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IMPACTS OF PETROLEUM, EXPLORATION,
EXTRACTION AND TRANSPORT
COVENTRY UNIVERSITY
M54GED COURSEWOR ABUBAKAR BASHIR
OIL AND GAS MANAGEMENT
(6787486
Introduction.
The recent discovery of shale oil in commercial quantity in the United States of America has revolutionized
the landscape of the global energy market. Horizontal drilling in combination with large-scale hydraulic
fracturing has being a major technological breakthrough in and a glimpse of hope in the face of the rising
global energy demand due to the dramatic growth in population and economic development. The
successful development of shale gas reservoirs which offers an alternative cleaner source of energy, with a
lower carbon foot print. (Finer 2013).
The Green River Formation (GRF) in the western U.S. has been divided into several distinct geological
basins, namely Piceance, Uinta, Green River, and Washakie Basins (Fig. 1). The richest and most thoroughly
explored deposits occur in the Piceance Basin of North-western Colorado. Basin-wide geospatial data,
including meteorological, topographic, geologic, and hydrological “baseline”, were acquired for the
Piceance Basin study area (Zhou et al. 2015). This area is also some of the most valuable wildlife habitat in
the United States; the area supports an impressive array of wildlife, from mule deer and elk to mountain
lions, black bears, and bald eagles. Especially in small communities, these lands and their wildlife resources
provide the basis of economies that hunters, anglers, wildlife viewers, outfitters, and guides support (Bill
2008).
Fig.1: Locations of four Green River Formation basins in Colorado, Utah, and Wyoming (Zhou et al. 2015)
However, there have being several concerns on the environmental concerns on the hydraulic stimulation
technology, which is usually necessary to create complex fracture network to increase the flowing ability
due to the extremely low permeability, which involves injection of a large amount of water, proppants and
chemical additives into the formation (DOE 2009). However, as the use of hydraulic fracturing has
increased widely, so have the concerns and debates on its potential impacts on environment, including
consuming fresh water resources and intensifying water supply stress (Freyman 2014), contaminating
surface and groundwater (Jackson et al. 2013), inducing earthquakes (Green et al. 2012), and polluting air
(Bamberger, M.2012)
Development of oil shale resources in the Western U.S. will require significant quantities of water for oil
shale retorting or extracting, reclamation, and associated economic growth. Oil shale development could
have a number of impacts on water quality and quantity. The current rate of water consumption is
estimated, based on retorting methods from the oil shale industry, to be averagely 3:1 water-to-oil ratio. For
oil shale resources with potential to yield almost 1 Mm3 of oil per day, this equates to 3 Mm3 of water per
day for in-situ heating processes, retorting, refining, reclamation, dust control and on-site worker demands.
Task 2: Relevant aspects of the EIA operating principles to be focused on in assessing the impact of the
exploration and production activities of shale oil in Green River formation (Colorado’s Piceance Basin), are
seismic data acquisition, vibration trucks/geophones and shot holes and routine operations.
Task 1: Irreversible Cumulative Synergistic Positive
Atm
osph
ere
Production of Oil and Gas is the major
source of CO2 emission and other
GHG such as CO and NOx (Caro et al.
2014). Thus E&P activities in
Colorado, even on a small scale, will
contribute to climate change.
Continuous release of carbon
substances over a period of time in the
21st century could result in an
irreversible climate change, such as
changes in rainfall on global and
regional scale (Frolicher and Joos
2010).
Accumulation, of fugitive gases and
toxic particulate emanating from gas
production in Colorado over a given
period (Years) will drastically reduce the
air quality as well as pollute the entire
region, and also rise the already growing
concerns of global Hearth’s temperature
(Hogrefe 2012). Conversely, this could
also impact on the vegetation due to the
prolong exposure to the pollution and
reduce the growth rates of plant
(Hopkin 2007).
Oil and gas production, is
accompanied with the release of
several harmful gases, however the
gases also tend to react spontaneously
and for complex compounds that
proven to be harmful to humans and
the environment (Sutter 2011)
Therefore engaging in E&P activities
in Colorado could lead to severe health
challenges to the population,
irrespective of the scale at which these
gases are released (Mckee and
Rodriguez 1993).
Lith
osph
ere
Apart from the fact that the green
vegetation of Colorado stands a risk of
losing its soil nutrient due to routine
activities such as seismic shop hole
(Laurance 1998). The ground stands a
risk of contamination from loss in
containment of drilling chemicals
The removal of the covering vegetation
due to exploration activities would
expose the soil, and thereby cause
erosion (Southgate and Whitaker 1992).
This soil erosion over a given time could
result in surface hydrology, drainage
arrays, increase in the siltation and
damage of the habitat (UNEP 1997).
The combination of the ground
disturbance made in cause of the E&P
activities and the spill of chemical on
the soil will result in a dramatic change
in soil composition of the area because
most micro and macro organism
would have migrated due to the
disturbances (Binelli et al. 2011).
The proportionate and controlled
increase of CO2 concentration in a
giving region, it could enhance the
productivity of plants and improve the
efficacies of resource use in farmland
(Olesen and Bindi 2002)
thereby affecting the flora and fauna
(Amadi et al. 1999)
Hyd
rosp
here
The release of toxic waste and
chemicals spill, from produced water
and waste from drilling activities can
lead to the contamination of nearby
aquifer and ground water (Wang et al
2014).
Trees play a very significant role in
absorbing rain fall and produce water
vapour to the atmosphere, however,
cutting these trees during seismic and
shot hole drilling, and other routine
activities would impact soil and the
water cycle (Muthukrishnan 2015). It
also degrades the water quality, and
reduce fish stock due to turbidity
(Caffrey 2002)
The combination of drill cutting,
contaminated produced water and
deposits of spent mud could cause a
condition referred to as Hypoxia,
which is the shortage of oxygen, and
can result in the death of Benthic
communities and reduce the river
flowrate (Bamberger, M. 2012)
Bio
sphe
re
Disturbance of the land scape and
deforestation could result to
fragmentation and degradation of
habitats that supports biological
diversity (Caffrey 2002)
The combine effect of flux of personnel,
noise from seismic operations will result
to migration of animal from the region.
While land and water pollution will
jeopardize the socio-economic activities
of the population which is usually
agriculture/fishing/hunting. (Tresierra
1999).
Multiple drilling and seismic activities
can lead to acoustic deafening,
vibration and noise (Clark, B. and
Dutzik 2002) Non-native aggressive
species and disease may be
involuntarily introduced into an area
with crews and/or equipment. In the
long run, this can displace and even
eliminate native flora and fauna over
time (YK 2006).
Oil and gas production would lead to
commercialization, and job creation
which will be a means of economic
empowerment for the locals as well as
generate revenue for the government.
Seismic Data Acquisition to Build 3D Images of the Colorado Piceance Basin
Alternatives
1. The safest alternative to this would be having no seismic activities done thereby leaving the
environment in its original state.
2. Use of Mulchers: using mulchers in cutting flora fauna, leaves rapidly bio-degradable mulch with
their seeds intact, and thus reduce the impact.
3. Use of Hand tools with thinner cut lines: hand tools or lighter machinery could be used in place of
the heavy duty machineries to minimize the destruction caused to the basin. Furthermore, with
recent technological is evolution, smaller portable and lighter navigation system capable of carrying
out seismic exploration without cutting overhead vegetation or clearing of the basin (Gibson and
Rice 2003).
Impact Analysis
Modern-day seismic exploration makes use of a combination of helicopter and heavy duty road vehicles to
access the target location these equipment’s tends to heavily impact any environment, and especially the
green river that is a traditional wildlife area (Finer et al. 2013). Preliminary activities for the acquisition of
3D images of the Colorado basin would involve basic line operations that would require the use of vertical
and horizontal heavy duty slashers (see fig 2), for land clearing and deforestation.
Fig. 2: Heavy Duty Slashers in line operation
According to Seversen-Baker (n.d.) when opening seismic lines with these heavy duty equipment, access
roads and other cut lines tends to create a separation or disrupt the ecosystems. While YG (2006) in
agreement opined that preliminary activities generally impacts the wildlife populations, distortion of settled
herds, migration of wildlife due to loud noise from machinery, human presence and smells from exhaust
and chemical fumes.
Furthermore, some animals might tend to wonder away to new population via the accesses created by the
bush clearing, and then become either prey or predators in the new population, therefore causing an
ecological imbalance. Also, bush clearing would also involve the scrapping of the topsoil and vegetation
thereby making the soil vulnerable to erosion cases of severe rainfall. In addition, the usual deployment of
line-of-sight techniques used for surveying, is another major impact as it involves the clearing of large
portions of the green formation (Gibson, D. 2003). (Prickett 2001) (see fig.3).
Fig. 3: Vegetation Clearing for Surveying
Although in recent times most countries now have strict guidelines and stipulated dimensions on the line
width which varies between 1.2 and 2 meters (SPE 2014), this even though an improvement of the earlier
practice is still a significant expanse of forest cleanout. With respect to the use of helicopter as opposed to
the earlier use of land, which causes land distortion, the helicopter operation still cause significant noise
pollution, as well as space for landing and take-off which still requires ample land space (fig 4).
Environmentalist however do strongly advise that during nesting, migration and mating periods (critical
periods for wildlife) helicopter operation should be avoided or minimised (Bamberger, M. and Oswald,
R. 2012). (Seversen-Baker n.d.).
fig.4: Heliport Landing (Pardo 2016).
Decision Making
The use of portable GPS devices capable of carrying out seismic surveys is the safest process, however the
results accuracy might be a challenge, therefore the helicopter process in conformance with flight path
restriction, used with GPS-survey would be recommended.
4. Vibrator trucks/geophone operation and shot hole drilling.
Vibrator truck is generally used to generate vibrations underneath the ground by elevating themselves above
the ground on a short pole, therefore concentrating their entire weight on a platter and shaking for several
seconds per location, thereby sending vibrations through the ground, which causes loud noise in addition
to the vibration into the ground. The geophone converts the underground movements to voltage which is
then recorded and analysed to determine the subsurface structure (Bagaini 2010).
Fig. 5: Schematic of Vibration and Geophones
Alternatives
1. Use of low ground pressure equipment: this with drastically reduce the amount of disturbances
caused to the soil, as contact surface will cause less harm.
2. Use of Eco-drills: these a relatively smaller light weight compact drill, mounted on a light truck, to
reduce the impact on the top soil. These trucks also do not require large line cut, as they are capable
of operating efficiently even in smaller line cut (SPE 2014).
Impact Assessment
Seismic operation involving vibration trucks are associated with high vibration and noise therefore
impacting wildlife, which can cause long-term impact on habitat (Wilson 2011). In some cases, this can
result in vulnerable species migration to an uncomfortable habitat where they may be prey, or not being
able to adapt therefore face the possibility of extinction (Severson-Baker 2006). As part of the operations
of a vibration truck, it compresses the soil to be able to lift itself to vibrate. This act tends to impact on the
top surface of the soil, especially for already cleared location which will result in compacting the soil tightly
and thus making it difficult fot little offshoots of plant to grow.
In contrast to vibration trucks shot hole drilling do not need huge soil clearing (Clark, B. and Dutzik, T.
2002). (Bowles and Prickett 2001). Nevertheless, the quality of water could be affected by the increased
turbidity as a result of drilling of many shot-holes along seismic line. In addition, drilling shot hole has been
characterized by huge dust generation and mud capable of changing surface water PH value, disposed in
the river surface (SPE 2014). Shot hole could also lead to the disruption of ground water.
Lastly, because of the duration of such seismic activities field logistics base are often created to
accommodate or shelter the workforce this also will lead to the generation of human waste which in most
cases are not biodegradable. With the possibility of workers having to burn their waste in situ, burning
mixed solid waste at low temperatures could create emissions of air toxics (Finer 2006).
Decision Making
According, IOGP (n.d.) states that companies favour lower-energy source for seismic survey such as
vibroseis as it causes less disturbance to than dynamite. However, in reality, in area such as the Amazon
forest with dense vegetation and difficult access, the shot-hole is still preferred to vibrator engine (Anon
2016) (SPE 2014). Anyhow, before any shot hole are drilled and dynamite is used, companies should
consult with local communities. They should also make sure that those activities are not carried out during
crucial periods in the life cycles of wildlife (e.g. reproduction).
Routine Activities
Alternatives
1. Proper designation of chemical storage and refuelling dump: the chemical storage area should be
properly designed to have a secondary containment in case of emergency or unplanned loss in
containment. The secondary containment should be able to isolate the liquid from entraining to
the environment. A dedicated refuelling dump will help make refuelling not only less impactful to
the environment but will also ensure reduction in loss of fuel due to proper planning
2. Development of an emergency response plan for Oil/Chemical Spill: Since the probability of spill
is relatively high and do occur on a daily basis development of an emergency response and
communicating same to the work force would help reduce the impact of the spill. Response
equipment such as absorbent pad should also be readily available.
3. Training and Environmental Awareness Campaign: work force should be trained on safe handling
of chemical and response to spill. However, periodic lectures and awareness campaign should be
conducted on the need to protect the environment and also the dangers of not doing so.
Emergency drill on environmental spills should also be conducted periodically
Impact Assessment
The major routine activity that devastates the environment is that of chemical spills which commonly occur
during refuelling of mechanical devices or equipment’s and storage of chemical. Chemical spills particularly
tends to significant affect the supply of water (EIA 2003). Refuelling of heavy duty machineries have being
associated with spillages, refuelling activities accounts for over most of the underground water
contamination. Diesel and petrol are the common fuel used for such heavy duty engines. Continuous release
of this petroleum based product to the soil would lead to contamination of the both the soil and the
underground water table, as well as the flora (Westlund, Thurber 2010). The atmosphere also stands the
risk of contamination though in small scale but could also impact the fauna owing to the fact that it could
contain toxic substances such as benzene that could lead to cancer.
Contamination of underground water by the continuous release of toxic chemical could also lead to the
gross water pollution, bearing in mind that the same water is what is used for bathing, cooking, agriculture
and drink by local communities. These could lead to serious health implication for the local community.
Waste disposal: This relates to the removal of waste from the different activities, some of which include
shot hole drilling to avoid the potential impact. It also involves the proper disposal of human waste during
operation on the site so as to minimize waste.
Decision Making
The periodic self-assessment and conduction of environmental audits aimed at reviewing the environmental
impact in locations like the Green River Formation (Colorado), would help in monitoring the environment.
The enforcement of the carbon economy law and the strict adherence by operators would help in sanitizing
and protecting the environment.
Task 3.
EIA (Potential Impact) EMP (Mitigation EMS (Continual Improvement) Déforestation and soil contamination
Revegetation by replanting species
Periodic monitoring and testing of soil content to be enforce by regulatory body
Water contamination Produced water can be treated
Water should be tested by Professional periodically
Contaminated air The air should be tested periodically
Regular equipment check and measurement of emission
Noise disturbance Control of noise level by using noise tools like silencer, acoustic insulator etc.
Regular use of noise auxometer to check the noise level in the environment.
Unseen accidents Safety personnel’s should monitor operations.
Conclusion
In this paper, potential environmental impacts associated with hydraulic fracturing in shale gas development
are analysed, from four aspects, water consumption, water contamination, earthquake inducement and air
pollution. Although the water consumption of a single shale gas well is high, the consumptive water
intensity of energy production is lower than conventional oil and EOR. Water use for shale gas
development in the United States do not cause significantly extra water stress in the state level. However,
water withdrawal usually concentrates in the early well completion stage, thus water use and source data
needs to be collected, and comprehensive plan should be made to maintain the local water balance.
Although elevated methane concentration in drinking water wells near active shale gas wells have been
detected in some areas in the US, due to the absence of baseline data prior to development, no definitive
conclusion can be made on whether hydraulic fracturing would lead to methane leak or migration to shallow
aquifers. To evaluate the impacts of shale gas development, baseline data pre-drilling needs to be acquired,
and continuous monitoring needs to be carried out to identify the source of contaminants through
geochemical indicators and isotopic signatures. Microseismic data reveals that hydraulic fractures are
unlikely to extend to shallow aquifers from shale formations, and fracturing fluid is more likely to be
bounded and sealed within deep shale formations by capillary force even if pathways exist. However the
transport mechanisms, affecting factors and the fate of fracturing fluid still need to be further understood.
Compared with risks of subsurface leaks and movements, the impacts and treatments of flowback are more
serious issues that need further study and evaluation, including geochemical signatures, monitoring plan
and indicators of flowback. Hydraulic fracturing is unlikely to induce destructive earthquakes, and the
hydraulic fracturing cases inducing earthquakes higher than 3 in magnitude were likely caused by unknown
pre-existing faults. More efforts need to be put into the study on the mechanisms of fracture initiation and
development, and the impacts of injected fracturing fluids and water on in-situ stress and earthquakes. Due
to the different assumptions of flowback ratio and EUR, estimation of life-cycle greenhouse gas emissions
of a shale gas well varies a lot in existing literatures. More effective measures need to be taken to reduce
natural gas leaks, measure emissions and increase utilization rate.
REFERENCE Alvarez, R. (2009). Emission of natural gas production in the barnet shale arae and opportunities for cost effective improvements. [online] Available at: https://www.citethisforme.com/cite/journal [Accessed 16 Feb. 2016]. Anon. (2016) Environmental Management In The Oil And Gas Exploration And Production. [online] available from <http://www.ogp.org.uk/pubs/254.pdf> [19 February 2016] Anon, (2002). Strategic Responses to Global Climate Change: Conflicting Pressures on Multinationals in the Oil Industry. [online] Available at: Anomohanra, O. (2011). Estimating the Greenhouse Gas Emission from Petroleum Product Combustion in Nigeria. Journal of Applied Sciences, 11(17), pp.3209-3214. AVAILABLE AND EMERGING TECHNOLOGIES FOR. (2010). [online] Available at: https://www.citethisforme.com/cite/journal [Accessed 17 Feb. 2016]. Bamberger, M. and Oswald, R. (2012). Impacts of Gas Drilling on Human and Animal Health. NEW SOLUTIONS: A Journal of Environmental and Occupational Health Policy, 22(1), pp.51-77. Bagaini, C. (2010). land seismic techniques for high quality data. [online] Available at: https://www.citethisforme.com/cite/journal [Accessed 16 Feb. 2016]. Butler, R. (2012). OIL EXTRACTION: The Impact Oil Production in the Rainforest. mongabay. [online] Available at: http://rainforests.mongabay.com/0806.htm [Accessed 16 Feb. 2016]. Clark, B. and Dutzik, T. (2002). The threat of oil and gas drilling in michigans great lakes. [online] Available at: http://research.policyarchive.org/18724.pdf [Accessed 18 Feb. 2016].
D, B. and S, R. (2007). Oil & gas exploration and production activities in Brazil: The consideration of environmental issues. [online] Available at: http://scholar.google.co.uk/scholar?q=Environmental+critical+issues+% DECC, (2010) Onshore Oil & Gas Licensing [online] Strategic Environmental Assessment for a 14th and Subsequent Onshore Oil & Gas. available from <https://www.gov.uk/government/uploads/system/uploads/attachment_data/file/66721/onshore-er.pdf> [12 February 2016]. determinig the impact significant. (2005). [online] Available at: http://scholar.google.co.uk/scholar Finer, M., Jenkins, C. and Powers, B. (2013). Potential of Best Practice to Reduce Impacts from Oil and Gas Projects in the Amazon. PLoS ONE, 8(5), p.e63022. Gibson, D. (2003). promoting environmental responsibility in seismic operation. [online] Available at: https://www.slb.com/~/media/Files/resources/oilfield_review/ors03/sum03/p10_21.pdf [Accessed 17 Feb. 2016]. Girton, C., Chapman, A., Hartong, J., Stephenson, M., Loppinet, A., Harrison, K. and Read, A. (1991). The E&P forum oil industry operating guideline for tropical rainforest. [online] Available at: https://www.citethisforme.com/cite/journal [Accessed 17 Feb. 2016]. Petersohn, E. (1998). Drilled wells in. [online] p.46. Available at: https://cumoodle.coventry.ac.uk/pluginfile.php/1203795/mod_resource/content/1/Brazil%20Round%2010%20Parana%20Basin%20-%20Barra%20Bonita.pdf [Accessed 22 Feb. 2016]. Petersohn,, E. (1998). Generation and migration of hydrocarbon model. [online] Available at: https://cumoodle.coventry.ac.uk/pluginfile.php/1203795/mod_resource/content/1/Brazil%20Round%2010%20Parana%20Basin%20-%20Barra%20Bonita.pdf [Accessed 22 Feb. 2016]. Petersohn, E. (1998). Geologic Cross-. [online] Available at: https://cumoodle.coventry.ac.uk/pluginfile.php/1203795/mod_resource/content/1/Brazil%20Round%2010%20Parana%20Basin%20-%20Barra%20Bonita.pdf [Accessed 22 Feb. 2016]. Rabanal, L., Kuehl, H., Mundry, R., Robbins, M. and Boesch, C. (2010) "Oil Prospecting And Its Impact On Large Rainforest Mammals In Loango National Park,". Elsevier [online] 2.
Availablefrom<http://www.eva.mpg.de/psycho/pdf/Publications_2010_PDF/Rabanal_Kuehl_Mundry_2010.pdf> [22 February 2016] SYSTEM OPERATION. (2015). [online] Available at: http://orr.gov.uk/__data/assets/pdf_file/0006/18744/system-operation-consultation-2015-08-13.pdf [Accessed 25 Feb. 2016].
helcopter, s. (2012). seismic oil and gas. [online] Available at: http://www.skylinehelicopters.ca/about-us [Accessed 26 Feb. 2016].