energy revolution and low-carbon energy technologies will have a crucial role to play.

Energy efficiency, many types of renewable energy, carbon capture and storage (CCS), nuclear power and new transport technologies will all require widespread deployment if we are to reach our greenhouse gas (GHG) emission goals. Every major country and sector of the economy must be involved. The task is also urgent if we are to make sure that investment decisions taken now do not saddle us with sub-optimal technologies in the long term.

Awareness is growing of the urgent need to turn political statements and analytical work into concrete action. To spark this movement, at the request of the G8, the International Energy Agency (IEA) is leading the development of a series of roadmaps for some of the most important technologies. By identifying the steps needed to accelerate the implementation of radical technology changes, these roadmaps will enable governments, industry and financial partners to make the right choices. This will in turn help societies make the right decisions.

The global energy need for heat is significant in both OECD and non-OECD countries: in 2009 the IEA reported that global energy demand for heat represented 47% of final energy use. Solar heat thus can make a substantial contribution in meeting climate change and security objectives.

Solar heating is a straightforward application of renewable energy; solar domestic hot water heating is already widely used in a number of countries but on a global level contributes to 0.4% only of energy demand for domestic hot water. Moreover, solar heating also includes technologies for other purposes such as space heating and space cooling, and hot water for industrial processes. As different solar heating technologies are at widely differing stages of development and use, policy support must offer custom-made solutions.

Aims and objectives

Project aims

  • Investigate and analysis of current available low cost solutions, its materials, cost, design and manufacturing methods.
  • Design and develop a low cost solar water heating system for domestic use through appropriate thermal management.

Project Objectives

  • Carry out research of the opportunities in low cost solar water heating systems and analyse its uses for domestic application.  
  • Research and analysis suitable materials existent in todays market and compare their design and methods of manufacturing.  
  • Analyse and compare price of other suitable materials in order to produce cost effective alternative.
  • Design and build solar thermal system using Creo Parametric.
  • Examine the performance of proposed low cost solar water heating systems for domestic purposes.

Literature Review

A solar water heating system for domestic use that is both affordable and effective in actualizing its intended purpose will be designed in this project. The system works by not only harnessing solar power and subsequently using this renewable source of energy to heat water depending on the environmental condition or intended use of the water rather than using electricity; but also by ensuring that domestic utility bills are significantly reduced as well as making sure that there is optimization of the effectiveness and efficiency of the system.

The Creo software will be outsourced for the designing of the solar water heating system, particularly for the purpose of domestic use. As a result, in the attempts to achieve the aims and objectives of the research project it will highly possible to ensure that solar water heating systems are not only made affordable, but also considerably efficient and effective.  

Solar Hot Water Systems, abbreviated as SHWS are widely used in domestic as well as industrial applications. SHWS of 200 liter capacity are most suited for a family with two adults and two children. The performance of SHWS is a widely researched area. A briefly reviewed summary of studies on SHWS is presented and discussed in the literature review chapter.

A review of 50 years of research work on solar energy has been discussed by Hoogwijk and Graus (2008). The history of MIT, USA Solar House-I, MIT Solar House-II, MIT Solar House-III and MIT Solar House-IV are enumerated in detail. Useful heat gains ranging from 20 to 40% of the total incident solar radiation are reported. The relative performance of gray absorber, selective absorber and low-reflecting glasses are reported.

Heller (2000) has reported 15 years of research and development on solar heating in Denmark. As a result, I would like to ensure that I undertake a review of the possible low cost alternative materials as well as appropriate and effective models with potential to perform optimally. This goes a long way in ensuring that households are saved a significant proportion of their utility bills as well as improvement of the performance of the solar water heating systems.

In the recent decades, attempts have been made to design and fabricate low cost solar water heaters. Henning and Wiemken (2007) studied the effects of storage tank volume and configuration on efficiency of thermosyphon solar water heaters. Whereas Shariah and Shalabi (1997) presented the effects of auxiliary heater on annual performance of thermosyphon solar water heater simulated under variable operating conditions.

The effects of system configuration and load pattern on the performance of thermosyphon solar heaters were analyzed by Henning and Wiemken (2007); whereas, plastic film liquid layer solar water heaters have also been designed and developed. Thus, I will personally embark on the attempts to consider the effects of a wide array of factors that are likely to influence the performance of a solar water heating system.

Kalogirou and Papamarcou (2000) have modeled the thermosyphon solar water heating system and validated the model with experimental data. An analytical approach has been employed by Belessiotis and Mathioulakis (2002) to analyze the performance of thermosyphon solar domestic hot water system. An alternative approach to thermosyphon solar energy water heater performance analysis and characterization has been put forth by Norton et al (2001).

Modeling the performance of a large area plastic solar collector has been carried out by Janjai et al (2000). Artificial neural networks have been used by Kalogirou et al (1999) for the performance prediction of a thermosyphon solar water heater. Four types of system data are used to train the network. Prediction accuracy within 2.2 C is obtained. These studies have demonstrated that Domestic Solar Hot Water System (DSHWS) performance can be modeled with good accuracy.  

Henning and Wiemken (2007) has reported the measurements of SHWS in residential houses’ performance over a period of 22 years and proposed methods for simulation. Upto 63% reductions in glass cover transmissivity were reported over the years due to fogging. As a result, I consider this as one of the ways of increasing the longevity of these solar water heating systems mainly because I have previously been a victim of cold showers due to breakdown of solar water heating system or electricity failures.

Various system configurations were investigated by Abd-al Zahra and Joudi (1984) to improve the performance of solar heaters. Lee and Sharma (2007) attempted to improve the solar absorption efficiency by an affordable solar selection coating and observed the tank water temperature to increase by 5 °C when compared to commercial black paint coating.

A 15 °C increase in tank water temperature over conventional ones was observed by Ardente et al (2005) using thermoplastic natural rubber tubing as absorber plate. This is highly likely to be an important strategy to me, especially during the winters when the temperatures are very low because it will ensure that the relevant water temperatures are maintained by the solar water heating system.

In recent times, considerable efforts have been made towards optimization of the system performance of SHWS while also ensuring that the prices of these systems do not go beyond the purchasing power of many households. I can personally articulate the inconvenience caused by poorly performing solar water heating systems, especially when there are numerous domestic chores mainly because at our elementary school I had to undergo this experience first-hand.

Duffie and Beckman (1991) have analyzed the performance optimization of solar water heater flat plate collector based on the impact of the number and type of cover plate. Therefore, it would be my pleasure and delight to embark on this noble and worthy project to make sure that I can contribute to the well-being of the living standards of the humanity.

Collector surface coating (black paint, black chrome painting), PU form density (high, low) of the collector insulation and tank (with and without) insulation are used as control parameters. It is undoubtedly evident that through these measures the insulation forms used on a day-to-day basis are going to be utilized in this project to ensure an appropriate model is designed and developed.     

According to Ambrosini et al (2010), it is worthwhile to make significant attempts in ensuring that economic optimization of low-flow solar domestic heating water plants has been attained. The flow has been provided by solar PV panels. Life cycle cost analysis has been carried out and the PV powered system is found to be economic when compared to direct electricity use. This implies that even the households that are off-grid can enjoy the privileges enjoyed by those connected to electricity.

I can vividly connect with this because once in a while there are times during my travelling expeditions when I have been forced to bath with cold water or take longer time to warm the bathing water using other forms of water heating methods.  Sharia and Shalabi (1997) have carried out experiments on rotor wind turbine with the help of wind tunnel towards optimization of the configuration of the wind turbine. Ardente et al (2005) has done the optimization of a natural circulation two phase closed thermosyphon flat plate solar water heater.

Mugnier and Jakob (2012) have optimized the minimum backup required for the SHWS under varying load conditions. Optimization of tilt angles for the solar collectors is attempted by Crawford et al (2003) and that for the low latitude countries. Optimal design for a thermosyphon solar water heater is carried out by Shariah and Shalabi (1997). Hoogwijk and Graus (2008) have attempted towards the optimization of tank-volume-to-collector-area ratio for a thermosyphon solar water heater.

Capital cost as well as economic viability of thermosyphon solar water heaters made from alternate materials is also essential in the attempts of improving the feasibility of such a project. This is because development and production of low cost materials without compromising the performance of the solar water heating systems intended for domestic use will make them more affordable, and this will go along way in promoting the adoption of these systems by a wider population. Considering the financial constraints facing many people globally, I am very sure that through increased affordability many people will have access to these solar water heating systems.

Wara and Abe (2013) have designed and developed a one dimensional transient numerical model for flat plate solar thermal devices and gave a description of the fundamentals of a model for the design as well as optimization of flat plate collectors. Dalenbäck (2010) has presented a detailed techno-economic appraisal of integrated collector in addition to the storage water heating systems. I consider the adoption of these new technologies to be really important since they play a crucial role promoting efficiency and effectiveness.

Lee and Sharma (2007) have made a performance evaluation of an integrated solar water heater as an option for building energy conservation. Daytime collection efficiencies of about 60% and overall efficiencies of about 40% are reported. Kalogirou (2009) has conducted a study on optimization of size and structure for solar energy collection system by considering three solar energy applications and economical indices like net present value and internal return rate. The author has suggested that best performance is obtained with the use of unglazed, single and double glazed collectors. 

Duffie and Beckman (2012) have discussed the design of solar thermal systems utilized for storage of pressurized hot water for applications in the industries, in which the authors developed a design space methodology procedure for component sizing of concentrating collectors, pressurized hot water storage and load heat exchanger by considering the design variables as collector area, storage volume, solar fraction, storage mass flow rate and heat exchanger size.

I am highly optimistic that through these measures, it will be possible to ensure that low cost solar water heating systems are designed and developed that are effective and optimally functioning, which subsequently improves their performance. Liu et al (2012) have optimized the system parameters of solar hot water system of with the help of f-chart and models. In addition, Liu et al (2012) have emphasized that discharge from different levels in solar storage tanks will improve the performance of the system.  

Methodology

The research design to be adopted in this project is a mixed research design, because it will involve a review of both primary and secondary information concerning the research topic while at the same time enabling experimentation of the low cost solar system that shall be designed and developed in course of this project to determine its performance. As a result, the principal method that will be used in this project is experimentation, which shall involve conducting experimental trials on various low cost solar water heating systems in order to determine the optimal design in terms of performance efficiency and effectiveness. 

Creo Parametric software is used to design and develop the proposed low cost solar water heating system intended for domestic use. The choice for the Creo Parametric software is because it is undoubtedly one of the most flexible and powerful 3D modeling software in the market today. This is because Creo Parametric has the core modeling strengths you’d expect from the industry leader, along with breakthrough capabilities in additive manufacturing, model based definition (MBD) and smart connected design. Streamlined workflows and an intuitive user interface complete the picture.

References

Abd-Al Zahra, H.A.A. and Joudi, H.A. (1983). An experimental investigation into the performance of a domestic thermosyphon solar water heater under varying operating conditions. Energy Conversion and Management, Vol. 24 Issue 3, pp. 205-214. Doi: https://doi.org/10.1016/0196-8904(84)90037-2

Ambrosini, A., Lambert, T. N., Staiger, C. L., Hall, A. C., Bencomo, M. and Stechel, E. B. (2010). Improved High Temperature Solar Absorbers for use in Concentrating Solar Power Central Receiver Applications’ SANDIA REPORT SAND2010-7080.

Ardente, F., et al. (2005) “Life cycle assessment of a solar thermal collector”, in: Renewable Energy 30, pp 1031-1054.

Arvizu, D., et al., “Direct Solar Energy”, in: IPCC Special Report on Renewable Energy Sources and Climate Change Mitigation [O. Edenhofer, O. et al. (eds)], Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA.

Belessiotis, V. and  Mathioulakis, E. (2002). Analytical approach of thermosyphon solar domestic hot water system performance. Sol. Energy, Vol. 72, Issue 2, pp. 307–315.

Crawford; R., et al., (2003) “Comparative greenhouse emissions analysis of domestic solar hot water systems”, in: Building Research & Information, Volume 31, pp 34-47.

Dalenbäck, J-O (2010). “Success factors in Solar District Heating”. WP2 – Micro Analyses Report. European Commission, IEE-project “SDH-takeoff”. CIT Energy Management AB, Gothenburg.

Duffie, J. A. and Beckman, W.A. (1991). Solar Engineering of Thermal Processes. Hoboken, NJ: John Wiley and Sons.

Duffie, J.A. and Beckman, W.A. (2012). Solar Engineering of Thermal Processes. Hoboken, NJ: John Wiley Sons.

Dupeyrat, P., S. Fortuin, G. Stryi-Hipp (2011). Photovoltaic/Solar Thermal hybrid collectors: overview and perspective, ESTEC 2011. ESTIF (2011), Solar Thermal Markets in Europe, trends and market statistics 2010, ESTIF, Brussels.

European Solar Thermal Technology Platform (ESTTP) (2007) Solar Heating and Cooling for a Sustainable Energy Future in Europe, ESTTP Brussels.

Henning, H-M. and Wiemken, E. (2007). Solar Cooling, ISES Solar World Congress 2007, Beijing, China.

Hoogwijk, M. and Graus, W. (2008). Global potential of renewable energy sources: a literature assessment. Background report prepared by order of REN21. Ecofys, Utrecht.

IEA (2009), Renewable Energy Essentials: Solar Heating and Cooling, OECD/IEA, Paris, http://www.iea.org/papers/2009/Solar_heating_cooling.pdf

IEA (2010a), World Energy Outlook 2010, OECD/IEA, Paris. IEA (2010b), Technology Roadmap, Concentrating Solar Power, OECD/IEA, Paris.

IEA (2011a), Solar Energy Technology Perspectives, OECD/IEA, Paris.

IEA (2011b), Co-Generation and Renewables, OECD/ IEA, Paris.

IEA (2011c), Technology Roadmap, Energy-efficient Buildings: Heating and Cooling Equipment, OECD/ IEA, Paris.

IEA (2011d), Energy Balances of non-OECD countries, OECD/IEA, Paris. IEA (2012), Energy Technology Perspectives 2012, OECD/IEA, Paris.

IEA-RETD (2007). Renewables for Heating and Cooling – untapped potential, http://www.iea.org/textbase/nppdf/free/2007/Renewable_Heating_Cooling_Final_WEB.pdf

Kalogirou, S. (2009). Solar Energy Engineering: Processes and Systems. London, UK: Elsevier Publications.

Lee, D.W and Sharma, A (2007). Thermal Performance of the Active and Passive Heating Systems Based on Annual Operation. Solar Energy, Vol. 81 Issue 2, pp. 207-215.

Liu, Y.-M., Chung, K.-M., Chang, K.-C. and Lee, T.-S. (2012). Performance of Thermosyphon Solar Water Heaters in Series’ Energies, Vol. 5, Issue 12, pp. 3266-3278.

Mugnier,  D. and Jakob, U. (2012), “Keeping cool with the Sun” in: International Sustainable Energy Review, Vol. 6, Issue 1, pp. 28-30.

REN21 (2009), Background paper: Chinese Renewables Status Report, REN21, Paris. Singhal, A.K., presentation “Status & Prospects of Solar Heating & Cooling Technologies in India”, 1st IEA Solar Heating and Cooling workshop, 28-29 April 2011, Paris.

Shariah, A. and  Shalabi, B.(1997). Optimal design for a thermosyphon solar water heater. Renewable Energy, Vol. 11, Issue 3, pp. 351-361.

UNIDO (2011), Renewable Energy in Industrial Applications. An assessment of the 2050 potential, UNIDO, Geneva.

Wara, S. T. and Abe, S. E. (2013). Mitigating Climate Change by the Development and Deployment of Solar Water Heating Systems. Journal of Energy Hindawi Publishing Corporation, Volume 2013, Article ID 679035, pp. 9-15.

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Disaster Response Plan

Disaster Response Plan
Disaster Response Plan

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Disaster Response Plan

While no plan can guarantee that death and damage will not occur, excellent plans implemented by experienced and well-trained individuals may and will reduce losses. The purpose of the Chemtool chemical plant Emergency Operation Plan (EOP) is to identify and respond to incidents by outlining the responsibilities and duties of Chemtool chemical plant, its employees and the locals as well.

The goal of this plan is to offer adequate life safety measures, limit property loss, and safeguard the environment, as well as to reassure and care for the public and ensure the quick restoration of impacted companies and community services. Accidents resulting in the discharge of chemicals or hazardous waste will occur despite staff’s best efforts to operate cautiously in the laboratory. 

Disaster Response Plan 

Spills in Hazardous Waste Accumulation Areas administered by the Facilities Department are also a possibility. 

There are two main types of chemical spills namely the minor and major chemical spills (Manitoba, 2013). The minor spill is one whereby the chemical is known and does not pose a major threat to safety and health. As a result, it has little chance of becoming an emergency. Workers in the local vicinity or Facilities personnel can absorb, neutralize, or otherwise control and clean up the substance (Manitoba, 2013).

Major spills, on the other hand, the chemical is unknown and hence poses a threat as highly toxic or reactive. It poses an immediate and serious threat to one’s health. Outside a fume hood, there is a probability of a fire hazard or an explosion risk, resulting in harm to persons nearby (Manitoba, 2013). The tools and materials needed to effectively contain and clean up the spill are not available, and the response and cleanup are beyond the knowledge and capabilities of workers in the local area or Facilities personnel (Manitoba, 2013).

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Disaster Response Plan

The Chemtool Inc. chemical plant in Rockton manufactures finish greases for the manufacture of automobiles and industrial machines (Chemtool Incorporated, 2020). The firm also creates ecologically friendly and cost-effective functional fluid products. Agriculture, automotive, construction, energy, food, and heavy mobile sectors all benefit from manufactured items (Chemtool Incorporated, 2020).

The plant, however, experienced a major spill that, if not managed soon, would lead to the infection of the Rock river close to it as well as serious health and security problems to both the employees and residents within its vicinity. Considering the fact that it was a major spill, all sorts of threats have to be considered. Toxic or toxic gases can cause serious disease, and in rare circumstances, death.

When corrosive chemicals are handled, they can inflict serious burns, impair vision, and affect the respiratory tract. Some chemical spills cause cancer years after the first exposure, such as asbestos inhalation, which causes lung cancer years later. Chemical spills can have serious consequences for the environment as well. With run-off pollution in the ocean, spilled oil and other pollutants can cause physical harm to marine life. In this case, a major impact is anticipated for the Rock river. 

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Disaster Response Plan 

Spilled chemicals can also flow down into the soil, causing significant ecological harm and rendering certain regions uninhabitable for flora and wildlife.

To guarantee a quick and safe chemical spill response that minimizes the effect of any chemical spills, adopt the following procedures. An important factor in swift chemical clean-up is the ability of employees to understand the severity of a spill and assess the safety of the spill site. If an immediate threat is posed, the area in which the spill occurred should be evacuated immediately. Large spills that are too difficult to clear with normal chemical cleanup kits should also be reported as soon as possible to fire and medical officials.

In the event of an accidental leak, begin conventional chemical cleanup measures right once. The Occupational Safety and Health Act of 1970 (OSH Act) was passed to prevent workers from being killed or otherwise harmed at work (OSHA, 2017). The law requires employers to provide their employees with working conditions that are free of known dangers. The OSH Act created the Occupational Safety and Health Administration (OSHA), which sets and enforces protective workplace safety and health standards (OSHA, 2017).

OSHA also provides information, training and assistance to employers and workers (OSHA, 2017). Hence, based on the OSHA, anyone working with chemicals should put on Personal Protective Equipment (PPE) that is appropriate for the chemical and the hazard it poses right away. 

Disaster Response Plan

In order to minimize the after-effect of the spill, funding is needed from the federal government as well as other organizations. The cost includes spill response actions, on-site sampling and analysis, full environmental site investigation and remediation of contaminated sites (Green Ocean, 2017). Where spills of oils or liquids are contained within a barrier or drainage system rather than being absorbed in the surface. Natural resource damage assessment and restoration is also to be considered (Green Ocean, 2017).

The Chemtool chemical plant will restore natural resources injured as a result of hazardous substance releases into the environment and pay for it too. The action of reducing the severity and seriousness of possible consequences for the environment and communities may involve specialists from diverse areas and industries (Green Ocean, 2017). The federal government is requested to provide funds for the mitigation as well as litigation.

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Lastly, in order to prevent the occurrence of another chemical spill, certain steps will be taken. First, a realistic assessment of the risk at the outset will be made (Scientific American, 2010). Second, government oversight needs an overhaul. This will play a big role in prevention of the occurrence of another spill (Scientific American, 2010). Also, the employees of the company will taken through some classes to educate them on spill prevention and also how to handle such a situation if it is to occur again in the future (Scientific American, 2010).

References

Manitoba, U. o. (2013, April). From https://umanitoba.ca/admin/vp_admin/risk_management/ehso/media/ChemicalSpillProcedures.pdf

Chemtool Incorporated. (2020). From https://www.chemtool.com

Green Ocean. (2017). From http://greenocean.nl/cost-of-oil-and-hazardous-liquid-spills-and-who-pays-for-it/

OSHA. (2017). Workers’ Rights. 3.

Scientific American. (2010, August 1). From https://www.scientificamerican.com/article/catastrophic-thinking/

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