Transctions of the Korean Hydrogen and New Energy Society - Vol. 32 , No. 2

[ Article ]
Transactions of the Korean Hydrogen and New Energy Society - Vol. 32, No. 2, pp.127-133
Abbreviation: KHNES
ISSN: 1738-7264 (Print) 2288-7407 (Online)
Print publication date 30 Apr 2021
Received 19 Jan 2021 Revised 20 Mar 2021 Accepted 21 Apr 2021
DOI: https://doi.org/10.7316/KHNES.2021.32.2.127

Comparative Life Cycle Assessment of Liquefied Natural Gas and Marine Fuel for Ship from Well to Hull
OCKTAECK LIM1, ; SANGJIN YOON2
1School of Mechanical Engineering, University of Ulsan, 93 Daehak-ro, Nam-gu, Ulsan 44610, Korea
2School of Mechanical Automotive Engineering, Nambu University, 1 Nambudae-gil, Gwangsan-gu, Gwangju 62271, Korea

유정에서 선체까지 선박의 액화천연가스 및 해양 연료의 비교 수명주기 평가
임옥택1, ; 윤상진2
1울산대학교 기계공학부
2남부대학교 자동차기계공학과
Correspondence to : otlim@ulsan.ac.kr


2021 The Korean Hydrogen and New Energy Society. All rights reserved.
Funding Information ▼

Abstract

In this study, well to hull was obtained by life cycle assessment (LCA) and the greenhouse gases, regulated emissions, and energy use in transportation model (GREET), which is developed by Argonne National Laboratory to evaluate the environmental impact of marine liquified natural gas (LNG) and marine fuel. This study compared the environmental impact of marine LNG and marine fuels, which were caused by green house gases (GHG) emissions and energy consumption. The effect resulted from well to pump (WTP) process and pump to hull (PTH). Natural gas has the potential to generate more greenhouse gases than liquid fuels due to the amounts of leaks of the gas that were sent out the air during production and processing. Nevertheless, the results showed that the greenhouse gases produced during transportation were enough to reduce the disadvantages of PTH process. The research expects that the results will be in accordance with the environmental policy of South Korea.


Keywords: Liquified natural gas(LNG), GREET, Well to hull, Life cycle assessment(LCA), Marine fuel, Greenhouse gas
Keywords: 액화천연가스, 에너지⋅교통 분야 환경 영향성 평가 모델, 선체 적정성, 전 과정 평가, 해양 연료, 온실가스

1. Introduction

Since January 2020, the International Maritime Organization (IMO) will strengthen a regulation to enforce the content of sulfur compounds in ship engine exhaust gas from 3.5% to 0.5%. In response, using LNG as a fuel of transportation has emerged. To respond to IMO’s environmental regulations, shipbuilders in each country are ordering eco-friendly ships in consideration of new ship construction. The order status of ships using LNG as fuel is shown in Fig. 1. LNG-fueled ships are rapidly being applied and distributed in Northern Europe1). Since the first passenger ship ‘Glutra’ was built in Norway for the first time in 2000, NASSCO has recently ordered 3,400 TEU container ships.


Fig. 1. 
Order status of ships using LNG as fuel

The current market is still hesitant to introduce LNG-fueled vessels. However, if LNG-fueled vessels are ordered in earnest, the size of the market is not expected. However, the biggest obstacle to ordering LNG fueled vessels is the lack of infrastructure for fueling vessels2). Even though the disadvantages, The Korea Government plans to introduce the LNG industry. Life Cycle Assessment for vehicles is studied in South Korea3). There is little research on ship emissions. Especially, emissions from return gas, boil-off-gas are hard to evaluate.

In this study, we evaluated the environmental impact of the whole process for well-to-hull. It analyzes and evaluates the environmental problems arising from each process of the product through evaluation, including the production and transportation of fuel used for ships as well as operation and compared fossil fuels with NG. Therefore, it is necessary to compare and analyze the well to pump (WTP) process using The greenhouse gases, regulated emissions, and energy use in transportation model (GREET). Generally, NG occurs greenhouse gas in the WTP than diesel due to the amounts of leakage generated during the production and treatment process.

Nevertheless, the greenhouse gases produced during transportation are expected to be good enough to reduce the shortcomings because of the pump to hull (PTH) process. A more detailed comparison of the operation part is needed through WTP analysis using GREET. The PTH result is obtained from the emission information in operating. There are many limitations to conducting experiments using large marine engines. Therefore, the PTH is calculated from an engine specification which is operated in ships (Ilshin Shipping and Incheon Port Authority).


2. Methods
2.1 Life cycle analysis (LCA)

LCA provides analysis of the environmental prospect and potential environmental impacts throughout life cycle of a product from raw material acquisition through production, use, end-of-life treatment, recycling and final disposal. LCA is developed and utilized by many companies, and research institutes around the world in the 1970s in order to compare and analyze the environmental friendliness of products. The process in LCA is described in Fig. 2. It is possible to analyze and evaluate the environmental problems caused by the process of the product, and it is possible to perform a comparative analysis of the products.


Fig. 2. 
Process of life cycle assessment

2.2. GREET

GREET developed by Argonne under the auspices of the US Department of Energy (Energy Efficiency and Renewable Energy)4). It is a program that enables LCA of energy usage and emissions which occur during production and transportation of fuel as well as the driving of the vehicle. Also, it can accumulate data on a wide range of data, including moving parts in the picking and transportation production of raw materials. It is calculated based on actual measurement results rather than simulation results. In addition to gasoline and diesel, there is data on full-range fuels used in transportation such as NG, electricity, and bio-oil. Not only energy consumption but also exhaust gas and greenhouse gas emissions are investigated, and it is very useful for comparative analysis in accordance with the purpose of LCA. GREET includes more than 100 fuel routes, including petroleum and NG fuels, as well as biofuels, hydrogen, and electricity from a variety of energy sources. It is easy to compare and analyze the effects of each stage in the calculation by dividing the process from fuel production to supply. It provides the sources, usage from, contents of the data used in the GREET development process in the public domain.

2.3 LCA method

Well-to-Hull processes of marine fuel and LNG are described in Figs. 3, 4. To evaluate the environmental impact of diesel compared to NG, we use GREET to compare the following WTP processes5). In the case of NG, it is expected that more greenhouse gases will be generated than diesel due to the amounts of leaks generated during production and processing. However, compared to diesel, the amount of traffic generated during transport is expected to be good enough to reduce the above disadvantages. In order to compare and analyze this, we want to compare and analyze the operation part using GREET and WTP analysis, PTH data.


Fig. 3. 
Well to hull process of marine fuel


Fig. 4. 
Well to hull process of LNG

In the case of the WTP process, it is difficult to obtain reliable data, and there is a lack of extensive data on each process. In order to solve this problem, we would like to compare and analyze the results using the following GREET results.

2.4 WTP
2.4.1. Marine fuel

The use of LNG as a common marine fuel is likely to increase as a bunkering infrastructure develops and it becomes a recognised and viable alternative to traditional marine fuels, driven mainly by the need to comply with the forthcoming IMO global sulphur regulation in 2020.

GREET shows five things related to the WTP process of Marine fuels. The values are 1) petroleum-based marine fuels from crude oil, 2) fisher-tropsch diesel fuel from NG, coal and cellulosic biomass, 3) hydro processed esters and fatty acids (HEFA) or hydro processed renewable diesel (HRD) diesel fuel from bio-oil found in soybeans, palm, rapeseed, jatropha, camelina, and algae, 4) renewable diesel from pyrolysis of cellulosic biomass, and 5) biodiesel or fatty acid methyl esters (FAMEs) from bio-oil found in soybeans, palm, rapeseed, jatropha, camelina and algae. Among them, crude oil based marine fuels is chosen. The average distance from oil importing country to the Korean refinery is 12,135 km based on Korea National Oil Corporation’s data, using Voyage calculator. According to the Korea National Oil Corporation, most volume of crude oil is imported from overseas. 76% of total crude oil imports are from the Middle East (Saudi Arabia, Kuwait, Iraq, Qatar, etc.) in 2018. Domestic data on crude oil import, preparation and distribution for the diesel LCA were provided by the Korea Petroleum Association.

2.4.2. LNG

The data of LNG required for WTP analysis are as follows. We consider the energy efficiency of raw material extraction and processing and the ratio of process fuel in NG production in the NG recovery and NG processing steps. Korea Gas Corporation provides information about NG import. From the information, we calculate the import distance to consider the transportation step6). The information describes in Table 1. In the case of storage, regasification, and distribution step after importing LNG, the data was used in GREET because there was not enough data accumulated.

Table 1. 
Import distance to South Korea of natural gas (2018)
Country Distance (km) Import volume (ton)
Qatar 11,297 14,250,000
Australia 6,667 7,870,000
Oman 10,556 4,280,000
The U.S. 10,556 4,660,000
Malaysia 4,598 3,700,000

2.5 PTH

Although, it is necessary to find and compare diesel ships of similar specifications as LNG vessels, it is difficult to obtain information on the number of days of sailing, sailing distance, ship weight (including load weight), fuel consumption and electricity consumption for a certain period required for calculation. There are three types of marine fueled vessels which are bulk carriers, oil tankers, and container ships. At the time, GREET only provided specifications of these ships. We average the total energy use and greenhouse gases to calculate data in the operation step. The information related to ships using LNG as fuel is not explained. Therefore, we get data from a company that operates LNG ships in South Korea.


3. Results

In the case of marine fuel, the WTP result of energy use and greenhouse gas emissions are in Table 2. In the pump to hull pathway, the GHG emissions are only calculated from the specification of HYUNDAI MAN B & W TYPE: 6G50ME-GI used in Ilshin Shipping LNG propulsion vessel because of the company’s secret. The GHG emissions result is 74.4 g/MJ in diesel mode.

Table 2. 
Well to pump results in marine fuel
Parameter Residual oil Marine distillate Low suffer marine distillate
Energy use (kJ/MJ) 152.1 202.8 202.8
GHG emissions (g/MJ) 13.74 16.77 16.78

Include processes of extraction, production processing, and storage before importing LNG to Korea. Since NG also uses GREET, it is necessary to analyze additional information by importing the country later. Based on GREET, energy use: 59,287 kJ/GJ. GHGs emission results: 12,606 gCO2/GJ. In the NG processing step, energy use is 4,510 kJ/GJ, and GHGs emission result is 34,741 gCO2/GJ. In the transportation step, GREET only provides a specification of oil tankers which transport crude oil, so we use the same value as well. LNG carriers are expected to generate fewer emissions than diesel ships because it generates electricity and heat using vented gases. The results are 19,646 kJ/GJ and 1,643.8 gCO2/GJ. In the storage, re-gasification, and distribution step, the data is not accumulated enough to evaluate, so we use the value in GREET. The values are 15,478 kJ/GJ and 1,904 gCO2/GJ.

For LNG, the WTP result of energy use is 194.8 kJ/MJ, and GHG emissions is 19.75 g/MJ. In the pump to hull step, the GHG emissions result is 56.5 g/MJ in gas mode.

In Figs. 5-7, all the results of WTP are organized to be comprehensive. In the case of WTP, LNG has higher energy consumption and GHGs emissions due to the addition of processes such as compressed gas and re-liquefaction, as well as the amount of gas discharged during production compared to marine fuels such as residual oil and marine distillate. Energy consumption data in PTH can’t have been obtained from Ilshin. However, it is considered that the energy consumption of LNG is higher because of use to boil-off-gas reliquefaction For PTH, GHGs emissions from operations are far above the WTP process.


Fig. 5. 
Marine fuel WTP energy usage results (kJ/MJ)


Fig. 6. 
Marine fuel WTP GHG emissions results (g/MJ)


Fig. 7. 
Marine fuel WTH GHG emissions results (g/MJ)


4. Conclusions

The research was carried out to investigate the environmental impacts of LNG as fuel, comparing Marine fuels. LCA analysis shows that NG produces more GHGs in WTP compared to liquid fuel for ships, but fewer in PTH. In the case of PTH, the energy consumption and GHG emissions in operation far exceed the WTP process due to the nature of ships that must cross the Pacific. Therefore, LNG, which emits less GHGs than diesel, is thought to be much better than diesel in terms of the environment but may differ from actual operating conditions, so engine experiments and additional data are needed to confirm in the future.

In South Korea, both NG and marine fuels depend on imports, so GHG emissions from WTP are relatively low. In order to satisfy the IMO regulations, the exhaust gas generated during ship operation (PTH) should be managed in a focused manner. Therefore, the amount of exhaust gas generated during operation is less than that of marine fuel, so it is considered to suitable for satisfying environmental regulations. However, more detailed comparisons are needed between engine efficiency and operating costs (price, storage costs, safety management costs, etc.) compared to diesel. Nevertheless, the emissions from WTP in LNG, which is higher than marine fuels, couldn’t ignore.


Nomenclature
LCA : life cycle assessment
GHG : green house gases
LNG : liquified natural gas
WTP : well to pump
PTH : pump to hull
HRD : hydro processed renewable diesel
HEFA : hydro processed esters and fatty acids
IMO : international maritime organization
GREET : the greenhouse gases, regulated emissions, and energy use in transportation model

Acknowledgments

This research was financially supported by the EU Cooperation Promotion Project of National Research Foundation (NRF-2019K1A3A1A7911296711, Technology for improvement energy efficiency and environmental footprint of inland waterway vessels).


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