Risk Assessment of Fishing Trawl Activities to Subsea Pipelines of Sabah and Labuan Waters

Introduction. Trawling is a method of catching fish in a large volume where fish nets are pulled through water using one or two boats. Bottom trawling is where the nets are pulled over on the seabed. The gear of the bottom trawling would impact the exposed subsea pipeline, on the seabed. Subsea pipelines transport crude oil and gas from the offshore platform to shore facility. This study assesses the risk of fish trawling activities to the subsea pipelines at Sabah and Labuan offshore. The specification of trawl equipment used by local trawlers in Sabah was determined by the on-site survey. The frequency of a fish trawler crossing over the pipelines was calculated based interview on operation and site survey. The calculation of the pull-over load of the otter board was calculated using the DNVGL algorithm. The severity and frequency index of the risk matrix was developed based on literature review. Results showed that the pull-over load of the otter board would not damage the pipelines. The risk posed by the fish trawler activity to the pipelines is low and moderate.


Introduction
Sabah is known for its fresh sea catches. Seas of Sulu, Sulawesi, and South China, which surround Sabah, contribute to 41.8% in marine fish catches in Malaysia. Sabah fisheries and aquaculture industries produce nearly 200,000 metric tons of fish annually and contribute to Sabah's annual Gross Domestic Product by 2.8%. e marine capture fishery is the major contributor, which accounts for about 80% of the statistics.
is is a catalyst by various fishing gear methods used by the fisherman in Sabah. e main fishing method that contributes to the total catches is the trawl net. Trawling is a method of fishing where fish nets are pulled through water using one or two boats. Trawl can be split into bottom trawling and midwater trawling [1]. Apart from fisheries and aquaculture industries, Sabah has an oil and gas industries with a reservoir that consist of West Sabah Basin, Northwest Sabah Basin, and Northeast Sabah deep-water area. Most oil and gas come from the West Basin, namely, Erb West, Tembungo, and Kababangan oil fields as shown in Figure 1.
However, the existing subsea pipelines connecting oil field to shore are affected by fishing activities especially the bottom-trawling. e interaction may cause damage to the subsea pipelines, which eventually leak and cause marine pollution.
is interaction is considered as a third-party impact due to the human activity at sea. e third-party impact is the impact caused by external activities such as trawling, anchoring, and dropped objects [3].
A number of studies have been conducted on the interaction between trawl gear and subsea pipelines [4][5][6][7][8]. DNV had introduced the algorithm to calculate the pull-over load and hooking of trawl gear on the subsea pipelines [9]. e behaviour of X65 pipeline during impact has been studied by Kristoffersen et al. [10]. Longva et al. [11] had conducted a load test of fishing gear on subsea pipelines. e study had identified the friction of board pipe, the tension of wire between the board and trawl net, the towing line drag properties, and the direction of over-trawling that profoundly influenced the impact's load. Wu et al. [12] had proposed a new approach to quantify the probability of the trawl board hooking by using simulation tools and statistical data. DNV had updated their recommended practice on interference between trawl gear and pipelines in 2017 [9].
Hitherto, no study has been conducted on the fish trawlers activities to subsea pipelines, particularly at Sabah offshore. erefore, the objective of this research is to determine the impact of the pull-over load of trawlers to the subsea pipelines from Sabah and Labuan offshore to shore gas and crude terminal, respectively.

Methods
In this research, several methods were used to achieve the main objective. e overall research activities are shown in Figure 2. e explanation of each process is given in the following paragraphs. e first step of the research is to obtain information on oil and gas pipelines from offshore fields to shore facilities at Sabah and Labuan. e data were obtained from the relevant MAL chart series, produced by the Malaysia National Hydrographic Centre. e electronic navigation chart series are available from C-Map and Navionics. e pipelines data were also obtained from the oil and gas company that owns the pipelines. e second step is to determine the frequency of crossing by trawlers on the pipelines. According to the Sabah Fisheries Department, less than 30% of fishing vessels in Sabah is fitted with the Automatic Identification System (AIS). us, the AIS data for trawlers were not available. To determine the number of crossings on pipelines, an alternative way was developed. e first method of the second step was to determine the typical operation of trawlers in Sabah. e information was gathered by conducting a survey on the three operator fish trawlers at Kota Kinabalu fish jetty. e information was the location of fishing ground, speed and duration to the fishing ground, trawling speed and duration, the number of trawling per day, duration of fishing, speed and duration to return to fish landing jetty, duration of transfer cargo to jetty, and replenishment before going back to fishing. e second method of the second step is to do a site verification survey by boating along the route of the pipelines. e course, speed, name, and type of fishing vessels detected on-site were recorded. e third method of the second step is to determine the density of fishing trawler per area of fishing ground. is step was started by identifying fishing grounds in Sabah waters. e area for each fishing ground was marked and measured by using the Google Earth application. e third step was to identify the specification of the trawl gear and otter board used by trawlers. e site survey was conducted to fishing trawlers at the Kota Kinabalu fishing port and shipyard at Sepanggar Bay. During the survey, the dimension of the otter board was measured, and the thickness of the warp line was measured. e fourth step was to calculate the force of the pull-over load by using equations (1)-(4) developed by DNV [9]. e pull-over load is the horizontal and vertical forces from the trawl boards acting towards the subsea pipeline. It shall be applied as single point load to the pipeline under consideration [13]. e equation for the pull-over load of an otter board or trawl door is given below [9]:  2 e Scientific World Journal where F P is the pull-over load of an otter board/trawl door, k w is the warp line stiffness, V is the trawling velocity, m t is the steel mass of board/beam with shoes, and C F is an empirical coefficient. C F is determined by where H is a dimensionless height and is determined by where H sp is the span height (negatively for the partly buried trenched pipeline). OD is the pipeline outer diameter including coating . B is half of the trawl board height. e warp stiffness, k w , is assumed as where L W is the length of warp line in meter. e fifth step was to conduct the risk analysis, which consists of the frequency index, severity index, and risk matrix.
e frequency index and severity index will be developed based on DNV GL and ISO publications. e frequency index developed in this study is shown in Table 1. e table is a 9-point scale ranging from 0 to 8,100 frequencies with an increment of 900 between categories. e table is developed based on the DNV GL report on recommended failure rates for pipelines by adapting table criteria for score assessment, threats related to shipping loss, emergency anchoring, and dragged anchors from anchored ships [14]. e table has 3 scores as follows: 0, 1, and 2 for the number of crossing less than 90,000, between 90,000 and 180,000, and above 180,000, respectively. e adaptation was by taking 1% of the scores of each category from the DNV GL table and developed the ratings in 9 scales. is adaptation would increase the impact probability to 100 per cent, which is due to the impact of trawl gear on the pipeline on each crossing. e severity index in Table 2 was developed based on research conducted by Kristoffersen et al. [10]. However, no results of the calculated force are shown in the table in this section. e test conducted in the research is in accordance with DNV-RP-F111: interference between trawl gear and pipelines [9]. Results from the research were used to determine the magnitude of the force that resulted in the extent of damage to the pipeline, which also subjects to the thickness of the pipeline. A pipeline's load resistance against external interference primarily depends on the pipeline diameter and wall thickness. Tests have shown that the most commonly used excavators and construction equipment do not exercise enough load to cause leaks or rupture to pipelines with a wall thickness larger than 11-12 mm [14]. e index number and meaning of the index of severity in Table 2 is developed based on ISO 17776 Risk Matrix with index number starting from 0 to 4 [15]. Table 3 is the Risk Matrix Table for fishing activities on pipeline, which is used to determine the result of the risk index. Table 3 combined the severity index and frequency index in one table and was used to calculate the summation between the frequency and severity index for a particular pipeline.
e result of the summation and the corresponding level of risk are shown in Table 4. ere are five levels of risk matrix shown in Table 4 from very low to very high risk.

Results and Discussion
ere were four pipelines that were identified in the study. Pipelines ID85 and ID80 cross from Erb West oil field to Sabah Gas Terminal Kota Kinabalu (SBGAST) and to Labuan Gas Terminal (LGAST), respectively (Table 5). Pipelines ID107 and 144A from Semarang oil field to LGAST are shown in Figures 3 and 4.

3.1.
e Density of Fishing Trawler in Sabah Waters. According to Kristoffersen et al. [10], there are four main fishing grounds of Sabah, as shown in Figure 5. Fishing ground A is located between Erb West oil field and Kota Kinabalu mainland. Fishing ground B is located at Teluk Kimanis. Fishing ground C is located between Mantani Island and the mainland, and fishing ground D is located between Semarang oil field and Labuan mainland. e area of fishing ground A is 488 nm 2 . Results of site survey at ground A show that twelve trawlers were found, as shown in Figure 6 (the positions depicted by camera icon). e density of fishing trawlers in an area was obtained by dividing the area measured with the number of fishing trawlers found; thus, the density of fishing trawler in area A is 40.7 nm 2 per trawl. Fishing ground A is used as the benchmark for density of trawler because it has the highest number of fishing trawlers registered at its coast (Kota  Kinabalu) compared to other fishing ground, and it is also the biggest fishing ground in Sabah. By using the result from ground A, the density of trawler for fishing ground B, C, and D is calculated. e area for ground B, C, and D is 157 nm 2 , 213 nm 2 , and 156 nm 2 , respectively. e density of trawler for ground B, C, and D is 4, 5, and 4, respectively.

Typical Operation of Fishing Trawlers in Sabah Waters and Frequency of
Crossing. An interview with three skippers of fishing trawler had identified the typical operation of the fishing trawlers in Sabah waters. e information of the operation is applied to fishing ground A, an area between Erb West oil field and the coast of Kota Kinabalu to Karambunai Sabah (Figure 4). e result for fishing ground A is as follows: (i) e duration of one cycle of fishing trawl operation is 10 days, which consists of 0.5 days going to a fishing ground, 7 days of trawling, 0.5 days to return to fish landing jetty, and 2 days for discharge cargo and replenishment.
(ii) e trawling operation is conducted 5 times per day, where the duration for each trawling operation is 4 hours, namely 1 hour to deploy and retrieve net, and 3 hours to tow net. (iii) e trawl distance per day is 45 nm, which resulted from 5 times trawl per day, multiply 3 hours duration per trawl, and multiply speed 3 knots. (iv) e distance of the fishing area is 28 nm, which is measured from pipeline Erb West-Labuan Gas Terminal to pipeline Erb West-Sabah Gas Terminal in Figure 2. For a trawler that makes a U-turn after 28 nm trawling to make a new trawl leg, with a trawling distance of 45 nm, a vessel would cross 1 pipeline twice and 1 pipeline once. However, by taking into consideration the slight increase of speed, lesser time in deployment, and retrieval of trawl gear, it is assumed that a trawler may cross these two pipelines 2 times per day.      e frequency index table for the number of crossing on a pipeline by trawlers in a year is developed based on the assumed frequency of trawlers passing on the pipelines. is frequency is developed based on the assumption of the vessel speed, route taken, distance travelled, and commonly practiced by the fishermen. e frequency developed had to be developed based on the assumption because accurate information leading to the frequency was not available.

Specification of Trawl Gear.
e type of trawl gear used in Sabah is the typical otter trawl gear, which is using the polyvalent or rectangular board.
is type of trawl gear consists of a pair of otter boards, warp line, and net. ere are two types of otter board used by trawlers in Sabah, namely the steel otter board and the steel-reinforced wooden otter board as shown in Figure 8.  Table 6. e category of fish trawlers that are using these otter boards must have sufficient power to tow the heavy fishing gear at 3 knots. erefore, the engine horsepower is 350 HP and above. e majority of engine used in the fishing trawlers have horsepower between 350 hp to 500 hp. e diameter of the warp line used is 2.5 cm.

Calculation of the Pull-Over Load.
e calculation of the pull-over load was done using equations (1)- (4). e inputs to the equations are trawl depth of 60 meters (Figure 2), trawling speed of 3 knots (1.54 m/s), 300 kg steel vee door specification (Tables 6 and 7), and span height on the seabed. All the pipelines are buried. However, by taking into consideration that the pipelines sit on the seabed, the span height is zero [16].
Based on the calculation, the result of the pull-over load of a trawl board on Erb West to Labuan Gas Terminal is 24.01 kN and on Erb West to Sabah Gas Terminal is 25.98 kN (Table 8).
ese results were compared with the yield strength of the pipelines in Table 7. ese results show that the trawl board's pull-over load on Erb West to Labuan Gas Terminal and Erb West to Sabah Gas Terminal pipelines is far lower than the yield strength of both pipelines. e percentage of the pull-over load over yield strength of Erb West to Labuan Gas Terminal and Erb West to Sabah Gas Terminal pipelines are 7.8% and 4.5%, respectively. erefore, the force of the pull-over load of the trawl boards would not give a significant impact to damage the pipelines. However, due to age factor and corrosion, the yield strength of the pipelines should be lower than new condition [14].

Calculation of the Frequency Index, Severity Index, and
Risk Matrix for Fishing Activities. Both severity index for pipeline Erb West to the Labuan Gas Terminal and Erb West to the Sabah Gas Terminal is zero because the impact force from the otter board resulted in no damage to the pipelines. e risk matrix results for both pipelines depend on the frequency of crossing as shown in Table 9.
Based on the observation of fishing trawl operating in Sabah (Area A) and Labuan (Area D), the fish trawl skippers are aware that they were operating within the area with offshore pipelines but do not know the exact location of the pipelines. e reason that they fish in the area is that the yield from the catch was good, and the seabed is flat and suitable for trawl operation. According to Rouse et al. [17], snagging may damage fishing gear, disrupt the fishing operation, and may cause injuries to crew. However, no fish trawlers in the study area (Sabah and Labuan) had snagged their fishing gear with the pipelines. is may be due to the pipelines e Scientific World Journal buried in the muddy seabed. erefore, the fishermen did not consider the pipelines as a snagging hazard.

Conclusion
e trawling method used in Sabah waters is the bottom otter trawl. is type of trawling would cause contact between the trawl boards with subsea pipelines. Based on the specification of the trawl board and the subsea pipeline of the study area, the impact force of the trawl board's pull-over load is lower that the force would cause slight damage to the pipelines. e interaction between the otter boards and subsea pipelines in West Sabah area and Labuan waters would not damage the subsea pipelines. However, the frequency of the crossing in Labuan and Sabah (Kota Kinabalu) waters are moderate and high, respectively. Based on the severity index and frequency index, the risk of fishing activities Labuan and Sabah (Kota Kinabalu) waters are low risk and moderate risk, respectively.

Data Availability
e data used to support the findings of this study are available from the corresponding author upon request.