Published at : 01 Apr 2022
Volume : IJtech
Vol 13, No 2 (2022)
DOI : https://doi.org/10.14716/ijtech.v13i2.5087
Sumanta Buana | Department of Marine Transportation Engineering, Institut Teknologi Sepuluh Nopember, Surabaya 60111, Indonesia |
Katsuhisa Yano | Hibiki, Wakamatsu, Kitakyushu, Fukuoka 808-0035, Japan |
Takeshi Shinoda | Department of Marine Systems Engineering, Kyushu University, 744 Motooka Nishi-ku, Fukuoka 819-0395, Japan |
All
ocean-going ships must be outfitted with adequate ballast water equipment in
compliance with Regulation D-2, Section D, Standards for Ballast Water
Management, International Convention for the Control and Management of Ships’
Ballast Water and Sediments, promoted by the International Maritime
Organization. However, it is difficult to choose the appropriate equipment
because the methods used to develop the equipment have similar advantages and disadvantages
. Such circumstances make it difficult for two parties who have conflicting
priorities, ship designers and ship owners, to choose the most suitable
equipment. To address this issue, multi-criteria analysis is effective because
it can simultaneously consider several criteria under evaluation as early as
possible in the design stage. The aim of this paper is to propose an evaluation
methodology for out?tting appropriate ballast water management system (BWMS)
equipment by applying multi-criteria analysis combined with the value
engineering concept. This combination can directly compare the bene?ts of
function and the disbenefits of cost aspects of a particular system. Nine
available methods were evaluated before their installation on ocean-going vessels
with a carrying capacity of 300,000 deadweight
tons (DWT). The results of the analyses
show that, from a ship designer’s point of view, the most appropriate method is
one that uses ozone; while, from the viewpoint of a ship owner, the most
appropriate method is one that uses a combination of a filter and ultraviolet
radiation. Ship designers and ship owners have di?erent opinions. A ship
designer emphasizes cost reductions and profit maximization. On the other hand,
a ship owner prefers to have a ship out?tted with a system that is easy to
operate as well as to maintain.
Ballast water management system; Multi-criteria analysis; Ship outfitting; Value engineering
Ship out?tting, which consists of various types of processes, is one of the most important stages in designing and building a vessel. Outfitting requires equipment that must comply with the International Convention for the Control and Management of Ships’ Ballast Water and Sediments promoted by the International Maritime Organization (IMO), which entered into force on September 8, 2017 (IMO, 2004). Ballast water is very important for ensuring the seaworthiness of non-fully-laden vessels (NRC, 1996). When a vessel o?oads its cargo, its ballast tanks are flooded with seawater for stability. The seawater is then discharged at a particular port when the vessel is reloaded with cargo (see Figure 1). However, ballast water also introduces invasive organisms, which are very dangerous to ocean health (La Carbona et al., 2010).
Figure 1 Ballasting proc
A ballast water treatment system must be
selected at an early stage of ship design because it in?uences the layout of
the machinery space and increases capital cost. Each treatment method sometimes
performs similarly, making it difficult for both ship owners and ship designers
to choose the most appropriate equipment. To address this issue, multi-criteria
analysis is effective because it can simultaneously consider several
qualitative criteria under evaluation as early as possible in the design stage.
However, conventional multi-criteria analysis usually ranks criteria without
considering the degree of appropriateness of the results. And yet, it is
important to consider the degree of appropriateness as doing so yields clear
insights that can reduce the gap between the opinions of ship owners and ship
designers. Thus, the aim of this paper is to
propose an evaluation methodology for out?tting ut appropriate ballast water
management equipment by applying multi-criteria analysis combined with a value
engineering concept. The value engineering concept will be introduced in the
evaluation methodology because it is considered the bene?ts of function aspect
and disbenefits of cost aspects The evaluation based on the views of ship
owners and ship designers/shipyard was conducted for vessels with a carrying
capacity of 300,000 deadweight tons (DWT): very large crude carriers/very large ore
carriers. These vessels must comply with Regulation D-2, Annex – Section D,
Standards for Ballast Water Management, International Convention for the
Control and Management of Ships’ Ballast Water and Sediments (IMO, 2004).
Table 1 Ballast Water Management System (BWMS)
Method
Treatment Components |
Treatment Process |
Capacity |
Neutralization | |
(T1) |
Ozone |
Ozone injected into ballast tank will kill harmful
microorganisms and produce hypobromite as a byproduct. The byproduct will be
neutralized when de-ballasting is carried out. |
3,000 |
yes |
(T2) |
Filter + |
After filtrating plankton sized 50 m? or larger, harmful microbes will be
exterminated by filling tanks with sodium hypochlorite, agitated by a venture
tube. The residual chemical is then neutralized. |
4,500 |
yes |
(T3) |
Filter + UV |
Microbes resulting from plankton filtration through
a disk-filter will be destroyed using UV. |
6,000 |
no |
(T4) |
Filter + UV + TiO2 |
After filtrating plankton sized 50 m? or larger,
microbes will be killed using UV, supplemented with titanium dioxide. The
residual chemical is neutralized when de-ballasting. |
3,000 |
yes |
(T5) |
Filter + N2 gas +
Cavitation |
After filtrating plankton sized 50 m? or larger, microbes are destroyed by sterilization in the
cavitation unit using nitrogen gas and electrolysis. |
10,000 |
no |
(T6) |
Flocculant + Filter |
Microbes are sedimented by filling tanks with
flocculant and magnetic powder and are then separated from seawater by a
magnetic disc. |
2,400 |
yes |
(T7) |
Electrolysis |
The microbes are destroyed by sodium hypochlorite
and the residual chemical is neutralized. |
300 or more
|
yes |
(T8) |
Filter + CO2 |
After filtrating plankton sized 50 m? or larger, remaining microbes are
killed using chlorine dioxide. |
16,000 |
yes |
(T9) |
Filter + Hypochlorite |
After filtrating plankton sized 50 m? or larger, microbes are destroyed
using sodium hypochlorite. The residual chemical is then neutralized. |
625 |
yes |
An
evaluation methodology for out?tting BWMS equipment by applying a
multi-criteria analysis method can be constructed and used to select the most
appropriate system among the available methods. Each method has several
con?icting aspects regarding function and cost. By applying the value
engineering concept, these aspects were evaluated with respect to the bene?ts
of function items and the detriments of cost items. The results of the
evaluation show the degrees of appropriateness of a particular method. Because
the evaluation results from two perspectives, i.e., those of the ship designer
and the ship owner, were di?erent, both parties must compromise about which
system to install on board an ordered vessel.
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