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Natural gas and CO2 price variation: Impact on the relative cost-efficiency of LNG and pipelines

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Natural gas is often promoted as the most environmentally friendly of all fossil fuels, and liquefied natural gas (LNG) as a modern and efficient way of transporting it. Some research has been carried out into the local environmental impact of LNG facilities, but almost none into aspects related to climate change. What actually causes most greenhouse gas emissions, LNG or pipelines? This question is highly relevant for climate change, but in practice the choice of transport option for natural gas in the real world will depend on the cost of CO2 emissions. How these costs play out depend on the volume of gas to be transported, the distance etc. This article therefore develops a formal model for comparing LNG and pipelines. In particular, it evaluates how variations in the prices of natural gas and greenhouse gas emissions affect the relative cost-efficiency of these two options. The paper concludes that, at current price levels for natural gas and CO2 emissions, the distance from field to consumer and the volume of natural gas transported are the main determinants of transport costs. The pricing of natural gas and greenhouse emissions influence the relative cost-efficiency of LNG and pipeline transport, but only to a limited degree at current price levels. Because more energy is required for the LNG process (especially for fuelling liquefaction) than for pipelines at distances below 9100 km, LNG is more exposed to variability in the price of natural gas and greenhouse gas emissions up to this distance. If the prices of natural gas and/or greenhouse gas emission rise dramatically in the future, this will affect the choice between pipelines and LNG. Such a price increase will be favourable for pipelines relative to LNG.
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Natural gas and CO2 price variation:
impact on the relative cost-efficiency
of LNG and pipelines
Marte Ulvestad a & Indra Overland a
a Norwegian Institute of International Affairs (NUPI)
Available online: 01 May 2012
To cite this article: Marte Ulvestad & Indra Overland (2012): Natural gas and CO2 price variation:
impact on the relative cost-efficiency of LNG and pipelines, International Journal of Environmental
Studies, 69:3, 407-426
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Natural gas and CO
2
price variation: impact on
the relative cost-efciency of LNG and pipelines
MARTE ULVESTAD* AND INDRA OVERLAND
Norwegian Institute of International Affairs (NUPI)
(Received 12 February 2012)
This article develops a formal model for comparing the cost structure of the two main transport
options for natural gas: liqueed natural gas (LNG) and pipelines. In particular, it evaluates how vari-
ations in the prices of natural gas and greenhouse gas emissions affect the relative cost-efciency of
these two options. Natural gas is often promoted as the most environmentally friendly of all fossil
fuels, and LNG as a modern and efcient way of transporting it. Some research has been carried out
into the local environmental impact of LNG facilities, but almost none into aspects related to climate
change. This paper concludes that at current price levels for natural gas and CO
2
emissions the
distance from eld to consumer and the volume of natural gas transported are the main determinants
of transport costs. The pricing of natural gas and greenhouse emissions inuence the relative cost-
efciency of LNG and pipeline transport, but only to a limited degree at current price levels. Because
more energy is required for the LNG process (especially for fuelling the liquefaction process) than
for pipelines at distances below 9100 km, LNG is more exposed to variability in the price of natural
gas and greenhouse gas emissions up to this distance. If the prices of natural gas and/or greenhouse
gas emission rise dramatically in the future, this will affect the choice between pipelines and LNG.
Such a price increase will be favourable for pipelines relative to LNG.
Keywords: Natural gas; Liqueed natural gas; Pipelines; Greenhouse gases; Pricing
Introduction
The natural gas from large elds is normally transported by one of two means: either by
pipeline or in the form of liqueed natural gas (LNG) [1]. In recent years, the production
of LNG has risen rapidly as new facilities have been brought online, increasing its share
of internationally traded natural gas to 30% in 2011 [2]. For the period 20052020, LNG
production is expected to continue growing at a clip of 6.7% per year [3].
The building of new LNG facilities has often resulted in local resistance due to
fears over the risk of explosions. Interestingly, however, there has been limited discus-
sion of the environmental impact of LNG in terms of greenhouse gas emissions. This
question is becoming increasingly pertinent as natural gas is cast as the transitional
fossil fuel for a low-carbon world: worse than renewable or nuclear energy, but better
than coal and oil. LNG is relatively abundant, the necessary technology exists, and
much of the infrastructure needed for its exploitation is already in place. If natural gas
*Correspondence address: marte_ulvestad@hotmail.com
International Journal of Environmental Studies,
Vol. 69, No. 3, June 2012, 407426
International Journal of Environmental Studies
ISSN 0020-7233 print: ISSN 1029-0400 online Ó2012 Taylor & Francis
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is part of the medium-term solution to reducing greenhouse gas emissions and this is
going to lead to increasing amounts of it being moved around the globe as LNG, the
emissions aspect of LNG will become increasingly salient. In Norway, for example,
the new LNG facility at Melkoya is the countrys fourth largest source of greenhouse
gas emissions [4].
Regardless of the mode of transport for natural gas, some of the gas is used to generate
the energy required to transport the rest of the gas. In pipelines, a portion of the gas is
burned in order to run the turbines that force the rest of the gas through the pipeline to the
consumers. In an LNG plant, a portion of the gas is burned in order to generate enough
energy to cool the rest of the gas. When natural gas reaches a low of 161°C (260°F),
it shrinks into a liquid that takes one 600th the amount of space of the gaseous form,
becoming far more economical to ship [5,6].
Since both pipelines and LNG involve the burning of a portion of the gas, they also
result in the emission of greenhouse gases. The market value of the gas that is burned as
well as the cost of the resultant emissions will vary over time. Any major natural gas
extraction project that has to choose between pipelines or LNG thus also has to take into
account whether such future price variations may change the relative cost of the two infra-
structure types. Some of the largest natural gas elds currently slated for extraction are
located at distances from markets where such choices between pipelines and LNG need to
be made, including those in the Barents Sea, on the Yamal Peninsula and possibly in the
Persian Gulf.
Current assumptions in the literature
LNG and pipelines differ in their cost structures. Whereas the cost of pipelines tends to
rise steeply and linearly with distance, the cost of LNG has a high initial threshold but a
lower increase with distance [6]. When choosing between these two options for transport-
ing natural gas from a new eld, a break-even point somewhere between 3000 and 5000
kilometres is often mentioned in the literature [7]. For the transport of natural gas over
shorter distances, pipelines are assumed to be cheaper, whereas transport using LNG is
normally more cost-effective for distances longer than this.
The literature offers several different formulations of this break-even point. Tongia and
Arunachalam note that, due to the expense of building LNG facilities such as tankers,
re-gasication facilities and reception and storage terminals pipelines will have a lower
cost over shorter distances of around 2000 miles (3219 kilometres) or less [8]. According
to Cornot-Gandolphe et al. [9], in 2003 the break-even point was around 4500 km at a
price level of $1.60/MMBtu ($1.90/MMBtu in 2010). The same year, Quintana [10]
argued that LNG is the best option for markets located more than 4000 kilometres away
from the gas eld and which have a volume of more than 16 MMm
3
/day.
In a 2009 report, Paul Stevens argued that the cost of LNG had risen signicantly, and
that the break-even point had therefore risen to around 5000 km [1]. Further nuancing the
comparison of LNG and pipelines, Mäkinen [11] claimed that, In general, LNG becomes
economically feasible in contrast to 3000 to 4000 kilometres of land pipe or 2000 km of
offshore pipe.The break-even point will differ from project to project, depending on the
geography, logistics and legal and political factors involved [11].
The literature says little about the analysis and data upon which these break-even points
are based. This leaves several important questions unanswered: are both construction and
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operating costs taken into account? If the price of natural gas rises, will the transport of
natural gas as LNG still be cheaper than pipeline transport over distances greater than
4000 kilometres, taking into account the fact that the LNG chain consumes more gas than
do pipelines? Are costs related to CO
2
emissions included in the calculations? This article
aims to ll the void in the literature represented by these questions, by developing a for-
mal model for estimating the impact of natural gas and greenhouse gas price variation on
the overall cost of the two transport options.
The prices of natural gas and greenhouse gas emissions are, however, only two out of
many factors that determine the cost of LNG and pipelines. In order to understand their
impact on overall costs, we must view these prices in the context of the other factors upon
which the overall costs depend, in particular the amount of natural gas and the distance it
must be transported. As the comparative advantages of LNG and pipelines change in
accordance with these factors, we need to understand their impact before examining how
variation in the prices of natural gas and greenhouse gas emissions plays into the relative
cost-efciency of LNG and pipelines.
In addition to the various factors that affect the cost structure of LNG and pipelines
that we will cover here, there are many other factors which might affect the choice of
transport method, for supplier and importer: taxes, capital charge, interest rates, insurance,
the economic lifetime of capital, the exibility of the LNG spot marked, demand and
supply security, the risk of terrorist attacks, and the value of scrap metal at end of capi-
tals lifetime. Putting a general price on these conditions is difcult, so they are not
included in this analysis but they remain important for the decisions made about such
infrastructure.
Before developing a model for comparing LNG and pipelines, it is necessary to explain
some of the basics of pipelines and LNG. We start with pipelines, as this is the older,
baseline technology.
Note: Figures in brackets show gas delivery capability in BCM
2000 4000
MILES
6000 8000
1
2
3
/MMBTU /BBLOE
20
10
20"
Onshore
Gas Line
(2.5)
36" LP
Offshore
Gas Line
(10)
36" LP
Onshore
Gas line
(10)
42" HP Offshore
Gas Line (29)
56" LP Onshore
Gas Line (31)
Single Train LNG (4.3)
Onshore
Crude Line
Crude Oil
Tanke r
Coal by Collier
15
5
Figure 1. Break-even points.
Source of data: [6].
Natural gas and CO
2
price variation 409
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Pipeline economics
The costs of pipelines and LNG can be divided into capital (construction) expenditure
(CAPEX) and operating expenses (OPEX). CAPEX consists of pipe materials, installation
and coating of the pipe, the building of compressor stations, construction management and
right-of-way clearance. OPEX include compressor station fuel, pipe repairs, environmental
permits and administrative costs [12].
Both construction and operating costs may vary signicantly from one region to another.
Differences in terrain, climate, labour costs, population density and the degree of
competition between different natural gas provinces make pipeline economics highly pro-
ject-specic [9]. Pipeline planners are therefore often hesitant to generalise the costs of
constructing pipelines. A pipeline that runs through a dense urban area might cost ve times
more than a pipeline of the same length and diameter crossing a rural area [13]. The generic
model for estimating the impact of variations in natural gas and emissions costs developed
in this article will therefore have to be adapted when applied to individual cases.
Pipeline CAPEX
This article focuses on onshore pipelines, which are more common and normally less
expensive than offshore pipelines. Several approaches will be used in this section in order
to make an estimation of the costs of transporting natural gas by pipeline. The estimation
will mainly follow the cookbookapproach developed in Jung et al. [14] for East Asian
projects, drawing on Kubota [15]. This is combined with a formula for cost per pipe diam-
eter per distance as suggested by the Canadian Energy Pipeline Association [16], while
pipeline data from the USA published by Parker [13] are used to discuss the costs of
constructing and operating natural gas pipelines.
Pipeline construction costs depend mainly on the cost of material (carbon steel), cost of
labour, pipeline length and diameter and the number and capacity of the compressor sta-
tions. The data published in the Oil & Gas Journal were derived from the US Federal
Energy Regulatory Commission and are divided into four categories: material, labour, right
of way and miscellaneous costs [17]. The latter category includes surveying, engineering,
supervision, administration and overhead, interest, contingencies and allowances for funds
used during construction, and regulatory ling fees [18].
The capital costs (C) for a common onshore pipeline can be calculated by means of the
following equation:
C¼$52;675ld þð$3 107Þaþ$3091c
The costs of constructing the pipeline are calculated by multiplying a constant cost by the
diameter (μ) measured in inches, and by the length of the pipeline (δ) measured in km. α
is the number of compressor stations and c is the total capacity of the compressor stations,
measured in horsepower. Jung et al. [14] used $21,300 as the cost per inch per kilometre
for a common onshore pipeline in 2000. The estimated costs used in Jung et al.s report
[14] are more than 10 years old, and may no longer be valid for new projects. The costs
of labour, materials or other components may have risen, or new cost-reducing technology
may have been introduced to the market. We will ignore the last problem because, as pipe-
line transport is less complex, there have been only small cost reductions for pipeline
transport compared to LNG in recent years [9] . The cost estimates from 2000, however,
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do need to be revised in view of the increased costs of vital inputs. In the USA, actual
costs per pipeline mile rose by an average of 247.3% from 2001 to 2010, rising from
approximately $1,310,000 per mile to $4,550,000 per mile in the same period. This
increase was caused mainly by higher costs of labour and materials [18]. In the absence of
more reliable data, we will use these gures to revise the gures from Jung et al.s [14]
report.
Nevertheless, price levels may have changed differently, depending on the country in
question. The gures used by Jung et al. [14] are for a Common Onshore Pipeline, and
it is unclear upon which countrys prices the estimates are based. For example, the USA,
Russia and Japan have seen the price level of investment (PPP over investment) develop
in different directions over the past decade. In the USA, 20002007, the price level of
investments decreased by 11.7% (although it has probably increased sharply since then)
and in Japan by 32.8%, whereas in Russia the price level of investments increased by
124.1% during the same period [19]. But it is nevertheless important to revise the pipeline
costs from 2000 to make them comparable with the revised LNG costs.
It is possible to check the accuracy of these estimates by comparing them with a
proposed pipeline where the estimated costs are more or less current. We have estimated
the costs of the Nabucco pipeline by entering the pipeline details (diameter of 56 inches,
11 compressor stations, distance 3893 km) into the equation below [20,21]. The equation
calculates a total construction cost of almost $16.8 billion agure much higher than the
estimated e7.9 billion ($11.5 bn) stated on the Nabucco project website [22]. According
to Webb [23], however, the oil and gas company BP has produced a new estimate of e14
billion ($20 bn) for the same construction costs. These differing estimates exemplify the
difculty of determining pipeline construction costs.
Compressor stations constitute a large percentage of total construction costs. Jung et al.
[14] use a xed cost per compressor station (α) and then a variable cost per unit of horse-
power. We assume that average distance between the compressor stations is 200 km [24]
and that average capacity per compressor station is 110 MW. The latter assumption was
made after a comparison of several proposed Russian pipelines and their capacities [25].
Parker [13] uses construction cost projections for over 20,000 miles of pipelines in the
USA to generalise the construction costs for a pipeline of a given length and diameter. Par-
ker concludes: Materials costs account for approximately 26% of the total construction
costs on average. Labour, right of way, and miscellaneous costs make up 45%, 22% and
7% of the total cost on average, respectively.These shares are estimated on the basis of
US data for the years 19912003. The data refer to pipelines between 4 and 42 inches in
diameter, which is less than many of the long-distance pipelines in Russia. For example
the diameter of the pipeline running from Yamal to Europe is 56 inches (1420 mm) [26].
The small pipeline size is a problem, as pipeline diameter determines the share of the total
costs within the four construction cost categories. For example, for a 4-inch diameter pipe-
line, materials account for 15% of total construction costs, but this gure rises to 35% for
a pipeline 42 inches in diameter [13].
The cost of labour often differs signicantly between countries or regions, as does the
cost of materials (steel not least), which are never exactly the same throughout the world
[27]. Furthermore, pipeline construction costs do not remain static within a country.
Therefore, the relative share of construction costs depends on a range of interlinked fac-
tors with, for example, material or labour costs uctuating as wages or steel prices
change. Figure 2 shows the average breakdown of construction costs in the USA for the
period 2009/2010.
Natural gas and CO
2
price variation 411
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Here, the cost of materials differs markedly from the 26% share mentioned by Par-
ker [13] above. The reason is that Parkers data are from 19912003, whereas the data
presented in the gure are from July 2009June 2010. Figure 3 below shows the
development of the share of material and labour costs in the USA over the past 10
years.
According to Chandra [28], steel may account for as much as 45% of the total cost of a
typical pipeline. It is possible to estimate the cost of steel in the overall share of
construction costs in greater detail by using the Figure 3 graph above, Figure 5, and the
US Carbon Steel Plate Prices from Figure 7 g7 below. The estimates show that steel
accounted for 5.6% of total construction costs from 2001 to 2003. The share rose mark-
edly in 2004, due to a steep increase in steel prices, and was as high as 14.5% of total
costs from 2005 to 2008. This may even be an underestimate.
Figure 2. Pipeline construction cost components.
Source of data: [18].
Figure 3. The share of the two major cost components in pipeline construction, 20012010.
Source of data: [18].
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Pipeline OPEX
A pipeline has annual operating costs such as fuel for the compressor stations, repair costs,
SCADA and telecommunications, lease and rental, wages and administrative costs [12].
Operating costs are relatively project-specic, but may be broken down into two catego-
ries: operating costs as a xed percentage of the construction costs and fuel.
Operating costs for a typical onshore pipeline can be estimated as follows:
Op¼Csþ1ð1lÞd
g

Np
N is the volume of natural gas, measured in cubic meters per year, p is the price of natural
gas, measured in dollars per cubic meter, and ηis the number of kilometres between the
compressor stations. The operating cost as a share of the capital costs (τ) is 3.5% for a
common onshore pipeline. The percentage of the natural gas used as fuel in the compres-
sor stations () is 0.4% per every 100 miles (according to Jung et al. [14]). The reason
why authors use the term every 100 milesis probably that they account for compressor
stations every 100 miles on average. But 100 miles (161 km) between the compressor sta-
tions seem short compared with long-distance pipelines like the proposed Nabucco pipeline
and the Altai project. The Nabucco pipeline route is 3893 km long, with an estimated 11
compressor stations [20,22]: thus, the average distance between compressor stations will
be 354 km. Furthermore, the Altai gas pipeline will be over 2600 km long and will have
10 compressor stations [25], corresponding to one compressor station every 260 km. In
contrast, the GryazovetsVyborg pipeline will have a compressor station every 131 km,
and the UkhtaTorzhok pipeline every 198 km on average. The estimated distance between
the compressor stations (η) will therefore be 200 km, as mentioned in Whists article [24].
LNG economics
The production and transport of liqueed natural gas is a three-step process: rst liquefac-
tion of the natural gas, then tanker transport and nally re-gasication. Here we will ignore
the transport of natural gas from the eld to the liquefaction plant, which is usually situ-
ated on the coast, because this stage is necessary for both pipeline and LNG transport and
will not make a difference in the comparison[29]. The costs of LNG projects are difcult
to generalise because they vary signicantly from location to location, and depend on
whether the project is greeneld or an expansion of an existing plant [30].
The liqueed natural gas is made in a liquefaction plant where the gas is refrigerated to
161°C (260°F). The gas becomes a liquid, in the process shrinking to 1/600th of its
volume in gaseous form. The liquefaction plant consists of so-called trains, processing
modules, the size of which depends on the available compressors. In 2004, the largest
trains could produce around 4 million tonnes per year (tpy). But, with improved compres-
sor technology it is now possible to produce larger trains and further exploit the economies
of scale. These costs may be further reduced by around 25% by replacing two 2-million-
tonne trains with one 4-million-tonne train [6]. Today, Qatar has several single-train lique-
faction plants with a capacity of 7.8 million tpy per train [31].
Field
development Liquefaction Shipping Re-gasification Power
generation
Figure 4. The LNG chain.
Natural gas and CO
2
price variation 413
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The liquefaction plant is usually the most expensive link in the LNG chain. This is
because the liquefaction process demands a considerable amount of the gas delivered to
the plant [32], but also because of the remote locations, strict design and safety standards
and the large amounts of materials required [30].
Most LNG plants have their own eet of LNG carriers, ... operating a virtualpipeline,
according to Chandra [28]. This might change, however, with the increasing spot-trade mar-
ket [28]. According to Jensen [6], a typical LNG carrier can transport 135,000 to 138,000
cubic meters of cargo: this capacity is currently increasing, due to better designs. By March
2011, the world eet of LNG carriers had 44 active carriers with a capacity of over 200,000
cubic meters. The largest LNG carriers have a capacity of 266,000 cubic meters of LNG [33].
The nal link in the LNG chain is the re-gasication terminal with vaporisers which
warm the liqueed natural gas from 161°C to about +5°C, and into its normal gaseous
form. Other main components of the re-gasication facilities are the ofoading berths,
LNG storage tanks and pipelines to the local gas grid [28].
Due to new technology and designs, there will be several changes or options coming in
the near future that might improve the LNG chain. Floating LNG production, which will
make the costly gas transport from the eld to the onshore LNG plant unnecessary, is on its
way. Vautrain and Holmes [34] claim that for a remote offshore eld the cost of bringing
the gas to an onshore plant might add as much as 40% to the total cost of the LNG plant.
Furthermore, the possibility of ofoading the LNG offshore is currently under study, as
is ship-to-ship transfer. This might lead to larger ships ofoading some of the LNG onto
smaller ships which could transport it directly into port, warm the LNG into gaseous form
and ofoad it directly into the local pipe grid [28]. As this technology is not in widespread
use, it is therefore outside the focus of this paper.
LNG CAPEX
The costs of LNG projects are difcult to determine because the costs of the components,
such as steel, nickel, wages and services may vary signicantly over time. For example, in
2004 the cost of building a liquefaction plant had fallen to less than $300 tpy, due to the
exploitation of economies of scale and the development of trains with larger capacity.
Because of rapid increases in the price of materials and services, however, the cost of a
liquefaction plant rose to $650 tpy in 2008 more than double the 2004 price [35].
This corresponds well with the gures used in the report Natural Gas Pipeline Develop-
ment in Northeast Asiaby Jung et al. [14], which will be used as a basis for the cost
composition, but with revised gures. Jung et al. [14] break the total LNG costs into LNG
liquefaction plant costs, LNG carrier costs and LNG re-gasication terminal costs.
The capital costs of the LNG liquefaction plant (P) are divided into a xed cost for a
greeneld plant with a capacity of 4 million tpy of LNG (5.5 bcmpa) and a variable cost
per extra million tonne, if further expansion is needed. L is the amount of LNG, measured
in million tonnes per year.
P¼ð$5:5109Þþð$1 109ÞðL4Þ
The cost of a single-train 4-million tpy onshore LNG plant is $5.5, billion according to
Vautrain and Holmes [34]. Train sizes of around 4 million tpy are the most common
capacities, but this will probably change as the designs are further developed. Qatar
already has several 7.8 million tpy trains [31]. Moreover, adding a train to an LNG plant
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in order to expand the capacity is far cheaper than a greeneld project. Adding a second
train can reduce the unit costs per train by 20 to 30% [9], because many of the expensive
facility components are already constructed and can be shared [30]. The Qatargas 4
project, where Qatargas added another train, with a capacity of 7.8 million tpy, to the
existing Qatargas 2 and 3, will have a cost of around $8 billion [36,37].
According to the US Energy Information Administration [30] around 50% of LNG liq-
uefaction plant costs are construction and related costs, 30% are equipment costs and 20%
are for bulk materials. These shares are only approximations and may change as the prices
of the various components change.
The sizes of LNG carriers are also increasing due to better designs and technology.
Today, a carrier might have a capacity of 266,000 cubic meters. There are 10 carriers of
this size; these are also among the newest. Qatar Gas Transport CompanysRasheeda was
delivered in August 2010. All the largest carriers have a speed of 19.5 knots, or about 36
km/h.
The cost of an LNG carrier with a capacity of 266,000 cubic meters is about $290 mil-
lion. The size of the eet needed to transport the LNG depends on the distance (δ) from
the market, the speed (λ) and the capacity (k) of the LNG carriers, and annual production
at the liquefaction plant (N). λis measured in kilometres per hour and k is measured in
cubic meters of natural gas. The following equation is derived to nd the number of carri-
ers required and the capital cost of the LNG carriers (s). Here 266,000 cubic meter carriers
will be used irrespective of the size of the eld, because the aim of this paper is to analyse
long-distance and large-scale transport.
S¼ð$29 107ÞN
365
ðd
24k2Þþ2K
0
5,000
10,000
15,000
20,000
25,000
30,000
35,000
40,000
2000 2001 2002 2003 2004 2005 2006 2007
USD per Short Ton
Figure 5. Nickel prices.
Source of data: [35].
Natural gas and CO
2
price variation 415
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According to the US Energy Information Administration [30], the costs of building regasi-
cation or receiving terminals show wide variation and are very site-specic. Therefore, it
is also difcult to estimate the cost of a general LNG re-gasication terminal. The most
expensive components are the storage tanks, which may account for one-third to one-half
of the total construction costs, and the marine facilities [30].
The capital cost of a re-gasication terminal (R) is highly site-specic, but a rough
estimate might be $1 billion for every 10 million tpy of LNG (L), or $100 million per
million tpy LNG:
R¼ð$1 108ÞL
A US Energy Information Administration report from 2003 estimated that a new
re-gasication terminal in the United States, with capacity between 3.8 and 7.7 million
tpy, would cost $200 to $300 million. That estimate is probably too low today, because of
the escalation of costs for materials and wages that started in 2004 and has not been
reversed [36]. Furthermore, two LNG regasication terminals, the Gulf terminal in the
United States and the Gate terminal in the Netherlands, which will both be operating from
2011, have announced their estimated total project costs to be $1.1 billion [38,39]. The
Gulf terminal has a capacity of 5 million tpy; the Gate terminal has a capacity of 8.8
million tpy (12bcmpa), but this can be expanded to 16 bcmpa [31,39]. Jung et al. [14] use
$500 million as an estimate for the cost of a 6-million-tpy re-gasication terminal.
LNG OPEX
Annual operating costs for the facilities needed to transport natural gas as LNG include
maintenance costs, port charges, capital charges, taxes, fuel and boil-off. Boil-off is the
small amount of LNG that evaporates from the storage tank during transport [40]. Fuel
costs include liquefaction of the natural gas, fuel for the LNG carriers and re-gasication
of the LNG [14,35][35] [14]. Operating costs are rst divided into different shares of the
construction costs, mainly covering operational and maintenance costs. Thereafter the
amount of the natural gas used as fuel deserves discussion (see below).
Annual operating costs for the transport of natural gas as LNG may be estimated as
follows:
Operating costs as a share of capital costs ( ,ν,σ) are 3.5% for the LNG liquefaction plant
(P), 3.6% for the LNG carriers (S) and 2.5% for the LNG re-gasication terminal (R) [14].
The variable share used as fuel (ω) depends on several parameters. These include the
share of natural gas used in the liquefaction process (Θ), the share of natural gas used in
the re-gasication process (Ω), boil-off per day (ξ) and shipping fuel per day (u).
x¼HþXþð1ð1nÞd
24kÞþð1ð1uÞd
24k2Þ
The liquefaction process whereby the natural gas is cooled down to 161°C consumes a
considerable share of the natural gas. Re-gasication and shipping consume a portion of
the gas as fuel. The quantity of natural gas used for cooling, heating, boil-off and LNG
carrier fuel depends on the design, efciency and the size of the liquefaction plant, the
LNG carrier and the re-gasication terminal [41].
416 M. Ulvestad and I. Overland
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According to the engineer Kandiyoti [42], a total of up to 20% of the natural gas is used
in the process of liquefaction, shipping and re-gasication. This was supported by ship-
owner Trygve Seglem in 2007, who stated that 2025% of the natural gas is needed for
the entire LNG transport chain [43]. Nevertheless, others have claimed that less natural
gas fuel is necessary for LNG transport. An anonymised source in an international oil
company [44] informed us by email that only 56% is needed specically for the liquefac-
tion process, 12% for transport by LNG carriers and 1% for re-gasication. According to
a report from 2004 by the Norwegian Directorate for Watercourses and Energy [45],
between 5 and 15% of the natural gas is used in the liquefaction process [46].
A share of only 56% for the liquefaction process, however, seems too low compared
with gures given in the majority of the published sources available. Furthermore, the
gure of 12% natural gas usage for shipping must refer to shorter distances only, where
the return journey is not accounted for. Jung et al. [14] cite the following gures: 9% for
liquefaction, 2.5% for re-gasication and 0.17% per day to boil-off. LNG carriers may also
use some of the natural gas as fuel. These gures t well with those indicated by Kandiy-
oti, who claims that the liquefaction process takes up to 910% of the natural gas, and that
up to 6% is needed for a 20-day voyage. This seems to include both boil-off and fuel, but
not fuel for the return voyage. This means that a little less than 0.14% per day is fuel only
(not including boil-off). The re-gasication process claims 23% of the natural gas [47].
These shares may vary due to differences in design, efciency and technology, among
other factors. The natural gas that boils off during shipping may be used as fuel or other
fuels, such as bunker fuel or diesel, may be used instead [47]. This will probably reduce
the share of the natural gas needed for the LNG chain. We assume that the boil-off is lost,
and that the fuel for the LNG carriers is natural gas taken from the cargo.
Comparison of LNG and pipeline CAPEX
We will rst discuss the break-even point between the two transport options by examining
only the capital costs. The break-even pointrefers to the position when the cost of con-
structing the pipeline infrastructure is equal to the cost of constructing the LNG chain
needed to transport the natural gas. As mentioned, the literature assumes a break-even
point somewhere between 3000 and 5000 km. Because the cost of pipeline construction
starts from a low level and rises relatively steeply with distance (whereas LNG has a high
threshold, but thereafter increases less), LNG construction costs will be lower after the
break-even point has been reached. The costs of pipeline constructions will be lower for
distances shorter than the break-even point.
Not only the distance, but also the quantity of natural gas transported affects the costs
and the break-even point. According to our calculations, the economies of scale are more
pronounced for pipelines than for LNG. Even though there are signicant cost reductions
for adding trains to an already-planned LNG greeneld plant, the cost reductions are
higher for increasing the diameter of a pipeline (not yet constructed) to expand the capac-
ity. Not only the pipeline diameter, but also the power of the compressor stations must be
increased in order to expand the capacity of a pipeline [48]. That point is not accounted
for in this analysis because we have used a xed capacity per compressor station (110
MW). In any case, this seems to be a relatively high gure, as a 110 MW compressor sta-
tion every 200 km will probably be able to pump relatively large amounts of natural gas
through the pipeline. In addition, the LNG chain might gain something from economies of
Natural gas and CO
2
price variation 417
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scale, because it is cheaper to increase the size of an existing plant than to build a
greeneld plant. It is also cheaper to use a large LNG carrier than several carriers with
smaller capacities. But, the transport of natural gas is not associated with economies of
scale to the same degree as is pipeline transport.
The break-even point for an annual transport of 30 bcm is about 5100 km, assuming a
pipeline diameter of 1420 mm (56 inches). If, however, if the amount of natural gas is 20
bcmpa, and the pipeline has a diameter of 1220 mm (48 inches), the break-even point is
around 3750 km. For 10 bcmpa, with a pipeline diameter of 1020 mm (40 inches), it is
around 2200 km.
Comparison of LNG and pipeline OPEX
We have used the actual market price for natural gas sold by Russia to Germany in 2010
to price the natural gas throughout this comparison, $296 per 1000 cubic meter [49].
Even though construction costs might be lower for LNG when considering long dis-
tances or relatively small volumes of natural gas, this does not necessarily mean that LNG
will be the cheapest transport option. The large amounts of natural gas needed during the
LNG chain usually make annual operating costs higher for LNG than for pipelines.
The break-even point for constructing the transport facilities needed to transport 20
bcmpa is around 3750 km. Pipeline construction costs will be the lowest for shorter dis-
tances, whereas LNG construction costs will be lower for longer distances. But, if we
include the operating costs and assume that the project will run for 20 years, the distance
break-even point for 20 bcmpa will increase to around 4550 km; for 30 bcmpa it will
increase from 5100 km to 5900 km when operating costs are included. The break-even
point for 10 bcmpa will be 2800 km, increased from 2200 km.
Operating costs will not always be higher for LNG than for pipeline transport. Our esti-
mates show that for transporting 30 bcmpa over distances greater than 6550 km, annual
operating costs for pipelines exceed those for LNG. One reason is that pipeline construc-
tion costs are higher, and we have developed operational and maintenance costs as a share
of construction costs. Furthermore, for long distances the share of natural gas used as fuel
for the compressor stations will approach the share of fuel used in the LNG chain. For
particularly long distances, the fuel share will be higher for pipelines than for LNG
0.00
0.50
1.00
1.50
2.00
2.50
3.00
3.50
4.00
5 1015202530
Unit cost,
Bn per bcmpa
Volume, bcmpa
Cost per unit construction -
pipeline
Cost per unit construction -
LNG
Figure 6. Capital cost per unit for 4000 km.
418 M. Ulvestad and I. Overland
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transport. If the natural gas is transported more than 9100 km, pipeline transport will
demand a greater share of the natural gas than LNG transport, regardless of transport vol-
ume. Nevertheless, LNG transport is more exposed to changes in the natural gas price than
pipeline transport for reasonably long distances. This is shown in Figure 9, which is based
on a distance of 4550 km from the eld to the market, a volume of 20 bcmpa and a pro-
ject life of 20 years. The costs of European Union Allowances (EUAs) are also included
here.
CO
2
emissions
Because of the relatively large amount of fuel required by the LNG process compared to
pipelines, LNG causes greater CO
2
emissions than pipeline transport. CO
2
emission
allowances will therefore be used in order to estimate the extra costs associated with the
environmental damage brought on by LNG.
0
5
10
15
20
25
30
35
40
0
1,000
2,000
3,000
4,000
5,000
6,000
7,000
Bn
Distance, km
Construction costs -
pipeline
Construction costs -
LNG
Figure 7. Break-even point for 20 bcmpa.
0
10
20
30
40
50
60
70
80
1000
2000
3000
4000
5000
6000
7000
Bn
Distance, km
Total costs - pipeline
Total costs - LNG
Figure 8. Break-even point for 20 bcmpa.
Natural gas and CO
2
price variation 419
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The extra operating costs can be calculated as follows:
Ep¼
36N1ð1ð1lÞd
nÞ

106A
EL¼
36NHþXþð1ð1nÞd
24kÞþð1ð1uÞd
24k2Þ

106A
CO
2
emissions (ɛ) from natural gas are around 53.06 kg CO
2
per million Btu [50]. The
price per ton CO
2
of emissions (A) is currently $29.84 when buying from the European
Union emission trading scheme, the European Union Allowance (EUA) [51]. As shown in
Figure 10, LNG transport is more exposed to changes in the price of CO
2
emission allow-
ances than pipeline transport. Figure 10 is based on a distance of 4550 km from eld to
market, a volume of 20 bcmpa and a project life of 20 years.
The model
Combining all the equations results in a model that may help to answer the question about
the relative cost-efciency of pipelines and LNG. Let fbe equal to total pipeline costs and
let g equal total LNG costs, measured in dollars. (A full list of variables and parameters is
provided at the end of the article.)
0
20
40
60
80
100
120
0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0 1.1 1.2 1.3
Bn
Price of natural gas ( per m3)
Total pipeline costs (+EUA)
Total LNG costs (+EUA)
Figure 9. Total transport costs and gas price.
420 M. Ulvestad and I. Overland
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If the equation yields a gure higher than 1 for a given set of parameters, then LNG trans-
port has the lowest costs. If the equation gives a gure smaller than 1, pipeline transport is
economically preferable.
Such a large and complicated equation is not particularly elegant, and one may question
whether it is necessary. But, according to our analysis, this equation captures the main
factors that must be taken into account in choosing which type of infrastructure to build.
Thus it mirrors the calculations that anyone choosing between LNG and pipelines must
make, and the complexity of these decisions about crucial infrastructure. It is also possible
to calculate the partial derivatives of f(total pipeline cost) and (g) (total LNG cost) with
respect to the natural gas price (p) or with respect to the price of CO
2
emission allowances
(A), where all other variables are held constant, in order to calculate how a one unit price
increase affects total pipeline and LNG costs.
@f
@p¼N1ð1Þd
g

c
@g
@p¼NHþXþð1ð1nÞd
24kþð1ð1uÞd
24k2Þ

c
@f
@A¼N1ð1Þd
g

36e
106c
@g
@A¼NHþXþð1ð1nÞd
24kÞþð1ð1uÞd
24k2Þ

36e
106c
For example, the transport of 10 bcmpa over a distance of 3000 km during 20 years,
and with the values of the other parameters as discussed above, gives:
48
50
52
54
56
58
60
10 20 30 40 50 60 70 80 90 100
Total pipeline costs
Total LNG costs
Figure 10. Transport costs and EUA prices.
Natural gas and CO
2
price variation 421
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@f
@p¼11;669;754;730 @g
@p¼27;114;448;860
This demonstrates how the costs of LNG transport (g) are more sensitive to changes in
the price of natural gas than pipeline costs (f).
Similarly, the parameters give the following expressions for the partial derivatives with
respect to A:
@f
@A¼22;291;099 @f
@A¼51;792;936
Again, LNG transport appears more exposed to price variations than transport by pipe-
line. A one unit increase in the price of greenhouse gas emission allowances results in a
considerably larger cost increase for LNG than for pipelines, as shown below:
C= ($52,675 × 56 inches × 1615km) + ($3 ×10
7
)11 + ($3091 × 1,327,612 hp)=
$9,189,537,160
C¼$9;189;537;160 þ$10;750;000;000 þ$2;000;000;000
2¼$15;564;537;160
C= ($52,675 × 56 inches × 1365 km) + ($3 × 10
7
)10 + ($3091 ×1,206,920 hp)=
$8,050,272,517
PþSþR¼ð$5:5109Þþð$1 109Þð20:34Þþ ð$29107Þð28109Þ
365
ð3520
2436 2Þþ2152;950;000
þð$1 108Þ20:3$25;280;000;000
Op¼ð$21;939;537;160 3:5%Þþð28;000;000;000 ð28;000;000;000
ð10:4%Þ2839
200 Þ$0:296Þ¼$1;226;257;190
OL¼ðð$5:5bnþð$1:0bn ð20:34ÞÞÞ  3:5%Þþðð$ 290 MM 5Þ3:6%Þ
þðð$100MM 20:3Þ2:5%Þþð28;000;000;000 13:8% 0:296ÞÞ
Conclusions
Many variables affect the cost of pipeline and LNG transport of natural gas. In this article
we have developed a generic model for the comparison of pipelines and LNG that can be
adapted to different projects by revising the prices for the various factors included in the
model.
The exact break-even point between LNG and pipelines will depend on the volume of
natural gas and the distance that it is transported. Pipeline transport is a better option for
larger volumes and shorter distances. LNG transport has the lowest costs for smaller vol-
umes (up to 15 bcmpa) and for longer distances.
422 M. Ulvestad and I. Overland
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A substantial amount of natural gas is required as fuel for internal use in the liquefac-
tion process, and for compressor stations in the case of pipelines. This causes the costs of
both transport options to vary with the price of natural gas and greenhouse gas emissions.
For distances up to 9100 km, LNG transport is more exposed to uctuations in the prices
of natural gas and greenhouse gas emissions than pipeline transport. This is because the
LNG process liquefaction, shipping and re-gasication requires a larger share of the
natural gas than do pipeline compressor stations over such distances. At greater distances,
pipelines will expend more gas than will LNG, making pipelines more sensitive to changes
in the price of natural gas and greenhouse gas emissions. We have thus identied 9100 km
as an important threshold for the comparison of LNG and pipelines. In addition to this
threshold, the amount of gas transported also impacts signicantly on the comparison. In
general, an increase in the price of natural gas and/or greenhouse gas emissions will favour
the choice of pipeline transport.
If the aim is to replace coal and oil with natural gas in order to reduce greenhouse gas
emissions, account should also be taken of the emissions associated with the different
transport options for natural gas. On the other hand, more effective technologies developed
in the future may reduce the burning of natural gas in connection with its transport. This
is particularly true in the case of LNG, where the technology is newer and far more
complex than the technology involved in pipelines. Future innovations within LNG may
improve the viability of LNG relative to pipeline transport, as well as relative to coal and
oil.
Additional conditions must also be taken into account when considering the transport of
natural gas. LNG transport avoids transit countries and the associated, possible legal and
political risks, and provides exibility to sell on the market where the price is highest.
Price differences for natural gas on different regional markets can be so great as to cancel
out the impact of the higher fuel consumption and greenhouse gas emissions involved in
LNG.
This article has not taken into account greenhouse gas emissions from the production of
steel for pipelines, or the materials for LNG facilities and tankers. We have shown the
effect of variations in the prices of natural gas and greenhouse gas emissions on the
relative cost-efciency of LNG and pipelines, but with only a partial analysis of the full
climate impacts. Full assessment of the full carbon footprint of these two transport options
for natural gas would require expanding the model to cover also the production of steel
for pipes. That would be a logical next step for further research.
List of variables
N = natural gas (cubic meter per year)
L = LNG (million tonnes per year)
p = price of natural gas (US$ per cubic meter)
δ= distance (in km)
γ= number of operating years
C = pipeline capital costs (US$)
μ= pipeline diameter (inches)
α= number of compressor stations
c = total capacity of compressor stations (horsepower)
O
P
= pipeline operating costs per year (US$)
Natural gas and CO
2
price variation 423
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τ= OPEX as a share of CAPEX pipelines (%)
= loss per compressor station (%)
η= distance between compressor stations (in km)
P = capital cost of liquefaction plant
S = capital cost of LNG carriers
λ= speed of LNG carrier (km/h)
k = capacity per LNG carrier (cubic meter natural gas)
R = capital cost of re-gasication terminal
O
L
= LNG operating costs per year (US$)
= OPEX as a share of CAPEX liquefaction plant (%)
ν= OPEX as a share of CAPEX LNG carriers (%)
σ= OPEX as a share of CAPEX re-gasication terminal (%)
ω= share of natural gas used as fuel for the LNG chain (%)
Θ= liquefaction share of natural gas used in the liquefaction process (%)
ξ= boil-off per day (% of natural gas)
/= shipping fuel per day (% of natural gas)
Ω= re-gasication share of natural gas used in the re-gasication process (%)
E
P
= pipeline CO
2
emission costs
E
L
= LNG CO
2
emission costs
A = price of CO
2
emission allowance (US$ per ton CO
2
)
=CO
2
emission (kg per million Btu of natural gas)
List of parameters
p = $0.296 per m
3
[49]
γ= 20 [45]
μ=40‘‘,48‘‘ ,56‘‘
c = 147,512 per compressor station
τ= 3.5% [14]= 0.4% [14] η= 200 km [24]
λ= 36.114 [33]
k = 152,950,000 [33]
= 3.5% [14]
ν= 3.6% [14]
σ= 2.5% [14]
Θ= 9.5% [14,47]
ξ= 0.17% per day [14]
/= 0.1389% per day [47]
Ω= 2.5% [14,47]
A = $29.84 per ton CO
2
[51]
= 53.06 kg per MMBtu [50]
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426 M. Ulvestad and I. Overland
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... In the literature, there are a small number of research scrutinizing costs of NGPC projects. Those studies, almost all of which were studied in United States, indicate that there are several cost components in NGPC like labor, material (pipes), miscellaneous and right of way (ROW) (Parker, 2004;Rui et al., 2011aRui et al., , 2011bRui et al., , 2012Thaduri, 2012;Ulvestad & Overland, 2012;Zhao, 2000). In these studies, details of which will be shared in literature part, while some researchers try to obtain an equation that gives total estimated cost with those four cost components, others contributed the descriptive statistics of the total costs of pipeline projects in the past to the literature. ...
... Because of the evaluations, it was stated that the cost items with the highest share in the costs of natural gas pipelines were labor with 40% and material costs with 31% (Thaduri, 2012). Ulvestad and Overland (2012) examined the cost analysis of two different natural gas transmission options, pipeline and liquefied natural gas (LNG). Authors concluded that pipeline transport is a better option for larger natural gas volumes and shorter distances while it is LNG for smaller volumes and longer distances (Ulvestad & Overland, 2012). ...
... Ulvestad and Overland (2012) examined the cost analysis of two different natural gas transmission options, pipeline and liquefied natural gas (LNG). Authors concluded that pipeline transport is a better option for larger natural gas volumes and shorter distances while it is LNG for smaller volumes and longer distances (Ulvestad & Overland, 2012). Bai et al. (2013) estimated the annual cost for the pipelines required for CO2 supply, with the support of the existing literature in their studies. ...
Conference Paper
Natural gas pipeline construction (NGPC) projects are inherently includes high changefulness like any other construction works. Considering that variability, it can be stated that to make an accurate cost estimation is difficult. The main objective of this paper is to achieve a coherent mathematical equation to be able to make a preliminary cost estimation of NGPC costs. To this end, a number of pipeline cost data, which is in US dollar currency, was obtained for the period 1986-2010. With this data, a simple regression equation was tried to be revealed by working through statsmodels, one of the libraries used for the Python programming language. It was concluded that a significant part of the NGPC cost could be explained with the diameter and length variables. In this respect, this paper has the potential to assist the institutions responsible for the execution of the NGPC processes of the Turkey or the contractors considering investment or at the decision-making stage. Moreover, the paper presents a first attempt at both predicting of NGPC costs in Turkey and executing that operation by using Python programming language.
... 4,6,19,21 The EFs we use are consistent with those compiled for the National Renewable Energy Laboratory (NREL) harmonization project 16 and used as input to lifecycle analysis models such as the Greenhouse gases, Regulated Emissions, and Energy use in Transportation (GREET) model. 17 We estimate lifecycle AFs from combustion of NG and HFO assuming energy is generated by the powerships 68.75% of each day (as per the licensing requirement), 22 that the LNG tanker used holds $170 000 m 3 LNG, 23 that LNG is from Shell operations in Nigeria 24 $2600 nautical miles from South African ports, that the LNG tanker travels at 20 knots 25 with an energy capacity of 40 MW, 26 that the energy required for liquefaction is 0.38 kWh (kg LNG) À1 , 27,28 and that regasication uses 2.5% LNG by volume. 28 We also consider the effect of longer tanker travel distances if instead LNG is from Shell facilities further aeld that already supply to Atlantic and Indian Ocean markets. ...
... 17 We estimate lifecycle AFs from combustion of NG and HFO assuming energy is generated by the powerships 68.75% of each day (as per the licensing requirement), 22 that the LNG tanker used holds $170 000 m 3 LNG, 23 that LNG is from Shell operations in Nigeria 24 $2600 nautical miles from South African ports, that the LNG tanker travels at 20 knots 25 with an energy capacity of 40 MW, 26 that the energy required for liquefaction is 0.38 kWh (kg LNG) À1 , 27,28 and that regasication uses 2.5% LNG by volume. 28 We also consider the effect of longer tanker travel distances if instead LNG is from Shell facilities further aeld that already supply to Atlantic and Indian Ocean markets. These include Oman ($5000 nautical miles) and Trinidad and Tobago ($6700 nautical miles). ...
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Power barges or powerships that operate on natural gas (NG) are an increasingly appealing easy-to-use solution to electricity deficits in Africa, Asia, the Middle East, and the Caribbean. Global generating capacity has increased from 0.1 to 2.6 GW, and 4.4 GW is under construction. South Africa has licensed three powerships to provide 1.2 GW generating capacity with foreign liquefied NG (LNG) over 20 years. To understand the importance of this source, we estimate lifecycle emissions of GHGs and air pollutants for South Africa and extend this to the global fleet. Annual lifecycle GHG emissions for 1.2 GW generating capacity total 2.6–3.8 Tg carbon dioxide equivalents (CO2e) using 100 year global warming potentials (GWPs). This increases to 4.0–7.1 Tg CO_{2} e using 20 year GWPs, due to the potency of fugitive methane (CH4). Adoption of air pollutant emission control technology will need to be enforced to achieve compliance with national standards for fine particles (PM) and nitrogen oxides (NO_{x}). A global fleet of 7.0 GW generating capacity reliant on domestic NG could emit 12 Tg CO_{2}, 2.2–8.6 Tg CH_{4}, 4.3 Gg NO_{x}, and 2.6 Gg PM. Additional NOx and SO2 emissions would result from imported LNG, as LNG tankers burn dirty fuel oil, though SO_{2} emissions may be curtailed with recent stricter limits on the fuel sulfur content. These powerships could have important regional impacts, but emission estimates are uncertain. Characteristic emission factors, detailed operating conditions, and NG composition data are urgently needed to address uncertainties in emissions for air quality and climate modelling of this emergent source.
... κ is the rate of the NG utilized as fuel for the compressor stations (0.05 percent), N volume of NG (cmy), P cost of NG ($/cm), η distance (km) between the compressor stations. κ varies for common onshore pipeline (Ulvestad and Overland, 2012). The feedstock costs depends on the extraction costs and processing costs which increased one and a half times Salameh and Chedid (2020)'s numbers. ...
Chapter
Full-text available
The purpose of this study is to estimate economic values of pipeline gas transitions from the Eastern Mediteranean offshore resources to Southern Europe in the presence of energy crisis in Europe. Net present values of seven pipelines are estimated. To determine which transition is more economically feasible for Europe, we have used two different price models and six different cost models to estimate net present values of seven natural gas pipelines six of which through Turkey and one through Greece. The study focuses on economic values of Mersin pipeline and the Eastern Mediterranean pipeline. Subsequently, each is compared with liquefied natural gas shipping from Egypt to Cartegana of Spain.
... Therefore, it can also be used to fuel natural gas vehicles (NGV), including cars, buses and trucks of various sizes [127]. In the past, natural gas (NG) was considered to be economically unimportant due to the absence of viable method for NG storage or transport existed being flared and/or entirely consumed within the local network [144]. Developments of production processes, storage, and transportation created the tools required to commercialize NG into a global market Table 5 Comparative table of end-use and production cost of biogas/biomethane from sugarcane vinasse. ...
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Anaerobic digestion (AD) is a multipurpose technology. One of the AD outcomes is biogas that can be used to supply a local thermal demand, electricity generation or upgraded to fuel vehicle. Brazil has the largest potential for producing biogas, due to its extensive agroindustrial production plus the fact that the country has a population of over 210 million inhabitants. The Brazilian Association of Biogas and Biomethane (ABiogás) reports a potential biogas production of 41.4 billion m³ per year in the sugar-energy sector. However, less than 2% of this is achieved, indicating that the biogas is still chemically, economically, and politically invisible. The current technologies for the production, purification and end-use of biogas/biomethane were reviewed and presented in the context of sugarcane biorefineries. One of the major findings has indicated a thermal efficiency of 85% and a national grid surplus of 74–121 kWh.ton⁻¹ sugarcane when steam boilers connected to electricity generators are used. Alternatively, a quarter of the vinasse generated by a medium-size sugarcane mill (600 m³ d⁻¹) would be enough to supply the diesel consumption of on agricultural operations. The motivation of this review came from the fact that normally renewable energy does not reach its potential due to the lack of references on technological, regulatory and management in their productive arrangements: essential aspects to make them feasible. Therefore, it is expected to strengthen the panorama of research in the biogas system to properly fit with the current expansion and diversification of the Brazilian energy matrix.
... This is multiplied by the number of stations (compressors route_pipe,i,j ) along that route. Data on the number of compressor stations sited along each pipeline in Europe was not publicly available; therefore, an assumption of 200 km between stations is assumed [67], p. 411). ...
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As indigenous production declines, the European gas market is becoming increasingly dependent on imports. This poses energy security questions for a number of countries, particularly in the north-east of Europe. A suite of mathematical models of the European natural gas network has been borne from these concerns and has traditionally been used to assess supply disruption scenarios. The literature reveals that most existing European gas network models are insufficiently specified to analyse changes in supply and demand dynamics, appraise proposed infrastructure investments, and assess the impacts of supply disruption scenarios over a range of time horizons. Furthermore, those that are suited to these applications are typically proprietary and therefore publicly unavailable. This offers an opportunity to present a new model. The Gas Network Optimisation Model for Europe (GNOME) is a dynamic, highly granular mixed-integer linear optimisation model of the European natural gas network and its exogenous suppliers. GNOME represents demand and supply for all EU-27 Member States except Cyprus, Luxembourg, and Malta. The UK, Norway, Switzerland, Belarus, Ukraine, and Turkey are also included. Russia, the Southern Corridor suppliers, Qatar, North Africa, Nigeria, and the Americas are modelled as supply-only regions. GNOME satisfies gas demand in each country by generating a cost-minimal mix of indigenous gas production, pipeline flows, LNG imports, and storage use. If demand cannot be met using existing infrastructure, GNOME will generate a cost-optimal investment strategy of pipeline, LNG regasification, and gas storage capacity additions. The model solves on a monthly basis, from 2025 to 2040, in 5-year steps. The capabilities of GNOME are demonstrated by tasking it to analyse the impacts of a failure to complete the upcoming Nord Stream 2 pipeline between Russia and Germany. The complete formulation of GNOME including input files, equations, and source code is provided.
... Comparison of some sample "green" electromotive energy chains. Sources:[5,[6][7][8][9][10] ...
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While PV is poised to become the leading renewable energy source in the EU and globally, both in terms of capacity and net output, its low spatial power density poses challenges in its effective use and distribution. One of the emerging use-cases for PV power is in electromotive applications, ranging from automotive (Vehicle integrated PV-VIPV-for cars, buses, trucks), rail-transportation (urban and extra-urban rail) and marine (recreational boats and sea-and inland waterway transport). Each of these has a particular topology, both of proximity to stationary PV, energy density of storage, and available surface area for mobile PV (which integrates VIPV with fixed PV assets dedicated to vehicle fleet electricity supply). In order to maximize benefit the entire PV Value chain in these applications, we identify the individual importance of several necessary components in planning and operational intelligence, and provide relevant examples based on current and emerging technology as well as an integrative framework for the modeling of these and related value chains based on energy flow modeling.
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Residential emissions significantly contribute to air pollution. To address this issue, a clean heating campaign was implemented to replace coal with electricity or natural gas among 13.9 million rural households in northern China. Despite great success, the cost-benefits and environmental equity of this campaign have never been fully investigated. Here, we modeled the environmental and health benefits, as well as the total costs of the campaign, and analyzed the inequality and inequity. We found that even though the campaign decreased only 1.1% of the total energy consumption, PM2.5 emissions and PM2.5 exposure experienced 20% and 36% reduction, respectively, revealing the amplification effects along the causal pathway. Furthermore, the number of premature deaths attributable to residential emissions reduced by 32%, suggesting that the campaign was highly beneficial. Governments and residents shared the cost of 2,520 RMB/household. However, the benefits and the costs were unevenly distributed, as the residents in mountainous areas were not only less benefited from the campaign but also paid more because of the higher costs, resulting in a notably lower cost-effectiveness. Moreover, villages in less developed areas tended to choose natural gas with a lower initial investment but a higher total cost (2,720 RMB/household) over electricity (2,190 RMB/household). With targeted investment and subsidies in less developed areas and the promotion of electricity and other less expensive alternatives, the multidevelopment goals of improved air quality, reduced health impacts, and reduced inequity in future clean heating interventions could be achieved.
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Türkiye’nin Karadeniz’de tarihinin en büyük doğal gaz keşfinin ardından net doğal gaz ihracatçısı olmasına yetecek doğal gazı keşfetmesi ihtimaline dair bir gelecek öngörüsü sunmak amacıyla hazırlanan çalışma dünya doğal gaz piyasasını talep temelli inceleyerek doğal gaz pazarının 2019 yılındaki durumunu özetlemeyi hedeflemektedir. Bununla beraber çalışmada, doğal gazın taşınması için kullanılan denizyolu LNG taşımacılığı ve boru hattı taşımacılığını ayırt edici hale getirilmeye çalışılmıştır. Araştırma neticesinde elde edilen verilerden hareketle de tartışma bölümünde Türkiye’nin doğal gaz ihracatı için hangi pazarlara hangi taşımacılık yöntemiyle ulaşabileceği ve muhtemel uluslararası işbirliği ihtimalleri derlenmeye çalışılmıştır.
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The development of a hydrogen infrastructure is the subject of increasing research interest. Many researchers are working toward estimating the cost of such an infrastructure. Pipeline delivery of hydrogen is being considered but the expected costs are not well understood, as few pipelines exist today. This paper analyzes the construction costs of natural gas, oil, and petroleum product transmission pipelines and poses questions about the difference that hydrogen would make in these costs.
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There must be few other situations where there are eager purchasers of natural gas (India and Pakistan), willing suppliers of natural gas (Turkmenistan, Iran, Qatar and Oman), and yet, no pipeline. The distances involved are modest, and techno-economic viability appears straightforward. This paper examines in detail the policy, technology, and economics of an overland pipeline supplying natural gas to Pakistan and India. Such a pipeline would be shared by both countries, and would represent a unique opportunity for cooperation.† As pipelines exhibit significant economies of scale, a shared pipeline would offer the lowest price natural gas for both countries. Pakistani consumers would obtain cheaper gas than from a lower capacity pipeline for their exclusive use, also benefiting from transit fees paid by Indian consumers. An alternative to land-based pipelines through Pakistan for India would be liquefied natural gas, which is more expensive due to the capital-intensive nature of the liquefaction process. However, any overland gas pipeline does not depend solely on economic viability, but on political acceptance as well. This study addresses some of the potential concerns, briefly discussing options for overcoming security of supply worries. Through cooperating on such a venture, one that offers the promise of significantly helping to build the infrastructure of both countries, there is the possibility of the neighboring countries becoming partners in progress, instead of languishing as prisoners of geography.
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Natural gas pipeline operators in 2009 saw their profits drop to lows not seen since 2006, falling nearly 9% despite the lesser 4.27% drop in revenues. The diminished quantity of proposed pipeline mileage coincided with continued upward momentum in labor costs, as reflected in data OGJ gathered for the 12 months ending in June 30, 2010. Volumes of natural gas sold by pipelines have been steadily declining, so that, beginning with 2001 data in the 2002 report, the table only lists volumes transported for others. The FERC made an additional change to reporting requirements for 1995 for both crude oil and petroleum products pipelines. Positions in these rankings shift year to year, reflecting normal fluctuations in companies' activities and fortunes. But also, because these companies comprise such a large portion of their respective groups, the listings provide snapshots of overall industry trends and events.
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Book
The issue of energy supply revolves around not only hydrocarbon resources but also their delivery. This is a new way the international politics of oil and natural gas crucial to any explanation of the tensions involving Central Asia, the Middle East, Russia, China and, indeed, Europe.
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The emerging global market in natural gas has the potential to meet rising demand for electricity worldwide. The United States' own gas supplies are dwindling, but elsewhere vast, unexploited resources are becoming ever more accessible now that gas can be liquefied, shipped, and used efficiently. New energy linkages will create new risks, but none that cannot be managed through proper diversification.
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A process is disclosed for producing a purified liquefied natural gas (LNG) from a raw natural gas feed containing methane and hydrocarbon impurities of Câ and higher wherein the raw feed is cooled, distilled to remove impurities, and liquefied, such that the distillation reflux is supplied by a portion of a subcooled methane-rich liquid stream exiting the middle bundle of a three bundle main cryogenic heat exchanger having a mixed cryogenic refrigerant. The raw feed is cooled in the first bundle of said main exchanger.