Environmental Implications of Recreational Boating a Study of Kosterhavets Marine National Park

Environmental Implications of

Recreational Boating

A study of Kosterhavets Marine National Park

Joseph Santhi Pechsiri

Master of Science Thesis Stockholm 2009

Environmental Implications of Recreational Boating A study of Kosterhavets Marine National Park

By Joseph Santhi Pechsiri Advisor: Fedrik Grondahl

Master’s Thesis M.Sc. Sustainable Technology Department of Industrial Ecology Kungliga Tekniska Högskolan 2009

TRITA-IM 2009:16 ISSN 1402-7615

Industrial Ecology, Royal Institute of Technology www.ima.kth.se Abstract

Koster archipelago is high in diversity; Koster has atleast 200 unique species, and also contains various elements attracting a lot of tourists. Koster archipelago resembles various factors that are highly suitable for recreational boating. However, this may become a massive environmental threat. This study investigates the environmental implications of recreational boating and the factors facilitating the impacts by conducting a systems analysis of recreational boating. The investigation has led to the identification of releases of NOx, COx, HCs, and TBT, among other pollutants. In addition, the investigation have estimated the possible total emissions amounts of boats in Koster, with approximately 850 000 kg CO2, 2500 kg NOx, 256 kg sewage Nitrogen, 32 kg sewage Phosphorous, 126.6 kg, and a minimum of 3.2 kg of TBT released per year. Table of Contents

1.0 Introduction 1

1.1 Location of Study 1 1.2 Prologue 1 1.3 Aims, Objectives, Scopes, and Boundaries 2

2.0 Literature Review 4

3.0 Methodology 20

3.1 Framework overview 20 3.2 Emission Estimation Methodology 28

4.0 Result 35

4.1 Process Inventories Identification Result 35 4.2 Impact Assessment of Recreational Boating Result 36 4.2.5 Emission Estimates Summary 52

5.0 Discussion 54

6.0 Conclusion 63

7.0 Acknowledgement 64

8.0 Reference 65

Appendix A Boats and Ships Registered with the Swedish Transport Agency 68

Appendix B Filtered Data Collected on Registered Boats and Engine Specs 204

Appendix C Fuel Estimation for 805 Boats using Regression and Means 225

Appendix D Questionnaire 245

1.0 Introduction

1.1 Location of Study

Koster islands are located to the west coast of Sweden in the vicinity of the Norther Skaggerak Sea. The archipelago consists mainly of 2 islands: the main island Sydkoster (South Koster) and the natural reserved Nordkoster (North Koster). The koster islands will become a marine national park by mid 2009, which include approximately 450 km2 of area, excluding some islands, and would be bordering the to be proposed Ytre Hvaler marine national park over the Norwegian border (Hambrey J., 2008). Kosterhavets Marine National Park Fig. 1. Map over Koster provided by map is shown to the right with the red line representing personals at Tjarno marine biology the border of the marine national park. laboratory, Goteborg University.

The Kosterhavets Marine National Park covers a variety of terrain. Fjords, terrestrial and marine based ecosystem are within the boundaries of the marine national park with 80% of its area are under water. The park has atleast 200 species of plants and animals that are unique to Koster. There are species of Porifera, Cnidaria, Annelida, Echiura, Arthropoda, Mollusca, Brachiopoda, Bryozoa, Echinodermata, and Chordata, among others (Jonsson L.G. et al, 2004). The underwater profile of Koster vary between several meters deep in the inter-tidal zone up to more than 200 meters deep in the trenches, which also serves as the main shipping route from the South to the North, cutting through the Kosterhavets Marine National Park area, as shown on the dotted line in figure 1 (Bohuslän, 2009). The island itself contains several infrastructures to support the human population with some accommodation available for tourists. The island is almost 100% car free, making the island ideal for outdoor activities, which is appealing for outdoors-loving tourists, especially hikers and cyclers. There is also a daily public ferry service between Koster and Strömstad.

1.2 Prologue

In the past, environmental concerns are mainly due to fishing where unsustainable fishing practices have led to a decline of corals and various marine life in the area. Today, however, Koster has become a symbol of sustainable fisheries, which have been widely practiced, partly due to the ongoing dialogue between fishermen and scientists in the region (Hambrey J., 2008). There is also a marine biology laboratory in the area (in Tjärnö), which will also serve as a visitor center for Kosterhavets Marine National Park. Now those problems regarding fisheries are limited, tourism is the next main environmental threat to be observed.

The archipelago is almost 100% car free, the main pollutant emitters are from households, marine vessels, touristic accommodations and service centers. Since the area is underwater by more than 80% of its total area, the area is highly suitable for boating, especially during

summers (which is the main boating season) when the weather is not too cold and the water is not frozen.

The human population within the area is 24000, with 1000 people living adjacent to the water. There are many summer houses in the area as well. The main vehicles used on the island are bicycles and boats. By Koster being a marine national park, with Norther Koster being a natural reserve and the area covering various types of prestine terrains, in combination with the fact that more than 80% of Kosterhavets Marine National Park’s area is underwater, Koster becomes a perfect boating destination during the summers. Furthermore, the existence of a shipping route and the fact that Koster is very close to Strömstad (a major boating destination) gives Koster the perfect condition to have heavy boat traffic.

There have been very limited studies on the problems of recreational boating. Recreational boating has been seen by many as a not-so-environmental damaging activity, which is made more prominent by the lack of researches found and the need for this study to be conducted using several internet-based sources . Researches done by Liddle M.J. and Scorgie H.R.A. (1980) suggest recreational boating as the main environmental impact contributor of all water based activities towards the biota as a whole. Baden S. et al (2003) suggested causes of the rapid decline of Seagrass in the West coast of Sweden, notably the Skaggerak Sea area, to include recreational boating. Davenport J. and Davenport J.L. (2006) also highlighted the significance of boating when tourists come in mass. Pechsiri J.S. (2006) also emphasizes boating related activities’ impacts on coastal environments. From these findings, it was concluded that the main aim of this project is to investigate the environmental implications of recreational boating, to provide enough information for decision makers to take into consideration of environmental problems of recreational boating when creating policies.

In this study, there are 8 main chapters. The aims and objectives will be discussed in the next in this chapter. Chapter 2 will discuss the framework required to comprehend the environmental implications of recreational boating through making past literature reviews, and observe past works that have studied the environmental impacts of recreational boating. Chapter 3 will demonstrate the main conceptual methodology and framework used in this study. Chapter 4 will show the results of literature searches, data collection, and on site observations to demonstrate the environmental implications of recreational boating. Chapter 5 will discuss the uncertainties and problems that occur in this study and how they can be improved in future studies. The project will finally conclude itself in chapter 6. The acknowledgement, showing the people who have contributed in providing information and expertise for the completion of the project, will be shown in chapter 7. The references can be found in Chapter 8, which is followed by 3 more appendixes that contain necessary information vital to calculations required in this study.

1.3 Aims, Objectives, Scopes, and Boundaries

The ultimate aim of this project is to semi quantitatively investigate the environmental implications of recreational boating. The impacts will not only observe the direct impacts of

recreational boating but identify the causes, the factors that facilitate the impacts which are important for predicting the distribution, the magnitude, and the secondary impacts. In order to fulfill the ultimate aim, several objectives are to be fulfilled. The objectives are as follows:

• To inventory the causes, processes, of impacts that occur due to recreational boat.

• To investigate various emissions or environmental impacts semi quantitatively. If quantitative data becomes unfeasible, then qualitative investigation will be applied.

• It is well established that a lot of boats used internal combustion engines to operate. This often leads the production of NOx, which has many environmental problems. Hence environmental related problems of NOx should be investigated and the quantification of NOx must be achieved, atleast semi quantitatively.

• If there are any uncertainties within the emissions, i.e. differences in emission factors used by various institutions, and if possible then the reason behind the differences should be investigated. This is to promote a clearer perspective of the environmental implications of recreational boating.

• Any emissions are found should be further investigated to understand the environmental implications of that particular emission and how various factors may facilitate the impacts to create other environmental impacts at greater scale.

• Causes of emissions should be thoroughly studied as the factors that lead to the release of emissions govern the amount and contributes in facilitating the impacts in to the environment. By understanding the causes, the mitigation measures may be suggested.

• Since the Baltic Sea is known for its Eutrophication problem and that the Skaggerak Sea connects the flow of water between the Baltic and the North Sea, any factors leading to the loading of nutrients should be investigated and if possible calculated.

• Lastly, because the project is only allowed for a period of 6 months, starting from January until June and this project needs to be submitted within the timeframe as a fulfillment of the Masters program, the project is to be completed by that time.

There are several scopes, boundaries, and assumptions applied in this study. First of all, the study mainly, and will only focus on the Kosterhavets Marine national Park. This means that the study will mainly consider factors within the geographical region (+ - 250 meters) of the national park. The boating season is usually observed to be during the summer season. In this research it is assumed that the boating season lasts 100 days (approximately 3 months of June, July, and August, and a little bit into May and September). Since the boating speed is very hard to be determined, after looking at many boating sales websites, it is assumed that the average speed of boats would be 10 knots, or 18.5 km/h, which is obtainable by most boats. Another assumption made is that each boats traveled will contain 1 person. Although usually there are more than 1 person that conduct boating but the boats often are able to be operated by 1 person. Other assumptions made will be mentioned later in the report. 3

2.0 Literature Review

There have been previous researches conducted to understand impacts of recreational boating. However, most of previous works are more focused on interactions of boating on a targeted organism or problem rather than exploring the problems of recreational boating as a whole, which is the aim of this work. In order to achieve the understanding of the environmental implications of boating, previous research frameworks and previous investigated environmental problems of recreational boating are reviewed. Furthermore, various possible frameworks to be applied to this investigation are also reviewed.

2.1 Associated Environmental Problems

A study by Pechsiri J. (2006) in Thailand suggests a variety of recreational activities involving boats, including snorkeling, diving, sea walking, and sightseeing, where only 25% of the tourist believed that coral degradation in the area was influenced by human activities whereas 17% believed the degradation was influenced by heat. In addition boats investigated was seen to be the causes of some emissions and a direct contributor to environmental degradation where the report revealed sightings of people physically harming corals in many ways that involve direct contact. Although whether natural influence or anthropogenic influence is the main contributor to coral degradation was not proven but the study suggests anthropogenic influence to remain a significant contributor. Davenport J. and Davenport J. (2006) revealed that environmental damage due to divers are the result of spear guns usage, collection of benthic organisms like crabs and lobsters, feeding large fish, physical contact of corals, and suffocating sever benthic organisms (i.e. corals) by causing benthic sediment resuspension which mainly compose of silt. Liddle M.J. and Scorgie H.R.A. (1980) reviewed several previous studies that have proven disturbances to the environment due to water-based activities, where it is revealed that direct disturbance (i.e. noise and human use of abiotic elements of the ecosystem that is being used as refuge by animals) may be as important as indirect disturbances (i.e. how reduction of primary productivity would impact the whole foodchain). Although some previous studies involving the use of experimental ponds suggest fish production is not affected by the use of outboard motors but emigration, resdistribution, and reproduction failures have been found to result from various environmental disturbances including boating and sounds generated during the boating process. Bellefleur D. et al (2009) revealed disturbances to Marbled Murrelets due to boat traffic where more than 41% of the birds observed react to an incoming boats (11.7% flew and 30.8% dove) with the number of reacted birds increasing inversely with boat-bird distance and that more than 82% of the birds that flew left the feeding area. A study by Buerger R. et al (2000) records the number of impact sites that have been anthropogenically influenced and naturally mitigated. It was noted however that the natural processes which mitigates the impact did not necessary reverse the impacts such that the environmental conditions would return to the previous state but may have altered the impacted environment to a set of new conditions. In addition, the investigation shows the rapidness of the environmental change where 29.3% of the impact areas documented on Masonboro Island was mitigated naturally in 6 months.

Sediment resuspension and mixing due to propeller action and boat cruising are one of the impacts due to boating. Liddle M.J. and Scorgie H.R.A. (1980) suggested that when propeller action exists near the bottom of a water body, dispersion of sediments occur. Yousef et al (1980) observed how the levels of phosphorous in lakes with limited boat use may be affected by mixing from motor boats. Limited change in dissolved oxygen was recorded as the result of mixing from motorboats but significant differences in chlorophyll a concentrations, phosphorus amounts and turbidity levels were observed. An experiment was undertaken where water samples collected after 2 – 6 hours of mixing by motors showed a 39% increase in total phosphorous (29% increase of total phosphorous under control conditions) and 46 mg/m2 of orthophosphorous resuspended for a 2.55 m. deep lake with low surface area pertaining to oligotrophic and mesotrophic profiles. Meanwhile, results of a 1.5 m. deep lake with larger surface area and pertaining to hypereutrophic profiles showed an increase of total phosphorous by 55% after mixing (which is a 5% increase of total phosphorous under control conditions) and 105 mg/m2 of orthophosphorous resuspension was observed. Apart from sediment resuspension, there are also other problems related to nutrients. Boating activities, such as littering and sewage deposition, have been found to lead to deposition of nutrients and organic compounds. This can become problematic in several senses. According to Boeker E. and Grondelle R.V. (2001), organic substances like carbohydrates would allow bacteria to oxidize these carbon compounds as demonstrated in the following reaction.

Nitrogen is arguably the most important element for plant and microorganism growth. Hence a direct release of ammonia forms of nitrogen, nitrate, or even nitrogen itself would enhance the nitrification and nitrate assimilation (VanLoon G.W. and Duffy S.J., 2005). The release of nitrogen and phosphorous lead to increases in nutrient loading amounts. If this trend continues, problems like eutrophication, algae bloom, and regime shifts may arise. (Hakanson L. and Blenckner T., 2008).

Boating in shallow waters, berthing/anchoring, launching, and beaching can also become environmental problems. Anchoring and boating activities have the capacity to degrade coastal environments as portrayed by Pechsiri J.S. (2006), where corals are often damaged by anchoring activities. Liddle M.J. and Scorgie H.R.A. (1980) suggested that flora and fauna of the littoral zone will be affected from the abrasions that are caused by berthing, launching, and beaching. Propeller action can also cut through macrophytes, whereas the forces exerted from the propeller can cause uprooting of macrophytes.

Another direct physical impact suggested is also from boat wake, also called boat wash. According to Liddle M.J. and Scorgie H.R.A. (1980), the cause of waves is due to the power required to move the boat being dissipated on to the adjacent water body. The waves can lead to erosion to abiotic elements in the coastal ecosystem, i.e. cliffs and rocks. These waves can also cause uprooting of macrophytes. The amount of power that is transferred on to the water body depends on many factors, i.e. boat design, engine design and capacity, boat load, among others. If the boat is cruising in the same direction as the water current and that the boat is a transom stern design, large transverse waves maybe generated. The height of the waves and

5 the energy contained in it is governed by speed, boat design, environmental conditions, and engine design. How these waves affect the shoreline and the sediments remains a complex issue. This complexity was explored by Bishop M.J. (2007) where benthic organism- sediment relationship has been found to be more complex than originally explored, of which it was originally believed that the benthic fauna and flora are affected by the resuspension of fine sediments. The study revealed that the taxonomy assemblage between a wash and no wash zone remained similar with changes in the taxonomy assemblages dynamically changing accordingly with environmental conditions. However Bishop M.J. (2008) suggested that the composition of epifauna changes significantly after boat wake exposure on sea grass. “Five- fold” decrease of the number of amphipods and polychaetes, and other significant decline of invertebrates’ taxa were recorded.

Antifouling processes have been applied to marine transport since ancient history to prevent submerged materials, i.e. boat hulls and fishing gear, from the settlement of organisms. Fouling of organisms began with the process of bacterial driven micro-fouling, and followed by macro-fouling of invertebrates. During the sailing periods, including periods like the 1700s and 1800s, ships were copper or lead bottomed for anti fouling purposes (Melander C. et al, 2009). The modern common practice for antifouling is to use an organo-tin biocide compound known as Tributyl Tin (TBT), which became popular since the 1960s. TBT has been found to leach in to the adjacent water bodies and has been found to be toxic to benthic invertebrates at concentrations between 0.1 to 100 µg/l and effect gastropods’ reproduction at concentrations greater than 0.001 µg/l (Lalli C.M. and Parsons T.R., 2004). Meanwhile, Copper, which is still being used on some vessels in the modern days, is both a necessity as a nutrient and toxic at excessive concentrations (VanLoon G.W. and Duffy S.J., 2005).

Estimating emissions from copper and TBT is difficult, especially when Cu and TBT are prohibited from use for recreational boating in most parts of Sweden. Leon L.M. and Warnken J. (2008) estimated the Cu leaching rate to be 8.2 µg/cm2 of submerged antifouled area per day. Eklund B. et al (2008) have experimented on sediment and water samples in Stockholm marinas to determine levels of heavy metals and TBT. Despite the fact that TBT , Cu or Irgarol containing paints are prohibited from use, it was believed that they are being painted over by non TBT containing paint, since sediments sampled found top layers containing concentrations of TBT.

The nature of which these contaminants have on the environment is still an ongoing study due to its complexity. Apart from its toxicity mentioned earlier, Davenport J. and Davenport J.L. (2006) have mentioned a secondary impact that these contaminants may cause. TBT, for example, may have cause a lot of harm to the local biota population, which is the main competitor and pressure for invasive species. The decrease of the local biota population would increase the likelihood for a successful bioinvasion.

Impacts from engines have also been reported. According to Heywood J.B. (1988), internal combustion engines are the main source of noise. Every sequence of the operating cycle of a reciprocating engine emits a certain amount of noise which is generated by aerodynamics, combustion, and mechanical excitations due to combustion. There are several ways to

6 classify various types of engines for recreational boats. The main types that are observable are outboard engines and inboard engines. However, as evident in Appendix A, some engines used in Sweden are stern drives, shaft drives, sail drives, among others. In this research, these are considered inboards since the majority of these types of engines have its main engine inboard with its propeller shaft outboard. The combustion within these engines depends on various factors, i.e. fuel type and temperature. Combustion is achieved through the transformation of fuel into CO2 and H2O. Under ideal stoichiometric combustion portrayed by Guzzella L. and Onder C.H. (2004), the combustion process is achieved by the following reaction:

or as explicitly demonstrated by Guzzella L. and Onder C.H. (2004) as:

where under the assumption that the air is normally composed of 79% of N2 and 21% O2 Guzzella L. and Onder C.H. (2004) states that:

, where y = a/b

From Heywood J.B. (1988)’s Gasoline and light Diesel formula, which is CnH1.87n and CnH1.8n respectively, it is possible to estimate that the amount of air needed for stoichiometric Gasoline combustion is 14.5 kg and 14.4 kg for light Diesel.

In order to achieve the ideal combustion process, maximum combustion efficiency is required. The combustion efficiency is governed by controlling 3 Ts: Time, Turbulence, and Temperature, where sometimes the amount of input Oxygen is also controlled (Persson P.O., 2005). The 3 Ts mentioned differ accordingly with each engine’s designs. However, since simplicity, high power to weight ratio and high ruggedness are favored for recreational boats’ engines, often the suitable conditions for an ideal combustion process is not achieved, hence resulting in incomplete combustions that lead to emissions of various pollutants, including unburnt hydrocarbons (HCs) and NOx. These NOx can also result in the generation of low altitude ozone (VanLoon G.W. and Duffy S.J., 2005). The following reactions show the principal reactions of nitrogen oxides formulation:

It is discussed in Heywood J.B. (1988) that the ratio of NO : NO2 is “negligibly small” for spark-ignition engines, whereas NOx for diesel engines can be as high as 30%. NO2 is said to have formed from NO in the flame zone, following the reaction shown below:

This NO2 can be converted back to NO as follows:

Apart from the mentioned reaction of NOx formation, there are other factors that contribute to the type of Nitrogen compounds formulated in the exhaust. A study by Kowalski J. and Torelko W. (2009) on NOx emissions modeling for 2 stroke engines revealed the involvement of N2O as well. In addition, it is noted that temperature and pressure are the 2 most important parameters that influence the final Nitrogen oxides concentrations. Hence, in reality the following summarizes the reaction achieved through combustion in an internal combustion engine:

In order to understand the general processes of how these emissions are formulated, it is necessary to explore the processes of the engines, how these processes contribute to generating emissions, and what factors should be considered.

Internal combustion engines work in operating cycles (also called strokes). In general, there are 4 operating sequences, the intake stroke, the compression stroke, the power stroke, and the exhaust stroke. A 4 stroke engine would undergo all 4 sequences and requiring 2 crankshaft revolutions to complete a cycle. A 2 stroke engine, under simpler designs, would complete all 4 sequences in 1 crankshaft revolution and hence offer more power when the engine size is relatively similar.

In the intake stroke, the piston travels downwards and the inlet valve opens, drawing in fresh air. The inlet valve then closes and enters the compression stroke. In the compressions stroke, the piston travels up and compresses the air. The combustion then takes place at the end of the compression stroke. The method of combustion depends on if the engine is spark- ignited or compression-ignited. As the crank angle reaches the top dead center and combustion takes place, the power stroke (also known as the expansion stroke) is then initiated. During the power stroke, the combustion process increases the pressure and temperature within the cylinder and pushes the piston downwards. As the crank angle reaches the bottom dead center, the exhaust stroke begins. In the exhaust stroke, the exhaust valve opens and the piston travels upwards until the crank angle reaches the top dead center, expelling the burnt gases. As the crank angle reaches the top dead center, the valve closes and begins the cycle over again (Heywood J.B., 1988).

Inlet Exhaust Inlet Exhaust Inlet Exhaust Inlet Exhaust Valve Valve Valve Valve Valve Valve Valve Valve

Piston Piston Piston Piston

Cran Cran Cran Cran k k k k

Intake Compression Power Exhaust Fig 2. 4 sequences of 1operating cycle

The 2 stroke engine follows a similar set of sequences in 1 operating cycle, but the nature of completion and initiation of each sequence differs due to the simpler design of 2 stroke engines. The operating cycle for a 2 stroke engines can be divided in to 2 sequences: the compression stroke and the power stroke, where the intake and exhaust of air are processed in parallel. In the compression stroke, the inlet port is closed while the exhaust port is also closed by the position of the piston which is moving upwards, compressing the air. Combustion is initiated when the crank angle reaches the top dead center. The Start of the combustion begins the power stroke. The explosion pushes the piston downwards. As the piston move downwards and the crank angle is going towards the bottom dead center, it first uncovers the exhaust port. The exhaust gases leave the cylinder by the process called the “exhaust blowdown” process. As the crank angle approaches the bottom dead center further, it uncovers the inlet port which takes in new air. The cycle then repeats again (Heywood J.B., 1988).

Piston Piston Piston

Power Compression

Fig 3. Operating cycle of a 2 stroke engine 9

From these illustrations, it can be concluded that the 3 Ts are controlled differently under a 2 stroke and a 4 stroke design. Guzella L. and Onder C.H. (2004) have demonstrated in the investigation on spark-ignited engines that an early ignition timing within the cycle would result in better combustion efficiency but would also result in greater NOx output due to increase in peak pressure and burnt gas temperatures. The 4 stroke design would definitely increase the amount of time for combustion, but may lead to thermal NOx generation. The 2 stroke design however has less time for the combustion to take place efficiently, increasing the risk of incomplete combustion which results in higher CO and HC emissions. In addition to the efficiency differences as the result of the stroke design, other design factors to allow the engine to run smoothly also affect the amount of emissions produced. Liddle M.J. and Scorgie H.R.A. (1980) pointed out that a special crankcase design is required for a 2 stroke engine to avoid a condition known as “hydraulic lock” and this crank case design have led to losses of fuel. Figures for fuel loss varies from 10% – 20% up to 56%. Davenport J. and Davenport J. (2006) suggested 30% loss from 2 stroke engines used in personal watercraft vehicles. An interview with a mechanic however suggested that these crank casing has already been redesigned to prevent such losses but are only applied for new engines. A 2 stroke engine has a combustion process with a lower temperature profile, which also contributes to lower NOx and higher HCs (VanLoon G.W. and Duffy S.J., 2005). Another problem associated with engine design is the use of engine lubricating oil. Liddle M.J. and Scorgie H.R.A. (1980) also suggested that often the engine oil are mixed with petrol at the ratios of 1:25 up to 1:50, where these engine oil and petrol contain additives of various elements and compounds including metals, phosphorous, anti-knock agents, and scavengers. The direct contamination of fuel and oil mixture increases the toxicity of the contaminated water as portrayed by Juttner F. et al (1995b), where changing lubricants to environmental friendly lubricants has found no significant difference in terms of toxicity. Juttner F. (1995a) also found no significant differences in NOx, HCs, and CO produced as a result of changing engine lubricant oil. Furthermore, petroleum based lubricant has a higher molar mass and hence would decrease the efficiency in the combustion process (VanLoon G.W. and Duffy S.J., 2005). Other environmental problems associated with fuel are the use of additives. Methyl-Tert-Butyl Ether is an example. Brown J.S. et al (2001) observed how MTBE contaminates coastal areas. MTBE is an additive to gasoline that would reduce CO and HC emissions for combustion exhaust.

The method of which the combustion process is initiated within the engine can vary among each engine. Generally there are 2 common ignition systems for internal combustion engine: the Spark Ignition engine (SI engines) and the Compression Ignition engines (CI engines).

The spark-ignition engines have several names. It was primarily called the Otto engine, named after Nicolaus Otto’s single cylinder engine, but is also called gasoline/petrol engines due to its common use with gasoline. For the very same reason, among other previously mentioned reasons, this study will assume that spark-ignited engines (which are the main design for outboard engines) use gasoline despite the fact that they are applicable with other types of fuel.

In spark-ignition engines, the air and fuel are mixed in the Intake sequence of the operating cycle. There are several methods for air and fuel injection. The two common methods is to either use carburetors or a direct fuel injection system. The selection of the fuel and air injection system will influence the nature of the combustion process and the fuel economy per operating cycle. As calculated earlier, the air – fuel ratio should be approximately 14 – 15 to 1 for a reliable combustion. The air used maybe fresh air or air & preheated air mixture. Preheating of the Intake for fuel evaporation enhancement is often favored to increase the uniformity of fuel distribution within the cylinder. The compression sequence then follows, which would increase the pressure within the cylinder while reducing the cylinder’s volume at the same time. This sequence can also lead to a reduction of temperature for the piston, the cylinder head and walls. Just before the crank angle reaches the top center, an electronic discharge is sent to the spark plug, which initiates the combustion process. The spark discharged would lead to the creation of turbulent flames, incinerating the air and fuel mixture throughout the cylinder. As the power stroke nears completion, the exhaust valve then opens, leading to a blowdown process. Then the exhaust stroke is initiated (Heywood J.B., 1988).

Pollutant formation is governed by many factors. The air-fuel ratio influences the concentrations of various emitted pollutants. The generation of HC results from extreme lean conditions while the lack of oxygen would also increase the amount of CO produced. Misfires that occur due to extreme lean conditions can lead to the reduction of temperature within the cylinder and hence lowering the post-combustion oxidation, leading to an increase in HC. The amount of CO, however, may be reduced from misfires since failure of ignition sometime occurs during misfires. Since HC and CO formation are not limited to the combustion process but also the post-combustion processes, other factors that contribute towards post-combustion conditions within the cylinder and the exhaust manifold influence the amount of HC and CO produced (including time and temperature, among others). Other factors that would influence the HC and CO are the air/fuel injection system design and the crank angle of fuel injection. The main nitrogen oxide species emitted from SI engines is NO. NOx formation in SI engines occurs at peak temperatures. Oxygen availability, cylinder pressure, and burnt gas temperature are the main parameters that govern the output NOx amounts. Other factors that influence the NOx output are the ignition timing, the temperature of the piston and cylinder walls, among others. It is noted that almost all engine-system variables is required to determine the output NOx (Guzella L. and Onder C.H., 2004).

Compression-Ignition engines are also known as diesel engines. Unlike the SI engines, the air is injected in to the cylinder before the fuel. For marine applications, the fuel is often preheated and is injected in to the cylinder right before the combustion process (20o before the crank angle reaches the top dead center). This also allows the possibility of load control through controlling the amount of injected fuel. Usually at full load, the injected fuel will make up 5% of the total air in the cylinder. The black smoke generated during combustion often makes injection of more fuel unfavorable, since any more injected fuel will not be burnt efficiently. The air injected during intake, is compressed in the compression sequence, resulting in approximately a pressure of 4 MPa and the temperature of 527 oC. As the fuel is injected, it disperses and evaporates throughout the cylinder. As the pressure and temperature

11 reaches the fuels ignition point, auto-ignition occurs. When the power stroke initiates, the fuel, air, and burnt gases mixes and continuous combustion is achieved throughout the cylinder. This is then followed by the exhaust stroke and the cycle reinitiates itself (Heywood J.B., 1988).

One of the main causes of emissions for CI engines is due to the choice of fuel: diesel. Diesel by nature has a higher density, has a lower heating value, and gives high amounts of energy (Heywood J.B., 1988). VanLoon G.W. and Duffy S.J. (2005) described diesel as being lower- graded and higher-boiling when compared to gasoline. These factors led to lower gaseous hydrocarbon emissions. However, the main emissions would probably be found as soot. This is due to the method of fuel injection, where the air-fuel mixture is incomplete, resulting in unburnt carbon particles. In addition, inorganic sulfates emitted from diesel fueled engines are 0.1-0.3% higher than gasoline fueled engines.

Although substantial amount of soot is emitted, the amounts of HCs and CO emitted are substantially low, sometimes almost negligible. The main pollutant for diesel engines is NOx and particulate matter (being soot). The main parameter that governs these emissions is the air-fuel ratio, which in this case varies accordingly with load control. When the load is low, incomplete combustion occurs due to too low and too lean air-fuel conditions within the cylinder and causing some dispersed fuel to be left unburnt. When the load is high, combustion is more complete but there will be areas that is lacking in oxygen, leading to the formation of CO. NOx formations within diesel engines are high and are somewhat complex. This is partly due to the lack of homogeneity of the combustion process and the nature of the local air-fuel ratio. The air-fuel ratio is not uniform throughout the cylinder, leading to inhomogeneous combustion throughout. Some local air-fuel ratio, accompany with the burnt air temperature resulted from the combustion of the specific local air-fuel ratio, lead to conditions suitable for NOx formation. Although NOx formation reactions are reversible, but because the cool down phase that follows the power stroke happens so drastically that the reversing reaction becomes frozen (Guzella L. and Onder C.H., 2004).

The released pollutants may lead to many environmental consequences. Juttner F. et al (1995b) study shows water contaminated by 2 and 4 stroke gasoline engines to remain highly toxic greater than 14 days. A toxicity study by Eklund B. in Cerne o. et al (2008) report shows that a 2 stroke gasoline engine produced exhaust water which are toxic for bacteria, algae, and fish.

NO2 and NO have low health hazards, with NO essentially having no health impacts at all. The main problems lie in the photochemical smog which leads to respiratory anomalies (Boeker E. and Grondelle R.V., 2001). NOx release can lead to secondary impacts however. The nature of impact of NOx is complex and the partitioning of NOx in the environment is still an ongoing study. The combination of HCs and NOx release can lead to the generation of photochemical smog. As the name suggest photochemical smog requires sunlight radiation. The other factor required for the occurrence of photochemical smog is stable atmospheric conditions with cold air remaining in the lower atmosphere. The high density cold air which remained in the lower atmosphere does not rise, causing limiting amounts of air mixed

12 between the lower and the upper atmosphere and lead pollutants to concentrate and form a haze in the lower atmosphere (VanLoon G.W. and Duffy S.J., 2005).

The haze formed is the result of air pollutants and air particles remaining in the lower atmosphere. Photochemical smog is formed afterwards when NO produces more NO2 with the aid of HCs, Oxygen, high inputs of NO and NO2, and sunlight. There are 3 main ways which NO transforms in to NO2. The first is by reacting with O2 as follows:

The second method is through reacting with peroxyl radicals as follows:

The Third method is through reacting with O3. Ozone is also a product of reactions with NO2 and hence the presence of ozone would be continuously released when there are high concentrations of NO2. The reaction between NO and O3 is as follows:

The NOx formed from the reaction with peroxyl radicals absorbs energy from solar radiation to form O and NO as follows:

Oxygen alone is very reactive, especially when third party molecules are available. Once the

Oxygen reacted with O2, ozone is formed as follows:

where M is the third party molecule. The ozone then contributes to NO2 formation as demonstrated earlier (VanLoon G.W. and Duffy S.J., 2005). NO2 has also been found to contribute in climate change, which would be discussed later. The photochemical smog generation also requires the initiation of another actor: HCs, which is will be discussed later.

Other problems associated with NOx are eutrophication and acid rain. Eutrophication occurs through nitrogen fixation, often by lightning strikes and nitrogen fixing bacteria. Since recreational boats’ engines are water cooled, the exhaust are quenched, resulting in additional direct NOx deposition in to the water and hence would enhance the nitrification process (increase in NOx would result in increase in Nitrogen availability). The third problem with NOx is the increase in acidity in the atmosphere, which increases the likelihood for acid rain.

The main contributing reaction regarding NOx towards acid rain is the removal of NO2 after they are generated through reacting with hydroxyl radicals and forming HNO3 or nitric acid, as follows:

The formed nitric acid is then deposited to the surface through wet and dry deposition.

HCs can become a problem in many ways. Since most of these HCs are VOCs, so a lot will enter the atmosphere and is the second main actor to the formation of photochemical smog. The HCs produced from combustion reacts with hydroxyl radicals forming various other compounds, most importantly peroxyacetic nitric anhydride (PAN), as follows:

From the last reaction, it is evident that the PAN is a reservoir of NO2 and ozone. In addition, PANs are the main cause for eye irritation symptoms that occur when there is a photochemical smog in the area (VanLoon G.W. and Duffy S.J., 2005).

The release of Carbon dioxide also has many environmental consequences. CO2 has a residence time of 500 years, 4 – 5 times of nitrous oxides, and is perceived as the main greenhouse gas that is inducing a global climate change. Although CO2 has a low estimated heat potential over its lifetime, but the increasing amounts are being released in to the atmosphere, in combination with increasing trends of temperature, has made CO2 the primary global focus in combating global climate change. The topic is still highly controversial and is still being debated due to the observed increase in temperatures not reaching the expected amounts, but is widely accepted to hold high creditability. The debate still surrounds the compounds of CO2, SOx, NOx, and soot where some suggest that, in addition to CO2, SOx, NOx, and soot also play an essential role towards climate change by being the main molecules to attract water molecules. A high input of NOx, SOx, and soot would essentially form the “condensation nuclei”, leading to the formation of clouds and increasing the albedo levels. The albedo reflects solar radiation but the clouds would also keep the warm temperature beneath. Hence the increasing temperature effect of climate change would not be easily predictable, especially in areas with high NOx, SOx, and soot inputs (Bush M.B., 2003).

Nonetheless, climate change phenomenon holds true and CO2 plays an important role in raising global average temperatures annually. CO2 also impacts the oceanic acidity and CaCO3 availability in marine environments. The main reaction that constitutes this effect involves the dissolution of calcium carbonate, as follows:

where changes in the seawater’s CO2 level is influenced by the atmospheric CO2 (Phinney J.T. et al, 2006).

2.2 Framework

Environmental implications of recreational boating have been reviewed by several past researches. Liddle M.J. and Scorgie H.R.A. (1980) and Davenport J. and Davenport J.L. (2006) have attempted to review environmental implications of recreational boating by conducting literature based study on the issue. Liddle M.J. and Scorgie H.R.A. (1980) have reviewed the impacts of recreation on freshwater plants and animals. The review conducted 14 involves studying previous literature studies, experiments, and conduct observations of impacts. Part of the review conducted observed the impacts of boating, since boating has been viewed as the main water-based activity to have caused environmental problems. The main problems regarding boating found by this research include the problems of physical impacts, which often result in damage to fresh water plants, impacts to animals via disturbances and toxic pollutants released from engines. Although the work is focused on freshwater, but its findings are proven to be useful for this study. Similar work has been done by Davenport J. and Davenport J.L. (2006).

Davenport J. and Davenport J.L. (2006) have reviewed the impact of tourism on coastal environments. The work focused on the often neglected problem of tourism activities’ increase in the degree of magnitude when tourists come to a specific location in mass. The work assessed the environmental problems due to the increase in tourists by conducting literature reviews on environmental impacts touristic accommodations and transports as this will likely increase due to an increase in the number of tourists. The paper reviewed critical problems of recreational boating and laws regarding recreational boating. The study found that the prohibition of TBT in many parts of the world have led to a secondary problems, such as bioinvasion of non-indigenous species.

These 2 researches have achieved showing an array of impacts that may occur due to recreational boating through doing an extensive information and literature search. Although lieterature studies review a tantamount of environmental issues related to recreational boating, but it does not ensure a full coverage of recreational boating’s problems. Furthermore, there has been profound lack of studies that covers an overview of the environmental implications of recreational boating. In order to fully perceive impacts of recreational boating, a systematic overview of recreational boating is required. Hence this study plans to investigate environmental implications of recreational boating by applying environmental systems analysis and sustainability assessment techniques.

Singh R.K. et al (2009)’s research on sustainability assessment methodologies have suggested an overview of various methodological approaches of conducting sustainability assessment for various issues. Since the project we are conducting aims to investigate the environmental implications of boating for policy makers to decide how to deal with issues of boating, the environmental indices for policies given by Singh R.K. et al is observed. The research suggested the use of environment quality index where environmental factors to be considered are based on numerical evaluations and the theory on “multiattribute-utility” and producing environmental quality index of 0 – 10. This method requires the understanding of various environmental impacts and the importance of each environmental factor which needs to be weighted in accordingly. However, this approach would have required that the environmental impacts are fully acknowledged and researched by many academic scholars and authorities in the area.

Pechsiri J.S. (2006) have observed environmental impacts of recreational boating by conducting a field observational study, where a transect study is made in the bay of an island to observe the environmental degradability as common tourism activities continued. The

15 study suggests boating related activities to have caused a great deal of coal degradation in the area. Although the study fully determines the impacts from boating and its related activities through observation, but the study failed to quantify the impacts in comparison to the amount of boats and how the impacts are boating related. In addition, the study observes more of the physical impacts than other impacts and did not focus well on the recreational boating itself.

Håkanson L. and Blenckner T. (2008) have examined the use of bioindicators to help the authoritative body of the society and decision makers when confronted with environmental problems. The research proposes the use of the Effect Load Sensitivity (ELS) analysis model in combination with various bioindicators to determine the ecosystem’s health. The ELS model involves 4 steps: observing the mass balance of a given process or ecosystem, statistically analyse the concentration of related chemicals that may cause specific effects to the affected variable by using correlation and linear regression, indentify the effect on production rates and/or amounts of biomass to identify the effected species in a food chain, and analyse the scenario that resulted from the disturbance of the foodweb and abiotic elements in the environments. The study then observes possible bioindicators that can assist decision makers to use the ELS model that contains the attribute of being low cost and has the ease and simplicity for coastal management use. The bioindicators including observing the mean concentration of toxic substance in predatory fish, chlorophyll a analysis, dissolved oxygen analysis, and secchi disc depth analysis, among others. The problem with this study is the need of laboratory or monitoring stations that can perform these tests or observe these bioindicators which are required for the ELS model. Although the author have successfully created a low cost and simple monitoring method but due to data availiability and funding limitations in this project, conductiong an ELS model on a fullscale would have been too costly. However the concept behind the ELS model can be applied to this project to perceive possible environmental impacts of various emissions.

Håkanson L. and Blenckner T. (2008) wasn’t the only literature to suggest the use of mass balance analysis to predict environmental impacts. Nilsson L. et al (2007) have emphasized the importance of the use of mass balance analysis. The book observes various cleaner production measures that can be applied to industries. One of the chapters explained how a simple mass balance can be beneficial in determining how substances are input and output during each process. Following the thermodynamics’ laws, if the inputs and outputs are not in equilibrium, then they are accumulated somewhere within the process. Accumulation would often result in the process braking down. Quantification and the understanding of processes within are necessary for achieving mass balance analysis. This would require a well monitored environment to obtain data required to perform the mass balance, with a group of experts to perform calculations of various processes. Hence mass balance is only achievable through experimentation in combination with the computation of quantified data by teams of experts related to the issue being computer, which are limited in this study. This project can, however, adapt the mass balance concept in order to perceive the inputs and outputs of a system, and scavenge data from previous studies.

There are several ways to obtain the data. Buerger R. et al (2000) conducted a study on Masonboro island by having an expedition on the island. Pechsiri J.S. (2006) conducted a transect study in the inter-tidal zone to qualitatively identify environmental impacts of recreation. Bellefleur D. et al (2009) conducted the investigation on boat traffic disturbances on birds by taking a boat on a predefined route and observing the birds’ reactions from the boat. The study then uses statistical method to evaluate the impacts. Leon L.M. and Warnken J. (2008) have observed the leachate of Cu and sewage from boats where emissions factors are used in combination with statistical analysis of the boating population to estimate the amount of leachate emissions. Aerial photography has also been used in addition to the statistical analysis used. These methods would require observations made on site and large amounts of data to implement statistical analysis methods. Experimentation can also provide some data required for the mass balance approach.

Eklund B.et al (2008), for example, have observed the impacts of boats by studying the toxic substances released by boats and performing chemical analysis to the samples. Since laboratory work is limited in this project, literature containing experimental studies involving recreational boating must be gathered to provide the understanding and to allow the quantification of emissions. These works discussed above would provide the essential conceptual means of evaluation for environmental implications of recreational boating, where most of the previous works have either focused on a certain issue or a certain organism impacted by boating. By combining these works systematically through mass balance analysis, environmental implications of recreational boating can be fully grasp. However, this would only achieve a more complete perception of impacts from recreational boating. In order to see how these perceived issues effect Koster, integration of these findings to the condition of Koster is mandatory. In addition, environmental systems analysis techniques are needed to be used to capture how these environmental problems have been facilitated by boating and how these impacts will interact with the environment.

The simplest systems analysis that can be applied is the use of cost-benefit analysis. In the cost benefit analysis, all costs are evaluated. This is not only limited to environmental problems but also include financial costs, social costs, and economic costs. Cost benefit analysis would acquire full scale accounting of all inventories, often a monetary value is assigned to each inventory for the accounting of costs. The system is evaluated by balancing the costs and profits. In general, this method does not focus on the factors that facilitate the environment problems and requires high data availability. The method of analysis is also ethically problematic as monetary values are assigned on invaluable objects. However, cost- benefit analysis does give a simple perception of environmental problems which would be well received by the public majority. However, this project observes recreational boating from a broader point of view, where monetary evaluations would have been extremely complex, data unavailability and inaccessibility would have been high, and most of the environmental problems associated with recreational boating is yet unknown. Although various problems have been addressed in the academic field, but not on a broadened scale that could be applicable with coastal marine environments, where most are done with freshwater environments (Hanley N. and Spash C.L., 1993).

In order to focus on environmental problems, a more specialized systems analysis on environmental issues is needed. Strategic environmental assessment (SEA) is a system assessment specialized in observing various scenarios where different alternatives are compared to a scenario where a project or a process is not applied. The assessment would focus on various possibilities rather than the factors that cause the environmental impacts as the practice aims to provide decision makers with a clear policy on how to deal with a certain project or activity. However, in order to perform an SEA, possible environmental problems of the area must be readily studied and addressed (Therivel, R. and Partidario M.R., 1996). Although environmental problems have been considered on Koster in the past, regarding fishing practices and during the setting up phase of the marine Natural Park, problems of recreational boating have not been addressed specifically over Koster.

Environmental Impact assessment (EIA) is a systems analysis study of a project or activity before its initiation phase, but after the decision phase, to consider possible mitigations measures to be implemented with the project. EIA focuses on the environmental effects and the framework which facilitates the environmental problems after the environmental damage has been caused. There are 4 major processes in an EIA. The EIA first observe if the project or activity requires an EIA. The EIA then performs an impact prediction, evaluation, and mitigations study to observe the impacts and various factors that facilitate those impacts. The main objective is to see not only the impacts caused by the project but how widespread is the impact and what other concerns need to be addressed due to those impacts, where mitigation measures should be applied to compensate, remediate, and if possible prevent the impacts from occurring. A full public participation is followed to acknowledge their inputs. Once everyone agrees on the terms and conditions of the project, monitoring and auditing then follows with the objective to monitor the environmental problems that may have been caused by the project, after the project is initiated (Glasson J. et al, 2005). The EIA clearly provide a systematic study of an environmental problem from a project or activity, but does not include a clear method of inventorying the impacts. Hence, an EIA can often lead to a focus on a specific problem while neglecting other problems that are not foresighted.

Life cycle analysis (LCA), on another hand, would fully observe possible influence of the project or activity on to the environment. An LCA observes the whole of life cycle of the project, product, or activity. If a product is observed, for example, the processes that would have been included in the study involves the mining and processing of raw materials required for the specific product, the manufacturing of the product, the distributions of the materials and the products, and how the materials and products be recycled or put to landfill. There are 5 stages to a life cycle: premanufacture, manufacture, product delivery, product use, and refurbishment. Recreational boating would have fit very well in to the product use stage. The LCA framework contains 3 main stages, goal and scope definition, inventory analysis, and impact analysis. In simple terms, the goal and scope is set upon the life cycle of a product, since often the life cycle is large and would be too costly if the scope is too big. The project then often becomes goal specific. The inventory is then analysed to observe all inventory required to be observed, after which the impacts due to the processing of the inventories are observed (Graedel T.E. and Allenby B.R., 2005). Thus, the impacts of the inventories and the

18 processes are well observed more than the factors that facilitate the impacts after they are made. The life cycle framework is often enhanced by the application of mass balance analysis (also known as materials/substance flow analysis) in order to give a full inventory of each process studied. As mentioned earlier, performing mass balance is often costly, but remains a good fundamental concept overlying the method of inventory and process accounting.

The best possible method for this project would be to apply an integrated sustainability assessment approach with the focus only on the environmental pillar of the 3 bottom line of sustainability. The approach was proposed by weaver P.M. and Rothmans J. (2006) where an interdisciplinary approach is applied through a combination systems analysis performance to meet the demands of various members of the society and environmental requirements. However, since this project focuses on environmental implications of recreational boating, only the environmental demands will be observed. In order to fulfill the investigations, which involves the identification and clarification of environmental demands of recreational boating and observe how will these impacts induce other following impacts that would require the understanding of the factors that facilitate the environmental impacts, this project integrates partial EIA and Partial LCA (partial LCIA in particular). The partial EIA would give a good perception of the environmental impacts while a stage 4 based LCIA would provide a well analyzed inventory for further assessment to be conducted in the partial EIA. The partial LCA would be enhanced through applying the concepts of mass balance analysis, which would provide understanding of the processes where its characteristics may pose an environmental threat. Data collection would follow the integrated sustainability approach, where information would be gathered from various sectors of the society and from various experts on any issues regarding recreational boating.

It was then concluded that the partial LCIA in combination with partial EIA would form up the systematic framework of viewing and processing of the information regarding recreational boating while the conceptual method of evaluating the environmental concerns due to recreational boating will be performed by using data from previous researches and information provided by various members of the society. Following the partial EIA framework and the ELS model provided by Håkanson L. and Blenckner T. (2008), factors that further facilitate the environmental problems can then be assessed to provide a higher coverage of an array of impacts by recreational boating. The end result would be a good coverage of environmental implications that needs to be considered for recreational boating in either a marine or freshwater environments to support decision makers in designing the policies.

3.0 Methodology

3.1 Framework Overview

In this research, recreational boating will be viewed as a major process where its sub processes are running in parallel to each other, causing the release of various substances to the environment while demanding environmental resources in the process. Classification of the subprocesses will be conducted by overservation and online boats’ market studies. Clarification of environmental implications of recreational boating will involve conducting 2 major investigations: “Process Inventories Identification” and “Impact Assessment of Recreational Boating”. The Process Inventories Identification will involve investigating the recreational boating process using partial LCIA approach to reveal the substance input and output of recreational boating, resulting in a semi-quantitative mass-balance-like inventory flow diagram, or the conceptual model, of the recreational boating process. In addition, processes that may lead to biotic and abiotic changes in Kosterhavets marine national park area will be identified. The second investigation, Impact Assessment of Recreational Boating, will involve investigating the environmental concerns towards the use or release of substances identified in the Process Inventories Identification investigation on Kosterhavets marine national park. Partial EIA will be the main approach towards assessing the possible environmental impacts of substances used and released by recreational boating, as well as direct impacts of recreational boating towards the environmental biotic and abiotic elements of the Kosterhavents marine national park. An investigation for possible mitigation or preventive measures will be followed after completing the 2 investigations mentioned above.

3.1.1 Process Inventories identification

Following the laws of thermodynamics, the clarification of environmental implications of recreational boating requires the identification and understanding of the substance flow within the recreational boating process. In order to elaborate a substance flow diagram for recreational boating, LCIA will be used to map out the sub processes and inventory the substances involved in recreational boating. As stated by Graedel T.E. and Allenby B.R. (2003) LCIA process involves the construction of the inventory flow diagram with a design and/or manufacturing team/expert, which requires grasping the concepts of how material and energy flows through a system/process. An LCIA often results in a flow diagram that is similar to a mass-balance where one can identify the material and energy input, output, or accumulated within the system/process. In LCIA, quantitative data is often preferable, but qualitative data is also acceptable under

specific circumstances. However, due to the lack of available data, a semi quantitative approach is used in this research.

In order to ensure a feasible LCIA to be conducted, additional boundaries and assumptions are set prior to conducting the LCIA. In addition to the scope and boundaries set in chapter 1, the LCIA to be conducted in this investigation will only be limited to the recreational boating activity, meaning only stage 4 of the recreational boat’s life cycle will be considered. As mentioned earlier, LCIA often inventory energy and materials. However, energy balances will not be considered in this investigation since the energy consumption will vary greatly between each boat involved in this investigation. In addition, following Einstein’s mass-energy equivalence concept (the concept behind E=mc2) and the Energy Conservation law of Thermodynamics, the emissions that may due to energy consumption in the recreational boating process will be perceived in respect to fuel consumption. It is also assumed that all boats involved are motorized. Furthermore the level of detail will not be set as a boundary to ensure that all possible environmental implications of recreational boating due to the inventory flows are considered.

Performing the LCIA in this research will require 2 major steps:

1. The first step is to identify what are the actual sub processes in recreational boating. Identifying sub processes involved in recreational boating can be done in various ways. Ideally, it is best to work with the designer and the manufacturer of products involved with recreational boating. However, since there is the lack of data availability and personals, identifying the sub processes will be done through using both primary and secondary source data. The primary source data will be obtained from field observations, conducted by visiting areas rich in recreational boating including Stromstad, Koster, Goteborg, and Stockholm to observe how recreational boating is often practiced, i.e. what kinds of boats is used and what are they used for, how many people travel on recreational boats at 1 time, etc. In addition, observations at Koster will be made on how boating is conducted, i.e. the use of boats in shallow waters. The secondary source data that are used to identify the sub processes involved include literature studies, checking the internet for boating affiliated websites, contacting companies, communicating with the appropriate authorities, and interviewing experts regarding elements of boating.

2. Step 2 is then initiated once the sub processes are identified. Step 2 inventories substances and analyze its flow throughout the recreational boating process, which can be accomplished in accompany with figures obtained from literature studies. Although

which substance will be quantified in detailed is not yet certain, but following the assumption that all boats are motorized combustion processes will surely be involved, quantify the magnitude of NOx and other possible forms of Nitrogen released will be conducted. NOx estimation, among other quantifiable pollutants estimations can be achieved by using emission factors obtainable from literature studies that are either the results of laboratory experimentations on processes related to boating or documents used in governmental agencies and organizations regarding emissions estimations. Policy figures involving NOx emissions due to combustion processes of recreational boating will also be considered. However, since emission factors have been found to vary in terms of how it is measured, the emissions released due to combustion will be observed in 2 aspects: emission factors with respect to fuel consumption and with respect to engine horsepower since both may lead to varying emissions estimations to be conducted in the next investigation. Other quantifiable substances would be dealt with in a similar manner. For the substances that lack the data availability for quantification purposes, they will be analyzed either qualitatively or semi quantitatively depending on the nature of data that would be available after the sub process identification step and the nature of the sub processes themselves.

3.1.2 Impact Assessment of Recreational Boating

An EIA framework has 4 main processes: “Scoping and Screening”, “Impact prediction, evaluation, and mitigation”, “Participation, presentation, and review”, and “monitoring and auditing” (Glasson et al., 2005). Since this investigation focuses on assessing the impacts associated with recreational boating and that the third investigation to be conducted in this research involves seeking possible mitigation techniques to environmental problems associated with recreational boating, the impact prediction and evaluation process within the EIA framework will be used as the main approach in this investigation. In the impact prediction process, the magnitude of the changes in the environment is observed. Often a comparison is made between scenarios with the cause of environmental change with the scenario without the cause of environmental change, because the aim of the EIA is to decide whether a project or action is to be allowed to continue with the consideration of the environmental impacts. Since this research focuses on a process that is already occurring, a comparison of different scenarios will be omitted in this investigation. The evaluation process will attempt to assess the seriousness, acceptability, and the significance of the impact. Uncertainties that occur during the investigations will also be evaluated.

3.1.2.1 Emissions Estimation and Impact Prediction

Impact prediction can be accomplished through using various approaches. There are 3 major methodological approaches of impact prediction in an EIA: soft, mixed, and hard. A hard model approach would predict impacts through the integration of various mathematical methods and representations of the fundamental elements that make up the parameters in a given scenario. A mixed model approach applies some mathematical amd/or statistical techniques in combination with qualitative justifications derived from field observations, literature studies, and theoretical understanding. A soft model approach fully embraces the use of qualitative analysis to evaluate possible impacts (Glasson et al., 2005). In this research a mixed model approach will be constructed for quantifiable process’ inventories. Soft-model approach will be applied to inventories that are qualitatively identified in the previous investigations, as well as to processes that caused direct changes to the biotic and abiotic elements of Koster.

3.1.2.1.1 Mixed Model Approach

The mixed model approach for quantifiable emissions will predict the magnitude of emissions by combining the emission factor values with boat properties information and estimates of the total usage time, distance and boat frequencies in 1 year using simulation based on secondary data, under the assumption that 1 year has 1 boating season and 1 boating season contains 100 days where the maximum distance traveled by boats would be 50 km (a possible 1 round trip circulating the islands of the Kosterhavets marine national park). Since the method of estimating emissions varies accordingly with how the emission factors are given, measured, and estimated, the boating behavior (usage time, distance, and boating frequencies) estimation and the emission estimation method for air pollutants due to combustion will be described in this section. The mixed model approach to air emission estimation due to combustion process can be analogously applied with other emissions factors that use similar forms of data. The methods of emission estimations for emission factors that do not follow the method for estimating emissions of combustion will be shortly described within the Result chapter.

Since this research aims to quantify the resulting amount of NOx from the recreational boating process, the mixed model approach to NOx emission estimation will be described. The main sub process of recreational boating that lead to the production of NOx is the combustion occurring within the boat engines, meaning that in order to predict the amount of NOx, one needs to know the boat population, the details of the boats, i.e. engine type, the amount of boat usage, among others, including the NOx emission factors themselves. Predicting the amount of NOx is achievable in 5 steps as follows:

Step 1. Collect the data of boats used in Sweden. Since emission factors for NOx are usually given either in g/litre fuel consumed or g/KwH, the details of boats that would be necessary in predicting the resulting amount of NOx annually would be the engine type, engine horsepower, type of fuel applicable, engine cycle type (stroke) of each boat, with the assumption that each boat has 1 engine. This information must be gathered from a variety of sources and literature studies. Some literature describes the percentage of engine type sold in Sweden in the year 2004, since this data is not yet old it can be later extrapolated in other steps. Meanwhile, there is also a register of Swedish boats. Information on registered recreational boats and ships was obtained through communicating with Katrin Sundholm, whom is the person in contact of the Transportstyrelsen (the Swedish Transport Agency). The information provided includes approximately 2000 boats and 2000 ships registered with length, width, and engine model details (see Appendix A). In order to obtain the engine details required for each engine model, internet search has been made on each engine model, while some information is obtained through personal contact with some of the engine companies and through the companies’ engine databases. Engine details in combination with boat details are then tabulated to further investigate the average rated power and average fuel consumption, assuming the fuel density, where the fuel density of Diesel fuel is 850 g/l and the density for gasoline is 719.7 g/l (Heywood J. B., 1988). The resulted data will then be used for further extrapolation.

Step 2. This step tries to estimate the amount of hours spent in recreational boating (boat hours). This is estimated by obtaining the information on the Swedish boating behavior from literature. The Swedish boating behavior was provided by Wester M. (2009) in a report published for the Nordic Council of Ministers regarding green boating, which includes information on the amount of days that Swedes use recreational boats annually, the amount of distances traveled via recreational boating in Sweden, the attitudes towards environmental friendly boating in Nordic countries, among several others. The report was obtained through personal contact with Misse Wester at the Royal Institute of Technology (KTH) in Stockholm, Sweden.

Using the information provided, one can give an estimation of the amount of days and the amount of distance traveled. However, because the values were given within several intervals, estimating the amount of days and distances are achieved through simulation within that particular interval. The amount of hours is then obtained by using the speed, distance and time relationship. Since we don’t know the speed, it is required to do an internet search on boats and yachts market places to assume a reasonable speed for recreational boating. For this project, it is assumed that the average boat speed is 18.5

km/h. An example of how the amount of hours traveled by 100 boats is estimated is shown in the 2 tables below.

Table 1. Number of boat days estimated for 100

Table 2. Distance and time estimationfor 100 boats.

The 2 tables above show that if there are 21.8% of the recreational boating population in Sweden that used boats to travel between 1 – 10 days and if there were 100 boats, there will be a total of 22 boats that would travel between 1 – 10 days. Simulation is used to estimate the amount of days and from the 2 tables above one can see that 7 days is estimated within the same class. This means that from the total of 22 boats, each boat travels 7 days. Thus, the total number of days traveled by all 22 boats is 154, or 154 boat days to avoid confusion. The estimation of the number of boat days is the same for all the class, leading to a total of 3400 boat days per season. Since it is assumed that there is only 1 season per year, so from the tables above it can be said that the total amount of days traveled by all boats is 3400 boat days. The second table shows that 21.5% of the total recreational boating population travels between 0 – 5 km per day. Knowing that there is a total of 3400 boat days, and that 21.5% travels 0 – 5 km per day, it can be said that there is a total of 714 boat days where boats traveled between 0 – 5 km. The estimated distance in the interval is simulated. From the table above, 2 km is estimated and under the assumption that the boat is going at the speed of 10 km/h, it will take 0.2 hours to travel 2 km. Hence, the total amount of hours required by 714 boat days to travel 2 km is 142.8 hours. The same method of time estimation is applied to all classes, resulting in a total of 4581.9 hours per year. From this table, it is estimated that 100 boats would travel 4581.9 hour per year.

Step 3. In order to estimate the emissions of recreational boating in Koster, it is mandatory to know the amount of boats used in Kosterhavets marine national park. This information is obtained by using an aerial photograph taken on a random summer day in 25

2006. ArcGIS software is used to assist in counting the amount of boat while recording the length of each boat. According to communications with Katrin Sundholm, “Under Swedish law, vessels (fartyg) are, divided into ships (skepp) and boats (båtar). Ships are vessels, the hull of which has a length over all of not less than twelve metres and a beam of at least four metres. Other vessels are referred to as boats”, making length measurements mandatory. The counted vessels that would be taken in to consideration for further emissions estimations must be less than or equal to 13 meters (in case of errors). Once the amount of boats in Koster is known, the data for engine types and averaged specifications of each type used in Sweden are estimated, resulting in an estimation of the types and amounts of engines used in boats counted from Kosterhavets marine national park. This information obtained in combination with estimation of the number of hours traveled by the boats in Koster, would allow the estimation of total NOx emissions by multiplying these values with NOx emission factors. It is to be noted that although the types of engines can be extrapolated, the manner of which the values are extrapolated also depends on the data available for the emission factors. For example, NOx’s emission factor with respect to Fuel consumption are categorized as Inboard Diesel, Inboard Petrol, and Outboard Petrol whereas the NOx emission factor with respect to engine horse power are categorized as 4 stroke Diesel engine, 2 stroke Petrol engine, and 4 stroke Petrol engine. Hence the manner of which the types of engines are to be extrapolated with its specifications on to the Koster’s boat population depends upon the nature of emission factors available as well.

Step 4. This step attempts to approach emission estimations by generating a model for engine details extrapolation for Koster’s boat population. Multiple Regression is used to generate a fuel consumption model where fuel consumption is dependent upon the boat length, engine rated power (Kw), the engine cycle type (stroke), the type of fuel, and whether the engine is inboard or outboard. Boat length is used to represent the boat size, since the length is obtained both in Step 1 (from the Swedish boat register) and in Step 3 (where the boats in Koster are counted with lengths recorded). The rated power is used to represent the engine design and capacity. The engine stroke governs the combustion process and how the 3 T rule of combustion is controlled. Whether the engine is outboard or inboard helps to categorize the engine design in relations with the boat design type. The fuel type is used since different types of fuel gives different combustion properties; hence the rate consumption should vary considerably. Although these parameters are not the best figures to be used as representations mentioned above, but these parameters are more available to the public than other parameters at low cost. Once the model is made, F- test is made to ensure that the independent parameters significantly determine fuel consumption. T- test and F- test are also used to test if the engines differ significantly by its class, i.e. to test whether gasoline and diesel engines 26

differ significantly with respect to fuel consumption. If the T- test result and the F- test result disagree, then the Mann-Whitney’s non-parametric 2 independent sample test is used to confirm whether the differences are significant. All of these statistical calculations are made using statistical packaged software.

Once the fuel consumption model is generated, T – test is used to determine significant differences between diesel and gasoline engines with respect to length. The same is applied to inboard/outboard and engine cycle type parameters. The result is to be able to estimate the boat’s engine type from the boat’s length. Through using the recorded length, T – test estimated engine type, and averaged rated power of each engine type, an estimation of fuel consumption is obtainable for each boat counted in Koster.By applying Step 2 with the counted boats while using the regression generated fuel consumption model, total NOx estimation with respect to fuel consumption is obtainable.

Step 5. The NOx emissions calculated from emission factor with respect to fuel consumption, the NOx emissions calculated from emission factor with respect to engine rated power, and the fuel consumption based NOx emissions estimations calculated using the regression model are then compared.

The resulted amounts of NOx are then assessed to see which possible environmental impact they can cause. Identifying possible impacts will be achieved through literature studies. However, there are other emissions that are not resulted from combustion. The method to estimate these emissions’ are similar. See 3.2 for details.

3.1.2.1.2 Soft Model Approach

The substances used and released within the recreational boating process that are not quantifiable or are semi quantitatively described, will be investigated and described qualitatively on how they can become an environmental threat. For other processes that doesn’t lead to substances used or released but can cause direct environmental changes, possible environmental impacts from these processes will be assessed in accompany with field observations. Identifying possible impacts will be achieved through literature studies.

3.1.2.2 Impact Evaluation

The impact evaluation process evaluates the impacts that are investigated in the previous section. In order to see which sub processes of recreational boating can be seen to be more significant in terms of its impact on the biota, the max win voting method is used where the several experts are asked to judge from the emissions investigated in the previous section using questionnaire shown in Appendix D. In addition, the emissions estimated are to be compared with the regulations set by the government, i.e. the EURO IV engine emissions limit and the Swedish regulation on the use of TBT. These investigations will be conducted using literature studies and consulting with experts. For the NOx emissions, comparison with the governmental regulation can be achieved by estimating the NOx emissions following the Mixed Model Approach but using EURO IV emission standards as the emission factors, and see the differences in the amount of total emissions estimated while seeking the answer behind the differences.

3.1.3 Mitigation Measures

From the investigation on the impacts evaluation, one must identify if there needs to be a policy change, if so in which direction can it change. In addition, other mitigation measures that are possible must also be discussed. This can be achieved through literature studies where a combination of many measures will be discussed if they can be applied to mitigate the environmental problems related to recreational boating identified by the previous 2 investigations.

3.2 Emissions Estimation Methodology

From the literature review conducted, several investigations on various emissions need to be investigated. These emissions are the result of various sub processes of elements of recreational boating, i.e. recreational activities.

In order to estimate the emissions and observe possible implications of these impacts, it is necessary to understand the dynamics of diffusion of these emissions and estimate the amount of boat use in Koster first. The study of diffusion involves looking at various aspects of the environmental conditions. Principally the aspects of diffusion involve understanding the flux of a particular substance that is the guest to the environment and the concentration of that particular substance. As demonstrated by Boeker E. and Grondelle R.V. (1999), following Fick’s law, the diffusion of a given substance is as follows:

where F is the mass of guest particles going through a given area and a given direction. D is the diffusitivity of the guest substance given as diffusion coefficients that is dependent on various factors including temperature, molecular weight, among others. C is the concentration of the substance, defined by the substances’ mass, M, and the volume that contains the substance, V. The interaction between C, M, and V follows the following equation:

As explained above, diffusion of environmental contaminants are dependent on various factors. Hydraulic flows, water and air retention time, and air flow dynamic studies would be required to perform diffusion studies, which an interview with an expert in Tjarno suggest such studies are currently lacking. Hence an emissions’ diffusion study would require more time and resource to investigate and would be kept for further study.

One of the main concerns of recreational activities that causes environmental impacts is the actual human metabolism and human littering. Littering is often a sophisticated problem and would require more time to make a study since littering is depended to the consumable goods available in the area, the nature of those products, and the behavior of the people in the region. Hence littering isn’t quantified in this study. Human metabolisms often lead to sewage production. Liddle M.J. and Scorgie H.R.A. (1980) assumed that 137 litres of sewage is released per person per day where 10 g of Nitrogen (ammonia form), 0.4 g of Nitrate, 1.5 g of Phosphorous and 6 g of Carbohydrate carbons are released per person per day. Leon L.M. and Warnken J. (2008) study on sewage inputs from recreational vessels used an estimation of 9 – 17.5 g of Nitrogen released per person per day. From these figures, the amount of Nitrogen released per person per day will be assumed as 12.17 g. In addition, phosphorous and carbohydrate released will be assumed equivalent to the figures provided by Liddle M.J. and Scorgie H.R.A. (1980). These figures will be treated as the nutrient deposition factor. Assuming that one boat has only 1 person, the captain, and these emissions can be estimated as follows:

The number of boat hours is obtainable using the method described in 3.1.2.1.1.

For problems related to antifouling agents, the results of an experimental work conducted by Eklund B. et al (2008) will be used. An accumulated boat wash (from cleaning) sample taken by Eklund B. et al (2008) of over a 3 - 4 months period shows concentrations of organo-tin compounds and metals shown below.

Table 3. Organo-tin compounds and metals obtained from Eklund B. et al (2008)’s results

Although these results represent the water quality after boat cleaning, but it can be assumed the friction between boats’ hull surface and the sea water may result in similar a similar action of cleaning. Furthermore, the waters resulted from boat wash has a high possibility of re-entering the natural water body if boat washing is not conducted within a regulated facility. Hence, the findings of Eklund B. et al (2008) will be used as the main emission factors to estimate the total leachate of antifouling compounds. Therefore, estimations of antifouling compounds can be achieved as follows:

Estimating emissions from boat engines can be achieved as follows:

However, estimating emissions from boats engines are more complex due to the idiosyncrasies between each boat engine, the availability and accessibility of various types of fuels, the chemical properties of the fuel, and the large amounts of varieties of engine models. Furthermore, as seen from earlier discussions in 2.1, the factors that have led to various emissions are very complex in nature and modeling these factors would have required more time and resources. Hence it is more suitable and feasible to use experiment results engines that represent the majority, and emission factors used by governmental agencies. Estimating boat hours would have to be done separately for emission investigation of engines as well.

Emission factors are given in various means, usually a fuel-based assessment would result in emissions per fuel consumed while an engine assessment would result in emissions per rated power. Since the rated power of the engines are determined by the internal average pressure of the cylinders during various sequences of the operating cycle, the piston’s swept volumn, and the speed of the piston as stated by Schnobert H.H. (1990) in combination with the fact that these parameters are influenced by the engines stroke and ignition designs and combustion conditions as discussed earlier, the emissions factors given in respect to engine rated power is first

observed. Cerne O. et al (2008) gave an emission estimation of HC, NOx, and CO for 4 stroke diesel engine based on Volvo’s engineering test report, where is it estimated that an old 4 stroke diesel engine would give 5.6 g/KwH, 0.77 g/KwH, and 0.22 g/KwH of NOx, CO, and HC respectively. Juttner F. et al (1995) made an experiment on 3 outboard engines, 2 of which are 2 stroke gasoline outboard engines and 1 4 stroke gasoline outboard engine, where it is estimated that a 2 stroke gasoline outboard engine gives 0.9 g/KwH, 495 g/KwH, and 267 g/KwH of NOx, CO, and HC respectively. A 4 stroke gasoline outboard engine gives 2.2 g/KwH, 380 g/KwH, and 22 g/KwH for NOx, CO, and HC respectively. Since experiments on gasoline inboard engines are lacking, figures to be estimated will be assumed equivalent to the gasoline outboard engines, following the argument that the main influential parameters come from the type of operating cycle and fuel ignition system (as discussed in earlier in 3.1) and not whether the engine is outboard or inboard. The influence of external temperature should remain similar since, as stated by (Heywood J.B., 1988), both inboard and outboard engines are water cooled. The following table summarizes the emission factors with respect to engine power. Table 4. Emissions of experimented internal combustion engines with respect to engine power

However, it has been found when estimating emissions in respect to fuel consumption, often the estimation would result in significant difference when compared with emission estimation based on emission estimation values with respect to engine power (Kean A.J. et al, 2000). Explanation for this phenomenon is still lacking. A possibility is due to the efficiency of which the fuel is burnt. However, this should have been taken in to the account since the experiments done by Juttner F. et al (1995) and Cerne O. et al (2008) are operated on old engines that lacked efficiency and uses fuel that is commercially and commonly available for testing. Further study would have been required to look into this matter. For the time being, the emission estimation based on emission factors with respect to fuel consumption will also be used. The National

Pollution Inventory of the Australian government have provided the emission factors with respect to fuel consumption, where it is estimated as shown in the following table (NPI, 1999). It is to be noted that NPI (1999) originally gave VOCs estimations but was noted that they were converted from HC estimations; hence the HC figures shown below have been reversely converted from VOC estimates. Table 5. Emission factors used by the Australian Government to estimate emissions of boating

From this table, one may argue that the estimation did not consider the operation cycles which influences the amount of emissions. However, if a comparison is made between table 4 and table 5, it is evident that the nature of emissions for inboard petrol and outboard petrol engines follow the comparative nature of 4 stroke petrol engines and 2 stroke petrol engines.

Carbon dioxide estimation can be achieved in several ways. The first method would be to

estimate the amount CO2 produced from the ideal stoichiometric combustion formula given earlier. However, the problem with this method is, first of all the equation applies when the combustion occurs at 100% efficiency but the combustion process observed in this study is not

100% efficient, resulting in CO, NOx, and HCs. Even if we are to continue using this method, ignoring the problem with efficiency, there is another problem. The determination of the fuel’s chemical composition is difficult. Gasoline, for example, has chemical compositions of alkanes,

among various other compounds. The hydrocarbons of gasoline varies from C4 to C10 as suggested by the gas chromatography analysis provided by Bartok W. and Sarofim A.F. (1991), which also shows a composition of 35 different compounds. Hence, extensive review for estimating CO2 emissions from vehicles would have been needed, and this is obtainable from governmental facts and figures. For this study, the figures used by the USEPA are applied. According to USEPA (2005), the carbon content of gasoline and diesel per gallon is 2.42 and

2.78 grams respectively, where the amount of CO2 emitted from combusting 1 gallon of gasoline and diesel is 8.8 kg/gallon and 10.1 kg/gallon respectively. The third method of estimation would

be to obtain numbers from experimentation. Cerne O. et al (2008) have acquired CO2 emission results from Volvo’s engineering report of a diesel marine engine. However, because only the result of a diesel 4 stroke engine was obtained, using this method would not give a fair treatment for gasoline engines and hence is not used for estimation calculation in this study. The amount of CO2 emission estimated for diesel and gasoline engines are summarized as follows. 32

Table 6. Fuel’s CO2 emission estimates

There are other specific emissions also, i.e. VOCs, fuel additives, etc., but because some of the information is incomplete for comparison, and others like those found in Cerne O. et al (2008) requires extensive translation, in combination with the fact that the main aim of this study is to quantify NOx and other Nitrogen sources, these data are not being quantified for this study. However, values can be found in Cerne O. et al (2008) and Juttner F. et al (1995a). Cerne O. et al (2008), for example have found PAH compounds, i.e. benzene, in the cooling water. Juttner F. et al (1995a) tested on 2 and 4 stroke gasoline engines and found VOCs including Benzene, Toluene, Formaldehydes and Xylene, among 12 – 13 other VOC species. However it is noted that HC estimation values can be used to estimate VOCs where VOC/HC = 0.971 (NPI, 1999). From this conversion however, one can see that most HCs emitted are VOCs.

As mentioned earlier, the reason for the differences between the engines rated power based emission estimation and the fuel based emission estimation is still lacking. The engine rated power based emission estimation are based on laboratory experiments on old engines, where a common commercially available fuel is used and the engines are tested at full load. Hence, the resulted emissions should already have taken into consideration of combustion inefficiencies. The engine rated power, which basically represented most of the engine design’s contribution to combustion efficiencies, would also have taken into consideration of fuel consumption since, in order to produce the engine rated power, constant input of fuel is needed. However, it is possible that other factors may have effected fuel consumption that has been overlooked, which would result in increases in the amount of fuel combusted and the emissions that follow. Therefore, it is required to see whether other factors contribute to fuel consumption differences.

In order to investigate for possible parameters that may have contributed to fuel consumption apart from engine combustion, analysis of variance is used on the data provided in Appendix B, to see if other parameters that is readily available and feasible to obtain may have contributed to fuel consumption. The test would demonstrate if length, engine power, and engine’s operating cycle, the inboard/outboard factor, and fuel type would significantly determine the rate of fuel consumption. It is also necessary to observe which of these factors significantly contribute to the amount of fuel consumed. T test and F test will be used. Regression analysis will be conducted afterwards on the factors that have been tested with the analysis of variance, which would result in a regression model based equation that will be capable of predicting the fuel consumption.

However, before anything estimation can be conducted regarding combustion of boat engines, it is necessary to collect data on engine specifications for the engines shown in Appendix A. The engine specs that we have looked at are the engine rated power in Kw, fuel consumption in l/hr, torque, engine speed, operating cycle design of the engine, fuel type, and whether the engine is an inboard or an outboard type. However, as evident in Appendix A, some boats registered did not give a clear engine model, some models are out dated and no data is available on the internet. Acquiring data for all registered boats then become impossible, and only a handful of boats can be found through company sites and boat online sales. For these rare-find engines, websites like www.yachtworld.com, where there are large numbers of boat sales, have been observed for boat engine specifications that are sold along with boats. Engine models from Yanmar, Volvo, and Albin have the most available data, since the companies kept and provide online access to the engine databases, especially Volvo where the most extensive database record of engines are kept and provided with most data compare to other engines registered. Yanmar engines require looking up databases of many countries, i.e. Yanmar Norway, Yanmar Australia, and Yanmar Japan. Other companies that have some available data include Yamaha, Honda, Suzuki, Evinrude and Johnson. Some marine engine manufacturing companies have ended its business, i.e. Ford Marine engines. For these companies there are some “remakes” available, with Lancing marine being one of the companies remaking some Ford marine engines and providing the engine specifications on their website. Some engine specifications provided are also incomplete, making it difficult to find the necessary data. For some engines, the fuel consumption is not given in l/hr, but is given by g/rated power per hour. These values are converted using the fuel density and the given crankshaft’s rated power of the engine.

The fuel to be taken in to account in this study will be gasoline and diesel as they are primarily abundant and gas stations for Fig 4. Picture taken at a gas boats. The fuel density of gasoline and diesel are estimated to station for boats showing 2 kinds of fuels available be 719.7 g/l and 850 g/l respectively (Heywood J.B., 1988).

4.0 Results

4.1 Process Inventories identification Results

After extensive literature studies and field observations, several sub processes have been identified in the recreational boating process. Each sub processes have been found to demand and release a considerable amount of substances. In order to understand the flow and inventory the substances, the mechanism within each sub process is observed.

4.1.1 Electric Power Generation

Several yacht and boat online marketplaces have indicated that some vessels have been designed for overnight traveling and are equipped with electric power generators (not including those for emergency uses). However, since this sub process was identified near the end of the project, obtaining information on how electric is generated from most boats was not achieved. Electric power generation for mobile offshore use can be achieved by various means, i.e. combustion, wind, and solar, among others. More time would be needed to analyze the common process of electric power generation. Hence the substance flow of this sub process was not assessed. Without knowing the actual process, determining substance flows and environmental impacts is not possible

4.1.2 Recreation

Recreation is probably the first sub process of the recreational boating process that is evident to be environmentally damaging. The recreational activities that involve boating vary, i.e. diving, fishing, and boating itself. Literature studies and field observations show high possibilities for sewage deposition which would increase the amount of nutrients

4.1.3 Antifouling

Literature studies show Antifouling as one of the major environment damaging factors of recreational boating as antifouling agents are toxic towards marine organisms. Although the use of substances like TBT has been prohibited and the use of Cu has been limited, it is assumed in this study that the compound are still widespread since it has been pointed out that these compounds are being covered by non toxic paints. These paints wear-off over time and leading to the leaching of the antifouling agents that were formerly existent on the surface. Compounds that are thought to be involved include TBT, DBT, MBT, Cu, Pb, Irgarol, Zn, and Sn.

4.1.4 Combustions within Internal Combustion Engines

The main combustion process in boating is within the engines themselves which is the common mechanism to move boats. Although one may argue that combustion can also be due to onboard cooking or other possible means, but that is omitted in this research since we have not been able to identify such occurrences in the area of study. Engines have several emissions: air pollutants (NOx, HCs, and CO2), noise, among others.

4.1.5 Process inventory summary

The result of “Process Inventories Identification” investigation has led to the identification of major sub processes occurring in parallel within the recreational boating process. A conceptual model of the recreational boating process is given below.

SOx HCs COx NOx

Metals

H2O • Recreation • Electric Power Generation Biocide • Antifouling

Air • Combustion within boat Engines Fuel Etc.

HCs PM Metals Oil Biocide Etc.

Fig 5. Conceptual Model summarizing the Recreational Boating Process, sub processes, and inventories A number of substances shown in the conceptual model have been found to be quantifiable. Impact predictions have been completed by estimating the magnitude of these emissions and identify the possible impacts that these substances may cause following the method described in chapter 3

4.2 Impact Assessment of Recreational Boating Results

The amount of boats is estimated from an aerial photograph taken on a random summer day provided by Tjarno marine laboratory. The total amounts of boats to be considered are those located within the outer boundary of the Kosterhavets marine national park, shown to the right. Boats that are located + and – 250 m. of the boundary are also taken in to consideration, as their geographical closeness to the area would have a high likelihood to cause environmental impacts to the national park’s area. The aerial photograph showed more than 800 boats within the area of study. The locations of these boats are marked on the aerial photo and its length overalls measured. However, it should be noted that there was a technical error during the = 1 boat process, where data of the location for 100 boats = Area Boundary

mysteriously disappeared. In addition, there are Fig 6. Map of Kosterhavets marine national park also possible human errors when using the GIS with boats’ locations marked.

36 software to measure the length overalls of the boat. The total amount of boats considered is 805 boats, and is assumed to be the total number of boats used in Kosterhavets marine national park. Using methods shown in chapter 3, it is estimated that the total amount of time used by 805 boats are as follows.

Table 7. Estimated Total number of days of boat use for 805 boats without specific classification

Table 8. Estimated Total number of hours of boat use for 805 boats without specific classification

From the table above, it can be described that there are a total of 805 boats, of which 21.8% travels 9 days per season and resulting in a total of 175 boats that travel for 9 days per season. The total of days traveled by 175 boats is 1575 days. Through estimating in the same manner, a total of 21104 days is estimated to be traveled by 100 boats in 1 season, assuming that 1 year gas 1 boating season. Wester M. (2009) has found that 21% of the total boats traveled, go on a 3 km journey. This means that out of 21104 days traveled, 4431 is the total amount of days that boats go on a 3 km journey. Assuming that the boat speed is 18.5 km/h, the boat requires 0.162 hours to travel 3 km. So, if there are a total of 4431 days that boats travel approximately 3km, this will require a total of 718.541 hours of traveling time. By applying the same estimation approach on boats traveling at various distances, a total of 17378.811 hours of traveling time is estimated for 805 boats.

4.2.1 Emission Estimations and Impacts Observed due to Recreation

From the total amount of days traveled by 805 boats, the total amount of nutrients loaded from sewage can be estimated (shown below).

Table 9. Estimated nutrient loading from sewage

This first investigation also detected possible sediment resuspension from 2 observations. The first is the visual evidence suggesting that sediment resuspension is possible due to the shallowness as seen in the photo below.

Fig. 7 Showing a 2 stroke outboard boat and the shallowness of the water as the benthos are clearly visible.

Another observation that suggest possible sediment resuspension is the power of the waves generated by boats. It is observable that during cruising often the water would pile up in front of the boat, and declining along the stern with “tangential waves” being generated along the stern. It is also observable that, a boat with an inboard engine has less powerful wave than outboard engines, but if the engine is a stern drive (engine inside the boat but the propeller is outside) without a tunnel for the stern propeller, then the waves generated would be different. This should be furthered experimented as observations made do not take engine power into consideration which ultimately affects the power of waves generated.

Not to Scale

Tangential waves

Transverse waves

Fig. 8 Diagram showing the observed tangential wave and transverse wave pattern generated when cruising

The combination of these observations suggest possible sediment resuspension since you require high enough power output in combination with shallow waters to achieve resuspension.

Other impacts associated with recreation are also evident. Several sightings where seagrass patches have been cut through by boats have been sighted, shown in the photo below.

Fig. 9. Benthic seagrass damaged by boat

Other activities that are boating related and may cause damage to the environment has not been recorded from Koster. However, interviews with experts at the Tjarno marine laboratory suggested several activities that may cause environmental damage, i.e. Jet skis. Other sources include a video on youtube where a diver was filming underwater diving experience in the area near Koster. The photo below was taken in Lidingo. Although it is not Koster related, but it suggest possible activities practiced in Sweden that may lead to environmental damage. The photo below shows the use of banana boats.

Fig. 10. showing banana boat mounted on top of the boat.

4.2.2 Emission Estimations of Antifouling Compounds

The estimated contaminations due to antifouling are shown below. It is highly probable that locations with concentrated boat use would have a greater impact on the benthic substrates. In addition to the contamination of TBTs, there are also estimated substantial amounts of metals, i.e. Cu and Pb, which are toxic at high concentrations. Table 10. Antifouling Contamination Estimates

4.2.3 Combustion of Engines Emission Estimates Normal Approach

After extensive data collection, various boats are left with incomplete engine specifications and many with no data at all. In order to make the data usable in this study, various parameters have to be abandoned (including Torque and Engine speed) and the data collected from boats need to be filtered such that only those with completed engine specifications are taken into consideration. See Appendix B for the filtered collected data.

Data filtration, however, has led to another problem: the filtered data only contains approximately 600 records, from the 1989 boats registered. Furthermore, according to Cerne O. et al (2008), there are all together 480000 boat engines sold in 2004, with 470000 boats containing these engines. So the Swedish boats registered, only represent a small fraction of the total boat population in Sweden. In order to solve this problem, the recorded percentage of engines sold provided in Cerne O. et al (2008), shown below, are simplified. It is assumed that other types of engines, i.e. sterndrives, and unknown engine sales are inboard engines. The nature of which the engine is simplified depends on the emission factors to be applied. As shown in 3.2, the emission factors with respect to fuel consumption are classed by diesel inboards, gasoline inboards, and gasoline outboards, while emission factors with respect to engine rated power are classed by diesel inboard, 4 stroke gasoline, and 2 stroke gasoline. The simplified engine percentages sold will be used to represent the percentages of engine types of the boating population in Koster. Furthermore, although some boats contain 2 engines, but since the given information on boat sales portrays the total estimated boats with engines are similar to the total engine sold, it is assumed that each boat contains 1 engine.

Table 11. Estimated % of engine sold by type

In order to estimate the emissions due to combustion, the simplified percentages are applied to the boating population in Koster, which is considered to have a total of 805 boats as mentioned at the beginning of 4.2. Emissions due to combustion are first observed with respect to the engine rated power. The 805 boats are classified into subgroups predefined by the simplified percentages from Cerne O. et al (2008). The rated power for each subclass are then assigned by averaging the engine rated power of boats containing the engines that fit in to the criteria of each subclass in Appendix B. The table below summarizes the number of boats divided accordingly with the assigned averaged engine rated power.

Table 12. Boats Classification for emission calculations with respect to engine power

The estimation of days, distances, and time in total traveled by boats in each subclass are then estimated following the method shown in chapter 3. The following figure shows a set of tables of day, distance, and time estimates for each subclass.

Fig 11. Estimated day, distance, and time for boats classified by their rated power and engine type

Once the day, distance, and time estimation is fully established, emission factors given in 3.2 is then applied. By multiplying the emission factors with the total amount of boats per subclass and the total amount of hours traveled by each subclass, a result of total amount of emissions can be achieved. The table below shows the total estimated emissions from combustion with respect to its engine power, per year. Table 13. Total emission estimated with respect to engine power, per year.

As mentioned in 3.2, there are differences when applying emission estimations with fuel consumption. In addition, by calculating the emissions estimations with respect to fuel consumption, estimating CO2 will also be achieved. First engine percentages given by Cerne O. et al (2008) are simplified in to 3 subclasses: Diesel Inboard, Gasoline inboard, and

Gasoline outboard (following the emission factors for fuel consumed given in 3.2). The 805 boats are then classified following the percentages of their subclasses, with their fuel consumption rates averaged from the engine specifications data provided in Appendix B. The amount of days, distances and hours traveled are then estimated using the method demonstrated in chapter chapter 3. The following figure gives a set of tables showing results of days, distances, and time traveled in total by each subclass.

Fig. 12. Estimated day, distance, and time for boats classified by engine type for fuel consumption estimation

The estimated hours in combination with the classification of boats allow the total fuel consumption required for the boats to travel at estimated distance and time to be calculated. The total amount of fuel consumed is estimated as shown in the following table. Table 14. Fuel consumption estimation for 805 boats

Once the total fuel consumption estimation is fully established, the emissions factors can then be used to estimate the amount of emissions. By multiplying the emission factors given in 3.2 with the total amount of fuel consumption, a result of total amount of emissions can be achieved. The table below shows the total emissions from combustion with respect to the fuel consumption estimated per year.

Table 15. Total emission estimated from total fuel consumed

Both estimations of show high amounts of released NOx, Cox, and HCs per year. Although the diffusion rates and modeling of pollutant transports are not achieved in this study, data has been collected on natural harbors in combination with the aerial photo used for boat counts (kept at the Tjarno marine lab) suggests the spatial distribution of boats over the area of the Koster islands.

Fig. 13. The map to the left shows a grid drawn map of Koster with the dots representing the boat locations on the aerial photographs. Each square grid represents 1 aerial photograph. The map on the right shows Koster and its depth profile with the dots represents the location of natural harbors observed for several years.

Both maps suggest a fairly distributed pattern of boating locations and its harbors. The map on the left suggest high intensity in boat populations between the North and South Koster, especially at 003014 and 002015. The map to the right suggest natural harbors situating more towards the Southwest of the South Koster island, in the proximity of 003016, 003017, and 003015. The deep areas demonstrated in the map on the right are the shipping routes, with ferries and ships that are greater than 20m long being spotted. Hence the boats traveling in quadrants 004XXX and 005XXX suggest they are traveling to and from the main land. From

43 these maps, it is possible to say that these emissions will be likely to distribute over the national park rather than concentrate at a particular location. In addition, the heavy boat traffic to the main island in combination with the fact that the area is open to the Atlantic and is geographically situated near the Arctic Circle, there is a possibility for emissions to be transported elsewhere and creating environmental problems.

4.2.4 Combustion Engine Emission Estimates using Statistical Approach

The analysis of variance revealed a significance score of 0.000 (shown in the figure below), which means that the combination of the length, engine power, and engine’s operating cycle, the inboard/outboard factor, and fuel type would highly determine the amount of fuel to be consumed.

b ANOVA Sum of Model Squares df Mean Square F Sig. 1 Regression 239513.1 5 47902.625 623.602 .000a Residual 46396.848 604 76.816 Total 285910.0 609 a. Predictors: (Constant), In_1_in, kw, Length (m), Ful_1_D, stroke b. Dependent Variable: fuel consumption (l/hr) Fig. 14. Analysis of various calculated with the dependent variable being fuel consumption and independent variables being inboard/outboard factor, rated power, length, fuel type, and engine’s operating cycle

The analysis of variance shows that there are possible other factors that may have been overlooked if the engine rated power based emission estimation is used. The result of testing the significant differences between the fuel consumption of 2 stroke and 4 stroke engines is as follows:

Fig. 15. T-test and F-test comparing the fuel consumption of 2 and 4 stroke engines The test performed showed that the average fuel consumption differences between 2 stroke engines and 4 stroke engines are insignificant with the resulted T-test and F-test significance score of 0.73 and 0.97 respectively. To test if the fuel consumption would significantly differ between the inboard design and the outboard design, T-test and F-test is used as follows:

Group Statistics

Std. Error In_1_in N Mean Std. Deviation Mean fuel consumption (l/hr) 0 13 27.1385 24.02263 6.66268 1 596 13.7129 21.55689 .88300 Independent Samples Test Levene's Test for Equality of Variances t-test for Equality of Means 95% Confidence Interval of the Mean Std. Error Difference F Sig. t df Sig. (2-tailed) Difference Difference Lower Upper fuel consumption (l/hr) Equal variances 2.970 .085 2.216 607 .027 13.42561 6.05809 1.52825 25.32296 assumed Equal variances 1.998 12.425 .068 13.42561 6.72094 -1.16267 28.01389 not assumed Fig. 16. T-test and F-test comparing the fuel consumption of inboard and outboard designs. In the table on the top, 0 represent outboard design and 1 represent inboard design.

The test performed showed fuel consumption differences between inboard and outboard designs are significant with the resulted T-test and F-test significance score of 0.027 and 0.085 respectively. To test if the fuel consumption would significantly differ between fuel types, T-test and F-test is used. The result is as follows: Group Statistics

Std. Error Ful_1_D N Mean Std. Deviation Mean fuel consumption (l/hr) 0 37 16.7907 22.78184 3.74531 1 572 13.8189 21.61286 .90368 Independent Samples Test

Levene's Test for Equality of Variances t-test for Equality of Means 95% Confidence Interval of the Mean Std. Error Difference F Sig. t df Sig. (2-tailed) Difference Difference Lower Upper fuel consumption (l/hr) Equal variances 5.181 .023 .808 607 .419 2.97178 3.67831 -4.25198 10.19553 assumed Equal variances .771 40.305 .445 2.97178 3.85279 -4.81317 10.75672 not assumed Fig. 17. T-test and F-test comparing the fuel consumption between fuel types. In the table on the top, 0 represent Gasoline and 1 represent diesel.

The test performed showed fuel consumption differences between fuel types to contain mixed results. The T-test performed showed that the fuel consumption differences between gasoline and diesel is insignificant with significance score of 0.42, whereas the F-test performed showed that the fuel consumption differences between gasoline and diesel is significant with significance score of 0.02. In order to confirm whether fuel consumption differences between fuel types are significant, the non parametric 2 independent sample test is used. The result is Test Statisticsa as follows. Ranks fuel consumption Ful_1_D N Mean Rank Sum of Ranks (l/hr) fuel consumption (l/hr) 0 37 259,14 9588,00 Mann-Whitney U 8885,000 1 572 307,97 176157,00 Wilcoxon W 9588,000 Total 609 Z -1,638 Asymp. Sig. (2-tailed) ,101 a. Grouping Variable: Ful_1_D Fig. 18. Nonparametric 2 independent sample test comparing the fuel consumption of gasoline engines with fuel consumption of diesel engines. In the table on the left 0 represent gasoline and 1 represent diesel

The nonparametric 2 independent sample test result shows that the fuel consumption between gasoline and diesel engines are significantly different, with significance score of 0.1.

For length and engine rated power, regression analysis will be used since the data is continuous, in accompany with analysis of variance and T-test. The linear regression performed on fuel consumption and length results show that fuel consumption differences are significant for boats at varying lengths, with both analysis of variance and T-test significant scores equal to 0.00. However, since the R Square value obtained is 0.39, the regression analysis showed that less than 10% of the time the length can determine the fuel consumption rate as shown below. Model Summary

Adjusted Std. Error of Model R R Square R Square the Estimate 1 ,197a ,039 ,037 21,26972 a. Predictors: (Constant),ANOVA Lengthb (m)

Sum of Model Squares df Mean Square F Sig. 1 Regression 11106,886 1 11106,886 24,551 ,000a Residual 274607,4 607 452,401 Total 285714,3 608 a. Predictors: (Constant), Length (m)Coefficientsa b. Dependent Variable: fuelUnstandardized consumption (l/hr) Standardized Coefficients Coefficients Model B Std. Error Beta t Sig. 1 (Constant) -7,199 4,364 -1,650 ,100 Length (m) 2,140 ,432 ,197 4,955 ,000 a. Dependent Variable: fuel consumption (l/hr) Fig. 19. Regression Analysis for Fuel Consumption and length It may be possible that the R Square may improve if other possible curve fits are observed. Various curves are applied as shown in the graph below.

fuel consumption (l/hr)

Observed 200,00 Linear Logarithmic Inverse Quadratic Cubic Compound 150,00 Power S Growth Exponential Logistic 100,00

50,00

0,00 0,00 5,00 10,00 15,00 20,00 Length (m) Fig. 20. Graph of fuel consumption and length relationship

The best curve that represents the relationship between fuel consumption and boat length that can be seen from the graph is the cubic curve, where the R Square value obtained from this curve is 0.066 and the relationship is “F = 150.91- 42.24L + 3.94L2-0.11L3” where F = fuel consumption and L= length in meters. However, there are other curves that are able to achieve higher R Square values (with the highest obtainable R Square value is 0.113) including logistic, growth, compound, and exponential curves, suggesting that the fuel and length relationship is exponential as the following equation:

The linear regression performed on fuel consumption and engine power results show that fuel consumption differences are significant for boats at varying engine power, with both analysis of variance and T-test significant scores equal to 0.00. However, since the R Square value obtained is 0.83, the regression analysis showed that approximately 80% of the time the engine power can determine the fuel consumption rate as shown below. Model Summary

Adjusted Std. Error of Model R R Square R Square the Estimate 1 ,913a ,834 ,833 8,84947 a. Predictors: (Constant), kw Coefficientsa Unstandardized Standardized Coefficients Coefficients Model B Std. Error Beta t Sig. 1 (Constant) -1,745 ,458 -3,808 ,000 kw ,382 ,007 ,913 55,149 ,000 a. Dependent Variable: fuel consumptionANOVA (l/hr)b Sum of Model Squares df Mean Square F Sig. 1 Regression 238178,2 1 238178,246 3041,358 ,000a Residual 47536,064 607 78,313 Total 285714,3 608 a. Predictors: (Constant), kw b. Dependent Variable: fuel consumption (l/hr) Fig. 21. Regression analysis for fuel consumption and engine power

It may be possible that the R Square may improve if other possible curve fits are observed. Various curves are applied as shown in the graph below.

Fig. 22. Graph of fuel consumption and power (Kw) relationship

The best curve that represents the relationship between fuel consumption and boat engine power (in Kw) is the cubic curve, where the R Square value obtained from this curve is 0.872 and the relationship is as follows:

Where F = fuel consumption and P = engine power (Kw).

From these statistical tests, it is observable that engine power play the essential role in determining the rate of fuel consumption, but other parameters, including length, fuel type, and inboard/outboard design also contribute in determining the amount of fuel consumed. Other parameters that may affect the amount of fuel consumed also include other dimensions that are more difficult to obtained, i.e. width and height of the boat. However, it would be more efficient to keep with the parameters that are feasibly obtainable within a short period of time. The “length-over-alls” of a ship can be directly measured when observing the amount of boats through satellite imagine and aerial photographs.

These parameters that have been described can help to predict the fuel consumption of a boats using regression analysis on the 5 parameters. The result of regression analysis is as follows:

Model Summary

Adjusted Std. Error of Model R R Square R Square the Estimate 1 .915a .838 .836 ********** a. Predictors: (Constant), In_1_in, kw, Length (m), Ful_1_ D, stroke Coefficientsa

Unstandardized Standardized Coefficients Coefficients Model B Std. Error Beta t Sig. 1 (Constant) 3.089 7.679 .402 .688 Length (m) -.306 .194 -.028 -1.583 .114 kw .385 .007 .918 53.683 .000 stroke 2.020 2.445 .020 .826 .409 Ful_1_D -.970 1.867 -.011 -.520 .604 In_1_in -9.228 4.028 -.062 -2.291 .022 a. Dependent Variable: fuel consumption (l/hr) Fig. 23. Linear regression Analysis of 5 parameters to predict fuel consumption rates From the linear regression analysis, it is evident that the 3 most significant parameters for the determination of fuel consumption rates include inboard/outboard design, length, and engine power. The R score of 0.92 suggests that the parameters are highly correlated to fuel consumption and the R Square score of 0.84 ensures the high predictability of fuel consumption using these 5 parameters. Although the fuel type and operating cycle may be significant in predicting the fuel consumption, but these 2 parameters play an important role in determining the characteristics of emissions the engine will produce.

The resulted linear regression model capable of predicting the fuel consumption rate is as follows:

Where F = fuel consumption, L = length in meters, P = Engine power (Kw), S = Engine’s operating cycle (stroke), T = fuel type where 0 = gasoline and 1 = diesel, and I = inboard/outboard design where 0 = outboard and 1 = inboard.

In order to see if this model would be able to be applied for emission estimation, the model is applied on to the 805 boats counted at Koster. Since the boats were counted using aerial photographs, lengths measured using GIS software was recorded for the 805 boats. From the lengths recorded, predicting the engine’s operating cycle, inboard/outboard design, and fuel type is achievable using statistical T-test with the data provided in Appendix B. The T-test results to determine the length differences for engines with different amount of engine’s operating cycle are as follows:

Group Statistics

Std. Error stroke N Mean Std. Deviation Mean Length (m) 2 7 7.1643 1.55022 .58593

4 602 9.9356 1.98022 .08071

Fig. 24. T-test result for stroke estimation from length

The t-test shows that there is a significant difference in length of boats with 2 stroke and 4 stroke engines. The engines operating cycle is then predicted using the means calculated from the T-test. From the means resulted from the T-test, it is evident that larger boats have 4 stroke engines and smaller boats have 2 stroke engines. In this case, boats smaller than 7.16 meters are 2 stroke, and boats larger than 9.93 meters are 4 stroke. The problem is that there are some boats in between these two lengths. Judging from the standard deviation, the assumption is then made that boats that are less than 8.16 are 2 stroke engines and the rest are 4 stroke engines.

The T-test results to determine the length differences for boats with inboard designs and outboard designs are as follows: Group Statistics

Std. Error In_1_in N Mean Std. Deviation Mean Length (m) 0 13 6.9646 1.57580 .43705

1 596 9.9678 1.95740 .08018

Fig. 25. T-test result for inboard/outboard estimation from length The t-test shows that there is a significant difference in length of boats with inboard and outboard designs. The inboard/outboard design is then predicted using the means calculated

50 from the T-test. From the means resulted from the T-test, it is evident that larger boats have inboards and smaller boats have outboards. In this case, boats smaller than 6.96 meters are outboards, and boats larger than 9.98 meters are inboards. The problem is that there are some boats in between these two lengths. Judging from the standard deviation, the assumption is then made that boats that are less than 7.96 are outboards and the rest are inboards.

The T-test results to determine the length differences for boats using diesel and gasoline are as follows: Group Statistics

Std. Error Ful_1_D N Mean Std. Deviation Mean Length (m) 0 37 7.6176 1.47271 .24211

1 572 10.0516 1.93605 .08095

Fig. 26. T-test result for fuel type estimation from length The t-test shows that there is a significant difference in length of boats using gasoline and diesel. The fuel type is then predicted using the means calculated from the T-test. From the means resulted from the T-test, it is evident that larger boats use diesel and smaller boats use gasoline. In this case, boats smaller than 7.62 meters use gasoline, and boats larger than 10.05 meters use diesel. The problem is that there are some boats in between these two lengths. Judging from the standard deviation, the assumption is then made that boats that are less than 8.65 are considered to use gasoline and the rest are considered to use diesel.

Since the statistical test showed that the engine rated power is the most essential factor in determining the fuel consumption rate, and they are often available, predicting engine rated power will be achieved by using the engine power averages of boat engines in Appendix B that fits the predicted engine design and fuel type. The Appendix B should have enough models and brand variations to cover a range of engine characteristics. Once the engine power, engine’s operating cycle, inboard/outboard design, and fuel type is predicted, the amount of fuel consumption can then be predicted. The predicted fuel consumption is for each 805 boats can be viewed in Appendix C. Once the fuel consumption is predicted, emission estimation can be fulfilled similar to what has been done in 4.2.3, resulting in the figure shown below.

Fig. 27. Tables summarizing the emissions estimated using statistical assisted approach 4.2.5 Emission Estimates Summary

In summary the amount of NOx, CO, HCs, and CO2 estimated from 3 approaches is shown in the graphs below.

Fig. 28. Graph showing total NOx estimates calculated using different approaches and emission factors.

Fig. 29. Graph showing total CO, HCs, and CO2 estimates calculated using different approaches and emission factors.

The following diagram summarizes the estimated emissions of a 100 day recreational boating with 805 boats within Kosterhavets marine National park.

2 800 kg NOx 50 000 kg HCs 850 000 kg CO Etc. 2 256.84 kg A lot of Metals Nitrogen

A lot of H2O 100 days of recreational boating in 31.68 kg A lot of Biocide Koster, with an estimated 805 boats Phosphorous used in total during the 100 days. A lot of Air 126.62 kgC

Fuel (70000 l diesel, Carbohydrate 300 000 l gasoline) Etc. Etc.

Minimum of 241500 mg Cu Oil Minimum of 3220 mg TBT Etc.

Fig 30. Estimated emissions summary

5.0 Discussion

5.1 Impact Evaluation

Evaluating impacts for the subprocesses of recreational boating is complicated for this project since a lot of impacts are semi-quatitative and highly lacks the required data and resources. However, if one is to compare the results of this study with the regulations, the emissions estimated are significantly high. The TBT and Cu antifouling has been prohibited by the Swedish law to prevent impacts from TBT and Cu leachate from boats. However, as explained in 2.1, and estimated in 4.2.2, TBT and several metals are still found to be depositing on the top sediment layer at toxic levels for invertebrates. This is confirmed by another study conducted by Martinez P.G. (2009)’s study on mussel growth differences in areas with high boat usage intensity. In terms of recreation, physical impacts have been found. However, since the fishing problems in the past have impacted a lot of the benthic communities, especially coral communities, the significance of recreation in terms of direct physical impacts is relatively low but in terms of impacts to the seagrass, recreational boating is considered to be a great threat. Further study needs to be made to confirm this claim. In terms of nutrient emissions, it is unable to determine a quantitative answer of significance, since the problems due to nutrient load can only be addressed after knowing the hydraulic flows in the vicinity of Koster. However, if the water remains confined to Koster, nutrient loading can become highly problematic. The release of carbohydrates can also lead to increase in the usage of oxygen in the water as stated by Boeker E. and Grondelle R.V. (2001). Since many areas of the Baltic and adjacent seas are oligotrophic, which often run a low risk of oxygen depletion and often contains a <70 μg/l of nitrogen and <10 µg/l of phosphorous. An input of 256.84 kg of nitrogen and 31.66 kg of phosphorous in combination of126.62 grams of carbon for carbohydrates could increase algae and growth of microorganism growth and initiate the regime shift from oligotrophic to mesotrophic, depending on the hydraulic flows, the water retention time, and how these nutrients flow within the system.

The most controversial problems of recreational boating is due to the combustion process. If the regulation is reviewed, it would be observable that combustion release the quantity of emissions greater than it would have under EURO IV regulations emissions. This can be observed by setting up a scenario where all boats follow the EURO IV regulations, which a gasoline engine would produce 0.08 g/km, 1 g/km, and 0.1 g/km of NOx, CO, and HCs respectively (Guzella L. and Onder C.H., 2004). The total emissions for boats using gasoline would produce total emissions as follows:

By taking these calculated emission results and compared it with figures given in chapter 4.2, it is evident that the release from combustion in recreational boating is much more than the EURO

IV regulation scenario. In addition, the significance of this issue is also heightened by the fact that the emission factor for high speed marine boats (recreational boats) are comparable to emissions from trucks (see below) as demonstrated by Kean A.J. et al (2000). These factors indicate the seriousness of recreational boating problems and that it should be treated equally to other modes of transport, i.e. trucks and cars.

Comparison of Emission Factors of Various Diesel Engine Uses (Kean A.J. et al 2000) Application NOx (g/kg) PM10 (g/kg) Trucks 42 ± 5 2.5 ± 0.2 Locomotives 75 ± 9 1.9 ± 0.3 high speed marine vessels 40 1.2

However, if the emissions estimations of recreational boating are compared to the total CO2 emissions transportation in Sweden, then the emissions from boats in Koster becomes less significant. A figure given by Chris J. (2009) showed Swedish transport sector to produce 22 million tons of CO2 in 1 year in 2004 while the recreational boats in Koster releases 900 tons of CO2 per year (0.004% of the Swedish CO2 released in the transport sector). If a comparison is made with the total amount of marine engines sold in Sweden in 2004, approximately 570000 tons of CO2 can be estimated with the method used in 3.2, which is equivalent to 2.6% of the total CO2 produced by the Swedish transport sector in 2004. This is because of the amount of usage of recreational boats in one year, the nature of how it’s used and the limitations boats have.

From the emissions estimated, there are high amounts of HCs, which as mentioned in 3.2 consists of high amounts of VOCs. The releases of substances like PAH and VOCs have led to ecotoxicological effects. NOx and HCs released may also lead to the generation of photochemical smog, acid precipitation, and eutrophication possibilities. Another problem related to emissions of combustion engines that is required to be discussed is the release of CO and CO2. CO is poisonous to the blood and is a health hazard in itself. This is more of a boat design and health related issues, but high amounts of local CO may affect the wildlife in the area. CO2 however has other important effects. As mentioned earlier, CO2 may lead to increase oceanic acidity, leading to CaCO3 dissolution. The dissolution of CaCO3 means that the organism that relies on CaCO3 formation will be impacted. However, this is also determined by the rate of photosynthesis for primary producers in the system. These problems in combination with increasing trends of boat use lead to the re-determination of the significance of boating impacts for Sweden would need to be further studied but for Koster, where boats are the main means of transportation, emissions due to boating remains highly significant.

Furthermore, there is no available meteorological model and NOx partitioning model available to predict how will the released of pollutants from recreational boating will be dispersed, making it difficult to determine the significance of recreational boating impact. Nonetheless, Koster

islands have very small roads, contain almost no cars, making recreational boating the main source of emissions in the area.

A set of questionnaires have been sent to 5 experts located at Tjarno marine biology laboratory station in Tjarno, which is located near Stromstad and Koster. The questionnaire aims to have their views to see whether which sub-processes of recreational boating should be given the highest priority. By the end of this project, only one has returned, suggesting that recreation and antifouling impacts mostly on marine ecosystem, especially its biota, and greatly effects the human settlements while combustion would heavily effect everything. In total, combustion from internal combustion engines score highest as a precursor to impacts from recreational boating.

5.2 Possible Mitigation Measures

The results shown in 4.2 have shown many precursors to various environmental problems. However, as portrayed in 5.1, the ways of which the policies have been implemented for recreational boats should definitely be revised. There are many possibilities in policy revision. Although boat control would have been difficult, since setting up check points to check up all the boats would have been near impossible, but it is possible to introduce policies that would have favoured the boaters while controlling the environmental impacts in return. Policies can range from the encouragement for boat registration through giving incentives, i.e. fuel and washing coupons, free paint job etc. Boat free zone can also be set up, with inflatable mechanisms to prevent trespassing and preventing direct impacts that can occur in shallow waters. Other policies may involve the encouragement to use alternative fuels, i.e. ethanol and LPG fuel. However, before implementing alternative fuels like ethanol and LPG fuels, it is necessary to classify which kind of problem is likely to happen. These problems can only be predicted through a study on flow dynamics in the vicinity of Koster. The reasons behind the study requirement of alternative fuels are that often various fuels once applied would have led to a shifting of problem. The use of ethanol base fuel has been found to reduce some amounts of HC species while releasing more formaldehyde (Cerne O. et al, 2008). LPG usage reduces the amount of CO produced in outboard engines while releasing more NOx due to its high heating value (Murillo S. et al, Fig 31. Photo showing boat out of the water 2005). A better policy would be to limit the use of

fuel-based engines, and instead promote the use of renewable energy sources for powering boats. Electric motors can be used with a possible solar generator onboard perhaps? These issues must be further studied. Although the use of elecgeneration system was not studied, but a contact with the Petroleum Authority of Thailand that had worked with shipping suggested the implementation of “cold ironing”, which observes the possibility of shutting ships power and electricity at ports. Nontheless, the problems of increasing nutrient loading and air pollution would have remained for a very long time.

Other solutions involving the increase of nutrient loading and air emissions would require working with the recreational boating process directly. Encouragement towards the use of newer engine designs that has catalytic deNOx and soot filtration system would reduce the air emission pollutants. However, the emissions of CO2 would be unavoidable. The reduction of the carbon footprint for recreational boats can be implemented in many ways, which is also applicable for other ecological footprint reductions in Koster. Bioregenerative life support systems can be applied to Koster to take up the produced CO2 while releasing back the exact amount O2 required for combustion (Nelson M. et al, 2003). However, this would require many more new researches on mass balances to see the amount of CO2 release of engines and uptake by a particular bioregenerative life support system design, which would often lead to other by products, i.e. food, which can lower other aspects of ecological footprints. This can also be applied to applied problems, i.e. an onboard miniaturized contructed wetland to directly absorb the nutrients released from sewage or miniaturized and simplified agro-ecosystems to take the pollutants released (Nelson M. et al, 1999, and Volk T., 1996). Other concepts of ecological engineering may be applied to have reduce the severity of the impacts, i.e. the use of mussel farming to take up nutrients (Odum H.T., and Odum B., 2003). However, the use of ecological engineering method must be studied carefully with as little use of non-primitive species as possible. In addition, the use of ecological engineering may affect several organisms within the ecosystem. In Koster, the coral recovery is being processed over the area and placing mussel farms may reduce the recovery rates. All of these require further studies.

The problems of antifouling are difficult to address. There are already strict laws prohibiting its use. To prevent further leachate, it may be possible for the government to regulate how boat washing should be processed. An alternative that is observable in the market is having a special none environmentally damaging sheet/fabric attached to buoys for the prevention of fouling. This alternative is already in the market as found on some internet websites. Another simpler alternative is to have the boat out of the water, as in on the photo to the right, but may be complicated for bigger boats.

5.3 Uncertainty Evaluation

The environmental implications identified and the quantification of environmental emissions in the previous chapter clearly shows that the project was able to fulfill its aims to semi quantitatively analyzed the environmental implications of recreational boating, but fail to give a

solid prediction of possible impacts. A lot of limitations in this study were due to the lack of information, problems with data collection, lack of resources, and the instability and complexity of atmospheric and hydraulic conditions of Koster. There has been a lack of information on the boats used in Sweden and Koster alike, since the Swedish recreational boats register does not represent the Swedish population well. There is a lack of knowledge on hydraulic and atmospheric conditions at Koster as well, causing the prediction of impacts on Koster to be soft, and hence, a study on atmospheric and hydraulic modeling over Koster would be appealing for future studies. Another problem is the method of data collection. When aerial photos are used to count boats, with dimensions of boats measured, there are often problems associated to it.

Rock

Fig 32. An aerial photo of a harbor in South Koster For example, the aerial photograph above shows a harbor with several recreational boats, recognized by their shapes. The problem comes when out in the middle of the ocean, an image with the same shape, size, or color can be something else, i.e. rocks. Another problem is due to the boats themselves; some boats do not have engines (picture C), while others have sails which would greatly influence the speed and fuel needed to be consumed (Picture B). Furthermore, it was assumed using statistical methods that boats less than 8 meters used 2 stroke engines, but as seen below (Picture A), boats with its length overalls as short as a car can use a 4 stroke engine.

Sails 4 Stroke outboard

A B C Fig 33. Boat photos showing boats with sails, outboard engines, and some without engines at all Another problem associated with the aerial photography is the fact that the photo only represented one day, meaning that the average amount of boats over the season could have been either much more than 805 boats or less than 805 boats. Also, the aerial photograph provided by the Tjärnö Marine Laboratory was taken on a summer day in 2006 but was not recorded by which month. This meant that the aerial photograph might have been taken during the month at the beginning of the summer, midsummer, or even the end of the summer. Each temporal difference can either lead to the result conveyed in this study to be either underestimated or over estimated. Furthermore, available information obtained is sometimes wrong. One of the documents that this study has referenced had some discrepancies where a unit of g was mistakenly mistyped as mg.

There is also another problem when the investigations were conducted on boat speed and engines. A direct contact with Volvo claims that the speed of the boat requires testing as boats’ speed are dependent on the engine power, realistic load, and hull design. This project has assumed the speed to be 18.5 km/h, equivalent to approximately 10 knots. Further studies may have to be made a more realistic prediction of speed for boats. A more realistic speed prediction would differentiate the amount of hours estimated in this study and would give a better picture of the emissions released. Furthermore, one of the greatest uncertainties in this project is the prediction of total time used in recreational boating in Koster. It is evident that various figures of total fueled consumed and emissions that resulted from combustion are not consistent. This is due to the use of random simulation of the amount of days and distances traveled, which ultimately affect the magnitude of boat use and its emissions.

Apart from the problems related to the actual execution of the investigation, there are also several uncertainties that should be taken in to consideration when reading the results. First of all, the observation made regarding the power of waves generated by boats’ cruises is questionable. The differences in power are judged by observing the length and size of waves formed. However, this is not accurate as waves generated are governed by other factors including boats. In addition, whether the environmental problems associated with the emissions generated will occur in Koster depends on various factors. As mentioned earlier, factors involving atmospheric conditions and hydrological dynamics play an important role in

determining where and how these emissions will be transported. Eutrophication may not be as significant if the water retention time is low but the direction of flow may influence nutrient loading elsewhere. From looking at the meteorological data provided on the Swedish Meteorological and Hydrological Institute’s website, where satellite images in June is provided, unstable atmospheric conditions for Kattegat and Skagerrak Sea are observable, which meant that predicting these impacts would be a great challenge for future research.

The hydrological dynamics within the Skagerrak and Kattegat Sea is also complex. The flows are influenced by various inputs of water and the flowing mass of water from the Baltic Sea towards the North Sea. A study of the hydrological conditions of the area would require extensive use of marine vessels, where a fleet of 17 research vessels was required to observe the oceanographic variability of the Skagerrak and Kattegat Sea which have found various variability of nutrient and algae concentrations over the area (Danielssen D.S. et al, 1997). However, the main water mass flow reported over the area where Koster and Stromstad is situated seems to be flowing out towards the North Sea. Since the study was more focused on the Skagerrak and Kattegat Sea, the area of Koster wasn’t extensively covered, and further study would be required to make any appropriate suggestions.

It is, however, necessary to clear out one uncertainty. The fact that the emission factors used with fuel consumption are obtained from an internet source lowers its creditability. Hence the fuel-based emission estimation used in this report will be compared with another source that has been published in a scientific journal. Kean A.J. et al (2000) provided a fuel based estimation for NOx, where 40 g of NOx is estimated to be produced per kg of fuel. From this figure, a comparison is made for boats with diesel engines by applying the method of estimating the amount of fuels consumed and time estimation used in this study. The result is as shown below.

Table 16. Estimated NOx from diesel consumption using (Kean A.J. et al, 2000)’s estimates.

The result of the comparison showed that estimates used in this report (shown in 4.2) is similar to the amount estimated using figures provided by Kean A.J. et al (2000), where the amount of NOx estimated by the method used in this study suggests a total of 2765.86 kg NOx released from diesel engines and the amount of NOx estimated by Kean A.J. et al (2000) suggests a total of 2293.64 kg of NOx released from diesel engines. Thus the emission factors used in this study is creditable enough to be used.

Another uncertainty that requires proving is the issue regarding the inboard and outboard design, and how it may affect the amount of engine rated power to be estimated. This report argued that the main influential parameters for emissions with consideration of engine rated power come from the type of operating cycle and fuel ignition system and not whether the engine is outboard

or inboard. In order to prove this, the statistical T-test and F-test is applied to Appendix B, to see if there would be any differences between the engine rated power of inboard engines and the outboard engines. The T-test revealed a significance score of 0.42 and the F-Test revealed a significance score of 0.65 (shown in the figure below), which means that the differences of the engine rated power between inboard and outboard engines are insignificant.

Group Statistics Std. Error In_1_in N Mean Std. Deviation Mean kw 0 13 52.7243 46.46200 12.88624 1 596 40.9111 51.86083 2.12430

Independent Samples Test

Levene's Test for Equality of Variances t-test for Equality of Means 95% Confidence Interval of the Mean Std. Error Difference F Sig. t df Sig. (2-tailed) Difference Difference Lower Upper kw Equal variances .208 .649 .814 607 .416 11.81319 14.51124 -16.68513 40.31151 assumed Equal variances .905 12.661 .383 11.81319 13.06016 -16.47859 40.10497 not assumed Fig 34. Statistical test for differences between the engine rated power given for inboard motors and outboard motors. In the table to the top, 0 represents outboard motors and 1 represent inboard motors

One of the main interesting findings of this study is the differences in the emission factors for combustion of boat engines. Statistical assisted approach to emission estimation resulted in calculated estimated emissions that are similar when compared with the results of fuel-based emission factors for combustion. This shows that the statistical model resulted in this chapter can be used to help predict emission estimations in the future while allowing simpler means of data collection. Until now, the statistical tests are able to prove that fuel consumption is not only determined by engine power, but often the engine power is enough to be considered. From the model it can be perceived clearly that the engine power predicted most of the fuel consumption. Nevertheless, one reason to the differences in fuel-based estimated emissions and engine power based estimated emissions are the factors to be considered for fuel consumption estimation. However, should the emission factors used in this study follow the fuel based estimation or engine power based estimation is an interesting issue for future research, since it is now out of the boundary of this project study but this factor will greatly influence on the accuracy of emissions estimated for combustion. This also emphasized the need for further study to improve many inaccuracies in this study. For example in reality some outboard engines are also 4 stroke engines (see Appendix B). In addition, only gasoline and diesel will be taken in to consideration. Furthermore, ethanol fuel should also be considered, among other variety of fuels.

There is a high likelihood that the result presented in this project is under estimated. During the execution of the investigations, it can be recognized that the boundary chosen for the study might be either too confined to the open sea. During the field observations at Koster, most small boats

have been noted not to cross the gap between Koster and the main land. Reasons are speculated to be due to the oceanic wave’s sizes and strong oceanic currents. During the investigations using aerial photographs, large proportions of recreational boats (approximately double the amount in Koster) can be found confined to the coastal areas of the main land. This have pointed the limitations of the geographical boundaries set at the beginning of the investigation and has led to underestimation of emissions from boats in Koster. The underestimation of the impacts is not only due to the limitations of the boundary but also the lack of a structured grid observation of the island. This is mainly due to the lack of funding and time. Grid studies would allow a more detailed observation of the island, which would allow a better insight on the impacts of recreational boating on coastal areas of Koster.

In general the main problem of this study lies in the lack of information and data that would have allowed a lot of inaccuracies and uncertainties to improve. However, this led to a good point. Due to the lack of data, the study finds a method for estimating emissions that can cope with the lack of data or the lack of funds to obtain specific details. This can become helpful for management implications and decision makers. The equation formed by using linear regression analysis and T-test analysis based on a general boat data, have shown that only the engine power (often easiest to obtain when compared to other engine specifications) and the length of boat is needed to estimate fuel consumption rates. When applied with the emissions data provided and the boating behavior regarding space and time within Sweden in general, quantifiable emissions estimations are obtainable where various factors of boats are taken in to consideration. The model provided can assist in scenarios studies when various policies are to be determined or when various management practices are to be tested upon.

Although, currently the emissions of boats in total in Koster and Sweden are relatively small when compared to the total emissions from the transport sector as a whole, boat engines’ emissions are relatively equivalent to trucks and would become an environmental problem as the number of boats grew. A study of the growth in boating population would need to be further study in order to predict impact growths in the future.

6.0 Conclusion

This project has conducted 3 main investigations on recreational boating with the objective to understand possible environmental implications of recreational boating. The first investigation involved performing a life cycle inventory analysis of recreational boating, where recreational boating is seen as a major process with subprocesses including Recreation, Electric Power Generation, Antifouling, and Combustion from boat engines. Each subprocesses have various environmental implications. The impacts from electric power generation weren’t investigated since the process was identified at the end of the project and hence would require more time and resources. Environmental implications due to recreation involved nutrient loading and physical impacts of boating related activities. Although littering have been left out in this investigation, but signs of littering are not so high. In addition, there were garbage sites near harbors for litter deposits, and has been often found to be in constant use. Hence littering in to the ocean was assumed to be unlikely at most times, but in order to claim whether littering will become a problem require a detailed study where extensive observations and questionnaire would be involved. Boating and its related activities can also cause physical damages to benthic and inter-tidal ecosystems. This can be prevented through zoning management. Antifouling on the other hand has a more complex situation where the use of TBT is prohibited, but are still leaching from boats after boat wash. Solutions to this would involve the monitoring and providing guidelines for boat cleaning businesses. Environmental Implications due to combustion is complex in many ways. The complexity is due to the nature of which the combustion takes place within each engine, the types of available engines. In addition, there are myriads of fuel types available for consumption. The complexity is enhanced by the fact that often a solution to a problem of engine’s combustion would often lead to a new problem. In addition, sometimes the use of environmental friendly products may not help the environment at all. In general, environmental implications of recreational boating are similar to other types of automobiles where the release of NOx, HCs, COx, VOCs, and fuel additives is the main environmental concern.

In Conclusion, there are many environmental implications of recreational boating. These include a variety of environmental problems ranging from release of toxic contaminants to urban air pollution problems. The study was able to semi quantitatively analyzed the emissions from recreational boating and environmental concerns involved but predicting environmental impacts became a challenge. Data collection was made mainly through literature search in text books and scientific journals, and through various contacts at many levels of the society. The environmental impacts involved have been considered by looking up various theories related to the emissions involved and the processes leading to the emissions obtained. The result of this study has led to a simple fuel consumption prediction model that can be implemented by various members of the society. In general, it is concluded that there are many environmental problems related to recreational boating but its significance has been clouded. This is however a great concern since Koster is a marine national park as of 2009, hence may lead to a possible increase in the number of visitors and leading to increase in the amount of pollutions emitted. Thus, making recreational boating a significant issue to be determined and should not be ignored by the authoritative body of Koster.

7.0 Acknowledgement

This project would not have been possible without the aid of various persons and institutions. This project would like to credit KTH for assisting in providing resources, materials, and some financial support in the process of making this project, Göteborg University and Tjärnö Marine biology laboratory for their resources and aerial photos, Stockholm University’s toxicity findings, The Swedish Environmental Institute (MVL) tests on engines and Far Eastern company for their financial support. This project would not have succeeded without the advices provided by Associate Professor and supervisor, Fredrik Gröndahl. Various information and data have been collected through various contacts from various parts of the society. Advices on environmental problems regarding Koster have been obtained through working with a marine biologist, Paulina Garza Martinez, Mahidol University’s Laird Allan, Assistant Professor Kobkaew Manomaipiboon and Dr. Wayne N. Phillips, and direct contacts with Lisbeth Jonsson, Per Nilsson, Tomas Lundälv, Anita Tullrot, Andrea Morf, Gunilla Trot and Martin Larsvik from Göteborg University. Data collection regarding the boating behavior in Sweden was obtainable through contacts with Misse Wester from the Royal Institute of Technology (KTH). Experimental results on toxicity have been provided by Associate Professor Britta Eklund from Stockholm University’s Department of Applied Environmental Sciences, whom has also provided the MVL’s engine tests’ report. The information regarding Koster would have not been possible without the assistance of the municipality of Strömstad. Information regarding boats’ register is obtained through direct contact with the Swedish sjöverket’s Katrin Sundholm. The Petroleum Authority of Thailand (PTT), which had worked with shipping and logistics industries, have provided assistance in providing information on how the company have assisted other companies in more environmental friendly methods at ports, and information on problems regarding petroleum’s chemical composition. This is done through contacting an employee named Kobkaeo Damri. Others whom have assisted in providing information regarding petroleum chemicals and other chemical engineering related issues include Thai Royal Army’s Dr. Soraj Pechsiri, chemical engineer Pennapa Jansongsri, chemical engineer Orelie Mahot and Construction Engineer Urmat Makulov from the Royal Institute of Technology (KTH). Mechanical related issues have been observed with the consulting of 2 mechanical engineers: Amir Sattari, and Sawayos Jaynutapong from the Royal Institute of Technology (KTH). This project would not have been succeeded without the assistance of Associate Professor Chaveevan Pechsiri from Dhurakijphundit University, whom have consulted in computer related issues and issues regarding data manipulation (especially when there is a lack of data), and Associate Professor Rapepun Piriyakul from Ramkhamhaeng University, whom provided consultancy on Statistical related issues. Consultations regarding mass balance analysis have been made with Associate Professor Bjorn Frostell and Lennart Nilsson. Observations and transportation was achievable through the assistance of the local ferry of Strömstad, and the region’s tourism industry which have provided information on Koster. Data on Volvo engines are obtained directly from the company’s contact. Lastly, consultations regarding Swedish translation and computer techniques are made with Ronja Kriche, Cristobal Viedma, and Nisarath Santisukdamrong from the KTH. Additional thanks to friends and family for their support.

8.0 Reference

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Appendix A Boats and Ships Registered with the Swedish Transport Agency

Boats: 1989 vessels ordered by type and length Width Length Call sign Name (m) (m) Machinery Type of ship SFC‐7506 ANIARA 3.70 11.50 Ford 2725 E ‐83 Fritidsegelmotorbåt SFC‐8622 MARMAR 3.35 11.28 Yanmar 3JH2TE Diesel Fritidsegelmotorbåt SFC‐8110 KASTRUP II 3.90 11.51 Volvo Penta LB‐100B, 1965 Fritidsfiskemotorbåt SFB‐9256 BRITT 3.00 8.40 Volvo Penta TAMD 31 Fritidsfiskemotorbåt SFB‐7538 JERRY 3.00 8.20 Fritidsfiskemotorbåt SFC‐7915 ELIDA 2.60 7.50 Penta 2030, 2001 Fritidsfiskemotorbåt SFC‐8623 SIGNE 2.60 7.10 Honda 90, 2008 Fritidsfiskemotorbåt SFC‐5984 HILMA 2.53 6.07 Ducati Fritidsfiskemotorbåt SFC‐7429 GOLUB 3.72 22.75 SCANIA DCI 11 ‐75 Fritidsmotorbåt SFC‐4471 SANTA MARIA 3.90 21.30 2 Scania D816 Fritidsmotorbåt SFC‐6383 3.80 21.00 Diesel 3D6 Fritidsmotorbåt SFC‐7789 VALEN 3.95 19.50 Ford 2710 1973 Fritidsmotorbåt SFB‐4763 EKOLN 3.70 18.52 Fritidsmotorbåt SFB‐4827 NAJADEN II 3.66 18.38 Volvo Penta MD 67C Fritidsmotorbåt SFC‐5128 SLUG 3.50 17.93 Volvo Penta MD96B Fritidsmotorbåt SFC‐7218 MUNTER 3.63 17.75 AB.Penta‐297 MD 96 Fritidsmotorbåt SFB‐8334 ÖRNEN 3.53 17.58 Scania DSI‐II, 1963 Fritidsmotorbåt SFC‐3432 TUMLAREN 3.96 17.50 Scania DSI10 Fritidsmotorbåt SFC‐4725 HURTIG 3.85 17.50 Volvo Penta MD96 1960 Fritidsmotorbåt SFC‐8893 CRI‐MA‐HE 3.96 17.50 Perkins Fritidsmotorbåt SFC‐7202 RAGNHILD 3.85 17.16 Scania DS 11, 1987 Fritidsmotorbåt SFB‐6673 BOLLSTA 3.76 16.90 Cat P 342 T Fritidsmotorbåt SFC‐3646 SVK 1 3.90 16.90 Scania Vabis Fritidsmotorbåt SFC‐7168 ÅRÅS 3.86 16.53 Seffle S10BF, 1951 Fritidsmotorbåt 68

SFB‐4780 KUNGSHOLM 3.31 15.58 Albin Fritidsmotorbåt SFB‐5470 ASTRIDA 3.71 15.56 Albin Diesel 1957 6 cyl Fritidsmotorbåt SFB‐5758 DIANA 3.56 15.53 2 Scania Vabis DSI10 1961 Fritidsmotorbåt SFC‐7068 VALEN 3.60 15.30 Ford 6 cyl 2714E, 1972 Fritidsmotorbåt SFC‐7748 ATLAVIK RE‐159 3.93 15.28 Scania DSI‐11, 1984 Fritidsmotorbåt SFB‐6807 FAXE 3.56 15.13 Volvo Penta TMD96 Fritidsmotorbåt SFB‐6368 TOY 3.80 15.08 Volvo Penta TMD96 Fritidsmotorbåt SFB‐8951 HJORTEN 3.30 15.00 Ford Mermaid,turboplus 88 Fritidsmotorbåt SFB‐6501 MYRA 3.99 15.00 Volvo D47 Fritidsmotorbåt SFB‐4787 SKOGHALL I 3.78 14.98 Volvo Penta TMD96B 1957 Fritidsmotorbåt SFB‐5339 MÄLARÖ 3.85 14.91 Säffle 3 cyl 327 EV Fritidsmotorbåt SFB‐6726 EBBA 3.40 14.69 Scania 6‐cyl Fritidsmotorbåt SFB‐4765 BJÖRN 3.87 14.66 Bolinder‐Munktell 1951 Fritidsmotorbåt SFB‐6634 NALLE 3.97 14.56 Volvo Penta TMD96 Diesel Fritidsmotorbåt SFC‐5597 STORSJÖN 3.60 14.50 Volvo MD67C Fritidsmotorbåt SFC‐6356 MY NANGIJALA 3.40 14.40 Volvo Penta 100A, 1967 Fritidsmotorbåt SFB‐5734 DRAGÖN 3.17 14.40 Skandia 265 C 1954 Fritidsmotorbåt SFC‐7052 SPJUTET 3.40 14.30 2 x TAMD70C, 1975 Fritidsmotorbåt SFC‐6534 TUNSTA 3.18 14.18 Scania Vabis Fritidsmotorbåt SFC‐8636 INKA 3.00 14.00 Cummins, 1991 Fritidsmotorbåt SFC‐3227 MIDNIGHT SUN 3.40 14.00 2 GM Detroit Fritidsmotorbåt SFC‐5138 JUNGFRUN 2.96 13.85 Ford Marin diesel 1981 Fritidsmotorbåt SFC‐5858 VINGOLF 3.97 13.70 Volvo TAMD 120B 1986 Fritidsmotorbåt SFB‐9066 NAUTILUS 3.90 13.50 Bolinder‐Munktell Fritidsmotorbåt SFC‐8289 YASURAGI 3.85 13.47 2 x Volvo Penta IPS600 Fritidsmotorbåt SFC‐4611 ALKA IV 3.70 13.40 2 Volov Penta TMD70 1970 Fritidsmotorbåt SFC‐7263 VIDAR 3.30 13.40 MD67 Snr 0443 Fritidsmotorbåt SFB‐8572 ERIKA II 3.91 13.29 Mercedes 352 Fritidsmotorbåt SFC‐4682 CORCAT 3.70 13.20 Ford Lehman Fritidsmotorbåt 69

SFC‐6301 EVY LINN 3.97 13.20 2 Scania Fritidsmotorbåt SFC‐8611 LILLA B 3.73 13.15 2 st VP TAMD74P Fritidsmotorbåt SFC‐5533 3.60 13.11 Perkins 1990 Fritidsmotorbåt SFC‐3839 GORM 3.92 13.05 Volvo Penta TAMD Fritidsmotorbåt SFC‐8771 ANKAN 3.80 13.04 2 x Volvo Tamd 75 P, Diesel, 2003 Fritidsmotorbåt SFC‐3749 MEATBALL III 3.98 13.00 2 Volvo Penta KAD42 1992 Fritidsmotorbåt SFB‐7921 EIAN 3.34 13.00 2 BMC Diesel Fritidsmotorbåt SFC‐7458 THIAL 3.90 12.95 2 Volvo Penta TAMD 75 P Fritidsmotorbåt SFB‐7652 LOMEN 3.95 12.85 Volvo Penta TMD70B 1973 Fritidsmotorbåt SFC‐3757 LELITA AF HUDIKSVALL 3.96 12.84 2 Detroit Diesel 1968 Fritidsmotorbåt SFC‐5947 ARGUS 3.20 12.50 2 Volvo Penta AD40 Fritidsmotorbåt SFC‐3561 LUDVIG 3.90 12.40 2 Volvo Penta TAMD6 Fritidsmotorbåt SFC‐5259 MIRAMIS II 3.80 12.30 2 Volvo Penta KAD42 1997 Fritidsmotorbåt SFC‐5843 MALAMBO 3.96 12.29 Cummins 1994 Fritidsmotorbåt SFC‐7333 PANDORA 3.35 12.27 Fritidsmotorbåt SFC‐4793 SANDRINA 3.96 12.25 2 Volvo Penta TAMD60B 81 Fritidsmotorbåt SFC‐6907 QUEEN S 3.84 12.20 2xKAD 300 EDC/DP ‐ G Fritidsmotorbåt SFC‐8041 ALBERTA 3.50 12.20 Peugeot, DTP 106 Fritidsmotorbåt SFC‐8825 REGINA 3.90 12.20 Volvo Penta, 2006 Fritidsmotorbåt SFC‐6107 CRYSTAL CRUISER 3.95 12.15 2 VP TAMD 70B Fritidsmotorbåt SFC‐8122 FRAGANCIA 3.91 12.09 2xVolvoPenta TAMD70E Fritidsmotorbåt SFC‐5827 BAHAMA MAMA 3.91 12.09 TAMD 71A VP, 1987 Fritidsmotorbåt SFC‐7155 CUBA LIBRE 3.91 12.04 Volvo Penta GJP, 2003 Fritidsmotorbåt SFC‐5995 CHRISTINA 3.75 12.00 Volvo Penta MD 1975 Fritidsmotorbåt SFC‐5298 LINA 3.70 12.00 Perkins range 4, 1980 Fritidsmotorbåt SFC‐3945 HEUREKA 3.75 12.00 2 Volvo TAMD60 1975 Fritidsmotorbåt SFC‐7966 VIKING 3.85 12.00 2 Volvo TMD45 1970 Fritidsmotorbåt SFB‐7763 REBECKA 3.55 12.00 Volvo TD 70 Fritidsmotorbåt SFB‐6543 BJÖRN I 3.35 12.00 Volvo Penta MD70 1977 Fritidsmotorbåt 70

SFC‐7120 KAJENNE 3.76 11.98 Volvo AQ41A, 1992 Fritidsmotorbåt SFC‐4363 RELAX 4.27 11.96 2 Volvo Penta TAMD61 Fritidsmotorbåt SFB‐6512 SAVONA 3.97 11.95 Tempest sealord 1980 Fritidsmotorbåt SFC‐8650 ÄLGSKÄR 3.50 11.90 2 KAD 300, 2003 Fritidsmotorbåt SFC‐7353 JIANELI 4.43 11.90 2xVolvo Tamd 74P,2001 Fritidsmotorbåt SFC‐6369 3.20 11.90 2 Mercruiser, 1988 Fritidsmotorbåt SFC‐4744 SUNFIRE 3.04 11.88 2 Mercruiser INU Fritidsmotorbåt SFC‐5082 YVETTE 3.50 11.85 Volvo Penta TMD40 1982 Fritidsmotorbåt SFC‐4091 LAURA 4.18 11.85 Scania D442E3751 1965 Fritidsmotorbåt SFC‐3897 KENILU 3.85 11.80 Mercedes 180 diesel Fritidsmotorbåt SFC‐3563 LA PETITE 3.80 11.80 2 Volvo Penta TAMD41 Fritidsmotorbåt SFB‐8400 OLLE 3.00 11.80 Scania DSI 10 1969 Fritidsmotorbåt SFC‐3401 JONICA 3.50 11.75 Volvo Penta MD‐30 Fritidsmotorbåt SFC‐8730 WHITE LADY 3.50 11.60 DAAF, 1980 Fritidsmotorbåt SFC‐8704 POLARIS 3.50 11.52 Yanmar Fritidsmotorbåt SFC‐6326 TOFFI 3.95 11.51 2 Volvo Penta TAMD Fritidsmotorbåt SFC‐4133 LACOM III 4.27 11.47 2 Volvo Penta 61A 1988 Fritidsmotorbåt SFB‐8604 TRACY 4.50 11.40 Hundestedt 1971 Fritidsmotorbåt SFC‐5783 NORVIK 3.65 11.40 Perkins 4.236 Marin 1966 Fritidsmotorbåt SFC‐5249 FREEDOM 3.86 11.23 2 John Deer 1975 Fritidsmotorbåt SFC‐8887 LILLY MAJ 3.60 11.20 2 Volvo Penta TAMD 40 B, 1986 Fritidsmotorbåt SFC‐7785 FOLLY 3.60 11.20 TAMD 42A, 1993 Fritidsmotorbåt SFB‐5202 INDIGO 2.60 11.20 Bolinder 2053 1961 Fritidsmotorbåt SFC‐3584 NN 3.60 11.20 2 Volvo Penta TAMD41 Fritidsmotorbåt SFB‐4423 TONGA 4.20 11.20 Volvo Penta MD67 Fritidsmotorbåt SFB‐2307 FANNY ALBA 3.96 11.15 Volvo Penta TMD70 1978 Fritidsmotorbåt SFC‐3263 DO UT DES 3.71 11.07 2 John Deere 404 Fritidsmotorbåt SFC‐4077 CONTOY 3.80 11.00 Volvo Penta MD47B 1976 Fritidsmotorbåt SFC‐4178 GERIK II 3.90 11.00 Twin Cummings 6BT5.9 Fritidsmotorbåt 71

SFC‐5422 CITO IV 5.45 11.00 Volvo Penta KAD42A 1992 Fritidsmotorbåt SFC‐8335 KATALIN 3.05 10.97 Volvo Penta TMD 40 A Fritidsmotorbåt SFC‐5655 ANNIKA 3.84 10.97 Ford Tempest diesel Fritidsmotorbåt SFC‐8372 TRINDA 3.10 10.94 Perkins Fritidsmotorbåt SFC‐2591 BATAVIA 2 3.35 10.94 Volvo AQD32A/280 Fritidsmotorbåt SFC‐8014 DOLCE VITA 3.40 10.94 2 VolvoPentaKAD300,2004 Fritidsmotorbåt SFC‐8204 SVK 02 2.80 10.90 Fritidsmotorbåt SFC‐8205 SVK 03 2.80 10.90 Fritidsmotorbåt SFC‐8071 OCEAN STAR 3.50 10.85 Ford 2720 Fritidsmotorbåt SFC‐7295 NJORD 3.50 10.85 Perkins Range 4 M135,1988 Fritidsmotorbåt SFC‐2486 SALOFSIE 3.50 10.85 Ford 703‐F8582 1974 Fritidsmotorbåt SFB‐4776 WILMO 4.48 10.82 Albin Fritidsmotorbåt SFC‐8419 NORTECH 3600 3.60 10.80 2 x MRD Fritidsmotorbåt SFC‐6524 MARNAT 3.50 10.80 2 OMC‐460, 1988 Fritidsmotorbåt SFB‐2275 CRESTON 4.50 10.80 Volvo Penta Fritidsmotorbåt SFC‐6589 SEA GULL 3.80 10.80 2 X Volvo Penta TAMD60,80 Fritidsmotorbåt SFC‐7159 SAZY 3.05 10.76 VP2003, 1986 Fritidsmotorbåt SFC‐7229 NIAN 3.50 10.75 Yanmar,6LY2A‐STP,‐04 Fritidsmotorbåt SFC‐7054 PRINCESS EVA 3.68 10.74 Cummins TA 358, 1990 Fritidsmotorbåt SFC‐6882 KORPEN 2.83 10.70 Volvo MD 40, 1988 Fritidsmotorbåt SFC‐8100 MARLENE 3.50 10.68 VP TAMD 61 A, 1992 Fritidsmotorbåt SFC‐6198 BLUEBONNET 3.37 10.67 Twin Ford Lehman diesel Fritidsmotorbåt SFC‐6924 PHILEAS 3.80 10.62 VP 2003, 1993 Fritidsmotorbåt SFC‐6466 3.53 10.60 2 Mercruiser 5,0EFI 2002 Fritidsmotorbåt SFC‐3860 TRANSIENT 8.00 10.60 Fritidsmotorbåt SFB‐4336 KOH‐I‐NOOR 3.50 10.60 Ford 2.715‐E 6 cyl. Fritidsmotorbåt SFC‐6287 FAIR LADY 3.80 10.60 Volvo Penta 271 87 Fritidsmotorbåt SFC‐6539 JUNO III 3.55 10.60 2 X KAD 300, 2002 Fritidsmotorbåt SFC‐3713 RONJA II 3.55 10.60 2 Volvo Penta Fritidsmotorbåt 72

SFC‐8701 WOLF 3.97 10.57 Hino250, 1995 Fritidsmotorbåt SFC‐3655 RASSY BRAVO 1.63 10.54 Volvo Penta Fritidsmotorbåt SFC‐3672 PATRICIA 3.50 10.50 Volvo Penta TAMD60 Fritidsmotorbåt SFC‐3935 DAPHNE 3.70 10.50 2 Volvo Penta TAMD40 Fritidsmotorbåt SFB‐7185 MICA 3.18 10.44 Perkins 4.236 diesel Fritidsmotorbåt SFC‐6281 GITTE 3.73 10.42 Volvo Penta TMD100A Fritidsmotorbåt SFC‐7114 SANDRA 3.30 10.40 Volvo MD47, 1980 Fritidsmotorbåt SFC‐6847 DHAMMA 3.20 10.35 2xTAMD60B, 1982 Fritidsmotorbåt SFC‐3879 MADAME OTT 3.50 10.35 2 Volvo Penta diesel Fritidsmotorbåt SFC‐3906 LADY S 3.20 10.35 Volvo Penta TMD41MS4 1988 Fritidsmotorbåt SFC‐2952 GOING 3.20 10.35 2 Perkins 1973, 1984 Fritidsmotorbåt SFC‐8436 LADY GE 3.20 10.35 2 Perkins T6 354M, 1974 Fritidsmotorbåt SFB‐9049 SORAYA 4 3.30 10.35 Volvo Penta PAMD 60 Fritidsmotorbåt SFC‐4809 3.77 10.23 Volvo Penta TAMD41B Fritidsmotorbåt SFB‐4420 MARINA 3.90 10.20 Fritidsmotorbåt SFC‐8258 3.19 10.19 VP AQAD40B, 1984 Fritidsmotorbåt SFC‐7293 LAGUN 3.85 10.18 Ford Diesel Fritidsmotorbåt SFB‐6677 LIMANDA 3.20 10.15 Perkins V 8 510 1980 Fritidsmotorbåt SFB‐7004 4.05 10.10 Ford diesel NG6‐2715 1981 Fritidsmotorbåt SFC‐4074 FELICIA AF LIMHAMN 3.81 10.10 Fritidsmotorbåt SFC‐5436 SISU 3.41 10.06 Cummins diesel 1996 Fritidsmotorbåt SFC‐7450 SURVIVAL 3.40 10.06 Volvo Penta 40B ‐84 Fritidsmotorbåt SFC‐4043 TRENTO 3.30 10.00 Volvo Penta MD40 Fritidsmotorbåt SFC‐3580 3.20 10.00 Volvo Penta Fritidsmotorbåt SFB‐4155 INGEGÄRD 3.50 10.00 Bolinder Fritidsmotorbåt SFC‐5220 ARNLJOT II 3.40 10.00 Volvo Penta PRO 41/290DP Fritidsmotorbåt SFC‐6614 CARPE DIEM 3.30 10.00 Volvo Penta TMD31,1990 Fritidsmotorbåt SFC‐8112 FREJA 3.30 10.00 2 Volvo Penta AD41B,1992 Fritidsmotorbåt SFB‐4428 ANITA 3.60 10.00 Volvo Penta D 67 Fritidsmotorbåt 73

SFB‐4412 BRITT 3.60 10.00 Fritidsmotorbåt SFB‐7441 MARIA 3.60 10.00 Albin O 41 Fritidsmotorbåt SFC‐6825 JUANITA 3.00 9.95 NanniDiesel 3.75HE,1999 Fritidsmotorbåt SFB‐4056 ANITA 3.60 9.90 Fritidsmotorbåt SFB‐2944 SONETTE 3.60 9.90 Fritidsmotorbåt SFC‐8046 IOR 4.00 9.85 Mercury, 2004 Fritidsmotorbåt SFC‐7045 SUN BRIS 3.35 9.85 Cummins 6BTA59m2,1991 Fritidsmotorbåt SFB‐5236 ERNA‐MARI 3.60 9.80 Sabb F4 254 MVP 1976 Fritidsmotorbåt SFC‐8386 DEMITE 2.45 9.80 ATM‐TD, 2003 Fritidsmotorbåt SFC‐7400 INGA 3.30 9.79 Yanmar 6LY‐UTE, 1999 Fritidsmotorbåt SFC‐5537 KINGSTON 2.83 9.78 Hundestedt Fritidsmotorbåt SFC‐6654 ALEXANDRA 3.58 9.75 2 X Volvo Penta, 1996 Fritidsmotorbåt SFC‐5588 OFFA 3.40 9.70 Volvo Penta KAD 44P 1998 Fritidsmotorbåt SFC‐2617 CAROLINE 3.18 9.62 2 PRO 40 Volvo Fritidsmotorbåt SFB‐9979 HELGA 3.50 9.60 Volvo Penta MD30 1987 Fritidsmotorbåt SFB‐8340 GURKAN 3.23 9.60 Volvo Penta AQAD 1982 Fritidsmotorbåt SFB‐4333 ANDROS 3.30 9.60 Fritidsmotorbåt SFC‐2706 NAUTILUS 31 3.50 9.60 BMW D 50 1982 Fritidsmotorbåt SFC‐7163 MY TOY 3.25 9.50 2 Volvo, 1984 Fritidsmotorbåt SFC‐8354 SWEET LANA 2.87 9.47 Volvo KAD300, 2005 Fritidsmotorbåt SFC‐7121 PÄRLAN II 3.00 9.45 Yanmar 3GM, 1987 Fritidsmotorbåt SFB‐4435 3.40 9.40 Fritidsmotorbåt SFB‐2941 ZENITA 3.70 9.30 Volvo Penta 1973 Fritidsmotorbåt SFC‐3842 ORCA 3.20 9.30 AQAD40B 1984 Fritidsmotorbåt SFC‐4986 NINA 3.20 9.30 Volvo Penta TAMD40A 1982 Fritidsmotorbåt SFC‐7266 TIGER NILES 3.20 9.30 TMD 40 Fritidsmotorbåt SFC‐6749 @CE VENTURA 3.20 9.30 2 Inombords, 1984 Fritidsmotorbåt SFC‐8377 KONTES 3.35 9.27 Fritidsmotorbåt SFC‐7185 2.71 9.26 Marna M2, 1959 Fritidsmotorbåt 74

SFC‐3838 BOUMIAN 2.70 9.26 Sabb Fritidsmotorbåt SFC‐3524 MIRO 3.20 9.20 Volvo Penta TAMD41 Fritidsmotorbåt SFB‐6993 FALKEN 3.36 9.20 Tempest 6 cyl Fritidsmotorbåt SFC‐6791 GALENE 3.00 9.20 Volvo AD41A290DP,‐90 Fritidsmotorbåt SFC‐2563 ACAPPELLA 3.00 9.20 AQAD41/290DP 1990 Fritidsmotorbåt SFC‐5414 JUNE 3.10 9.15 TAMD70 1997 Fritidsmotorbåt SFB‐6581 TOVA 3.18 9.15 Bolinder Munktell Fritidsmotorbåt SFC‐7167 BUBBLE GUM 3.23 9.14 Mercury, 2003 Fritidsmotorbåt SFC‐4631 BARTMANN 2.57 9.14 Volvo Penta TMD31 Fritidsmotorbåt SFC‐4626 SEA RAY 270 DA 2.59 9.12 Mercruiser 4,3L Fritidsmotorbåt SFC‐3434 SOL‐GUN 2.65 9.10 Volvo Penta MD50A 1967 Fritidsmotorbåt SFB‐4202 SIV 3.30 9.10 Albin Marin AD‐2 1962 Fritidsmotorbåt SFB‐4057 HELENA 4.00 9.00 Säffle Fritidsmotorbåt SFB‐2744 3.40 9.00 Ford Fritidsmotorbåt SFB‐3656 4.15 9.00 Fritidsmotorbåt SFB‐6479 DROTT 2.53 9.00 BMC Commander Fritidsmotorbåt SFC‐2732 MARIA 3.60 9.00 Skandia diesel Fritidsmotorbåt SFC‐2798 WESTÖ 3.15 9.00 BMC Sea Lord 82 Fritidsmotorbåt SFC‐3649 KALLE 2.83 9.00 Volvo Penta D50A Fritidsmotorbåt SFC‐3386 SEA FOR TWO 2.85 9.00 Volvo Penta Fritidsmotorbåt SFC‐3652 SYDÖ 3.10 9.00 Perkins Fritidsmotorbåt SFB‐5258 FLOURICH 3.00 9.00 MD 42 A 1974 Fritidsmotorbåt SFB‐2096 3.00 9.00 Fritidsmotorbåt SFB‐5824 MARICA 3.50 9.00 Volvo Penta 6152MD3B 1975 Fritidsmotorbåt SFC‐3465 FLICWA IV 2.80 8.99 2 Volvo Penta AQ271C Fritidsmotorbåt SFC‐2477 POPEYE 2.70 8.96 Volvo Penta TMD40 1983 Fritidsmotorbåt SFB‐2969 SILVIA 2.70 8.90 Albin Fritidsmotorbåt SFB‐8925 LADY LUSTA 3.20 8.90 2 st Volvo Penta 1988 Fritidsmotorbåt SFC‐2969 BERIT 2.90 8.90 TAMD 31 1989 Fritidsmotorbåt 75

SFC‐4895 ALPHA 2.43 8.90 Mercruiser 4,7l Fritidsmotorbåt SFC‐8197 BIANCA 3.00 8.90 Volvo Penta KADYY P‐6,‐02 Fritidsmotorbåt SFB‐9513 LINDA 3.00 8.85 Isuso, 1987 Fritidsmotorbåt SFB‐6234 SIRENE 2.67 8.85 Perkins T6354 1978 Fritidsmotorbåt SFB‐3661 FRIDA 3.65 8.85 Perkins Fritidsmotorbåt SFB‐9631 2.70 8.80 Mercedes, 1982 Fritidsmotorbåt SFB‐7945 INGEBORG 3.27 8.80 Yanmar 1984 Fritidsmotorbåt SFB‐4047 GLITTRAN 3.50 8.80 Bolinder‐Munktell Fritidsmotorbåt SFC‐3634 CHESS 3.28 8.80 Volvo Penta AQAD‐40B Fritidsmotorbåt SFC‐3521 LA ROSSA 2.60 8.78 2 Riva 350 CV Fritidsmotorbåt SFB‐5026 JENNY 3.40 8.75 Ford 1968 Fritidsmotorbåt SFB‐3517 3.20 8.75 Sabb Fritidsmotorbåt SFC‐3615 ZABA 3.00 8.75 Volvo Penta Fritidsmotorbåt SFC‐3687 TERESIA 3.00 8.75 Volvo Penta AD41 Fritidsmotorbåt SFB‐2067 BILLAN 3.33 8.75 BSM Skandia Fritidsmotorbåt SFB‐6398 SUNNSKÄR 3.05 8.75 Ford Diesel 1979 Fritidsmotorbåt SFB‐7162 AMMY 3.40 8.75 BMW D 50 1981 Fritidsmotorbåt SFC‐3333 LIRBERTY 2.70 8.71 Wizeman 36 Fritidsmotorbåt SFB‐4951 MERCI 3.70 8.70 Hundested Fritidsmotorbåt SFB‐6107 RIMMON 3.05 8.70 Volvo Penta MD40 1979 Fritidsmotorbåt SFB‐6851 VÅGEN 3.27 8.70 Yanmar 1979 Fritidsmotorbåt SFB‐6149 3.00 8.70 BM diesel Fritidsmotorbåt SFC‐4021 SOLENA 2.98 8.70 Cummins V8185M 1969 Fritidsmotorbåt SFC‐8319 ELLA 3.15 8.66 Ford Sabb, 1978 Fritidsmotorbåt SFC‐3760 DUGA 3.00 8.65 Sabb 4JHR ‐81 Fritidsmotorbåt SFC‐7268 JESSICA 2.98 8.62 2 x Volvo Penta‐KAD42 Fritidsmotorbåt SFC‐3769 MARIANNE 2.75 8.60 Ford 2722E Fritidsmotorbåt SFC‐3772 OBELIX 2.70 8.60 Volvo‐Penta MD4 1968 Fritidsmotorbåt SFB‐7462 EVAMARI 2.75 8.60 Ford Fritidsmotorbåt 76

SFB‐7760 EFFENDI 2.75 8.60 Ford 2712E 4 cyl 1981 Fritidsmotorbåt SFC‐6296 SEA WIND 3.10 8.60 Yanmar 6LPSTE Fritidsmotorbåt SFC‐7032 JOHANNA II 3.04 8.56 VP KAD 44 P‐C Fritidsmotorbåt SFC‐8773 2.59 8.53 Fritidsmotorbåt SFC‐4195 MERIT 2.82 8.52 Volvo MD32 1977 Fritidsmotorbåt SFB‐5807 3.00 8.50 Yanmar 2 SM 20 1976 Fritidsmotorbåt SFB‐2153 YVETTE 2.80 8.50 Fritidsmotorbåt SFB‐2158 GITSY 3.00 8.50 Fritidsmotorbåt SFB‐4383 RANHI 3.30 8.50 Fritidsmotorbåt SFC‐2595 RULLANGÅR 3.00 8.50 Bolinder M 62511022 1958 Fritidsmotorbåt SFB‐4993 3.10 8.50 Säffle 1952 diesel Fritidsmotorbåt SFB‐2674 KAJSA 2.75 8.50 Fritidsmotorbåt SFC‐4183 VICTORIA 2.90 8.50 Volvo Penta KAD 42 1992 Fritidsmotorbåt SFB‐4038 ELINA AF MÖJA 3.10 8.50 Ford Diesel Fritidsmotorbåt SFC‐7906 LA CAOTICA 2.70 8.45 6LPA‐STZP, 2002 Fritidsmotorbåt SFB‐7371 MARIA 2.85 8.45 Perkins H 108M 1977 Fritidsmotorbåt SFC‐7442 SJÖGLIMT 2.85 8.45 TAMD 31 Volvo Penta Fritidsmotorbåt SFC‐5567 CAVATINA 3.05 8.41 Cobra 460OMC Fritidsmotorbåt SFB‐9992 DEMITRA 3.00 8.40 Mercedez Benz 190 1965 Fritidsmotorbåt SFB‐8206 ANDREA 3.20 8.40 Mitsubishi S6E2 Fritidsmotorbåt SFC‐8863 JOY 2.55 8.40 Singel Volvo Penta KAD 44, 2000 Fritidsmotorbåt SFB‐8746 AUSI 3.00 8.40 Volvo Penta TAMD30 1986 Fritidsmotorbåt SFB‐7232 LINDA 3.00 8.40 Sabb 1976 Fritidsmotorbåt SFC‐3516 3.20 8.40 Yanmar 4JH2DTE Fritidsmotorbåt SFC‐8182 MJOLNER 2.95 8.36 Iveco 8141, 1992 Fritidsmotorbåt SFB‐4399 BIRGIT 2.70 8.30 Yanmar diesel Fritidsmotorbåt SFB‐6278 VIKING 3.40 8.30 Volvo Penta MD17C Hydro Fritidsmotorbåt SFC‐2813 MALIN 2.85 8.30 Volvo TAMD41/MS4 Fritidsmotorbåt SFB‐3636 RAMONA 3.10 8.30 Fritidsmotorbåt 77

SFB‐4130 2.60 8.30 Fritidsmotorbåt SFC‐4851 LOVISA III 2.93 8.30 Mercruiser Diesel Fritidsmotorbåt SFC‐5358 HARD‐NUT 2.97 8.30 2 Aifo Fiat 1980 Fritidsmotorbåt SFC‐3585 2.59 8.28 Mercruiser Fritidsmotorbåt SFC‐3660 FIFTY‐FIFTY 3.00 8.25 Volvo Penta TAMD40 Fritidsmotorbåt SFB‐7608 DEBBIE 3.00 8.25 Sabb Fritidsmotorbåt SFC‐8890 VEGA 912 2.46 8.25 Volvo Penta 2010, 1999 Fritidsmotorbåt SFC‐4060 GINNIE 3.05 8.25 Volvo Penta TAMD41A 1989 Fritidsmotorbåt SFC‐8738 PILEN 2.46 8.25 BETA MARINE BZ 48Z, 2007 Fritidsmotorbåt SFC‐3508 TERESA 2.59 8.23 OMC Cobra Stern Fritidsmotorbåt SFB‐9028 SUSA I 2.80 8.20 Volvo Penta MD 21 1978 Fritidsmotorbåt SFB‐6782 ORION 2.90 8.20 Perkins 4‐108 1980 Fritidsmotorbåt SFB‐6963 MERITA 3.00 8.20 MD47A Fritidsmotorbåt SFB‐7097 VIGGEN 2.90 8.20 Ford 2712 1984 Fritidsmotorbåt SFC‐8555 ALCHEMY 3.00 8.20 Volvo Penta D3, 2005 Fritidsmotorbåt SFC‐5558 XIPHOIDEA 3.12 8.20 Perkins M 20, 1990 Fritidsmotorbåt SFB‐8837 RIMSÖ 3.00 8.20 Volvo Penta Fritidsmotorbåt SFB‐8863 SVALAN 3 3.15 8.20 Bukh DV36 1986 Fritidsmotorbåt SFB‐8075 RIO 2.70 8.20 Penta MD 19 1970 Fritidsmotorbåt SFB‐5604 JESSICA AF TORSÖ 3.30 8.20 Yanmar 1977 Fritidsmotorbåt SFB‐4391 TÄRNÖ 3.30 8.20 Västervik Fritidsmotorbåt SFB‐4392 RAUKEN 3.30 8.20 Fritidsmotorbåt SFB‐7770 3.15 8.15 Yanmar 2QM20 1976 Fritidsmotorbåt SFC‐4281 NIMBA 3.10 8.15 Volvo Penta MD40 1982 Fritidsmotorbåt SFC‐7881 ALFHILD 2.75 8.15 MD 17C, 1973 Fritidsmotorbåt SFC‐5730 SENAPSON 2.85 8.10 Yanmar 1990 Fritidsmotorbåt SFC‐5455 CALVIN 2.55 8.10 Mercruiser D‐Tronic 250 Fritidsmotorbåt SFC‐4720 2.70 8.10 Fritidsmotorbåt SFB‐7858 STENSKÄR 3.00 8.10 Volvo Penta TMD30 Fritidsmotorbåt 78

SFB‐9084 ERICA 2.65 8.10 Volvo Penta TDM 40 Fritidsmotorbåt SFB‐8769 ELVIRA 3.00 8.10 Volvo Penta MD40 1977 Fritidsmotorbåt SFB‐9603 EVELIN 3.15 8.10 Bolinder 1114BR Fritidsmotorbåt SFB‐7016 MALIN 3.10 8.10 Sabb 1981 Fritidsmotorbåt SFC‐4654 2.98 8.10 Volvo Penta MD40 1983 Fritidsmotorbåt SFB‐3109 ANNIKA 3.03 8.05 BM 1052E11361 Fritidsmotorbåt SFC‐6804 2.76 8.03 Yanmar 2GM20F Fritidsmotorbåt SFC‐8633 BRENDAN 2.76 8.03 Volvo Penta MD 2010 C Fritidsmotorbåt SFB‐5036 MARIA 2.80 8.00 Volvo Penta 1974 Fritidsmotorbåt SFB‐3967 FRAM 3.00 8.00 Fritidsmotorbåt SFB‐2083 3.00 8.00 Seffle FV 17 Fritidsmotorbåt SFB‐2591 RIMMON 3.80 8.00 Fritidsmotorbåt SFB‐2655 ANNE 2.50 8.00 Fritidsmotorbåt SFB‐3486 SABBINA 2.80 8.00 Fritidsmotorbåt SFB‐3493 LATIKA 3.00 8.00 Seffle Fritidsmotorbåt SFB‐9456 CARPE DIEM 3.00 8.00 Sabb diesel 2JHVP Fritidsmotorbåt SFB‐9503 JESSICA 2.85 8.00 Volvo Penta MD 31 Fritidsmotorbåt SFC‐3264 GLAUCUS 2.40 8.00 Albin AD21 Fritidsmotorbåt SFB‐8117 TERESA 2.80 8.00 Volvo Penta MD21 1984 Fritidsmotorbåt SFB‐7684 MANDA 2.85 8.00 Volvo Penta MD21 1983 Fritidsmotorbåt SFB‐7759 SIROCCO 2.80 8.00 Volvo Penta TMD30 Fritidsmotorbåt SFC‐4598 MAJVOR 2.80 8.00 Volvo Penta 1984 Fritidsmotorbåt SFB‐3709 2.50 8.00 Fritidsmotorbåt SFC‐2560 ULSTER 2.40 8.00 Volvo Penta MD4 081638 Fritidsmotorbåt SFB‐7765 HELENE 2.65 8.00 Volvo Penta MD3 Fritidsmotorbåt SFB‐8451 2.80 8.00 Volvo Penta TMD30 Fritidsmotorbåt SFC‐3204 TREO 3.01 8.00 Sabb Marin 1992 Fritidsmotorbåt SFC‐2878 HURTIG 2.80 8.00 Volvo Penta TAMD31B Fritidsmotorbåt SFB‐7523 VINITA 1.50 8.00 16 H Volvo Penta Fritidsmotorbåt 79

SFB‐8996 BARON 2.80 8.00 Perkins 4108 1986 Fritidsmotorbåt SFB‐2855 3.00 8.00 Albin diesel Fritidsmotorbåt SFB‐6109 SOFIA 2.85 8.00 Perkins 4108 Fritidsmotorbåt SFB‐3826 FLIPPER 2.70 8.00 Fritidsmotorbåt SFC‐7761 DELFIN 2.59 7.98 2 Mercruiser V6 175,1989 Fritidsmotorbåt SFC‐3659 SIROCCO 2.75 7.95 Volvo Penta Fritidsmotorbåt SFC‐8002 LOUISE 2.90 7.95 OMCT72407, 1988 Fritidsmotorbåt SFC‐3277 RONJA 2.60 7.95 Volvo Penta Fritidsmotorbåt SFC‐8614 ANGEL STAR 2.59 7.92 Mercruiser, 2007 Fritidsmotorbåt SFB‐2815 SYLVIA 2.74 7.92 Fritidsmotorbåt SFB‐4431 SANNA 3.00 7.92 Volvo Fritidsmotorbåt SFC‐5145 LOVA 2.53 7.91 Volvo Penta Fritidsmotorbåt SFB‐9589 ORION 3.00 7.90 Skandia, 1952 Fritidsmotorbåt SFB‐6087 MARITA 2.75 7.90 Lister luftkyld diesel Fritidsmotorbåt SFC‐5278 2.59 7.86 Volvo Penta 200/280 1981 Fritidsmotorbåt SFC‐5243 MARIANNE 2.59 7.86 Volvo Penta 200D 1983 Fritidsmotorbåt SFB‐6655 NORDÖ 2.83 7.85 Perkins 1980 Fritidsmotorbåt SFB‐7964 RÅÖ 2.85 7.85 Volvo Penta MD29 Fritidsmotorbåt SFC‐5943 BJÖRN 3.00 7.85 Mercedes Fritidsmotorbåt SFB‐5880 INGER 2.75 7.80 Perkins 4.108 M diesel Fritidsmotorbåt SFB‐7015 KOOKABURRA 2.75 7.80 VP MD17HD 1981 Fritidsmotorbåt SFC‐3865 AURORA FRANSSON 2.60 7.80 Yanmar 1981 Fritidsmotorbåt SFC‐2243 BIRGIT 2.65 7.80 Volvo MD3 1980 Fritidsmotorbåt SFB‐7495 ALDEBARAN 3.00 7.80 Sabb diesel 2 cyl 1981 Fritidsmotorbåt SFB‐3697 2.55 7.80 Fritidsmotorbåt SFB‐5548 ERMA 3.20 7.80 Yanmar Diesel 77 Fritidsmotorbåt SFB‐6151 LINDÖ 2.80 7.80 Perkins 4.108 M 1976 Fritidsmotorbåt SFB‐6193 RAMONA 2.60 7.80 Volvo Penta 1975 Fritidsmotorbåt SFB‐5721 BESSIE 2.99 7.78 Lister Fritidsmotorbåt 80

SFB‐9505 MÅSEN 2.65 7.75 Yanmar 2QM20, 1980 Fritidsmotorbåt SFB‐5013 ARCONA 2.70 7.70 Volvo Penta MD21A 1976 Fritidsmotorbåt SFC‐2523 SALTSKÄR 2.65 7.70 Volvo Penta MD21A 1980 Fritidsmotorbåt SFB‐6366 EVY 2.70 7.65 FM DA 22 1963 Fritidsmotorbåt SFC‐5199 LOVA 2.90 7.65 Volvo Penta AQAD40B 1983 Fritidsmotorbåt SFB‐6282 HANNA 2.78 7.62 Volvo Penta MD3 1979 Fritidsmotorbåt SFB‐2837 SVALAN 3.00 7.62 Albin diesel Fritidsmotorbåt SFB‐3487 NÄCKEN 3.20 7.61 BMC Marin 1500 Fritidsmotorbåt SFC‐6549 MAY BE III 2.60 7.60 Volvo Penta MD 2030 1994 Fritidsmotorbåt SFC‐4978 FISKAREFLICKAN 2.90 7.60 Mercruiser 95 Fritidsmotorbåt SFB‐3024 LOLA 2.80 7.60 Fritidsmotorbåt SFB‐4759 EMMA II 2.65 7.60 Volvo‐Penta MD 21 Fritidsmotorbåt SFB‐4381 2.40 7.60 Fritidsmotorbåt SFB‐6365 ÅSA 3.20 7.60 Volvo Penta MD17 Fritidsmotorbåt SFC‐3157 NUNNE 2.60 7.60 Yanmar 4JH‐DTE30679 1987 Fritidsmotorbåt SFC‐4399 FRIDA 2.30 7.60 Merzedes OM314 1981 Fritidsmotorbåt SFC‐3948 ARÖ 2.85 7.60 Mercedes Benz Fritidsmotorbåt SFC‐8740 BOITE A SAVON 2.60 7.60 MD 17C, 1985 Fritidsmotorbåt SFB‐6172 ANN 2.54 7.55 Volvo Penta BB30F 1979 Fritidsmotorbåt SFB‐3292 VIPAN 2.60 7.50 Penta Fritidsmotorbåt SFB‐3265 ICE 2.60 7.50 Fritidsmotorbåt SFB‐3507 2.80 7.50 Lister Fritidsmotorbåt SFB‐2374 MIRENO 2.96 7.50 Fritidsmotorbåt SFB‐2381 MARITA 2.75 7.50 Sabb Fritidsmotorbåt SFC‐3111 MATILDA 2.00 7.50 Sabb Fritidsmotorbåt SFB‐9953 KÄMPE 2.85 7.50 Perkins 4‐108 1979 Fritidsmotorbåt SFC‐8805 SPLIT 2.89 7.50 Fritidsmotorbåt SFC‐4661 2.65 7.50 TMD22 1995 Fritidsmotorbåt SFC‐5438 SAVOY 2.60 7.50 Volvo Penta MD21 1980 Fritidsmotorbåt 81

SFC‐7254 2.45 7.50 Yanmar 4LHA‐STP Fritidsmotorbåt SFC‐6051 LILY 2.90 7.50 2 Volvo Penta AQ151A Fritidsmotorbåt SFB‐4533 MARIANA 2.85 7.50 Säffle Semidiesel Fritidsmotorbåt SFB‐5512 DAHLIA II 2.40 7.50 Sleipner 1968 Fritidsmotorbåt SFB‐3331 ANNA‐KARIN 2.80 7.50 Fritidsmotorbåt SFB‐9689 MITZI 2.45 7.50 Yanmar 81545 Fritidsmotorbåt SFB‐8817 PIA 2.85 7.50 Fritidsmotorbåt SFB‐6891 2.85 7.50 Perkins 4.108 Fritidsmotorbåt SFC‐3438 ELLA LYKKE 2.90 7.50 Volvo Penta AQAD41 Fritidsmotorbåt SFB‐6312 ANITA 3.00 7.50 Yanmar 1979 Fritidsmotorbåt SFB‐3827 BODIL 2.00 7.50 Fritidsmotorbåt SFB‐4307 CLIPPER 3.00 7.50 Fritidsmotorbåt SFB‐3795 YVONNE 2.80 7.50 Skandia Fritidsmotorbåt SFC‐8824 MADAM MOET 2.85 7.47 Mercruiser 4,2 L Fritidsmotorbåt SFC‐4428 PACHAMAMA 2.54 7.47 Yamaha utombord 1990 Fritidsmotorbåt SFB‐7074 ELISABETH 2.52 7.46 MD 21 A Fritidsmotorbåt SFB‐9552 BELFI 2.65 7.45 Volvo Penta TAMD 30A Fritidsmotorbåt SFB‐5963 2.35 7.45 Wikström W‐3 1976 Fritidsmotorbåt SFC‐8311 DANIARA 2.75 7.45 Vetus Diesel, 2004 Fritidsmotorbåt SFC‐7899 ROBIN HOOD 2.54 7.42 Volvo Penta D 3 SX Fritidsmotorbåt SFC‐7124 LOVISA I 2.80 7.40 VP290A Fritidsmotorbåt SFB‐7114 EMMA 3.00 7.40 Volvo Penta MD11C 1978 Fritidsmotorbåt SFB‐8124 3.30 7.40 Fritidsmotorbåt SFC‐5343 ANNA 2.60 7.40 Yanmar QM3‐30 Fritidsmotorbåt SFB‐8166 SILVANA 2.80 7.40 Volvo Penta MD17 1982 Fritidsmotorbåt SFB‐2132 ORCA 2.50 7.40 Fritidsmotorbåt SFB‐5737 ANNA 3.00 7.33 Volvo Penta 1977 Fritidsmotorbåt SFB‐6704 VESTAN 2.80 7.30 Yanmar 2 Q M 20 1980 Fritidsmotorbåt SFC‐5826 BLIXTEN 2.60 7.30 Yanmar 3 cyl 1992 Fritidsmotorbåt 82

SFB‐8165 CAROLINE 2.70 7.30 Yanmar 2QM20 diesel Fritidsmotorbåt SFB‐5611 2.80 7.30 MD 17 1978 Fritidsmotorbåt SFB‐6357 2.45 7.30 Seffle S15 BF 1958 Fritidsmotorbåt SFB‐9151 HELENA 2.50 7.30 Sabb Diesel 1962 Fritidsmotorbåt SFC‐2820 JENNY 2.80 7.30 JQM 30 1978 Fritidsmotorbåt SFC‐4307 GUNILLA 3.60 7.30 Sabb Fritidsmotorbåt SFB‐2355 ÖSKÄR 3.02 7.28 Säffle Fritidsmotorbåt SFB‐8291 LILLAN 2.85 7.28 Volvo Penta 17M Diesel Fritidsmotorbåt SFC‐8551 TRYGG 2.40 7.27 Honda BF200AXL, 2007 Fritidsmotorbåt SFC‐5462 OUT OF THE BLUE 2.59 7.26 Mercruiser Fritidsmotorbåt SFC‐3570 BEAUT N 2.50 7.25 Mercruiser 57L Fritidsmotorbåt SFC‐3597 SORCERER 2.43 7.25 OMC 1989 Fritidsmotorbåt SFC‐6507 WHITESNAKE 2.45 7.20 Optimax Mariner 225/2002 Fritidsmotorbåt SFB‐6773 2.60 7.20 Västervik Fritidsmotorbåt SFB‐9259 MOBY DICK 2.95 7.20 Mercedes 190 1965 Fritidsmotorbåt SFC‐8817 ARCHIBALD HADDOCK 2.40 7.20 SUZUKI DF 150, 2007 Fritidsmotorbåt SFC‐7855 ÄCKERÖ 2.85 7.20 Sabb 2 G, 1964 Fritidsmotorbåt SFB‐2402 JANETA 2.45 7.20 BMC Commander diesel Fritidsmotorbåt SFB‐3754 ZITA 2.50 7.20 Volvo Penta MV 2 B Fritidsmotorbåt SFB‐6879 SIESTA 2.67 7.20 Volvo Penta AQ 145/280 Fritidsmotorbåt SFB‐6971 MARION 2.70 7.20 SABB 2H 1977 Fritidsmotorbåt SFB‐9245 MONICA 2.45 7.20 Albin 0‐41 Fritidsmotorbåt SFC‐2099 MAGGAN 2.40 7.20 Volvo Penta 1985 Fritidsmotorbåt SFB‐7561 3.05 7.20 Yanmar 80625 1980 Fritidsmotorbåt SFC‐8684 NEMO 2.67 7.20 Fritidsmotorbåt SFB‐6173 2.60 7.15 Sabb 2H 1978 Fritidsmotorbåt SFB‐7606 2.40 7.15 Volvo Penta Fritidsmotorbåt SFB‐5197 OCEAN 3.00 7.10 Sabb 1976 Fritidsmotorbåt SFC‐2447 ROCKAN 2.72 7.10 M4 1988 Fritidsmotorbåt 83

SFB‐5045 2.72 7.10 Yanmar Diesel 2QM20 Fritidsmotorbåt SFC‐4161 PÄRLAN 2.55 7.10 Scania Fritidsmotorbåt SFC‐3803 AVANCE 2.72 7.03 Volvo Penta AD31/DP 1992 Fritidsmotorbåt SFC‐8183 VIRUS VIII 2.55 7.01 Mercruiser 4,3L MPI Alpha Fritidsmotorbåt SFC‐2135 JENNY 2.75 7.00 Albin Diesel Fritidsmotorbåt SFB‐3128 ERNA 2.50 7.00 Sabb 1981 Fritidsmotorbåt SFB‐5991 OSSIE 2.50 7.00 Sabb 1973 Fritidsmotorbåt SFB‐4694 MARGARETA 2.60 7.00 Volvo Penta Diesel 1974 Fritidsmotorbåt SFC‐3068 LISBETH 2.40 7.00 Yanmar 4JHTE 1985 Fritidsmotorbåt SFB‐4625 ANJA 2.50 7.00 Fritidsmotorbåt SFB‐5621 BÅDEN 2.30 7.00 Yanmar 1977 Fritidsmotorbåt SFB‐9154 DINO III 2.80 7.00 Marna diesel 1971 Fritidsmotorbåt SFB‐5023 KAJSA 2.60 7.00 Albin AL 23 Fritidsmotorbåt SFB‐5337 INA 2.75 7.00 Saab diesel Fritidsmotorbåt SFB‐5846 2.65 7.00 BMC Captain 1969 Fritidsmotorbåt SFB‐4653 GRAM 2.00 7.00 Sabb Diesel Fritidsmotorbåt SFB‐3260 CARINA 2.80 7.00 Volvo Penta MD21 Fritidsmotorbåt SFC‐2162 LIV 2.65 7.00 Yanmar 2QM20 1979 Fritidsmotorbåt SFC‐3281 SEA SONG 2.50 7.00 Volvo Penta Fritidsmotorbåt SFB‐9104 NINA 2.40 7.00 Sabb 1974 Fritidsmotorbåt SFB‐9124 2.10 7.00 MD 2 B Fritidsmotorbåt SFB‐8500 LEX 2.50 7.00 Sabb diesel 1972 Fritidsmotorbåt SFC‐4857 KATARINA 2.60 7.00 Volvo Penta MD21 1985 Fritidsmotorbåt SFC‐4397 ANNA‐MARIA 2.60 6.95 Volvo Penta Fritidsmotorbåt SFB‐5191 HERMON 2.60 6.95 Volvo Penta Diesel Fritidsmotorbåt SFB‐5814 WINDÖ 2.65 6.90 SABB 1969 Fritidsmotorbåt SFB‐3865 INGER 2.30 6.90 Fritidsmotorbåt SFB‐3209 DICK 2.80 6.90 Fritidsmotorbåt SFB‐3290 EVY 2.80 6.90 Fritidsmotorbåt 84

SFC‐2685 2.60 6.90 Albin AD‐2 1968 Fritidsmotorbåt SFB‐5192 LADY GULL 2.30 6.90 Volvo Penta MD2B 1974 Fritidsmotorbåt SFC‐7140 COMPANY 2.40 6.88 Yamaha, 2004 Fritidsmotorbåt SFB‐5291 RÅNÄS 2.80 6.85 Sabb Fritidsmotorbåt SFB‐5318 CHARLOTTA 2.60 6.80 MD 3 1977 Fritidsmotorbåt SFB‐5005 SKÄRELÄJA 2.40 6.80 MD2B Penta 1971 Fritidsmotorbåt SFC‐4914 2.35 6.80 Volvo Penta 250SP 1993 Fritidsmotorbåt SFC‐3682 GUNEA NULL 6.80 Johnson Fritidsmotorbåt SFC‐4335 HORISONT 2.80 6.80 Yanmar 1986 Fritidsmotorbåt SFB‐3715 1.90 6.80 Fritidsmotorbåt SFB‐5004 ANNELIE 2.40 6.80 MD2B 1971 Fritidsmotorbåt SFB‐5120 KAMI 2.60 6.80 Yanmar 2QM20 Fritidsmotorbåt SFB‐4924 MILLAN 2.40 6.80 Yamaha Fritidsmotorbåt SFB‐7104 2.60 6.80 Volvo Penta MD3B 1977 Fritidsmotorbåt SFB‐2425 VIKINGEN 2.60 6.80 Volvo Penta MD21 Fritidsmotorbåt SFB‐2287 ULLA 2.50 6.80 Fritidsmotorbåt SFB‐7786 MARI 2.60 6.80 MD17C 1978 Fritidsmotorbåt SFC‐3395 2.40 6.80 Volvo Penta Fritidsmotorbåt SFC‐3362 MARLENE 2.55 6.75 Volvo Penta MD11C Fritidsmotorbåt SFB‐7955 MARIEL 2.80 6.75 Saab diesel 1978 Fritidsmotorbåt SFB‐4913 SEABIRD 2.45 6.75 Fritidsmotorbåt SFC‐7996 AARTI 2.25 6.75 AQ 140 A, 1980 Fritidsmotorbåt SFB‐7459 2.25 6.75 FORD 2614 E Fritidsmotorbåt SFB‐8054 KONDOR 2.55 6.75 Yanmar 2QM20 1980 Fritidsmotorbåt SFB‐5128 HANNA 2.24 6.70 MD 11C 1976 Fritidsmotorbåt SFC‐6194 LILLAN AF SVARTLÖGA 2.35 6.70 Yamaha AETO Fritidsmotorbåt SFC‐8142 ALBERTINA 2.41 6.70 OMC 985288, 1992 Fritidsmotorbåt SFC‐5671 BUSTER 2.47 6.70 Volvo Penta AQD40 280DP Fritidsmotorbåt SFB‐7240 GERDA 2.00 6.70 Volvo MD 1 1969 Fritidsmotorbåt 85

SFB‐5006 1.85 6.60 Vikström 1972 Fritidsmotorbåt SFB‐6157 MALIN 2.45 6.60 Yanmar 1979 Fritidsmotorbåt SFB‐3421 GUNNAREN 2.40 6.60 Lister Diesel 3 cyl Fritidsmotorbåt SFC‐2701 1.80 6.60 Johnson 45 SL Fritidsmotorbåt SFC‐3481 GEMINI 2.70 6.60 Volvo Penta MD3B 1976 Fritidsmotorbåt SFB‐4721 MIMMI 2.50 6.60 Sabb Fritidsmotorbåt SFB‐7398 GROGGEN 2.27 6.60 Albin 021 1964 Fritidsmotorbåt SFC‐2422 ACHALANTIS 2.50 6.60 Sabb 1985 Fritidsmotorbåt SFB‐2552 ZULEIKA 2.40 6.60 Fritidsmotorbåt SFB‐5731 TERESE 2.50 6.55 Volvo Penta 1974 Fritidsmotorbåt SFB‐8420 ODD 2.60 6.55 Yanmar 2QM20 1977 Fritidsmotorbåt SFC‐7457 PRINCESS II 2.59 6.55 Mercruiser ‐03 Fritidsmotorbåt SFB‐4940 MALIN 2.50 6.50 Lister Fritidsmotorbåt SFB‐4354 KULING 2.50 6.50 Volvo MD Fritidsmotorbåt SFC‐3420 META 2.50 6.50 Volvo Penta diesel Fritidsmotorbåt SFC‐4381 KARLSÖ 2.25 6.50 Volvo Penta 1980 Fritidsmotorbåt SFB‐9270 MARIO 2.50 6.50 Volvo Penta AQAD41 1981 Fritidsmotorbåt SFB‐7426 FÅGEL 2.50 6.50 Diesel AQD21 1982 Fritidsmotorbåt SFC‐7583 SVEA 2.20 6.50 Volvo Penta D3, 2004 Fritidsmotorbåt SFC‐5946 EMMA 2.40 6.50 Yanmar SB12 Fritidsmotorbåt SFB‐2848 2.44 6.50 Seffle Fritidsmotorbåt SFB‐3473 2.20 6.50 Fritidsmotorbåt SFB‐4337 INGELA 2.20 6.50 Fritidsmotorbåt SFB‐2282 2.00 6.50 Skandia 10 B Fritidsmotorbåt SFC‐3249 TTO PEPE 2.40 6.50 Chrysler Fritidsmotorbåt SFC‐8083 MAGDALENA 2.61 6.47 Mercruiser 5.0, 1994 Fritidsmotorbåt SFC‐3916 MISSTRESS 2.45 6.45 Mercruiser Fritidsmotorbåt SFB‐7478 2.45 6.45 Sabb nr 888 1970 Fritidsmotorbåt SFB‐2995 2.32 6.41 Bolinder Fritidsmotorbåt 86

SFB‐5705 2.30 6.40 Albin 0‐2 Fritidsmotorbåt SFB‐9947 2.20 6.40 Yanmar 2QM15 Fritidsmotorbåt SFC‐3462 1.80 6.40 Merkure 265 Fritidsmotorbåt SFC‐4298 ÅSA 2.40 6.40 Volvo Penta MD2 1975 Fritidsmotorbåt SFC‐6358 MISTRAL 2.35 6.40 Yahmar E11295, 1999 Fritidsmotorbåt SFC‐6201 TAILA 2.50 6.40 Yanmar 1985 Fritidsmotorbåt SFC‐2973 2.40 6.40 Yanmar 8 KW 1981 Fritidsmotorbåt SFB‐8221 2.35 6.40 Yanmar 4JM‐TE 1983 Fritidsmotorbåt SFC‐4624 BULLIT 2.44 6.38 OMC V8 5L EFI 1993 Fritidsmotorbåt SFB‐9481 INGRID 2.46 6.35 Yanmar, 1987 Fritidsmotorbåt SFC‐3272 2.11 6.30 Interceptor 215 Fritidsmotorbåt SFB‐5516 INGA‐MAJ 2.30 6.30 Sabb 1977 Fritidsmotorbåt SFB‐5278 GÖTILDA 2.30 6.30 Sabb 1976 Fritidsmotorbåt SFB‐2646 MYRAN 2.20 6.30 Volvo Penta Fritidsmotorbåt SFB‐4221 2.45 6.30 Volvo Penta MD 2 Fritidsmotorbåt SFB‐3291 HAMA 2.30 6.30 Volvo Penta Fritidsmotorbåt SFB‐3763 SIAM 2.40 6.30 Fritidsmotorbåt SFB‐3040 2.55 6.30 Sabb Fritidsmotorbåt SFC‐5991 YOANNE 2.60 6.30 Yamaha 85 1981 Fritidsmotorbåt SFB‐9557 SAGA 2.25 6.30 Volvo Penta, 1985 Fritidsmotorbåt SFB‐5562 HOLMÖN 2.22 6.30 Sabb diesel 1974 Fritidsmotorbåt SFB‐5578 DUX 2.30 6.30 Yanmar 2QM20 Fritidsmotorbåt SFB‐6063 GUN‐MARIE 2.30 6.30 Albin AD2 Fritidsmotorbåt SFB‐6799 RANA 2.30 6.30 Sabb Diesel‐G 1980 Fritidsmotorbåt SFB‐2193 ANNE MARIE 2.50 6.30 Sabb Diesel Fritidsmotorbåt SFB‐3762 JULLAN 2.10 6.30 Fritidsmotorbåt SFB‐3773 LIBERTY 2.40 6.30 Fritidsmotorbåt SFB‐4955 2.30 6.30 Sabb Fritidsmotorbåt SFB‐4861 2.20 6.30 Saab Fritidsmotorbåt 87

SFB‐2485 ANNA 2.25 6.30 Fritidsmotorbåt SFB‐3966 WINDY 2.40 6.30 Fritidsmotorbåt SFC‐5983 TORA 2.54 6.27 Evinrude utombord 2000 Fritidsmotorbåt SFB‐7093 MAJ 2.45 6.25 Ducati IS 16 Fritidsmotorbåt SFB‐3690 PELLA 2.10 6.20 Volvo Penta MD2 Fritidsmotorbåt SFC‐2085 2.20 6.20 Mercury 1974 utombord Fritidsmotorbåt SFB‐9957 2.45 6.15 Volvo Penta 1988 Fritidsmotorbåt SFC‐4357 ANNIKA 2.30 6.15 Fritidsmotorbåt SFC‐6603 NANNA 2.28 6.15 Fritidsmotorbåt SFC‐2166 DEBORA 2.50 6.15 Yanmar Fritidsmotorbåt SFC‐8735 2.45 6.14 Mercury 115 ELPTO S.nr OP194114 Fritidsmotorbåt SFC‐8749 FRANK 2.29 6.14 V6‐4200 ,kb, Fritidsmotorbåt SFB‐9996 2.33 6.14 Yanmar Fritidsmotorbåt SFB‐6943 ELIN 2.38 6.14 Sabb 2H 1971 Fritidsmotorbåt SFC‐7451 PAULA 2.31 6.14 Mercruiser, 1994 Fritidsmotorbåt SFC‐8299 2.39 6.13 Mercruiser 5,0 MPI Fritidsmotorbåt SFC‐4862 KOS 1.80 6.12 Utombord Fritidsmotorbåt SFC‐4393 LELA 2.20 6.10 Yamaha 30 DEOL 1989 Fritidsmotorbåt SFC‐4597 LOLLO 2.50 6.10 Sabb Fritidsmotorbåt SFB‐9939 2.05 6.10 Yanmar 3 HM 1984 Fritidsmotorbåt SFB‐9753 2.44 6.10 Volvo Penta Fritidsmotorbåt SFB‐9178 1.95 6.10 Fritidsmotorbåt SFB‐8701 MARIANA 2.20 6.10 Yanmar 3GM 1984 Fritidsmotorbåt SFC‐8322 2.20 6.10 Volvo Penta MB10, 1979 Fritidsmotorbåt SFB‐6485 DANA 2.40 6.10 Volvo Penta MD 17 C Fritidsmotorbåt SFB‐6639 LILLAN 2.40 6.10 Yanmar Fritidsmotorbåt SFB‐8293 ARGO 2.40 6.10 Volvo Penta MD11A 1981 Fritidsmotorbåt SFC‐4463 2.08 6.10 Suzuki 1983 Fritidsmotorbåt SFC‐4500 SNIPAN 2.25 6.10 Volvo Penta 1978 Fritidsmotorbåt 88

SFC‐3476 2.05 6.10 BJ45RSLU Fritidsmotorbåt SFB‐6327 IAN 2.30 6.10 Yanmar YSE 12 1978 Fritidsmotorbåt SFC‐7948 2.40 6.10 Suzuki 4‐takt, 2003 Fritidsmotorbåt SFC‐2433 LENA 2.10 6.10 Yanmar Fritidsmotorbåt SFB‐7730 1.95 6.10 Sabb diesel Fritidsmotorbåt SFC‐4261 ANNA 2.30 6.08 Volvo Penta MD11 1982 Fritidsmotorbåt SFC‐2234 2.00 6.05 Utombord Fritidsmotorbåt SFC‐4730 LYNGÖ 2.20 6.05 Utombord 1994 Fritidsmotorbåt SFB‐6970 KARIN 2.45 6.05 Yanmar 1981 Fritidsmotorbåt SFB‐9477 KRISTINA 2.20 6.05 Monark 3 cyl, 1974 Fritidsmotorbåt SFB‐4510 TÄRNAN 2.00 6.00 Fritidsmotorbåt SFB‐2822 MI 2.38 6.00 Fritidsmotorbåt SFB‐3532 2.20 6.00 Sabb Fritidsmotorbåt SFC‐7011 LA RIVE 2.35 6.00 Yamaha 90, 1999 Fritidsmotorbåt SFC‐3443 LOTTA 2.35 6.00 Volvo Penta 2002 Fritidsmotorbåt SFC‐3120 TUTTAN 2.10 6.00 Skandia 6 1965 Fritidsmotorbåt SFC‐2255 2.20 6.00 1988 Fritidsmotorbåt SFC‐2687 VIKTORIA 2.35 6.00 Utombord YAMAHA 1990 Fritidsmotorbåt SFB‐9163 BRITT 2.30 6.00 Volvo, diesel Fritidsmotorbåt SFB‐7372 ANNA 2.20 6.00 Buch diesel Fritidsmotorbåt SFB‐4942 DEA 2.50 6.00 Diesel Fritidsmotorbåt SFC‐3912 SIGNAL 2.35 6.00 Yamaha utombord Fritidsmotorbåt SFC‐3632 CREAM LADY 2.05 6.00 Volvo Penta Fritidsmotorbåt SFB‐7902 KNÖLSVANEN 2.50 6.00 Saab 1979 Fritidsmotorbåt SFB‐7554 2.10 6.00 Mariner 1981 Fritidsmotorbåt SFC‐3027 LABBEN 2.50 6.00 Mariner 1987 Fritidsmotorbåt SFB‐3730 LISSA 2.00 6.00 Fritidsmotorbåt SFB‐3741 EVY 2.25 6.00 Fritidsmotorbåt SFB‐3776 SPERO 2.44 6.00 Fritidsmotorbåt 89

SFB‐3359 RAN 2.50 6.00 Saab diesel 1981 Fritidsmotorbåt SFB‐3680 NN 2.48 6.00 Fritidsmotorbåt SFB‐3854 SABINA 2.00 6.00 Fritidsmotorbåt SFB‐4351 RAMNÖ 2.20 6.00 Sefle Fritidsmotorbåt SFB‐4621 ERIK 2.35 6.00 Fritidsmotorbåt SFC‐4325 NINA 2.00 6.00 Utombordsmotor Fritidsmotorbåt SFC‐4894 MARINE 2.20 6.00 Mercrusier 1996 Fritidsmotorbåt SFC‐4182 2.40 6.00 Yanmar SB8 1978 Fritidsmotorbåt SFC‐4989 TREAN 2.40 6.00 Sabb Fritidsmotorbåt SFC‐4301 EOR 21 2.08 5.98 Lister SL2 1973 Fritidsmotorbåt SFC‐7402 STARCROSS 2.40 5.95 Evinrude Fritidsmotorbåt SFB‐9681 DILFINEN 2.20 5.90 Sabb 1973 Fritidsmotorbåt SFB‐9859 2.10 5.90 Sabb HG 1976 Fritidsmotorbåt SFC‐4147 2.02 5.90 Utombord 1980 Fritidsmotorbåt SFC‐3756 GRODAN 2.12 5.90 Yamaha 1993 Fritidsmotorbåt SFC‐8376 SEABIRD 2.44 5.90 Yamaha, 1997 Fritidsmotorbåt SFC‐5269 2.30 5.85 Suzuki 1991 Fritidsmotorbåt SFB‐4265 OLIVIA 2.00 5.85 Volvo Penta Fritidsmotorbåt SFC‐2680 DOLLY 2.40 5.85 Kubota diesel Fritidsmotorbåt SFC‐4400 ELIN 1.90 5.80 Mariner Fritidsmotorbåt SFB‐8084 LINDA 2.35 5.80 MD 6 B Fritidsmotorbåt SFC‐4548 2.05 5.80 Yamaha 60FEOL 1992 Fritidsmotorbåt SFC‐5098 2.25 5.75 Yamaha 1991, bensin Fritidsmotorbåt SFC‐7924 2.18 5.74 F80BETL, 2005 Fritidsmotorbåt SFC‐8753 NATALIJA 2.20 5.73 Suzuki DF140/14001885222, 2008 Fritidsmotorbåt SFC‐4344 SIW 2.00 5.72 Yanmar Fritidsmotorbåt SFC‐6417 AMAZON 2.20 5.70 Yamaha Saltwater Series Fritidsmotorbåt SFC‐4295 MALIN 2.00 5.70 Yanmar YSE12 1978 Fritidsmotorbåt SFC‐3661 SANDRA 2.20 5.70 Mercury Fritidsmotorbåt 90

SFB‐5898 ANNA 2.10 5.70 Saab Fritidsmotorbåt SFB‐9887 2.26 5.70 Sabb typ GG 1970 Fritidsmotorbåt SFB‐4679 LENA 2.30 5.70 Fritidsmotorbåt SFB‐5646 ATHENA 2.20 5.65 Mariner Fritidsmotorbåt SFB‐4464 2.05 5.65 Fritidsmotorbåt SFC‐3697 OTELLO 2.21 5.64 Force 1254 8A M Fritidsmotorbåt SFC‐4119 LARITA II 2.20 5.60 Suzuki Fritidsmotorbåt SFB‐8170 ANNETTE 2.40 5.60 Fritidsmotorbåt SFC‐2000 2.10 5.60 Volvo Penta Fritidsmotorbåt SFB‐9264 RAYON 2.20 5.60 Yamaha Fritidsmotorbåt SFC‐3224 LAHÄLL II 2.05 5.60 Fritidsmotorbåt SFC‐8296 BRITA 2.17 5.60 Yamaha, 2007 Fritidsmotorbåt SFB‐5221 REGINA 2.25 5.60 Yanmar YSE 12 1975 Fritidsmotorbåt SFB‐4454 2.10 5.60 Fritidsmotorbåt SFB‐9781 2.15 5.60 Jonsson 1984 Fritidsmotorbåt SFB‐9415 LÄSJÖ 1.85 5.60 Volvo Penta 200 Fritidsmotorbåt SFB‐4469 EVA 1.70 5.50 Fritidsmotorbåt SFB‐2648 WALLY 2.12 5.50 Fritidsmotorbåt SFB‐4588 CARMENCITA 2.00 5.50 Volvo‐Penta Fritidsmotorbåt SFB‐2466 1.85 5.50 MD 1 Fritidsmotorbåt SFB‐6163 2.65 5.50 Volvo Penta MD2B Fritidsmotorbåt SFB‐2824 SAGA 1.80 5.49 Fritidsmotorbåt SFC‐3028 2.20 5.45 Yamaha Fritidsmotorbåt SFB‐9528 2.20 5.45 Yanmar Fritidsmotorbåt SFB‐6183 2.03 5.40 Evinrude 1977 Fritidsmotorbåt SFC‐2257 2.15 5.40 Johnson 1983 Fritidsmotorbåt SFC‐4383 ÖRNVIK 2.00 5.40 Johnson 1985 Fritidsmotorbåt SFB‐9185 1.95 5.36 Johnson utomb. 1982 Fritidsmotorbåt SFB‐9937 1.89 5.36 Evinrude Fritidsmotorbåt 91

SFC‐2244 1.89 5.36 Mercury 40E 1975 Fritidsmotorbåt SFC‐8404 LINNÉA 2.11 5.35 Mercruiser 3,0L Fritidsmotorbåt SFB‐9731 1.90 5.33 Albin bensin Fritidsmotorbåt SFC‐4539 2.05 5.30 Yamaha utombord 1986 Fritidsmotorbåt SFC‐8905 FANNY 2.05 5.30 Yamaha, 2008 Fritidsmotorbåt SFC‐5325 AMOBILE 2.24 5.30 Mercruiser, 1990 Fritidsmotorbåt SFC‐4191 1.75 5.30 Utombord Fritidsmotorbåt SFB‐2487 DAGNY 2.15 5.30 MD 1 Fritidsmotorbåt SFC‐7103 2.10 5.25 Mercury Fritidsmotorbåt SFC‐2233 1.77 5.23 Yanmar 1GM 1982 Fritidsmotorbåt SFC‐4317 2.35 5.20 Jonson Fritidsmotorbåt SFC‐7571 ALKYONEUS 2.20 5.20 Tohatsu M40D,utombord Fritidsmotorbåt SFC‐7901 SILVER VIKING 2.07 5.20 Mercury E50, 2000 Fritidsmotorbåt SFB‐9230 UTTERN 520 2.10 5.20 Mercury 45ELO 1987 Fritidsmotorbåt SFC‐2044 2.05 5.20 Fritidsmotorbåt SFB‐9527 JAPPE 1.78 5.15 Yanmar Fritidsmotorbåt SFC‐2628 ELLEONOR 1.70 5.15 30ECS 1989 Fritidsmotorbåt SFC‐8759 DCM 69 2.02 5.12 Mercury 70, 1984 Fritidsmotorbåt SFC‐4804 SOFIA WEST 1.85 5.10 Johnsson Fritidsmotorbåt SFB‐9526 GULINGEN 1.80 5.10 Johnsson, 1979/80 Fritidsmotorbåt SFB‐9422 2.20 5.10 Evinrude Fritidsmotorbåt SFB‐3845 1.90 5.10 Fritidsmotorbåt SFC‐7038 PÄRLAN 1.95 5.10 Evinrude utombordare,‐69 Fritidsmotorbåt SFC‐3410 1.65 5.10 Monark Fritidsmotorbåt SFB‐9414 GULLSJÖ 1.80 5.07 Volvo Penta 200 Fritidsmotorbåt SFC‐2727 1.95 5.05 Yamaha 1989 Fritidsmotorbåt SFB‐9918 1.92 5.05 Mercury 500 1976 Fritidsmotorbåt SFC‐4429 SAFIR 2.00 5.00 Johnson utombord Fritidsmotorbåt SFB‐3692 BRIS 1.80 5.00 Fritidsmotorbåt 92

SFC‐8897 DAMPES RI 2.00 5.00 Utombordsmotor, Zuzuki Fritidsmotorbåt SFB‐2930 REBECKA 2.00 5.00 Johnsson Fritidsmotorbåt SFC‐8255 BB 845 2.03 4.88 Yamaha, 2004 Fritidsmotorbåt SFC‐8437 CASA 1.80 4.85 Johnson, 1985 Fritidsmotorbåt SFC‐7994 2.10 4.85 Mercury ELPTO 50, ‐95 Fritidsmotorbåt SFC‐7479 1.90 4.77 Mercury OT765S75, 2003 Fritidsmotorbåt SFC‐8754 BELAFONTE 1.91 4.76 Mercury F60, 2008 Fritidsmotorbåt SFC‐7944 MILICA 2.37 4.67 Mercury 50, 2006 Fritidsmotorbåt SFC‐8399 SMUNKEN 1.82 4.66 Evinrude, 1972 Fritidsmotorbåt SFC‐8422 1.85 4.60 Tohatsu Fritidsmotorbåt SFC‐8803 SAGA 1.85 4.58 Mariner 55E, 1984 Fritidsmotorbåt SFC‐5547 1.68 4.42 Evinrude Fritidsmotorbåt SFC‐4460 1.85 4.25 Johnson 1993 Fritidsmotorbåt SFC‐3334 BOSS 1.80 4.25 Mercury Fritidsmotorbåt SFC‐5807 1.64 4.05 Evinrude 35 Elan QL Fritidsmotorbåt SFC‐7123 1.95 3.99 Yamaha F25AES, 2004 Fritidsmotorbåt SFC‐7443 1.52 3.40 Yamaha, 1999 Fritidsmotorbåt SFC‐8713 MARIJO 1.17 3.22 Yamaha, 2005 Fritidsmotorbåt SFC‐7530 KENNETH PETTERSSON 1.25 3.15 66 D, 1999 Fritidsmotorbåt SFC‐8310 1.50 3.10 Fritidsmotorbåt SFC‐8710 KVAST‐HILDA 3.30 15.45 Lombardini LDW220YM, 2004 Fritidsmotorsegelbåt SFC‐8679 MARY AF RÖVARHAMN 3.68 14.50 Perkins 4.108, 1983 Fritidsmotorsegelbåt SFC‐7512 ELLINOR 3.89 14.44 Volvo TMD 31A, 1987 Fritidsmotorsegelbåt SFC‐8587 OHANA 3.94 14.32 Yanmar 4 PHME Fritidsmotorsegelbåt SFC‐5352 NADIR 3.97 14.20 Volvo Penta MD96 1959 Fritidsmotorsegelbåt SFC‐7092 INGURA 3.98 14.00 Mercedes Benz, 1989 Fritidsmotorsegelbåt SFC‐6786 CAROLINA IV 3.96 14.00 Yanmar 4JH3 TBE Fritidsmotorsegelbåt SFC‐8706 SERENADE 3.80 13.80 Volvo Penta MD3B, 1975 Fritidsmotorsegelbåt SFC‐7043 EJA AF SLUSSEN 3.80 13.75 Lombardini 1503, 1992 Fritidsmotorsegelbåt 93

SFC‐2121 ZEDNA 3.70 13.65 Ford Lehman 6 Fritidsmotorsegelbåt SFC‐7749 FREJA 3.47 13.53 Volvo MD 11 Fritidsmotorsegelbåt SFC‐8040 MARIANNE III 3.98 13.50 Yanmar 4JH3‐TBE 2,6 Fritidsmotorsegelbåt SFC‐8150 RAUK 3.95 13.50 Kubota, 1988 Fritidsmotorsegelbåt SFC‐5159 SOFI 3.58 13.45 Ford Diesel 2712E 1975 Fritidsmotorsegelbåt SFC‐7549 FULL MOON 3.81 13.41 Perkins 5/236, 1992 Fritidsmotorsegelbåt SFC‐7849 CAJOLA 3.95 13.40 Volvo MD22L, 1999 Fritidsmotorsegelbåt SFC‐7050 OLYMPIA 3.95 13.40 MD22L Volvo, 2000 Fritidsmotorsegelbåt SFC‐8593 SIGRID 3.95 13.40 Volvo Penta D55 Fritidsmotorsegelbåt SFC‐7885 RONJA 3.97 13.39 Yanmar 4JH3‐TBE, 2003 Fritidsmotorsegelbåt SFC‐8176 NOATUN 3.98 13.37 Perkins 4‐108, 1985 Fritidsmotorsegelbåt SFC‐8138 COMEDIE 3.95 13.22 VolvoPenta TMD31L‐A, 1995 Fritidsmotorsegelbåt SFC‐5733 LADY ESS 3.70 13.20 Ford 2715E 1980 Fritidsmotorsegelbåt SFC‐7141 ANNFIE 3.90 13.09 Yanmar 4JH3E, 2004 Fritidsmotorsegelbåt SFC‐7314 ABRA KADABRA 3.90 13.09 Volvo Penta D2‐55, 2004 Fritidsmotorsegelbåt SFC‐8180 CULOTTE BLEUE 3.90 13.09 Yanmar 4JH4E, 2006 Fritidsmotorsegelbåt SFC‐8769 DON'T LOOK BACK 3.90 13.09 Yanmar 4JH4E, 2005 Fritidsmotorsegelbåt SFC‐8653 SHIRAZ 3.90 13.09 Volvo D‐2‐55, 2003 Fritidsmotorsegelbåt SFC‐6828 STORA BLÅ 3.73 13.05 Volvo Penta 2030, 1994 Fritidsmotorsegelbåt SFC‐6297 ESS & GEE 3.90 13.00 MD 32A, 1979 Fritidsmotorsegelbåt SFC‐7546 HOKUS POKUS 2 3.82 13.00 Volvo Penta MD31, 1994 Fritidsmotorsegelbåt SFC‐6872 VÄLFARE 3.95 13.00 Ford 2712E Fritidsmotorsegelbåt SFC‐8520 ASYNJA 3.10 13.00 Volvo Penta MD17, 1988 Fritidsmotorsegelbåt SFC‐7444 HEUREKA II 3.99 12.99 Volvo MD2003T, 1989 Fritidsmotorsegelbåt SFC‐8336 KAROLINA 3.95 12.95 Ford 2712E, 1981 Fritidsmotorsegelbåt SFC‐3744 MA DONNA 3.88 12.95 Volvo Penta TMD 31 B Fritidsmotorsegelbåt SFC‐6724 CASTA DIVA 3.78 12.93 Volvo Penta MD21,1981 Fritidsmotorsegelbåt SFC‐7110 QUINTAMARE 3.90 12.90 Yanmar 3 JH3CE, 2001 Fritidsmotorsegelbåt SFC‐7031 MAYA 3.98 12.80 Perkins Prima ‐94 Fritidsmotorsegelbåt 94

SFC‐7356 ENGLA 3.95 12.80 Perkins 4,108 diesel Fritidsmotorsegelbåt SFC‐4996 BARAVARA 3.98 12.80 Yanmar diesel Fritidsmotorsegelbåt SFC‐7871 STORM 3.55 12.70 Yanmar 4JH3E, 2003 Fritidsmotorsegelbåt SFC‐4557 HEDDA AF FORSNÄS 3.70 12.70 Volvo Penta MD31 1989 Fritidsmotorsegelbåt SFC‐2816 AKKA THE GOOSE 3.72 12.70 Volvo Penta MD31A 1991 Fritidsmotorsegelbåt SFC‐8652 3.96 12.67 Ford 2725E 6.2l,1989 Fritidsmotorsegelbåt SFC‐8692 3.95 12.67 Yanmar 4JH3E, E24652 Fritidsmotorsegelbåt SFC‐3495 SIV 2.60 12.65 Volvo TD47 Fritidsmotorsegelbåt SFC‐8739 BOHEMIA 3.95 12.60 Volvo MD22, 2001 Fritidsmotorsegelbåt SFC‐8700 JIVA 3.26 12.50 Yanmar 3QM3 Fritidsmotorsegelbåt SFC‐7017 LOVA 3.60 12.50 Volvo Penta MD 21 A, 1977 Fritidsmotorsegelbåt SFC‐6761 STIMULANTIA 3.20 12.50 Yanmar 3 HM, 1984 Fritidsmotorsegelbåt SFC‐7357 AITUTAKI 3.70 12.49 2030 Volvo, 2004 Fritidsmotorsegelbåt SFC‐8523 3.90 12.45 Yanmar 3JH2E Fritidsmotorsegelbåt SFC‐7134 LADY ANN III 3.90 12.45 Yanmar, 1998 Fritidsmotorsegelbåt SFB‐6493 MIDNIGHT EXPRESS 3.92 12.40 Perkins 4108, 1986 Fritidsmotorsegelbåt SFC‐7433 METHANA 3.87 12.30 Volvo Penta 2030, 1999 Fritidsmotorsegelbåt SFC‐7151 OYZO 15 3.98 12.25 Perkins Prima M50 Fritidsmotorsegelbåt SFC‐8261 SONGONI III 3.76 12.24 Yanmmar Fritidsmotorsegelbåt SFC‐7810 YMER 3.92 12.23 Volvo D2‐55 5102965641 Fritidsmotorsegelbåt SFC‐5994 AURORA 3.90 12.20 Perkins M50 1992 Fritidsmotorsegelbåt SFC‐8748 CIRCE 3.95 12.20 Yanmar 54 HK 4Jh4E Fritidsmotorsegelbåt SFC‐8818 SWEET DREAMS 3.95 12.20 Yanmar diesel, 1999 Fritidsmotorsegelbåt SFC‐7355 LAMPONIA II 3.83 12.20 MD 2040‐DBT Fritidsmotorsegelbåt SFC‐7334 NORDIC STAR 3.95 12.20 Yanmar 4JH4‐E, 2005 Fritidsmotorsegelbåt SFC‐7866 AZIZA 3.95 12.20 Yanmar E02019, ‐05 Fritidsmotorsegelbåt SFC‐8113 RUBICON 3.70 12.20 Volvo Penta 2003T, 1986 Fritidsmotorsegelbåt SFC‐8306 MILENA 3.83 12.20 Volvo Penta D2‐40,2006 Fritidsmotorsegelbåt SFC‐7903 DAWN 3.85 12.18 Vetus 425H253 Fritidsmotorsegelbåt 95

SFC‐8302 YASMINE 3.91 12.15 Yanmar 3JH4E Fritidsmotorsegelbåt SFC‐8165 MAROUSCHKA V 3.97 12.14 Volvo Penta D55, 2005 Fritidsmotorsegelbåt SFC‐8895 WINDJAMMER 3.97 12.14 Volvo Penta D2 55, 2008 Fritidsmotorsegelbåt SFC‐7943 ELLEN AF LYSEKIL 3.83 12.10 Volvo Penta MD22P Fritidsmotorsegelbåt SFC‐7923 ANTIGONE 3.80 12.10 Volvo Penta 2003T, 1991 Fritidsmotorsegelbåt SFC‐6464 NOOMI 3.83 12.10 Yanmar HJH3E 2000 Fritidsmotorsegelbåt SFC‐8069 RANDIVÅG 3.83 12.10 Yanmar 4JH36B4E Fritidsmotorsegelbåt SFC‐8262 WILDA 3.48 12.10 Volvo Penta D2‐55, 2006 Fritidsmotorsegelbåt SFC‐7559 FRENJA 3.55 12.05 VP D2‐55, 2001 Fritidsmotorsegelbåt SFC‐8573 FOGELN 3.57 12.00 Volvo Penta MD 22 L, 2001 Fritidsmotorsegelbåt SFC‐6324 SAVANNA 3.90 12.00 Volvo D50, 1982 Fritidsmotorsegelbåt SFC‐7838 JAMBALAYA 3.80 12.00 Volvo Penta MD21 Fritidsmotorsegelbåt SFB‐8546 MARTINETTE 3.75 12.00 Status marine Fritidsmotorsegelbåt SFC‐8240 HARMONI II 3.96 12.00 Perkins M50, 1990 Fritidsmotorsegelbåt SFC‐7531 ARCTURUS II 3.81 12.00 Volvo Penta MD2‐55 Fritidsmotorsegelbåt SFC‐8586 FROGGY 3.96 11.98 Yamaha 4JH4E, 2006 Fritidsmotorsegelbåt SFC‐7360 AKKA 3.80 11.97 Perkins M35, 1990 Fritidsmotorsegelbåt SFC‐7007 FREJA 3.87 11.95 Yanmar 3JH2E, 1997 Fritidsmotorsegelbåt SFC‐8275 AIKA 4.00 11.90 Ford Lehman SP90, 1991 Fritidsmotorsegelbåt SFC‐6744 AURORA 3.95 11.90 Perkins 4.108 Fritidsmotorsegelbåt SFB‐8284 ELIONOR 3.82 11.86 Ford diesel typ 2711 1976 Fritidsmotorsegelbåt SFC‐6954 NIRVANA 3.85 11.85 Volvo Penta MD 2030,1998 Fritidsmotorsegelbåt SFC‐7048 SOCI 3.58 11.85 Diesel Universal 5444 Fritidsmotorsegelbåt SFC‐7148 FRI 3.30 11.85 Volvo Penta 01‐55,2004 Fritidsmotorsegelbåt SFC‐3483 CARMEN 3.84 11.85 Volvo Penta MD50A Fritidsmotorsegelbåt SFC‐7063 AYLA 3.87 11.83 Volvo Penta D2‐55,2004 Fritidsmotorsegelbåt SFC‐7087 STILL FREELANCE 3.76 11.82 Yanmar 3GM, 1997 Fritidsmotorsegelbåt SFC‐8513 ST GRAIUS 3.83 11.81 Yanmar 3 HMF 30 Fritidsmotorsegelbåt SFC‐3497 ELLY 4.60 11.80 Volvo Penta MD50A Fritidsmotorsegelbåt 96

SFC‐7262 MISS ELLIE 3.40 11.80 Ford 2715 E, 1976 Fritidsmotorsegelbåt SFC‐8634 SEAMILES 3.85 11.79 Volvo Penta MD 2040 2002 Fritidsmotorsegelbåt SFC‐5178 MODER 4.14 11.78 Scandia 1972 Fritidsmotorsegelbåt SFC‐8092 PANACEA 3.50 11.75 Volvo Penta MD30, 1989 Fritidsmotorsegelbåt SFC‐7872 ROBBI 3.60 11.75 Yanmar 4JH4 200 Fritidsmotorsegelbåt SFC‐6737 VIDFARE 3.50 11.75 Volvo Penta MD31, ‐94 Fritidsmotorsegelbåt SFC‐8270 SURYA 3.99 11.75 Volvo Penta MD22L, 1999 Fritidsmotorsegelbåt SFC‐8852 IKAROZ 3.90 11.72 Volvo Penta D2‐40, 2007 Fritidsmotorsegelbåt SFC‐8892 OTTILIA II AF PETERSBURG 3.67 11.70 Volvo P2 40 Fritidsmotorsegelbåt SFC‐3619 TITTI IV 3.11 11.70 BMC Captain Fritidsmotorsegelbåt SFC‐7891 VENTI 3.82 11.67 Volvo Penta, 2006 Fritidsmotorsegelbåt SFC‐8235 INSPIRO 3.85 11.65 Yanmar,1987 Fritidsmotorsegelbåt SFC‐8516 SVEA 3.74 11.64 Volvo Penta D55, 2002 Fritidsmotorsegelbåt SFC‐8199 OCTAV 3.20 11.60 MD17C, 1977 Fritidsmotorsegelbåt SFC‐7430 THE SPICE II 3.65 11.60 MD 21 B, 1983 Fritidsmotorsegelbåt SFC‐7837 LENA 3.65 11.60 Volvo Penta MD21B,1985 Fritidsmotorsegelbåt SFC‐7840 SPIRIT OF 3.76 11.60 Yanmar 3 HMF Fritidsmotorsegelbåt SFC‐7937 FORTUNA 3.48 11.57 Volvo Penta MD22, 2000 Fritidsmotorsegelbåt SFC‐7255 SWINGLISH 3.65 11.55 Yanmar 4JH4‐E Fritidsmotorsegelbåt SFC‐7296 BIFROST 3.38 11.55 Volvo Penta MD31A, 1990 Fritidsmotorsegelbåt SFC‐7264 PINELLA 3.68 11.55 Volvo Penta 2030C, 1999 Fritidsmotorsegelbåt SFC‐7468 EGGSKÄR 3.68 11.55 Volvo Perkins MD2030,‐01 Fritidsmotorsegelbåt SFC‐7841 SPRAY 3.65 11.55 Yanmar 4JH4‐E Fritidsmotorsegelbåt SFC‐7829 GARM 3.50 11.50 3 cyl.Perkins, 1970 Fritidsmotorsegelbåt SFC‐8792 DIVAN 3.54 11.50 VP D2‐4, 2008 Fritidsmotorsegelbåt SFC‐4935 WANNABE 3.40 11.50 Volvo Penta MD29 1969 Fritidsmotorsegelbåt SFC‐8443 LEVANA 3.50 11.50 Ford, 1967 Fritidsmotorsegelbåt SFC‐3378 SOUTH SEA 3.50 11.50 Ford 2712E Fritidsmotorsegelbåt SFC‐8140 CALYPSO 3.40 11.42 Fritidsmotorsegelbåt 97

SFC‐7579 JUSTINE 3.60 11.40 Yanmar 3JH4E, 2005 Fritidsmotorsegelbåt SFC‐5632 NORDWIND 3.65 11.40 Perkins 4236 4 cyl Fritidsmotorsegelbåt SFC‐8414 NEMO 3.40 11.40 Volvo Penta MD3B, 1974 Fritidsmotorsegelbåt SFC‐8514 CYGNE BLEU 3.60 11.40 Volvo Penta 2030, 1999 Fritidsmotorsegelbåt SFC‐8509 BLÅTUNGA 3.93 11.37 Volvo MD30, 2004 Fritidsmotorsegelbåt SFC‐8603 TINGELING 3.75 11.35 Yanmar 3JH4E Fritidsmotorsegelbåt SFC‐8158 ANNA SOFIA 3.48 11.35 Diesel, 1998 Fritidsmotorsegelbåt SFC‐8662 ANNIARA 3.80 11.35 Volvo Penta D2‐40B, 2007 Fritidsmotorsegelbåt SFC‐7473 TRAMONTANA 3.80 11.35 ED3321‐U‐600240K,1984 Fritidsmotorsegelbåt SFC‐8766 ALTAIR 3.48 11.35 Yanmar 3JH, 1997 Fritidsmotorsegelbåt SFC‐8356 AMANDA FRISCO 3.80 11.35 Volvo Penta Fritidsmotorsegelbåt SFC‐8914 MIRAGE II 3.65 11.33 Perkins Fritidsmotorsegelbåt SFC‐6767 CRUSADER 3.55 11.31 Volvo Penta MD22, 1995 Fritidsmotorsegelbåt SFC‐3722 LADY MONTANA 3.30 11.30 Perkins 4.108 1982 Fritidsmotorsegelbåt SFB‐7914 AKAIA 3.66 11.30 Ford Diesel 27/11 1978 Fritidsmotorsegelbåt SFC‐7411 IRONI 3.60 11.30 VP MD 17 C, diesel Fritidsmotorsegelbåt SFC‐7046 GALEJAN 3.65 11.30 Yanmar 4JH3‐BE Fritidsmotorsegelbåt SFC‐7791 RANI 3.60 11.30 Yanmar 3614, 1993 Fritidsmotorsegelbåt SFC‐8170 VIRGO 3.65 11.28 Volvo MD 2030, 1995 Fritidsmotorsegelbåt SFC‐8560 COQUELICOT 3.86 11.20 Perkins 4108, 1983 Fritidsmotorsegelbåt SFC‐7806 CADENCIA 3.45 11.20 VP 2003 T, 1993 Fritidsmotorsegelbåt SFC‐7768 AVATARA 2 3.45 11.20 Fritidsmotorsegelbåt SFC‐8821 SEA WIND 3.45 11.20 Yanmar 4JH2E, 1998 Fritidsmotorsegelbåt SFC‐8681 LINN 3.80 11.20 Volvo Penta DI‐30 Fritidsmotorsegelbåt SFC‐6841 BORITA II 3.48 11.19 Penta MD22L, 1994 Fritidsmotorsegelbåt SFC‐7415 BALP 3.35 11.10 Volvo Penta MD 31 Fritidsmotorsegelbåt SFC‐7534 HALINA 3.80 11.10 Yanmar 3GM30F, 2000 Fritidsmotorsegelbåt SFC‐7868 MADAME 3.35 11.10 Yanmar, 1999 Fritidsmotorsegelbåt SFC‐8392 ELLINOR 3.84 11.10 Yanmar 2GM 20, 1999 Fritidsmotorsegelbåt 98

SFC‐7853 ARKONA II 3.16 11.08 VolvoPenta MD11/110S,1980 Fritidsmotorsegelbåt SFC‐8230 ATHENA 3.63 11.07 Yanmar 3HM35HP Fritidsmotorsegelbåt SFC‐8751 MAGNOLIA 3.13 11.07 MD IIC, 1981 Fritidsmotorsegelbåt SFC‐7932 LA SIRENA 3.13 11.07 Yanmar 3HM, 1987 Fritidsmotorsegelbåt SFC‐7230 ARWEN 3.95 11.05 VP MD21A, 1977 Fritidsmotorsegelbåt SFC‐6783 PADDINGTON 3.95 11.05 VP MD 22L ‐01 Fritidsmotorsegelbåt SFC‐5074 CATTIE 3.25 11.05 Ford 2712E Fritidsmotorsegelbåt SFC‐8433 BORAGO 2.44 11.04 Yamaha, 1992 Fritidsmotorsegelbåt SFC‐7065 VILDRENEN 3.60 11.03 Yanmar 3GM30FC, 1999 Fritidsmotorsegelbåt SFC‐7780 MAIKEN 3.20 11.00 Yanmar Diesel, 2000 Fritidsmotorsegelbåt SFC‐8019 PELICAN BOTER 3.60 11.00 Ford 2725 E, 1996 Fritidsmotorsegelbåt SFC‐7554 STERNA 5.40 11.00 2 x Volvo 2020, 94 Fritidsmotorsegelbåt SFC‐8870 JOSHUA 3.65 11.00 MD 2003, 1985 Fritidsmotorsegelbåt SFB‐8975 ELIZABETH 3.63 11.00 Yanmar 3QM30 1977 Fritidsmotorsegelbåt SFC‐8220 EMILY ROSE 3.70 10.95 VP 2030 Diesel Fritidsmotorsegelbåt SFC‐8317 VÅGSPEL 3.15 10.94 Yanmar, 1984 Fritidsmotorsegelbåt SFC‐7954 TERPSICHORE 3.36 10.90 Mercedes OM636, 1979 Fritidsmotorsegelbåt SFC‐7010 DOBEDO 3.40 10.90 Merceders OM 636 Fritidsmotorsegelbåt SFC‐8539 PRIMA DONNA 3.40 10.90 VP D2‐40, 2007 Fritidsmotorsegelbåt SFC‐8008 RESOLUTA 2.74 10.88 Volvo Penta 2003, 1992 Fritidsmotorsegelbåt SFC‐7180 GREIP 2.74 10.88 Lombardini LW1003M, 2001 Fritidsmotorsegelbåt SFC‐7131 MÉDOC 3 3.50 10.85 Yanmar 3GM30,‐87 Fritidsmotorsegelbåt SFB‐7780 VIKTORIA 3.50 10.85 Mercedes Benz Fritidsmotorsegelbåt SFC‐6613 MARI 3.50 10.85 Bedford 330M, 1973 Fritidsmotorsegelbåt SFC‐7091 LA FOLIA 3.06 10.84 Volvo Penta MD11C 33391 Fritidsmotorsegelbåt SFC‐7399 TESLA 2.75 10.80 VP MD7A 110‐S, 1979 Fritidsmotorsegelbåt SFC‐7533 ADALALSA 3.30 10.80 Ford Lehman 2722E 1985 Fritidsmotorsegelbåt SFC‐7417 GARMA 3.48 10.80 Volvo PentaND 2030, 2001 Fritidsmotorsegelbåt SFC‐7325 EMMI 3.40 10.75 Volvo Penta 2003 T Fritidsmotorsegelbåt 99

SFC‐6821 HILDA 3.40 10.75 MD11C, 1982 Fritidsmotorsegelbåt SFC‐7777 PHILULA III 3.40 10.75 Nanni 4.150SD, 2004 Fritidsmotorsegelbåt SFC‐8511 MY NOW 3.49 10.75 Yanmar 3YM30, 2005 Fritidsmotorsegelbåt SFC‐8567 JOHELINA 3.20 10.74 VP Md22, 1999 Fritidsmotorsegelbåt SFC‐7284 ELVIRA 3.30 10.72 VP 2030, 2004 Fritidsmotorsegelbåt SFC‐7024 CHRISTINA 3.30 10.72 Volvo Penta Diesel, 2003 Fritidsmotorsegelbåt SFC‐6835 LOVA NOVA 3.20 10.70 Yanmar 3GH30F 2002 Fritidsmotorsegelbåt SFC‐7310 ALENE 3.30 10.70 Volvo Penta MD11D Fritidsmotorsegelbåt SFC‐7101 ZORBA 3.60 10.70 MD 11C, 1979 Fritidsmotorsegelbåt SFC‐7912 CALETA 3.56 10.70 Yanmar 3JH2E, 1996 Fritidsmotorsegelbåt SFC‐8665 CLAUDIE 3.25 10.70 Yanmar 3cyl. serienr 11940 Fritidsmotorsegelbåt SFC‐7371 M.J. SISTER 3.30 10.67 Volvo MD2, 1978 Fritidsmotorsegelbåt SFC‐6807 KYOUNG‐SOOK 3.10 10.65 Perkins 4.108 Fritidsmotorsegelbåt SFC‐7080 MASCOT 3.40 10.65 Volvo Penta BT2003 1991 Fritidsmotorsegelbåt SFC‐8159 ACANTHA 3.40 10.60 Yanmar 27 PS, 1989 Fritidsmotorsegelbåt SFC‐3925 MINANDRA 3.13 10.60 Perkins dielse 4.236M Fritidsmotorsegelbåt SFC‐5203 FORTUNA 3.12 10.60 Perkins 4.236 1972 Fritidsmotorsegelbåt SFB‐7151 HELLEN 3.13 10.60 Perkins diesel 4.236 1970 Fritidsmotorsegelbåt SFC‐8908 LADY ANN 3.38 10.54 VP D2‐55, 2001 Fritidsmotorsegelbåt SFC‐7570 MISS BLUE 3.38 10.54 Volvo Penta MD 21 B Fritidsmotorsegelbåt SFC‐6738 MARIA HONUNGSHÖST 3.38 10.54 Volvo Penta MD22L, 2001 Fritidsmotorsegelbåt SFC‐8106 AQUILA 3.38 10.54 VP 2003T, 1987 Fritidsmotorsegelbåt SFC‐6817 CARMEN 3.45 10.54 MB 21 Volvo Penta ‐80 Fritidsmotorsegelbåt SFC‐8682 GERONIMO 3.14 10.51 VP MD2020, 1996 Fritidsmotorsegelbåt SFC‐7214 TONIKA 3.05 10.50 Perkins 4.107 Fritidsmotorsegelbåt SFC‐6784 CONSTANZIA 3.05 10.50 MD22, 2001 Fritidsmotorsegelbåt SFC‐7763 IMPULS 3.38 10.50 Volvo Penta 2003, 1989 Fritidsmotorsegelbåt SFC‐8876 EMBLA 3.05 10.50 Yanmar 3JH2E, 2000 Fritidsmotorsegelbåt SFC‐7291 ANEMOS II 3.05 10.50 Volvo Penta MD21, 1976 Fritidsmotorsegelbåt 100

SFC‐4968 NIKONIKA 3.05 10.50 Volvo Penta MD21 1973 Fritidsmotorsegelbåt SFC‐4461 ANGELICA 3.05 10.50 Volvo Penta MD21 Fritidsmotorsegelbåt SFC‐8207 SKRUBBEN 3.10 10.45 VP MD3B Fritidsmotorsegelbåt SFC‐7020 XAVITA IV 3.10 10.45 Volvo Penta MD17C, 1979 Fritidsmotorsegelbåt SFC‐7476 KALLISTE 3.10 10.45 VolvoPenta MD17C, 1980 Fritidsmotorsegelbåt SFC‐7113 BEATA 3.50 10.40 Volvo Penta, 2003 Fritidsmotorsegelbåt SFC‐7382 GRÅGÅS 3.40 10.40 Lombardini 1404M, 2001 Fritidsmotorsegelbåt SFC‐8502 TUULIKKI 3.15 10.40 Volvo Penta MD3 Fritidsmotorsegelbåt SFC‐3408 COLONEL 3.00 10.40 Volvo Penta MD2002 Fritidsmotorsegelbåt SFC‐7364 HENNY 3.02 10.36 Volvo Penta MD47 B Fritidsmotorsegelbåt SFC‐8318 JENNIFER 3.40 10.35 Yanmar 3GM 30F, 2003 Fritidsmotorsegelbåt SFC‐7988 AVANTI 3.40 10.35 Yanmar 3YM20,2005 Fritidsmotorsegelbåt SFC‐7836 AMILLIA 3.40 10.35 VP 2020, 2003 Fritidsmotorsegelbåt SFC‐7773 JEANETTE 3.29 10.30 Yanmar E 24421, 1999 Fritidsmotorsegelbåt SFC‐7086 AYSIN 3.35 10.30 Volvo Penta Fritidsmotorsegelbåt SFC‐7016 NIGHT 3.10 10.30 Volvo Penta MD3B, 1975 Fritidsmotorsegelbåt SFC‐7239 LENA 3.35 10.30 Volvo Penta MD2020, ‐04 Fritidsmotorsegelbåt SFC‐3485 LINUS II 2.90 10.30 Volvo Penta MD21 Fritidsmotorsegelbåt SFC‐8869 SOMMARVIND 3.00 10.30 Yanmar 2GM Fritidsmotorsegelbåt SFC‐7186 NOCTILUCA 3.42 10.28 Volvo Penta MD2030,‐02 Fritidsmotorsegelbåt SFC‐6834 FREJA 3.33 10.28 VP 2003, 1986 Fritidsmotorsegelbåt SFC‐6753 WINDÖGA 3.42 10.28 Volvo 2030, 1995 Fritidsmotorsegelbåt SFC‐8025 ACAMAR 3.00 10.28 Yanmar 3GM30F, 2002 Fritidsmotorsegelbåt SFC‐7888 WILMA 2.95 10.25 Yanmar 3JH3GBE, 2003 Fritidsmotorsegelbåt SFC‐5119 MESSIMERI 2.95 10.25 Volvo Penta MD21 1984 Fritidsmotorsegelbåt SFC‐6532 BON BON 3.21 10.21 Volvo Penta MD11 110S Fritidsmotorsegelbåt SFC‐7946 APOLLONIA 3.51 10.21 Yanmar 3YM30 Fritidsmotorsegelbåt SFC‐8530 KOF 3.48 10.20 Volvo Penta MD2030, 2005 Fritidsmotorsegelbåt SFC‐7037 HOLIDAY 3.48 10.20 Volvo Penta MD2040 Fritidsmotorsegelbåt 101

SFC‐6591 RONJA 3.40 10.20 Volvo Penta 2003T, 1989 Fritidsmotorsegelbåt SFC‐6733 TYRWILD 3.33 10.20 Volvo Penta MD 17 D Fritidsmotorsegelbåt SFC‐7452 MANDALAY 3.33 10.20 Volvo Penta MD17, 1981 Fritidsmotorsegelbåt SFC‐7900 SECOND LIFE 3.48 10.20 Volvo Penta, 2004 Fritidsmotorsegelbåt SFC‐8186 AWAPUHI 3.26 10.10 Ford marine diesel Fritidsmotorsegelbåt SFC‐8407 NOATUNE 3.25 10.10 Ford 2712E, 1979 Fritidsmotorsegelbåt SFC‐5735 GRILLAN 3.25 10.10 Volvo Penta MD47 1961 Fritidsmotorsegelbåt SFC‐6012 CATJA 3.26 10.10 Perkins diesel 1985 Fritidsmotorsegelbåt SFC‐6220 ECHO IV 3.25 10.10 Volvo Penta MD40A Fritidsmotorsegelbåt SFC‐5933 MARTINA 3.26 10.10 MD 47 Fritidsmotorsegelbåt SFC‐4032 LADY MARIA 3.26 10.10 Tempest Commodore 1974 Fritidsmotorsegelbåt SFC‐6681 MEJJA 3.35 10.10 Beta Marine BD 722 2000 Fritidsmotorsegelbåt SFC‐4828 AURORA 3.25 10.10 Sealord 5,7 1970 Fritidsmotorsegelbåt SFC‐7126 MOON CAT 3.35 10.10 Ford 2712 E, 1979 Fritidsmotorsegelbåt SFC‐8172 GRETA GARBO 3.30 10.10 VolvoPenta MD 2030 DBT Fritidsmotorsegelbåt SFC‐8175 BLUE DREAM 3.25 10.10 Perkins 4236, 1971 Fritidsmotorsegelbåt SFC‐8657 RINA 3.30 10.10 VP MD11, 1981 Fritidsmotorsegelbåt SFC‐8787 MADAM 3.26 10.10 FORD 2712, 1979 Fritidsmotorsegelbåt SFC‐7982 X‐ON LINE 3.30 10.06 Yanmar Fritidsmotorsegelbåt SFC‐8020 CABRIMA 3.45 10.00 3GM30, 2001 Fritidsmotorsegelbåt SFC‐8174 SAKANA 3.40 10.00 Volvo Penta 2030S, 1993 Fritidsmotorsegelbåt SFC‐7532 BLUE DUCK 3.00 10.00 Bukh 3869, 1986 Fritidsmotorsegelbåt SFB‐7563 ETERNITY 3.05 10.00 Volvo Penta MD21 1971 Fritidsmotorsegelbåt SFB‐8917 YTIC 3.15 10.00 Volvo MD32 1969 Fritidsmotorsegelbåt SFC‐7176 JOHANNA 3.30 10.00 Yanmar 3 HM 35 Fritidsmotorsegelbåt SFC‐6827 RAHMANI 3.60 9.99 Volvo 2 DB Fritidsmotorsegelbåt SFB‐6619 BLUE MARLIN 3.35 9.99 Highpowermarine JAM1210 Fritidsmotorsegelbåt SFC‐8297 COYOTE 6.25 9.99 Yamaha 9,9 Fritidsmotorsegelbåt SFC‐7029 NAUSIKAA 3.26 9.98 MD 2030 Fritidsmotorsegelbåt 102

SFC‐7354 LINNÉA 3.18 9.90 Nanni diesel, 2003 Fritidsmotorsegelbåt SFC‐7015 MÅNSTRÅLEN 3.25 9.90 Volvo Penta 2002/1985 Fritidsmotorsegelbåt SFC‐6731 JAJJA 3.25 9.90 VP MD 2030 2002 Fritidsmotorsegelbåt SFC‐7851 ALETEIA 3.18 9.89 VolvoPenta MD17D,1983 Fritidsmotorsegelbåt SFC‐8093 KAIROS 3.18 9.89 MD2B, 1978 Fritidsmotorsegelbåt SFC‐8103 HULDA 3.18 9.89 Volvo Penta DI‐30, 2005 Fritidsmotorsegelbåt SFC‐5977 LA VIATA 3.20 9.87 Volvo Penta MD11C Fritidsmotorsegelbåt SFC‐7856 VICKI 3.27 9.85 Yanmar diesel 1985 Fritidsmotorsegelbåt SFC‐7190 SOMMERWIND 3.15 9.83 MD 2030, 1998 Fritidsmotorsegelbåt SFC‐7088 VIRGO 3.33 9.81 V.P.2003, 1990 Fritidsmotorsegelbåt SFC‐7125 KALLA 2.88 9.81 Lombardini LDW 1003 M Fritidsmotorsegelbåt SFC‐6748 NORTHERN DUCK 3.33 9.81 Yanmar 3JH 3E, 1999 Fritidsmotorsegelbåt SFC‐8206 MOBY DICK 2.88 9.81 Yanmar 36M30, 1999 Fritidsmotorsegelbåt SFC‐7327 LÄRKAN 2.88 9.81 Volvo Penta MD2040‐DBT,03 Fritidsmotorsegelbåt SFC‐8683 ENISE 3.23 9.75 Volvo Penta MD 11 C, 1979 Fritidsmotorsegelbåt SFC‐8786 PACIFIC SPIRIT 3.35 9.75 Universal M40, 1981 Fritidsmotorsegelbåt SFC‐6816 NADA 2.88 9.71 Yanmar 3GM30F, 1988 Fritidsmotorsegelbåt SFC‐8121 SEA QUILL 3.20 9.70 Yanmar, 2003 Fritidsmotorsegelbåt SFC‐7269 MARELD 3.10 9.65 Yanmar 2GM, 1991 Fritidsmotorsegelbåt SFC‐3578 STORMFÅGELN 3.13 9.65 Perkins Fritidsmotorsegelbåt SFC‐8830 TEKLA 3.30 9.62 Volvo Penta D1‐20 Fritidsmotorsegelbåt SFC‐7309 ALFRIDA III 3.00 9.58 Volvo penta MD11C, 1980 Fritidsmotorsegelbåt SFC‐8597 TINDRA II 3.00 9.56 Volvo Penta MD 2030, 2002 Fritidsmotorsegelbåt SFC‐8640 CARPE DIEM 3.05 9.55 Yanmar 3JH 4BE Fritidsmotorsegelbåt SFC‐6762 CALISTA 3.05 9.55 Volvo Penta MD 17C 1980 Fritidsmotorsegelbåt SFC‐8598 ISETTE 2.98 9.55 Volvo Penta MD II C Fritidsmotorsegelbåt SFC‐8532 YVONNE 2.90 9.55 IVECO M40, 2004 Fritidsmotorsegelbåt SFC‐8181 TAMBUKA 3.20 9.54 Volvo Penta S‐drive,2002 Fritidsmotorsegelbåt SFC‐8383 MYC 4 3.27 9.50 Volvo Penta 2002/1990 Fritidsmotorsegelbåt 103

SFC‐7796 LEJOHANNA 3.20 9.50 Lombardini, 2004 Fritidsmotorsegelbåt SFC‐6772 MY LIFE 3.10 9.50 Yanmar 1989 Fritidsmotorsegelbåt SFC‐8242 GUNGNER 3.20 9.50 Vetus diesel 2006 Fritidsmotorsegelbåt SFC‐7378 ANNIE 2.80 9.50 Volvo Penta MD6B, 1976 Fritidsmotorsegelbåt SFB‐8897 FIA 3.10 9.50 Volvo 2003 Fritidsmotorsegelbåt SFC‐8385 NELLY MORGAN 2.65 9.50 VP 2030, 1998 Fritidsmotorsegelbåt SFC‐4979 LASANNA 3.20 9.50 Volvo Penta MD11C 1980 Fritidsmotorsegelbåt SFC‐7816 MEJA 3.29 9.45 Volvo Penta DI‐20,‐05 Fritidsmotorsegelbåt SFC‐7869 SELMA 2.65 9.41 Yanmar 2GM20F, 1998 Fritidsmotorsegelbåt SFC‐8556 CARPE VENTUM 3.20 9.40 Volvo Penta 2020, 2003 Fritidsmotorsegelbåt SFC‐8004 MILONGA 6.84 9.40 Yamaha, 2002 Fritidsmotorsegelbåt SFC‐7236 NANOQ 3.05 9.40 Volvo 2003T, 1993 Fritidsmotorsegelbåt SFC‐7302 VAGABOND 3.05 9.40 Yanmar 3GM30F, 1998 Fritidsmotorsegelbåt SFC‐8060 ARRANDIR 3.05 9.40 Volvo Penta MD7 Fritidsmotorsegelbåt SFC‐8375 KARIN LINNEA 2.00 9.40 Fritidsmotorsegelbåt SFC‐6355 VIRGO 3.20 9.38 Volvo Penta 2002 1984 Fritidsmotorsegelbåt SFC‐6743 MIMER II 2.87 9.36 Volvo Penta MD 11 C, 1977 Fritidsmotorsegelbåt SFC‐7519 LUCCA 2.87 9.36 Volvo Penta MD11C, 1979 Fritidsmotorsegelbåt SFC‐8225 WINDY 2.87 9.36 Volvo Penta MD 11C Fritidsmotorsegelbåt SFC‐8273 PÄRLAN 3.07 9.35 Fritidsmotorsegelbåt SFC‐8396 INGA‐LÅN II 2.78 9.33 VETUS D 13,2005 Fritidsmotorsegelbåt SFC‐7184 SHAG 2.78 9.33 Yanmar Diesel, 1975 Fritidsmotorsegelbåt SFC‐7019 ALLIE 2.76 9.33 Yanmar YSB12 1979 Fritidsmotorsegelbåt SFC‐8798 WINDHOVER 3.00 9.30 Yanmar 3GM30, 2003 Fritidsmotorsegelbåt SFC‐5493 NJORD 2.76 9.25 Volvo Penta MD3B Fritidsmotorsegelbåt SFC‐8050 RAAN 2.96 9.20 Sole Diesel Fritidsmotorsegelbåt SFC‐8146 TODELO 2.96 9.14 Volvo Penta 2002, 1987 Fritidsmotorsegelbåt SFC‐6729 TONITA 2.96 9.14 VolvoPenta 2002 BBT 94 Fritidsmotorsegelbåt SFC‐8643 MARY‐ANNE 2.96 9.14 Volvo Penta MD6A, 1974 Fritidsmotorsegelbåt 104

SFC‐6778 ARVIDA 3.18 9.10 VP MD 2030‐D, 2001 Fritidsmotorsegelbåt SFC‐6879 TESSA IV 3.00 9.07 Yanmar YSN 12 gr Fritidsmotorsegelbåt SFC‐8149 YVETTE 3.02 9.02 OZecoDrive, 2005 Fritidsmotorsegelbåt SFC‐8668 ARCTICA 2.80 9.00 Volvo Penta 2002, 1987 Fritidsmotorsegelbåt SFC‐6788 WIRGO II 2.80 9.00 Volvo Penta MD 7A, 1980 Fritidsmotorsegelbåt SFC‐7322 2.60 8.86 Yanmar Y5B8G ‐ 293/1976 Fritidsmotorsegelbåt SFC‐8367 INO 2.60 8.86 Solé Diesel MINI‐17,1992 Fritidsmotorsegelbåt SFC‐7362 ISIS 2.50 8.80 Honda, utombordare Fritidsmotorsegelbåt SFC‐8001 SPINIFEX 2.60 8.80 Yanmar Diesel, 1974 Fritidsmotorsegelbåt SFC‐4930 MADRE MIA 2.80 8.80 Volvo Penta MB10A Fritidsmotorsegelbåt SFC‐8423 GLORY 3.22 8.75 Yanmar, 2006 Fritidsmotorsegelbåt SFC‐4304 PINGA WINGA 3.25 8.75 Volvo Penta 2003 1991 Fritidsmotorsegelbåt SFC‐3645 AIDA 3.05 8.75 Volvo Penta MD3B Fritidsmotorsegelbåt SFB‐2038 MI 1 3.01 8.72 Perkins Fritidsmotorsegelbåt SFC‐8861 PIERINA 2.93 8.57 Yanmar 2YM15 E00382 Fritidsmotorsegelbåt SFC‐7772 LELISE 2.84 8.56 GM 10, 2003 Fritidsmotorsegelbåt SFC‐7981 GLÖMSAN 2.05 8.55 Thohatsu Fritidsmotorsegelbåt SFC‐7332 CARRIGALOE 2.95 8.54 MD 7115, 1978 Fritidsmotorsegelbåt SFB‐8610 ELISE 2 3.05 8.50 Mercedes Fritidsmotorsegelbåt SFC‐8745 KARIAM OF GLENCOE 3.00 8.47 Fritidsmotorsegelbåt SFC‐5736 DAFNE 2.90 8.40 Volvo Penta MD7A Fritidsmotorsegelbåt SFC‐5749 STELLA MARIS 3.00 8.35 D50 1982 Fritidsmotorsegelbåt SFC‐8211 SISKA 2.50 8.34 Yanmar, 1 cyl, 1989 Fritidsmotorsegelbåt SFC‐7079 MARE 2.65 8.30 Solé Mini 17, 1998 Fritidsmotorsegelbåt SFC‐7282 VIOLA 2.65 8.30 IVECO AIFO 4021 M 20/04 Fritidsmotorsegelbåt SFC‐8721 GRACE 2.18 8.28 Yamaha Fritidsmotorsegelbåt SFC‐8722 BEAGONVILLE 2.46 8.25 Albin 021, 1968 Fritidsmotorsegelbåt SFC‐8694 IDA 2.46 8.25 Yanmar 2GM, 1983 Fritidsmotorsegelbåt SFC‐8785 DORY 2.46 8.25 Perkins M20 Fritidsmotorsegelbåt 105

SFC‐8298 IKTORIA 2.46 8.25 Volvo Penta MDGA,1975 Fritidsmotorsegelbåt SFC‐7979 ON THE ROCKS 2.46 8.25 Albin 0‐22 kombi, 1970 Fritidsmotorsegelbåt SFC‐7369 2.46 8.25 Albin 021 Kombi Fritidsmotorsegelbåt SFC‐8658 2.46 8.25 Volvo‐Penta MD7A Fritidsmotorsegelbåt SFC‐8382 MAJA 2.46 8.25 MDBA, 1973 Fritidsmotorsegelbåt SFC‐8411 HUNK 2.46 8.25 Albin 021, 1972 Fritidsmotorsegelbåt SFC‐7049 MAKAI 2.33 8.23 Yanmar YSM12G 82 Fritidsmotorsegelbåt SFC‐8406 SÅNGMÖN 2.80 8.15 Diesel Volvo MD2B, 1974 Fritidsmotorsegelbåt SFC‐8578 SOLAN II 2.80 8.15 Volvo Penta MD, 1979 Fritidsmotorsegelbåt SFB‐8557 EIDERN II 2.23 8.08 Sabb diesel Fritidsmotorsegelbåt SFB‐7481 PRIMO ROSA 2.85 8.05 Volvo Penta MD2B 1973 Fritidsmotorsegelbåt SFC‐7370 AHKKA 2.76 8.03 Volvo Penta MD2020, 2005 Fritidsmotorsegelbåt SFC‐8762 LA BONITA 2.76 8.03 Kubota ZL‐600, 1986 Fritidsmotorsegelbåt SFC‐8430 RASTAREN 2.49 8.00 Mercury, 2004 Fritidsmotorsegelbåt SFC‐7919 WAIKIKI 2.80 8.00 MD 7 B, 1988 Fritidsmotorsegelbåt SFC‐6747 LA BLANCHE 2.76 8.00 Lombardini LDW702, 2000 Fritidsmotorsegelbåt SFC‐5595 STENYA 2.60 8.00 Yanmar 15QM20 1979 Fritidsmotorsegelbåt SFC‐7586 CISSI 4.60 7.92 Yamaha 4AC Fritidsmotorsegelbåt SFC‐8286 ARKEN 2.39 7.87 Suzuki Fritidsmotorsegelbåt SFC‐7193 GALADRIEL 2.39 7.87 Suzuki Fritidsmotorsegelbåt SFC‐7237 LION 2.39 7.87 Mercury, 2002 Fritidsmotorsegelbåt SFC‐6146 CARA MIA 2.95 7.85 Volvo Penta MD11C 1980 Fritidsmotorsegelbåt SFC‐7827 ALMAZ 2.25 7.85 Evinrude B006 200 Fritidsmotorsegelbåt SFB‐6459 CARPE DIEM 2.95 7.85 Volvo Penta MD11C 1980 Fritidsmotorsegelbåt SFC‐8134 ENZO 2.60 7.80 Volvo‐Penta MD5A, 1980 Fritidsmotorsegelbåt SFC‐7576 DYNING 2.65 7.80 Yanmar 2GM20 Fritidsmotorsegelbåt SFC‐6854 VICTORIA 2.50 7.70 Yanmar SB8G, 1977 Fritidsmotorsegelbåt SFC‐8090 WINDCHASER 2.50 7.50 Yanmar HDAC402741,1976 Fritidsmotorsegelbåt SFC‐8826 SOPRANO 2.30 7.35 Volvo Penta MD 5B, 1979 Fritidsmotorsegelbåt 106

SFC‐8832 REGINA 2.61 6.90 Volvo Penta MD2B Fritidsmotorsegelbåt SFC‐7950 ANDREA 2.20 6.30 Fritidsmotorsegelbåt SFC‐7175 INSHALLAH 2.16 6.09 Utombordsmotor Fritidsmotorsegelbåt SFC‐7905 JAZZVA 2.50 6.00 Jamaha, utombordare Fritidsmotorsegelbåt SFB‐6508 BOHEME 2.20 6.00 Mercury Fritidsmotorsegelbåt SFC‐7886 SJÖJUNGFRUN 3.55 11.32 Yanmar 4JH4E, 2006 Fritidsmotorsegelbåten SFC‐8793 ARCTIC 4.03 11.99 Perkins 4154, 1990 Fritidssegelbåt SFC‐8791 SEABORN 3.11 11.13 Perkins M25, 1991 Fritidssegelbåt SFC‐6830 EVA IV 3.80 10.62 Yanmar 1995 Fritidssegelbåt SFC‐8813 KAJSA 3.38 10.54 VOLVO PENTA 2003T, 86 Fritidssegelbåt SFC‐3717 COBACA 3.30 10.20 Fritidssegelbåt SFC‐6670 HAGUMACA 3.33 10.20 Volvo Penta MD 17 D Fritidssegelbåt SFC‐8912 NUKA 3.46 9.99 Volvo Penta MD 2020 Fritidssegelbåt SFC‐7545 EMELIN 2.88 9.88 Fritidssegelbåt SFC‐6656 DAPHNE 3.05 9.40 Volvo MD 7B Fritidssegelbåt SFC‐8922 CANTARE 2.78 9.33 Yanmar ,1977 Fritidssegelbåt SFC‐8617 TUA TUA II 2.50 8.34 Nanni Diesel 2,45 E10, 2000 Fritidssegelbåt SFC‐3350 SKUM II 2.20 7.85 Fritidssegelbåt SFC‐3566 LILLA BLÅ 2.00 6.00 Fritidssegelbåt GARVARN AV SFB‐7281 KAPPELSHAMN 1.84 5.86 Fritidssegelbåt SFC‐3309 LILLE ORM 1.75 5.34 Fritidssegelbåt SFC‐3824 BRIS 1.60 4.80 Fritidssegelbåt SFC‐7590 YRVIND 0.96 4.10 Fritidssegelbåt SFC‐6253 CACHEETAH 4.76 11.75 Perkins Fritidssegelkatamaran SFB‐8223 MARIA 3.76 16.50 Scania D11 1965 Fritidssegelmotorbåt SFC‐3295 FAST LANE 3.00 16.00 Volvo Penta MD11D Fritidssegelmotorbåt SFC‐6165 ZILVER 3.30 15.45 Volvo Penta 2003T 1986 Fritidssegelmotorbåt SFC‐5026 GRISONE 3.50 15.05 Volvo Penta MD21 1976 Fritidssegelmotorbåt 107

SFB‐7359 DAPHNE 3.65 14.90 Perkins Diesel 1961 Fritidssegelmotorbåt SFB‐8663 LYNX 3.26 14.40 Volvo Penta MD17D 1984 Fritidssegelmotorbåt SFC‐6183 EMMA 3.78 14.13 Volvo Penta MD30 1986 Fritidssegelmotorbåt SFC‐4507 MAJOKA 3.30 14.10 Isuzu UMC24 Fritidssegelmotorbåt SFC‐3368 SALSA 3.00 14.00 Volvo Penta MD17C Fritidssegelmotorbåt SFC‐3698 ELENA 3.95 13.85 Ford Fritidssegelmotorbåt SFC‐3364 TREVILJOR 3.00 13.85 Volvo Penta MD17 Fritidssegelmotorbåt SFC‐5008 SMILE 3.87 13.71 Ford diesel 2712 1980 Fritidssegelmotorbåt SFC‐6573 FRIDEBORG 3.70 13.70 Volvo Penta MD31A, 1991 Fritidssegelmotorbåt SFC‐5081 CAPELLA 3.89 13.62 Volvo Penta TMD31 1990 Fritidssegelmotorbåt SFC‐4860 MARILI II 3.95 13.50 Ford 6 cyl. diesel Fritidssegelmotorbåt SFC‐3245 TWILIGHT 3.96 13.40 Perkins Fritidssegelmotorbåt SFC‐6686 DESTINY 3.97 13.39 Yanmar 4JH3‐TBE Fritidssegelmotorbåt SFC‐5365 GALATEA 3.96 13.38 Volvo Penta MD22 Fritidssegelmotorbåt SFC‐6505 LOVINA 3.99 13.36 Fritidssegelmotorbåt SFC‐4858 TIME OUT 3.90 13.35 Volvo Penta 3002T‐88 Fritidssegelmotorbåt SFC‐3817 AMARANT II 3.99 13.30 Volvo Penta TMD31A Fritidssegelmotorbåt SFC‐5495 STORMPETREL 3.30 13.30 Mercedes 621 Fritidssegelmotorbåt SFB‐7870 MAGNUM BONUM 3.82 13.25 Perkins 4.236 1978 Fritidssegelmotorbåt SFC‐6357 AKVILEJA 3.95 13.22 Volvo Penta TMD 22 Fritidssegelmotorbåt SFC‐3383 CHARLOTTA 3.60 13.20 Perkins 4236M Fritidssegelmotorbåt SFC‐5228 CEKRITITO 3.83 13.16 Volvo Penta MD22L 1997 Fritidssegelmotorbåt SFC‐3921 ELISABETH 3.90 13.10 Ford diesel Fritidssegelmotorbåt SFC‐3471 3.90 13.10 Ford 2712E Fritidssegelmotorbåt SFC‐6366 YANA 3.60 13.00 Perkins 4‐108, 1980 Fritidssegelmotorbåt SFC‐4651 OFF COURSE 3.90 12.95 Volvo Penta MD21B Fritidssegelmotorbåt SFC‐5481 LADY ALLI CAT 3.78 12.93 Volvo Penta TMD22A 1997 Fritidssegelmotorbåt SFC‐3800 CLASSTRE 3.78 12.93 Fritidssegelmotorbåt SFC‐6420 ALBATROSS 3.78 12.93 Volvo Penta MD31A, 1988 Fritidssegelmotorbåt 108

SFC‐3774 SCARLETT O'HARA 3.90 12.85 MD29 1970 Fritidssegelmotorbåt SFC‐5925 EBI 3.90 12.85 Mercedes 1976 Fritidssegelmotorbåt SFC‐3464 COOL 3.80 12.80 Volvo Penta MD30A Fritidssegelmotorbåt SFC‐3325 ALPHA OF SWEDEN 3.09 12.80 Volvo Penta MD21 Fritidssegelmotorbåt SFC‐5919 RAFFLES 3.89 12.80 Yanmar 1987 Fritidssegelmotorbåt SFB‐8512 TINTOMARA 2.50 12.75 Kermath 1960 Fritidssegelmotorbåt SFC‐6270 PELA 3.76 12.73 Westerbeke 46, 1990 Fritidssegelmotorbåt SFC‐4069 SIGERLINN 3.60 12.70 MD17C 1983 Fritidssegelmotorbåt SFC‐3241 KATALIA IV 3.70 12.70 Volvo Penta Fritidssegelmotorbåt SFC‐3793 LINNEA 3.10 12.70 MDIIC Fritidssegelmotorbåt SFC‐4632 NIKE 3.82 12.60 Perkins diesel Prima 50 Fritidssegelmotorbåt SFC‐3266 3.82 12.52 Perkins Fritidssegelmotorbåt SFC‐6177 HXYACHT 3.90 12.51 Volvo Penta 2003T 1993 Fritidssegelmotorbåt SFC‐6503 AZZURRA 3.90 12.51 Yanmar 3JH3E, 1999 Fritidssegelmotorbåt SFC‐6966 DUDE 3.90 12.51 Yanmar Diesel, 2003 Fritidssegelmotorbåt SFC‐4475 WINDFALL 3.60 12.50 Volvo Penta MD21A 1977 Fritidssegelmotorbåt SFC‐4501 KARIN AF NÄSKE 3.95 12.50 Volvo Penta 2003 Turbo Fritidssegelmotorbåt SFC‐4022 JO‐JO IX 3.60 12.50 Volvo Penta MD21 Fritidssegelmotorbåt SFC‐3525 JULIA 3.60 12.50 Volvo Penta MD21 A Fritidssegelmotorbåt SFB‐7209 PHNATTAPOO 2.50 12.50 Volvo MB10A 1978 Fritidssegelmotorbåt SFC‐5177 ISMINI 3.94 12.50 Perkins 4.108 1987 Fritidssegelmotorbåt SFC‐6541 ETOILE DU NORD 3.60 12.50 Volvo Penta MD21A, 1977 Fritidssegelmotorbåt SFC‐6483 PHILING 3.99 12.48 VPMD22L, 2001 Fritidssegelmotorbåt SFB‐8498 RESTLESS 3.12 12.40 Ford diesel 1974 Fritidssegelmotorbåt SFC‐5865 IRREANTUM 3.70 12.40 Kobta universal 1980 Fritidssegelmotorbåt SFC‐3822 MYRAX 3.60 12.40 Perkins Fritidssegelmotorbåt SFC‐3433 HULDAS KARIN 3.50 12.40 Volvo Penta MD21A Fritidssegelmotorbåt SFC‐8687 CITRON BLEU 3.90 12.31 VPMD22L, 1998 Fritidssegelmotorbåt SFB‐8432 FREEDOM 3.65 12.30 Volvo MD 40 A, 1979 Fritidssegelmotorbåt 109

SFC‐3747 CANDELA 3.85 12.30 Perkins 4108 1981 Fritidssegelmotorbåt SFC‐5762 GATHENHIELM 3.85 12.30 Perkins 4108 1982 Fritidssegelmotorbåt SFC‐6000 LI 3.76 12.30 Yanmar 4JH2‐TBE 1997 Fritidssegelmotorbåt SFC‐5763 KRYSSAREN 3.85 12.30 Perkins 4108 Fritidssegelmotorbåt SFC‐6411 BLUE MOON 3.76 12.22 Volvo Penta MD22, 1998 Fritidssegelmotorbåt SFC‐3533 VIKTORIA 3.50 12.20 Volvo Penta MD21 Fritidssegelmotorbåt SFC‐3595 SHEILA IV 3.70 12.20 Volvo Penta Fritidssegelmotorbåt SFC‐5927 BOREA 3.87 12.19 Volvo Penta MD22L 1994 Fritidssegelmotorbåt SFC‐4900 MOANA 3.85 12.19 Perkins diesel 1980 Fritidssegelmotorbåt SFC‐5324 SWEDWIND 2.55 12.19 Volvo Penta MD 6, 1976 Fritidssegelmotorbåt SFC‐3328 MYOPTION 3.96 12.19 Perkins Fritidssegelmotorbåt SFC‐5892 LAMPRIS 3.97 12.13 Perkins 6.354 Fritidssegelmotorbåt SFC‐4693 NOON MOON 3.85 12.10 Perkins 4.108 diesel Fritidssegelmotorbåt SFC‐5157 SAHARAH 3.54 12.10 Volvo Penta MD22A 1991 Fritidssegelmotorbåt SFC‐6499 ANNA V 3.65 12.10 Kubota KTT3000, 1985 Fritidssegelmotorbåt SFB‐8689 FIREFLY 3.50 12.10 Volvo Penta MD21A Fritidssegelmotorbåt SFC‐3593 GINGER 3.75 12.10 Volvo Penta Fritidssegelmotorbåt SFC‐6578 MARINENE 3.70 12.10 Volvo MD21, 1975 Fritidssegelmotorbåt SFC‐3276 CRUSANDER 3.75 12.10 Volvo Penta Fritidssegelmotorbåt SFC‐3706 NEREIA 3.55 12.08 Ford 2700/S841116 Fritidssegelmotorbåt SFC‐3885 FELICIA 3.68 12.07 Perkins Fritidssegelmotorbåt SFC‐4640 MONIQUE 3.20 12.00 Volvo Penta MD2B Fritidssegelmotorbåt SFC‐3306 ACARA 3.50 12.00 BMW D50 Fritidssegelmotorbåt SFC‐6029 XENA 3.67 12.00 Solé 1984 Fritidssegelmotorbåt SFC‐5702 THE TEMPTRESS 3.80 12.00 Mercedes 240 diesel Fritidssegelmotorbåt SFC‐2170 FRAGANCIA 3.89 11.99 Perkins 1989 Fritidssegelmotorbåt SFC‐3622 BLUES 3.89 11.99 Perkins Fritidssegelmotorbåt SFC‐3560 HOLIDAY 3.89 11.99 Perkins MD50 Fritidssegelmotorbåt SFC‐6523 OLIVIA 3.83 11.98 Yanmar 4JHE 2000 Fritidssegelmotorbåt 110

SFB‐8743 XANADU 4.35 11.97 Volvo Penta TMD50B 1982 Fritidssegelmotorbåt SFC‐6461 DIVING FROG 3.60 11.95 Perkings Diesel Fritidssegelmotorbåt SFC‐6185 SAILAWAY 3.60 11.92 Volvo Penta 2040 1999 Fritidssegelmotorbåt SFC‐3730 SPICE 3.62 11.92 Volvo Penta 2003 Fritidssegelmotorbåt SFC‐4263 SAHLEYA 3.62 11.92 Volvo Penta 2003 1986 Fritidssegelmotorbåt SFC‐5507 ULVINNA 4.05 11.91 Perkins 1989 Fritidssegelmotorbåt SFC‐8871 THINK TWICE 6.50 11.90 Yanmar 3YM30C, 2004 Fritidssegelmotorbåt SFC‐3818 ZI‐ZI 3.95 11.90 Yanmar 36M Fritidssegelmotorbåt SFC‐3265 BLUE PETER 3.62 11.89 Mercedes Benz Fritidssegelmotorbåt SFC‐3668 SEA ANN 3.62 11.89 Volvo Penta Fritidssegelmotorbåt SFC‐4086 ALBERTINA 3.62 11.89 Volvo Penta MD17C 1984 Fritidssegelmotorbåt SFC‐6509 MODUS VIVENDI IV 3.62 11.89 VP MD 17 C Fritidssegelmotorbåt SFC‐3690 SEA KING 3.62 11.89 Volvo Penta 2003 T Fritidssegelmotorbåt SFC‐3456 NAIM 3.35 11.88 Perkins Fritidssegelmotorbåt SFC‐3259 ELIONOR 3.82 11.86 Ford Fritidssegelmotorbåt SFC‐6060 SEFIR 3.76 11.85 Volvo Penta MD22 Fritidssegelmotorbåt SFC‐3951 VARUNA 4.35 11.85 Mitsubishi S4E2 1985 Fritidssegelmotorbåt SFB‐7211 PINTA 4.05 11.85 GM‐72 Fritidssegelmotorbåt SFC‐5916 VILJA 3.76 11.85 Volvo Penta MD22 Fritidssegelmotorbåt SFC‐5806 WIRAKON 3.81 11.82 Volvo Penta MD3 1975 Fritidssegelmotorbåt SFC‐3875 ANNA 3.00 11.80 Yanmar diesel Fritidssegelmotorbåt SFC‐5721 YEMANJA 3.85 11.80 Volvo Penta MD17 1983 Fritidssegelmotorbåt SFC‐6249 SUSANNA OF CROUCH 3.43 11.78 Perkins 4236M Fritidssegelmotorbåt SFC‐3530 LINNEA 4.48 11.77 Volvo Penta D47 Fritidssegelmotorbåt SFB‐8754 AHNRI 3.40 11.76 Peugeot XD3 1987 Fritidssegelmotorbåt SFC‐6548 SEA SON 3.85 11.75 Perkins 4.108m 1985 Fritidssegelmotorbåt SFC‐3909 TINGELING 3.50 11.75 Volvo Penta diesel Fritidssegelmotorbåt SFC‐5641 SANDSTORM 3.90 11.75 Perkins 4108M 1982 Fritidssegelmotorbåt SFC‐3825 LADY 3.90 11.75 Fritidssegelmotorbåt 111

SFC‐5084 ELIDA 3.85 11.74 Perkins 4108 Fritidssegelmotorbåt SFC‐6374 KERMIT 4.29 11.73 Perkins M90 1996/1997 Fritidssegelmotorbåt SFB‐8342 LA CLE 3.60 11.72 Volvo Penta 2003 Fritidssegelmotorbåt SFC‐3247 ÄLVAN 3.97 11.70 Volvo BM Fritidssegelmotorbåt SFC‐4023 NOOMI 3.70 11.70 Perkins 4‐236M 1989 Fritidssegelmotorbåt SFC‐3768 FERNET BRANCA 3.54 11.66 Volvo Penta 2003T Fritidssegelmotorbåt SFC‐5256 JETTE 3.46 11.66 Yanmar 3GM30F4449 Fritidssegelmotorbåt SFC‐3513 DELIGHT 3.90 11.65 Perkins diesel Fritidssegelmotorbåt SFC‐3396 SPLIT PASSION 3.90 11.65 Volvo Penta 2003 Turbo Fritidssegelmotorbåt SFC‐5450 XTRA 3.65 11.65 Volvo Penta MD21B 1983 Fritidssegelmotorbåt SFC‐2109 XANADU 3.90 11.65 Perkins Prima Fritidssegelmotorbåt SFC‐3406 NJORD 3.15 11.60 Volvo Penta MD3B Fritidssegelmotorbåt SFC‐3549 KIAMA III 3.40 11.60 Volvo Penta Fritidssegelmotorbåt SFC‐4066 PETINA 3.65 11.60 Volvo Penta MD21 1983 Fritidssegelmotorbåt SFC‐3460 LOUISE 2.70 11.60 Yanmar Fritidssegelmotorbåt SFC‐3487 SAE GULL 3.60 11.60 Volvo Penta MD17C Fritidssegelmotorbåt SFB‐7491 NORDIC LADY 3.65 11.60 Yanmar 4JH3CE, 1999 Fritidssegelmotorbåt SFC‐6069 ANCHEE III 3.65 11.58 Yanmar 3QM3FG 1984 Fritidssegelmotorbåt SFC‐3625 ALVICLARA 3.48 11.57 Volvo Penta Fritidssegelmotorbåt SFC‐3337 FRAGANCIA 3.48 11.57 Volvo Penta MD21 Fritidssegelmotorbåt SFB‐7014 HAVSVIND 3.48 11.57 Volvo Penta MD21B Fritidssegelmotorbåt SFC‐3827 AMANDA 3.54 11.57 Volvo Penta MD21 Fritidssegelmotorbåt SFC‐3317 SURPRISE 3.89 11.56 Perkins Fritidssegelmotorbåt SFB‐8398 PEPPELI 3.20 11.55 Feriman Fritidssegelmotorbåt SFC‐5619 DAPHNE 3.55 11.55 Bukh DV24ME 1986 Fritidssegelmotorbåt SFC‐4256 CHIQUITITA 3.57 11.53 Volvo Penta MD3 1982 Fritidssegelmotorbåt SFC‐3783 FREYA X 2.40 11.50 Mercruiser 1993 Fritidssegelmotorbåt SFC‐3709 OCTAVIA 3.90 11.50 Perkins Prima Fritidssegelmotorbåt SFC‐3640 HELENE 3.90 11.50 Perkins 50PRIMA Fritidssegelmotorbåt 112

SFC‐3320 MERETE 3.90 11.50 Perkins 4108 Fritidssegelmotorbåt SFC‐3332 HELENA 3.90 11.50 Perkins Fritidssegelmotorbåt SFB‐7619 INDRA 3.50 11.50 BMC diesel Fritidssegelmotorbåt SFC‐4886 GRANDESSA 3.90 11.50 Perkins 1987/1988 Fritidssegelmotorbåt SFC‐6137 STORNOWAY 3.70 11.50 Yanmar 3GM30F, 1998 Fritidssegelmotorbåt SFB‐7165 ARIEL 2.73 11.50 Volvo Penta MDIIB Fritidssegelmotorbåt SFC‐3613 SHASA 3.70 11.50 Volov Penta MD17D Fritidssegelmotorbåt SFC‐5985 CORA 3.70 11.48 Peugot diesel Fritidssegelmotorbåt SFC‐3357 KOLIJOX 3.50 11.46 Volvo Penta 2003 Fritidssegelmotorbåt SFC‐4187 AVALON 3.70 11.46 Yanmar 3QM30 1981 Fritidssegelmotorbåt SFC‐3412 NITCHEVO 3.60 11.45 Perkins Marind Fritidssegelmotorbåt SFC‐6506 HALLôJA 3.50 11.45 Yanmar 1999 Fritidssegelmotorbåt SFB‐8859 ALBATROSS 3.32 11.43 Volvo Penta MD17 1983 Fritidssegelmotorbåt SFC‐3453 CRUSADER 3.20 11.40 Volvo Penta MD2 Fritidssegelmotorbåt SFC‐4957 ARGO NAVIS 3.24 11.40 Yanmar 3GM30F 1987 Fritidssegelmotorbåt SFC‐5678 LINNéA 3.00 11.40 Yanmar Fritidssegelmotorbåt SFC‐8839 JASMIN 3.60 11.40 Volvo MD 2030, 1999 Fritidssegelmotorbåt SFB‐8745 REFANUT 3.00 11.35 Sabb Diesel 1978 Fritidssegelmotorbåt SFC‐5552 BRYNHILD 3.76 11.32 Perkins Prima M 50, 1994 Fritidssegelmotorbåt SFC‐6280 TURANDOT 3.55 11.31 Volvo Penta MD22P, 2000 Fritidssegelmotorbåt SFC‐4639 NOA‐NOA II 3.55 11.31 Volvo Penta MD22 1995 Fritidssegelmotorbåt SFC‐3470 MILES AHEAD 3.24 11.30 Volvo Penta MD11 Fritidssegelmotorbåt SFC‐5370 ATTUTTALÖR 3.50 11.30 Volvo Penta MD17C 16277 Fritidssegelmotorbåt SFC‐5893 VAGABOND 3.50 11.30 Perkins 4‐108 1979 Fritidssegelmotorbåt SFC‐5714 BLESSING 3.30 11.30 Volvo Penta MD 11 C Fritidssegelmotorbåt SFC‐6180 WILLROSE 3.50 11.30 Volvo Penta MD21B 1984 Fritidssegelmotorbåt SFC‐5170 EOS 3.48 11.25 Volvo Penta MD11C 1981 Fritidssegelmotorbåt SFC‐6554 APHRODITE 3.59 11.25 Volvo MD2040, 2002 Fritidssegelmotorbåt SFC‐5820 MORNING SUN II 3.66 11.23 Mazda Diesel Fritidssegelmotorbåt 113

SFC‐3424 JAI ALAI 3.35 11.20 Fritidssegelmotorbåt SFC‐4008 NAVICULA'S 3.50 11.20 Volvo Penta MD21 1980 Fritidssegelmotorbåt SFC‐6239 CORONA 3.50 11.20 Volvo Penta 2003T Fritidssegelmotorbåt SFC‐6715 CHARUMA III 3.50 11.20 Volvo Penta MD22L, ‐97 Fritidssegelmotorbåt SFB‐8014 BOJAN 3.45 11.20 Universal Atomic M 5444 Fritidssegelmotorbåt SFC‐6560 ALEGRIA 3.50 11.20 Volvo Penta MD 22 Fritidssegelmotorbåt SFC‐6597 ALTERA EA 3.45 11.20 Yanmar 4JH2 Fritidssegelmotorbåt SFC‐6443 IRO‐ERI 3.50 11.20 YANMAR 3HM 35SD30 Fritidssegelmotorbåt SFC‐6412 LINDISFARNE 3.48 11.20 MD22, 1995 Fritidssegelmotorbåt SFC‐6460 UNICORN 3.50 11.20 Volvo Penta 2003T, 1991 Fritidssegelmotorbåt SFC‐7001 ELLINOR 3.45 11.20 Yanmar 4JH2BE, ‐95 Fritidssegelmotorbåt SFC‐5095 STRESSLESS 3.45 11.20 Volvo Penta MD17C 1979 Fritidssegelmotorbåt SFC‐4880 FLAVIA 3.45 11.20 Volvo Penta MD17C 1981 Fritidssegelmotorbåt SFC‐5938 SOLITUDE 3.45 11.20 Yanmar 1987 Fritidssegelmotorbåt SFC‐3716 THALATTA 3.45 11.20 Yanmar Fritidssegelmotorbåt SFC‐3670 GENUINE 3.45 11.20 Yanmar Fritidssegelmotorbåt SFC‐3608 VIMANAS 3.59 11.20 Mercedes Fritidssegelmotorbåt SFC‐4052 TALISMAN 3.45 11.20 MD17D 85 Fritidssegelmotorbåt SFC‐5364 GALAPAGOS 3.60 11.15 Yanmar 36M‐30FC‐SD20 Fritidssegelmotorbåt SFB‐7285 SARA TVÅ 3.29 11.13 Yanmar Fritidssegelmotorbåt SFC‐3226 CARPE DIEM 3.13 11.12 Volvo MD17C 1982 Fritidssegelmotorbåt SFC‐7139 VILMA 3.70 11.11 Ford 2715 E, 1974 Fritidssegelmotorbåt SFC‐5917 ELIDANTE 3.20 11.10 Yanmar 3HM35F 1993 Fritidssegelmotorbåt SFC‐3656 FANTASI 3.35 11.10 Volvo Penta Fritidssegelmotorbåt SFC‐3499 ANNIE 3.35 11.10 Volvo Penta MD21 Fritidssegelmotorbåt SFB‐8685 RED LABEL 3.13 11.07 Volvo Penta MD2B Fritidssegelmotorbåt SFC‐6161 OANA 3.13 11.07 Volvo Penta MD17D Fritidssegelmotorbåt SFC‐5180 SHANGRI LA III 3.13 11.07 Volvo Penta MD11C/100S 77 Fritidssegelmotorbåt SFC‐6855 ELVINA 3.13 11.07 Yanmar 3GM30F, 1999 Fritidssegelmotorbåt 114

SFC‐3589 ENDORFINA 3.13 11.07 Volvo Penta MD11C Fritidssegelmotorbåt SFB‐8308 TUSSEN 3.13 11.07 Volvo MD17D 1983 Fritidssegelmotorbåt SFC‐3399 ISA 4.00 11.05 Volvo Penta MD21B Fritidssegelmotorbåt SFC‐5480 IMAGE 3.95 11.05 Volvo Penta MD21B 1979 Fritidssegelmotorbåt SFC‐5416 STORMPIPPI 3.60 11.05 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐4999 BAKBRUS OF SWEDEN 3.97 11.05 Volvo Penta MD21A 1979 Fritidssegelmotorbåt SFC‐3346 MOTVIND II 3.20 11.05 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐3754 BETELGEUZE 3.60 11.04 Volvo Penta 2003 1986 Fritidssegelmotorbåt SFC‐3901 WIGGEN 2.44 11.04 Yamaha utombord 1993 Fritidssegelmotorbåt SFB‐7219 TINTOMARA II 3.13 11.04 Volvo MD11C,1977 Fritidssegelmotorbåt SFC‐3489 MARIE LOUISE 3.60 11.03 Volvo Penta MD17C Fritidssegelmotorbåt SFC‐3494 KRAKA 3.60 11.03 Volvo Penta Fritidssegelmotorbåt SFC‐3857 FLAMENCO 3.80 11.00 Yanmar 3GM7297 Fritidssegelmotorbåt SFC‐4035 LIVA 3.20 11.00 Yanmar 2QM20 1977 Fritidssegelmotorbåt SFC‐5368 MARTHA 3.80 11.00 Yanmar 3GM 1989 Fritidssegelmotorbåt SFC‐3297 NEREIDE 6.70 11.00 2 Volvo Penta MB2 Fritidssegelmotorbåt SFC‐3451 3.30 11.00 Yanmar 3GM30FC Fritidssegelmotorbåt SFC‐3345 CREYOLA 2.95 11.00 Volvo Penta 2002 Fritidssegelmotorbåt SFC‐3449 LIONHEART 3.65 11.00 Volvo Penta 2003 Fritidssegelmotorbåt SFC‐4037 CHARLOTTE 3.20 11.00 Volvo Penta MD 11 Fritidssegelmotorbåt SFC‐3881 INDEPENDENCE 3.30 11.00 Volvo Penta 2003 Fritidssegelmotorbåt SFB‐7298 TARANTELLA 2.98 11.00 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐3260 MEGABUCK 3.80 11.00 Yanmar Fritidssegelmotorbåt SFC‐5785 ISIS 3.20 11.00 Thornycroft 1500D 1991 Fritidssegelmotorbåt SFC‐6765 AURORA BOREALIS 3.25 11.00 Ford NG27RE 1983 Fritidssegelmotorbåt SFC‐3636 VORE 3.35 11.00 Perkins Fritidssegelmotorbåt SFC‐5403 ESTELLE 3.65 11.00 Volvo Penta MD2003 1985 Fritidssegelmotorbåt SFC‐5738 LOUNETTE 3.36 10.99 3GM30F Fritidssegelmotorbåt SFC‐5691 COCKTAIL 3.50 10.97 Volvo Penta 2003T 1989 Fritidssegelmotorbåt 115

SFC‐5428 VINDROSA 3.50 10.97 Volvo Penta MD22L 1995 Fritidssegelmotorbåt SFC‐3405 DON QUIJOTE 3.50 10.97 Volvo Penta 2003 Turbo Fritidssegelmotorbåt SFC‐4159 MARIA KRISTINA 3.40 10.95 Volvo Penta MD11C 1975 Fritidssegelmotorbåt SFC‐4039 TETTINA III 3.36 10.95 Yanmar 3GM 1988 Fritidssegelmotorbåt SFC‐3922 APHRODITE 3.50 10.93 Yanmar 3GMC diesel Fritidssegelmotorbåt SFB‐7309 KABRIFOL 3.50 10.93 Volvo Penta MD21 Fritidssegelmotorbåt SFC‐3707 3.40 10.90 Volvo Penta 2003 Fritidssegelmotorbåt SFC‐3237 GOOD RUN 3.35 10.90 Ford 2712E Fritidssegelmotorbåt SFC‐3710 BACCINA 2.80 10.90 Volvo Penta MD11D Fritidssegelmotorbåt SFC‐3429 SHEBA 3.45 10.90 Yanmar 2QM15GH Fritidssegelmotorbåt SFC‐3255 WINDA V 3.38 10.90 Buch DV20ME Fritidssegelmotorbåt SFC‐3890 VAGABONDO 3.35 10.90 Ford 4 cyl 1985 Fritidssegelmotorbåt SFC‐3696 SALOME 3.30 10.90 Perkins Fritidssegelmotorbåt SFC‐5526 TEHLIKELI 3.45 10.90 Volvo Penta MD2030B 1996 Fritidssegelmotorbåt SFC‐3459 SIMURG 2.74 10.88 Volvo Penta MD2B Fritidssegelmotorbåt SFC‐4034 BIET 2.74 10.88 Volvo MD11 Fritidssegelmotorbåt SFC‐5509 CINDERELLA 3.55 10.87 Volvo Penta MD22 1991 Fritidssegelmotorbåt SFC‐6682 NEFERTITI 3.55 10.87 VPMD22A, 1992 Fritidssegelmotorbåt SFC‐5431 VAHINE 3.10 10.85 Perkins A4 270 Fritidssegelmotorbåt SFC‐3529 MADELEN II 3.50 10.85 Volvo Penta MD32A Fritidssegelmotorbåt SFC‐5819 BOLD VENTURE 3.55 10.84 Perkins Diesel Fritidssegelmotorbåt SFC‐6481 QUANDARY 3.48 10.80 Volvo Penta MD 2030,2000 Fritidssegelmotorbåt SFC‐3288 SAMPIZ III 3.40 10.80 Volvo Penta Fritidssegelmotorbåt SFC‐3657 STORASYSTER 3.48 10.80 Volvo Penta MD11C Fritidssegelmotorbåt SFB‐7946 VICTORIA 3.48 10.80 Yanmar 2 QM 20 Fritidssegelmotorbåt SFC‐6314 FORGANCIA 3.38 10.80 VP 2003/1205, 1989 Fritidssegelmotorbåt SFC‐3304 NANDI 3.63 10.80 Volvo Penta MD2 Fritidssegelmotorbåt SFC‐4508 SOMMARFÅGEL 3.48 10.80 Volvo Penta MD7A 1981 Fritidssegelmotorbåt SFC‐3703 ELIDA 3.30 10.80 Ford Fritidssegelmotorbåt 116

SFC‐3284 FRU LARSSON 3.30 10.80 Perkins MD20 Fritidssegelmotorbåt SFB‐6895 ZENDA VÄSTERVIK 3.82 10.80 BMC‐Tempest Sea Lord Fritidssegelmotorbåt SFC‐5246 VIOLA 3.30 10.80 Volvo Penta 2002 1991 Fritidssegelmotorbåt SFC‐6448 ACAPELLA 3.40 10.80 Volvo Penta 2040‐C 2001 Fritidssegelmotorbåt SFC‐5234 CHRISTINA 3.42 10.80 Volvo Penta 2003T 1989 Fritidssegelmotorbåt SFC‐6190 MAY 3.80 10.78 Volvo Penta 2040 B Fritidssegelmotorbåt SFC‐6275 MAH JONG 3.40 10.75 Volvo Penta MD11C, 1979 Fritidssegelmotorbåt SFC‐5231 CHINOOK 3.40 10.75 Volvo Penta MD2003T 1987 Fritidssegelmotorbåt SFC‐5712 ANDREA 3.40 10.75 Volvo 2003T, 1990 Fritidssegelmotorbåt SFC‐5680 SEAQWEST 3.40 10.75 Volvo Penta MD22L 1998 Fritidssegelmotorbåt SFC‐5444 ONYX 3.40 10.75 Volvo Penta MD21B Fritidssegelmotorbåt SFC‐3641 KADIRA 3.40 10.75 Volvo Penta MD11D Fritidssegelmotorbåt SFC‐4002 HARMONY 3.40 10.75 Volvo Penta MD21 110S Fritidssegelmotorbåt SFC‐5216 DA CAPO 3.40 10.75 Volvo Penta 2003 Turbo 89 Fritidssegelmotorbåt SFC‐5954 HYBRIS 3.30 10.72 Yanmar 2QM20 Fritidssegelmotorbåt SFC‐3663 POSEIDON 3.60 10.72 Volvo Penta 2003 Fritidssegelmotorbåt SFC‐6003 INFERNO 3.28 10.71 Yanmar 4JH2E 1997 Fritidssegelmotorbåt SFC‐5384 BEAUTEN 5.00 10.70 Mercury utombord Fritidssegelmotorbåt SFC‐3762 ANNA 3.15 10.70 Volvo Penta MD29 Fritidssegelmotorbåt SFC‐3545 WILMA 3.50 10.70 Ford Fritidssegelmotorbåt SFC‐3587 ILO 3.30 10.70 Volvo Penta MD11C Fritidssegelmotorbåt SFB‐8677 GARBO 4.70 10.70 Johnson 1986 Fritidssegelmotorbåt SFC‐3705 EXIL AF ÖSMO 3.49 10.69 Perkins Perma M35 Fritidssegelmotorbåt SFC‐3575 GRÅTRUT 3.50 10.65 Mercedes Fritidssegelmotorbåt SFC‐5494 ATTINA 3.45 10.65 Yanmar 4KH2‐GBE 1990 Fritidssegelmotorbåt SFC‐4848 ELAIDA V 3.16 10.65 Volvo Penta 2003 1992 Fritidssegelmotorbåt SFC‐3510 GAIA 3.10 10.65 Bukh Fritidssegelmotorbåt SFC‐6192 MARIA 3.80 10.62 Yanmar Fritidssegelmotorbåt SFC‐5235 CIKORIA 3.55 10.60 Volvo Penta MD17 1983 Fritidssegelmotorbåt 117

SFC‐5923 GANESHA 3.40 10.60 36M30 Fritidssegelmotorbåt SFC‐5939 MATILDA 3.35 10.60 Volvo Penta MD17 Fritidssegelmotorbåt SFC‐5888 TWINGO 6.04 10.60 Yanmar utomb. diesel 1992 Fritidssegelmotorbåt SFC‐8808 YAJA 3.25 10.60 MD‐17, 1982 Fritidssegelmotorbåt SFB‐9043 AROS BEST 3.10 10.60 Yanmar diesel Fritidssegelmotorbåt SFC‐5076 BABY BREEZE 3.35 10.58 Yanmar 1996 Fritidssegelmotorbåt SFC‐3280 TURTLE 3.47 10.57 Volvo Penta MD71 Fritidssegelmotorbåt SFC‐3653 AMALIE 3.40 10.55 Perkins Fritidssegelmotorbåt SFC‐3574 MISS X 3.25 10.55 Volvo Penta MD7B Fritidssegelmotorbåt SFC‐3310 PEJA 3.38 10.54 Volvo Penta MD21B Fritidssegelmotorbåt SFC‐3312 3.38 10.54 Volvo Penta MD21 Fritidssegelmotorbåt SFC‐3637 LA BAMBA 3.38 10.54 Volvo Penta MD Fritidssegelmotorbåt SFC‐3681 ADA 3.38 10.54 Volvo Penta MD2003T Fritidssegelmotorbåt SFC‐3927 SHENANDOAH 3.38 10.54 Volvo Penta MD21B 1982 Fritidssegelmotorbåt SFC‐5153 SAIFON 3.38 10.54 Volvo Penta 3T 1988 Fritidssegelmotorbåt SFC‐5772 PETINA 3.38 10.54 Volvo Penta 2003 Turbo Fritidssegelmotorbåt SFC‐6846 DOLPHIN 3.38 10.54 Volvo Penta MD21B,‐79 Fritidssegelmotorbåt SFC‐6988 BARACUDA 3.38 10.54 Volvo Penta MD21B,‐82 Fritidssegelmotorbåt SFC‐4270 HELENA 3.38 10.54 Volvo Penta MD21B 1980 Fritidssegelmotorbåt SFB‐8020 INCREDIBLE 3.38 10.54 Volvo Penta MD21B 1983 Fritidssegelmotorbåt SFB‐8870 AKKA PINN PINN 3.38 10.54 Volvo Penta MD Fritidssegelmotorbåt SFC‐3639 DIANA 3.60 10.51 Perkins Perama Fritidssegelmotorbåt SFC‐2587 JAVADOS 3.60 10.51 Perkins diesel Fritidssegelmotorbåt SFC‐3233 SNOWBIRD 3.50 10.50 Volvo Penta Fritidssegelmotorbåt SFC‐3617 WINDRUSH 3.05 10.50 Volvo Penta MD21A Fritidssegelmotorbåt SFC‐4280 AYA 2.14 10.50 Utombord Fritidssegelmotorbåt SFB‐7177 PASSION 3.05 10.50 Volvo Penta 22 L, ‐94 Fritidssegelmotorbåt SFC‐6726 NABOB 3.05 10.50 Volvo Penta P2‐55, 2001 Fritidssegelmotorbåt SFC‐6746 SERENAD 3.05 10.50 VolvoPenta MD222,‐99 Fritidssegelmotorbåt 118

SFC‐4859 TELLINA 3.05 10.50 Mercedes‐Benz diesel 1972 Fritidssegelmotorbåt SFC‐3559 MIROMA II 3.05 10.50 Volvo Penta MD21 Fritidssegelmotorbåt SFC‐3643 FREYJA 3.00 10.50 Vesterbeke Fritidssegelmotorbåt SFC‐3988 MAMAMI 3.07 10.50 Volvo Penta MD21A Fritidssegelmotorbåt SFC‐3742 GING‐GING III 3.38 10.50 Volvo Penta 2003 1991 Fritidssegelmotorbåt SFC‐3340 SOLITUDE 3.05 10.50 Volvo Penta MD21A Fritidssegelmotorbåt SFB‐8913 MORNING SUN 3.05 10.50 Volvo Penta MD21A 1974 Fritidssegelmotorbåt SFB‐8228 MARY READ 3.05 10.50 Perkins 4.107 Fritidssegelmotorbåt SFB‐6839 ESCAPADE III 3.05 10.50 Perkins 4108 Fritidssegelmotorbåt SFC‐3354 PUSAN 3.04 10.46 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐5996 LIBERTY 3.10 10.45 Volvo Penta MD17C 1979 Fritidssegelmotorbåt SFC‐6577 MATANZAS 2.62 10.45 Volov Penta MD 5 A Fritidssegelmotorbåt SFC‐6123 FELICIA 3.10 10.45 Volvo Penta MD22, 1999 Fritidssegelmotorbåt SFC‐5049 BALOO 3.20 10.44 Yanmar 3 cyl diesel 1996 Fritidssegelmotorbåt SFC‐4802 SOLEADO 2.84 10.42 Volvo Penta MD2B 1976 Fritidssegelmotorbåt SFC‐3370 KARIN 2.84 10.42 Yanmar YSE8391 Fritidssegelmotorbåt SFC‐3694 ELIN 3.37 10.40 Volvo Penta 2002 Fritidssegelmotorbåt SFC‐6561 JUDITH 3.15 10.40 Volvo Penta MD17C, 1976 Fritidssegelmotorbåt SFC‐5226 L'AMIE 3.40 10.40 Volvo Penta 1994 Fritidssegelmotorbåt SFC‐6033 FELICIA II 2.80 10.40 Volvo Penta Fritidssegelmotorbåt SFC‐6462 EMMA AF TROSA 3.40 10.40 Volvo Penta MD17‐110S Fritidssegelmotorbåt SFC‐4653 MATHILDA 3.50 10.40 Volvo Penta 2003 1989 Fritidssegelmotorbåt SFC‐3556 DELFIN 3.00 10.40 Volvo Penta Fritidssegelmotorbåt SFC‐3526 WHITE LADY 3.30 10.40 Volvo Penta Fritidssegelmotorbåt SFC‐5197 MATE 3.35 10.36 Volvo Penta MD17C Fritidssegelmotorbåt SFC‐5064 ELLINOR 3.10 10.35 Volvo Penta MD3B Fritidssegelmotorbåt SFC‐7453 ZINGOALLA 3.50 10.35 Perkins 4.108 Fritidssegelmotorbåt SFB‐7555 HORISONT 3.37 10.30 Volvo Penta Fritidssegelmotorbåt SFC‐3528 HELENA 3.10 10.30 Volvo Penta MD35917 Fritidssegelmotorbåt 119

SFB‐8729 KUMA 3.10 10.30 Volvo Penta MD21A Fritidssegelmotorbåt SFB‐8416 HELIA 3.10 10.30 BMC Captain 1976 Fritidssegelmotorbåt SFC‐6254 MIGHTY QUINN 3.50 10.30 Yanmar Diesel 3GM30F 1991 Fritidssegelmotorbåt SFC‐3915 MAROUSCHKA IV 3.43 10.30 Yanmar 3GM 30 FG EU, 2002 Fritidssegelmotorbåt SFC‐3732 JOILGIMO 3.10 10.30 Volvo Penta MD3B Fritidssegelmotorbåt SFC‐3840 KEVITA 3.10 10.30 Volvo Penta MD3B Fritidssegelmotorbåt SFB‐8752 LINA CARLSKRONA 3.33 10.28 Yanmar 3HM 5794 1982 Fritidssegelmotorbåt SFC‐5645 JULIETTE 3.42 10.28 Volvo Penta 2030 1998 Fritidssegelmotorbåt SFC‐3869 NIRVANA 3.10 10.26 Volvo Penta 2003 Fritidssegelmotorbåt SFC‐3409 ANNICA 2.71 10.25 Perkins Fritidssegelmotorbåt SFC‐3455 EBREZZA II 3.05 10.21 Universal QM25 Fritidssegelmotorbåt SFC‐3444 EOS 3.30 10.20 Volvo Penta MD17C Fritidssegelmotorbåt SFC‐3292 PANTERN 2.25 10.20 Honda Fritidssegelmotorbåt SFC‐3624 WII 2.98 10.20 Volvo Penta Fritidssegelmotorbåt SFC‐3854 LAZER 3.48 10.20 Volvo Penta MD2MD11C Fritidssegelmotorbåt SFC‐6433 LOVISA 3.40 10.20 2003 Turbo, 1990 Fritidssegelmotorbåt SFC‐3751 LINA 3.33 10.20 Volvo Penta MD22L 1993 Fritidssegelmotorbåt SFC‐6527 AMARANT 3.48 10.20 Beta 28, 2000 Fritidssegelmotorbåt SFC‐5102 TAIFUN 3.05 10.18 Perkins 4.108 1986 Fritidssegelmotorbåt SFC‐3859 LINDA 3.43 10.16 Yanmar Fritidssegelmotorbåt SFC‐3375 LA CLE 3.43 10.16 Yanmar 3GM Fritidssegelmotorbåt SFC‐3740 4 SAIL 3.30 10.10 Volvo Penta 2003 1984 Fritidssegelmotorbåt SFC‐6367 CARAMELLE 3.30 10.10 Volvo Penta MD11D, 1982 Fritidssegelmotorbåt SFC‐7743 KALEVALA 3.25 10.10 Ford 0807051 FJK Fritidssegelmotorbåt SFC‐3372 PANTA REI 3.40 10.08 Volvo Penta MD17C Fritidssegelmotorbåt SFC‐5016 ODYSSEY 3.50 10.06 D 2983‐90 Torncraft 1979 Fritidssegelmotorbåt SFB‐8645 ORKESTERN 2.81 10.05 Diesel Bukh Dvm 20 1981 Fritidssegelmotorbåt SFB‐8599 GIRO 3.00 10.00 Volvo Penta MD2 Fritidssegelmotorbåt SFB‐8720 IDUN 3.00 10.00 Yanmar diesel 2QM20 Fritidssegelmotorbåt 120

SFC‐3248 SEAQUESTER 3.60 10.00 Volvo Fritidssegelmotorbåt SFC‐3665 MIO 3.00 10.00 Volvo Penta MD11D 1983 Fritidssegelmotorbåt SFC‐6719 ÖSTANVIND 3.20 10.00 Yanmar 3GM30F, 1994 Fritidssegelmotorbåt SFC‐3633 AMIE DEUX 2.50 10.00 Volvo Penta Fritidssegelmotorbåt SFC‐3229 PRIDE 3.70 10.00 Volvo Penta MDIIB Fritidssegelmotorbåt SFC‐3576 JOHN 3.80 10.00 International BD281 Fritidssegelmotorbåt SFC‐3447 AURORA 2.98 9.98 Fritidssegelmotorbåt SFC‐5990 WILD ROSE 3.40 9.98 Volvo Penta 2003B‐BT 1992 Fritidssegelmotorbåt SFC‐5198 EL CORDERO 3.40 9.95 Volvo Penta 2003HEBT 1995 Fritidssegelmotorbåt SFC‐3648 CARAMBA 3.00 9.95 Volvo Penta MD2003 Fritidssegelmotorbåt SFC‐6187 SUNBEAM 3.26 9.95 Volvo Penta 2003 1989 Fritidssegelmotorbåt SFC‐3225 ANNA PERENNA 3.00 9.94 Volvo Penta MD7B Fritidssegelmotorbåt SFC‐4881 RED BLAZE 3.23 9.92 Yanmar YSM12 Fritidssegelmotorbåt SFC‐5553 TJORVEN 3.23 9.90 Volvo Penta 2003 S Fritidssegelmotorbåt SFC‐3862 VIRGIN 3.23 9.90 Volvo Penta 2003 Fritidssegelmotorbåt SFB‐8742 SLABANG III 3.25 9.90 Volvo Penta 2002S Fritidssegelmotorbåt SFC‐4551 MARINA 3.23 9.90 Volvo Penta 2003T 1990 Fritidssegelmotorbåt SFC‐6145 PRIMULA VERIS 3.23 9.90 Volvo Penta 2003 S Fritidssegelmotorbåt SFC‐3514 MIANCA 3.25 9.90 Volvo Penta 2002 Fritidssegelmotorbåt SFC‐3539 ACHILLES 2.65 9.90 BMC Leyland Fritidssegelmotorbåt SFC‐3567 MUCKLE FLUGGA 3.10 9.90 Volvo Penta MD2B Fritidssegelmotorbåt SFC‐3234 CURACAO 3.00 9.90 Yanmar Fritidssegelmotorbåt SFC‐3398 EMMA 3.18 9.89 Volvo Penta MD17C Fritidssegelmotorbåt SFC‐3552 TAPTO 3.18 9.89 Volvo Penta Fritidssegelmotorbåt SFB‐8680 BLÅSUT 3.18 9.89 Volvo Penta MD3B Fritidssegelmotorbåt SFC‐3236 UHURU 3.33 9.89 Volvo Penta MD3 Fritidssegelmotorbåt SFB‐7651 BELLA 3.18 9.89 Beta 1505, 1996 Fritidssegelmotorbåt SFC‐5935 BALOO 3.18 9.89 Yanmar 3JH2E Fritidssegelmotorbåt SFC‐3507 MILANKA II 3.18 9.89 Volvo Penta MD2003 Fritidssegelmotorbåt 121

SFC‐3371 APRILIA 3.18 9.89 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐3330 LADY DAY 3.18 9.89 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐6039 HELENA 3.18 9.89 Volvo Penta MD11C 1984 Fritidssegelmotorbåt SFC‐3991 SAYONARA 3.18 9.89 Volvo Penta MD11D 1990 Fritidssegelmotorbåt SFC‐3677 ANIARA 3.18 9.89 Volvo Penta MDIIB 1976 Fritidssegelmotorbåt SFC‐3686 OCEAN SPIRIT 3.18 9.89 Volvo Penta Fritidssegelmotorbåt SFC‐3381 KAVAT 3.18 9.89 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐3531 RAMNOE 3.18 9.89 Volvo Penta MD2B Fritidssegelmotorbåt SFC‐3496 VAGANT 3.18 9.89 Perkins Fritidssegelmotorbåt SFB‐8684 LEVANT 3.18 9.89 Volvo MD211C 1978 Fritidssegelmotorbåt SFC‐6310 MANANA 3.18 9.89 Yanmar 2QM20, 1979 Fritidssegelmotorbåt SFC‐3588 CASA‐NOVA 3.16 9.87 Yanmar 2GM Fritidssegelmotorbåt SFC‐3293 LADY BÄVER II 3.33 9.87 Yanmar Fritidssegelmotorbåt SFC‐5072 SOFIA 3.15 9.87 Yanmar, 1982 Fritidssegelmotorbåt SFC‐3250 VISNA 3.18 9.86 Volvo Fritidssegelmotorbåt SFC‐3238 ANJO 3.15 9.85 Mercedez OM636 Fritidssegelmotorbåt SFC‐6042 SCHARONA 3.27 9.85 Yanmar 1989 Fritidssegelmotorbåt SFB‐6825 FRIDA 2.89 9.84 Yanmar 2QM2081008 1976 Fritidssegelmotorbåt SFC‐4517 MALAIKA 3.33 9.83 Volvo Penta 2003 1989 Fritidssegelmotorbåt SFC‐4502 LELI 2.88 9.82 Volvo Penta MD2B 1977 Fritidssegelmotorbåt SFC‐4385 ARGO 2.88 9.82 Perkins MD30 1994 Fritidssegelmotorbåt SFC‐3240 MORNING STAR 2.88 9.82 Sabb 2HG Fritidssegelmotorbåt SFB‐7003 YEN 2.98 9.82 Volvo Penta MD2B 1975 Fritidssegelmotorbåt SFB‐6759 AMIGA MIA 2.88 9.81 Volvo Penta MD11C 1978 Fritidssegelmotorbåt SFB‐8395 EASY II 2.88 9.81 Volvo Penta MD2B Fritidssegelmotorbåt SFB‐9026 LAGOM 2.88 9.81 Perkins MD30 Fritidssegelmotorbåt SFC‐3458 IVRAREN 2.88 9.81 Yanmar 3GM30 Fritidssegelmotorbåt SFC‐3351 AKKA 3.33 9.81 Yanmar 2QM20 Fritidssegelmotorbåt SFC‐3243 ALIZé 2.88 9.81 Perkins M30 Fritidssegelmotorbåt 122

SFC‐5315 SOLVIK 2.88 9.81 Volvo Penta MD11B 1987 Fritidssegelmotorbåt SFC‐5508 SHANTY 3.33 9.81 Volvo Penta 2003T 1994 Fritidssegelmotorbåt SFC‐3262 CHARLOTTA 3.33 9.81 Volvo Penta MD2B Fritidssegelmotorbåt SFC‐3348 AMADEA 2.88 9.81 Volvo Penta Fritidssegelmotorbåt SFC‐3478 MOBY DICK 3.33 9.81 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐6315 ORCA 2.88 9.81 Volvo Penta MD2B Fritidssegelmotorbåt SFB‐7092 GORMLAITH 3.33 9.81 Volvo Penta MD11C Fritidssegelmotorbåt SFB‐8259 HAVSSULAN 2.88 9.81 Yanmar 2QM20 1979 Fritidssegelmotorbåt SFB‐8653 RÖDE ORM 2.88 9.81 Yanmar 3HM 1982 Fritidssegelmotorbåt SFB‐8904 TOPEA 3.33 9.81 Volvo Penta MD11C 1981 Fritidssegelmotorbåt SFB‐8355 HAZEL 2.88 9.81 Yanmar USE 12G78 Diesel Fritidssegelmotorbåt SFB‐8627 DUNDI 3.33 9.81 Volvo Penta MD11C 1981 Fritidssegelmotorbåt SFB‐8241 CORONA AQ 2.88 9.81 Yanmar 3HMF 1984 Fritidssegelmotorbåt SFB‐7332 MARIA 2.83 9.81 Volvo Penta MD2C 1975 Fritidssegelmotorbåt SFB‐6575 SKAI TO 3.33 9.81 Volvo MD 26 1976 Fritidssegelmotorbåt SFC‐4642 FRIDA 2.88 9.81 Yanmar 2QM20 1977 Fritidssegelmotorbåt SFC‐3914 DISCOVERY 3.33 9.81 Fritidssegelmotorbåt SFC‐4046 YOLANDA 3.33 9.81 Yanmar 2QM20H 1980 Fritidssegelmotorbåt SFC‐4025 BLUE BITCH 2.88 9.81 Volvo Penta MD11 Fritidssegelmotorbåt SFC‐3728 SVASUD III 3.33 9.81 Volvo Penta Fritidssegelmotorbåt SFC‐3651 SARANG 2.88 9.81 BMW Fritidssegelmotorbåt SFC‐3852 ANNARELLA 2.88 9.81 Yanmar YSM12G Fritidssegelmotorbåt SFC‐3837 LEONI 2.88 9.81 Volvo Penta diesel Fritidssegelmotorbåt SFC‐3599 BALOO 2.85 9.81 Volvo Penta MD11C 1979 Fritidssegelmotorbåt SFC‐3582 TOVE 3.33 9.81 Yanmar Fritidssegelmotorbåt SFC‐3491 UNDA MARIS 2.88 9.81 Yanmar 3GM30F Fritidssegelmotorbåt SFC‐3551 FRIDA 2.88 9.81 Perkins Fritidssegelmotorbåt SFC‐3428 TRUD 3.33 9.81 Yanmar 3GM Fritidssegelmotorbåt SFC‐3338 MULLIGAN 3.33 9.81 Volvo Penta MD11C Fritidssegelmotorbåt 123

SFC‐5628 VINDILA 3.33 9.81 Lister‐Petter LPW/S2 Fritidssegelmotorbåt SFC‐5591 OONA 3.33 9.81 Sale 1998 Fritidssegelmotorbåt SFC‐4888 ELIN 2.88 9.81 Yanmar 3GM30F Fritidssegelmotorbåt SFC‐5430 ANNA 3.33 9.81 Yanmar 2QM20 1980 Fritidssegelmotorbåt SFC‐6463 MARION HOOD 3.33 9.81 Perkins Fritidssegelmotorbåt SFC‐6535 TRUSTY 2.88 9.81 Yanmar 2QM20, 1977 Fritidssegelmotorbåt SFC‐3918 CHARLOTTA 2.88 9.81 Yanmar 2QMdiesel Fritidssegelmotorbåt SFC‐3666 MOLLY 3.33 9.81 Volvo Penta Fritidssegelmotorbåt SFC‐3612 BANJO 2.88 9.81 Volvo Penta Fritidssegelmotorbåt SFC‐3669 BLÅVALEN 2.88 9.81 Volvo Penta MS11C Fritidssegelmotorbåt SFC‐3538 GASTON 2.88 9.81 Volvo Penta MD2B Fritidssegelmotorbåt SFC‐6023 MONA‐MI 3.33 9.81 Volvo Penta MD11C 1981 Fritidssegelmotorbåt SFC‐5707 JANITA II 2.80 9.80 Izusu 1997 Fritidssegelmotorbåt SFB‐7351 TAI 2.88 9.80 Sachs diesel Fritidssegelmotorbåt SFC‐3486 BIRD ON THE WING 3.20 9.80 Yanmar YSB12GM Fritidssegelmotorbåt SFC‐3658 HORISONT 2.88 9.80 MD2 Fritidssegelmotorbåt SFC‐6257 MANANNAN 3.33 9.80 Yanmar 2QM20 Fritidssegelmotorbåt SFC‐3379 RENESSAN 3.10 9.80 Yanmar 3GM30F Fritidssegelmotorbåt SFC‐6989 IRIZ 2.90 9.75 Yanmar diesel Fritidssegelmotorbåt SFC‐6350 JOSEFINE 3.05 9.75 Perkins 4236 Fritidssegelmotorbåt SFC‐5272 CAMILLA II 2.88 9.71 Volvo Penta MD2B 1972 Fritidssegelmotorbåt SFC‐3461 ANJA 2.84 9.70 Albin 022 Kombi Fritidssegelmotorbåt SFC‐3810 POLAR BEAR 3.00 9.70 Volvo MD3 1976 Fritidssegelmotorbåt SFC‐5751 LINNéA 3.20 9.70 Volvo Penta 3002 1987 Fritidssegelmotorbåt SFC‐6468 MARINA 3.16 9.60 IVECO aifo 4141M48 2001 Fritidssegelmotorbåt SFC‐3517 TUATARA 3.00 9.60 Isuzu Fritidssegelmotorbåt SFC‐7825 CROWN II 3.01 9.60 Bukh DV20SMF, 1979 Fritidssegelmotorbåt SFC‐3307 THETIS 3.60 9.60 Perkins Fritidssegelmotorbåt SFC‐3349 TRAVEL 3.03 9.60 Yanmar 2GM20 1986 Fritidssegelmotorbåt 124

SFC‐3253 TILIA 2.88 9.60 Volvo Fritidssegelmotorbåt SFC‐3638 AURORA BOREALIS 2.55 9.60 Yanmar YSE8 Fritidssegelmotorbåt SFC‐5524 ZULIKA 2.98 9.60 Volvo Penta MD7A Fritidssegelmotorbåt SFC‐4824 FRISCO 3.20 9.60 Volvo Penta 2002 1986 Fritidssegelmotorbåt SFC‐3326 MÄSCHA 3.00 9.58 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐3604 IDA‐LINA 3.00 9.56 Volvo Penta MD2B Fritidssegelmotorbåt SFC‐4589 MOONBA 3.05 9.55 Volvo Penta MD17C, 1979 Fritidssegelmotorbåt SFC‐6164 P.S. 3.05 9.55 Volvo Penta MD17C 1984 Fritidssegelmotorbåt SFC‐3493 LOKE 2.98 9.55 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐4085 BOTTIN II 3.05 9.55 Volvo Penta MD17C 1979 Fritidssegelmotorbåt SFC‐3287 SJÖFÅGEL 3.05 9.55 Volvo Penta Fritidssegelmotorbåt SFB‐8881 LUNKENTUSS 3.05 9.55 Volvo Penta MD17C Fritidssegelmotorbåt SFC‐6231 CINDERELLA 3.05 9.55 Yanmar 1987 Fritidssegelmotorbåt SFB‐8630 MANI 3.05 9.55 Volvo Penta MD17C/15560 Fritidssegelmotorbåt SFC‐3534 CAPRICHO 3.05 9.55 Volvo Penta MD3 Fritidssegelmotorbåt SFC‐3377 BIANCA 3.20 9.50 Volvo Penta MD11D Fritidssegelmotorbåt SFC‐3621 ALEXANDRA 3.20 9.50 Volvo Penta MD2B Fritidssegelmotorbåt SFC‐3718 MYC 5 3.27 9.50 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐3738 GITSI II 3.20 9.50 Volvo Penta MD11A Fritidssegelmotorbåt SFC‐6196 ORION 3.20 9.50 Volvo 2020, 2000 Fritidssegelmotorbåt SFC‐6241 KIKE 3.20 9.50 Volvo Penta MD11C 1976 Fritidssegelmotorbåt SFC‐3467 3.30 9.50 Volvo Penta 2002 Fritidssegelmotorbåt SFC‐3445 MOONLIGHT 3.25 9.50 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐3537 CASCADE 3.20 9.50 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐4016 LITORINA 3.20 9.50 Volvo Penta MD11C 1978 Fritidssegelmotorbåt SFC‐3794 MISCHA 3.20 9.50 Volvo Penta MD11c 1981 Fritidssegelmotorbåt SFC‐3466 IRRWIND 3.27 9.50 Volvo Penta 2002 Fritidssegelmotorbåt SFC‐3546 SIRENA 3.20 9.50 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐3586 MIDNAIGHTS ANN 3.27 9.50 Volvo Penta MD11C Fritidssegelmotorbåt 125

SFC‐3439 GALATEA 3.20 9.50 Volvo Penta MD11 Fritidssegelmotorbåt SFB‐6835 MAXIMANT 3.20 9.50 Volvo Penta MD11C 1980 Fritidssegelmotorbåt SFC‐6173 HERMES 3.20 9.50 Volvo Penta MD2B 1977 Fritidssegelmotorbåt SFC‐6232 MYSING 3.20 9.50 Volvo Penta 2030 2001 Fritidssegelmotorbåt SFC‐5484 DELTA HARMONI II 3.20 9.50 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐6856 INCH BY WINCH 3.27 9.50 Volvo Penta 2002, 1984 Fritidssegelmotorbåt SFC‐3611 SIRéNE 3.27 9.50 Volvo Penta 2002S Fritidssegelmotorbåt SFC‐4026 FLEX 3.27 9.50 Volvo MD11C 1980 Fritidssegelmotorbåt SFC‐4608 CARISMA 3.11 9.48 Yanmar 2GMF 1990 Fritidssegelmotorbåt SFC‐3673 FLAMMAN 3.11 9.48 Volvo Penta MD7A Fritidssegelmotorbåt SFC‐3423 LI 2.70 9.46 Albin 021 Fritidssegelmotorbåt SFC‐3911 RUSTICA 2.76 9.46 Saab 2HSP371 Fritidssegelmotorbåt SFC‐3767 UNICORN AF SÖLVESBORG 2.88 9.45 Perkins M5OBA Fritidssegelmotorbåt SFC‐6248 TRYGGA RÄKAN 4.50 9.45 Lombardini TMD 1998 Fritidssegelmotorbåt SFC‐3302 3.00 9.45 Yanmar 2GM20 Fritidssegelmotorbåt SFC‐3752 CANTUS 2.98 9.45 Volvo Penta D2003 1992 Fritidssegelmotorbåt SFC‐3699 3.10 9.45 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐7970 HAFSORKESTERN 3.29 9.45 Volvo Penta D1‐20 Fritidssegelmotorbåt SFC‐5171 MEHETIA 5.48 9.44 Yanmar SB8G Fritidssegelmotorbåt SFC‐6508 TRINE 3.00 9.44 VP2001S, 1987 Fritidssegelmotorbåt SFC‐6256 FELICIA 2.95 9.43 Volvo MD11, 1977 Fritidssegelmotorbåt SFC‐3629 ARMADA 2.95 9.43 Volvo Penta MD2B Fritidssegelmotorbåt SFC‐3940 MANANA 3.08 9.42 Volvo Penta MD11S120 Fritidssegelmotorbåt SFC‐3289 BEL AIR 3.00 9.42 Yanmar 1GM Fritidssegelmotorbåt SFC‐3512 ALLO ALLO 2 3.20 9.41 Yanmar YSB12 Fritidssegelmotorbåt SFC‐3536 MALENA 3.20 9.41 Volvo Penta MD7A Fritidssegelmotorbåt SFC‐5746 XAVANTE 3.20 9.41 Volvo Penta MD7A 1978 Fritidssegelmotorbåt SFC‐6238 3.14 9.40 Yanmar 2QM20 1988 Fritidssegelmotorbåt SFC‐5866 KAJSA 3.05 9.40 Yanmar 3GM30F 1985 Fritidssegelmotorbåt 126

SFC‐5265 KURTISAN 3.25 9.40 Volvo Penta MD17 Fritidssegelmotorbåt SFC‐6482 ALMA 3.05 9.40 Volvo 2002 nr1554, 1983 Fritidssegelmotorbåt SFC‐6811 MAY4US 3.25 9.40 Volvo Penta 1988 Fritidssegelmotorbåt SFC‐5189 MARELD 2.70 9.40 Volvo Penta MD2B, 1977 Fritidssegelmotorbåt SFC‐5464 RUNAWAY 3.05 9.40 Volvo Penta 2002 1983 Fritidssegelmotorbåt SFC‐3296 FIREFLY 3.20 9.40 Volvo Penta MD7 Fritidssegelmotorbåt SFC‐3359 BEDA 3.25 9.40 Volvo Penta MD17 Fritidssegelmotorbåt SFC‐3352 VITESSE 3.08 9.40 Volvo Penta Fritidssegelmotorbåt SFC‐3591 JOAR II 2.75 9.40 Perkins MD20 Fritidssegelmotorbåt SFC‐4967 LA BRIQUE 3.20 9.40 Volvo Penta MD11C 1977 Fritidssegelmotorbåt SFC‐5418 3.20 9.40 Volvo Penta MD11C 1980 Fritidssegelmotorbåt SFB‐8783 JANTAR 2.70 9.40 Volvo Penta MD1 Fritidssegelmotorbåt SFC‐3413 JOSEFIN 3.05 9.40 Yanmar 2GM20F Fritidssegelmotorbåt SFB‐8356 CAYA 2.75 9.40 Volvo Penta MD2 1967 Fritidssegelmotorbåt SFB‐7943 AVEC TOI 3.22 9.37 Volvo Penta MB10 1978 Fritidssegelmotorbåt SFC‐3684 CULEX 3.20 9.37 Volvo Penta Fritidssegelmotorbåt SFC‐3700 ADELé 3.05 9.36 Yanmar 2QM20 Fritidssegelmotorbåt SFC‐5988 ZARINA 2.87 9.36 Volvo Penta 1979 Fritidssegelmotorbåt SFC‐6373 BIANCA 2.87 9.36 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐6932 ISI 2.87 9.36 Volvo Penta MD 2B Fritidssegelmotorbåt SFC‐6223 NUEVA 2.87 9.36 Volvo Penta MD 11 C, 1978 Fritidssegelmotorbåt SFC‐3271 BRISA MEDIA 2.87 9.36 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐3394 MARIANA 2.87 9.36 Volvo Penta MD2B Fritidssegelmotorbåt SFC‐3535 GALICIA 2.87 9.36 Volvo Penta MD2B Fritidssegelmotorbåt SFC‐3541 HAVSULAN 3.05 9.36 Yanmar 3QM30 Fritidssegelmotorbåt SFC‐4153 NAVICULA 2.87 9.36 Volvo Penta MD2030 1994 Fritidssegelmotorbåt SFC‐4092 ERATO 2.87 9.36 Volvo Penta MD2B Fritidssegelmotorbåt SFB‐7551 ELISABETH 2.87 9.36 Volvo Penta MD2B 1974 Fritidssegelmotorbåt SFB‐7850 ATOLL II 3.05 9.36 Volvo Penta MD17 Diesel Fritidssegelmotorbåt 127

SFC‐5236 PEACE III 3.05 9.36 Yanmar 3HM35 Fritidssegelmotorbåt SFC‐5204 ANEMONE 2.87 9.36 Volvo Penta MD11C 1977 Fritidssegelmotorbåt SFC‐5114 SOLBRIS 2.87 9.36 Volvo Penta MD2B 1976 Fritidssegelmotorbåt SFC‐4956 FRIDA 2.87 9.36 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐4943 WISA 3.15 9.35 Yanmar GM3 1994 Fritidssegelmotorbåt SFC‐3515 NESHA 2.95 9.35 Volvo Penta MD2 Fritidssegelmotorbåt SFC‐3572 JASMIN 3.07 9.35 Yanmar Fritidssegelmotorbåt SFC‐3600 DANCING GIRL 3.04 9.35 Yanmar SGM09556 Fritidssegelmotorbåt SFC‐3403 MALGORZATA 3.07 9.35 Yanmar YSM12G80 Fritidssegelmotorbåt SFC‐3331 JOY TOY 3.07 9.35 Yanmar YSM12 Fritidssegelmotorbåt SFB‐8971 ERATO DE LUND 2.95 9.35 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐3558 CILLA II 2.85 9.35 Volvo Penta MD2 Fritidssegelmotorbåt SFC‐3402 LENA 2.78 9.33 Yanmar YSB212G Fritidssegelmotorbåt SFC‐4088 FANDAGO 2.78 9.33 Yanmar 1975 Fritidssegelmotorbåt SFC‐3654 2.78 9.33 Yanmar Fritidssegelmotorbåt SFC‐6608 2.78 9.31 Yanmar, 1975 Fritidssegelmotorbåt SFC‐6498 PRO EN CONTRA 2.96 9.30 BUKH DV24ME, 1992 Fritidssegelmotorbåt SFC‐3244 WENONAH 2.70 9.30 Lloyd Fritidssegelmotorbåt SFC‐3715 ANNIKEN AF SKÄLDERVIKEN 3.00 9.30 Yanmar Fritidssegelmotorbåt SFC‐3500 CHARLOTTA 3.20 9.30 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐5860 MANASSE AV STRÄNGNÄS 3.00 9.30 Volvo Penta MD3 1984 Fritidssegelmotorbåt SFC‐5945 MARE 3.20 9.30 Volvo Penta MD7B 1981 Fritidssegelmotorbåt SFC‐5542 FRIDA 3.00 9.30 Yanmar YSB 12 Fritidssegelmotorbåt SFC‐3968 BERTA II 2.70 9.30 Volvo Penta 2002 1992 Fritidssegelmotorbåt SFC‐3731 ISIS 2.70 9.30 Volvo Penta MD5B Fritidssegelmotorbåt SFC‐3376 HIPPO III 2.80 9.30 Volvo Penta MD21 Fritidssegelmotorbåt SFC‐3336 COOL 3.20 9.30 Volvo Penta 2003 1989 Fritidssegelmotorbåt SFC‐3365 GOVINDA 2.50 9.30 Inombord, diesel Fritidssegelmotorbåt SFC‐3577 BANTAR EJ 3.20 9.30 Volvo Penta Fritidssegelmotorbåt 128

SFC‐3505 ANNKRISTIN 3.20 9.30 Volvo Penta MD2B Fritidssegelmotorbåt SFC‐3550 BEATRICE 3.20 9.30 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐3547 CARIOCA III 3.20 9.30 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐3294 ANDROMEDA 2.80 9.25 Yanmar 12TR16 Fritidssegelmotorbåt SFC‐5726 WINNIE 3.20 9.20 Yanmar 1980 Fritidssegelmotorbåt SFC‐3502 RUDOLF 2.85 9.20 Perkins Fritidssegelmotorbåt SFC‐3298 BONNIE LEE 3.20 9.20 Volvo Penta MD7A Fritidssegelmotorbåt SFC‐5745 LIBRA 2.70 9.20 Bukh 1986 Fritidssegelmotorbåt SFC‐3267 KULING 2.96 9.17 Volvo Penta MD6A Fritidssegelmotorbåt SFC‐3581 THETIS 2.96 9.16 Volvo Penta MD6A Fritidssegelmotorbåt SFC‐3688 MINDANAO 2.96 9.15 Volvo Penta MD7 Fritidssegelmotorbåt SFC‐6456 FRU MUSICA 2.98 9.15 Volvo Penta 2020‐C 1999 Fritidssegelmotorbåt SFB‐7333 SAMARIA 2.96 9.14 Volvo Penta MD6B Fritidssegelmotorbåt SFC‐3430 LADY 2 2.96 9.14 Volvo Penta MD7A Fritidssegelmotorbåt SFC‐4099 PETRA 2.98 9.14 Yanmar YSE8 GO 1470 Fritidssegelmotorbåt SFC‐3683 2.96 9.14 Volvo Penta MD6A Fritidssegelmotorbåt SFC‐3623 DIGNITY 2.96 9.14 Volvo Penta MD7A Fritidssegelmotorbåt SFC‐5169 CHAKINA 2.96 9.14 Nanni 3.75HE 1996 Fritidssegelmotorbåt SFC‐5688 MARIE CLAIRE 2.96 9.14 Volvo Penta MD6 Fritidssegelmotorbåt SFC‐6472 UHURU 4.30 9.10 Honda EF25, 1999 Fritidssegelmotorbåt SFC‐3609 ARESCHENUT III 3.05 9.10 Volvo Penta MD7D Fritidssegelmotorbåt SFC‐3878 HOBO 3.05 9.10 Yanmar diesel Fritidssegelmotorbåt SFB‐8294 CARMEN 2.95 9.10 Volvo Penta 2002 MS2 Fritidssegelmotorbåt SFC‐5859 FAUVE 3.05 9.10 Volvo Penta MD 7B Fritidssegelmotorbåt SFC‐3311 RUFFINA 2.90 9.10 Renault Fritidssegelmotorbåt SFB‐8861 KAMI 3.05 9.10 Yanmar 3GM 1984 Fritidssegelmotorbåt SFC‐3548 EXPLORER OF SWEDEN 3.28 9.09 Yanmar 1GM Fritidssegelmotorbåt SFC‐3532 FELICIA 3.03 9.09 Volvo Penta MB10 Fritidssegelmotorbåt SFC‐3327 SEUTE DEERN II 3.00 9.07 Yanmar2GM20F Fritidssegelmotorbåt 129

SFC‐4872 ANIA 3.00 9.07 Yanmar Fritidssegelmotorbåt SFC‐3427 JASMINE 2.55 9.05 Yanmar YSE8 Fritidssegelmotorbåt SFC‐3999 STINA 2.35 9.04 Perkins Perama MD20 1993 Fritidssegelmotorbåt SFC‐3569 CONCORDIA 2.08 9.03 Yanmar YSB12 Fritidssegelmotorbåt SFC‐5907 PIRELLA 3.02 9.00 Volvo Penta 2002 1985 Fritidssegelmotorbåt SFC‐5140 TANOE II 2.75 9.00 BMW LloydLM400 1975 Fritidssegelmotorbåt SFC‐6710 ANJIN 2.80 9.00 Volvo Penta MD11, 1981 Fritidssegelmotorbåt SFC‐3382 LABANA 3.00 9.00 Yanmar Fritidssegelmotorbåt SFC‐3421 SILENTIUM 3.20 9.00 Faryman 28S 1978 Fritidssegelmotorbåt SFC‐3469 MONA‐LISA 3.08 9.00 Volvo Penta 2002BT Fritidssegelmotorbåt SFC‐3242 MANANA 2.80 9.00 Yanmar YSE10/12 Fritidssegelmotorbåt SFC‐6504 PAULINA 2.80 9.00 Penta 2002 1984 Fritidssegelmotorbåt SFC‐5274 ORACABESSA 2.85 9.00 Faryman 31R30M0051 Fritidssegelmotorbåt SFB‐8770 BONNE CHANCE 2.76 8.95 Volvo Penta MD 7/110 S Fritidssegelmotorbåt SFC‐4870 ANGUILLA 2.84 8.95 IGM10 Fritidssegelmotorbåt SFC‐5143 MELANIE 3.00 8.90 Yanmar YSE8G 1974 Fritidssegelmotorbåt SFB‐7439 HATI SENTOSA 3.90 8.90 Yanmar Fritidssegelmotorbåt SFC‐3540 PELLINA 2.83 8.90 Volvo Penta MD7B Fritidssegelmotorbåt SFC‐3360 OPTIMIST 2.83 8.90 Volvo Penta MD7B Fritidssegelmotorbåt SFC‐3620 LADY 2.50 8.89 Yanmar IGM Fritidssegelmotorbåt SFB‐7989 BARINA 2.76 8.88 Perkins M20 Fritidssegelmotorbåt SFC‐3269 JOHANNA 2.60 8.86 Yanmar 2GM Fritidssegelmotorbåt SFB‐8628 NATASJA 2.60 8.86 Yanmar YSE8 1976 Fritidssegelmotorbåt SFC‐3251 AVOSETTA 2.60 8.86 Faryman Fritidssegelmotorbåt SFC‐5601 MARIA 2.60 8.86 Yanmar USE8 1974 Fritidssegelmotorbåt SFC‐3389 MAJONG 2.65 8.85 Volvo Penta MD5B Fritidssegelmotorbåt SFC‐6351 LANA III RÅÅ 2.50 8.81 Albin 0‐22, 1970 Fritidssegelmotorbåt SFC‐3708 CARAMELL 2.70 8.80 Volvo Penta MD6a Fritidssegelmotorbåt SFC‐4006 LARUS 2.60 8.80 Yanmar YSB‐12 1986 Fritidssegelmotorbåt 130

SFC‐4017 SAMANTA 2.70 8.80 Volvo Penta MD7A 1978 Fritidssegelmotorbåt SFB‐7444 EXUMA 2.70 8.80 Volvo MD6A 1975 Fritidssegelmotorbåt SFC‐3278 PÅLLIANNA 2.60 8.80 Faryman Fritidssegelmotorbåt SFC‐3554 TONA 2.70 8.80 Volvo Penta MD6A Fritidssegelmotorbåt SFC‐7999 EEKAROS 2.50 8.80 Yanmar YSE8, 1978 Fritidssegelmotorbåt SFC‐3853 OYA 2.40 8.77 Volvo Penta MD1 Fritidssegelmotorbåt SFB‐8270 LIANA 3.06 8.72 Sabb Typ G 1977 Fritidssegelmotorbåt SFC‐6437 JOHANNA 3.00 8.70 VP 2002, 1990 Fritidssegelmotorbåt SFC‐5230 TURI 2.75 8.70 Yanmar 2GM20F 1987 Fritidssegelmotorbåt SFC‐4959 ORCA 3.80 8.65 BMW D50‐2 diesel 1986 Fritidssegelmotorbåt SFB‐8113 MARLIN 2.63 8.64 Volvo Penta MD2 Fritidssegelmotorbåt SFC‐3523 TALISMANA 2.35 8.64 Albin 021 Fritidssegelmotorbåt SFC‐3431 TAKA TAKA 2.92 8.62 Volvo Penta 2001 Fritidssegelmotorbåt SFC‐6586 RUSALKA 2.70 8.60 Volvo Penta MD 6B 1976 Fritidssegelmotorbåt SFC‐3910 TARONA 2.97 8.56 Volvo Penta MD7B Fritidssegelmotorbåt SFC‐3452 AGNES 2.50 8.50 Yanmar YSE8 Fritidssegelmotorbåt SFC‐3335 2.70 8.50 Volvo Penta MD6A Fritidssegelmotorbåt SFC‐4658 2.30 8.50 Volvo Penta 140300298 87 Fritidssegelmotorbåt SFC‐3856 CHRISTINA 2.85 8.50 Volvo Penta MD5 Fritidssegelmotorbåt SFC‐3832 YETTAN 3.00 8.50 Couach, bensin Fritidssegelmotorbåt SFC‐6406 JOSEPHINE 2.43 8.43 Yanmar SB8, 1982 Fritidssegelmotorbåt SFC‐3607 RUT 2.65 8.40 Yanmar YSE8 Fritidssegelmotorbåt SFC‐3520 2.20 8.40 Yamaha Fritidssegelmotorbåt SFC‐6863 FRILLAN 2.55 8.40 Yanmar diesel 4SE8 Fritidssegelmotorbåt SFC‐3380 ZENIA 2.93 8.40 Volvo Penta MD7A Fritidssegelmotorbåt SFC‐3519 MIA 2.95 8.40 Volvo Penta Fritidssegelmotorbåt SFB‐7347 DIONE 2.90 8.40 Volvo Penta MD7C Fritidssegelmotorbåt SFC‐3590 HULDA 2.50 8.35 Volvo Penta MD1 Fritidssegelmotorbåt SFC‐3356 GERONIMO 2.50 8.35 Volvo Penta MD7A Fritidssegelmotorbåt 131

SFC‐3647 ESCAPAD 2.75 8.35 Yanmar Fritidssegelmotorbåt SFC‐3833 ARJUNA 2.50 8.34 Volvo Penta MD1B Fritidssegelmotorbåt SFC‐3583 LAUR‐ANN 2.50 8.34 Yanmar SB8G Fritidssegelmotorbåt SFC‐3274 AMMEFANT 2.50 8.34 Volvo Penat MD1B Fritidssegelmotorbåt SFC‐5448 SHEHERAZADE 2.50 8.34 Volvo Penta 2001 1992 Fritidssegelmotorbåt SFC‐3303 2.50 8.34 Volvo Penta Fritidssegelmotorbåt SFC‐3441 ALBA NOVA II 2.83 8.34 Volvo Penta MD5B Fritidssegelmotorbåt SFB‐6934 TUA‐TUA 2.50 8.34 Farymann FK 2 1980 Fritidssegelmotorbåt SFB‐7315 NONAME 2.50 8.34 Yanmar SB8 Fritidssegelmotorbåt SFB‐7500 YELLOW ROSE 2.50 8.34 Volvo Penta MD1B Fritidssegelmotorbåt SFB‐7642 MICASA III 2.40 8.30 Yanmar Fritidssegelmotorbåt SFC‐3321 GOLIF III 2.50 8.30 Yamaha 668L Fritidssegelmotorbåt SFC‐5154 ARTEMISIA 2.44 8.25 Volvo Penta MD1B Fritidssegelmotorbåt SFC‐5651 MISS LINNéA 2.46 8.25 Albin 022 Fritidssegelmotorbåt SFB‐8048 BIRGITTA 2.46 8.25 Yanmar Fritidssegelmotorbåt SFC‐3353 WILMA 2.46 8.25 Volvo Penta combi Fritidssegelmotorbåt SFC‐3390 NINNA 2.40 8.25 Volvo Penta MD6A Fritidssegelmotorbåt SFC‐5397 NICKAN 2.46 8.25 Alvin 022 Fritidssegelmotorbåt SFC‐3874 MILNA 2.46 8.25 Fritidssegelmotorbåt SFC‐3702 VISAN 2.46 8.25 Volvo Penta MD6B Fritidssegelmotorbåt SFC‐5932 KIPPIS 2.46 8.25 Volvo MD 7A Fritidssegelmotorbåt SFB‐7445 KICK 2.46 8.25 Albin O‐21 bensin 1969 Fritidssegelmotorbåt SFB‐8076 NAVIGO 2.46 8.25 Albin 0,21 1969 Fritidssegelmotorbåt SFC‐3626 SIROCCO 2.46 8.25 Volvo Penta MD6A Fritidssegelmotorbåt SFC‐4249 SCILLA II 2.46 8.25 Volvo Penta MD6A 1976 Fritidssegelmotorbåt SFC‐4403 2.46 8.25 Albin 021‐67 Fritidssegelmotorbåt SFB‐8547 TWILIGHT 2.63 8.23 Bukh DV20ME 1983 Fritidssegelmotorbåt SFC‐3454 MERISKI 2.60 8.22 Volvo Penta MD5C Fritidssegelmotorbåt SFC‐3605 WACK 2.76 8.20 Yanmar 2GM20F Fritidssegelmotorbåt 132

SFC‐4911 HAVGRIM 3.12 8.20 Volvo Penta MD 6 Fritidssegelmotorbåt SFC‐3739 DIOMEDES 2.78 8.13 Volvo Penta Fritidssegelmotorbåt SFC‐3882 SOLLAN 2.74 8.12 Volvo Penta MD5A Fritidssegelmotorbåt SFC‐3601 2.76 8.05 Volvo Penta Fritidssegelmotorbåt SFC‐3254 AQUARIUS 2.77 8.05 Yanmar YSB8 Fritidssegelmotorbåt SFC‐3579 HIME 2.75 8.04 Yanmar YSM8G Fritidssegelmotorbåt SFC‐4934 ANIMA 6.70 8.04 Yamaha 9.9AE 1991 Fritidssegelmotorbåt SFC‐4896 LITORINA 2.76 8.03 Volvo Penta MD7A Fritidssegelmotorbåt SFC‐5535 AYLA 2.76 8.03 Yanmar YSB8G 1976 Fritidssegelmotorbåt SFC‐5207 ANNA 2.76 8.03 Volvo Penta MD7A Fritidssegelmotorbåt SFC‐4064 RISSA 2.76 8.03 Volvo Penta MD7A 1978 Fritidssegelmotorbåt SFC‐5118 SENORITA 2.76 8.03 Yanmar 8/1980 diesel Fritidssegelmotorbåt SFC‐5529 JEMIMA 2.78 8.03 BMW D12 1983 Fritidssegelmotorbåt SFC‐3358 BLÅNUS 2.76 8.03 Volvo Penta, Suzuki Fritidssegelmotorbåt SFC‐3385 AZUR 2.80 8.03 Volvo Penta MD4A Fritidssegelmotorbåt SFC‐3367 2.76 8.03 Volvo Penta MD6 Fritidssegelmotorbåt SFB‐7618 CALYPSO 2.76 8.03 Yanmar SB8G 1981 Fritidssegelmotorbåt SFB‐8582 AKKJA 2.76 8.03 Volvo Penta MD1 1973 Fritidssegelmotorbåt SFB‐7314 HELENICA 2.76 8.03 Volvo Penta MD1 Fritidssegelmotorbåt SFB‐7152 ANNA III 2.76 8.03 Volvo Penta MD1 B Fritidssegelmotorbåt SFC‐3492 MARIE 2.76 8.03 Volvo Penta MD6B Fritidssegelmotorbåt SFB‐8915 ALFRIDA II 2.76 8.03 Yanmar YSE12 1978 Fritidssegelmotorbåt SFB‐9105 MOONSHINE 2.76 8.03 Volvo Penta 779 1973 Fritidssegelmotorbåt SFC‐5976 LAXEN 2.76 8.03 Volvo Penta MD5B 1970 Fritidssegelmotorbåt SFC‐3275 MAY BE II 2.76 8.03 Yanmar IGM10 Fritidssegelmotorbåt SFB‐8933 BORODA 2.78 8.03 Volvo Penta MD 7 A 1979 Fritidssegelmotorbåt SFC‐3344 MARIA 2.76 8.00 Volvo Penta MD7A Fritidssegelmotorbåt SFC‐3416 THOYA 2.20 8.00 Volvo Penta MD2 Fritidssegelmotorbåt SFB‐7524 SHAMAN 2.76 8.00 Yanmar I GM 1982 Fritidssegelmotorbåt 133

SFC‐3557 ALEXANDRA 2.50 8.00 Yanmar Fritidssegelmotorbåt SFC‐5915 STARDUST 2.60 8.00 Yamaha 1999 Fritidssegelmotorbåt SFB‐7875 PEA II 2.76 8.00 Yanmar Fritidssegelmotorbåt SFC‐3426 MONZUN 2.60 8.00 Volvo Penta MD3 Fritidssegelmotorbåt SFC‐3553 HANNIKAP 2.80 8.00 Yanmar YM8 Fritidssegelmotorbåt SFC‐3884 2.50 8.00 Volvo Penta MD1B Fritidssegelmotorbåt SFC‐3861 INGA 2.30 8.00 Fritidssegelmotorbåt SFC‐4625 AMANDA 3.04 7.97 Volvo Penta MD2B 1969 Fritidssegelmotorbåt SFC‐3733 CHARLES II 2.95 7.95 Volvo Penta MD5B Fritidssegelmotorbåt SFC‐3518 RELAX 2.51 7.95 Yanmar YSE8E Fritidssegelmotorbåt SFC‐3342 SARA 2.68 7.95 Volvo Penta MD5A Fritidssegelmotorbåt SFC‐4262 MEDUSA 2.68 7.95 Volvo Penta MD5A110S 1979 Fritidssegelmotorbåt SFB‐8609 WIND SONG 2.68 7.95 Volvo Penta MD5B Fritidssegelmotorbåt SFC‐3282 SAGITTA 2.68 7.95 Volvo Penta MD5B Fritidssegelmotorbåt SFB‐8578 RITA III 2.40 7.90 Volvo Penta MD2A 1978 Fritidssegelmotorbåt SFC‐5229 HYGGE MYS 2.50 7.90 Volvo Penta MD5B 1980 Fritidssegelmotorbåt SFC‐3509 TAO 2.66 7.90 Yanmar 1GM10 Fritidssegelmotorbåt SFC‐3506 SUN FLOWER 2.20 7.86 Johnson Fritidssegelmotorbåt SFC‐3628 MIMMI 2.25 7.85 Johnson Sailmaster Fritidssegelmotorbåt SFB‐8921 SAXIFRAGA 2.20 7.85 Johnson 1976 Fritidssegelmotorbåt SFC‐3522 BLUE 2.25 7.85 Mercury 1984 Fritidssegelmotorbåt SFC‐3841 ROMANCE 2.95 7.80 Volvo Penta MD11C Fritidssegelmotorbåt SFB‐6826 TAI‐FUN 2.28 7.80 Chrysler 3337 1970 Fritidssegelmotorbåt SFC‐6866 CYRANO DE BERGERAC 2.70 7.80 Yanmar Diesel YSB 12 Fritidssegelmotorbåt SFC‐3473 CLOWN 2.50 7.70 DT8 Fritidssegelmotorbåt SFC‐3388 FILIBUSTER 2.35 7.70 2 Volvo Penta MD5C Fritidssegelmotorbåt SFC‐4537 KEHAAR 2.50 7.70 Volvo Penta MD7A 1978 Fritidssegelmotorbåt SFC‐4673 TURTLE 2.70 7.70 Volvo Penta MD6A, 1975 Fritidssegelmotorbåt SFC‐3711 MAROUSCHKA III 2.50 7.70 Volvo Penta MD5A Fritidssegelmotorbåt 134

SFC‐3888 BLUE PI 2.60 7.70 Volvo penta MD5B Fritidssegelmotorbåt SFC‐5565 ARIA 2.50 7.70 Mercury 9,9 1996 Fritidssegelmotorbåt SFC‐4076 CARAMBA 2.40 7.65 Volvo Penta MD5B 1980 Fritidssegelmotorbåt SFC‐3913 HAMBO 2.52 7.64 Albin 0‐22 Fritidssegelmotorbåt SFC‐4949 CORINNE 2.40 7.60 Volvo Penta MD2 1766 Fritidssegelmotorbåt SFC‐3844 WIRGO 2.40 7.60 Volvo Penta MD2B Fritidssegelmotorbåt SFC‐3415 MANUELA 2.40 7.60 Volvo Penta MD11C Fritidssegelmotorbåt SFC‐3232 CASSIOPEJA 2.40 7.60 Volvo Penta MD2 Fritidssegelmotorbåt SFC‐3397 MARINA 2.50 7.50 Perkins Fritidssegelmotorbåt SFC‐3829 AFRODITE 2.50 7.50 Volvo Penta 2001 diesel Fritidssegelmotorbåt SFC‐3606 NADINA 2.25 7.35 Suzuki DT5 Fritidssegelmotorbåt SFC‐6028 SASKIA 2.30 7.35 Zuzuki utombord Fritidssegelmotorbåt SFC‐3995 GONDWA 2.30 7.35 Yamaha utombord Fritidssegelmotorbåt SFC‐3404 SAMMI 2.80 7.30 Volvo Penta MD17C Fritidssegelmotorbåt SFC‐6075 AMI 2.25 7.30 Mariner Fritidssegelmotorbåt SFC‐4662 LEDIGA STUNDER 2.50 7.30 Vire 1985 Fritidssegelmotorbåt SFC‐3425 BLACK PEARL 2.64 7.25 Volvo Penta MD22 Fritidssegelmotorbåt SFB‐7125 AALTO 2.36 7.10 Färe‐Göta Fritidssegelmotorbåt SFC‐3616 2.25 7.05 Mariner Fritidssegelmotorbåt SFC‐3369 PASSEPARTOUT 2.50 7.00 Seagull Fritidssegelmotorbåt SFC‐6001 2.39 6.90 Yamaha utombord 1998 Fritidssegelmotorbåt SFB‐6984 GALADRIEL 2.08 6.80 Suzuki Fritidssegelmotorbåt SFC‐6271 WAYLANY 2.38 6.71 Kubota, 1993 Fritidssegelmotorbåt SFC‐3391 MONICA 2.22 6.70 Johnson, Fritidssegelmotorbåt SFC‐6038 ANNA LAVINIA 1.81 6.70 Utombord 1993 Fritidssegelmotorbåt SFC‐3488 TELEMACHOS II 1.80 6.64 Johnson Fritidssegelmotorbåt SFC‐3644 2.45 6.50 Evinrude Fritidssegelmotorbåt SFC‐6903 MOROLINE 2.26 6.50 Johnson Fritidssegelmotorbåt SFC‐4997 PETER PAN 1.80 6.50 Yamaha Fritidssegelmotorbåt 135

SFC‐5458 AVA 2.20 6.00 Volvo Penta MD1 Fritidssegelmotorbåt SFC‐3484 SKIDBLADNER 2.20 6.00 Volvo Penta MD1B Fritidssegelmotorbåt SFC‐3997 AMANDA II 2.20 6.00 Albin 011‐69 Fritidssegelmotorbåt SFC‐3831 DARLING DUCK 2.20 6.00 Johnson Fritidssegelmotorbåt SFC‐4659 NJORD 2.20 6.00 Vira 1984 Fritidssegelmotorbåt SFC‐3366 GOODWIN II 2.20 6.00 Volvo Penta Fritidssegelmotorbåt SFB‐5481 TIN HAU 2.20 6.00 Färe Göta 6BR Fritidssegelmotorbåt SFC‐5922 SPRIGG II 2.20 6.00 Yanmar SB8G 1977 Fritidssegelmotorbåt SFC‐4937 TUA 2.20 6.00 Albin 0 11 Fritidssegelmotorbåt SFC‐4162 KRISTINA 2.20 6.00 Göta F‐typ 6BRE Fritidssegelmotorbåt SFC‐3835 LAKI ANTARI 2.20 6.00 Johnson, bensin Fritidssegelmotorbåt SFC‐3685 AMANDA 2.20 6.00 Volvo Penta MD1B Fritidssegelmotorbåt SFC‐5301 LIV 2.20 5.95 Volvo Penta MD 7A, 1979 Fritidssegelmotorbåt SFC‐3610 LINNEA 2.15 5.80 Mariner Fritidssegelmotorbåt SFC‐3315 AMIB 2.41 5.70 Yamaha Fritidssegelmotorbåt SFC‐3339 NYMUE 1.99 5.64 Suzuki Fritidssegelmotorbåt SFC‐3468 1.99 5.63 Mercury Fritidssegelmotorbåt SFC‐3828 ROUFY III 2.40 5.52 Yanmar diesel Fritidssegelmotorbåt SFC‐3384 PATRICIA 2.00 5.40 Yanmar Fritidssegelmotorbåt SFC‐5290 STEFAN 2.05 4.80 Yamaha 40TL 1994 Fritidssegelmotorbåt SFC‐3261 LE CANARD III 2.00 4.75 Suzuki DT9 9M Fritidssegelmotorbåt SFC‐8231 LUKA 145 2.16 5.50 VP 30, 2005 Fritidssmotorbåt SFC‐6766 BORGSUND 2.60 9.10 Ångmaskin 2000 Fritidsångbåt

Ships: 1909 vessels ordered by type and length Width Length Call sign Name (m) (m) Machinery Type of ship SHIN HELGE 5.60 18.75 Volvo Penta TMD 96B 1966 Fritidsarbetsmotorskepp

136

SEYG IDOG 3.80 23.10 Seffle råoljem. BF121 Fritidsmotorbåt SHDW REYMERSHOLM NR 1 3.90 15.72 Fritidsmotorbåt SDOL BRITTY 5.08 11.43 Fritidsmotorbåt SHXG HÅLLIDEJ 3.21 11.35 Fritidsmotorbåt SJYO PIANDELLE 3.80 11.15 Fritidsmotorbåt SHVK VÅGEN 4.55 11.13 Fritidsmotorbåt SETZ ELEONORE 2.79 10.94 Fritidsmotorbåt SEBZ PINGVINEN 4.55 10.94 Fritidsmotorbåt SHTK TAI‐PAN 3.85 10.93 Fritidsmotorbåt SHGD LEIF 4.50 10.90 Fritidsmotorbåt SIVP FYLGIA 4.53 10.63 Fritidsmotorbåt SIWX AMANDA AF LYSEKIL 3.65 10.04 Ford Marin N.G. 6 Fritidsmotorbåt SICW MON AMI 3.06 9.62 Fritidsmotorbåt SJZE MABICO 3.06 9.62 Fritidsmotorbåt SILW MONITA III 3.05 9.06 Fritidsmotorbåt SFBV TÄRNSKÄR 3.57 8.86 Fritidsmotorbåt SIVO FASTER KERSTIN 2.80 8.32 Fritidsmotorbåt SENB SAMUEL BENJAMIN 2.46 7.81 Fritidsmotorbåt SFJO JOLIMA 3.28 14.07 Fritidsmotorsegelbåt SIFK JULIET 3.66 12.51 Fritidsmotorsegelbåt SEOJ ANDANTE 3.54 10.59 Fritidsmotorsegelbåt SIXK MARITIM III 3.01 10.45 Fritidsmotorsegelbåt SICK PRIVAT 2.78 8.90 Fritidsmotorsegelbåt SEKV DE NELLY 5.95 34.36 DAF 1160, 1979 Fritidsmotorsegelskepp SBOE NORNA 5.44 28.11 Industri 3 cyl 1959 Fritidsmotorsegelskepp SKED MARIANN AV DONSÖ 6.98 27.09 Volvo Penta D12, 2004 Fritidsmotorsegelskepp SKOU SAN 6.90 26.82 Fritidsmotorsegelskepp SHZK GARPEN 6.39 26.80 Scania D10R80 1963 Fritidsmotorsegelskepp SIVW HULDA 6.70 25.36 Fritidsmotorsegelskepp 137

SHOK AGNES 6.30 25.21 Volvo Penta MD 96 A Fritidsmotorsegelskepp SLHK SOLSKEPP 6.90 24.79 Ford 1985 Fritidsmotorsegelskepp SCLI IL MORO DI VENEZIA III 6.24 24.32 Iveco Aifo 8061SM06,1987 Fritidsmotorsegelskepp SEFK FANTASY 4.15 24.00 NANNI 6.280 HE 1993 Fritidsmotorsegelskepp SKBJ CYGNUS MONTANUS II 5.98 23.72 Perkins Sabre M225TI,‐01 Fritidsmotorsegelskepp SMKB REBELL AF STOCKHOLM 5.60 23.42 Scania D11 1967 Fritidsmotorsegelskepp SFPR VERNADIA 6.20 23.30 Fritidsmotorsegelskepp SJVK TRAVEL V 5.83 23.30 Mercedes MG 507, 1981 Fritidsmotorsegelskepp SEOI SJÖSTRÖM 6.49 23.27 Cummins, 2002 Fritidsmotorsegelskepp SDVT TWEE GEBROEDERS 4.81 22.84 DAF 6 CYL. DS 575 M 1961 Fritidsmotorsegelskepp SHEO KAJSA 6.60 22.64 Fritidsmotorsegelskepp SDUW DEODAR 5.89 22.39 Volvo TIMD 96B 1959 Fritidsmotorsegelskepp SHUA MARIA SOFIA 6.32 22.26 Scania DS 11 R80 1975 Fritidsmotorsegelskepp SJZU TÄRNAN 5.86 22.04 Volvo Penta diesel Fritidsmotorsegelskepp SDHX CATHARINA UHRWEDER 4.46 21.56 Volvo TMD 96C 1968 Fritidsmotorsegelskepp SIPD MAYANGSARI 5.42 21.55 Perkins Sabre M225 Ti ‐94 Fritidsmotorsegelskepp SLBX TALISMAN 1920 4.10 21.46 Iveco 8061M, 1984 Fritidsmotorsegelskepp SLAH CARMEN AF KARLSTAD 5.40 21.41 B&W ALPHA Fritidsmotorsegelskepp SIEU KNUDSINE AF VEJLE 5.93 21.24 Fritidsmotorsegelskepp SDAX LUDMILA 5.46 21.00 Fritidsmotorsegelskepp SKRE ADRIENNE II 5.33 20.89 Perkins M215C 1983 Fritidsmotorsegelskepp SIPM GUNHILD AV LIDINGÖ 6.57 20.87 Albin G‐62 Fritidsmotorsegelskepp SJZO MINDE 5.83 20.86 Albin diesel G 61 Fritidsmotorsegelskepp SMTB WELLAMO 5.68 20.83 Scania Vabis 6 cyl. Fritidsmotorsegelskepp SMPT MÄLAR BALDER 5.51 20.46 Perkins M135, 2001 Fritidsmotorsegelskepp SJDM LEON 5.90 20.06 Fritidsmotorsegelskepp SEZL EUREKA 5.21 19.98 Albin Diesel G62 Fritidsmotorsegelskepp SDNH PATRIA 5.24 19.96 Fritidsmotorsegelskepp SHYL EVA VII AF VAXHOLM 4.97 19.81 Volvo MD40, 1993 Fritidsmotorsegelskepp 138

SKCQ WHO VALLEY 4.97 19.81 Perkins 6.354M 1979 Fritidsmotorsegelskepp SLKV DANNEVIRKE 5.46 19.78 Albin G62 1962 Fritidsmotorsegelskepp SCWE HVITE SWAN 4.20 19.65 Fritidsmotorsegelskepp SKQX AVANT 5.82 19.65 Volvo MD 100, 1982 Fritidsmotorsegelskepp SIGF DAWNBREAKER 5.15 19.63 Yanmar 4LH‐DTE, 2002 Fritidsmotorsegelskepp SGPZ AVANT OF SWEDEN 5.20 19.61 Yanmar, 4JH2M‐TE, 1993 Fritidsmotorsegelskepp SHTL LIBERTY 6.08 19.56 Volvo TMD 96 1976 Fritidsmotorsegelskepp SKJI CONDOR 4.70 19.51 Ford 1982 Fritidsmotorsegelskepp SLQV FREJA AF VALHALL 5.38 19.51 Dong Feng, 2002 Fritidsmotorsegelskepp SBNE ARIADNE AV STOCKHOLM 5.12 19.47 DAF 825, 1983 Fritidsmotorsegelskepp SBCE ROYAL EAGLE 5.18 19.44 Volvo Penta MD ‐32 1988 Fritidsmotorsegelskepp SMTV MERENGUE 5.18 19.44 Volvo Penta MD32 1988 Fritidsmotorsegelskepp SDCU GRAN TIBURON 5.10 19.43 Caterpillar 3208V8, 1980 Fritidsmotorsegelskepp SCIL BALLAD 4.27 19.38 GM diesel 1949 Fritidsmotorsegelskepp SHZU ARKADASIM DENIZ 5.48 19.37 2 MAN, 1989 Fritidsmotorsegelskepp SBVI WINDCATCHER 5.15 19.34 Yanmar, 1990 Fritidsmotorsegelskepp SHCM CHARLOTTE OF VARBERG 5.20 19.04 Volvo Penta TAMD 63L,2005 Fritidsmotorsegelskepp SMVQ YAGHAN 5.20 19.04 Volvo Penta TAMD 63M,2002 Fritidsmotorsegelskepp SITN BAMSEN 4 5.20 19.04 Volvo Penta TMD 62, 2002 Fritidsmotorsegelskepp SBXV OCEANUS 4.61 19.02 GM 6071E, 1961 Fritidsmotorsegelskepp SLED SYLVIANA 5.22 18.71 Fritidsmotorsegelskepp SHYM ELLEN 5.35 18.67 Fritidsmotorsegelskepp SEBF WALBORG 5.50 18.63 Fritidsmotorsegelskepp SKDT TILDA 4.63 18.45 Ford Sabre 1983 Fritidsmotorsegelskepp SLZW INVISIBLE 5.01 18.42 Volvo TMD41 1986 Fritidsmotorsegelskepp SMIG KAJSA JOHANNA 5.05 18.40 Caterpilar 3406B,1988 Fritidsmotorsegelskepp SEXZ LAKOTA 15.10 18.33 Volvo MD 2030, 1991 Fritidsmotorsegelskepp SJNP LEADBELLY 5.40 18.25 Perkins M135 Fritidsmotorsegelskepp SKEH ROSE GLUDBAEK 5.18 18.20 DAN‐NORMO 1965 Fritidsmotorsegelskepp 139

SEVI JUSTUS 5.51 18.06 Volvo Penta TMD 96B Fritidsmotorsegelskepp SHYA OCEAN VIKING 4.62 18.02 Ford‐Sabre Diesel 1978 Fritidsmotorsegelskepp SKCU LA‐VIE 5.00 18.00 Volvo Penta TMD 40 Fritidsmotorsegelskepp SJWT DIONE 5.04 17.98 Perkins 6.354, 1980 Fritidsmotorsegelskepp SIQA OCEAN OVATION 4.63 17.95 Ford Sabre, 1982 Fritidsmotorsegelskepp SEQB CARENCY 5.92 17.95 Ford diesel 6cyl 1974 Fritidsmotorsegelskepp SJTD AMBER 6.18 17.89 Fritidsmotorsegelskepp SIVF FRI 5.63 17.89 Fritidsmotorsegelskepp SLKC DOUBLE YOU 4.50 17.63 Volvo Penta TMD100A 1978 Fritidsmotorsegelskepp SDKE NERTHUS 4.42 17.60 Mercedes Fritidsmotorsegelskepp SCXA PALAWAN 4.43 17.53 Cummins 6B5.9M 1989 Fritidsmotorsegelskepp SCNX SHOGUN 4.80 17.52 Perkins 4,236 M Fritidsmotorsegelskepp SHTR EMMA 5.80 17.50 Fritidsmotorsegelskepp SBLC ZINA 5.05 17.50 Yanmar 4LH‐HTE, 2001 Fritidsmotorsegelskepp SBIT TRAVESSIA 4.80 17.50 PERKINS, 1983 Fritidsmotorsegelskepp SIWF VICTORY TOO 5.05 17.50 Yanmar Diesel 4LHHTE,‐02 Fritidsmotorsegelskepp SBHV ATINELLO 4.73 17.44 Scania D 5, 1972 Fritidsmotorsegelskepp SKWV SOUVENIR 4.02 17.35 Volvo MD67 1980 Fritidsmotorsegelskepp SCHT BENTE‐DORTE 4.83 17.28 Daimler‐Benz AG 410 1976 Fritidsmotorsegelskepp SLOB VIKING AV GILLINGE 5.02 17.20 Yanmar 4LHAHTP, 2005 Fritidsmotorsegelskepp SKMA DUEN 4.82 17.12 Volvo Penta TMD 96 Fritidsmotorsegelskepp SGHX HELLAS 4.90 17.10 Fritidsmotorsegelskepp SGAM TRIFT 4.76 17.02 Volvo Penta D4‐180, 2006 Fritidsmotorsegelskepp SJTO PELLE V 4.76 17.02 Volvo Penta D‐4 180,2006 Fritidsmotorsegelskepp SBAY SOLVÅG V 4.76 17.02 Volvo Penta D4‐180, 2007 Fritidsmotorsegelskepp SFMZ ELLIPS 4.95 16.94 Ford Diesel 2704ET,1982 Fritidsmotorsegelskepp SMTY LIBERTIN 4.93 16.94 DAF 1160 DKT, 1981 Fritidsmotorsegelskepp SKMR FRIDAN 4.22 16.80 Ford D 70 1964 Fritidsmotorsegelskepp SKGY SANNA 4.22 16.80 Ford diesel 1981 Fritidsmotorsegelskepp 140

SCJD LADY FOX 4.50 16.76 Ford diesel 2712E 1980 Fritidsmotorsegelskepp SLTV NAVIGARE 4.40 16.60 Yanmar Diesel Fritidsmotorsegelskepp SBJY FAIRWINDS 4.88 16.60 Perkins, 1987 Fritidsmotorsegelskepp SGWT FILIA MARIS 4.62 16.58 Volvo TAMD 41, 1996 Fritidsmotorsegelskepp SJAH NELLAN AF NACKA 4.90 16.58 Perkins M92, 2001 Fritidsmotorsegelskepp SMUR KATSUMOTO 5.10 16.58 Ford 2715E, 1975 Fritidsmotorsegelskepp SEVO CARAMELLE 4.64 16.58 Volvo Penta TAMD 41‐H, 2000 Fritidsmotorsegelskepp SHQC PANDORA AF GÖTEBORG 4.64 16.58 Volvo Penta TAMD 41, 2000 Fritidsmotorsegelskepp SDEL LASSE‐MAJA 4.62 16.58 Volvo Penta TAMD 41, 2004 Fritidsmotorsegelskepp SHML BAMSEN II 4.62 16.58 Volvo Penta TAMD 41HD Fritidsmotorsegelskepp SBAO MALINDA IV 4.05 16.55 Mercedes OM617, 1983 Fritidsmotorsegelskepp SCNJ FRIÖ 4.72 16.54 Scania D8 1972 Fritidsmotorsegelskepp SLQO GINSKÄR 5.20 16.51 IVECO 8061 M14, 1995 Fritidsmotorsegelskepp SGYA CATALINA III 4.75 16.48 Volvo, 2008 Fritidsmotorsegelskepp SHNQ VITAMIN 4.36 16.48 Volvo Penta 2003 Turbo 88 Fritidsmotorsegelskepp SDZH STARCROSS AF LINKÖPING 4.89 16.35 Yanmar 4JH4‐HTE, 2008 Fritidsmotorsegelskepp SLNH ANNE AF GÖTEBORG 4.89 16.35 Fritidsmotorsegelskepp SJGP ELVIRA 5.24 16.34 Albin Diesel H3 Fritidsmotorsegelskepp SMEX IRON MAIDEN 5.08 16.30 Mercedes Benz OM 352,1975 Fritidsmotorsegelskepp SFVJ AURORA 5.22 16.26 Skandia 1939 Fritidsmotorsegelskepp SGJM SALSA 4.89 16.19 Volvo TMD 31 B, 1991 Fritidsmotorsegelskepp SKPU BIG MOUSE 4.38 16.13 Ford Leyman, 1989 Fritidsmotorsegelskepp SMEY SHELA 4.88 16.11 Yanmar, 2006 Fritidsmotorsegelskepp SHMJ AMAT BERANI II 4.40 16.10 Detroit Diesel Fritidsmotorsegelskepp SLKM SINDBAD 4.02 16.09 Bukh, 1953 Fritidsmotorsegelskepp SBVZ THETIS 4.30 16.08 Perkins 4.236 Fritidsmotorsegelskepp SKWC AMFITRITE 4.56 16.08 GM Bedford 466M 1975 Fritidsmotorsegelskepp SFBY SELMA 4.35 16.07 Volvo Penta TMD31A 1992 Fritidsmotorsegelskepp SEJK VINDARNAS NOMAD 4.87 16.05 Volvo D50 Fritidsmotorsegelskepp 141

SMLJ JOYRIDE 4.87 16.05 Volvo Penta TD50A Fritidsmotorsegelskepp SMBK WILD LADY 4.35 16.00 Volvo Penta TMD 31, 1991 Fritidsmotorsegelskepp SKTL AMELIA 4.60 15.97 Perkins Diesel Fritidsmotorsegelskepp SBEN LORNA 4.60 15.97 Volvo Penta TAMD 22P,‐03 Fritidsmotorsegelskepp SBVF LADY ANNILA 4.60 15.97 VolvoPenta TMD22B, 1998 Fritidsmotorsegelskepp SDYX TINTO III 4.60 15.97 Yanmar 4JH3 HTE, 2004 Fritidsmotorsegelskepp SDON CHANTALLE 4.70 15.91 Yanmar 4JH3‐HTE, 2004 Fritidsmotorsegelskepp SDTB SANNSIPAPP 4.70 15.91 Yanmar 4LHM‐HTP Fritidsmotorsegelskepp SKDW GUNSAN 4.88 15.89 Yanmar 4JH4HTE, 2008 Fritidsmotorsegelskepp SIQG IKARUS 4.66 15.85 Volvo Penta TMD 22B, 1997 Fritidsmotorsegelskepp SKRC EXCALIBUR 4.30 15.85 Ford 1982 Fritidsmotorsegelskepp SJCW REBULA 4.47 15.84 Ford 4‐cyl, 1996 Fritidsmotorsegelskepp SIKU PAN 4.60 15.84 Volvo Penta TAMD 70, 1971 Fritidsmotorsegelskepp SDAM IRON LADY 4.71 15.82 Iveco, 1997 Fritidsmotorsegelskepp SBTW ISA 4.62 15.82 Scania D11, 1979 Fritidsmotorsegelskepp SIGQ NORYEMA 4.23 15.80 FIAT, AIFO 85 Cv, 1987 Fritidsmotorsegelskepp SCMR ARIANE AF STOCKHOLM 4.74 15.80 Perkins 4.236 Fritidsmotorsegelskepp SKDG ODELFINA 4.30 15.80 Volvo MD 22 1997 Fritidsmotorsegelskepp SKYR SARITA 4.36 15.80 Fritidsmotorsegelskepp SDMI NANDI 4.01 15.79 Volvo Penta TMD47 Fritidsmotorsegelskepp SDAI LAYA 4.53 15.78 Volvo Penta TAMD 31 1987 Fritidsmotorsegelskepp SCGT OM II AF GÖTEBORG 4.56 15.75 YANMAR 4 JH2DTE, 1993 Fritidsmotorsegelskepp SKMV WASAHOF 4.70 15.73 Albin G‐62 1962 Fritidsmotorsegelskepp SEVX WETSERA 5.55 15.72 Scania Vabis diesel 1968 Fritidsmotorsegelskepp SBYD BETTINA 4.63 15.71 Volvo TMD 100A, 1977 Fritidsmotorsegelskepp SKUX GALEJAN AF BASTMORA 5.05 15.69 Perkins T6 354, 1971 Fritidsmotorsegelskepp SFCN NORDIC SAGA 4.45 15.67 Ford Lehman, 1976 Fritidsmotorsegelskepp SBFU LADY SWAN 4.52 15.65 Perkins 4.236M 1982 Fritidsmotorsegelskepp SKFB MAGIC 4.52 15.65 Perkins 4.236M 1981 Fritidsmotorsegelskepp 142

SMUT CHRISTINA AF VRESTABY 4.48 15.65 Scania DS9 5061687, 1985 Fritidsmotorsegelskepp SEZP CéLESTE 4.52 15.65 Yanmar 4JH2‐DTH, 1993 Fritidsmotorsegelskepp SDER TRUE LOVE V 4.42 15.63 Volvo Penta TAM 41 1992 Fritidsmotorsegelskepp SDGA FUNNY 4.42 15.63 Volvo Penta TAMD41 1990 Fritidsmotorsegelskepp SKWP MICAROLA III 4.60 15.60 Ford 1982 Fritidsmotorsegelskepp SCTF COVER GIRL IV 4.50 15.56 Yanmar 4JH3‐HTE, 2004 Fritidsmotorsegelskepp SBFE LOUISE II 4.50 15.56 Volvo Penta D3, 2006 Fritidsmotorsegelskepp SCWD MALEHA NUI 4.30 15.50 Ford Lehmann 2712E,1981 Fritidsmotorsegelskepp SMKC BISAYA 4.60 15.40 Volvo Penta MD100 1967 Fritidsmotorsegelskepp SKCA HÄGRING 4.85 15.39 Scania DS 11 1979 Fritidsmotorsegelskepp SKCF STUGA 4.85 15.39 Scania DS11 1979 Fritidsmotorsegelskepp SFHG NJORDEN 5.27 15.38 Volvo Penta D 96 Fritidsmotorsegelskepp SBLD WINDA II 4.60 15.35 Yanmar 4LH‐DTE,1998 Fritidsmotorsegelskepp SDNI NIEVE 4.60 15.35 Yanmar Fritidsmotorsegelskepp SKCV ZONDA 4.75 15.34 Ford marindiesel 6 cyl Fritidsmotorsegelskepp SCNQ MARY‐ANN 4.93 15.33 Volvo D47B 1955 Fritidsmotorsegelskepp SHQT THE BELLE CATTE 4.20 15.32 Perkins Diesel 1988 Fritidsmotorsegelskepp SMEK SARA BELLE 4.57 15.32 Perkins 4236 Diesel 1987 Fritidsmotorsegelskepp SFZN ELSA AV STOCKHOLM 5.91 15.32 Albin Diesel G‐62T 1961 Fritidsmotorsegelskepp SLNU LADY H 4.30 15.30 Yanmar 72, 1995 Fritidsmotorsegelskepp SKBV FINNESEJ 4.14 15.28 Fritidsmotorsegelskepp SLJR ATLANTIS 4.02 15.27 Yanmar 4JH‐HTE, 1988 Fritidsmotorsegelskepp SEJI TELMA 4.70 15.26 Perkins LD14, 1989 Fritidsmotorsegelskepp SCQH XIT 4.75 15.26 Perkins 4236, 1989 Fritidsmotorsegelskepp SDGY WAVE 4.75 15.26 Perkins 4236, 1990 Fritidsmotorsegelskepp SCFN NANUK 4.41 15.26 Fritidsmotorsegelskepp SCMT FAIRY 4.70 15.26 PERKIIN 4236, 1991 Fritidsmotorsegelskepp SBHJ WOOLLOOMOOLOO 4.75 15.26 Perkins 4236 Fritidsmotorsegelskepp SBOD BABAR 4.74 15.26 Perkins 4236 1989 Fritidsmotorsegelskepp 143

SBWD MISS RUSTIS 4.75 15.26 Perkins 4236 1990 Fritidsmotorsegelskepp SFZC GERTRUD 4.09 15.25 Volvo Penta TAMD 31 1996 Fritidsmotorsegelskepp SBAL CARICIA 4.48 15.25 Yanmar 4JH3‐HTE, 2007 Fritidsmotorsegelskepp SGUI TABASCO AF STOCKHOLM 4.48 15.25 Yanmar 4JH3‐HTE, 1999 Fritidsmotorsegelskepp SGHV ANASTASIA AV GÖTEBORG 4.57 15.25 Yanmar Diesel Fritidsmotorsegelskepp SBRW IRONOS 5.00 15.25 Fritidsmotorsegelskepp SGWH KIA ORA 4.20 15.25 Nanni Diesel 5.250TDI,‐06 Fritidsmotorsegelskepp SKLB IMPULS 4.48 15.25 Yanmar 4JH3‐HTBE, 1999 Fritidsmotorsegelskepp SDJI SPIRIT 4.34 15.24 Volvo MD55, 2003 Fritidsmotorsegelskepp SENJ SHADDOCK 4.62 15.24 Fritidsmotorsegelskepp SDMU FREE WIND 4.30 15.24 Volvo Penta D2‐75, 2008 Fritidsmotorsegelskepp SMQW JENNIFER 4.75 15.24 Perkins Fritidsmotorsegelskepp SCWG TORD 4.68 15.23 Volvo TAMD 31 1992 Fritidsmotorsegelskepp SCWI BILLY A 4.68 15.23 Volvo TAMD 31 1992 Fritidsmotorsegelskepp SMZP SEA OTTER 4.41 15.22 Yanmar 4JH3‐HTE, 2004 Fritidsmotorsegelskepp SFYN BAROQUE 4.11 15.22 Lister HR3, 1969 Fritidsmotorsegelskepp SFUO ANNE 4.66 15.20 Volvo TMD 100 AK 1976 Fritidsmotorsegelskepp SHIJ BLUE ODYSSEY 4.45 15.16 Volvo TMD22, 1998 Fritidsmotorsegelskepp SBDN MARTINA AF GÖTEBORG 4.20 15.15 Thorny Craft 6 Diesel Fritidsmotorsegelskepp SKTB CAROLINA BLUE 4.49 15.10 Volvo Penta TMD 40 Fritidsmotorsegelskepp SLYM BALTIC QUEEN II 4.49 15.10 Volvo Penta TMD 40 1986 Fritidsmotorsegelskepp SBWU TINA PRINCESS 4.49 15.10 Volvo Penta TAMD41B, 1996 Fritidsmotorsegelskepp SLAE AMFITRITE 4.49 15.10 Volvo Penta MD40D 1983 Fritidsmotorsegelskepp SIEX AMAZING RACE 4.34 15.10 Volvo Penta TMD 31 B,1992 Fritidsmotorsegelskepp SBNI NATIBOU 7.90 15.10 2 Vetus M417, 2006 Fritidsmotorsegelskepp SGJF IRIS‐DIANA 4.60 15.10 Perkins M90, 1997 Fritidsmotorsegelskepp SLIV SYBILLAE 4.85 15.09 Yanmar 4JH3‐HTE, 2001 Fritidsmotorsegelskepp SMGR XAVANTE 4.85 15.09 Yanmar 4JH‐2DTE, 1990 Fritidsmotorsegelskepp SJHZ ANASTATICA 4.60 15.07 Ford RPM‐HD 1974 Fritidsmotorsegelskepp 144

SKLX RAVEN X 4.90 15.04 Perkins T 6.354 M, 1988 Fritidsmotorsegelskepp SBJA LAS BRISAS 4.50 15.03 Volvo Penta D3‐110, 2004 Fritidsmotorsegelskepp SGPO CASTELLANUS II 4.50 15.03 Volvo Penta D3‐110, 2005 Fritidsmotorsegelskepp SCVG RASSKER VI 4.50 15.03 Volvo‐Penta D3‐110,2004 Fritidsmotorsegelskepp SMAQ CASCADE AF VÄRMDÖ 4.50 15.03 Volvo Penta D3‐110, 2006 Fritidsmotorsegelskepp SFYB ATHLON 4.05 15.02 Volvo MD 32, 2001 Fritidsmotorsegelskepp SDQL ARCADIA 4.52 15.00 Yamnar Marindiesel, 1999 Fritidsmotorsegelskepp SFJA DINA II 4.52 15.00 Yanmar 4JH3GE‐HTBE3.3,‐05 Fritidsmotorsegelskepp SGBW IL BACIO 4.58 14.99 Volvo Penta TMD 22, 2001 Fritidsmotorsegelskepp SGRC NICE V AF GÖTEBORG 4.58 14.99 Volvo Penta D2.75, 2007 Fritidsmotorsegelskepp SMDB BEDA AF GÖTHEBORG 4.58 14.99 Volvo Penta D2‐75, 2007 Fritidsmotorsegelskepp SMFR SESSAN AV SALTSJÖBADEN 4.58 14.99 Fritidsmotorsegelskepp SMDE ADA AF GÖTHEBORG 4.58 14.99 Volvo Penta D2‐75, 2007 Fritidsmotorsegelskepp SMOW HELENA AF NACKA 4.58 14.99 Volvo, 1999 Fritidsmotorsegelskepp SDKU AKU‐AKU 4.58 14.99 Volvo Penta TMD 22B, 1999 Fritidsmotorsegelskepp SEZN BRAVARAI 4.58 14.99 Volvo Penta D2‐75, 2008 Fritidsmotorsegelskepp SHZF SPIRIT OF PIRAEUS 4.58 14.99 Volvo Penta MD 22, 2001 Fritidsmotorsegelskepp SMQX ATLIAJAT II 4.58 14.99 Volvo D2‐75, 2006 Fritidsmotorsegelskepp SEKI KLEFVA 4.58 14.99 Volvo TAMD 22, 2001 Fritidsmotorsegelskepp SMAL MIREILLE 4.48 14.98 Volvo Penta TMD 22, 1999 Fritidsmotorsegelskepp SBGF BLUES 4.48 14.98 Yanmar 4JH2DTE, 1998 Fritidsmotorsegelskepp SBXO GICA 4.48 14.98 Volvo TMD 22 Fritidsmotorsegelskepp SHCE STELLA AF GÖTEBORG 4.49 14.98 Perkins M65, 2003 Fritidsmotorsegelskepp SKOP INKA 4.73 14.97 Fritidsmotorsegelskepp SDGQ QUO VADIS 4.62 14.97 Ford Tempest Sea Lord ‐75 Fritidsmotorsegelskepp SLQX CHARLAINE 4.24 14.94 Ford 2701 E 1969 Fritidsmotorsegelskepp SEWT MINDFULNESS 5.00 14.93 Ford 2725 T Fritidsmotorsegelskepp SBOR PETRUS 4.50 14.92 Ford 1964 Fritidsmotorsegelskepp SMFW STOCKHOLMS GALATEA 4.32 14.90 Volvo MD 22A, 2000 Fritidsmotorsegelskepp 145

SKFJ CHAMPIONS 4.25 14.89 Perkins 6354, 1985 Fritidsmotorsegelskepp SHLE VEJDE 4.53 14.89 Volvo D2‐75, 2003 Fritidsmotorsegelskepp SGOZ ANASTASIA AV STOCKHOLM 4.25 14.89 Perkins Diesel, 1985 Fritidsmotorsegelskepp SFTY MONSUN AF EKERÖ 4.98 14.89 Ford 6 cyl diesel, 1974 Fritidsmotorsegelskepp SHYR ENJOY II 4.08 14.85 Nanni 6.280 HE, 1996 Fritidsmotorsegelskepp SMAZ AMORESS 2 AF KULLAVIK 4.32 14.83 Volvo Penta MD 22, 1995 Fritidsmotorsegelskepp SJKG CATALINA II 4.32 14.83 Volvo MD 22 1997 Fritidsmotorsegelskepp SGMR KATY C 4.57 14.81 Perkins Range 4 M 135,‐88 Fritidsmotorsegelskepp SBKP OLGA‐ELIDA 4.95 14.80 Vetus D64, 2002 Fritidsmotorsegelskepp SFJY WONDERWORLD 4.35 14.78 Volvo TMD 31, 1996 Fritidsmotorsegelskepp SGMC BORN FREE AF GÖTEBORG 4.40 14.78 Volvo Penta D3, 2006 Fritidsmotorsegelskepp SCHM MAYFLOWER II 4.40 14.78 Fritidsmotorsegelskepp SJKM SANNA V AF STRÄNGNÄS 4.40 14.78 Volvo Penta TMD 31 L 1998 Fritidsmotorsegelskepp SKZV MATHILDA IV 4.40 14.78 Volvo Penta TMD 31L 1998 Fritidsmotorsegelskepp SDQG OLYDIA II 4.40 14.78 Yanmar 4 LH‐TE, 1999 Fritidsmotorsegelskepp SBEZ DUNETT 4.40 14.78 Yanmar 4LHTE, 2000 Fritidsmotorsegelskepp SFPK NADINE 4.40 14.78 Volvo Penta TMD31L‐A1996 Fritidsmotorsegelskepp SBAM IMAGINE 4.11 14.78 Ford‐Lehman 1984 Fritidsmotorsegelskepp SMWR BARCARES 4.33 14.75 Yanmar 4 JH 2‐HTE, 2000 Fritidsmotorsegelskepp SLBO BALTAZAR 4.40 14.75 Perkins, 1983 Fritidsmotorsegelskepp SJKT ROXANNE AF STOCKHOLM 4.33 14.75 Yanmar 4 JH2‐HTE 1997 Fritidsmotorsegelskepp SJBK UTOPIA 4.14 14.75 Nanni 6.280 HE, 1995 Fritidsmotorsegelskepp SLMX GRACE AF TROSA 4.33 14.75 Yanmar 4JH2, 1997 Fritidsmotorsegelskepp SBFZ CHILL OUT 4.49 14.75 Yanmar Fritidsmotorsegelskepp SDYR L'HEURE BLEUE 4.33 14.75 Yanmar 4 SH3‐TE, 2001 Fritidsmotorsegelskepp SBNQ VICTORIA AF PITEÅ 4.49 14.75 Yanmar 4JH3HTE, 2006 Fritidsmotorsegelskepp SKJQ BLUE DAME 4.54 14.73 Yanmar 4JA4‐HTE, 2007 Fritidsmotorsegelskepp SDZQ DELIGHT 4.05 14.67 Yanmar 4JH‐3TE, 2000 Fritidsmotorsegelskepp SHKX LA DEÉSSE 4.51 14.66 Yanmar 4JH3TE, 2006 Fritidsmotorsegelskepp 146

SLXG CARLA AF STOCKHOLM 4.51 14.66 Yanmar 4JH3TE Fritidsmotorsegelskepp SJGR CORNELIA‐SVERIGE 4.48 14.64 Volvo Penta TMD 31B 1993 Fritidsmotorsegelskepp SCQN SOLA LONE 4.96 14.64 Hundersted 1962 Fritidsmotorsegelskepp SMXH MARIA HELENA 4.39 14.63 Volvo Penta TMD40 1980 Fritidsmotorsegelskepp SMBJ FAROUCHE II 4.19 14.62 Volvo Penta MD21A Fritidsmotorsegelskepp SKUR BEATRICE AF GRAVARNE 4.19 14.60 Volvo Penta TMD 22, 1998 Fritidsmotorsegelskepp SKYE CHESNOCK 4.23 14.60 Yanmar 4JH2DTB, 1998 Fritidsmotorsegelskepp SBPE AQUARISMA 4.40 14.55 Perkins 4154 1986 Fritidsmotorsegelskepp SJIA METTE 4.43 14.55 Bolinder V7 1936 Fritidsmotorsegelskepp SIWY EMBLA 4.56 14.54 Volvo Penta TMD 22, 2002 Fritidsmotorsegelskepp SIQE AMANDA OF SWEDEN 4.06 14.54 Volvo Penta TMD31B 1980 Fritidsmotorsegelskepp SDVB TOLLY 5.94 14.52 Skandia 2‐cyl råoljem.‐59 Fritidsmotorsegelskepp SDMZ SEVENTH WAVE 4.49 14.50 Yanmar 4J HBTE Fritidsmotorsegelskepp SJHG KIRRIBILLI 4.49 14.50 Volvo TMD 22, 2000 Fritidsmotorsegelskepp SMHZ BLÅ MÄRTA 4.49 14.50 Yanmar 43H3TE, 2000 Fritidsmotorsegelskepp SIGR MARELD 4.49 14.49 Volvo Penta MD 22 Fritidsmotorsegelskepp SDIJ YDALIR II 4.12 14.45 Nanni Diesel XO401‐214,01 Fritidsmotorsegelskepp SMWN REBECKA‐CHRISTINE 4.12 14.45 Yanmar 4JH3 HTBE, 1999 Fritidsmotorsegelskepp SLAX HELGA AF ÄLLMORA 4.12 14.45 Yanmar 4JH3‐HTBE, 2000 Fritidsmotorsegelskepp SBYL ZEPHYR JÄRNLADYN 4.30 14.45 Perkins 4108 1987 Fritidsmotorsegelskepp SKVJ EDEN 5.57 14.43 Volvo Penta TMD 96B 1950 Fritidsmotorsegelskepp SJWG ANTILIA 4.47 14.43 Perkins M60, 1995 Fritidsmotorsegelskepp SCUE MISS AV BREVIKSNÄS 4.20 14.43 Volvo Penta D2‐75,2004 Fritidsmotorsegelskepp SFLR ALBI 4.20 14.43 Volvo Penta D2‐55,2003 Fritidsmotorsegelskepp SGMJ L' AVALANCHE 4.20 14.43 Volvo TMD 22, 2001 Fritidsmotorsegelskepp SHGK MERMAID 4.31 14.40 Yanmar 4JH4‐HTE, 2005 Fritidsmotorsegelskepp SCHX MIDNIGHT SUN 4.31 14.40 Yanmar, 4JH3HTE, 2006 Fritidsmotorsegelskepp SFUL NJORD 4.31 14.40 Yanmar 4JH3 HTE, 2003 Fritidsmotorsegelskepp SGOP SEDNA AV NOTHOLMEN 4.31 14.40 Yanmar 4JH3 HTE,2003 Fritidsmotorsegelskepp 147

SBTM TUMBLING DICE 4.31 14.40 Volvo TAMD 22, 2003 Fritidsmotorsegelskepp SFNT QUEENIE II 4.23 14.40 VP TMD 22P, 2001 Fritidsmotorsegelskepp SKFY BETZY GRABLE 4.31 14.40 Volvo MD 22, 2002 Fritidsmotorsegelskepp SGMU SVEA TIGER 4.31 14.40 Volvo Penta MD 22 Fritidsmotorsegelskepp SGIL NEW MOON 4.23 14.40 Volvo Penta TMD 22, 2001 Fritidsmotorsegelskepp ELISABETH AV SDMQ SALTSJÖBADEN 4.23 14.40 Volvo Penta TMD22, 2001 Fritidsmotorsegelskepp SBKX WEST MONSUN 4.37 14.40 Volvo Penta D67C 1972 Fritidsmotorsegelskepp SHFU LAXEN 5.56 14.37 Scania‐Vabis diesel 1960 Fritidsmotorsegelskepp SMXQ TICKET III 4.62 14.37 Yanmar 4JH3HTE, 2005 Fritidsmotorsegelskepp SMKG BLÅKLINT 4.41 14.36 Perkins 4 154M, 1985 Fritidsmotorsegelskepp SLRJ JOSEPHINE AF GÅSHAGA 4.41 14.36 Perkins Fritidsmotorsegelskepp SELO SEABIRD 4.08 14.35 Arona Fritidsmotorsegelskepp SHCV FELICIA 4.49 14.35 Volvo Perkins TMD22, 2000 Fritidsmotorsegelskepp SKIE BARA‐VARA 4.49 14.35 Volvo D2‐55,2002 Fritidsmotorsegelskepp SDQJ FORTUNE LIGHT 4.49 14.35 Yanmar 4JH2, 1994 Fritidsmotorsegelskepp SMAF DOLOROSA 4.49 14.35 Volvo MD22, 2001 Fritidsmotorsegelskepp SMTU OSIBOVA 4.49 14.35 Volvo TAMD 22, 2001 Fritidsmotorsegelskepp SBJZ SOFIA AF SALTSJÖBADEN 4.48 14.31 YANMAR JH3‐TE, 2003 Fritidsmotorsegelskepp SMAC NOA AF STOCKHOLM 4.25 14.28 Volvo TD, 1989 Fritidsmotorsegelskepp SIHE BALTIC ROSE 4.12 14.26 Nanni 6280HE, 1995 Fritidsmotorsegelskepp SLPX SINGOALLA AF VINÖ 4.44 14.25 Perkins Typ 234 1984 Fritidsmotorsegelskepp SBIM JADE 4.62 14.25 Ford 2712 E Fritidsmotorsegelskepp SITK CARIB 4.04 14.25 Yanmar 4JH2‐DTBE, 1998 Fritidsmotorsegelskepp SKLN TINTO II 4.04 14.25 Yanmar 4JH2‐DTBE, 1998 Fritidsmotorsegelskepp SBYR ADELA 4.35 14.24 Volvo Penta TMD 31A 1989 Fritidsmotorsegelskepp SBXA ELBIA 4.35 14.24 Volvo Penta TMD31 1990 Fritidsmotorsegelskepp SCJR LADY ANN 4.35 14.24 Volvo Penta Fritidsmotorsegelskepp SKHG LINDA AF STOCKHOLM 4.25 14.22 Ford 2712E 1979 Fritidsmotorsegelskepp 148

SGMH ILE DE BORA BORA 4.51 14.21 Ford 2714 E Fritidsmotorsegelskepp SGAW NORDLAND AF GÖTEBORG 4.67 14.20 British Leiland, 1973 Fritidsmotorsegelskepp SLVW AQUAVIT 4.20 14.20 Volvo D2‐75, 2005 Fritidsmotorsegelskepp SLUR BLÅDÅREN 4.20 14.20 Volvo D2‐75, 2005 Fritidsmotorsegelskepp SMBO DAYNA 4.25 14.20 Perkins M60, 1993 Fritidsmotorsegelskepp SIHU SMILLA 4.22 14.20 Yanmar 4JH2‐DTE Fritidsmotorsegelskepp SHUE REFANETTE 4.18 14.20 Volvo Penta D2‐75, 2006 Fritidsmotorsegelskepp SKMC FLYKT 4.25 14.20 Ford 4:254 1975 Fritidsmotorsegelskepp SGUJ OLOMIA 4.20 14.20 Ford diesel Fritidsmotorsegelskepp SGUX CEMONIA 4.20 14.20 Volvo Penta MD 47 Fritidsmotorsegelskepp SLCD FIRST AMBER 4.34 14.20 Perkins 4.108 1984 Fritidsmotorsegelskepp SMBF ESMERALDA OF SWEDEN 4.17 14.20 Volvo TD 50 1972 Fritidsmotorsegelskepp CHAMPAGNE AF SDTI STOCKHOLM 4.46 14.19 Yanmar 4JH4, 2007 Fritidsmotorsegelskepp SLNC SAGA AF GÖTEBORG 4.26 14.18 Nanni 5.250 TDI, 2002 Fritidsmotorsegelskepp SMWO ELLEN WESTERBERG 4.26 14.18 Yanmar 4JH3‐HTE, 2005 Fritidsmotorsegelskepp SGNT CILLE 4.26 14.18 Yanmar 4JH3‐HTE,E20940,01 Fritidsmotorsegelskepp SFWB TORDMULEN 5.55 14.17 Volvo Penta MD 47A‐9328 Fritidsmotorsegelskepp SIHQ SVENSSONS 4.35 14.15 Volvo Penta MD 22, 2001 Fritidsmotorsegelskepp SBIP VIVE LA MER 4.20 14.15 Yanmar 4JH4C, 2008 Fritidsmotorsegelskepp SHID L'INDIENNE 4.35 14.15 Volvo Penta TMD 22, 2001 Fritidsmotorsegelskepp SFQT SALT AV ÖSTERSKÄR 4.20 14.15 Yanmar 4JH4AE, 2008 Fritidsmotorsegelskepp SBMH GRACE II 4.20 14.15 VolvoPenta MDD2‐55,2006 Fritidsmotorsegelskepp SMVE MILLA 4.20 14.15 Volvo D2 55, 2006 Fritidsmotorsegelskepp SKNQ ALOHA 4.35 14.15 Volvo Penta TMD 22, 2003 Fritidsmotorsegelskepp SBWE SCIROCCO 4.04 14.12 Yanmar 4JH3, 2006 Fritidsmotorsegelskepp SFVB VILLOU 4.04 14.12 Yanmar 4JH3 TBE, 2001 Fritidsmotorsegelskepp SMCO MISS U II 4.08 14.12 Leyland SW400 M, 1987 Fritidsmotorsegelskepp SBHW CHERIMIE 4.12 14.10 Yanmar4JH3‐HTE,E21404,‐03 Fritidsmotorsegelskepp 149

SHYX TIMA AV LIDKÖPING 4.26 14.09 Volvo Penta MD50, 1978 Fritidsmotorsegelskepp SMQH ANDROMEDA OF SWEDEN 4.02 14.08 Volvo Penta MD21A 1975 Fritidsmotorsegelskepp SFGE AMORE DI MARE II 4.22 14.06 Ford Lehman, 1990 Fritidsmotorsegelskepp SLTJ KENAVO 4.49 14.05 Yanmar, 2001 Fritidsmotorsegelskepp SGDF WINDWARD STAR 4.57 14.02 Perkins 4‐154, 1977 Fritidsmotorsegelskepp SGBF ARIANNA AF SIMRISHAMN 4.42 14.01 Yanmar 4JH2, 1992 Fritidsmotorsegelskepp SMAN AMITA 4.15 14.00 Volvo D2‐75, 2006 Fritidsmotorsegelskepp SEFW RIKITIN 4.15 14.00 Volvo Penta D2‐55, 2005 Fritidsmotorsegelskepp SLUH PRIMA 4.15 14.00 Volvo Penta D2‐55, 2005 Fritidsmotorsegelskepp SLGT CORINNE AF VÄSTERÅS 4.82 13.99 2 Yanmar 4JH4E, 2004 Fritidsmotorsegelskepp SBNF MISS FORTYSIX 4.35 13.99 Volvo D2 55,2005 Fritidsmotorsegelskepp SMBG PAM 4.35 13.99 Volvo Penta D2 55C, 2004 Fritidsmotorsegelskepp SHLA LOUVIC 4.35 13.99 Volvo Penta D2‐55, 2005 Fritidsmotorsegelskepp SMNZ GALATEA AF STOCKHOLM 4.35 13.99 Volvo D2‐55, 2007 Fritidsmotorsegelskepp SIHP LIV 1 4.05 13.97 Fritidsmotorsegelskepp SDXT NIKITA OF KYRKBACKEN 4.48 13.96 Yanmar nr 36646 Fritidsmotorsegelskepp SMGB LIXA 4.48 13.96 Yanmar T.D. 4JH2‐UTE,1995 Fritidsmotorsegelskepp SKEW GIM‐KI 4.12 13.95 Yanmar JH4‐UTBE 1998 Fritidsmotorsegelskepp SJZA MISS BOOP 4.35 13.94 Volvo Penta D2‐75, 2006 Fritidsmotorsegelskepp SFRX AGGERUD 4.10 13.93 Ford 2715 E Fritidsmotorsegelskepp SJTV ENVISHETEN 4.81 13.92 Volvo D‐96 1963 Fritidsmotorsegelskepp SBGH SOLITUDE OF SWEDEN 4.37 13.91 Yanmar 4JHTE, 1989 Fritidsmotorsegelskepp SJLH NIGHTWISH 4.25 13.90 Yanmar 4JH2A‐HTE, 1990 Fritidsmotorsegelskepp SIWV MAJOSA II 4.30 13.90 Perkins 4.108, 1984 Fritidsmotorsegelskepp SBLN NORRSKEN AV GÖTEBORG 4.25 13.90 Perkins Prima Fritidsmotorsegelskepp SJIZ KARIBU 4.17 13.90 Perkins M6‐354 1979 Fritidsmotorsegelskepp SMAV IRIS 4.32 13.90 Perkins 4.108 1985 Fritidsmotorsegelskepp SGZM CRUX 4.34 13.88 Perkins 4.108, 1984 Fritidsmotorsegelskepp SECQ ALFHILD 5.73 13.88 Valmet Turbo Fritidsmotorsegelskepp 150

SLKW SVANEFLU 4.50 13.83 Volvo Penta TMD 96 1969 Fritidsmotorsegelskepp SMXV CHRISTOPHER COLUMBUS V 4.46 13.83 Ford 4/2720, 1985 Fritidsmotorsegelskepp SEYL STORMVOGEL 4.46 13.83 Volvo TMD 40A, 1997 Fritidsmotorsegelskepp SFAU INDIGO 4.25 13.81 Yanmar JH2‐DTE 1998 Fritidsmotorsegelskepp SIHK STING 4.25 13.81 Volvo Penta TAMD 22, 1997 Fritidsmotorsegelskepp SKPM RONJA OF SWEDEN 4.25 13.81 Volvo Penta TMD 22, 1999 Fritidsmotorsegelskepp SDML EMMA AF STOCKHOLM 4.25 13.81 Yanmar 4JH2TE, 1995 Fritidsmotorsegelskepp SGWX ANNABEL LEE 4.57 13.80 Ford Lehman 2715E, 1981 Fritidsmotorsegelskepp SKEQ NO WORRIES 4.30 13.78 Perkins 4236, 1990 Fritidsmotorsegelskepp SCFJ ANTARES AV GÖTEBORG 4.02 13.75 Volvo Penta TAMD30 1987 Fritidsmotorsegelskepp SGIN SAUVAGE 4.18 13.74 Volvo Penta MD22, 1994 Fritidsmotorsegelskepp SKMO SUN CHASER 4.20 13.74 Perkins Fritidsmotorsegelskepp SLXN STUNDOM 4.04 13.72 Perkins 4236, 1998 Fritidsmotorsegelskepp LA CONDESA AV SIMC SKÄLDERVIKEN 4.36 13.72 Volvo Penta MD 32 Fritidsmotorsegelskepp SCMQ MBOLO 4.18 13.70 Yanmar Fritidsmotorsegelskepp SLTP PATIENCE 4.30 13.70 Yanmar, 2006 Fritidsmotorsegelskepp SBXU LA SKVALL 4.28 13.68 Volvo Penta MD 22, 1997 Fritidsmotorsegelskepp SLXF NYMPH ERRANT 4.05 13.68 Ford 1971 Fritidsmotorsegelskepp SBFV FREDRIKA AV ORUST 4.10 13.67 Volvo Penta D2‐75, 2003 Fritidsmotorsegelskepp SIAH GLITTRA 4.05 13.67 Volvo Penta TMD22C, 2001 Fritidsmotorsegelskepp SHWV CASTELLANUS 4.05 13.67 Volvo Penta TMD 22, ‐01 Fritidsmotorsegelskepp SJKH ELIN AF STOCKHOLM 4.05 13.67 Volvo Penta TMD22,2002 Fritidsmotorsegelskepp SJNX THERICA 4.05 13.67 Volvo Penta D2‐55,2002 Fritidsmotorsegelskepp SJNZ MERIBELLE 4.05 13.67 Volvo Penta MD55, 2002 Fritidsmotorsegelskepp SIAJ LA BAMBA 4.10 13.67 Volvo Penta D2‐75, 2005 Fritidsmotorsegelskepp SELX BEJOELLE 4.10 13.67 Volvo Penta D2‐55, 2005 Fritidsmotorsegelskepp SJMF SALLY 4.09 13.67 Volvo Penta D2‐55,2004 Fritidsmotorsegelskepp SCLB LOTOSLAND 4.05 13.67 Volvo Penta D2‐55, 2002 Fritidsmotorsegelskepp 151

SCWZ BELLA LUNA 4.05 13.67 Yanmar 43H3‐TE, 2002 Fritidsmotorsegelskepp SJMR ELISABETH III 4.25 13.66 Perkins Prima M50 1991 Fritidsmotorsegelskepp SHOY KLÖS 6.30 13.65 2 Yamaha utombordare, 2003 Fritidsmotorsegelskepp SBIZ VAGGSÅNG 4.05 13.65 Volvo Penta TAMD30 1986 Fritidsmotorsegelskepp SLWV CHANEL 4.19 13.64 Volvo AD 55, 2002 Fritidsmotorsegelskepp SBMU ROSE 4.45 13.64 Perkins 6.3544, 1980 Fritidsmotorsegelskepp SCPO LADY B 4.19 13.64 Volvo Penta D‐55, 2004 Fritidsmotorsegelskepp SJMN HÄXAN 4.16 13.62 Volvo Penta, 1996 Fritidsmotorsegelskepp SKCB MAJA AF GÖTEBORG 4.16 13.62 Yanmar 4JH2CE, 2001 Fritidsmotorsegelskepp SKRQ XELÄNS 4.16 13.62 Yanmar 4JH3E‐SD31 1999 Fritidsmotorsegelskepp SJIT XARA 4.16 13.62 Yanmar 4JH2E‐SD Fritidsmotorsegelskepp SBFN VIOLI AF GÖTEBORG 4.16 13.62 Yanmar 4JH3E, 2003 Fritidsmotorsegelskepp SGXY NORTHERN STAR 4.16 13.62 Yanmar 4JH2CE, 2000 Fritidsmotorsegelskepp SMGF CILLA II 7.70 13.61 Fritidsmotorsegelskepp SDOX ZIPPI 7.70 13.61 2 Volvo Penta D2‐55,2006 Fritidsmotorsegelskepp SMEV STORMVÅG 5.73 13.61 Ford 2713E 1974 Fritidsmotorsegelskepp SDZJ VINDHEIM 4.54 13.60 Hundersted A/S AA/L 2078 Fritidsmotorsegelskepp SCFU PEARL 4.17 13.60 Volvo D2‐55, 2002 Fritidsmotorsegelskepp SJUB PACIFIC WIND 4.25 13.60 Volvo D2‐55, 2002 Fritidsmotorsegelskepp SKQF BONNIE AF STOCKHOLM 4.10 13.56 Deutz MWM D 226‐6,1993 Fritidsmotorsegelskepp SBGA AMARONE 4.26 13.55 Volvo D2‐55, 2007 Fritidsmotorsegelskepp SMZD KRAKA 4.24 13.53 Volvo Penta MD22L, 2000 Fritidsmotorsegelskepp SBMN LONE 4.08 13.53 Volvo Penta MD40 1979 Fritidsmotorsegelskepp SJRC MARC O'POLO 4.24 13.52 Volvo Penta MD 17 1978 Fritidsmotorsegelskepp SKUC SWEJA 4.06 13.52 Peugeot 505, 1973 Fritidsmotorsegelskepp SLPJ MIMMI 4.02 13.50 Perkins 4108 1986 Fritidsmotorsegelskepp SJIX FAST FRIEND 4.25 13.48 Nannidiesel 6.280 HE 1995 Fritidsmotorsegelskepp SJEH AGNES LINNEA 4.03 13.46 Volvo Penta D2‐75, 2006 Fritidsmotorsegelskepp SGNA LEEWAY 4.03 13.46 Volvo Penta D2 75‐S, 2008 Fritidsmotorsegelskepp 152

SCJY MODESTY II 4.03 13.46 Volvo Penta D2 75‐S, 2007 Fritidsmotorsegelskepp SBVG MICHAELA AF UPSALA 4.21 13.43 Yanmar 1988 Fritidsmotorsegelskepp SLJC KLARA 5.48 13.42 Volvo MD 70 1984 Fritidsmotorsegelskepp SENX FILOSOFI II 4.26 13.41 Volvo Penta D2‐75, 2008 Fritidsmotorsegelskepp SDHT MISS FINE 4.26 13.41 Fritidsmotorsegelskepp SCIP JEANNE 4.37 13.41 Yanmar 4JH4‐TE75LV, 2008 Fritidsmotorsegelskepp SKFX AMORTINA AF STOCKHOLM 4.26 13.41 Fritidsmotorsegelskepp SKGJ STORA VIT AF SVINNINGE 4.26 13.41 Fritidsmotorsegelskepp SIJB GRAND LARGE 4.26 13.41 Volvo D2 75 150S, 2005 Fritidsmotorsegelskepp SBHK SEA PEARL 4.26 13.41 Volvo Penta D2,75,2006 Fritidsmotorsegelskepp SKXE SWALLOW 4.10 13.40 Perkins 4‐236 Fritidsmotorsegelskepp SGKL SANCH II 4.37 13.38 Yanmar 4JH3TE, 2006 Fritidsmotorsegelskepp SLFA CUTTY SARK 4.37 13.38 Yanmar 4JH3TE, 2005 Fritidsmotorsegelskepp SIGV SALT AF LANDSKRONA 4.37 13.38 Yanmar 4JH3TE, 2006 Fritidsmotorsegelskepp SIAX FILOSOFI 4.12 13.37 Iveco 4141 SRM 82, 2003 Fritidsmotorsegelskepp SEUL ALOHA AF VÄSTERVIK 4.08 13.37 Ford Fritidsmotorsegelskepp SMQO VIKING AF OXELÖSUND 4.15 13.35 Volvo Penta MD47 Fritidsmotorsegelskepp SBOG DOLPIN 5.76 13.33 Skandia 161 A 1935 Fritidsmotorsegelskepp SBXM MIRANDA 4.36 13.32 Foden F4 diesel, 1964 Fritidsmotorsegelskepp SKVW CANDOR 4.20 13.31 Perkins 4:236 1978 Fritidsmotorsegelskepp SCNW ISABELLE AF STOCKHOLM 4.12 13.30 Volvo D2‐55, 2004 Fritidsmotorsegelskepp SMCH DECLEOR 4.12 13.30 Volvo D‐2 55, 2001 Fritidsmotorsegelskepp SKRI ALDARION 4.12 13.30 Volvo Penta D2‐55, 2007 Fritidsmotorsegelskepp SDXM LOCURA IX 4.12 13.30 Volvo MD 22, 1995 Fritidsmotorsegelskepp SDTN DIVA 4.40 13.30 Perkins diesel Fritidsmotorsegelskepp SLEF SAYONARA 4.08 13.28 Ford 2712 1981 Fritidsmotorsegelskepp SKZP MADELEINE AF STOCKHOLM 4.26 13.28 Volvo Penta TMD 22 Fritidsmotorsegelskepp SHUJ TREASURE 4.43 13.25 Yanmar, diesel Fritidsmotorsegelskepp SBUL MALIN 4.00 13.25 Volvo Penta TMD31 1987 Fritidsmotorsegelskepp 153

SBIR HERO II AF VÄSTERVIK 4.11 13.24 Volvo Penta 2003TR 1986 Fritidsmotorsegelskepp SJKF LOTTA 2 4.22 13.24 Scania diesel 1970 Fritidsmotorsegelskepp SGJQ JOY 4.11 13.24 Volvo 2003T, 1986 Fritidsmotorsegelskepp SJPE TARSIA III 4.76 13.20 Chrysler‐Nissan CN 6‐33 Fritidsmotorsegelskepp SEKL VALKYRIA 4.97 13.20 Volvo‐Penta MD 67 1971 Fritidsmotorsegelskepp SGTW MOBITEX 4.21 13.19 Volvo Penta 2003T 1987 Fritidsmotorsegelskepp SCKY LISA AV LUGNET 4.07 13.19 Volvo MD50, 1984 Fritidsmotorsegelskepp SKDN IANTHI 4.25 13.16 Perkins Prima, 1992 Fritidsmotorsegelskepp SGFH ALVA SOFIA 4.25 13.16 Perkins M50 1992 Fritidsmotorsegelskepp SBTJ SHARDIK 4.08 13.14 Yanmar 4JHBE 1989 Fritidsmotorsegelskepp SBVM CHIC 4.08 13.14 Yanmar 4JHBE 1989 Fritidsmotorsegelskepp SBOU ANOMALI 4.08 13.14 Yanmar 1989 Fritidsmotorsegelskepp SKFL KRITSANA 4.20 13.13 Perkins Fritidsmotorsegelskepp SBZN EXIT ONE 4.26 13.11 Perkins Prima 1990 Fritidsmotorsegelskepp SCMK WINDJAMMER 4.26 13.11 Perkins 4,20 Fritidsmotorsegelskepp SEUH SWEET 4.26 13.11 Perkins Prima M50, 1989 Fritidsmotorsegelskepp SCFP THEA 4.19 13.11 Yanmar 3JH4CE, 2007 Fritidsmotorsegelskepp SILA APOLLO 4.09 13.10 Perkins Prima 50BHP,1988 Fritidsmotorsegelskepp SFXA JOUIR‐VITAMIN 4.06 13.10 Yanmar 4HJHTE NR21631,‐87 Fritidsmotorsegelskepp SLVJ L'ESKARGOT 4.51 13.07 Volvo Penta BM 1113‐B Fritidsmotorsegelskepp SBVY ALTAI 4.05 13.05 Yanmar 4JH‐HTE 1989 Fritidsmotorsegelskepp SMQC AINA ELFINA 4.83 13.02 Volvo D70 1968 Fritidsmotorsegelskepp SKTN PANGEA 4.12 13.02 Perkins 4.108 1985 Fritidsmotorsegelskepp SLOI ELINA AV GÖTEBORG 4.21 13.01 Volvo Penta D2‐75, 2005 Fritidsmotorsegelskepp SBIY AGDA AURORA 4.21 13.01 Volvo Penta D2‐76, 2004 Fritidsmotorsegelskepp SKZD ELEONORA AV DALARÖ 4.21 13.01 Volvo Penta D2‐75, 2005 Fritidsmotorsegelskepp SKZF ARGO NAVIS 4.21 13.01 Volvo Penta D2‐55, 2005 Fritidsmotorsegelskepp SMIE LADY D'OR 4.21 13.01 Volvo Penta D2‐75, 2006 Fritidsmotorsegelskepp SMIQ ISOLDE OF LIMHAMN 4.21 13.01 Volvo Penta D2‐75, 2006 Fritidsmotorsegelskepp 154

SBMK PIM PIM 4.21 13.01 Volvo D2‐75, 2006 Fritidsmotorsegelskepp SBMZ PANDORA 4.21 13.01 Volvo D2‐75, 2006 Fritidsmotorsegelskepp SGEN NOIR DUNDER 4.21 13.01 Volvo Penta D2‐55, 2007 Fritidsmotorsegelskepp SGNC TINJA 4.21 13.01 Volvo Penta D2‐75, 2007 Fritidsmotorsegelskepp SHLG IMPRESSION 434 4.21 13.01 Volvo Penta D2‐75 C, 2008 Fritidsmotorsegelskepp SFPC ELSA AF SKÄRHAMN 4.21 13.01 Volvo Penta D2‐75, 2008 Fritidsmotorsegelskepp SCAP FESTINA LENTE 4.21 13.01 Volvo Penta D2‐75 C, 2007 Fritidsmotorsegelskepp SMGD NEMO AF SMÖGEN 4.14 13.00 2 Volvo Penta D6‐435,2006 Fritidsmotorsegelskepp SHKF RAZZLE DAZZLE 4.00 13.00 Volvo 2003, 1985 Fritidsmotorsegelskepp SFLZ TIKAI 4.15 13.00 Perkins 4.108 Fritidsmotorsegelskepp SJZX SANTA‐MARIA 4.75 13.00 Volvo 1961 Fritidsmotorsegelskepp SCLW RAFIKI 4.03 12.99 Yanmar 4jh2dte Fritidsmotorsegelskepp SBUA QUEEN RANE 4.22 12.98 Ford Lehman 2722E 1990 Fritidsmotorsegelskepp SLMI SIGMA 4.22 12.98 Ford 2722 1985 Fritidsmotorsegelskepp SKVO TUSAN 4.22 12.98 Ford Lehman, 1986 Fritidsmotorsegelskepp SJUZ SANTANA II 4.22 12.98 Ford Lehman 2722 E, 1984 Fritidsmotorsegelskepp SLAQ FRENESI AF ÖREGRUND 4.22 12.98 Ford 2723, 1986 Fritidsmotorsegelskepp SMNX LAURA AF MALMÖ 4.45 12.97 Volvo Penta D2‐75, 2006 Fritidsmotorsegelskepp SEBO ECLIPSE 4.30 12.95 2 Perkins M80T, 1991 Fritidsmotorsegelskepp SKEL Q‐COON 4.04 12.90 Deutz OT43, 1998 Fritidsmotorsegelskepp SMUI LADY CHEKEDA 4.26 12.86 Yanmar 4JH3‐E, 2000 Fritidsmotorsegelskepp SKDX ADVENTURE 2 4.01 12.86 Perkins 4108M 1981 Fritidsmotorsegelskepp SKCX SAFARI 4.06 12.85 Perkins 4.108 1981 Fritidsmotorsegelskepp SCNO FÅGEL FENIX 4.20 12.85 Volvo DA 55, 2003 Fritidsmotorsegelskepp SMIZ ALOUETTE 4.19 12.85 Yanmar 4JH3, 2002 Fritidsmotorsegelskepp SJBZ JANA 4.20 12.85 Yanmar 4TE 3GM, 2002 Fritidsmotorsegelskepp SDYG MOON RIVER 4.20 12.85 Yanmar 4JH3TE, 2000 Fritidsmotorsegelskepp SBYP SHADOW 4.06 12.80 Perkins 4.108 Fritidsmotorsegelskepp SDAV JAMMEN 4.07 12.77 Volvo Penta Fritidsmotorsegelskepp 155

SKOX IDROTT 4.07 12.75 Albin H3 1940 Fritidsmotorsegelskepp SDOT NICESMILE 4.12 12.75 Yanmar, 2008 Fritidsmotorsegelskepp SDVG ELVIN A 4.07 12.70 Thornycraft T98, 1989 Fritidsmotorsegelskepp SDEJ GOSI 4.04 12.70 Volvo D2‐55, 2002 Fritidsmotorsegelskepp SMOG BLUE FILOU 4.15 12.69 Volvo Penta MD 22, 1997 Fritidsmotorsegelskepp SLCV MANDALAY 4.15 12.68 NEWAGE‐BMC 57VD, 1968 Fritidsmotorsegelskepp SBIX SANDRA‐MARIA 4.24 12.65 Perkins Prima 50, 1989 Fritidsmotorsegelskepp SBKL MADAME TOPI 4.24 12.65 Perkins Prima 50,1989 Fritidsmotorsegelskepp SLZF KISMET 4.22 12.65 Perkins Prima 4108, 1986 Fritidsmotorsegelskepp SKRT EILEAN OF RHU 4.06 12.65 Perkins 4.236 Fritidsmotorsegelskepp SJAP THALIA 4.24 12.65 Perkins Prima 50 1990 Fritidsmotorsegelskepp SLOQ ALEGRIA 4.22 12.65 Perkins 4,108M 4cyl,1987 Fritidsmotorsegelskepp SDOY JOSEPHINE SUN 4.22 12.65 Perkins Prima M50, 1990 Fritidsmotorsegelskepp SEYC THERIA 4.22 12.65 Perkins, 1986 Fritidsmotorsegelskepp SMFV CONDOR OF SWEDEN 4.22 12.63 Perkins 4.108 1987 Fritidsmotorsegelskepp SMHR MONIQUE 4.22 12.63 Perkins Prima 1988 Fritidsmotorsegelskepp SLDX TAAROA 6.15 12.63 Volvo‐Penta 1975 Fritidsmotorsegelskepp SHDX MILJON 4.04 12.62 Perkins Diesel 1978 Fritidsmotorsegelskepp SDBG FRENCH KISS 4.18 12.62 Yanmar 4JH4‐E, 2007 Fritidsmotorsegelskepp SCHY MIRAGE 4.18 12.62 Yanmar, 2006 Fritidsmotorsegelskepp SJYK SUPERBE 4.18 12.62 Yanmar 4JH4‐E, 2008 Fritidsmotorsegelskepp SCIF KALYPSO 4.18 12.62 Yanmar 4JH4‐E, 2007 Fritidsmotorsegelskepp SCMH CRISTINA AF GÅSHAGA 4.18 12.62 Yanmar 4JH4‐HTE, 2008 Fritidsmotorsegelskepp SFHD SO LONG AV NACKA 4.16 12.60 Volvo, D2‐55 Fritidsmotorsegelskepp SLCX ALIDA 4.04 12.60 Yanmar 4LH, 2005 Fritidsmotorsegelskepp SFRP FRISSE 4.60 12.56 Ford Bowman FH 220 1972 Fritidsmotorsegelskepp SHTB ROYAL TREAT 4.11 12.53 Perkins 4‐108, 1985 Fritidsmotorsegelskepp SKPQ GEFION AV LIMHAMN 4.08 12.50 Volvo Penta D2‐55, 2005 Fritidsmotorsegelskepp SIFZ SOFIA CHARLOTTA 4.56 12.50 BMW diesel Fritidsmotorsegelskepp 156

SGLV JOSEFIN 4.09 12.49 NG6 Ford Fritidsmotorsegelskepp SDJX RONJA AF KÖPING 4.61 12.48 Volvo MD 67C 1968 Fritidsmotorsegelskepp SEQN GURU 6.45 12.45 Volvo Penta MD19 1982 Fritidsmotorsegelskepp SDBC PINTA 4.46 12.35 Ford 592, 1955 Fritidsmotorsegelskepp SLPG CAROLINA JOOS 4.05 12.33 Volvo Penta 2040 MD, 1998 Fritidsmotorsegelskepp SJOX NIKE AV STOCKHOLM 4.73 12.32 Herkules 1952 Fritidsmotorsegelskepp SLIB CRAZY JANE AGAIN 4.08 12.30 Yanmar 4JH3E, 1999 Fritidsmotorsegelskepp SCGR LAURA 4.64 12.29 Marna M4 1969 Fritidsmotorsegelskepp SCIZ POWDER 4.18 12.29 JSUZU 3 kc 1989 Fritidsmotorsegelskepp SLUQ NOMAD 4.40 12.27 Volvo Penta MD27 1968 Fritidsmotorsegelskepp SHYU OZ 4.10 12.24 Fritidsmotorsegelskepp SDPC NORDKOSTER 4.63 12.22 Volvo Penta MD40, 1992 Fritidsmotorsegelskepp SLQD FAST FOOD SALLY 4.04 12.20 Yanmar 5250 Fritidsmotorsegelskepp SGLK GODDAHA 4.37 12.19 Ford 2712E 1974 Fritidsmotorsegelskepp SKPL CARISMA 4.12 12.17 Leyland 160‐24‐311 1966 Fritidsmotorsegelskepp SBDX LITORINA AF HELSINGBORG 4.05 12.10 Cubota KTT 3000 1987 Fritidsmotorsegelskepp SLGV NEW PATRICIA 4.04 12.08 Chrysler‐Nissan SD33 1978 Fritidsmotorsegelskepp SDCB ANIARA AF SPACE 4.07 12.07 2 Volvo Penta diesel Fritidsmotorsegelskepp SGHR BELLIS 4.00 12.06 Perkins diesel 4.108 Fritidsmotorsegelskepp SMUX FOAM 4.39 12.03 Fritidsmotorsegelskepp SKND ROYAL VIKING 4.34 12.02 Perkins 4.236M 1982 Fritidsmotorsegelskepp SBCN SEACAT 39 5.95 12.01 Volvo Penta MD 2002 1988 Fritidsmotorsegelskepp SBQM ANASTHASIA V 4.00 12.01 Ford Lehman Fritidsmotorsegelskepp Fritidsmotorsegelskepp SHGO LINNEA 6.12 14.67 jakt SLGX ST LOUIS 9.28 54.72 Mirless Blackstone Fritidsmotorskepp SJTR SKREDSVIK 8.50 49.90 Hedemora 16V Fritidsmotorskepp SBNP ZABULL 7.90 44.93 2 Mercedes Benz Fritidsmotorskepp SBIK ARKÖ 7.90 44.93 2 Mercedes‐Benz 820Gb1958 Fritidsmotorskepp 157

SCDM BLIDÖ 7.90 44.93 2 Mercedes‐Benz 820Gb1958 Fritidsmotorskepp SCDF STYRSÖ AV SÖDERTÄLJE 7.88 44.93 2 Mercedes Benz 820GB Fritidsmotorskepp SKEN MADAME LOUISIANA 11.19 38.85 2 Scania DSI 14, 1990 Fritidsmotorskepp SCRU VIVE LA VIE 5.07 38.77 Badovin 80CV, 1951 Fritidsmotorskepp MONA GREEN AF SKYF GÖTEBORG 6.77 38.20 Jönköpings motorf. 1967 Fritidsmotorskepp SGMV DOLORES 6.65 37.90 404 VO Alpha Diesel 1957 Fritidsmotorskepp SCBU KLARA AF STOCKHOLM 6.21 37.30 2 Scania Fritidsmotorskepp SGBJ MYSING AF NYNÄSHAMN 6.32 36.62 2 Scania V8 141, 1980 Fritidsmotorskepp SLON UNITED SPIRIT 4.84 34.20 2 MTU 396V8 1975 Fritidsmotorskepp SION ALBATROSS IMPERIUM 6.72 34.08 Scania DSI 11 1969 Fritidsmotorskepp SKMH HERI 5.52 33.56 Hundested 1963 Fritidsmotorskepp SKLH BELLA 6.82 33.02 Cummins VT171OM, 1980 Fritidsmotorskepp SKPN WILJO 5.70 33.00 DAF 1160 1974 Fritidsmotorskepp SHFD TAMPA 7.00 32.03 Busch‐Sulzer St Louis 44 Fritidsmotorskepp SFNJ GULLVOR 6.97 32.02 Scania DSI 14 48 M23, 1992 Fritidsmotorskepp SGZI AILA AF KARLSTAD 6.88 31.97 Cummins NVH12 1960 Fritidsmotorskepp SBZG FÄLLAREN 6.30 31.93 2 Volvo Penta MD100 1984 Fritidsmotorskepp SBNW LINNEA BLADNER 6.28 31.93 2 scania D11 R81 1971 Fritidsmotorskepp SDEM ARGO 6.80 31.86 Volvo Penta TAMD 120A Fritidsmotorskepp SMBY CERMONA 6.34 31.85 Industrie 1961 Fritidsmotorskepp SDME LÅNGÖ II 5.39 31.82 Skandia 285B 1953 Fritidsmotorskepp SJUK VIEILLE MONTAGNE 6.87 31.70 J Munktell typ MB 1951 Fritidsmotorskepp SERM SVANEFJORD 6.86 31.69 Fritidsmotorskepp SCAV SKRAMSÖSUND 7.42 31.20 2 Scania DSI 11 1970 Fritidsmotorskepp SDHI BACKE 5.58 31.16 Triple exp. Akers MV 1910 Fritidsmotorskepp SHLR RAGVALD 5.69 30.53 Mercedes 617, 1981 Fritidsmotorskepp SFKJ FIRST EDI 4.33 30.50 Fritidsmotorskepp SELK GRUNO 5.40 30.47 Volvo TMD 100 Fritidsmotorskepp 158

SEWD TRESOR 6.30 30.32 Volvo TMD 100 1985 Fritidsmotorskepp SDCA SANDY HOOK 6.30 30.32 Scania Vabis DSI 11 1984 Fritidsmotorskepp SFVI STEGE 6.30 30.10 Volvo‐Penta TAMD120 1976 Fritidsmotorskepp SLEB GÄLNAN 6.07 29.30 June Munktell 1943 Fritidsmotorskepp SDJR KARLIZA 5.23 29.28 2 Cummins NTA 855, 1992 Fritidsmotorskepp SFDB GERDA 6.60 29.27 Volvo Penta TD 100, 1975 Fritidsmotorskepp SLAN VEINO 5.52 29.26 B & W Alpha 342V 1945 Fritidsmotorskepp SBQE HOOP OP ZEGEN 5.41 29.25 Brons 1624 1929 Fritidsmotorskepp SEPM BLOMÅS 5.82 29.18 Normo, 1955 Fritidsmotorskepp SBKD BALTIC LADY 5.23 29.13 2 Scania DSI 11 1980 Fritidsmotorskepp SKVM MORMOR 6.82 28.88 Man/B&W‐Alpha 1988 Fritidsmotorskepp SHKR CONATUS 5.40 28.87 Volvo Penta TMD100, 1976 Fritidsmotorskepp SIYO MOA AF HARG 6.02 28.64 Scania DSI14MO1SF 1973 Fritidsmotorskepp SJOI ODEN AV HJO 6.80 28.64 Volvo Penta TMD 96 1961 Fritidsmotorskepp SLJW BILLIE PILGRIM 6.58 28.39 Scania D 10 1973 Fritidsmotorskepp SDZU NICA AF GOTHENBURG 6.48 28.29 Scania D11, 1982 Fritidsmotorskepp SLCY ILDERIM IV 4.90 28.22 Fritidsmotorskepp SFQR MONIKA 6.30 28.20 Scania DSI 11, 1975 Fritidsmotorskepp SIBR DAGNY 7.31 28.11 Fritidsmotorskepp SCIM EMM XXIII 5.00 28.03 2 Scania DSI 11 R82A 1970 Fritidsmotorskepp SBZU DORIAN GREY 5.02 27.86 2 Scania DSI11 1975/1983 Fritidsmotorskepp SJLQ THERON 5.03 27.75 2 Kockums diesel 1942 Fritidsmotorskepp SBZP IDSKÄR AF NORRTÄLJE 5.17 27.70 2 Scania DS 11 Fritidsmotorskepp SBZO DAS BOOT WISBY 5.17 27.70 2 Scania DS11 Fritidsmotorskepp SDMG VILJAN 5.22 27.49 Volvo TAMD 120 B,1985 Fritidsmotorskepp SHAL SHIP HOTEL SJÖHÄSTEN 5.67 27.37 Atlas Polar K45E/ASEA LE Fritidsmotorskepp SJRQ BENITA 7.05 27.16 Alfa 343 F 1951 Fritidsmotorskepp SMYH JÄRN 5.29 27.14 2Volvo‐PentaTAMD100A 1975 Fritidsmotorskepp SLCM ANNA‐EVA AF LJUSTERÖ 5.82 27.00 Wichmann 3 ACAT 1964 Fritidsmotorskepp 159

SGPJ JULIANE 5.49 26.97 Fritidsmotorskepp SHFO LADY ANNE III 7.02 26.91 Scania DSI 11, 1993 Fritidsmotorskepp SGRX LEO 7.25 26.61 Busch‐Sulzer 6DFMT‐17 Fritidsmotorskepp SKCI VERTROUWEN 5.02 26.50 Albin G‐62 1961 Fritidsmotorskepp SMCD TIGER 7.26 26.24 Clark Bros Co diesel,1944 Fritidsmotorskepp SMZR FALKLAND 6.74 26.22 Motorw.Mannheim MWM ‐60 Fritidsmotorskepp SJZB ROYAL SUND 5.22 26.15 2 st Scania DS11 1978 Fritidsmotorskepp SFCZ PETER 6.90 26.06 Scania Vabis diesel 1966 Fritidsmotorskepp SJVM SOLAMIT 6.26 25.90 Volvo Penta TMD96B1 1962 Fritidsmotorskepp SKUD GUNNAREN 6.58 25.75 Volvo Penta RMD 1965 Fritidsmotorskepp SEVU ANDIAMO 6.12 25.72 2 MTU Fritidsmotorskepp SECO FLOTTISTEN 5.33 25.51 Volvo Penta TMD100 6 cyl Fritidsmotorskepp SHMR JAGAREN 4.86 25.47 2 st G.M. 1955 Fritidsmotorskepp SKLM MINUT 6.13 25.42 Scania D11 diesel 1981 Fritidsmotorskepp SFGP SAGITTA 5.03 25.23 Scania Vabis Turbo 1940 Fritidsmotorskepp SHYB FREEDOM 5.56 25.18 Volvo‐Penta TMD100A 1966 Fritidsmotorskepp SKUY MIO 5.10 25.17 2st Volvo Penta MD96,1955 Fritidsmotorskepp SCQA REBECKA 5.22 25.16 2 Volvo TMDA Fritidsmotorskepp SFTV REMI 5.10 25.12 2 Scania DSI‐11 1985 Fritidsmotorskepp SFIG SJÖKRONAN 5.22 25.11 2 DS 10 Scania Vabis 1959 Fritidsmotorskepp SDAF ARGUS 4.73 25.10 Volvo Penta VDF6 Fritidsmotorskepp SBYZ ANDEN 5.05 25.10 2 Scania D815 1954 Fritidsmotorskepp SMCW AMIGO 5.05 25.10 2 Scania D815 Fritidsmotorskepp SDKR DRAGA 6.74 25.03 11 SCANIA DSI 14, 1990 Fritidsmotorskepp SFBZ BENJAMIN 5.90 25.00 SACM/Poyaud 1983 Fritidsmotorskepp SCWA EJDERN AF STOCKHOLM 4.77 24.98 BUDA 1955 Fritidsmotorskepp SMWQ TRESNO 6.62 24.95 Grenå diesel 6cyl,1988 Fritidsmotorskepp SKXG KARIN 4.98 24.88 Volvo Penta TMD100AK 1969 Fritidsmotorskepp SHLW CLIPTON 6.61 24.85 Lister Blackstone 6 cyl Fritidsmotorskepp 160

SGXV LÄCKÖ 6.54 24.81 Alpha diesel 40626VO 1978 Fritidsmotorskepp SMCI LIWUMI 6.02 24.78 MWM TRHS 526 A 1959 Fritidsmotorskepp SDHP MEGRUNDET 5.38 24.62 2 Lister Blackstone 1944 Fritidsmotorskepp SKXW WANDERLUST 5.01 24.61 Albin G‐62 1961 Fritidsmotorskepp SCNA RAMBO 5.19 24.59 2 Valmet 815 D11 1960 Fritidsmotorskepp SCMX OLD GROGG 5.53 24.46 Volvo Penta TMD 100 Fritidsmotorskepp SLGM CANDIDA 6.68 24.42 Volund 250 1959 Fritidsmotorskepp SLVU BJARMI 6.01 24.39 Fritidsmotorskepp SDAC AGE I 4.81 24.38 June Munktell 11MV 1953 Fritidsmotorskepp SEXO SINGAPORE 6.43 24.32 Jönköpings motorf. 1964 Fritidsmotorskepp SHDJ ANDROMEDA 6.60 24.32 Caterpillar 6cyl Fritidsmotorskepp SGPU ELLINOR 5.22 24.26 Bergsund MV 1927 Fritidsmotorskepp SCAI BLACKAN 6.56 24.20 Scania DSI 14, 1994 Fritidsmotorskepp SEZT ANDASU 6.19 24.14 Grenaa 6F24T 1975 Fritidsmotorskepp SMBQ MOANA 4.50 24.12 2 MWM V12 Fritidsmotorskepp SDHN NYMPHE 6.41 24.11 Deutz SF 16M 716, 1974 Fritidsmotorskepp SCAJ DÄMMAN 6.49 24.10 Scania DSI 14, 1997 Fritidsmotorskepp SCDO RÖDLÖGA AV BOHUS 6.56 24.08 Scania DS 14, 1977 Fritidsmotorskepp SIDZ FANÖ 6.60 24.08 Jönköpings Motorf.6TFD Fritidsmotorskepp SHVF SANA 6.39 24.05 Modag SRB 55 1951 Fritidsmotorskepp SGNI HILDUR 5.29 24.05 B&W, Lathrop D‐155‐v,1968 Fritidsmotorskepp SKXO SVK09 DALARÖ 5.06 24.05 MTU 8V 396 TB 83 ‐83 m.fl Fritidsmotorskepp SLFV SVK11 ÖSTHAMMAR 5.06 24.05 MTU 8V 396 TB 83, 1983 Fritidsmotorskepp SFMD ELECTRA III 6.10 23.99 2 Carterpillar 3412E,2001 Fritidsmotorskepp SCAH HISINGEN 6.46 23.99 Scania DSI 14,1994 Fritidsmotorskepp SGMF WHATS THE RUSH 6.42 23.96 J‐M diesel 6TFD 260MVH 64 Fritidsmotorskepp SGVN QROOZ 01 5.01 23.92 2 Volkswagen SDI 75‐5 Fritidsmotorskepp SHNX SUECIA 6.44 23.87 Detroit diesel 1968 Fritidsmotorskepp SLRW CECILIA 4.41 23.87 Paxman Pacardo 1953 Fritidsmotorskepp 161

SFKD SENTOSA 5.00 23.85 De Laval Råoljemotor 1941 Fritidsmotorskepp SKLC SPERANZA 5.28 23.78 Wickman 4 DCT 1962 Fritidsmotorskepp SFRE SJÖSTJERNAN 4.64 23.68 Volvo‐Penta TMD 120 AK Fritidsmotorskepp SFNR RYA 4.06 23.65 Penta MD96 diesel Fritidsmotorskepp SEJG SAGAN AF MÄLAREN 6.80 23.63 Caterpillar V8 D 379 Fritidsmotorskepp SLPM TELL 5.03 23.56 Scania‐Vabis DS10R01 1966 Fritidsmotorskepp SBIO FEDDE HENDRIKA 4.44 23.34 Peugot 1979 Fritidsmotorskepp SMAX T 46 6.07 23.27 3 Isotta‐Franschini 184C Fritidsmotorskepp SCBJ CHABLIS 6.07 23.27 3 st Scania 1975 Fritidsmotorskepp SFZG NIMA 4.74 23.22 Fritidsmotorskepp SDNA BIG ENOUGH 6.00 23.20 Fritidsmotorskepp SHPZ MARSTRAND 5.84 23.16 2 Scania DS 11 1983 Fritidsmotorskepp SHNP SANDRA AF CARLSHAMN 6.52 23.15 M V M diesel Fritidsmotorskepp SGTZ VÄINÖ 5.05 23.10 Wikström Special 1 Marin Fritidsmotorskepp SGQB CROSSBY 6.40 23.08 6 cyl. diesel 1973 Fritidsmotorskepp SIQD GONDUL 6.52 23.08 Volvo‐Penta 6 cyl diesel Fritidsmotorskepp SKUQ RETSINA ONE 5.55 23.06 Fritidsmotorskepp SKAZ SHARK 5.20 23.05 2 Scania DSI‐11‐R80 1963 Fritidsmotorskepp SHGX ASTRAL DREAM 5.20 23.05 Scania DS1 10 R 80 Fritidsmotorskepp SBNV CAPELLA 5.52 23.00 Volvo TMD 100 1968 Fritidsmotorskepp SIOE XENIA ONATOPP 4.04 23.00 Rysk Detroit K161M2 1990 Fritidsmotorskepp SFRH TINGVALLA 5.30 22.97 Seffle 547‐FV, 1960 Fritidsmotorskepp SFEW ELAINE 6.49 22.89 MGO diesel Fritidsmotorskepp SCBR KRISTIN 6.53 22.87 2 Volvo TMD 100, 2003 Fritidsmotorskepp SFZJ BORKA 6.38 22.80 Skandiaverken 5cyl diesel Fritidsmotorskepp SJRI BO 5.39 22.75 Fritidsmotorskepp SFRC HÅRSFJÄRDEN 5.80 22.67 Scania Vabis DS11, 1985 Fritidsmotorskepp SGWM TAAVI 4.47 22.52 Cummins 685.9N, 1991 Fritidsmotorskepp SDIM THOR AF STOCKHOLM 5.54 22.49 Alpha Diesel 404 R 1942 Fritidsmotorskepp 162

SGJX REX 6.03 22.47 2 cyl semidiesel 502MV Fritidsmotorskepp SMXI HANGÖ 6.05 22.41 Scania Vabis diesel 1983 Fritidsmotorskepp SLBF SICILIA IV 5.70 22.38 2xCaterpillar C30, 2004 Fritidsmotorskepp SJXY ORSA 4.90 22.37 Scania‐Vabis 6 cyl 1956 Fritidsmotorskepp SMWU MOSKUS 5.06 22.31 Wichman, 1962 Fritidsmotorskepp SHAU STRÖMÅKAREN 4.54 22.29 Scania DSI11, 1970 Fritidsmotorskepp SDHG FIX 5.18 22.29 3 Penta TMD 96B1 1963 Fritidsmotorskepp SLKH ZEN 4.30 22.24 2 Scania DSI 11 1991 Fritidsmotorskepp SEFI VIGOR 5.00 22.23 Skandia råoljemotor 1953 Fritidsmotorskepp SFIH OLD‐SPERO 6.19 22.23 Skandia råoljemotor 1949 Fritidsmotorskepp SFLH HAMMARÖ 6.17 22.19 Alfa diesel Fritidsmotorskepp SFOH SILVERVÅG AV STOCKHOLM 6.46 22.18 Grenå 6F24T 1975 Fritidsmotorskepp SJWQ GÖTA KANAL I 5.42 22.18 Fritidsmotorskepp SHCZ FORSS I 5.26 22.17 Volvo TAMD120, 1988 Fritidsmotorskepp SJAM JONNY 6.28 22.12 Albin diesel 1958 Fritidsmotorskepp SMRW AZEB 6.17 22.11 Caterpillar 3408DITA 1983 Fritidsmotorskepp SHZE HAFBORG 5.41 22.10 Caterpillar D353TA, 1983 Fritidsmotorskepp SGDV DUNDERHONUNG 6.11 22.09 Scania‐Vabis DSI 14M 1985 Fritidsmotorskepp SDNX ASTRID AV TIMMERNABBEN 6.28 22.04 Scania 1959 Fritidsmotorskepp SJQE THREE SEASONS 5.71 22.04 2 MAN D2842LE406, 1998 Fritidsmotorskepp SIWH HJERNET 5.15 21.95 Albin 6cyl G‐62 1958 Fritidsmotorskepp SGDO EDA 4.50 21.94 Scania Vabis D814 8 cyl Fritidsmotorskepp SGZP ÖSTERÖ AF VÄSTERÅS 6.52 21.93 2 Detroit Fritidsmotorskepp SIFL KLIPPVIK 6.28 21.88 Grenå Diesel 1973 Fritidsmotorskepp SDZM ISDRONNINGEN 6.95 21.79 Cummins KT‐1150‐N Fritidsmotorskepp SLJB ALTARSKÄR 4.82 21.76 3 Scania DSI 11 Fritidsmotorskepp SMRV BJÖRG 6.12 21.69 Caterpillar D 353 1943 Fritidsmotorskepp SFAE ESCORPION 5.20 21.68 Volvo Penta MD100A 1970 Fritidsmotorskepp SKJH YGGDRASIL 5.54 21.63 Volvo‐Penta TMD100A 1976 Fritidsmotorskepp 163

SEWX ENSKÄR 6.23 21.56 Volvo‐Penta TAMD121C 1984 Fritidsmotorskepp SIWO STANLEY 6.10 21.55 Fritidsmotorskepp SGVR MIEN 5.31 21.52 Jönköpings Motorf. 1956 Fritidsmotorskepp SLGE CARMEN AF STOCKHOLM 5.08 21.52 Ahlström Compound 1915 Fritidsmotorskepp SMNO MÄLAREN 6.06 21.51 Mercedes‐Benz MD896A6‐66 Fritidsmotorskepp SGVK MARY 5.02 21.50 General Motors diesel Fritidsmotorskepp SJOV BALTIC SEA 4.02 21.46 Scania D 10 Fritidsmotorskepp SFOC KATTEGATT 6.02 21.45 Volvo Penta TMD 100, 1983 Fritidsmotorskepp SHPK SONJA 4.05 21.41 Fritidsmotorskepp SDJH TORSKÄR 4.86 21.40 3 Volvo Penta TMD96B1 66 Fritidsmotorskepp SBEI ÖRSKÄR 4.86 21.40 3 Scania DSI 11, 1980 Fritidsmotorskepp SFTI KARMINA 4.62 21.39 Volvo 96 BI 1968 Fritidsmotorskepp SDJA SEA BREEZE 4.24 21.38 3 Scania DSI 11 1974/76 Fritidsmotorskepp SLZY NORMANDIE 4.24 21.38 3 Scania D815 1957 Fritidsmotorskepp SMAY PRO DIVER 4.24 21.38 3 Scania D816 Fritidsmotorskepp SMAU BEACH BOY 4.24 21.38 3 Scania D816 1957 Fritidsmotorskepp SMRF MARINESHOP 1 4.24 21.38 Scania Vabis DSI 11 1965 Fritidsmotorskepp SBKQ TORNADO 4.24 21.38 3 Scania D816 Fritidsmotorskepp SFCQ SVK 248 4.27 21.38 3 Scania DS 11, 1992 Fritidsmotorskepp SJVR MARTHA AF STOCKHOLM 5.51 21.37 Shottel Navigator, 1976 Fritidsmotorskepp SLGH TVÅHUNDRASJUTTIOSEX 4.24 21.36 3 Scania DS11,1977 Fritidsmotorskepp SDHC TVÅHUNDRAFEMTIOSJU 4.28 21.36 3 Scania DSI 11, 1989 Fritidsmotorskepp SDAQ TVÅHUNDRAFJORTON 4.28 21.36 3 Scania DSI 10, 1980 Fritidsmotorskepp SDEW SAINT X 4.28 21.36 Scania DC11 Fritidsmotorskepp SDFW IOWA CCLV 4.28 21.36 3 Scania DSI 11, 1980 Fritidsmotorskepp SDAY TVÅHUNDRASEXTON 4.28 21.36 3 Scania DSI 10, 1980 Fritidsmotorskepp SDQN TRIBEL 4.28 21.36 3 Volvo TMD 100A 1976 Fritidsmotorskepp SFLJ LOMMEN AV MUSKÖ 4.82 21.36 Fritidsmotorskepp SFJT VINCENT 5.98 21.36 Volvo diesel P96B 1968 Fritidsmotorskepp 164

SFMK VÄDERÖ AF FISKETÅNGEN 5.92 21.35 General Motor V12 1979 Fritidsmotorskepp SEWU HUGIN 5.02 21.33 Mercedes‐Benz Fritidsmotorskepp CHARLOTTA AV SLHE STOCKHOLM 6.10 21.30 Volvo Penta 120ACC, 1983 Fritidsmotorskepp SBEP FLAGGSKÄR 4.82 21.30 3 Scania DSI 11,1987/1990 Fritidsmotorskepp SGVQ NALINA 4.27 21.30 2 Volvo TAMD 120 Fritidsmotorskepp SBNA NOTOS 4.27 21.30 3 Scania DSI 11 Fritidsmotorskepp SDKA TPBS 222 4.27 21.30 3 Scania DSI11M01,1961 Fritidsmotorskepp SDUH TPBS 233 4.27 21.30 2 Volvo TAMD122A,1963 Fritidsmotorskepp SEHA TPBS 256 4.27 21.30 3 Scania DSI11R82,1973 Fritidsmotorskepp SEHR TPBS 259 4.27 21.30 3 Scania DSI11R82,1975 Fritidsmotorskepp SEIO OCTAVIA AF CALMARE 4.27 21.30 3 Scania DSI11R82,1975 Fritidsmotorskepp SERN TPBS 268 4.27 21.30 3 Volvo TAMD100A,1976 Fritidsmotorskepp SETM TPBS 277 4.27 21.30 3 Scania DSI11M01,1977 Fritidsmotorskepp SDJC TPBS 213 4.27 21.30 3 Scania DSI11M01,1960 Fritidsmotorskepp SEGU TPBS 253 4.27 21.30 3 Scania DSI11R82,1972 Fritidsmotorskepp SDVF TPBS 249 4.27 21.30 3 Scania DSI11R82,1971 Fritidsmotorskepp SEWF DYKAREN 4.27 21.30 3ScaniaDSI11R82A,1960 Fritidsmotorskepp SMOQ GLIMTEN 4.27 21.30 2 Volvo TAMD 122A Fritidsmotorskepp SFLB JOFFSKÄR 4.27 21.30 Fritidsmotorskepp SFMR TRÄFFEN 4.27 21.30 Fritidsmotorskepp SHDG NAUTICA 4.21 21.29 Scania Vabis DSI 10 1961 Fritidsmotorskepp SCUA SEALODGE 5.43 21.27 2 Detroit 12V71T1,1986 Fritidsmotorskepp SMYN LADY FONTAINE 6.06 21.25 Scania‐Vabis DS 11 1968 Fritidsmotorskepp SMFX BLAU MALIN 5.51 21.25 Alpha diesel Fritidsmotorskepp SGQP EGGSKÄR 4.83 21.24 2 Scania DSI 11 82 A 1985 Fritidsmotorskepp SHRF STOLT III 5.40 21.22 2 M:T:U:12V 183 TE 93,98 Fritidsmotorskepp SBED JAKO 4.82 21.21 Volvo‐Penta TAMD 163 1994 Fritidsmotorskepp SDAE EKEN AV TYRESÖ 4.83 21.20 Scania DSI 11R82ASF, 1975 Fritidsmotorskepp 165

SKRO NOVA BERGSMAN 4.65 21.20 2 Wola‐Henschel 28H12A 76 Fritidsmotorskepp SKJM SKIFTESKÄR 4.82 21.20 3 Scania DSI11 40M20S ‐88 Fritidsmotorskepp SCHQ STEINTJE 4.12 21.19 DAF D575/6 1982 Fritidsmotorskepp SJVB TERMIK 5.23 21.18 2 MAN D284‐LE406, 1998 Fritidsmotorskepp SFVQ DEHRA DUN 5.23 21.18 2 MAN 2842 LE, 1996 Fritidsmotorskepp SIFA US SKUTSJE 4.34 21.14 Mercedes OM67/8 1953 Fritidsmotorskepp SFLY HISPANO 6.10 21.10 Caterpillar D343 6cyl ‐77 Fritidsmotorskepp SKQW TAJFUN 4.65 21.10 2 Wola‐Henschel 28H12A 74 Fritidsmotorskepp SKTZ PONTUSA 4.65 21.10 2 Wola‐Henschel 28H12A‐77 Fritidsmotorskepp SFXV SVANLAND AV GÖTEBORG 6.53 21.09 Scania DSI 14 61M41T 1996 Fritidsmotorskepp SLFT ALINE 4.84 21.08 3 Scania DSI 11, 1987 Fritidsmotorskepp SHPY FALKE 5.74 21.03 Volvo Penta TMD100 1965 Fritidsmotorskepp SKJG LINDOS 5.43 20.98 Gardner 1970 Fritidsmotorskepp SGXI NELLA 4.70 20.86 2 Scania Vabis D 11 R 81 Fritidsmotorskepp SLFC NIMIS 6.43 20.85 Scania D7, 1964 Fritidsmotorskepp SDZO MORRAN 4.99 20.84 Leyland 1961 Fritidsmotorskepp SFJR OCEAN PEARL 4.95 20.79 2 Scania DSI 10, 1962 Fritidsmotorskepp SFUH CANNING 5.93 20.76 Volvo Penta TMD 96, 1964 Fritidsmotorskepp SHPI OCEANMOON 6.11 20.72 Volvo Penta 1973 Fritidsmotorskepp SDNT JENS KIIL 5.24 20.70 Kromhout Tv8 1968 Fritidsmotorskepp SFLU ASTA 2 6.28 20.66 Scania Vabis DSI 10R80 Fritidsmotorskepp SEFM HAMNESKÄR 4.66 20.65 Klöckner‐Hamboldt Deutz Fritidsmotorskepp SDCN ANNA HUDSON 6.10 20.63 Skandia tändkulem. 1950 Fritidsmotorskepp SFXJ ATHENE 4.72 20.60 Skandia 1956 Fritidsmotorskepp SDMK ATLE 4.36 20.57 Fritidsmotorskepp SLDZ DAWN OF DAY 5.28 20.51 Wickman 1956 Fritidsmotorskepp SIEO ELSA 5.08 20.49 Scania D11R01 6 cyl, 1973 Fritidsmotorskepp SIKO FORTUNA 6.25 20.48 Penta MD96 diesel 1957 Fritidsmotorskepp SIDR DYNÄS II 4.36 20.47 Skandia 465C 1955 Fritidsmotorskepp 166

SHBQ ÖRN 4.28 20.45 Skandia 395C 1954 Fritidsmotorskepp SLIM MAHAL KITA 5.43 20.43 MAN Fritidsmotorskepp SHDR GESAR 4.39 20.41 Scania DSI 14 Fritidsmotorskepp SLTI ARTICI 6.00 20.39 Volvo Penta TAMD 120A Fritidsmotorskepp SFQC ARIEL AF SÖDERHAMN 6.08 20.38 Volvo Penta TMD120A 1978 Fritidsmotorskepp SFJZ VILDAND 6.30 20.36 Deutz diesel 1974 Fritidsmotorskepp SMHP KAROLINA ÅLAND 4.65 20.33 Albin G 62 Fritidsmotorskepp SLUN ANNE‐MARIE AF VÄSTERVIK 5.23 20.31 2 MAN 820, 1993 Fritidsmotorskepp SDMA SEAESTA 5.23 20.31 2 Volvo Penta TAMD162 Fritidsmotorskepp SCHE PRINCESS ELISABETH 5.23 20.31 2 st Volvo‐Penta TAMD 162 Fritidsmotorskepp SBCO BIANCA II 5.07 20.22 2 CRM 18 DSS, 1976 Fritidsmotorskepp SLAU TOLVAN 4.73 20.20 Fritidsmotorskepp SELW MILOS 4.73 20.16 Skandiaverken 1957 Fritidsmotorskepp SGJW FANZY 4.95 20.14 Albin G‐62 Fritidsmotorskepp SGNP TÅNGÖ 6.02 20.10 Alpha 4‐cyl diesel, 1957 Fritidsmotorskepp SEYU INGEBORG 4.88 20.09 Scania D625 1953 Fritidsmotorskepp SMKU HÄLLEVIKSSTRAND 5.93 20.07 Fritidsmotorskepp SHCI KORSHOLMEN 7.17 20.02 Volvo Penta MD100A 1962 Fritidsmotorskepp SGCZ ALEX 4.82 20.00 Volvo TD 47 år 1966 Fritidsmotorskepp SBRY ELIN AF WISBY 6.02 20.00 Volvo TMD 120, 1975 Fritidsmotorskepp SFPO ANNA‐MAJ 5.90 19.98 Volvo‐Penta TAMD 120A ‐73 Fritidsmotorskepp SFXL K.A. WALLENBERG 6.03 19.95 2 Scania Vabis DSI 10R 80 Fritidsmotorskepp SBCU BENLI 5.40 19.93 Hundestedt 1976 Fritidsmotorskepp SFBQ ELISABETH 6.05 19.92 Alpha Diesel405 5cyl 1959 Fritidsmotorskepp SMWJ GERDA AF SÖRLEVIKEN 5.85 19.92 Scania DSI 11, 1970 Fritidsmotorskepp SMOL CHIRUNDO 5.10 19.92 2 Caterpillar 3406, 2004 Fritidsmotorskepp SFGB ULVEN 6.00 19.87 Caterpillar D333B 1970 Fritidsmotorskepp SLXQ MIDGAARD 5.26 19.87 Hundested 1956 Fritidsmotorskepp SMRE LIZZIE 6.02 19.80 Fritidsmotorskepp 167

SLPN LARUS 4.39 19.80 Volvo TD 70B, 1973 Fritidsmotorskepp SMLZ VIKING AF STOCKHOLM 5.03 19.79 Fritidsmotorskepp SLMZ CRUSCO IV 6.10 19.77 Scania DSI 11 1977 Fritidsmotorskepp SJRT ALEXANDRA 5.02 19.74 2 GM 12‐V 71N 1966 Fritidsmotorskepp SITE ISBJÖRN AV STOCKHOLM 5.10 19.73 Volvo Penta VDF 175 1953 Fritidsmotorskepp SDWK ÅLFORS 4.50 19.73 Volvo Penta MD 100 1974 Fritidsmotorskepp SFLG PILOT 67 5.09 19.73 Wola Henschel 1976 Fritidsmotorskepp SFKU PILOT 61 5.88 19.73 Wola Henschel 1978 Fritidsmotorskepp SCOV SICILIA III 5.05 19.72 2 MAN D2842 LE404, 2004 Fritidsmotorskepp SHWQ WILLY AF SÖDERTELGE 4.54 19.70 Nohab‐Polar 1945 Fritidsmotorskepp SDTE VIOLET 5.94 19.63 Skandia Fritidsmotorskepp SMHN WET ASSET 5.52 19.60 Volvo Penta TAMD61A,1997 Fritidsmotorskepp SENP AVANCE N:O 15 4.69 19.58 Skandia Fritidsmotorskepp SKFE THE FLYING MUCHACHOS 5.21 19.55 Hundested GGL 330 1972 Fritidsmotorskepp SKNX SINGOALLA 5.57 19.55 Grenå 2.38T 1965 Fritidsmotorskepp SHBK ALFRED 4.80 19.53 Werkspor 1942 Fritidsmotorskepp SIBL WHITE CAT 4.96 19.43 2 MWM D232 V12 1969 Fritidsmotorskepp SKPD ZIROCCO 4.67 19.42 2 Fiat V8 8280 SRM 1981 Fritidsmotorskepp SJVP AKTIV AV FLÅSJÖN 4.53 19.41 Deutz SA 8 M 517 1958 Fritidsmotorskepp SLUO PLOMBEN III 4.91 19.37 2 Volvo Penta MD30A 1986 Fritidsmotorskepp SKOY CLAUS‐PIA 5.38 19.35 Grenå Diesel 1426 1959 Fritidsmotorskepp SHUD VALDE 4.65 19.32 Fritidsmotorskepp SHDK UNDINE AF LULEÅ 4.60 19.30 Caterpillar diesel, 1961 Fritidsmotorskepp SIDF NEMO 4.44 19.29 GM diesel 1945 Fritidsmotorskepp SJLZ HVITFELDT 5.24 19.29 Albin Diesel 1960 Fritidsmotorskepp SMGU LADY 5.24 19.29 Gardner, 1980 Fritidsmotorskepp SGLP SÖDERÖ 1 5.93 19.26 Volvo‐Penta TMD120A, 1976 Fritidsmotorskepp SERI TUNIA 5.15 19.26 June‐Munktell 402 MD 1939 Fritidsmotorskepp SERD CAPRICE 6.07 19.25 Scania DS11 C03, 1989 Fritidsmotorskepp 168

SGLE EVELINA 5.24 19.23 Scania D645 1955 Fritidsmotorskepp SGBV ZAIDA 5.85 19.22 June Munktell 1954 Fritidsmotorskepp SFZV ANNIKA 4.80 19.20 Fritidsmotorskepp SMLE NORDFORS 5.92 19.18 Alpha diesel Fritidsmotorskepp SGNV GUNVOR 6.27 19.18 Fritidsmotorskepp SGZK SILJAN 6.09 19.17 Skandia tändkulemotor1943 Fritidsmotorskepp SCDA CECILIA AV SÄFFLE 5.20 19.13 2 Volvo Fritidsmotorskepp SHCD TEKLA 4.32 19.12 Penta TMD 96 1963 Fritidsmotorskepp SMJE ELIANA 5.97 19.10 Volvo‐Penta TAMD 120BCC Fritidsmotorskepp SMNG JUNO 2 5.99 19.06 Volvo‐Penta TAMD 1980 Fritidsmotorskepp SHTM LÖFUDDEN 4.48 19.00 Fritidsmotorskepp SMUF RIVAGE 5.25 19.00 2 Detroit 12V71TI, 1987 Fritidsmotorskepp SKAY ÖRING 4.81 18.99 Penta Diesel TMD 96 1962 Fritidsmotorskepp SMOU VENUS AF STOCKHOLM 6.00 18.95 Skandia diesel 1961 Fritidsmotorskepp SICQ NORMANDIA 6.00 18.93 Skandia Fritidsmotorskepp SKZU GIT GAY 5.32 18.90 Zaklady Mechaniczne 1974 Fritidsmotorskepp SBRF TANANGER 6.09 18.87 Vichmann 4 DCT 1970 Fritidsmotorskepp SJPD SVEN 5.06 18.87 Jönköpings Motorf. 5cyl, 1963 Fritidsmotorskepp SLJQ LÄVIK 4.36 18.86 Scania 1955 Fritidsmotorskepp SICR CIRCE 5.04 18.86 GM, 12V 71, 1964 Fritidsmotorskepp SETG CHELONIA 6.00 18.85 Hundersted 1956 Fritidsmotorskepp SBKT LAPYCOS 4.01 18.83 2st MWM D232 1966 Fritidsmotorskepp SKCZ CHAR MAR 5.85 18.80 2 Rolls‐Royce C8TFL, 1973 Fritidsmotorskepp SBPW KASKEN 5.06 18.79 Detroit Diesel V71 1974 Fritidsmotorskepp SCPA LANGESUND 6.01 18.79 Wichman 4 DCT s4 1971 Fritidsmotorskepp SIBQ MALORCA 5.54 18.78 Scania‐Vabis DSI 10 1965 Fritidsmotorskepp SHJB SILVERSKÄR 6.05 18.78 Cummins diesel NHRS‐6‐M Fritidsmotorskepp SJIF LORELEI 4.72 18.71 2 st GM diesel 1959 Fritidsmotorskepp SHZC PIRAYA 4.58 18.70 2 st Volvo TD 96B Fritidsmotorskepp 169

SHLM T 18 4.58 18.70 2 Volvo Penta MD 1960 Fritidsmotorskepp SLNR BARRACUDA 4.70 18.70 2 Volvo Penta TMD 96 1970 Fritidsmotorskepp SBUQ MONA 4.86 18.65 Callesen 425DO 1965 Fritidsmotorskepp SLRT TUA 4.93 18.64 Detroit, 1958 Fritidsmotorskepp SGDW ALPHA 5.29 18.63 Scania Vabis D821 1952 Fritidsmotorskepp SFBN TYRA 4.22 18.54 Bolinder VA40M25, 1952 Fritidsmotorskepp SMPG ALTANA 6.20 18.53 Volvo Penta TAMD 120 A Fritidsmotorskepp SHQU SAMARKAND 5.26 18.51 2 MAN D2840 LE 401, 1976 Fritidsmotorskepp SDIP BALOO 5.31 18.51 2 MAN D2840 LE403EDC,2001 Fritidsmotorskepp SBTN LIBERAE 5.31 18.51 2 Scania DI 14, 2000 Fritidsmotorskepp SITW HELGA 5.94 18.50 Fritidsmotorskepp SENI BORE 4.78 18.49 Saab‐Scania DS11 01MO1 SF Fritidsmotorskepp SDRN DANORA 4.94 18.47 2 Volvo D12/700,2002 Fritidsmotorskepp SKGF GARM 5.73 18.46 Volvo Penta Fritidsmotorskepp SLGJ SASKIA 5.20 18.45 2 Volvo TAMD 71A, 1994 Fritidsmotorskepp SECU STORA LE 2 4.41 18.44 Volvo‐Penta MD 96 Fritidsmotorskepp SHZN DAN WIKING 5.48 18.43 Skandia 285 B Fritidsmotorskepp SIJG THUNDER 4.85 18.32 Fritidsmotorskepp SGDY HAMNERÖ 6.04 18.31 June Munktell Fritidsmotorskepp SKPO DRUMMER 4.80 18.30 MAN D2848,1997 m.fl. Fritidsmotorskepp SBKA JENS KRISTIAN 5.18 18.29 DAF BK, 1983 Fritidsmotorskepp SJYL VICTORIA AF BERGSUND 4.12 18.26 Volvo, MD 47 1958 Fritidsmotorskepp SDKP VESIKKO 4.20 18.26 Scania D8, 1976 Fritidsmotorskepp SHUB ISBJÖRN AF WISBY 4.64 18.23 Albin G‐62 TK 1963 Fritidsmotorskepp SKUB YRSA 5.04 18.18 Säffle Fritidsmotorskepp SHTX VANGUARD 5.80 18.16 Skandia Fritidsmotorskepp SEGN ESEA 4.87 18.08 2 Caterpillar C15, 2008 Fritidsmotorskepp SCBL MERANDA 6.05 18.03 Volvo‐Penta TMD100A 1980 Fritidsmotorskepp SGNB BRÖDERNA 6.03 18.02 Volvo‐Penta TMD 100 6cyl Fritidsmotorskepp 170

SEHU TOVE 5.05 18.02 Volvo Penta TMD100 1972 Fritidsmotorskepp SFAI SAMANTA 4.30 18.02 Detroit V71, 1968 Fritidsmotorskepp SFCJ SLÄNDAN 5.84 18.00 Volvo Penta diesel 1972 Fritidsmotorskepp SFJP PINERO 6.02 17.98 June Munktell Fritidsmotorskepp SFQJ PIERINA IV 6.11 17.97 2 Volvo Penta D70 1971 Fritidsmotorskepp SDZT FRIGG AF STOCKHOLM 4.09 17.97 Scania 1969 Fritidsmotorskepp SHIC WANGARATTA 6.00 17.92 Albin G 62 1959 Fritidsmotorskepp SCLD AILOS 4.70 17.92 Scania D11, 1971 Fritidsmotorskepp SFVE SAGALILL 4.44 17.90 Volvo Penta 1958 Fritidsmotorskepp SDPR SEXAN 5.03 17.88 Albin Motor G62 diesel Fritidsmotorskepp SENW BUNKEROIL 5.77 17.88 Volvo Penta Fritidsmotorskepp SGJV BRANDY 5.79 17.79 Volvo Penta Tmd 120 Fritidsmotorskepp SHQD TAKE OFF II 4.49 17.75 2 Volvo D‐12, 2005 Fritidsmotorskepp SKDV REBEL 4.49 17.75 2 Volvo Penta D12 EVC, 2005 Fritidsmotorskepp SFGX VERDANDI 6.15 17.74 Fritidsmotorskepp SEQU TOP HAT 5.46 17.73 2 Detroit Diesel 6‐7 IN, 1979 Fritidsmotorskepp SDGI ALONA 5.26 17.72 June‐Munktell MB 25 1935 Fritidsmotorskepp SHKZ AMONA 5.97 17.68 Jönk. Motorf. typ 752 Fritidsmotorskepp SMHG STROMBOLI 5.78 17.68 Volvo Penta TMD 96 B 1964 Fritidsmotorskepp SHGQ BRITTANA AF STOCKHOLM 6.13 17.68 Albin Motor 1958 Fritidsmotorskepp SHBE JOY ROYAL 4.59 17.68 2 MAN D2848LE420, 2005 Fritidsmotorskepp SDHR BITCHES BREW 4.59 17.68 2 Volvo D12‐715, 2003 Fritidsmotorskepp SKIL NORDIC SPIRIT 5.63 17.68 2 Volvo DI2, 2002 Fritidsmotorskepp SLWA BLUE PRINCESS 4.30 17.68 2 Volvo AQAD 31A, 1988 Fritidsmotorskepp SMEN KONSTANTIN 5.91 17.68 Mercury 200 EFI, 2000 Fritidsmotorskepp SKWO AVA MARIA 4.72 17.67 2 MAN 680, 1999 Fritidsmotorskepp SJRL MOBILE LADY 4.72 17.67 2 MAN D2848 LE401, 1995 Fritidsmotorskepp SHTP MATILDA 5.99 17.67 June Munktell Fritidsmotorskepp SGAU FEELING 5.25 17.67 Volvo‐Penta 96B 1955 Fritidsmotorskepp 171

SFBD MARCONIA 5.95 17.62 Scania‐Vabis 8‐cyl Fritidsmotorskepp SMVC INDEPENDENCE 4.56 17.61 2 Volvo Penta TMD50 1986 Fritidsmotorskepp SMWX FARALLON 5.19 17.58 L Gardner & Sons Ltd 1975 Fritidsmotorskepp SENU NIRVANA AF STOCKHOLM 4.90 17.57 Ford Turbo Diesel, 1984 Fritidsmotorskepp SFYV SUN VIKING III 4.85 17.57 2 Volvo D12‐700 EDC II,01 Fritidsmotorskepp SGQH CLOUDE NINE 4.85 17.57 2 Volvo D12, 2002 Fritidsmotorskepp SBQP BON VIVANT 4.85 17.57 2 Volvo Penta D12‐800, 2007 Fritidsmotorskepp SGCP QUEEN MARIMAR 4.85 17.57 VolvoPenta D12‐800, 2007 Fritidsmotorskepp SCQU SMULAN AF STOCKSUND 4.85 17.57 2 Volvo D 12 EDC, 2003 Fritidsmotorskepp SDPV FRIDHEM 6.00 17.54 Volvo Penta MD 966 1963 Fritidsmotorskepp SGMK GUSTAFSHÖG 4.38 17.49 Diesel GM 2T 6 cyl Fritidsmotorskepp SEFU GREPEN 6.62 17.49 Volvo MD 96, 1968 Fritidsmotorskepp SKNP NINA AF LILJEDAL 4.56 17.48 Caterpillar 3208 TA, 1990 Fritidsmotorskepp SFWO TURISTEN 4.40 17.47 Albin Marin G‐6D 1952 Fritidsmotorskepp SMVI WINGAFJORD 5.97 17.47 Fritidsmotorskepp SHLD PIA I 4.75 17.41 Fritidsmotorskepp SGFC CLYFTON 6.02 17.40 Volvo Penta TMD 96B1 Fritidsmotorskepp SJIQ HAVHELD 4.76 17.37 Wickman AB 60 1944 Fritidsmotorskepp SGJO FREE FOUR LIFE 4.72 17.37 2 Caterpillar 3196, 1997 Fritidsmotorskepp SHDV FRODE 4.47 17.35 MG‐4 NOHAB 1956 Fritidsmotorskepp SFJD HILLEVI 5.88 17.35 Volvo‐Penta TMD 100 1976 Fritidsmotorskepp SDWZ ZARITZA 6.12 17.34 Fritidsmotorskepp SDOG MINANDRA 5.00 17.28 Penta diesel D 96 M 1957 Fritidsmotorskepp SKWZ PASS 5.40 17.27 Volvo MD96 1967 Fritidsmotorskepp SHOM FELICIA AF SKUM 5.96 17.25 Fritidsmotorskepp SFYU TRAFIK 4.77 17.23 Jönköpings Motorf. 1934 Fritidsmotorskepp SDJQ MELINGSVÅG 4.86 17.23 Gardner 6 L X 1964 Fritidsmotorskepp SDUY SVANLAND 6.00 17.19 Seffle motorv. 1964 Fritidsmotorskepp SGQO JARL 4.23 17.18 Säffle tändkulem. 1958 Fritidsmotorskepp 172

SCMP MAGNUM 4.83 17.16 2 MTU 8v183 1991 Fritidsmotorskepp SMQP ITAPOA II 4.60 17.15 2 Volvo MD70 1986 Fritidsmotorskepp SHGF ANITA 6.10 17.15 Seffle 332 FV 1959 Fritidsmotorskepp SFVC MARTINA 5.80 17.15 Volvo Penta TMD 100 1972 Fritidsmotorskepp SGUP MODIG AV STOCKHOLM 5.12 17.15 Ford diesel 6‐cyl. Fritidsmotorskepp SHJL SYDLAND 5.34 17.15 ScaniaVabisDSI11R82SF,84 Fritidsmotorskepp SLZH FABIOLA 4.83 17.15 2 Volvo Penta D‐12, 2005 Fritidsmotorskepp SIVK YASUMI 4.83 17.15 2 VolvoPentaD12‐715, 2005 Fritidsmotorskepp SINT LIBERTY YSTAD 5.95 17.14 Scania Vabis DSI‐11‐R80 Fritidsmotorskepp SGVX INGA‐LILLY 5.70 17.13 Tändkulem. 2LD350 1962 Fritidsmotorskepp SDZF MARIA II 4.75 17.12 Kromhout TS 117 1961 Fritidsmotorskepp SMBX FLATGARN 7.04 17.10 Schottel 9/200 1982 Fritidsmotorskepp SDJM HERA 4.41 17.08 Volvo‐Penta T‐D 96B 1969 Fritidsmotorskepp SLNP VÅR VIND 4.93 17.07 Hundested Semidiesel, ‐60 Fritidsmotorskepp SFZE SÄLÖ 5.85 17.05 Fritidsmotorskepp SGKF LÄPPEN 4.80 17.04 2 Scania DIO 1983 Fritidsmotorskepp SJQT DOVRE 4.30 17.00 Scania d 814 1954 Fritidsmotorskepp SBWO LILO 4.75 17.00 2 MAN D2842 LE423, 2007 Fritidsmotorskepp SIEW MEKA 4.92 16.98 Bolinder diesel Fritidsmotorskepp SHXA BLIXT 4.24 16.98 Mercedes‐Benz MB 836 B6 Fritidsmotorskepp SEPC PASSAD 4.04 16.97 Fritidsmotorskepp SLVM GRAND LADY 5.00 16.97 2 Caterpillar 3208, 2001 Fritidsmotorskepp SGVB MIMMA 6.02 16.96 Scania DSI 14MO1SF 1973 Fritidsmotorskepp SCIH NEPP LADY 5.10 16.96 2 MAN diesel 12V, 1991 Fritidsmotorskepp SGBR HILDA 4.24 16.94 Volvo‐Penta TMD100 1977 Fritidsmotorskepp SGRB GEFION AV STOCKHOLM 4.16 16.94 Volvo Penta TMD 96 B 1957 Fritidsmotorskepp SLWD RINGHOLM 1 6.20 16.94 Volvo, 2005 Fritidsmotorskepp SFWT MONITOR 4.78 16.90 2 Volvo Penta TAMD 122 Fritidsmotorskepp SMJW WALONA AF VÄSTERVIK 6.00 16.89 Volvo Penta 6 cyl 1968 Fritidsmotorskepp 173

SKLF SAM II 4.45 16.88 Deutz 514 1960 Fritidsmotorskepp SKLD NORMY 6.00 16.85 Scania DSI 11 1972 Fritidsmotorskepp SHZX INGEBORG 6.10 16.85 Volvo Penta TAMD 120,1976 Fritidsmotorskepp SHBO AIGLE 4.62 16.85 2 Scania DSI14 1976 Fritidsmotorskepp SHAM LORD MANFRED 4.26 16.84 Volvo Penta TAMD 120A Fritidsmotorskepp SIGB EKESKÄR 5.73 16.83 Volvo Penta TMD 120 1975 Fritidsmotorskepp SLWZ LYDIA 5.98 16.82 Volvo Penta TMD100A‐CC 78 Fritidsmotorskepp SHEY CLIPTON 5.92 16.79 Jönköpings Motorfabrik Fritidsmotorskepp SGTV MORE MADNESS 4.60 16.79 2 MAN D2848, 2000 Fritidsmotorskepp SEVQ EMIL 4.25 16.78 Bolinder‐Munktell 1951 Fritidsmotorskepp SGYL BERTINA 5.88 16.77 Hundested diesel 1966 Fritidsmotorskepp SJHQ SYDVIK 5.74 16.75 Scania DS 11 Fritidsmotorskepp SLGB INGRID 5.15 16.75 Fritidsmotorskepp SGZC AMBER AF UDDEVALLA 4.65 16.73 2VolvoTAMD122P EDC,‐00 Fritidsmotorskepp SMKZ JOY AV LANDSKRONA 4.65 16.73 2VolvoPentaTAMD122PEDC Fritidsmotorskepp SDIV CALIBUR 5.15 16.73 DAF 575, 1987 Fritidsmotorskepp SKHV RIM 4.30 16.71 AB Penta TMD 96 1961 Fritidsmotorskepp SERC CORIOLA 5.91 16.71 Fritidsmotorskepp SHXF BLIDA 4.05 16.70 Perkins Diesel Fritidsmotorskepp SLWQ GJÖA 5.15 16.70 Scania 642 1965 Fritidsmotorskepp SKBF AMBER MOON 5.79 16.70 2 Detroit Diesel V6,1989 Fritidsmotorskepp SEMD BJÖRN III 4.74 16.67 Fritidsmotorskepp SMZW OTTERÖN 6.10 16.67 Volvo Penta MD96 1980 Fritidsmotorskepp SEQZ CHRISTIN 6.00 16.65 Albin diesel 1957 Fritidsmotorskepp SKZY AVONTUUR 5.35 16.64 2 Detroit Diesel, 1993 Fritidsmotorskepp SFYD TELLO 4.04 16.63 Volvo Penta MD 96 1958 Fritidsmotorskepp SCGY RAN OF STENKULLA 4.50 16.62 2 Cummins NTA855 1985 Fritidsmotorskepp SEJM MUNKTELL 6.11 16.61 Bolinder Fritidsmotorskepp SHLO RAGNA 6.00 16.60 Fritidsmotorskepp 174

SEMY ASTOR 6.09 16.60 Volvo Penta TAMD100 1980 Fritidsmotorskepp SLKE ARVE 4.05 16.59 Scania DSI 11 1970 Fritidsmotorskepp SJUQ ERNST 4.41 16.58 Volvo Penta TMD 96 1963 Fritidsmotorskepp SGFB MEGASEA 4.79 16.56 Fritidsmotorskepp SBAU CHIARA DI SALTSJÖBADEN 4.70 16.55 2 MAN ASD 12L, 2000 Fritidsmotorskepp SJLK ÄRNA 6.05 16.54 Fritidsmotorskepp SMVY VAGABOND 4.70 16.54 Scania DSI11R82 1972 Fritidsmotorskepp SKER CASITA 4.88 16.52 2 Caterpillar 3126B, 2002 Fritidsmotorskepp SEYV VÄDERÖ 5.80 16.48 Fritidsmotorskepp SFCP ELSA 6.10 16.48 Volvo‐Penta TD96 6‐cyl,65 Fritidsmotorskepp SFTZ CALMA 5.82 16.48 Säffle Semidiesel 332FV Fritidsmotorskepp SHEW KAMA 4.62 16.48 Fritidsmotorskepp SING ALMA 5.10 16.48 Ford NG 4 2712 E 1976 Fritidsmotorskepp SDOC KASKELOT 4.47 16.47 Volvo‐Penta TMD100AK,‐71 Fritidsmotorskepp SKNA TORSTEN 4.39 16.46 Crossley ESLA 1949 Fritidsmotorskepp SIFE NAIMA 6.04 16.45 Skandia 1956 Fritidsmotorskepp SHXM ELLA AV KNIPPLA 5.83 16.45 Skandia tändkulemotor Fritidsmotorskepp SKOT ÖRNEN 4.39 16.44 Lundby MV comp.ångmaskin, 1903 Fritidsmotorskepp SGYJ PRÅM 1820 6.15 16.44 Suzuki Fritidsmotorskepp SFZT HAPPY HOUR 4.78 16.43 2 Volvo Penta TAMD 71A Fritidsmotorskepp SCFM EMANUELLA 4.78 16.43 Volvo TAMD 122D 1990 Fritidsmotorskepp SBCL MADAME II 4.78 16.43 2 Volvo Penta TAMD71,1987 Fritidsmotorskepp SHNB LOU PARADOU 4.27 16.39 2 Mercedes Fritidsmotorskepp SJOM ROLF 4.40 16.38 Seffle Semidiesel 1949 Fritidsmotorskepp SILE LINNEA 6.08 16.38 Fritidsmotorskepp SFJW HOLMÖ 5.72 16.36 Volvo Penta TMD96B 1964 Fritidsmotorskepp SGMX MANNE 4.22 16.36 Volvo‐Penta MD 67A 1967 Fritidsmotorskepp SFUB KAREN MARIE 4.24 16.35 Tuxham Typ M.e.1 nr 2304 Fritidsmotorskepp SCPE SANCERRE AV GÖTEBORG 4.89 16.35 Volvo TAMD31S, 2003 Fritidsmotorskepp 175

SFJB SONETTE 4.57 16.34 Volvo Penta D12, 2002 Fritidsmotorskepp SMDI DAGA 6.00 16.34 Fritidsmotorskepp SBQD VITTFARI 4.59 16.33 2st Volvo Penta D12,2002 Fritidsmotorskepp SHAZ ULRIKA VIII WERMDÖ 4.59 16.33 2 Volvo Penta D12‐700,02 Fritidsmotorskepp SICY VIA NOVA AF STOCKHOLM 4.59 16.33 Fritidsmotorskepp SIFN NOT FOR SAIL 4.59 16.33 2 Scania D 12, 2002 Fritidsmotorskepp SGXJ KIARA 4.59 16.33 2 Volvo D12, 2001 Fritidsmotorskepp SBME VICTORIA I 4.27 16.32 2VolvoPenta D12C‐A,2001 Fritidsmotorskepp SGKY MALOO 4.68 16.31 Caterpillar 3196, 2003 Fritidsmotorskepp SBTC SOVEREIGN II 4.78 16.30 2 Volvo TAMD 1990 Fritidsmotorskepp SBWZ DIKMAR 4.56 16.30 DAF diesel DS 575 1957 Fritidsmotorskepp SFTB LENNART 4.27 16.29 Scania‐Vabis DSI 10R80, 1961 Fritidsmotorskepp SEXF BRISHAV 6.04 16.26 Volvo Penta TAMD 120AK Fritidsmotorskepp SFRG EMELIE AF STOCKHOLM 5.80 16.26 Penta MD 47 1961 Fritidsmotorskepp SKBW JIDELCHA 4.82 16.26 2 Iweco 8281 SRM07 Fritidsmotorskepp SFUY EMMA BUSY II 4.57 16.26 2 Volvo D12‐800 Fritidsmotorskepp SEAM VICTORIA SOFIE 4.53 16.25 Tuxham, 1956 Fritidsmotorskepp SEIU SNOBBEN 4.20 16.25 GM 6cyl diesel 1955 Fritidsmotorskepp SEYI RIVÖFJORD 5.96 16.24 Volvo Penta TD‐100 Fritidsmotorskepp SHYO NOVA AURORA 4.80 16.21 2 Volvo TAMD 122D, 1991 Fritidsmotorskepp SIVN RENDEZ‐VOUS 4.80 16.21 2 Volvo Penta TAMD 122 Fritidsmotorskepp SBDR GO II 4.80 16.21 2 Volvo 122, 1991 Fritidsmotorskepp SBYO MELODY AF BJÖRSUND 4.80 16.21 2 Caterpillar, 1988 Fritidsmotorskepp SKDH BYBLOS 4.82 16.18 2 Detroit 8V71TI 1977 Fritidsmotorskepp SBRQ SYMBOL I 4.96 16.18 2 TAMD 71B 1990 Fritidsmotorskepp SKXH HEDVIG 4.21 16.18 Fritidsmotorskepp SJFG JEAN 4.80 16.17 2 Caterpillar 3208 1990 Fritidsmotorskepp SJYH CORNELIA AF UMEÅ 4.80 16.17 2 Caterpillar, 1989 Fritidsmotorskepp SBKO FANTASY AF WAXHOLM 4.80 16.17 2 Volvo TAMD 122D, 1991 Fritidsmotorskepp 176

SDTL RAMSKÄR 5.71 16.16 Säffle Fritidsmotorskepp SLHB LISNEA 5.12 16.15 Scania DSI14 1974 Fritidsmotorskepp SLCF BOOMERANG 4.30 16.12 Volvo TD 50 A 1972 Fritidsmotorskepp SELJ ANNE MON 5.96 16.11 Detroit 110 1954 Fritidsmotorskepp SFDL VINDIA II 4.88 16.11 Yanmar 4JH36‐HTBE, 2004 Fritidsmotorskepp SKYZ ENDLESS SUMMER 4.88 16.11 Yanmar Diesel, 2005 Fritidsmotorskepp SGLA STYRBJÖRN ÖRSUNDSBRO 4.08 16.10 2 Scania Vabis 814D 1954 Fritidsmotorskepp SJED JUM 4.46 16.05 Atlas Polar M46EF Fritidsmotorskepp SDVC TVÅ BRÖDER 5.60 16.04 Skandia Fritidsmotorskepp SLOX BENE MERITUS 4.45 16.02 2 Volvo D12‐800, 2007 Fritidsmotorskepp SMNK DEEP PURPLE 4.45 16.02 2 Volvo D12‐800, 2007 Fritidsmotorskepp SLVB BOXÖ 6.04 15.98 Scania‐Vabis D11‐C07 1980 Fritidsmotorskepp SBJN TANT PRUSELIUS 4.70 15.97 Scania DSII 1983 Fritidsmotorskepp SCVB CHIHIRO 4.60 15.94 Fritidsmotorskepp SHOJ MAGNA 4.62 15.89 2 MAN D2840 Fritidsmotorskepp SKMF BYLGIA 4.07 15.89 Volvo‐Penta MD67C 1963 Fritidsmotorskepp SLQT ERHOLMEN 5.39 15.87 B & W Alpha 343V 1953 Fritidsmotorskepp SMOZ RÖDE ORM 6.15 15.84 Volvo AQ271C/DP290A 1988 Fritidsmotorskepp SGHO MAUD 4.52 15.83 Leyland 2T/SW680/197, ‐87 Fritidsmotorskepp SKAQ ESAB IV 4.00 15.81 Volvo‐Penta TMD 100 1970 Fritidsmotorskepp SDLX ROMANCE 4.40 15.80 2 Volvo TAMD 122D, 2001 Fritidsmotorskepp SBTZ SIGNE AV SKAFTÖ 4.43 15.79 2 Caterpillar 3208 1989 Fritidsmotorskepp SLYV BORN FREE 4.74 15.78 2 st Volvo Penta TAMD 71 Fritidsmotorskepp SFBA MARICHA AF STOCKHOLM 4.74 15.78 2 Caterpillar 3208, 1989 Fritidsmotorskepp SMUQ WAIT AND SEE 4.30 15.77 2 Volvo TAMD 122 P, 1996 Fritidsmotorskepp SHQY ROYAL BLUE 4.30 15.77 2 Volvo Penta TAMD122PEDC Fritidsmotorskepp SCBF CONTIKI 4.63 15.75 2 Volvo TAMD 122 Diesel Fritidsmotorskepp SDVA QUEEN ELIZABETH III 4.63 15.75 2 Volvo Penta TAMD 122 Fritidsmotorskepp SDGE EXCALIBUR II 4.63 15.75 2 Volvo Penta TAMD122 ‐92 Fritidsmotorskepp 177

SJZY SUSSIE II 4.66 15.75 Volvo Penta D70B/750 1973 Fritidsmotorskepp SKYP CRANCHI 4.40 15.75 2xVolvo Penta D9, 2005 Fritidsmotorskepp SMXU GALATEA 5.90 15.74 Skandia tändkula 1945 Fritidsmotorskepp SIMP MIDNIGHT DREAM 4.26 15.73 2 VolvoD12 800EVC,2006 Fritidsmotorskepp SEHO MINAS TIRITH 4.26 15.73 2 Volvo D12 800 EVC Fritidsmotorskepp SLYF CAMPDEN LADY 4.55 15.72 2 Volvo TAMD 122 P EDC Fritidsmotorskepp SFQW SAWAN II 4.55 15.72 2 Volvo D12, 2003 Fritidsmotorskepp SDVP IZA MARIE 4.55 15.72 Volvo D12, 2003 Fritidsmotorskepp SEIK OLIVIA 6.07 15.72 Fritidsmotorskepp SDKV FLORISSE 4.60 15.67 2 Volvo Penta TAMD122D 90 Fritidsmotorskepp SEMZ ASTREA 6.09 15.64 Fritidsmotorskepp SFRY ST. JORAN 4.88 15.62 2 Volvo 121C, 1985 Fritidsmotorskepp SGMI MARY JOSEFINA 5.72 15.61 Scania Vabis DSI 11 1972 Fritidsmotorskepp SEIT MÄRSGARN 5.09 15.58 Scania DSI11, 1979 Fritidsmotorskepp SGMT SJU NOLL TRE 5.09 15.58 Scania DS 11 Fritidsmotorskepp SJWC JULIET AV STOCKHOLM 4.80 15.58 Fritidsmotorskepp SFDQ XANTé 5.90 15.56 Volvo Penta diesel 1958 Fritidsmotorskepp SLOZ HATTIE BEAU 4.63 15.54 VolvoPenta TAMD12PEDC,‐99 Fritidsmotorskepp SHBI SHAMAL 4.63 15.54 Fritidsmotorskepp SHKL THOR AF DJURGÅRDEN 4.63 15.54 2 Caterpillar Fritidsmotorskepp SKUV SIAM AF HÄLSÖ 4.38 15.52 Fritidsmotorskepp SGQX INGER AF GRAVARNE 5.75 15.52 Scania DIO RO1 1963 Fritidsmotorskepp SHBA CAMPARI 5.75 15.50 Scania 640/0611 1958 Fritidsmotorskepp SGIA DAISY AV MARSTRAND 4.43 15.50 2VolvoPentaTAMD122P,2000 Fritidsmotorskepp FISKETÅNGEN AF SDIW SUNNINGEN 4.43 15.50 2 Volvo Penta TAMD 122‐99 Fritidsmotorskepp SCNV WILA 4.43 15.50 2 Volvo Penta TAMD122PEDC,1998 Fritidsmotorskepp SEQC CARITA 5.65 15.48 Scania Vabis D11R26 Fritidsmotorskepp SDUQ STELLA MARIES 5.20 15.47 Skandia tändkule Fritidsmotorskepp 178

SJFT TRUBBNOS 4.58 15.46 Volvo MD 96, 1965 Fritidsmotorskepp SINW IGEN 4.20 15.46 Ford 330 1975 Fritidsmotorskepp SLKO ZELONA 4.62 15.44 Volvo Penta TMD‐96 1963 Fritidsmotorskepp SHAW STUFVAREN I 4.16 15.44 Cummins NTCE 365, 1978 Fritidsmotorskepp SJIP NORDHAV 4.50 15.44 NORMO 71 1961 Fritidsmotorskepp SLRU GOTHIA 4.64 15.43 Volvo Penta MD 96 B 1963 Fritidsmotorskepp SFPZ CASSANDRA 4.44 15.43 2 Catepillar 3196, 2000 Fritidsmotorskepp SKIW DYNAMIC ONE 4.44 15.43 2 MAN D 2876, 2002 Fritidsmotorskepp SDUA KARIN AV RINDÖ 4.60 15.42 Volvo Penta TMD 100 Fritidsmotorskepp SHGR PAMELA E‐SON EDWARDS 5.80 15.41 Albin G‐62 T Fritidsmotorskepp SMNU YEMANJA II 4.61 15.41 2 Volvo D‐9 500i, 2007 Fritidsmotorskepp SIMJ ÄLVAN 4.60 15.40 Volvo Penta MD100 Fritidsmotorskepp SHJF SEASONG 4.54 15.39 2 Man V10, 1982 Fritidsmotorskepp SJZP JUVELEN 5.80 15.39 Volvo‐Penta TMD 120 Fritidsmotorskepp SFWN ROSPIGGEN AF STOCKHOLM 4.54 15.35 Volvo Penta MD 100 Fritidsmotorskepp SLXZ KESS 4.96 15.35 Gardner diesel 1965 Fritidsmotorskepp SLGD MARCONY 4.54 15.35 Volvo TMD 96, 1961 Fritidsmotorskepp SFLN MARITA AV SORUNDA 5.71 15.32 Volvo Penta D‐96 1954 Fritidsmotorskepp SHKC MEVIND 6.03 15.32 Skandia Fritidsmotorskepp SKYL VON ARX 4.13 15.30 Volvo MD96 1964 Fritidsmotorskepp SBLZ SUNSET BLVD. 4.47 15.30 2VolvoPenta TAMD122P,96 Fritidsmotorskepp SCLH LASATA 4.59 15.30 2 Volvo TAMD122, 1994 Fritidsmotorskepp SKVU DROTTNING ESTER 4.47 15.30 2 Volvo 122 EDC 1997 Fritidsmotorskepp SJQR LIANA 5.83 15.28 Volvo MD 96 Fritidsmotorskepp SGEP ELLA 5.80 15.27 Caterpillar Fritidsmotorskepp SHFZ ALFEN 4.20 15.25 Volvo‐Penta TMD 96 B1 Fritidsmotorskepp SLWK PRINCESS MISTY 4.38 15.24 2 Volvo Penta TAMD 72 ‐94 Fritidsmotorskepp SDIF PIRI‐PIRI 4.38 15.24 Catepillar 3708, 1994 Fritidsmotorskepp SLOF CHAPTER IV 4.60 15.24 2 VolvoPenta TAMD122D,‐91 Fritidsmotorskepp 179

SGRI DAISY AV KARLSTAD 5.98 15.23 Volvo D 96 1972 Fritidsmotorskepp SGTM KVICK 4.44 15.23 AB Bolinder‐Munktell 1962 Fritidsmotorskepp SCRP CHIVIVA 4.62 15.23 2 Caterpillar 3208 TA Fritidsmotorskepp SEOC BILLY 6.15 15.21 Fritidsmotorskepp SJYN LELIE 4.95 15.21 Volvo Penta TMD 100 1974 Fritidsmotorskepp SHAJ SPLENDID 4.72 15.20 Volvo Penta TAMD31A 1993 Fritidsmotorskepp SDJF KULING 4.06 15.20 Scania D640 1960 Fritidsmotorskepp SFAM LINDA IV LIMHAMN 4.44 15.20 2 Volvo Penta D12 715 EVC, 2006 Fritidsmotorskepp SKVL SHARK AF STOCKHOLM 4.47 15.19 2 Volvo Penta TAMD 122 D Fritidsmotorskepp SKJL DOLLY 5.85 15.19 Volvo‐Penta MD 96 1959 Fritidsmotorskepp SFOV LEIA II 4.30 15.16 2 Volvo D12, 2001 Fritidsmotorskepp SFMU NOBLESS II 4.63 15.15 Volvo Penta MD96B Fritidsmotorskepp SFXN JYLLAND 4.35 15.14 Hundestedt semidiesel Fritidsmotorskepp SBYA ANN‐CHARLOTTE 4.63 15.13 2 Volvo Penta TAMD122 Fritidsmotorskepp SFVY ZENITA AF STOCKHOLM 5.70 15.13 Penta Diesel Fritidsmotorskepp SDXH ZESTFUL 4.38 15.13 2 VolvoPentaTAMD73PEDC,98 Fritidsmotorskepp SGEV DANDY SCOTT 4.38 15.13 2 Volvo Penta TAMD 73P, 1999 Fritidsmotorskepp SENO EBERON 4.63 15.12 GM serie 71 1947 Fritidsmotorskepp SMUW LIVIA 4.95 15.12 Modag 1955 Fritidsmotorskepp SMLV PARAGON 4.18 15.11 Volvo Penta AQAD 41 1986 Fritidsmotorskepp SDKZ SNAPPER 5.86 15.11 Volvo‐Penta MD 96 B Fritidsmotorskepp SBJX ANNA‐SOFIA 4.27 15.10 Mercedes Diesel 1978 Fritidsmotorskepp SCGZ JATEKA 4.47 15.10 2 Volvo Penta TAMD 122 D Fritidsmotorskepp SCHW JASMINE II 4.47 15.10 2 VP TAMD 122D 1990 Fritidsmotorskepp SCLY VERONICA STOCKHOLM 4.47 15.10 2 Volvo Penta 1992 Fritidsmotorskepp SGAE ROYAL GRACE 4.47 15.10 2 MAN D2840 LX V10 1993 Fritidsmotorskepp SCVZ ALBATROSS AF RATAN 4.88 15.10 Scania D11 1970 Fritidsmotorskepp SGXD LASTRINA 4.47 15.10 2 Volvo Penta TAMD 122D Fritidsmotorskepp SHCT MARKISINNAN AF SJUHALLA 4.47 15.10 2 MAN V10, 1991/92 Fritidsmotorskepp 180

SMCA PAPILLON AF SKÄRHAMN 4.60 15.08 2 VolvoPentaTAMD71A, 1988 Fritidsmotorskepp SKDI GREY LADY 4.60 15.08 2 Volvo Penta TAMD71 1987 Fritidsmotorskepp SKWY MADONNA 4.92 15.07 Volvo D47B, F82 1960/1967 Fritidsmotorskepp SEBW REANA 5.04 15.06 Volvo Penta 6 cyl 1962 Fritidsmotorskepp SJHR CLARA STENUNGSUND 4.60 15.06 2 Volvo Penta TAMD 122D Fritidsmotorskepp SCDX JUST THE BUSINESS 4.60 15.06 2Volvo Penta TAMD 71A,‐88 Fritidsmotorskepp SMKV HOT ICE 4.60 15.06 2VolvoPenta TAMD122D,‐90 Fritidsmotorskepp SJIN FANNY 4.24 15.03 Volvo Penta TMD96B1 Fritidsmotorskepp SCIE ONDINA 4.58 15.01 2 Volvo TAMD 71 B 1991 Fritidsmotorskepp SJHY FISKMÅSEN SMÖGEN 5.77 15.00 Penta MDF6 Fritidsmotorskepp SDIE KTHANGA 5.98 14.99 Ford Marin 2715 E 1976 Fritidsmotorskepp SCHZ ÖSTERÖ 4.80 14.99 Volvo‐Penta TAMD 120 Fritidsmotorskepp SCMN SHEHERAZADE 4.30 14.99 2 Volvo Penta TAMD 71 Fritidsmotorskepp SFDP KRISTINA AF VÅRBY 4.65 14.99 2 Caterpillar 3208, 1986 Fritidsmotorskepp SLER SPICE TOO 4.53 14.98 2 Volvo D2‐55 c, 2005 Fritidsmotorskepp SLAY MAGDA 5.55 14.97 Säffle 227 FV 1962 Fritidsmotorskepp SJHN EURICA 5.58 14.94 Albin G‐01 1964 Fritidsmotorskepp SCBZ QUEEN OF SHEEBA 4.40 14.94 2 Volvo Penta D12‐715, 2008 Fritidsmotorskepp SMIA MISS SOPHIE 4.36 14.93 2 Caterpillar Diesel,1990 Fritidsmotorskepp SCNK LA PETITE II 4.55 14.92 2 Volvo Penta TAMD 718 Fritidsmotorskepp SCIG CHOISIE 4.55 14.92 2 Volvo TAMD71B 1991 Fritidsmotorskepp SFUM PAX 4.63 14.91 Fritidsmotorskepp SDQB GUN 5.43 14.91 Scania D 11 Fritidsmotorskepp SMHJ SJÖGREI 5.30 14.88 Scania DIO RO1 1965 Fritidsmotorskepp SEUA LA MER 4.60 14.84 Ford 380 1974 Fritidsmotorskepp SEPX BLUE O WHITE 4.63 14.83 GM‐diesel 3 cyl Fritidsmotorskepp SLEZ MYKA 4.47 14.83 Volvo DP‐575, 2005 Fritidsmotorskepp SHMG SIRU‐AVE 4.47 14.83 2 Volvo D12‐675, 2005 Fritidsmotorskepp SFRV MOONLIGHT II 4.47 14.83 2VolvoPentaTAMD74, 2002 Fritidsmotorskepp 181

SGUQ SUNNY 4.47 14.83 2 Volvo Penta D12, 2004 Fritidsmotorskepp SJWL PRINCESS OF LAGOON 4.47 14.83 2 Volvo TAMD 74P EDC,2002 Fritidsmotorskepp SLHI XANTIPPA 4.47 14.83 2 Volvo D12, 2002 Fritidsmotorskepp SMTD ALL TINA 4.47 14.83 2 VolvoPentaD12 675, 2004 Fritidsmotorskepp SLNM JOOS 4.45 14.81 Fritidsmotorskepp SEHW UTE 4.22 14.80 2 Volvo 72A, 1992 Fritidsmotorskepp SCJP AQUILA 4.72 14.80 2 Caterpillar 1989 Fritidsmotorskepp SDBM MARY AV GÖTEBORG 4.51 14.79 Bolinder 1959 Fritidsmotorskepp SJWF AGDA 5.96 14.79 Bolinder‐Munktell 1936 Fritidsmotorskepp SGRD HEIMDAL 4.83 14.76 Volvo Penta TMD96B1 1968 Fritidsmotorskepp SDWP VIRGINIA 5.90 14.76 Skania diesel 1961 Fritidsmotorskepp SEUT ARIANA 4.50 14.75 2 Caterpillar 3208 TAS Fritidsmotorskepp SKBP GABRIELLE 4.71 14.75 2 Caterpillar 3208Ti 1989 Fritidsmotorskepp SKGL FRAMÅT 5.52 14.73 Albin diesel G 62 TK 1962 Fritidsmotorskepp SMBI AMICA 4.22 14.71 2 Cummins VT 903, 1985 Fritidsmotorskepp SIBV FAR NIENTE 4.24 14.70 2 MTU 6R 183 TE93, 1997 Fritidsmotorskepp SBKR OCTOPUSSY 4.54 14.69 2 Volvo Penta TAMD71 Fritidsmotorskepp SDMJ BANCO 5.65 14.67 June Munktell Fritidsmotorskepp SKJB ESTER 5.80 14.66 Scania‐Vabis D‐644 Fritidsmotorskepp SHUL LAGUN AV LULEÅ 4.65 14.64 Scania DS11, 1982 Fritidsmotorskepp SGRW JUDIT 5.83 14.61 Scania Vabis DSI 11, 1978 Fritidsmotorskepp SEWC BELE 5.77 14.61 Caterpillar Fritidsmotorskepp SCXY FJORD 4.90 14.61 Volvo TAMD120B, 1965 Fritidsmotorskepp SIWL LA GITT 5.56 14.58 Fritidsmotorskepp SFON WESTVIND AF GÖTEBORG 5.64 14.58 Volvo‐Penta MD 100, 1970 Fritidsmotorskepp SLGQ BEMA 4.36 14.55 2 Volvo Penta KAD75,‐04 Fritidsmotorskepp SLFK CYTHERA 4.36 14.55 2 VolvoPenta TAMD75,2004 Fritidsmotorskepp SHUW VIRGO II 5.85 14.54 Fritidsmotorskepp SLZK JIROCA 4.66 14.52 2 Volvo Penta TAMD 71 Fritidsmotorskepp 182

SBDJ MISSLOPER 4.02 14.47 2 Volvo TAMD 75, 2003 Fritidsmotorskepp SJDW FREEDOM OF VÄRMDÖ 4.38 14.47 2VolvoPentaTAMD72PEDC,96 Fritidsmotorskepp SLNA SOL Y MAR 4.47 14.47 2 Volvo TAMD122, 1994 Fritidsmotorskepp SLNW MIDNIGHT SUN 4.47 14.47 Volvo 122D, 1996 Fritidsmotorskepp SBWY ARION 4.91 14.45 2 Volvo 122 TAD 1990 Fritidsmotorskepp SDUT DINA AF SOLVIK 5.55 14.45 Albin G 41 1962 Fritidsmotorskepp SKRN FÅGELN 5.60 14.45 Albin G‐61 1961 Fritidsmotorskepp SEJB ANELIDA 4.64 14.42 2 Ford Marine NG 4 1966 Fritidsmotorskepp SGDI LISS 4.63 14.41 Volvo Penta MD 96 B Fritidsmotorskepp SJGN REGINA 4.26 14.41 Scania D 814 1958 Fritidsmotorskepp SHXV MONTANA 5.70 14.40 Fritidsmotorskepp SDEB QUARTETTO 4.30 14.40 2 Cummins 6BTAS 9‐MI Fritidsmotorskepp SCLZ KERSTIN HALMSTAD 4.49 14.37 Fritidsmotorskepp SCRW MERLION 4.54 14.37 Twin Caterpillar 3208T Fritidsmotorskepp SDEF SEA LADY 4.05 14.36 2 John Deere 6404DF 1980 Fritidsmotorskepp SHPC VÄSTKUSTEN 5.33 14.36 Säffle 322 Fv Fritidsmotorskepp SHOG RUNE 4.92 14.35 Volvo Penta MD67A 1950 Fritidsmotorskepp SINK HANNAH AF KARLSHILL 4.02 14.35 2 Volvo D9 575 EVC, 2006 Fritidsmotorskepp SGAC VÅGASKÄR 4.02 14.35 2 Volvo D9, 2007 Fritidsmotorskepp SHKI CAPTAIN TOM CORLEY 4.31 14.35 2 Cummins 6BTA5.9‐M2, 1994 Fritidsmotorskepp SHGA SANS SAIL 4.50 14.35 2 Caterpillar 3208 TA, 1988 Fritidsmotorskepp SKNO SUSPICIOUS 4.35 14.34 Caterpillar SB, 1990 Fritidsmotorskepp SBMV SURPRISE 4.35 14.34 2 Caterpillar 3208,‐90 Fritidsmotorskepp SEPV BLÅVALEN 4.76 14.34 Penta 6cyl diesel 1967 Fritidsmotorskepp SDLZ UNITED DREAM 4.35 14.32 2 Cummins 3208, 1990 Fritidsmotorskepp SBUJ LADY KERI 4.27 14.32 2 Caterpillar 3116, 1996 Fritidsmotorskepp SFHL VIRGO 5.33 14.31 Penta Fritidsmotorskepp HELGOLAND AF SJXI HUMMELVIK 5.56 14.31 Säffle, 1921 Fritidsmotorskepp 183

SHQI TIARA 4.47 14.28 Fritidsmotorskepp SJTZ DYKBÅT 1309 4.25 14.28 Volvo MD 70 C, 1985 Fritidsmotorskepp SHNE SANDÖ AF STOCKHOLM 5.58 14.27 Scania D 624 Fritidsmotorskepp SEGI CONTESSA 4.63 14.26 2 st Scania DS I 11 Fritidsmotorskepp SBUH RAMI 4.75 14.25 Volvo TMD100 Fritidsmotorskepp SJQA SAWAN 4.22 14.25 2 Volvo TAMD 73P, 1998 Fritidsmotorskepp SJGD TRULSA 4.22 14.25 2 Volvo Penta TAMD EDC 98 Fritidsmotorskepp SEYT ANGI 4.22 14.25 2 VP TAMD73 PEDC, 1999 Fritidsmotorskepp SGRT STRÖMMING 4.80 14.25 2 Cummins QSC83, 2008 Fritidsmotorskepp SHVA JENNA 4.22 14.25 2 Volvo Penta TAMD73,1999 Fritidsmotorskepp SMDG SEA STAR 4.65 14.24 Scania DS11 1977 Fritidsmotorskepp SMTJ MARIMA 4.28 14.21 2 Scania DS 11R 80 Fritidsmotorskepp SMKL COMPASS ROSE 4.40 14.20 2 Volvo Penta TMD 70AB Fritidsmotorskepp SLEQ SIC 4.20 14.20 Volvo Penta MD 70 B Fritidsmotorskepp SFTD LINA 4.68 14.20 Normo T 2‐8017 1960 Fritidsmotorskepp SHKB EMILY AF MUSKÖ 4.96 14.20 Scania Vabis Fritidsmotorskepp SJMX SEACEROON 4.50 14.19 2 st SABRE FH 420 1979 Fritidsmotorskepp SJWK CINDY 4.14 14.18 Volvo Penta Fritidsmotorskepp SCPI JALIBA 4.29 14.18 Yanmar 4JH3‐HTE, 2002 Fritidsmotorskepp SFIN LORELEI II 4.07 14.17 2 Scania D634/D645 Fritidsmotorskepp SJHC MISS PATRICIA 4.40 14.14 2 st GM 8 V 71 TI Fritidsmotorskepp SEDR KRAKA AF GRÄNNA 4.20 14.14 2 Volvo TAMD 74, 2001 Fritidsmotorskepp SGJK WILMA OF SWEDEN 4.40 14.14 2 Detroit Diesel GM8V71T1 Fritidsmotorskepp SHZQ FRANSESCA 4.20 14.14 2 Volvo Penta TAMD74,2001 Fritidsmotorskepp SBZF INDRA 4.04 14.12 2 Caterpillar 3208TA Fritidsmotorskepp SKCO MY WAY 4.79 14.11 Scania D10R80 1963 Fritidsmotorskepp SCQY GREAT ESCAPE 4.27 14.11 2 Volvo TAMD, 2001 Fritidsmotorskepp SFIY GISELLE 4.14 14.10 2 VolvoPentaTAMD74PEDC,01 Fritidsmotorskepp SIKH CATHARINA II 4.64 14.10 2 MAN D 2566 MTE, 1977 Fritidsmotorskepp 184

SHIE MAJA 5.68 14.10 Fritidsmotorskepp SMPC GRIPEN AF SÖDERTÖRN 4.88 14.09 Scania DS11 1976 Fritidsmotorskepp SBAJ RATZEPUTS 4.36 14.08 2 Caterpillar 3208TA 1989 Fritidsmotorskepp SJYG HELFRID 5.60 14.08 Perkins V8 51OM, 1980 Fritidsmotorskepp SIEH TAPASYA 4.42 14.07 2 Caterpillar 3116TA 1995 Fritidsmotorskepp SHUM VIKING 5.65 14.06 Fritidsmotorskepp SDQZ LISÖ 5.69 14.05 Volvo TD 96 1967 Fritidsmotorskepp SBQG MECA V 4.47 14.05 Volvo Penta TAMD 122 1990 Fritidsmotorskepp SBKH VIA NOVA 4.47 14.05 2 Volvo TAMD71A 1988 Fritidsmotorskepp SBDL DUCHESSE 4.47 14.05 2 Volvo Penta TAMD 122 Fritidsmotorskepp SMAJ MIRAMAR 4.47 14.05 2 Volvo‐Penta TAMD 71A Fritidsmotorskepp SJPY MAINSTAR 4.60 14.05 2 Volvo 122C, 1989 Fritidsmotorskepp SJYD BROSUN 4.18 14.05 2st VolvoPenta TAMD74PEDC Fritidsmotorskepp SBIV LA STRAVAGANZA 4.18 14.05 2 Volvo Penta 74P‐EDC,03 Fritidsmotorskepp SMBR ZIGLET 4.34 14.03 2 Cummins VT8 1973 Fritidsmotorskepp SIKP WILMA 5.80 14.03 Fritidsmotorskepp SLXR DOLLYETTE 5.94 14.02 Scania Vabis DS 10 1961 Fritidsmotorskepp SBNG RIVIERA AF LIDINGÖ 4.27 14.02 2 Caterpillar 3208TA 1989 Fritidsmotorskepp SMEJ DUNDRET 4.32 14.02 2 Volvo TAMD 74p EDC 2000 Fritidsmotorskepp SIQW JOSEPHINE AV HÅTÖ 4.32 14.02 2 x Volvo TAMD74PEDC 2002 Fritidsmotorskepp SFWX BRILLIANT 4.32 14.02 2 Volvo TAMD 74,2001 Fritidsmotorskepp SGKU BARBARA J 4.32 14.02 2 Ford Sabre 6D380, 1980 Fritidsmotorskepp SJZK PHANTOM 46 4.32 14.02 2 Volvo TAMD75P, 2005 Fritidsmotorskepp SIDH NATALIE 4.24 14.00 2 x Cummins, 1996 Fritidsmotorskepp SCUY SVARTKLUBBEN 4.46 14.00 Volvo TMD 120A, 1977 Fritidsmotorskepp SFMW BEATRICE 4.34 14.00 Bedford 330, 1977 Fritidsmotorskepp SHEB RAPALLO 4.24 14.00 2 Caterpillar 3208, 1989 Fritidsmotorskepp SLDR BRITT‐G 4.50 14.00 2 Perkins T 6 354M 1978 Fritidsmotorskepp SGYB LILIAN 4.11 14.00 Ford Tempest diesel Fritidsmotorskepp 185

SLKG MÄRTA 5.85 14.00 Volvo Penta diesel 1972 Fritidsmotorskepp SJIY FERDINAND 4.31 13.99 Säffle 217 BF 1958 Fritidsmotorskepp SLFW LA RITA 4.50 13.99 Caterpillar 3208 1983 Fritidsmotorskepp SMIY BISCAYA AV VINDALSÖ 4.10 13.99 Volvo Penta MD21A, 1978 Fritidsmotorskepp SJIL NIO 5.84 13.98 June‐Munktell Fritidsmotorskepp SMIV ARIANA AV EKERÖ 4.37 13.96 2 Volvo TAMD 71 Fritidsmotorskepp SEJU MISH MASH 4.18 13.95 2 Volvo Penta TAMD 1988 Fritidsmotorskepp SHDY ZENOBIA 5.65 13.95 Volvo‐Penta TAMD70B 1975 Fritidsmotorskepp SDVL VALE 5.60 13.94 Volvo turbodiesel Fritidsmotorskepp SFKR LISELOTT 5.43 13.91 Volvo Penta MD 96 1963 Fritidsmotorskepp SGLT ORCA AF LIMHAMN 4.42 13.91 2 Detroit Dies 4‐53N, ‐77 Fritidsmotorskepp ALBATROSS AV SGAD KÖPMANHOLMEN 4.90 13.90 Volvo TMD 96, 1972 Fritidsmotorskepp SDTZ SAGA 4.76 13.89 Volvo Penta MD96 1961 Fritidsmotorskepp SHQW SVEALAND AF STOCKHOLM 5.24 13.89 Scania Vabis D 10, 1964 Fritidsmotorskepp SFVO LA PALOMA 4.32 13.84 Fritidsmotorskepp SLPQ PASSION TWO III 4.35 13.84 2 Caterpillar 3126 TA,96 Fritidsmotorskepp SHPE SO‐LONG II 5.60 13.82 Fritidsmotorskepp SLAO ERICA 4.24 13.82 Detroit Diesel LD 1967 Fritidsmotorskepp SGIR TWINS CREW 4.55 13.82 2 Hino US Marine Diesel Fritidsmotorskepp SMLB MADAM AF PITEÅ 4.55 13.82 US Marine diesel 1987 Fritidsmotorskepp SBNJ JENNIE II AF GREBBESTAD 4.55 13.82 2 HINO EN700 1985 Fritidsmotorskepp SBRN NANO 4.55 13.82 2 Hino 6‐393TJ 1988 Fritidsmotorskepp SHOE LADY CHRISTINA 4.22 13.81 2 Volvo TAMD72P EDC, 1997 Fritidsmotorskepp SMOA CARPE DIEM II 4.22 13.81 2 Volvo TAMD 74, 2005 Fritidsmotorskepp SFRO GLAMOUR 4.22 13.81 2 Volvo TAMD 72 P, 1995 Fritidsmotorskepp SBOW TROUBLE‐SHOOTER 4.22 13.81 2 Volvo TAMD 72,1997 Fritidsmotorskepp SBNZ MISS FLEXI 4.22 13.81 2VolvoPentaTAMD72EDC,‐96 Fritidsmotorskepp SKMP CHOJAMARU III 4.14 13.78 2 st Scania, 1999 Fritidsmotorskepp 186

SLDO GILDA VI 4.14 13.78 2 Scania D19 59M, 2000 Fritidsmotorskepp SBWI EMOS 4.14 13.78 2 Scania D19, 1999 Fritidsmotorskepp SIFJ YVONNE 4.27 13.77 2 Cummins 6BTA5.9, 2005 Fritidsmotorskepp SHQE ELINOR V 4.12 13.75 2 Volvo Penta TAMD 63P Fritidsmotorskepp SIFU ADELE AV SALTSJÖBADEN 4.22 13.75 2 Volvo Penta TAMD72 1994 Fritidsmotorskepp SCFQ GRETAS TORP 4.55 13.73 2 Marine EH700 1989 Fritidsmotorskepp SLCP Q‐RAGE 4.55 13.73 2 Heino, 1989 Fritidsmotorskepp SHTD SCORPION 4.55 13.73 2 Hino, 1987 Fritidsmotorskepp SCNU SCANDINAVIAN QUEEN 4.55 13.73 2 HINO, 1994 Fritidsmotorskepp SBPL COXTOLSTOJ 4.34 13.72 2 Caterpillar 1990 Fritidsmotorskepp SDMX LIZZIE AV DONSÖ 5.87 13.72 Scania Vabis diesel 1972 Fritidsmotorskepp SKNT ERLY 5.55 13.70 Fritidsmotorskepp SBKN THE QUEEN OF OAXEN 4.30 13.68 2 Volvo Penta TAMD71 1989 Fritidsmotorskepp SMDH NOX 4.68 13.68 2 Caterpillar 3208 1987 Fritidsmotorskepp SCEV KOSTER EXPRESS 4.33 13.68 2 Volvo 70E, 1986 Fritidsmotorskepp SIKL ERIANHE 4.05 13.67 Volvo D2‐55, 2004 Fritidsmotorskepp SHOZ FALKVÅG 4.84 13.67 Volvo Penta TAMD 121 C,1987 Fritidsmotorskepp SLRV HANNA 4.12 13.65 2 Volvo‐Penta TMD‐40 Fritidsmotorskepp SCVA AEOLUS 4.26 13.65 2 Volvo MD 70, 1973 Fritidsmotorskepp SCJO EVELINE 4.19 13.64 Volvo D2‐55, 2002 Fritidsmotorskepp SJQX RIVALEN 4.15 13.63 2 Cummins 1976 Fritidsmotorskepp SFKC MAYA PIRAYA 4.32 13.62 2 Caterpillar V8 1995 Fritidsmotorskepp SIPO SANTO DOMINGO 4.30 13.60 2 Caterpillar 3208, 1990 Fritidsmotorskepp SGCO POSIDONKEN 4.68 13.60 Ford 2704ET 1981 Fritidsmotorskepp SLWX PRINCESS LIZYMAR 4.30 13.60 2 Volvo TAMD 70 E 1986 Fritidsmotorskepp SBQA MOONLIGHT 4.30 13.60 2 Caterpillar 1990 Fritidsmotorskepp SMDY PIRR V 4.30 13.60 2 Volvo Penta TAMD70 1985 Fritidsmotorskepp LA DOLCE VITA AF SEQT ÖSTERÅKER 4.30 13.60 2 Volvo Penta TAMD 71 Fritidsmotorskepp 187

SMKF SOPHIA AF VIDEBERG 4.36 13.59 Volvo TMD 100 1971 Fritidsmotorskepp SEAK MISS ELLE 4.22 13.59 2 Caterpillar 3208, 1998 Fritidsmotorskepp SMBL LADY BLISS 4.04 13.58 2 Volvo TAMD 60 Fritidsmotorskepp SIYU CAVA 4.30 13.58 2 Volvo 71A, 1988 Fritidsmotorskepp SCBI SASCHA 4.30 13.58 2Caterpillar 3208,1990/95 Fritidsmotorskepp SGFZ SAFIR AF KÖPING 4.33 13.58 2 Volvo Penta TAMD 70 Fritidsmotorskepp SLEW MARIANNA III 4.30 13.58 2 Caterpillar 3208,1990 Fritidsmotorskepp SDJE JUMOTI 4.30 13.58 2 Volvo TAMD71A,1988 Fritidsmotorskepp SLOH PITZY DEE 4.30 13.58 2 Volvo, 1984 Fritidsmotorskepp SCEW DREAM OF THE SUN 4.30 13.58 2 Volvo TAMD71A, 1987 Fritidsmotorskepp SJIV MIDAH 4.30 13.58 2 Volvo TAMD 61 A, 1988 Fritidsmotorskepp SDUV SALADAENG 4.04 13.58 2 Volvo TAMD 71B, 1990 Fritidsmotorskepp SMFO QUINNA OF SWEDEN 4.30 13.58 Volvo Penta TAMD 70E 1986 Fritidsmotorskepp SLZM MISTRESS 4.30 13.58 2 Volvo Penta TAMD71A Fritidsmotorskepp SMAK BLUE HEAVEN 4.30 13.58 Volvo Penta TAMD61 1987 Fritidsmotorskepp SLIG JAZZ III 4.30 13.58 2 Volvo Penta TAMD70E,‐85 Fritidsmotorskepp SCMZ INDUS 4.52 13.58 Volvo Penta TMD96 1957 Fritidsmotorskepp SBVJ PACIFIQUE 4.30 13.58 Caterpillar 1990 Fritidsmotorskepp SBWG CARPE DIEM AF LOMMA 4.30 13.58 2 Volvo‐Penta TMD70C 1982 Fritidsmotorskepp SENT CAPRICE AF HÖGANÄS 4.04 13.58 2 Volvo TAMD61 1990 Fritidsmotorskepp SLAR CELINE AF TROSA 4.30 13.58 2 Volvo Penta TAMD 70E Fritidsmotorskepp SFJC SELENE 4.07 13.57 Ford E 2715 1978 Fritidsmotorskepp SKBR BLUE BIRD 5.08 13.55 Scania D 10R80 1961 Fritidsmotorskepp SBOQ VITANA 5.35 13.55 Volvo Penta MD47 1955 Fritidsmotorskepp SEAD AJA II 4.96 13.54 Volvo Penta MD 96 1957 Fritidsmotorskepp SCGV SAYONARA CAPRI 4.54 13.53 2 Detroit Diesel, 1982 Fritidsmotorskepp SDRC LÄRKAN 5.45 13.51 Volvo Penta Fritidsmotorskepp SDFG ALBATROSS 5.56 13.51 Bolinder‐Munktell Fritidsmotorskepp SDWB LILL SNURK 5.61 13.50 Fritidsmotorskepp 188

SCQF BALDERSON 7.43 13.50 2Volvo AQD70B/750,1973 Fritidsmotorskepp SBLJ CUCUSINA 4.20 13.50 2 Volvo TAMD 74 Fritidsmotorskepp SKLA NINTI 4.44 13.48 Scania 6 cyl diesel 1949 Fritidsmotorskepp SMFG PORFIN 4.40 13.46 2 Caterpillar 3208,1996 Fritidsmotorskepp SMWD OTIUM 4.35 13.44 2 Ford Lehman, 1980 Fritidsmotorskepp SFQZ WINDY 5.60 13.44 Albin G‐62TH 1960 Fritidsmotorskepp SGFR ANNE LETH 5.55 13.44 Volvo Penta diesel 1964 Fritidsmotorskepp SELZ ANNIE AF GÖTEBORG 5.32 13.43 Volvo Penta TMD 96 1963 Fritidsmotorskepp SJWZ BONITA 4.12 13.42 Skandia 1cyl semidiesel Fritidsmotorskepp SDXF KAMALA II 4.60 13.42 2 Volvo TAMD 70 C, 1976 Fritidsmotorskepp SBWF SAX II 4.42 13.42 2 Cummins, 1978 Fritidsmotorskepp SGJE MERKUR 4.70 13.40 Scania Vabis D 622 Fritidsmotorskepp SIBG SOLITUDE 4.37 13.40 2 Caterpillar 3208 1988 Fritidsmotorskepp SDTX RITA 5.22 13.36 Detroit‐Allison 71 1970 Fritidsmotorskepp SDOJ ULLA‐BRITTA 5.50 13.35 Volvo Penta TMD 96B Fritidsmotorskepp SHFE FRIDA AV SKÅNE 4.94 13.33 Volvo Penta MD 70A 1970 Fritidsmotorskepp SHJM NEPTUN 5.30 13.32 Fritidsmotorskepp SLBY ANTARES 4.27 13.32 2 Caterpillar 3208 1993 Fritidsmotorskepp SEMR TABASCO 4.07 13.31 2 Iveco M14.01, 1995 Fritidsmotorskepp SGNQ MUSTIQUE 4.27 13.28 2 Cat 3208,1991 Fritidsmotorskepp SMIK CREAM 4.27 13.27 2 Volvo TAMD 74P, 2000 Fritidsmotorskepp SGRA MAGNIFIQUE AF KULLAVIK 4.27 13.27 2X VolvoPentaTamd74P,‐02 Fritidsmotorskepp SMCL NORDIC CROWN 4.27 13.27 2 Volvo D9‐500, 2007 Fritidsmotorskepp SBHU POEM 4.27 13.27 2 Volvo D9‐500, 2007 Fritidsmotorskepp SDPX FOR FEELING 4.27 13.27 2 Volvo Penta D9‐500, 2006 Fritidsmotorskepp SHFG BELLA AF CARLSTAD 4.27 13.27 2 Volvo Penta D9, 2005 Fritidsmotorskepp SBJT DUNDERKLUMPEN 4.80 13.26 2 Caterpillar C12, 2007 Fritidsmotorskepp SFRB INGEBORG AF ÅKERSBERGA 4.67 13.26 Albin 43 Fritidsmotorskepp SBKE TYKO 4.88 13.23 Volvo Penta TAMD 70 Fritidsmotorskepp 189

SGCE ELINA 4.12 13.22 Perkins 4,236, 1985 Fritidsmotorskepp SEJA SUSETTE 4.09 13.20 Perkins 4108M Fritidsmotorskepp SJZF GRILL 5.50 13.20 Scania‐Vabis 6‐cyl 1966 Fritidsmotorskepp SLWI ATHENA AF SVINNINGE 4.44 13.20 2 Mercedes WM 240, 1976 Fritidsmotorskepp SFNK AVENTURA 4.44 13.20 2 Hino, 1991 Fritidsmotorskepp SLBH LABARRACA 4.14 13.19 2 Scania D 19M, 1999 Fritidsmotorskepp SJME JOHANNA AF STOCKHOLM 4.14 13.19 2 Scania DSI 9,1999 Fritidsmotorskepp SDAN SCOTS N WATER 4.29 13.19 2 Caterpillar 3208, 1977 Fritidsmotorskepp SHEQ KATTY 5.02 13.19 Scania D11 1979 Fritidsmotorskepp SJGL LILLA JUNGFRUN 5.55 13.18 Skandia 1935 Fritidsmotorskepp SMIF AMPHION 4.11 13.18 Volvo MD 70B 1976 Fritidsmotorskepp SJYZ SEA CAT 4.12 13.16 Ford MD 2715E 1980 Fritidsmotorskepp SJLY LOLA AF VINDÖN 4.20 13.16 Volvo Penta TAMD 73 P‐ED, 1999 Fritidsmotorskepp SLKT REFLECTION 4.12 13.16 2 Scania DSI 9, 2000 Fritidsmotorskepp SLKN CARUSO CARLSCRONA 4.14 13.15 2 Scania DI9, 1999 Fritidsmotorskepp SGWA DIAMOND 4.14 13.15 2 Caterpillar 3126 1997 Fritidsmotorskepp SIJN CAMURUS 4.14 13.15 2 Volvo Penta TAMD73P‐EDC Fritidsmotorskepp SLQI MY SUPPORT 2 4.14 13.15 Scania D19 59M, 2000 Fritidsmotorskepp SDYE DEWLISH 4.14 13.15 2 Scania DI 9, 1999 Fritidsmotorskepp SLYC HILDA ROSS 4.01 13.15 Ford 6 cyl diesel Fritidsmotorskepp SIAQ ETHEL 4.14 13.15 2 Volvo Penta TAMD 63P Fritidsmotorskepp SBRK CIRRUS 4.34 13.15 2 Caterpillar 3208TA 1989 Fritidsmotorskepp SCFZ CICI LA VIE 4.47 13.12 Volvo Penta TAMD70 1973 Fritidsmotorskepp SBQJ USCHI 4.47 13.12 Volvo Penta TAMD 706 Fritidsmotorskepp SEDW FRIDOLF 4.60 13.12 Lister Marin 35 JK 6ME9 Fritidsmotorskepp SDVJ TÖSEN 4.94 13.12 Volvo Penta MD 100B, 1973 Fritidsmotorskepp SKTJ INVERNESS CREAM 4.12 13.11 2 Sabre 300 typ 2581 1979 Fritidsmotorskepp SDCX MYTOY 4.20 13.11 2 st Volvo TAMD 72 1995 Fritidsmotorskepp SJVY ANDANTE 4.25 13.11 2 Volvo 61 A, 1988 Fritidsmotorskepp 190

SCJA ENEDINA 4.28 13.10 2 Volvo TAMD 61A 1990 Fritidsmotorskepp SBYC SUNQUEST 4.28 13.10 Volvo TAMD 61 1989 Fritidsmotorskepp SBGV DOLLAR 4.30 13.09 2 Detroit 8V‐92TI 1987 Fritidsmotorskepp SBLR LADY ARIADNE 4.12 13.08 2 Caterpillar 3208 1989 Fritidsmotorskepp SJBA SEA QUEEN II 4.14 13.08 2 Scania DSI 9 1998 Fritidsmotorskepp SJBG JOSEFINA IV 4.14 13.08 2 Volvo TAMD 73P‐EDC 1998 Fritidsmotorskepp SJBD LADY SUN 4.14 13.08 2 Scania DSI 9, 1998 Fritidsmotorskepp SLDT SJÖLILJAN 4.14 13.08 2 Scania D19 59M Fritidsmotorskepp SBFL LOUISE TROLLHÄTTAN 4.70 13.06 2 Caterpillar 3208 1988 Fritidsmotorskepp SFNM MASKEN AF TYRESÖ 5.03 13.05 Skandiaverken 1945 Fritidsmotorskepp SKEM MILLIS 4.17 13.05 2 Volvo Penta TAMD63P,‐99 Fritidsmotorskepp SKMW LUCKY LEON 4.17 13.05 2 Volvo 73P 1998 Fritidsmotorskepp SFKB NAJA 4.36 13.05 2 Volvo TAMD 70C, 1975 Fritidsmotorskepp SBJV PETILLANT 4.17 13.05 2VolvoPentaTAMD63P,1998 Fritidsmotorskepp SEOA MY DREAM 4.17 13.05 2 Volvo TAMD 63P, 1999 Fritidsmotorskepp SLRZ KAMA II 4.36 13.05 2 Volvo TAMD 70, 1973 Fritidsmotorskepp SCEQ PARADISA 4.20 13.03 2 Volvo TAMD 71, 1989 Fritidsmotorskepp SKMY CATCHA 4.20 13.03 2 Volvo TAMD72 1994 Fritidsmotorskepp SFIL ELITE 4.20 13.03 2 Volvo Penta TAMD 71, 1988 Fritidsmotorskepp SPIDER NERO AV SIJF STOCKHOLM 4.11 13.03 2 Volvo IPS, 2006 Fritidsmotorskepp SJZH LADY DIANE 4.20 13.03 2 Volvo 75 P Fritidsmotorskepp SBJR ESTRELLITA 4.25 13.03 2 Ford Lehman 2715E, 1974 Fritidsmotorskepp SMJF KARMA 4.25 13.03 2 Volvo Penta TAMD 1983 Fritidsmotorskepp SLQW SHA‐SHA III 4.25 13.03 2 Ford 1970 Fritidsmotorskepp SCJM SUNDANCE 4.05 13.03 2 John Deere Ammarine 404 Fritidsmotorskepp SIBO MICRO LAMBDA 4.20 13.03 2 Volvo Tamd 72P EDC1997 Fritidsmotorskepp SHDQ ELIN 5.10 13.02 Skandia 255 1954 Fritidsmotorskepp SLHD LADY CORNER 4.06 13.02 2 Scania DSI9,1999 Fritidsmotorskepp 191

SIPW PRINCESS EMELIE 4.01 13.01 Volvo Penta TAMD120A 1980 Fritidsmotorskepp SGQE PRINCESS OF SIGTUNA 4.14 13.00 2 Volvo TAMD 74 L, 2004 Fritidsmotorskepp SGPY CHABLIS AF GEFLE 4.14 13.00 2 Volvo TAMD 74L, 2005 Fritidsmotorskepp SHUI SUMMERTIME 4.14 13.00 2 Volvo TAMD 74L, 2005 Fritidsmotorskepp SJUN VICTORY 4.14 13.00 2 Volvo TAMD 75P, 2006 Fritidsmotorskepp SKZW EKAN III 4.14 13.00 2 Volvo TAMD 75P, 2006 Fritidsmotorskepp SCLX ALVA 4.14 13.00 2 Volvo D6 435, 2008 Fritidsmotorskepp SBGY BIRDIE 4.14 13.00 2 Volvo D6‐435, 2007 Fritidsmotorskepp SGUV EZ2 SEA 4.14 13.00 2 Volvo D6‐435 Fritidsmotorskepp SCMO SMILLA AF BROMMA 4.14 13.00 2 Volvo D6‐435, 2008 Fritidsmotorskepp SGTB NO HURRY 4.48 12.99 2 Caterpillar 3208, 2000 Fritidsmotorskepp SGFA MUM'S 4.16 12.99 2 Caterpillar 385CV, 1998 Fritidsmotorskepp SFRJ CONTENTEZZA 4.16 12.99 2 Caterpillar 3126‐385 Fritidsmotorskepp SEVG SUN AF STOCKHOLM 4.16 12.99 2 Caterpillar 3126‐385,01 Fritidsmotorskepp SMTE FRANCE 4.16 12.99 2 Caterp. M3126DITA, 1999 Fritidsmotorskepp SJDO TAYANA 4.23 12.98 2 Ford Lehman, 1987 Fritidsmotorskepp SMLW ESMERALDA II 4.22 12.98 2 Caterpillar 3208NA 1991 Fritidsmotorskepp SFGW PLEASURE 4.21 12.98 2VolvoTAMD74L EDC,2004 Fritidsmotorskepp SKFW SHERIDAN 4.21 12.98 2 Volvo D6‐435, 2007 Fritidsmotorskepp SCIV SEALINA AF RESARÖ 4.21 12.98 Fritidsmotorskepp SHRG SÄLEN 4.83 12.98 Volvo Penta MD96B 1962 Fritidsmotorskepp SGNY JAJA 4.21 12.97 2Volvo Penta TAMD 71B ‐91 Fritidsmotorskepp SMXL SMULAN AV SVARTSJÖ 4.21 12.97 Volvo TAMD 71, 1989 Fritidsmotorskepp SBRI MAGDALENA 4.29 12.96 2 Cummins diesel Fritidsmotorskepp SLHM MISS BEHAVEN 4.06 12.95 2 Volvo TAMD 60B 1983 Fritidsmotorskepp SGYP CHAPMAN AF STOCKHOLM 5.05 12.95 Albin diesel Fritidsmotorskepp SHDO ALEXANDRA AF FALSTERBO 4.28 12.95 2 Volvo Penta IPS 500, 2007 Fritidsmotorskepp SFKO AQUANOVA 4.28 12.95 2 Volvo Penta D6 IPS500, 2007 Fritidsmotorskepp SHKT ANAGADA 4.19 12.94 Volvo TAMD 72 P EDC, 1996 Fritidsmotorskepp 192

SJMH GARFIELD 4.19 12.94 2 Volvo 72 A, 1992 Fritidsmotorskepp SFOW LINNEA III AF STOCKHOLM 4.19 12.94 Volvo Penta TAMD72, 1991 Fritidsmotorskepp SKYM FLYING RUG 4.19 12.94 Volvo TAMD 72, 1993 Fritidsmotorskepp SKCT SUNSHINE 4.20 12.94 2 Volvo TAMD70 1995 Fritidsmotorskepp SBIL ANCYLUS AV LOVÖN 4.20 12.94 2 Volvo TAMD 71 1989 Fritidsmotorskepp SBFO PROTEUS 4.20 12.94 2 Volvo TAMD 71 1989 Fritidsmotorskepp SDZC SAMLINE 4.19 12.94 2 Volvo Penta TAMD 72EDC Fritidsmotorskepp SDWA EL COMMANDANTE 4.20 12.94 2 Volvo TAMD 71 1989 Fritidsmotorskepp SFUV AFRODITE AF VAXHOLM 4.20 12.94 2 Volvo TAMD 71 1989 Fritidsmotorskepp SFMA B & I 4.20 12.94 2 Caterpillar 3208TA Fritidsmotorskepp SDWJ GEMMA 4.20 12.94 2 Volvo TAMD 71 1988 Fritidsmotorskepp SCGM LA REGINA 4.20 12.94 2 Caterpillar 3208, 1990 Fritidsmotorskepp SCBX SANNALINA 4.20 12.94 2 Caterpillar 3208, 1989 Fritidsmotorskepp SBXG SIRENA DE MAR 4.20 12.92 2 Volvo Penta TMD70 1984 Fritidsmotorskepp SFDZ SISCA 4.17 12.91 2 VolvoPenta TAMD72EDC 96 Fritidsmotorskepp SHKY LYN 5.08 12.91 Skandia 125, 1930 Fritidsmotorskepp SIVL FYLGIA 5.13 12.90 Fritidsmotorskepp SMUP PUFFIN 4.30 12.90 2 Volvo‐Penta TAMD 41A Fritidsmotorskepp SEJO JOLIE 4.18 12.90 2 Volvo TAMD 72, 1995 Fritidsmotorskepp SBJD STARLITE EXPRESS 4.49 12.88 Volvo Penta TAMD 71A Fritidsmotorskepp SEVM LUCKY STAR 4.49 12.88 2 Volvo Penta TAMD 71 A Fritidsmotorskepp SERA SOUL MATES 4.77 12.87 2 Caterpillar 3126, 2001 Fritidsmotorskepp WHITE LADY AF SJOQ OXELÖSUND 4.17 12.86 Volvo Penta MD 70 1979 Fritidsmotorskepp SDQH MARIA AV UDDEVALLA 4.10 12.85 Volvo Penta diesel Fritidsmotorskepp SMHA SEA‐STAR AV GÖTEBORG 4.01 12.85 2 Volvo Penta TAMD70 1987 Fritidsmotorskepp SMEQ UNICA I 4.33 12.84 2 Volvo Penta TAMD61 1987 Fritidsmotorskepp SGAV ALL INCLUSIVE 4.11 12.84 2 Volvo TAMD 72A, 1994 Fritidsmotorskepp SDYJ SOLIETTE 4.11 12.84 2 Volvo TAMD 72, 1997 Fritidsmotorskepp 193

SCEB AMETIST 4.11 12.84 2VolvoPentaTAMD72EDC,1996 Fritidsmotorskepp SHVT SLICK 4.18 12.83 2 Volvo TAMD 71 B, 1994 Fritidsmotorskepp SERG MY SUN 4.18 12.83 2 Volvo TAMD 63 Fritidsmotorskepp SMOJ NEPTUNE AF STOCKHOLM 4.99 12.79 Scania 135A 1952 Fritidsmotorskepp SBHO MEDIANTE 4.24 12.78 2 Volvo TAMD61 1989 Fritidsmotorskepp SBHN EVITA AF DJURSHOLM 4.24 12.78 2 Volvo TAMD71 1989 Fritidsmotorskepp SBDQ CASSIOPEIA 4.24 12.78 2 Volvo TAMD71 1989 Fritidsmotorskepp SBPC THE PRINCE & I 4.24 12.78 2 Volvo TAMD 71A 1989 Fritidsmotorskepp SEQI AQUA QUEEN 4.24 12.78 2 Volvo Penta TAMD 71 Fritidsmotorskepp SBZE VICTORIA AF VÄTÖ 4.24 12.78 2 Volvo TAMD 71 1990 Fritidsmotorskepp SBYT LA SIRENE 4.24 12.78 2 Volvo TAMD61 1988 Fritidsmotorskepp SGUT EL MAR 4.18 12.78 2xVolvo TAMD 71B, 1990 Fritidsmotorskepp SJOA AQUILEIA 4.24 12.78 2 Volvo TAMD 71B,1991 Fritidsmotorskepp SJCN SVANEN AV DJURSHOLM 4.05 12.77 Volvo TAMD 72 1992 Fritidsmotorskepp SCRQ DREAM GIRL 4.05 12.77 2 Volvo Penta TAMD72 1992 Fritidsmotorskepp SDBL PRITHIKA 4.05 12.77 2 Volvo Penta TAMD72 1992 Fritidsmotorskepp SDCH HEJ DU 4.05 12.77 2 Volvo Penta TAMD 72 Fritidsmotorskepp SCWH SANDY LAINE 4.05 12.77 2 Volvo Penta TAMD 72 Fritidsmotorskepp SEAT BEDA AV DANDERYD 4.05 12.77 2 Volvo Penta TAMD75EDC Fritidsmotorskepp SFUR FIRST LADY 4.05 12.77 2 Volvo Penta TAMD72EDC Fritidsmotorskepp SEQV LENITA 4.05 12.77 2 Volvo Penta TAMD 72 Fritidsmotorskepp SGCY GOURMET 4.05 12.77 2 Volvo Penta TAMD 1993 Fritidsmotorskepp SFOE MARI II 4.05 12.77 2 Volvo Penta TAMD72 ‐92 Fritidsmotorskepp SDJT ALIMAR 4.05 12.77 2 Volvo Penta TAMD 72 A Fritidsmotorskepp SIHR BONA VITA 4.05 12.77 2 Volvo Penta TAMD 72 Fritidsmotorskepp SIHC BELVIRIA 4.05 12.77 2 Volvo Penta TAMD72 Fritidsmotorskepp SHVX SAYONARA AF HÖRVIK 4.05 12.77 2 Volvo Penta TAMD 72 Fritidsmotorskepp SHEN GIRL III 4.05 12.77 2 Volvo Penta TAMD72 Fritidsmotorskepp SGXC ROYAL PARK 4.05 12.77 2 Volvo Penta TAMD 72 Fritidsmotorskepp 194

SGZQ JASMINE 4.05 12.77 2 Volvo Penta TAMD72 1992 Fritidsmotorskepp SHCA SUPERNOVA 4.05 12.77 2 Volvo Penta TAMD72 Fritidsmotorskepp SGPN GRÖNSKÄR 4.03 12.77 Saab‐Scania D8A01 1974 Fritidsmotorskepp SDHK ANNA 5.15 12.76 Volvo Penta MD 67 Fritidsmotorskepp SBOZ TINGARA STOCKHOLM 4.67 12.75 2 Caterpillar W/MG 507‐1 Fritidsmotorskepp SEFD ALBION 4.67 12.73 2 Caterpillar 3208‐TA Fritidsmotorskepp SCNI SHALVA 4.24 12.73 2 Volvo‐Penta TAMD71 1991 Fritidsmotorskepp SCBA BUMBLE‐BEE 4.24 12.73 2 Volvo TAMD 71 1990 Fritidsmotorskepp SBXI JOYSEA 4.24 12.73 2 Volvo TAMD71 1990 Fritidsmotorskepp SJYB FEM 4.12 12.72 Mercury Big Foot, 2002 Fritidsmotorskepp SDYU HILDEGARD 4.52 12.71 Cummins Turbo Diesel,1990 Fritidsmotorskepp SHQR EMILY AF SALTARÖ 5.40 12.68 Bolinder Munktell Fritidsmotorskepp SEXW SVARTLIEN 4.86 12.67 Albin Fritidsmotorskepp SIDN MUZZE‐LINA 4.52 12.67 2 Cummins diesel, 2005 Fritidsmotorskepp SDXO MOA III AV UDDEVALLA 4.08 12.65 Penta diesel MD 96 Fritidsmotorskepp SIAC LÅGLAND 4.50 12.64 Marinmotor Hundersted Fritidsmotorskepp SMQZ NEPTUNUS AF TÄBY 4.04 12.64 2 Volvo TAMD 70C 1979 Fritidsmotorskepp SLNE MAYA PICASSO 4.03 12.64 2 Volvo Penta TAMD 63P Fritidsmotorskepp SCIT BAD HABIT I SUNDBYBERG 4.03 12.64 Fritidsmotorskepp SMPX BLUEBERRY 4.03 12.64 2 Volvo TAMD 63 P, 1999 Fritidsmotorskepp SBDY LADY SOFT 4.50 12.61 2 Volvo 41A 1988 Fritidsmotorskepp SCKN BADHOTELLET II 4.50 12.61 2 Caterpillar 3208TA 1989 Fritidsmotorskepp SKNI MARSEHOLM 4.20 12.61 Leyland VE 400 1982 Fritidsmotorskepp SDPB JOHANNA‐SOFIA 4.21 12.60 Grenaa Fritidsmotorskepp SLFY BIANCA 4.02 12.60 Volvo Penta TMD40 1988 Fritidsmotorskepp SLVY JOYA MIA 4.29 12.60 2 Caterpillar, 1996 Fritidsmotorskepp SMKW SUPREME 4.01 12.59 Volvo Penta TAMD 70D 1980 Fritidsmotorskepp SKDO ÅLEN 4.45 12.58 Volvo Penta MD 70 A 1966 Fritidsmotorskepp SLZN TIRAMISU 4.09 12.58 2 VolvoPentaTAMD 61,1991 Fritidsmotorskepp 195

SDFN PRAETOR 4.18 12.57 Volvo Penta TMD70 Fritidsmotorskepp SDPL THE SECOND RABBIT 4.75 12.57 Skandia tändkulemotor Fritidsmotorskepp SFCY TIAN 5.11 12.56 Albin motor G62 1962 Fritidsmotorskepp SBLA PARTNERSHIP 4.20 12.56 2 Cummins 3 2 1987 Fritidsmotorskepp SLDK JAN MAYEN 4.10 12.55 2 Ford IM 6‐2715‐PRM Fritidsmotorskepp SFML MILLENNIUM 4.60 12.55 2 Volvo Penta TAMD 70 C Fritidsmotorskepp SKJV LISA II 4.07 12.55 Perkins diesel 1976 Fritidsmotorskepp SEVR RANÖ 5.11 12.55 Scania Vabis 1963 Fritidsmotorskepp SMDV SPRUTTEN IV 4.50 12.55 2 Volvo TAMD 74PEDC 2000 Fritidsmotorskepp SICO SIMPLICITY 4.14 12.54 2 Volvo Penta TAMD63 1995 Fritidsmotorskepp SBEA SHALIMAR AF WISBY 4.14 12.54 2VolvoPenta TAMD63P,1995 Fritidsmotorskepp SCQI MELODY 4.14 12.54 2 Volvo TAMD63P,1997 Fritidsmotorskepp SKIP TEACHER 4.07 12.53 2 st Perkins TV 8 K Fritidsmotorskepp SCFO MONIQUE MOON 4.27 12.51 2 RWC Crusander 1987 Fritidsmotorskepp SGTD WHITE DIAMONDS 4.30 12.50 Detroit Diesel 53, 1999 Fritidsmotorskepp SEYP CAPRI 4.61 12.49 Skandia Fritidsmotorskepp SHGL EDIT 4.65 12.48 Säffle motorverkstad 1955 Fritidsmotorskepp SFNI HANINA AF HAMBURGÖ 4.74 12.48 Volvo Penta MD 96 1958 Fritidsmotorskepp SBAE SJÖULFEN 4.28 12.46 2 Caterpillar 1988 Fritidsmotorskepp SFPX PÄRLAN 4.27 12.45 2 Volvo TAMD 61 Fritidsmotorskepp SFCB 4.21 12.44 2 Cummins T380 Q58, 2008 Fritidsmotorskepp SFXM SVEA AF GÖTEBORG 4.94 12.42 Munktell 4FD 135 MB 1954 Fritidsmotorskepp SFWM SEAVIEW 147 4.20 12.41 2 Volvo Penta IPS 500, 2007 Fritidsmotorskepp SCZF VINDFAXE 4.61 12.40 Bolinder‐Munktell 1965 Fritidsmotorskepp SJLU CABO FRIO 4.77 12.40 Volvo Penta Fritidsmotorskepp SJQG ZELENA 4.00 12.40 Volvo Penta TMD 100 Fritidsmotorskepp SMBN KENITRA 4.26 12.40 2 Caterpillar 1986 Fritidsmotorskepp SFME MUNKEN 5.00 12.38 Fritidsmotorskepp SHVO ZIVA 5.26 12.38 Fritidsmotorskepp 196

SIBD MAGNIFIQUE 4.10 12.35 2 Volvo TAMD 62 1993 Fritidsmotorskepp TENDER ONE AV SGAZ STOCKHOLM 4.57 12.35 2 Volvo D6‐350DP, 2006 Fritidsmotorskepp SDYL MY FAIR LADY 4.09 12.34 2 Volvo TAMD 1994 Fritidsmotorskepp SDXE NIRVANA 4.28 12.32 2 Caterpillar 3208 1988 Fritidsmotorskepp SFVN RAN AF GÖTEBORG 4.56 12.31 Volvo Penta MD 96B 1967 Fritidsmotorskepp SMUC FALSTERBO 4.42 12.31 Volvo Penta MD 100 B 1973 Fritidsmotorskepp SJIC NORDSTIERN 4.46 12.31 Scania Vabis D 10 1962 Fritidsmotorskepp SCJH CONTE DI MONTECRISTO 4.30 12.30 2 Detroit 1990 Fritidsmotorskepp SFKZ BRUNNTE 40 4.35 12.28 Volvo TMD 102 Fritidsmotorskepp SFOR SNOWHITE 4.21 12.27 2 Volvo Penta TAMD61A Fritidsmotorskepp SMRH MARET 4.21 12.27 2 Volvo TAMD71 1987 Fritidsmotorskepp SMDZ DISCOVERY AF SOLLENTUNA 4.21 12.27 2 Volvo TAMD 61 1987 Fritidsmotorskepp SMIP SESSAN 4.21 12.27 2 Volvo MD70 1986 Fritidsmotorskepp SMHK CIRCUS 4.21 12.27 2 st Volvo TAMD 1988 Fritidsmotorskepp SBKM ISIS AV HOVENÄSET 4.21 12.27 2 Volvo TAMD60, 1986 Fritidsmotorskepp SBDZ RENÉE II 4.21 12.27 2 Volvo‐Penta TAMD71 1988 Fritidsmotorskepp SLHG KRISTINA AF WAXHOLM 4.21 12.27 2 Volvo TAMD61, 1990 Fritidsmotorskepp SBHL NO MO SNO 4.19 12.26 2 Cummins Turbo diesel, , 01 Fritidsmotorskepp SBRZ CHAGANZA 4.21 12.26 2 Volvo TAMD 61 1990 Fritidsmotorskepp SDZY KROMOSOM 5.54 12.26 Volvo MD 60 Fritidsmotorskepp SJTK BORÖ AF ARKÖSUND 4.47 12.25 Fritidsmotorskepp SHTU CAPRICORN 4.38 12.25 2 Perkins, 1973 Fritidsmotorskepp SKNR THALATTA 4.22 12.24 Volvo Penta MD70A 1969 Fritidsmotorskepp SDRZ SEA PRINCESS 4.21 12.22 2 Volvo Penta TAMD 61 A Fritidsmotorskepp SBMA MON AMI AF VÄSTERÅS 4.21 12.22 2 Volvo Penta TAMD 71 Fritidsmotorskepp SMCU JOSSAN 4.24 12.22 2 Ford‐Lehman 1986 Fritidsmotorskepp SGWB GANÖN 4.48 12.20 Scania DSI 11 MO1 SF 1800 Fritidsmotorskepp SFYG CHRISTINA AV ÄNGELHOLM 4.09 12.20 2 Volvo Penta KAD42DP,‐97 Fritidsmotorskepp 197

SEZF SPIRIT OF MIMOSA 4.09 12.20 2Caterpillar Diesel, 1996 Fritidsmotorskepp SMHX SEVENTH WAVE 4.32 12.20 Fritidsmotorskepp SMKN LOVISA AV STOCKHOLM 7.02 12.19 2VolvoPenta2003BT/1201988 Fritidsmotorskepp SFQY NERAIDA 4.02 12.15 Yanmar 4LHA/HTE Fritidsmotorskepp SKEX LA DéESSE 4.14 12.15 2 Volvo TAMD 61A, 1989 Fritidsmotorskepp SMJI ZARINA 4.03 12.15 2 Volvo TAMD 60A, 1980 Fritidsmotorskepp SLFI KATINA ANNE 4.18 12.15 2 Volvo TAMD 71B 1990 Fritidsmotorskepp SCWL CHAMSIN 4.18 12.13 2 Volvo Penta TAMD71 1991 Fritidsmotorskepp SIAR ACCESS 4.18 12.13 2 Volvo Penta TAMD71,1991 Fritidsmotorskepp CONTESSA AF SELH SALTSJÖBADEN 4.18 12.13 2 Volvo Penta TAMD 71A Fritidsmotorskepp SDXB ZIVA 4.78 12.12 Fritidsmotorskepp SCTD SUNDAY 4.27 12.12 2 Scania D8, 1980 Fritidsmotorskepp SLDF LILLJUNGFRUN 4.48 12.10 Volvo MD96 Fritidsmotorskepp SCJF KÅRE 4.37 12.09 Volvo MD96B 1979 Fritidsmotorskepp SHMV TERESA AV STOCKHOLM 4.48 12.08 2 Volvo D9‐500,2005 Fritidsmotorskepp SKZR CHARLOTTA AV VIKSNÄS 4.48 12.08 2 Volvo D9‐500, 2006 Fritidsmotorskepp SCPD BRUMMBÄR 4.30 12.07 Ford Lehman 2715E, 1979 Fritidsmotorskepp SJNW MY LADY 4.07 12.07 2 Volvo Penta VP TAMD 71B Fritidsmotorskepp SCMU NICE 4.07 12.07 2 VP TAMD 71B 1990 Fritidsmotorskepp SEJR EASY 4.07 12.07 2 Volvo TAMD 718, 1991 Fritidsmotorskepp SDKX VAGABOND AF ÖREGRUND 4.07 12.07 2 Volvo Penta TAMD71A Fritidsmotorskepp SBGZ SHALIMAR AF DALARÖ 4.08 12.05 2 Volvo Penta TAMD61 1988 Fritidsmotorskepp SIBU BONNY II 4.08 12.05 Volvo TAMD 61, 1987 Fritidsmotorskepp KAP HORN AV SBWP SALTSJÖBADEN 4.16 12.01 2 Volvo D6, 2006 Fritidsmotorskepp SBFA SILJE 4.35 12.01 2 Caterpillar 3208 1989 Fritidsmotorskepp SMRL RELAX I 4.27 12.01 2 Volvo Penta TAMD61 1987 Fritidsmotorskepp SJVI BRITT 4.50 12.00 Volvo MD 70 1980 Fritidsmotorskepp

198

SLYA DOLCE VITA 4.14 12.00 2 Volvo D6‐435, 2007 Fritidsmotorskepp Fritidsmotorskepp, SDPA ROSENBERG 7.30 26.55 MAK 1968 husbåt Fritidsmotorskepp, SJUP MELLSKÄR 4.82 19.18 Volvo Penta MD100 A 1966 husbåt Fritidsmotorskepp, SDQM ARKEN AF ASKEN 9.83 14.55 Mariner 1987 husbåt SITO XARIFA III 2.50 12.50 Fritidssegelbåt SJCK VICTORIA 3.27 11.13 Fritidssegelbåt SHWO SJU GLAS 2.83 10.90 Fritidssegelbåt SIUE DANSKA LILJAN 3.08 10.65 Fritidssegelbåt SHXE NICLA III 3.04 10.46 Fritidssegelbåt SJBO CARIOCA II 2.86 9.81 Fritidssegelbåt SJBW JUSTINA 2.86 9.81 Fritidssegelbåt SJDG VINDKULE 2.87 9.69 Fritidssegelbåt SJLD GIGEL 2.95 9.48 Fritidssegelbåt SJYR MOLLY 2.85 9.40 Fritidssegelbåt SJGO POULALU 2.85 9.40 Fritidssegelbåt SIUG CADACCA 3.16 9.37 Fritidssegelbåt SIUR CONTENTA 3.16 9.37 Fritidssegelbåt SJOW MIRAMIS 2.76 9.33 Fritidssegelbåt SJOU PILENA 2.94 9.19 Fritidssegelbåt SIXE BLUE LADY 2.94 9.19 Fritidssegelbåt SIYK JEANETTE 2.94 9.19 Fritidssegelbåt SHXK BALLADETT 2.94 9.19 Fritidssegelbåt SIOG PUELLA II 3.03 9.04 Fritidssegelbåt SJZD FRIDA 2.60 8.86 Fritidssegelbåt SJHW NEREIDEN II 2.50 8.78 Fritidssegelbåt SIGK JOHANNA 2.50 8.78 Fritidssegelbåt

199

SHXR TRAPPER 2.58 8.59 Fritidssegelbåt SDOP CAMILLA 3.68 12.15 Turham tändkulemotor Fritidssegelmotorbåt SLYE RIANDE 6.25 32.41 GM 671 1962 Fritidssegelmotorskepp SCJQ LIBRA AF STOCKHOLM 6.14 26.10 Caterpillar 353D, 1969 Fritidssegelmotorskepp SEPW MAGDALUS SECONDO 6.13 25.76 2 Caterpillar 3208 DITA Fritidssegelmotorskepp SFEA VESTA AF STOCKHOLM 6.84 24.36 Fritidssegelmotorskepp SBLT KLARA LUST 4.68 22.48 Kromhout Fritidssegelmotorskepp SILG ELSE NORA 4.22 20.72 DAF, 1996 Fritidssegelmotorskepp SDAZ DEA MARIS 6.20 20.10 Fritidssegelmotorskepp SEVA LELANTA 4.45 19.98 Detroit diesel 1979 Fritidssegelmotorskepp SCKA BLUE MARLIN 5.25 19.90 Cummins 6 BT 5 9M 1991 Fritidssegelmotorskepp SKPT TRAVEL 4.97 19.81 Perkius 115 1979 Fritidssegelmotorskepp SDVK BRUDEN II 5.15 19.75 Perkins 4 HD76 Fritidssegelmotorskepp SKTX ELIXIR 4.62 19.60 Scania D8 1965 Fritidssegelmotorskepp SBLX WINDY LADY 4.51 19.15 Cummins 359/5.9, 1991 Fritidssegelmotorskepp SDZP AEGIR 6.25 18.88 DSI 11 Scania 6 cyl Fritidssegelmotorskepp SDUN WESTWARD 4.98 18.62 VolvoPentaMD96281,1961 Fritidssegelmotorskepp SHKO EXPLORER OF SWEDEN 5.05 17.75 Iveco Aifo 8361SRM32 1995 Fritidssegelmotorskepp SCNL MAXIMUM 4.75 17.39 Volvo D 70 Fritidssegelmotorskepp SBGK VICTORIA MARIE 4.56 17.01 Volvo TMD100A 1971 Fritidssegelmotorskepp SGXP MYJOY 4.58 16.96 Perkins M135 1993 Fritidssegelmotorskepp SFDV BLUE CHARISMA 4.90 16.76 Perkins 1988 Fritidssegelmotorskepp SLRD STORMPRINCE 4.34 16.37 Scania D11 Fritidssegelmotorskepp SEDA EXET 4.34 16.36 Volvo Penta TAMD 31P Fritidssegelmotorskepp SGNL AMIBO 4.35 16.35 Volvo TAMD 63 Fritidssegelmotorskepp SBYW LION HEART 4.35 16.07 Volvo Penta TMD31 1990 Fritidssegelmotorskepp SMNH ARISTOCAT 4.60 15.60 Ford‐Lehman 2725E 1988 Fritidssegelmotorskepp SCNT ETHER 5.00 15.56 Leyland Delphine 6cyl1984 Fritidssegelmotorskepp SJMK STENO 5.09 15.40 Volvo MD 96 1964 Fritidssegelmotorskepp 200

SIJV ALIDA 4.32 15.36 Volvo Penta MD 47 1976 Fritidssegelmotorskepp SFAY PEPPELI 4.70 15.32 Mercedes OM352, 1965 Fritidssegelmotorskepp SBOK HANNA AF ÖCKERÖ 4.58 15.30 Volvo Penta MD100A 1966 Fritidssegelmotorskepp SCOR ATON 4.06 15.20 Mercedes, 1979 Fritidssegelmotorskepp SCMA ACQVA‐RUS 4.45 15.05 Volvo Penta TAM 41 1991 Fritidssegelmotorskepp SEQA TRADE WIND 4.47 15.01 2 Bedford 330 IAL2063‐PT Fritidssegelmotorskepp SLBW ROYAL SALUTE 4.52 15.00 Yanmar 4JH3G‐HTBE 2.6 ‐00 Fritidssegelmotorskepp SDEG BARCAROLE V 4.66 14.88 Yamaha 4JH‐DTH 1990 Fritidssegelmotorskepp SLJM HONEYSUCKLE 4.13 14.79 Volvo Penta MD30 1984 Fritidssegelmotorskepp SCNE TALISMAN 4.57 14.78 Perkins 4154 Fritidssegelmotorskepp SLQC ELEONOR AF OXELÖSUND 5.85 14.67 Volvo Penta MD67C 1967 Fritidssegelmotorskepp SMKE SABINE 4.30 14.30 Venus P4.25 1988 Fritidssegelmotorskepp SCHR MORGONSOL 4.35 14.24 Volvo Penta TMD 31 A 1991 Fritidssegelmotorskepp SHOC ALMA AF GRÄDDÖ 4.30 14.18 Perkins 4:236 1995 Fritidssegelmotorskepp SMPQ SÅNGMÖN 4.23 14.17 Volvo Penta MD21A 1979 Fritidssegelmotorskepp SLPE ÄLSKLING 4.60 14.00 Perkins 80 CV 1983 Fritidssegelmotorskepp SLNB CHERIE 5.24 13.91 Volvo Penta MD67 1959 Fritidssegelmotorskepp SDIQ WE DO 4.12 13.90 Ford 6.380 1976 Fritidssegelmotorskepp SHMP DECISION 4.30 13.90 Perkins 4108, 1983 Fritidssegelmotorskepp SBGD COLUMBINE 4.46 13.83 Volvo Penta MD30 1986 Fritidssegelmotorskepp SKGW CHARLATAN 4.03 13.70 Volvo‐Penta MD 17 1978 Fritidssegelmotorskepp SGOC NAUSIKA II 4.12 13.62 Perkins 6.354, 1981 Fritidssegelmotorskepp SHLC GLADAN AF WESTERVIK 7.70 13.61 2 Volvo D2‐55, 2008 Fritidssegelmotorskepp SHON DISCOVERY 4.36 13.60 Perkins diesel H6 354M Fritidssegelmotorskepp SGKQ BELLONA DE SERENA 4.18 13.54 Volvo MD 47 Fritidssegelmotorskepp SLYI HERO‐BRAVA 4.15 13.44 Perkins 4.108 1980 Fritidssegelmotorskepp SLTH MALOLELEI 4.00 13.24 Perkins 4236 1976 Fritidssegelmotorskepp SMWC MIN MIO 4.00 13.23 V.P. 2003 TS Fritidssegelmotorskepp SBYX APHOS 4.08 13.14 Yanmar 4 JHB 1990 Fritidssegelmotorskepp 201

SGXL BUKSTINA 4.01 13.10 Perkins diesel 4108 1978 Fritidssegelmotorskepp SCHU GANTIKA 4.24 13.08 Ford NG4 2722E, 1984 Fritidssegelmotorskepp SFVU PANDORA III AF GEFLE 4.22 12.98 Ford 2722 1983 Fritidssegelmotorskepp SHJK PINK LADY 6.68 12.95 2 Evinrude, 1985 Fritidssegelmotorskepp SLJD TYPHOON 4.03 12.80 Perkins 4.108 1985 Fritidssegelmotorskepp SMRD JENINA 4.00 12.65 Volvo Penta MD30 1985 Fritidssegelmotorskepp SMNJ JUST FOR FUN 4.00 12.65 Volvo Penta MD 40 1983 Fritidssegelmotorskepp SDXW CANTELLA 2 4.00 12.65 Kubota Diesel, 1986 Fritidssegelmotorskepp SBTG OF COURSE 5.80 12.45 Färe Göta 3 cyl 1975 Fritidssegelmotorskepp SGXA KALEA 4.04 12.41 Volvo MD17, 1983 Fritidssegelmotorskepp SCIU ANNE‐MARIE AV RÅÅ 4.35 12.18 Perkins diesel 4.236 1980 Fritidssegelmotorskepp SBAN SECOND LIFE 4.07 12.10 Volvo MD21B 1986 Fritidssegelmotorskepp SMLF DIANA AF WERMDÖ 4.16 12.02 Yanmar 1988 Fritidssegelmotorskepp SGPL TRE KRONOR 5.52 22.66 Fritidssegelskepp SLQF SOFIA LINNEA 6.62 20.10 Fritidssegelskepp SLFZ BLUE ADVENTURE 5.34 19.54 Daimler Benz, 1986 Fritidssegelskepp SMGX BONDEVENNEN 5.27 17.14 Fritidssegelskepp SEFT FIESTA 4.18 14.74 Volvo MD 21 A Fritidssegelskepp SCGO SOIR 4.63 13.82 Fritidssegelskepp SLJG ISIS 8.36 12.93 Fritidssegelskepp SKHY LAZY DUCK 4.26 12.84 Volvo D2 55C, 2006 Fritidssegelskepp SMFT HAVAIKI 5.86 12.19 Fritidssegelskepp SMIR CATANIA 6.60 25.99 Fritidsskepp SMVX BORD‐ELLEN 6.00 22.61 Fritidsskepp SDFI TVÅHUNDRAFEMTIOFYRA 4.28 21.36 Fritidsskepp SDET UGGLAN 4.28 21.36 Fritidsskepp SDEC TVÅHUNDRATJUGOFYRA 4.28 21.36 Fritidsskepp SDEP TVÅHUNDRAFYRTIOTVÅ 4.28 21.36 Fritidsskepp SIVZ VALENCI AF BERGSUND 6.11 17.15 Fritidsskepp 202

SIJX COCKNEY SPIRIT 4.55 12.70 Fritidsskepp SBLP SVEGUN 5.08 23.98 Fritidsskepp (pråm) SGDH BJÖRNEN 8.14 27.10 CD Holmes & Co Ltd 1941 Fritidsångskepp SKFN GÖRAN 5.00 22.39 Fritidsångskepp SDZL ELFDALEN 4.96 22.37 Ljusne Compoundångm. 1888 Fritidsångskepp SGLX SILJAN 4.70 21.99 Comp. ångm. Sjöström 1904 Fritidsångskepp SGUR STARK‐OTTER 5.50 20.15 Compound ångmaskin 1901 Fritidsångskepp SGEM CAMA III 5.21 19.94 Bolinder‐Munktell 1947 Fritidsångskepp SIYR FLOTTISTEN 4.12 19.54 Ångmaskin Härnösand 1890 Fritidsångskepp SHUG VENUS AV VÄDDÖ 4.20 18.47 Fritidsångskepp SHPU STRÖMFÄRJAN 1 4.94 18.46 Fritidsångskepp SJLT KURIREN 4.06 16.79 Wennbergs comp‐ångm. 1915 Fritidsångskepp

203

Appendix B Filtered Data collected on Registered Boats and its Engine Specifications.

Data of Boats Specifications with complete information (all units are given per engine) Call sign Length (m) Machinery kw stroke Fuel fuel consumption (l/hr) in/outboard SFC‐8611 13.15 2 st VP TAMD74P 358.08 4 diesel 197.15 inboard SFC‐4611 13.40 2 Volov Penta TMD70 1970 111.90 4 diesel 59.24 inboard SFC‐5947 12.50 2 Volvo Penta AD40 115.63 4 diesel 26.00 inboard SFC‐8112 10.00 2 Volvo Penta AD41B,1992 123.09 4 diesel 30.00 inboard SFC‐3749 13.00 2 Volvo Penta KAD42 1992 171.58 4 diesel 56.50 inboard SFC‐5259 12.30 2 Volvo Penta KAD42 1997 171.58 4 diesel 56.50 inboard SFC‐3388 7.70 2 Volvo Penta MD5C 7.09 4 diesel 5.07 inboard SFC‐8887 11.20 2 Volvo Penta TAMD 40 B, 1986 117.87 4 diesel 83.20 inboard SFC‐7458 12.95 2 Volvo Penta TAMD 75 P 343.90 4 diesel 188.54 inboard SFC‐3935 10.50 2 Volvo Penta TAMD40 117.87 4 diesel 83.20 inboard SFC‐3563 11.80 2 Volvo Penta TAMD41 126.82 4 diesel 71.62 inboard SFC‐3584 11.20 2 Volvo Penta TAMD41 126.82 4 diesel 71.62 inboard SFC‐4793 12.25 2 Volvo Penta TAMD60B 81 164.86 4 diesel 89.61 inboard SFC‐4363 11.96 2 Volvo Penta TAMD61 170.09 4 diesel 90.05 inboard SFC‐3945 12.00 2 Volvo TAMD60 1975 164.86 4 diesel 89.61 inboard SFC‐7966 12.00 2 Volvo TMD45 1970 67.14 4 diesel 35.58 inboard SFC‐6107 12.15 2 VP TAMD 70B 111.90 4 diesel 59.24 inboard SFC‐7052 14.30 2 x TAMD70C, 1975 111.90 4 diesel 59.24 inboard SFC‐6589 10.80 2 X Volvo Penta TAMD60,80 164.86 4 diesel 89.61 inboard SFC‐7268 8.62 2 x Volvo Penta‐KAD42 171.58 4 diesel 56.50 inboard SFC‐8771 13.04 2 x Volvo Tamd 75 P, Diesel, 2003 343.90 4 diesel 188.54 inboard SFC‐6847 10.35 2xTAMD60B, 1982 164.86 4 diesel 89.61 inboard SFC‐7353 11.90 2xVolvo Tamd 74P,2001 358.08 4 diesel 197.15 inboard SFC‐8122 12.09 2xVolvoPenta TAMD70E 157.40 4 diesel 57.41 inboard SFC‐8020 10.00 3GM30, 2001 20.14 4 diesel 6.63 inboard SFC‐5738 10.99 3GM30F 20.14 4 diesel 6.63 inboard 204

SFC‐7218 17.75 AB.Penta‐297 MD 96 94.74 4 diesel 26.45 inboard SFB‐6063 6.30 Albin AD2 11.94 4 diesel 3.67 inboard SFC‐2685 6.90 Albin AD‐2 1968 11.94 4 diesel 3.67 inboard SFC‐3264 8.00 Albin AD21 16.41 4 diesel 4.71 inboard SFB‐5023 7.00 Albin AL 23 11.19 4 diesel 4.24 inboard SFB‐4202 9.10 Albin Marin AD‐2 1962 11.94 4 diesel 3.67 inboard SFC‐3842 9.30 AQAD40B 1984 115.63 4 diesel 26.00 inboard SFC‐2563 9.20 AQAD41/290DP 1990 149.20 4 diesel 30.00 inboard SFC‐8406 8.15 Diesel Volvo MD2B, 1974 17.16 4 diesel 5.15 inboard SFC‐7789 19.50 Ford 2710 1973 71.62 4 diesel 10.00 inboard SFC‐8071 10.85 Ford 2720 106.68 4 diesel 22.46 inboard SFC‐3769 8.60 Ford 2722E 106.68 4 diesel 22.46 inboard SFC‐7506 11.50 Ford 2725 E ‐83 106.68 4 diesel 22.46 inboard SFC‐8019 11.00 Ford 2725 E, 1996 106.68 4 diesel 22.46 inboard SFC‐8652 12.67 Ford 2725E 6.2l,1989 106.68 4 diesel 22.46 inboard SFB‐7914 11.30 Ford Diesel 27/11 1978 71.62 4 diesel 10.00 inboard SFB‐8284 11.86 Ford diesel typ 2711 1976 71.62 4 diesel 10.00 inboard SFC‐4870 8.95 IGM10 6.71 4 diesel 2.30 inboard SFC‐7382 10.40 Lombardini 1404M, 2001 29.84 4 diesel 11.23 inboard SFC‐7125 9.81 Lombardini LDW 1003 M 22.38 4 diesel 7.66 inboard SFC‐6747 8.00 Lombardini LDW702, 2000 14.92 4 diesel 5.44 inboard SFC‐7180 10.88 Lombardini LW1003M, 2001 22.38 4 diesel 7.66 inboard SFB‐5128 6.70 MD 11C 1976 14.92 4 diesel 9.50 inboard SFC‐7101 10.70 MD 11C, 1979 14.92 4 diesel 9.50 inboard SFC‐3658 9.80 MD2 11.56 4 diesel 3.65 inboard SFB‐5004 6.80 MD2B 1971 17.16 4 diesel 5.15 inboard SFB‐5005 6.80 MD2B Penta 1971 17.16 4 diesel 5.15 inboard SFC‐8093 9.89 MD2B, 1978 17.16 4 diesel 5.15 inboard SFB‐6963 8.20 MD47A 52.97 4 diesel 15.12 inboard SFC‐7263 13.40 MD67 Snr 0443 64.16 4 diesel 17.71 inboard 205

SFC‐7295 10.85 Perkins Range 4 M135,1988 100.71 4 diesel 28.00 inboard SFC‐2969 8.90 TAMD 31 1989 82.06 4 diesel 21.72 inboard SFC‐7442 8.45 TAMD 31 Volvo Penta 82.06 4 diesel 21.72 inboard SFC‐5827 12.09 TAMD 71A VP, 1987 162.63 4 diesel 41.71 inboard SFC‐5414 9.15 TAMD70 1997 157.40 4 diesel 28.70 inboard SFC‐7266 9.30 TMD 40 87.28 4 diesel 31.83 inboard SFC‐4178 11.00 Twin Cummings 6BT5.9 91.01 4 diesel 23.40 inboard SFC‐6791 9.20 Volvo AD41A290DP,‐90 123.09 4 diesel 30.00 inboard SFC‐6882 10.70 Volvo MD 40, 1988 58.93 4 diesel 21.49 inboard SFC‐7371 10.67 Volvo MD2, 1978 11.56 4 diesel 3.65 inboard SFC‐8509 11.37 Volvo MD30, 2004 41.78 4 diesel 14.74 inboard SFC‐7114 10.40 Volvo MD47, 1980 52.97 4 diesel 15.12 inboard SFC‐5597 14.50 Volvo MD67C 70.87 4 diesel 19.67 inboard SFC‐6356 14.40 Volvo Penta 100A, 1967 99.22 4 diesel 26.91 inboard SFC‐3687 8.75 Volvo Penta AD41 123.09 4 diesel 30.00 inboard SFC‐5199 7.65 Volvo Penta AQAD40B 1983 115.63 4 diesel 26.00 inboard SFC‐3438 7.50 Volvo Penta AQAD41 149.20 4 diesel 30.00 inboard SFB‐9270 6.50 Volvo Penta AQAD41 1981 149.20 4 diesel 30.00 inboard SFC‐4183 8.50 Volvo Penta KAD 42 1992 343.16 4 diesel 113.00 inboard SFC‐5422 11.00 Volvo Penta KAD42A 1992 343.16 4 diesel 113.00 inboard SFC‐5714 11.30 Volvo Penta MD 11 C 14.92 4 diesel 9.50 inboard SFC‐6743 9.36 Volvo Penta MD 11 C, 1977 14.92 4 diesel 9.50 inboard SFC‐6223 9.36 Volvo Penta MD 11 C, 1978 14.92 4 diesel 9.50 inboard SFC‐8683 9.75 Volvo Penta MD 11 C, 1979 14.92 4 diesel 9.50 inboard SFC‐8225 9.36 Volvo Penta MD 11C 14.92 4 diesel 9.50 inboard SFB‐4827 18.38 Volvo Penta MD 67C 70.87 4 diesel 19.67 inboard SFC‐3362 6.75 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐5977 9.87 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3589 11.07 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐5416 11.05 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard 206

SFC‐3346 11.05 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFB‐7298 11.00 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3657 10.80 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3587 10.70 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3354 10.46 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3371 9.89 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3330 9.89 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3381 9.89 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3478 9.81 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFB‐7092 9.81 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3338 9.81 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3326 9.58 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3493 9.55 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3718 9.50 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3445 9.50 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3537 9.50 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3546 9.50 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3586 9.50 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐5484 9.50 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3699 9.45 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐6373 9.36 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3271 9.36 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐4956 9.36 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFB‐8971 9.35 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3500 9.30 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3550 9.30 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3547 9.30 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3841 7.80 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐3415 7.60 Volvo Penta MD11C 14.92 4 diesel 9.50 inboard SFC‐4159 10.95 Volvo Penta MD11C 1975 14.92 4 diesel 9.50 inboard 207

SFC‐6241 9.50 Volvo Penta MD11C 1976 14.92 4 diesel 9.50 inboard SFC‐4967 9.40 Volvo Penta MD11C 1977 14.92 4 diesel 9.50 inboard SFC‐5204 9.36 Volvo Penta MD11C 1977 14.92 4 diesel 9.50 inboard SFB‐7114 7.40 Volvo Penta MD11C 1978 14.92 4 diesel 9.50 inboard SFB‐6759 9.81 Volvo Penta MD11C 1978 14.92 4 diesel 9.50 inboard SFC‐4016 9.50 Volvo Penta MD11C 1978 14.92 4 diesel 9.50 inboard SFC‐3599 9.81 Volvo Penta MD11C 1979 14.92 4 diesel 9.50 inboard SFC‐4979 9.50 Volvo Penta MD11C 1980 14.92 4 diesel 9.50 inboard SFC‐6146 7.85 Volvo Penta MD11C 1980 14.92 4 diesel 9.50 inboard SFB‐6459 7.85 Volvo Penta MD11C 1980 14.92 4 diesel 9.50 inboard SFB‐6835 9.50 Volvo Penta MD11C 1980 14.92 4 diesel 9.50 inboard SFC‐5418 9.40 Volvo Penta MD11C 1980 14.92 4 diesel 9.50 inboard SFC‐5170 11.25 Volvo Penta MD11C 1981 14.92 4 diesel 9.50 inboard SFB‐8904 9.81 Volvo Penta MD11C 1981 14.92 4 diesel 9.50 inboard SFB‐8627 9.81 Volvo Penta MD11C 1981 14.92 4 diesel 9.50 inboard SFC‐6023 9.81 Volvo Penta MD11C 1981 14.92 4 diesel 9.50 inboard SFC‐3794 9.50 Volvo Penta MD11c 1981 14.92 4 diesel 9.50 inboard SFC‐6039 9.89 Volvo Penta MD11C 1984 14.92 4 diesel 9.50 inboard SFC‐7091 10.84 Volvo Penta MD11C 33391 14.92 4 diesel 9.50 inboard SFC‐7519 9.36 Volvo Penta MD11C, 1979 14.92 4 diesel 9.50 inboard SFC‐6275 10.75 Volvo Penta MD11C, 1979 14.92 4 diesel 9.50 inboard SFC‐7309 9.58 Volvo penta MD11C, 1980 14.92 4 diesel 9.50 inboard SFC‐5180 11.07 Volvo Penta MD11C/100S 77 14.92 4 diesel 9.50 inboard SFB‐6365 7.60 Volvo Penta MD17 26.11 4 diesel 7.58 inboard SFC‐3364 13.85 Volvo Penta MD17 26.11 4 diesel 7.58 inboard SFC‐5939 10.60 Volvo Penta MD17 26.11 4 diesel 7.58 inboard SFC‐5265 9.40 Volvo Penta MD17 26.11 4 diesel 7.58 inboard SFC‐3359 9.40 Volvo Penta MD17 26.11 4 diesel 7.58 inboard SFB‐8166 7.40 Volvo Penta MD17 1982 26.11 4 diesel 7.58 inboard SFC‐5721 11.80 Volvo Penta MD17 1983 26.11 4 diesel 7.58 inboard 208

SFB‐8859 11.43 Volvo Penta MD17 1983 26.11 4 diesel 7.58 inboard SFC‐5235 10.60 Volvo Penta MD17 1983 26.11 4 diesel 7.58 inboard SFB‐7850 9.36 Volvo Penta MD17 Diesel 26.11 4 diesel 7.58 inboard SFC‐7452 10.20 Volvo Penta MD17, 1981 26.11 4 diesel 7.58 inboard SFC‐8520 13.00 Volvo Penta MD17, 1988 26.11 4 diesel 7.58 inboard SFC‐6462 10.40 Volvo Penta MD17‐110S 26.11 4 diesel 7.58 inboard SFC‐3368 14.00 Volvo Penta MD17C 26.11 4 diesel 7.58 inboard SFC‐3487 11.60 Volvo Penta MD17C 26.11 4 diesel 7.58 inboard SFC‐3489 11.03 Volvo Penta MD17C 26.11 4 diesel 7.58 inboard SFC‐5197 10.36 Volvo Penta MD17C 26.11 4 diesel 7.58 inboard SFC‐3444 10.20 Volvo Penta MD17C 26.11 4 diesel 7.58 inboard SFC‐3372 10.08 Volvo Penta MD17C 26.11 4 diesel 7.58 inboard SFC‐3398 9.89 Volvo Penta MD17C 26.11 4 diesel 7.58 inboard SFB‐8881 9.55 Volvo Penta MD17C 26.11 4 diesel 7.58 inboard SFC‐3404 7.30 Volvo Penta MD17C 26.11 4 diesel 7.58 inboard SFC‐5370 11.30 Volvo Penta MD17C 16277 26.11 4 diesel 7.58 inboard SFC‐5095 11.20 Volvo Penta MD17C 1979 26.11 4 diesel 7.58 inboard SFC‐5996 10.45 Volvo Penta MD17C 1979 26.11 4 diesel 7.58 inboard SFC‐4085 9.55 Volvo Penta MD17C 1979 26.11 4 diesel 7.58 inboard SFC‐4880 11.20 Volvo Penta MD17C 1981 26.11 4 diesel 7.58 inboard SFC‐4086 11.89 Volvo Penta MD17C 1984 26.11 4 diesel 7.58 inboard SFC‐6164 9.55 Volvo Penta MD17C 1984 26.11 4 diesel 7.58 inboard SFB‐6278 8.30 Volvo Penta MD17C Hydro 26.11 4 diesel 7.58 inboard SFC‐6561 10.40 Volvo Penta MD17C, 1976 26.11 4 diesel 7.58 inboard SFC‐7020 10.45 Volvo Penta MD17C, 1979 26.11 4 diesel 7.58 inboard SFC‐4589 9.55 Volvo Penta MD17C, 1979 26.11 4 diesel 7.58 inboard SFB‐8630 9.55 Volvo Penta MD17C/15560 26.11 4 diesel 7.58 inboard SFC‐6161 11.07 Volvo Penta MD17D 26.11 4 diesel 7.58 inboard SFB‐8663 14.40 Volvo Penta MD17D 1984 26.11 4 diesel 7.58 inboard SFB‐3690 6.20 Volvo Penta MD2 11.56 4 diesel 3.65 inboard 209

SFC‐3453 11.40 Volvo Penta MD2 11.56 4 diesel 3.65 inboard SFC‐3304 10.80 Volvo Penta MD2 11.56 4 diesel 3.65 inboard SFB‐8599 10.00 Volvo Penta MD2 11.56 4 diesel 3.65 inboard SFC‐3515 9.35 Volvo Penta MD2 11.56 4 diesel 3.65 inboard SFC‐3558 9.35 Volvo Penta MD2 11.56 4 diesel 3.65 inboard SFB‐8113 8.64 Volvo Penta MD2 11.56 4 diesel 3.65 inboard SFC‐3416 8.00 Volvo Penta MD2 11.56 4 diesel 3.65 inboard SFC‐3232 7.60 Volvo Penta MD2 11.56 4 diesel 3.65 inboard SFC‐4949 7.60 Volvo Penta MD2 1766 11.56 4 diesel 3.65 inboard SFB‐8356 9.40 Volvo Penta MD2 1967 11.56 4 diesel 3.65 inboard SFC‐4298 6.40 Volvo Penta MD2 1975 11.56 4 diesel 3.65 inboard SFB‐3260 7.00 Volvo Penta MD21 33.57 4 diesel 11.12 inboard SFB‐2425 6.80 Volvo Penta MD21 33.57 4 diesel 11.12 inboard SFC‐7838 12.00 Volvo Penta MD21 33.57 4 diesel 11.12 inboard SFC‐4461 10.50 Volvo Penta MD21 33.57 4 diesel 11.12 inboard SFC‐3485 10.30 Volvo Penta MD21 33.57 4 diesel 11.12 inboard SFC‐3325 12.80 Volvo Penta MD21 33.57 4 diesel 11.12 inboard SFC‐4022 12.50 Volvo Penta MD21 33.57 4 diesel 11.12 inboard SFC‐3533 12.20 Volvo Penta MD21 33.57 4 diesel 11.12 inboard SFC‐3337 11.57 Volvo Penta MD21 33.57 4 diesel 11.12 inboard SFC‐3827 11.57 Volvo Penta MD21 33.57 4 diesel 11.12 inboard SFC‐3499 11.10 Volvo Penta MD21 33.57 4 diesel 11.12 inboard SFB‐7309 10.93 Volvo Penta MD21 33.57 4 diesel 11.12 inboard SFC‐3312 10.54 Volvo Penta MD21 33.57 4 diesel 11.12 inboard SFC‐3559 10.50 Volvo Penta MD21 33.57 4 diesel 11.12 inboard SFC‐3376 9.30 Volvo Penta MD21 33.57 4 diesel 11.12 inboard SFC‐4002 10.75 Volvo Penta MD21 110S 33.57 4 diesel 11.12 inboard SFB‐7563 10.00 Volvo Penta MD21 1971 33.57 4 diesel 11.12 inboard SFC‐4968 10.50 Volvo Penta MD21 1973 33.57 4 diesel 11.12 inboard SFC‐5026 15.05 Volvo Penta MD21 1976 33.57 4 diesel 11.12 inboard 210

SFC‐5438 7.50 Volvo Penta MD21 1980 33.57 4 diesel 11.12 inboard SFC‐4008 11.20 Volvo Penta MD21 1980 33.57 4 diesel 11.12 inboard SFB‐7684 8.00 Volvo Penta MD21 1983 33.57 4 diesel 11.12 inboard SFC‐4066 11.60 Volvo Penta MD21 1983 33.57 4 diesel 11.12 inboard SFB‐8117 8.00 Volvo Penta MD21 1984 33.57 4 diesel 11.12 inboard SFC‐5119 10.25 Volvo Penta MD21 1984 33.57 4 diesel 11.12 inboard SFC‐4857 7.00 Volvo Penta MD21 1985 33.57 4 diesel 11.12 inboard SFC‐3525 12.50 Volvo Penta MD21 A 33.57 4 diesel 11.12 inboard SFC‐7291 10.50 Volvo Penta MD21, 1976 33.57 4 diesel 11.12 inboard SFC‐6724 12.93 Volvo Penta MD21,1981 33.57 4 diesel 11.12 inboard SFC‐3433 12.40 Volvo Penta MD21A 33.57 4 diesel 11.12 inboard SFB‐8689 12.10 Volvo Penta MD21A 33.57 4 diesel 11.12 inboard SFC‐3617 10.50 Volvo Penta MD21A 33.57 4 diesel 11.12 inboard SFC‐3988 10.50 Volvo Penta MD21A 33.57 4 diesel 11.12 inboard SFC‐3340 10.50 Volvo Penta MD21A 33.57 4 diesel 11.12 inboard SFB‐8729 10.30 Volvo Penta MD21A 33.57 4 diesel 11.12 inboard SFB‐8913 10.50 Volvo Penta MD21A 1974 33.57 4 diesel 11.12 inboard SFB‐5013 7.70 Volvo Penta MD21A 1976 33.57 4 diesel 11.12 inboard SFC‐4475 12.50 Volvo Penta MD21A 1977 33.57 4 diesel 11.12 inboard SFC‐4999 11.05 Volvo Penta MD21A 1979 33.57 4 diesel 11.12 inboard SFC‐2523 7.70 Volvo Penta MD21A 1980 33.57 4 diesel 11.12 inboard SFC‐6541 12.50 Volvo Penta MD21A, 1977 33.57 4 diesel 11.12 inboard SFC‐4651 12.95 Volvo Penta MD21B 33.57 4 diesel 11.12 inboard SFB‐7014 11.57 Volvo Penta MD21B 33.57 4 diesel 11.12 inboard SFC‐3399 11.05 Volvo Penta MD21B 33.57 4 diesel 11.12 inboard SFC‐5444 10.75 Volvo Penta MD21B 33.57 4 diesel 11.12 inboard SFC‐3310 10.54 Volvo Penta MD21B 33.57 4 diesel 11.12 inboard SFC‐5480 11.05 Volvo Penta MD21B 1979 33.57 4 diesel 11.12 inboard SFC‐4270 10.54 Volvo Penta MD21B 1980 33.57 4 diesel 11.12 inboard SFC‐3927 10.54 Volvo Penta MD21B 1982 33.57 4 diesel 11.12 inboard 211

SFC‐5450 11.65 Volvo Penta MD21B 1983 33.57 4 diesel 11.12 inboard SFB‐8020 10.54 Volvo Penta MD21B 1983 33.57 4 diesel 11.12 inboard SFC‐6180 11.30 Volvo Penta MD21B 1984 33.57 4 diesel 11.12 inboard SFC‐7837 11.60 Volvo Penta MD21B,1985 33.57 4 diesel 11.12 inboard SFC‐6846 10.54 Volvo Penta MD21B,‐79 33.57 4 diesel 11.12 inboard SFC‐6988 10.54 Volvo Penta MD21B,‐82 33.57 4 diesel 11.12 inboard SFC‐5365 13.38 Volvo Penta MD22 44.01 4 diesel 4.00 inboard SFC‐6060 11.85 Volvo Penta MD22 44.01 4 diesel 4.00 inboard SFC‐5916 11.85 Volvo Penta MD22 44.01 4 diesel 4.00 inboard SFC‐3425 7.25 Volvo Penta MD22 44.01 4 diesel 4.00 inboard SFC‐5509 10.87 Volvo Penta MD22 1991 44.01 4 diesel 4.00 inboard SFC‐4639 11.31 Volvo Penta MD22 1995 44.01 4 diesel 4.00 inboard SFC‐6767 11.31 Volvo Penta MD22, 1995 44.01 4 diesel 4.00 inboard SFC‐6411 12.22 Volvo Penta MD22, 1998 44.01 4 diesel 4.00 inboard SFC‐6123 10.45 Volvo Penta MD22, 1999 44.01 4 diesel 4.00 inboard SFC‐7937 11.57 Volvo Penta MD22, 2000 44.01 4 diesel 4.00 inboard SFC‐5157 12.10 Volvo Penta MD22A 1991 44.01 4 diesel 4.00 inboard SFC‐3751 10.20 Volvo Penta MD22L 1993 44.01 4 diesel 4.00 inboard SFC‐5927 12.19 Volvo Penta MD22L 1994 44.01 4 diesel 4.00 inboard SFC‐5428 10.97 Volvo Penta MD22L 1995 44.01 4 diesel 4.00 inboard SFC‐5228 13.16 Volvo Penta MD22L 1997 44.01 4 diesel 4.00 inboard SFC‐5680 10.75 Volvo Penta MD22L 1998 44.01 4 diesel 4.00 inboard SFC‐8270 11.75 Volvo Penta MD22L, 1999 44.01 4 diesel 4.00 inboard SFC‐6738 10.54 Volvo Penta MD22L, 2001 44.01 4 diesel 4.00 inboard SFC‐6715 11.20 Volvo Penta MD22L, ‐97 44.01 4 diesel 4.00 inboard SFC‐7943 12.10 Volvo Penta MD22P 44.01 4 diesel 4.00 inboard SFC‐6280 11.31 Volvo Penta MD22P, 2000 44.01 4 diesel 4.00 inboard SFB‐7964 7.85 Volvo Penta MD29 68.63 4 diesel 22.73 inboard SFC‐3762 10.70 Volvo Penta MD29 68.63 4 diesel 22.73 inboard SFC‐4935 11.50 Volvo Penta MD29 1969 68.63 4 diesel 22.73 inboard 212

SFB‐8578 7.90 Volvo Penta MD2A 1978 11.56 4 diesel 3.68 inboard SFB‐6163 5.50 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐8832 6.90 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐4640 12.00 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFB‐8685 11.07 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐3459 10.88 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐3567 9.90 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐3531 9.89 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFB‐8395 9.81 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐3262 9.81 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐6315 9.81 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐3538 9.81 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐3604 9.56 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐3621 9.50 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐3629 9.43 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐3394 9.36 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐3535 9.36 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐4092 9.36 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐3505 9.30 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐3844 7.60 Volvo Penta MD2B 17.16 4 diesel 5.15 inboard SFC‐4625 7.97 Volvo Penta MD2B 1969 17.16 4 diesel 5.15 inboard SFC‐5272 9.71 Volvo Penta MD2B 1972 17.16 4 diesel 5.15 inboard SFB‐7481 8.05 Volvo Penta MD2B 1973 17.16 4 diesel 5.15 inboard SFB‐5192 6.90 Volvo Penta MD2B 1974 17.16 4 diesel 5.15 inboard SFB‐7551 9.36 Volvo Penta MD2B 1974 17.16 4 diesel 5.15 inboard SFB‐7003 9.82 Volvo Penta MD2B 1975 17.16 4 diesel 5.15 inboard SFC‐4802 10.42 Volvo Penta MD2B 1976 17.16 4 diesel 5.15 inboard SFC‐5114 9.36 Volvo Penta MD2B 1976 17.16 4 diesel 5.15 inboard SFC‐4502 9.82 Volvo Penta MD2B 1977 17.16 4 diesel 5.15 inboard SFC‐6173 9.50 Volvo Penta MD2B 1977 17.16 4 diesel 5.15 inboard 213

SFC‐5189 9.40 Volvo Penta MD2B, 1977 17.16 4 diesel 5.15 inboard SFB‐7332 9.81 Volvo Penta MD2C 1975 17.16 4 diesel 5.15 inboard SFB‐7765 8.00 Volvo Penta MD3 26.86 4 diesel 7.84 inboard SFC‐8502 10.40 Volvo Penta MD3 26.86 4 diesel 7.84 inboard SFC‐3236 9.89 Volvo Penta MD3 26.86 4 diesel 7.84 inboard SFC‐3534 9.55 Volvo Penta MD3 26.86 4 diesel 7.84 inboard SFC‐3426 8.00 Volvo Penta MD3 26.86 4 diesel 7.84 inboard SFC‐5806 11.82 Volvo Penta MD3 1975 26.86 4 diesel 7.84 inboard SFB‐6282 7.62 Volvo Penta MD3 1979 26.86 4 diesel 7.84 inboard SFC‐4256 11.53 Volvo Penta MD3 1982 26.86 4 diesel 7.84 inboard SFC‐5860 9.30 Volvo Penta MD3 1984 26.86 4 diesel 7.84 inboard SFC‐3401 11.75 Volvo Penta MD‐30 41.78 4 diesel 14.74 inboard SFC‐6183 14.13 Volvo Penta MD30 1986 41.78 4 diesel 14.74 inboard SFB‐9979 9.60 Volvo Penta MD30 1987 41.78 4 diesel 14.74 inboard SFC‐8092 11.75 Volvo Penta MD30, 1989 41.78 4 diesel 14.74 inboard SFC‐3464 12.80 Volvo Penta MD30A 41.78 4 diesel 14.74 inboard SFC‐4557 12.70 Volvo Penta MD31 1989 46.25 4 diesel 15.24 inboard SFC‐7546 13.00 Volvo Penta MD31, 1994 46.25 4 diesel 15.24 inboard SFC‐6737 11.75 Volvo Penta MD31, ‐94 46.25 4 diesel 15.24 inboard SFC‐2816 12.70 Volvo Penta MD31A 1991 46.25 4 diesel 15.24 inboard SFC‐6420 12.93 Volvo Penta MD31A, 1988 46.25 4 diesel 15.24 inboard SFC‐7296 11.55 Volvo Penta MD31A, 1990 46.25 4 diesel 15.24 inboard SFC‐6573 13.70 Volvo Penta MD31A, 1991 46.25 4 diesel 15.24 inboard SFC‐3529 10.85 Volvo Penta MD32A 51.47 4 diesel 16.96 inboard SFC‐5493 9.25 Volvo Penta MD3B 26.86 4 diesel 7.84 inboard SFC‐3645 8.75 Volvo Penta MD3B 26.86 4 diesel 7.84 inboard SFC‐3406 11.60 Volvo Penta MD3B 26.86 4 diesel 7.84 inboard SFC‐5064 10.35 Volvo Penta MD3B 26.86 4 diesel 7.84 inboard SFC‐3732 10.30 Volvo Penta MD3B 26.86 4 diesel 7.84 inboard SFC‐3840 10.30 Volvo Penta MD3B 26.86 4 diesel 7.84 inboard 214

SFB‐8680 9.89 Volvo Penta MD3B 26.86 4 diesel 7.84 inboard SFC‐3481 6.60 Volvo Penta MD3B 1976 26.86 4 diesel 7.84 inboard SFB‐7104 6.80 Volvo Penta MD3B 1977 26.86 4 diesel 7.84 inboard SFC‐8414 11.40 Volvo Penta MD3B, 1974 26.86 4 diesel 7.84 inboard SFC‐8706 13.80 Volvo Penta MD3B, 1975 26.86 4 diesel 7.84 inboard SFC‐7016 10.30 Volvo Penta MD3B, 1975 26.86 4 diesel 7.84 inboard SFC‐2560 8.00 Volvo Penta MD4 081638 29.09 4 diesel 12.02 inboard SFC‐4043 10.00 Volvo Penta MD40 58.93 4 diesel 21.49 inboard SFB‐8769 8.10 Volvo Penta MD40 1977 58.93 4 diesel 21.49 inboard SFB‐6107 8.70 Volvo Penta MD40 1979 58.93 4 diesel 21.49 inboard SFC‐4281 8.15 Volvo Penta MD40 1982 58.93 4 diesel 21.49 inboard SFC‐4654 8.10 Volvo Penta MD40 1983 58.93 4 diesel 21.49 inboard SFC‐6220 10.10 Volvo Penta MD40A 58.93 4 diesel 21.49 inboard SFC‐5735 10.10 Volvo Penta MD47 1961 52.97 4 diesel 15.12 inboard SFC‐7364 10.36 Volvo Penta MD47 B 52.97 4 diesel 14.78 inboard SFC‐4077 11.00 Volvo Penta MD47B 1976 52.97 4 diesel 14.78 inboard SFC‐3385 8.03 Volvo Penta MD4A 29.09 4 diesel 12.02 inboard SFC‐3856 8.50 Volvo Penta MD5 5.59 4 diesel 1.97 inboard SFC‐3483 11.85 Volvo Penta MD50A 70.12 4 diesel 21.01 inboard SFC‐3497 11.80 Volvo Penta MD50A 70.12 4 diesel 21.01 inboard SFC‐3434 9.10 Volvo Penta MD50A 1967 70.12 4 diesel 21.01 inboard SFC‐3882 8.12 Volvo Penta MD5A 5.59 4 diesel 1.97 inboard SFC‐3342 7.95 Volvo Penta MD5A 5.59 4 diesel 1.97 inboard SFC‐3711 7.70 Volvo Penta MD5A 5.59 4 diesel 1.97 inboard SFC‐4262 7.95 Volvo Penta MD5A110S 1979 5.59 4 diesel 1.97 inboard SFC‐3731 9.30 Volvo Penta MD5B 5.59 4 diesel 1.97 inboard SFC‐3389 8.85 Volvo Penta MD5B 5.59 4 diesel 1.97 inboard SFC‐3441 8.34 Volvo Penta MD5B 5.59 4 diesel 1.97 inboard SFC‐3733 7.95 Volvo Penta MD5B 5.59 4 diesel 1.97 inboard SFB‐8609 7.95 Volvo Penta MD5B 5.59 4 diesel 1.97 inboard 215

SFC‐3282 7.95 Volvo Penta MD5B 5.59 4 diesel 1.97 inboard SFC‐3888 7.70 Volvo penta MD5B 5.59 4 diesel 1.97 inboard SFC‐5976 8.03 Volvo Penta MD5B 1970 5.59 4 diesel 1.97 inboard SFC‐5229 7.90 Volvo Penta MD5B 1980 5.59 4 diesel 1.97 inboard SFC‐4076 7.65 Volvo Penta MD5B 1980 5.59 4 diesel 1.97 inboard SFC‐3454 8.22 Volvo Penta MD5C 5.59 4 diesel 1.97 inboard SFC‐5688 9.14 Volvo Penta MD6 7.46 4 diesel 2.63 inboard SFC‐3367 8.03 Volvo Penta MD6 7.46 4 diesel 2.63 inboard SFB‐4423 11.20 Volvo Penta MD67 52.22 4 diesel 14.41 inboard SFC‐3267 9.17 Volvo Penta MD6A 7.46 4 diesel 2.63 inboard SFC‐3581 9.16 Volvo Penta MD6A 7.46 4 diesel 2.63 inboard SFC‐3683 9.14 Volvo Penta MD6A 7.46 4 diesel 2.63 inboard SFC‐3708 8.80 Volvo Penta MD6a 7.46 4 diesel 2.63 inboard SFC‐3554 8.80 Volvo Penta MD6A 7.46 4 diesel 2.63 inboard SFC‐3335 8.50 Volvo Penta MD6A 7.46 4 diesel 2.63 inboard SFC‐3390 8.25 Volvo Penta MD6A 7.46 4 diesel 2.63 inboard SFC‐3626 8.25 Volvo Penta MD6A 7.46 4 diesel 2.63 inboard SFC‐4249 8.25 Volvo Penta MD6A 1976 7.46 4 diesel 2.63 inboard SFC‐8643 9.14 Volvo Penta MD6A, 1974 7.46 4 diesel 2.63 inboard SFC‐4673 7.70 Volvo Penta MD6A, 1975 7.46 4 diesel 2.63 inboard SFB‐7333 9.14 Volvo Penta MD6B 7.46 4 diesel 2.63 inboard SFC‐3702 8.25 Volvo Penta MD6B 7.46 4 diesel 2.63 inboard SFC‐3492 8.03 Volvo Penta MD6B 7.46 4 diesel 2.63 inboard SFC‐7378 9.50 Volvo Penta MD6B, 1976 7.46 4 diesel 2.63 inboard SFC‐8060 9.40 Volvo Penta MD7 9.70 4 diesel 3.19 inboard SFC‐3296 9.40 Volvo Penta MD7 9.70 4 diesel 3.19 inboard SFC‐3688 9.15 Volvo Penta MD7 9.70 4 diesel 3.19 inboard SFB‐6543 12.00 Volvo Penta MD70 1977 92.65 4 diesel 26.89 inboard SFC‐5736 8.40 Volvo Penta MD7A 9.70 4 diesel 3.19 inboard SFC‐5524 9.60 Volvo Penta MD7A 9.70 4 diesel 3.19 inboard 216

SFC‐3673 9.48 Volvo Penta MD7A 9.70 4 diesel 3.19 inboard SFC‐3536 9.41 Volvo Penta MD7A 9.70 4 diesel 3.19 inboard SFC‐3298 9.20 Volvo Penta MD7A 9.70 4 diesel 3.19 inboard SFC‐3430 9.14 Volvo Penta MD7A 9.70 4 diesel 3.19 inboard SFC‐3623 9.14 Volvo Penta MD7A 9.70 4 diesel 3.19 inboard SFC‐3380 8.40 Volvo Penta MD7A 9.70 4 diesel 3.19 inboard SFC‐3356 8.35 Volvo Penta MD7A 9.70 4 diesel 3.19 inboard SFC‐4896 8.03 Volvo Penta MD7A 9.70 4 diesel 3.19 inboard SFC‐5207 8.03 Volvo Penta MD7A 9.70 4 diesel 3.19 inboard SFC‐3344 8.00 Volvo Penta MD7A 9.70 4 diesel 3.19 inboard SFC‐5746 9.41 Volvo Penta MD7A 1978 9.70 4 diesel 3.19 inboard SFC‐4017 8.80 Volvo Penta MD7A 1978 9.70 4 diesel 3.19 inboard SFC‐4064 8.03 Volvo Penta MD7A 1978 9.70 4 diesel 3.19 inboard SFC‐4537 7.70 Volvo Penta MD7A 1978 9.70 4 diesel 3.19 inboard SFC‐4508 10.80 Volvo Penta MD7A 1981 9.70 4 diesel 3.19 inboard SFC‐3574 10.55 Volvo Penta MD7B 12.68 4 diesel 4.22 inboard SFC‐3225 9.94 Volvo Penta MD7B 12.68 4 diesel 4.22 inboard SFC‐3540 8.90 Volvo Penta MD7B 12.68 4 diesel 4.22 inboard SFC‐3360 8.90 Volvo Penta MD7B 12.68 4 diesel 4.22 inboard SFC‐3910 8.56 Volvo Penta MD7B 12.68 4 diesel 4.22 inboard SFC‐5945 9.30 Volvo Penta MD7B 1981 12.68 4 diesel 4.22 inboard SFC‐5352 14.20 Volvo Penta MD96 1959 94.74 4 diesel 26.45 inboard SFC‐4725 17.50 Volvo Penta MD96 1960 94.74 4 diesel 26.45 inboard SFC‐5128 17.93 Volvo Penta MD96B 94.74 4 diesel 26.00 inboard SFB‐9552 7.45 Volvo Penta TAMD 30A 78.33 4 diesel 25.34 inboard SFB‐9256 8.40 Volvo Penta TAMD 31 82.06 4 diesel 21.72 inboard SFB‐8746 8.40 Volvo Penta TAMD30 1986 78.33 4 diesel 25.34 inboard SFC‐2878 8.00 Volvo Penta TAMD31B 82.06 4 diesel 21.72 inboard SFC‐3660 8.25 Volvo Penta TAMD40 110.41 4 diesel 38.32 inboard SFC‐4986 9.30 Volvo Penta TAMD40A 1982 110.41 4 diesel 38.32 inboard 217

SFC‐3524 9.20 Volvo Penta TAMD41 126.82 4 diesel 35.81 inboard SFC‐4060 8.25 Volvo Penta TAMD41A 1989 126.82 4 diesel 35.81 inboard SFC‐4809 10.23 Volvo Penta TAMD41B 126.82 4 diesel 35.81 inboard SFC‐3672 10.50 Volvo Penta TAMD60 143.23 4 diesel 38.76 inboard SFB‐9084 8.10 Volvo Penta TDM 40 104.44 4 diesel 34.40 inboard SFC‐6357 13.22 Volvo Penta TMD 22 58.19 4 diesel 4.50 inboard SFC‐3744 12.95 Volvo Penta TMD 31 B 74.60 4 diesel 22.82 inboard SFC‐8335 10.97 Volvo Penta TMD 40 A 87.28 4 diesel 31.83 inboard SFC‐6281 10.42 Volvo Penta TMD100A 196.94 4 diesel 51.25 inboard SFC‐5481 12.93 Volvo Penta TMD22A 1997 58.19 4 diesel 4.50 inboard SFB‐7858 8.10 Volvo Penta TMD30 64.16 4 diesel 22.27 inboard SFB‐7759 8.00 Volvo Penta TMD30 64.16 4 diesel 22.27 inboard SFB‐8451 8.00 Volvo Penta TMD30 64.16 4 diesel 22.27 inboard SFC‐4631 9.14 Volvo Penta TMD31 74.60 4 diesel 22.82 inboard SFC‐5081 13.62 Volvo Penta TMD31 1990 74.60 4 diesel 22.82 inboard SFC‐6614 10.00 Volvo Penta TMD31,1990 74.60 4 diesel 22.82 inboard SFC‐3817 13.30 Volvo Penta TMD31A 74.60 4 diesel 22.82 inboard SFC‐5082 11.85 Volvo Penta TMD40 1982 104.44 4 diesel 34.40 inboard SFC‐2477 8.96 Volvo Penta TMD40 1983 104.44 4 diesel 34.40 inboard SFC‐3906 10.35 Volvo Penta TMD41MS4 1988 111.90 4 diesel 35.54 inboard SFB‐8743 11.97 Volvo Penta TMD50B 1982 89.74 4 diesel 27.32 inboard SFB‐2307 11.15 Volvo Penta TMD70 1978 126.82 4 diesel 35.00 inboard SFB‐7652 12.85 Volvo Penta TMD70B 1973 116.37 4 diesel 30.80 inboard SFB‐6807 15.13 Volvo Penta TMD96 119.36 4 diesel 22.59 inboard SFB‐6368 15.08 Volvo Penta TMD96 119.36 4 diesel 22.59 inboard SFB‐6634 14.56 Volvo Penta TMD96 Diesel 119.36 4 diesel 22.59 inboard SFB‐4787 14.98 Volvo Penta TMD96B 1957 119.36 4 diesel 22.59 inboard SFC‐5858 13.70 Volvo TAMD 120B 1986 253.64 4 diesel 63.26 inboard SFC‐2813 8.30 Volvo TAMD41/MS4 126.82 4 diesel 35.81 inboard SFC‐8258 10.19 VP AQAD40B, 1984 115.63 4 diesel 26.00 inboard 218

SFC‐6509 11.89 VP MD 17 C 26.11 4 diesel 7.58 inboard SFC‐7411 11.30 VP MD 17 C, diesel 26.11 4 diesel 7.58 inboard SFC‐7230 11.05 VP MD21A, 1977 33.57 4 diesel 11.12 inboard SFC‐8100 10.68 VP TAMD 61 A, 1992 170.09 4 diesel 45.02 inboard SFC‐3289 9.42 Yanmar 1GM 5.59 4 diesel 1.90 inboard SFC‐3548 9.09 Yanmar 1GM 5.59 4 diesel 1.90 inboard SFC‐2233 5.23 Yanmar 1GM 1982 5.59 4 diesel 1.90 inboard SFC‐3509 7.90 Yanmar 1GM10 6.71 4 diesel 2.30 inboard SFC‐8869 10.30 Yanmar 2GM 11.19 4 diesel 3.79 inboard SFC‐3588 9.87 Yanmar 2GM 11.19 4 diesel 3.79 inboard SFC‐3269 8.86 Yanmar 2GM 11.19 4 diesel 3.79 inboard SFC‐8392 11.10 Yanmar 2GM 20, 1999 13.43 4 diesel 4.55 inboard SFC‐8694 8.25 Yanmar 2GM, 1983 11.19 4 diesel 3.79 inboard SFC‐7269 9.65 Yanmar 2GM, 1991 11.19 4 diesel 3.79 inboard SFC‐7576 7.80 Yanmar 2GM20 13.43 4 diesel 4.55 inboard SFC‐3302 9.45 Yanmar 2GM20 13.43 4 diesel 4.55 inboard SFC‐3349 9.60 Yanmar 2GM20 1986 13.43 4 diesel 4.55 inboard SFC‐6804 8.03 Yanmar 2GM20F 13.43 4 diesel 4.55 inboard SFC‐3413 9.40 Yanmar 2GM20F 13.43 4 diesel 4.55 inboard SFC‐3605 8.20 Yanmar 2GM20F 13.43 4 diesel 4.55 inboard SFC‐5230 8.70 Yanmar 2GM20F 1987 13.43 4 diesel 4.55 inboard SFC‐7869 9.41 Yanmar 2GM20F, 1998 13.43 4 diesel 4.55 inboard SFC‐4608 9.48 Yanmar 2GMF 1990 11.19 4 diesel 3.79 inboard SFB‐9947 6.40 Yanmar 2QM15 11.19 4 diesel 3.71 inboard SFC‐3429 10.90 Yanmar 2QM15GH 11.19 4 diesel 3.71 inboard SFB‐5120 6.80 Yanmar 2QM20 16.41 4 diesel 4.05 inboard SFB‐5578 6.30 Yanmar 2QM20 16.41 4 diesel 4.05 inboard SFC‐5954 10.72 Yanmar 2QM20 16.41 4 diesel 4.05 inboard SFC‐3351 9.81 Yanmar 2QM20 16.41 4 diesel 4.05 inboard SFC‐6257 9.80 Yanmar 2QM20 16.41 4 diesel 4.05 inboard 219

SFC‐3700 9.36 Yanmar 2QM20 16.41 4 diesel 4.05 inboard SFB‐7770 8.15 Yanmar 2QM20 1976 16.41 4 diesel 4.05 inboard SFB‐8420 6.55 Yanmar 2QM20 1977 16.41 4 diesel 4.05 inboard SFC‐4035 11.00 Yanmar 2QM20 1977 16.41 4 diesel 4.05 inboard SFC‐4642 9.81 Yanmar 2QM20 1977 16.41 4 diesel 4.05 inboard SFC‐2162 7.00 Yanmar 2QM20 1979 16.41 4 diesel 4.05 inboard SFB‐8259 9.81 Yanmar 2QM20 1979 16.41 4 diesel 4.05 inboard SFB‐8054 6.75 Yanmar 2QM20 1980 16.41 4 diesel 4.05 inboard SFC‐5430 9.81 Yanmar 2QM20 1980 16.41 4 diesel 4.05 inboard SFC‐6238 9.40 Yanmar 2QM20 1988 16.41 4 diesel 4.05 inboard SFB‐8165 7.30 Yanmar 2QM20 diesel 16.41 4 diesel 4.05 inboard SFC‐6535 9.81 Yanmar 2QM20, 1977 16.41 4 diesel 4.05 inboard SFC‐6310 9.89 Yanmar 2QM20, 1979 16.41 4 diesel 4.05 inboard SFB‐9505 7.75 Yanmar 2QM20, 1980 16.41 4 diesel 4.05 inboard SFB‐6825 9.84 Yanmar 2QM2081008 1976 16.41 4 diesel 4.05 inboard SFC‐4046 9.81 Yanmar 2QM20H 1980 16.41 4 diesel 4.05 inboard SFC‐8861 8.57 Yanmar 2YM15 E00382 10.15 4 diesel 3.50 inboard SFB‐9939 6.10 Yanmar 3 HM 1984 22.39 4 diesel 7.24 inboard SFC‐7176 10.00 Yanmar 3 HM 35 25.36 4 diesel 8.36 inboard SFC‐6761 12.50 Yanmar 3 HM, 1984 22.38 4 diesel 7.24 inboard SFC‐6835 10.70 Yanmar 3GH30F 2002 20.14 4 diesel 6.63 inboard SFC‐3915 10.30 Yanmar 3GM 30 FG EU, 2002 20.14 4 diesel 6.63 inboard SFC‐8318 10.35 Yanmar 3GM 30F, 2003 20.14 4 diesel 6.63 inboard SFC‐3458 9.81 Yanmar 3GM30 20.14 4 diesel 6.63 inboard SFC‐8798 9.30 Yanmar 3GM30, 2003 20.14 4 diesel 6.63 inboard SFC‐7131 10.85 Yanmar 3GM30,‐87 20.14 4 diesel 6.63 inboard SFC‐3491 9.81 Yanmar 3GM30F 20.14 4 diesel 6.63 inboard SFC‐4888 9.81 Yanmar 3GM30F 20.14 4 diesel 6.63 inboard SFC‐3379 9.80 Yanmar 3GM30F 20.14 4 diesel 6.63 inboard SFC‐5866 9.40 Yanmar 3GM30F 1985 20.14 4 diesel 6.63 inboard 220

SFC‐4957 11.40 Yanmar 3GM30F 1987 20.14 4 diesel 6.63 inboard SFC‐6816 9.71 Yanmar 3GM30F, 1988 20.14 4 diesel 6.63 inboard SFC‐6719 10.00 Yanmar 3GM30F, 1994 20.14 4 diesel 6.63 inboard SFC‐7302 9.40 Yanmar 3GM30F, 1998 20.14 4 diesel 6.63 inboard SFC‐6137 11.50 Yanmar 3GM30F, 1998 20.14 4 diesel 6.63 inboard SFC‐6855 11.07 Yanmar 3GM30F, 1999 20.14 4 diesel 6.63 inboard SFC‐7534 11.10 Yanmar 3GM30F, 2000 20.14 4 diesel 6.63 inboard SFC‐8025 10.28 Yanmar 3GM30F, 2002 20.14 4 diesel 6.63 inboard SFC‐5256 11.66 Yanmar 3GM30F4449 20.14 4 diesel 6.63 inboard SFC‐3451 11.00 Yanmar 3GM30FC 20.14 4 diesel 6.63 inboard SFC‐7065 11.03 Yanmar 3GM30FC, 1999 20.14 4 diesel 6.63 inboard SFB‐8653 9.81 Yanmar 3HM 1982 22.38 4 diesel 7.24 inboard SFC‐6443 11.20 YANMAR 3HM 35SD30 25.36 4 diesel 8.36 inboard SFB‐8752 10.28 Yanmar 3HM 5794 1982 22.38 4 diesel 7.24 inboard SFC‐7932 11.07 Yanmar 3HM, 1987 22.38 4 diesel 7.24 inboard SFC‐5236 9.36 Yanmar 3HM35 25.36 4 diesel 8.36 inboard SFC‐5917 11.10 Yanmar 3HM35F 1993 25.36 4 diesel 8.36 inboard SFC‐8230 11.07 Yanmar 3HM35HP 25.36 4 diesel 8.36 inboard SFC‐8640 9.55 Yanmar 3JH 4BE 29.09 4 diesel 8.20 inboard SFC‐8622 11.28 Yanmar 3JH2TE Diesel 33.57 4 diesel 9.79 inboard SFC‐8302 12.15 Yanmar 3JH4E 29.09 4 diesel 8.00 inboard SFC‐8603 11.35 Yanmar 3JH4E 29.09 4 diesel 8.00 inboard SFC‐7579 11.40 Yanmar 3JH4E, 2005 29.09 4 diesel 8.00 inboard SFC‐7988 10.35 Yanmar 3YM20,2005 15.67 4 diesel 5.40 inboard SFC‐7946 10.21 Yanmar 3YM30 21.71 4 diesel 7.00 inboard SFC‐8511 10.75 Yanmar 3YM30, 2005 21.71 4 diesel 7.00 inboard SFC‐8871 11.90 Yanmar 3YM30C, 2004 21.71 4 diesel 7.00 inboard SFC‐6786 14.00 Yanmar 4JH3 TBE 53.71 4 diesel 16.09 inboard SFC‐8069 12.10 Yanmar 4JH36B4E 39.54 4 diesel 11.22 inboard SFC‐7046 11.30 Yanmar 4JH3‐BE 39.54 4 diesel 11.22 inboard 221

SFC‐6686 13.39 Yanmar 4JH3‐TBE 53.71 4 diesel 16.09 inboard SFC‐8040 13.50 Yanmar 4JH3‐TBE 2,6 53.71 4 diesel 16.09 inboard SFC‐7885 13.39 Yanmar 4JH3‐TBE, 2003 53.71 4 diesel 16.09 inboard SFC‐7255 11.55 Yanmar 4JH4‐E 41.03 4 diesel 11.90 inboard SFC‐7841 11.55 Yanmar 4JH4‐E 41.03 4 diesel 11.90 inboard SFC‐7334 12.20 Yanmar 4JH4‐E, 2005 41.03 4 diesel 11.90 inboard SFC‐8769 13.09 Yanmar 4JH4E, 2005 41.03 4 diesel 11.90 inboard SFC‐8180 13.09 Yanmar 4JH4E, 2006 41.03 4 diesel 11.90 inboard SFC‐7886 11.32 Yanmar 4JH4E, 2006 41.03 4 diesel 11.90 inboard SFC‐3157 7.60 Yanmar 4JH‐DTE30679 1987 57.44 4 diesel 16.31 inboard SFC‐7254 7.50 Yanmar 4LHA‐STP 171.58 4 diesel 50.00 inboard SFC‐8748 12.20 Yanmar 54 HK 4Jh4E 40.28 diesel 0.00 inboard SFC‐6296 8.60 Yanmar 6LPSTE 223.80 4 diesel 69.00 inboard SFC‐7400 9.79 Yanmar 6LY‐UTE, 1999 261.10 4 diesel 70.00 inboard SFB‐5045 7.10 Yanmar Diesel 2QM20 16.41 4 diesel 4.05 inboard SFB‐8720 10.00 Yanmar diesel 2QM20 16.41 4 diesel 4.05 inboard SFC‐6254 10.30 Yanmar Diesel 3GM30F 1991 20.14 4 diesel 6.63 inboard SFB‐7524 8.00 Yanmar I GM 1982 5.59 4 diesel 1.90 inboard SFC‐3620 8.89 Yanmar IGM 5.59 4 diesel 1.90 inboard SFC‐3275 8.03 Yanmar IGM10 6.71 4 diesel 2.30 inboard SFC‐5946 6.50 Yanmar SB12 7.46 4 diesel 2.67 inboard SFB‐7315 8.34 Yanmar SB8 5.22 4 diesel 1.98 inboard SFC‐4182 6.00 Yanmar SB8 1978 5.22 4 diesel 1.98 inboard SFC‐6406 8.43 Yanmar SB8, 1982 5.22 4 diesel 1.98 inboard SFC‐5171 9.44 Yanmar SB8G 5.22 4 diesel 1.98 inboard SFC‐3583 8.34 Yanmar SB8G 5.22 4 diesel 1.98 inboard SFC‐5922 6.00 Yanmar SB8G 1977 5.22 4 diesel 1.98 inboard SFB‐7618 8.03 Yanmar SB8G 1981 5.22 4 diesel 1.98 inboard SFC‐6854 7.70 Yanmar SB8G, 1977 5.22 4 diesel 1.98 inboard SFC‐4881 9.92 Yanmar YSM12 7.46 4 diesel 2.59 inboard 222

SFC‐3331 9.35 Yanmar YSM12 7.46 4 diesel 2.59 inboard SFC‐3852 9.81 Yanmar YSM12G 7.46 4 diesel 2.59 inboard SFC‐7049 8.23 Yanmar YSM12G 82 7.46 4 diesel 2.59 inboard SFC‐3403 9.35 Yanmar YSM12G80 7.46 4 diesel 2.59 inboard SFC‐3579 8.04 Yanmar YSM8G 5.22 4 diesel 1.81 inboard SFC‐7229 10.75 Yanmar,6LY2A‐STP,‐04 261.10 4 diesel 90.00 inboard SFC‐3327 9.07 Yanmar2GM20F 13.43 4 diesel 4.55 inboard SFC‐3297 11.00 2 Volvo Penta MB2 5.59 4 gasoline 3.00 inboard SFC‐4937 6.00 Albin 0 11 3.73 4 gasoline 1.63 inboard SFB‐8076 8.25 Albin 0,21 1969 7.46 4 gasoline 3.27 inboard SFC‐3997 6.00 Albin 011‐69 3.73 4 gasoline 1.63 inboard SFB‐5705 6.40 Albin 0‐2 7.46 4 gasoline 3.27 inboard SFC‐3423 9.46 Albin 021 7.46 4 gasoline 3.27 inboard SFC‐3523 8.64 Albin 021 7.46 4 gasoline 3.27 inboard SFB‐7398 6.60 Albin 021 1964 7.46 4 gasoline 3.27 inboard SFC‐7369 8.25 Albin 021 Kombi 7.46 4 gasoline 3.27 inboard SFC‐8722 8.25 Albin 021, 1968 7.46 4 gasoline 3.27 inboard SFC‐8411 8.25 Albin 021, 1972 7.46 4 gasoline 3.27 inboard SFC‐4403 8.25 Albin 021‐67 7.46 4 gasoline 3.27 inboard SFC‐5651 8.25 Albin 022 8.95 4 gasoline 4.17 inboard SFC‐3913 7.64 Albin 0‐22 8.95 4 gasoline 4.17 inboard SFC‐3461 9.70 Albin 022 Kombi 8.95 4 gasoline 4.17 inboard SFC‐7979 8.25 Albin 0‐22 kombi, 1970 8.95 4 gasoline 4.17 inboard SFC‐6351 8.81 Albin 0‐22, 1970 8.95 4 gasoline 4.17 inboard SFB‐9245 7.20 Albin 0‐41 17.90 4 gasoline 8.00 inboard SFB‐7441 10.00 Albin O 41 17.90 4 gasoline 8.00 inboard SFB‐7445 8.25 Albin O‐21 bensin 1969 7.46 4 gasoline 3.27 inboard SFC‐5397 8.25 Alvin 022 8.95 4 gasoline 4.17 inboard SFC‐8623 7.10 Honda 90, 2008 67.14 4 gasoline 70.40 outboard SFC‐8551 7.27 Honda BF200AXL, 2007 149.20 4 gasoline 66.81 outboard 223

SFC‐6472 9.10 Honda EF25, 1999 18.65 4 gasoline 4.50 outboard SFC‐8183 7.01 Mercruiser 4,3L MPI Alpha 164.12 4 gasoline 46.18 inboard SFC‐8299 6.13 Mercruiser 5,0 MPI 193.96 4 gasoline 71.17 inboard SFC‐8083 6.47 Mercruiser 5.0, 1994 193.96 4 gasoline 71.17 inboard SFC‐8817 7.20 SUZUKI DF 150, 2007 111.90 4 gasoline 49.78 outboard SFC‐8753 5.73 Suzuki DF140/14001885222, 2008 104.44 4 gasoline 37.48 outboard SFC‐4393 6.10 Yamaha 30 DEOL 1989 22.38 2 gasoline 13.00 outboard SFC‐7586 7.92 Yamaha 4AC 2.98 2 gasoline 2.20 outboard SFC‐4548 5.80 Yamaha 60FEOL 1992 44.76 2 gasoline 23.00 outboard SFC‐5991 6.30 Yamaha 85 1981 63.41 2 gasoline 34.50 outboard SFC‐8297 9.99 Yamaha 9,9 7.39 2 gasoline 5.10 outboard SFC‐4934 8.04 Yamaha 9.9AE 1991 7.39 2 gasoline 5.10 outboard SFC‐7011 6.00 Yamaha 90, 1999 67.14 2 gasoline 34.50 outboard SFC‐7123 3.99 Yamaha F25AES, 2004 18.65 4 gasoline 6.43 outboard

224

Appendix C Fuel Estimation for 805 Boats using Regression&Means

Est. Est. Fuel Est. Power Est. Est. Fuel Consumption Count ID length inboard/outboard type (Kw) Stroke (l/hr) 1 6.1 0 0 52.72 2 25.57 2 7.2 0 0 52.72 2 25.22 3 2.9 0 0 52.72 2 26.53 4 2.0 0 0 52.72 2 26.81 5 8.1 1 0 30.38 2 7.14 6 5.2 0 0 52.72 2 25.83 7 5.0 0 0 52.72 2 25.89 8 4.8 0 0 52.72 2 25.97 9 6.6 0 0 52.72 2 25.42 10 2.3 0 0 52.72 2 26.72 11 2.1 0 0 52.72 2 26.79 12 4.5 0 0 52.72 2 26.06 13 7.1 0 0 52.72 2 25.25 14 7.2 0 0 52.72 2 25.22 15 4.4 0 0 52.72 2 26.09 16 4.1 0 0 52.72 2 26.16 17 4.1 0 0 52.72 2 26.16 18 9.3 1 1 41.35 4 14.06 19 5.0 0 0 52.72 2 25.89 20 6.3 0 0 52.72 2 25.49 21 5.2 0 0 52.72 2 25.84 22 4.3 0 0 52.72 2 26.11 23 3.4 0 0 52.72 2 26.40 24 8.7 1 1 41.35 4 14.22 25 8.2 1 0 30.38 4 11.13 26 2.4 0 0 52.72 2 26.70 27 5.1 0 0 52.72 2 25.88 28 5.1 0 0 52.72 2 25.87 29 4.8 0 0 52.72 2 25.96 30 6.5 0 0 52.72 2 25.44 31 3.9 0 0 52.72 2 26.24 32 2.7 0 0 52.72 2 26.60 33 11.0 1 1 41.35 4 13.52 34 10.2 1 1 41.35 4 13.76 35 12.5 1 1 41.35 4 13.06 37 9.0 1 1 41.35 4 14.14 38 6.4 0 0 52.72 2 25.48 39 9.6 1 1 41.35 4 13.95 225

40 8.2 1 0 30.38 4 11.14 41 10.1 1 1 41.35 4 13.80 42 4.3 0 0 52.72 2 26.11 43 4.4 0 0 52.72 2 26.08 44 4.4 0 0 52.72 2 26.08 45 11.3 1 1 41.35 4 13.45 46 4.3 0 0 52.72 2 26.11 47 4.6 0 0 52.72 2 26.03 48 3.9 0 0 52.72 2 26.23 49 5.9 0 0 52.72 2 25.61 50 5.2 0 0 52.72 2 25.84 51 4.9 0 0 52.72 2 25.94 52 5.0 0 0 52.72 2 25.89 53 5.0 0 0 52.72 2 25.90 54 10.6 1 1 41.35 4 13.65 55 7.3 0 0 52.72 2 25.20 56 4.3 0 0 52.72 2 26.12 57 5.1 0 0 52.72 2 25.86 58 4.9 0 0 52.72 2 25.93 59 5.2 0 0 52.72 2 25.85 60 4.0 0 0 52.72 2 26.21 61 4.7 0 0 52.72 2 26.00 62 2.1 0 0 52.72 2 26.79 63 3.5 0 0 52.72 2 26.35 64 4.5 0 0 52.72 2 26.06 65 4.8 0 0 52.72 2 25.96 66 4.4 0 0 52.72 2 26.10 67 4.4 0 0 52.72 2 26.08 68 4.2 0 0 52.72 2 26.13 69 5.8 0 0 52.72 2 25.67 70 7.6 0 0 52.72 2 25.10 71 6.0 0 0 52.72 2 25.60 72 6.9 0 0 52.72 2 25.31 73 6.0 0 0 52.72 2 25.59 74 6.7 0 0 52.72 2 25.37 75 5.2 0 0 52.72 2 25.84 77 4.2 0 0 52.72 2 26.16 78 4.6 0 0 52.72 2 26.02 79 4.5 0 0 52.72 2 26.05 80 4.7 0 0 52.72 2 25.99 81 7.3 0 0 52.72 2 25.21 82 5.1 0 0 52.72 2 25.86 226

83 4.7 0 0 52.72 2 25.99 84 9.3 1 1 41.35 4 14.05 85 9.2 1 1 41.35 4 14.07 86 10.7 1 1 41.35 4 13.62 87 11.4 1 1 41.35 4 13.41 88 12.5 1 1 41.35 4 13.07 89 9.9 1 1 41.35 4 13.87 90 9.7 1 1 41.35 4 13.93 91 8.8 1 1 41.35 4 14.21 92 4.7 0 0 52.72 2 26.00 93 5.2 0 0 52.72 2 25.85 94 4.7 0 0 52.72 2 25.98 95 6.5 0 0 52.72 2 25.45 96 10.9 1 1 41.35 4 13.55 97 7.0 0 0 52.72 2 25.29 98 9.0 1 1 41.35 4 14.15 99 11.6 1 1 41.35 4 13.35 100 9.9 1 1 41.35 4 13.85 101 10.0 1 1 41.35 4 13.83 102 12.9 1 1 41.35 4 12.95 103 9.8 1 1 41.35 4 13.88 104 10.2 1 1 41.35 4 13.78 105 10.2 1 1 41.35 4 13.78 106 10.0 1 1 41.35 4 13.82 107 11.4 1 1 41.35 4 13.39 108 10.6 1 1 41.35 4 13.66 109 9.6 1 1 41.35 4 13.97 110 10.7 1 1 41.35 4 13.63 111 4.2 0 0 52.72 2 26.16 112 4.7 0 0 52.72 2 25.99 113 2.3 0 0 52.72 2 26.73 114 8.5 1 0 30.38 4 11.05 115 8.1 1 0 30.38 2 7.11 116 5.7 0 0 52.72 2 25.68 117 4.7 0 0 52.72 2 25.99 118 5.8 0 0 52.72 2 25.65 119 7.1 0 0 52.72 2 25.27 120 7.3 0 0 52.72 2 25.18 121 5.7 0 0 52.72 2 25.69 122 5.2 0 0 52.72 2 25.85 123 6.8 0 0 52.72 2 25.34 124 4.9 0 0 52.72 2 25.94 227

125 5.7 0 0 52.72 2 25.69 126 7.3 0 0 52.72 2 25.20 127 5.8 0 0 52.72 2 25.64 128 2.0 0 0 52.72 2 26.82 129 4.6 0 0 52.72 2 26.02 130 4.5 0 0 52.72 2 26.05 131 8.6 1 0 30.38 4 11.02 132 6.5 0 0 52.72 2 25.45 133 5.6 0 0 52.72 2 25.71 134 3.4 0 0 52.72 2 26.40 135 3.8 0 0 52.72 2 26.27 136 4.3 0 0 52.72 2 26.11 137 4.4 0 0 52.72 2 26.09 138 6.6 0 0 52.72 2 25.40 139 4.8 0 0 52.72 2 25.95 140 3.6 0 0 52.72 2 26.34 141 2.8 0 0 52.72 2 26.56 142 5.0 0 0 52.72 2 25.91 143 6.3 0 0 52.72 2 25.51 144 6.7 0 0 52.72 2 25.39 145 5.5 0 0 52.72 2 25.74 146 5.9 0 0 52.72 2 25.61 147 6.4 0 0 52.72 2 25.48 148 4.3 0 0 52.72 2 26.12 149 8.1 1 0 30.38 2 7.11 150 6.0 0 0 52.72 2 25.59 151 4.4 0 0 52.72 2 26.08 152 8.3 1 0 30.38 4 11.11 153 7.9 0 0 52.72 2 25.03 154 9.9 1 1 41.35 4 13.88 155 9.2 1 1 41.35 4 14.06 156 10.0 1 1 41.35 4 13.83 157 12.8 1 1 41.35 4 12.97 158 10.3 1 1 41.35 4 13.75 159 11.2 1 1 41.35 4 13.46 160 9.6 1 1 41.35 4 13.95 161 10.3 1 1 41.35 4 13.75 162 6.0 0 0 52.72 2 25.59 163 4.6 0 0 52.72 2 26.02 164 5.9 0 0 52.72 2 25.64 165 9.3 1 1 41.35 4 14.03 166 10.2 1 1 41.35 4 13.77 228

167 7.4 0 0 52.72 2 25.16 168 8.9 1 1 41.35 4 14.17 169 11.5 1 1 41.35 4 13.39 170 7.8 0 0 52.72 2 25.05 171 9.1 1 1 41.35 4 14.11 172 7.0 0 0 52.72 2 25.29 173 10.2 1 1 41.35 4 13.77 174 9.5 1 1 41.35 4 13.98 175 12.2 1 1 41.35 4 13.15 176 4.1 0 0 52.72 2 26.17 177 3.8 0 0 52.72 2 26.27 178 3.0 0 0 52.72 2 26.51 179 3.8 0 0 52.72 2 26.28 180 4.6 0 0 52.72 2 26.01 181 4.0 0 0 52.72 2 26.22 182 4.7 0 0 52.72 2 26.00 183 4.4 0 0 52.72 2 26.08 184 4.0 0 0 52.72 2 26.19 185 5.4 0 0 52.72 2 25.79 186 5.0 0 0 52.72 2 25.90 187 4.2 0 0 52.72 2 26.15 188 6.4 0 0 52.72 2 25.47 189 4.1 0 0 52.72 2 26.17 190 11.7 1 1 41.35 4 13.32 191 5.0 0 0 52.72 2 25.91 192 3.9 0 0 52.72 2 26.25 193 4.9 0 0 52.72 2 25.92 194 4.2 0 0 52.72 2 26.13 195 7.2 0 0 52.72 2 25.24 196 5.3 0 0 52.72 2 25.81 197 4.7 0 0 52.72 2 25.98 198 5.3 0 0 52.72 2 25.81 199 4.8 0 0 52.72 2 25.96 200 5.7 0 0 52.72 2 25.67 201 5.6 0 0 52.72 2 25.73 202 4.3 0 0 52.72 2 26.12 203 5.1 0 0 52.72 2 25.86 204 2.5 0 0 52.72 2 26.67 205 4.5 0 0 52.72 2 26.04 206 4.8 0 0 52.72 2 25.95 207 3.5 0 0 52.72 2 26.37 208 5.7 0 0 52.72 2 25.68 229

209 5.5 0 0 52.72 2 25.75 210 5.7 0 0 52.72 2 25.68 211 3.5 0 0 52.72 2 26.34 212 4.7 0 0 52.72 2 25.99 213 6.3 0 0 52.72 2 25.50 214 3.7 0 0 52.72 2 26.29 215 5.6 0 0 52.72 2 25.70 216 5.0 0 0 52.72 2 25.90 217 4.8 0 0 52.72 2 25.95 218 3.6 0 0 52.72 2 26.34 219 5.0 0 0 52.72 2 25.90 220 5.3 0 0 52.72 2 25.80 221 7.6 0 0 52.72 2 25.09 222 6.2 0 0 52.72 2 25.52 223 5.6 0 0 52.72 2 25.73 224 5.9 0 0 52.72 2 25.63 225 5.9 0 0 52.72 2 25.62 226 2.9 0 0 52.72 2 26.55 227 7.3 0 0 52.72 2 25.19 228 7.6 0 0 52.72 2 25.11 229 6.9 0 0 52.72 2 25.32 230 7.2 0 0 52.72 2 25.22 231 8.4 1 0 30.38 4 11.07 232 10.7 1 1 41.35 4 13.63 233 8.9 1 1 41.35 4 14.17 234 12.1 1 1 41.35 4 13.19 235 11.3 1 1 41.35 4 13.44 236 11.8 1 1 41.35 4 13.29 237 9.1 1 1 41.35 4 14.09 238 7.8 0 0 52.72 2 25.05 239 12.4 1 1 41.35 4 13.11 240 8.8 1 1 41.35 4 14.20 241 8.8 1 1 41.35 4 14.19 242 5.0 0 0 52.72 2 25.90 243 9.6 1 1 41.35 4 13.96 244 8.3 1 0 30.38 4 11.09 245 8.7 1 1 41.35 4 14.22 246 5.5 0 0 52.72 2 25.74 247 10.6 1 1 41.35 4 13.66 248 9.4 1 1 41.35 4 14.00 250 5.1 0 0 52.72 2 25.88 251 8.1 1 0 30.38 2 7.11 230

252 11.8 1 1 41.35 4 13.30 254 10.6 1 1 41.35 4 13.65 255 8.8 1 1 41.35 4 14.20 256 10.1 1 1 41.35 4 13.79 257 11.2 1 1 41.35 4 13.46 258 11.7 1 1 41.35 4 13.31 259 11.4 1 1 41.35 4 13.39 260 11.4 1 1 41.35 4 13.41 261 10.1 1 1 41.35 4 13.81 262 10.4 1 1 41.35 4 13.71 263 2.0 0 0 52.72 2 26.82 264 1.8 0 0 52.72 2 26.89 265 1.8 0 0 52.72 2 26.88 266 4.7 0 0 52.72 2 26.00 267 3.7 0 0 52.72 2 26.28 268 3.7 0 0 52.72 2 26.30 269 3.3 0 0 52.72 2 26.43 270 3.8 0 0 52.72 2 26.27 271 4.9 0 0 52.72 2 25.94 272 4.0 0 0 52.72 2 26.20 273 4.0 0 0 52.72 2 26.21 274 5.2 0 0 52.72 2 25.85 275 6.5 0 0 52.72 2 25.44 276 2.3 0 0 52.72 2 26.73 277 8.2 1 0 30.38 2 7.10 278 4.5 0 0 52.72 2 26.06 279 8.0 1 0 30.38 2 7.16 280 4.8 0 0 52.72 2 25.95 281 4.7 0 0 52.72 2 26.00 282 2.1 0 0 52.72 2 26.78 283 10.7 1 1 41.35 4 13.63 284 6.4 0 0 52.72 2 25.46 285 7.5 0 0 52.72 2 25.14 286 7.5 0 0 52.72 2 25.12 287 5.7 0 0 52.72 2 25.70 288 8.4 1 0 30.38 4 11.08 289 5.2 0 0 52.72 2 25.84 290 8.6 1 0 30.38 4 10.99 291 6.8 0 0 52.72 2 25.33 292 5.0 0 0 52.72 2 25.90 293 4.3 0 0 52.72 2 26.12 294 3.5 0 0 52.72 2 26.35 231

295 2.8 0 0 52.72 2 26.58 296 6.1 0 0 52.72 2 25.55 297 4.0 0 0 52.72 2 26.22 298 8.7 1 1 41.35 4 14.24 299 9.0 1 1 41.35 4 14.14 300 7.6 0 0 52.72 2 25.11 301 7.3 0 0 52.72 2 25.18 302 7.7 0 0 52.72 2 25.06 303 6.1 0 0 52.72 2 25.55 304 7.1 0 0 52.72 2 25.25 305 7.1 0 0 52.72 2 25.25 306 7.6 0 0 52.72 2 25.09 307 7.3 0 0 52.72 2 25.19 308 7.7 0 0 52.72 2 25.06 309 4.2 0 0 52.72 2 26.15 310 3.9 0 0 52.72 2 26.24 311 4.1 0 0 52.72 2 26.18 312 4.6 0 0 52.72 2 26.02 313 3.4 0 0 52.72 2 26.39 314 3.9 0 0 52.72 2 26.24 315 4.9 0 0 52.72 2 25.94 316 4.4 0 0 52.72 2 26.09 317 4.2 0 0 52.72 2 26.15 318 8.1 1 0 30.38 2 7.12 319 6.4 0 0 52.72 2 25.47 320 6.7 0 0 52.72 2 25.38 321 9.1 1 1 41.35 4 14.10 322 8.6 1 0 30.38 4 11.01 323 9.1 1 1 41.35 4 14.10 324 10.0 1 1 41.35 4 13.83 325 12.5 1 1 41.35 4 13.07 326 8.6 1 0 30.38 4 11.02 327 3.4 0 0 52.72 2 26.39 328 10.4 1 1 41.35 4 13.72 329 12.0 1 1 41.35 4 13.22 330 4.9 0 0 52.72 2 25.93 331 5.7 0 0 52.72 2 25.69 332 10.7 1 1 41.35 4 13.63 333 2.7 0 0 52.72 2 26.61 334 2.6 0 0 52.72 2 26.64 335 4.2 0 0 52.72 2 26.15 336 3.7 0 0 52.72 2 26.28 232

337 4.4 0 0 52.72 2 26.09 338 3.7 0 0 52.72 2 26.28 339 4.0 0 0 52.72 2 26.19 340 9.0 1 1 41.35 4 14.14 341 4.0 0 0 52.72 2 26.20 342 10.9 1 1 41.35 4 13.56 343 6.0 0 0 52.72 2 25.60 344 12.0 1 1 41.35 4 13.23 345 10.0 1 1 41.35 4 13.83 346 3.1 0 0 52.72 2 26.49 347 6.7 0 0 52.72 2 25.39 348 4.0 0 0 52.72 2 26.20 349 9.2 1 1 41.35 4 14.09 350 8.8 1 1 41.35 4 14.19 351 7.2 0 0 52.72 2 25.24 352 7.1 0 0 52.72 2 25.26 353 5.8 0 0 52.72 2 25.66 354 4.0 0 0 52.72 2 26.21 355 7.9 0 0 52.72 2 25.00 356 4.1 0 0 52.72 2 26.17 357 2.8 0 0 52.72 2 26.56 358 6.4 0 0 52.72 2 25.47 359 5.4 0 0 52.72 2 25.77 360 9.8 1 1 41.35 4 13.91 361 4.0 0 0 52.72 2 26.20 362 4.1 0 0 52.72 2 26.18 363 5.3 0 0 52.72 2 25.81 364 4.5 0 0 52.72 2 26.06 365 4.1 0 0 52.72 2 26.18 366 3.4 0 0 52.72 2 26.38 367 4.5 0 0 52.72 2 26.05 368 3.8 0 0 52.72 2 26.28 369 5.5 0 0 52.72 2 25.74 370 12.3 1 1 41.35 4 13.13 371 9.8 1 1 41.35 4 13.89 372 7.0 0 0 52.72 2 25.30 373 6.0 0 0 52.72 2 25.59 374 5.0 0 0 52.72 2 25.90 375 3.7 0 0 52.72 2 26.31 376 7.3 0 0 52.72 2 25.19 377 8.3 1 0 30.38 4 11.09 378 6.6 0 0 52.72 2 25.40 233

379 5.9 0 0 52.72 2 25.63 380 6.8 0 0 52.72 2 25.34 381 6.3 0 0 52.72 2 25.49 382 5.1 0 0 52.72 2 25.87 383 2.7 0 0 52.72 2 26.60 384 3.1 0 0 52.72 2 26.49 385 4.8 0 0 52.72 2 25.97 386 5.3 0 0 52.72 2 25.81 387 5.7 0 0 52.72 2 25.69 388 8.1 1 0 30.38 2 7.13 389 6.3 0 0 52.72 2 25.49 390 6.0 0 0 52.72 2 25.59 391 9.2 1 1 41.35 4 14.07 392 9.2 1 1 41.35 4 14.07 393 8.8 1 1 41.35 4 14.19 394 8.8 1 1 41.35 4 14.19 395 3.0 0 0 52.72 2 26.51 396 8.0 0 0 52.72 2 25.00 397 3.7 0 0 52.72 2 26.28 398 5.1 0 0 52.72 2 25.87 399 3.8 0 0 52.72 2 26.26 400 6.5 0 0 52.72 2 25.44 401 4.9 0 0 52.72 2 25.94 402 5.0 0 0 52.72 2 25.89 403 4.5 0 0 52.72 2 26.05 404 2.9 0 0 52.72 2 26.54 405 7.0 0 0 52.72 2 25.30 406 4.6 0 0 52.72 2 26.01 407 7.9 0 0 52.72 2 25.02 408 3.7 0 0 52.72 2 26.29 409 5.5 0 0 52.72 2 25.74 410 4.4 0 0 52.72 2 26.08 411 6.8 0 0 52.72 2 25.36 412 9.3 1 1 41.35 4 14.05 413 5.0 0 0 52.72 2 25.90 414 8.0 1 0 30.38 2 7.15 415 6.2 0 0 52.72 2 25.53 416 10.0 1 1 41.35 4 13.83 417 8.7 1 1 41.35 4 14.23 418 4.3 0 0 52.72 2 26.11 419 5.1 0 0 52.72 2 25.87 420 9.5 1 1 41.35 4 13.98 234

421 4.4 0 0 52.72 2 26.08 422 5.6 0 0 52.72 2 25.71 423 6.8 0 0 52.72 2 25.35 424 7.0 0 0 52.72 2 25.29 425 9.2 1 1 41.35 4 14.08 426 8.9 1 1 41.35 4 14.18 427 8.8 1 1 41.35 4 14.19 428 5.0 0 0 52.72 2 25.90 429 4.0 0 0 52.72 2 26.20 430 4.1 0 0 52.72 2 26.17 431 4.9 0 0 52.72 2 25.93 432 6.5 0 0 52.72 2 25.44 433 7.9 0 0 52.72 2 25.00 434 4.1 0 0 52.72 2 26.17 435 4.7 0 0 52.72 2 25.99 436 4.1 0 0 52.72 2 26.17 437 3.6 0 0 52.72 2 26.33 438 3.7 0 0 52.72 2 26.30 439 4.6 0 0 52.72 2 26.02 440 2.6 0 0 52.72 2 26.63 441 5.9 0 0 52.72 2 25.62 442 9.0 1 1 41.35 4 14.14 443 8.4 1 0 30.38 4 11.07 444 2.8 0 0 52.72 2 26.57 445 8.1 1 0 30.38 2 7.12 446 2.0 0 0 52.72 2 26.82 447 4.9 0 0 52.72 2 25.93 448 8.0 1 0 30.38 2 7.15 449 10.0 1 1 41.35 4 13.83 450 8.2 1 0 30.38 4 11.13 451 8.3 1 0 30.38 4 11.10 452 2.5 0 0 52.72 2 26.66 453 4.0 0 0 52.72 2 26.20 454 4.4 0 0 52.72 2 26.08 455 4.5 0 0 52.72 2 26.05 456 3.3 0 0 52.72 2 26.42 457 4.2 0 0 52.72 2 26.14 458 3.8 0 0 52.72 2 26.27 459 4.0 0 0 52.72 2 26.20 460 4.0 0 0 52.72 2 26.20 461 3.8 0 0 52.72 2 26.27 462 4.7 0 0 52.72 2 25.99 235

463 6.2 0 0 52.72 2 25.53 464 5.9 0 0 52.72 2 25.62 465 5.2 0 0 52.72 2 25.84 466 5.4 0 0 52.72 2 25.78 467 4.9 0 0 52.72 2 25.93 468 5.7 0 0 52.72 2 25.68 469 8.9 1 1 41.35 4 14.17 470 8.3 1 0 30.38 4 11.10 471 6.4 0 0 52.72 2 25.47 472 9.4 1 1 41.35 4 14.02 474 5.3 0 0 52.72 2 25.81 475 6.4 0 0 52.72 2 25.47 476 4.9 0 0 52.72 2 25.93 477 10.9 1 1 41.35 4 13.56 478 11.7 1 1 41.35 4 13.31 479 7.0 0 0 52.72 2 25.29 480 8.9 1 1 41.35 4 14.17 481 7.0 0 0 52.72 2 25.29 482 8.6 1 0 30.38 4 11.01 483 5.0 0 0 52.72 2 25.90 484 4.8 0 0 52.72 2 25.96 485 5.8 0 0 52.72 2 25.65 486 6.2 0 0 52.72 2 25.53 487 3.2 0 0 52.72 2 26.45 488 4.0 0 0 52.72 2 26.20 489 5.8 0 0 52.72 2 25.65 490 4.4 0 0 52.72 2 26.08 491 8.4 1 0 30.38 4 11.07 492 9.0 1 1 41.35 4 14.14 493 10.0 1 1 41.35 4 13.83 494 8.9 1 1 41.35 4 14.17 495 11.2 1 1 41.35 4 13.46 496 8.9 1 1 41.35 4 14.17 497 12.7 1 1 41.35 4 13.01 498 7.2 0 0 52.72 2 25.22 499 7.6 0 0 52.72 2 25.10 500 6.6 0 0 52.72 2 25.41 501 4.6 0 0 52.72 2 26.02 502 10.3 1 1 41.35 4 13.74 503 8.0 1 0 30.38 2 7.15 504 9.4 1 1 41.35 4 14.02 505 5.0 0 0 52.72 2 25.90 236

506 4.0 0 0 52.72 2 26.20 507 3.0 0 0 52.72 2 26.51 508 3.5 0 0 52.72 2 26.36 509 3.8 0 0 52.72 2 26.27 510 3.5 0 0 52.72 2 26.36 511 5.1 0 0 52.72 2 25.87 512 3.2 0 0 52.72 2 26.45 513 3.9 0 0 52.72 2 26.23 514 7.9 0 0 52.72 2 25.01 515 3.2 0 0 52.72 2 26.45 516 6.0 0 0 52.72 2 25.59 517 7.8 0 0 52.72 2 25.04 518 10.5 1 1 41.35 4 13.68 519 12.0 1 1 41.35 4 13.22 520 11.4 1 1 41.35 4 13.40 521 4.8 0 0 52.72 2 25.96 522 9.9 1 1 41.35 4 13.86 523 9.4 1 1 41.35 4 14.02 524 12.0 1 1 41.35 4 13.22 525 12.1 1 1 41.35 4 13.19 526 9.0 1 1 41.35 4 14.14 527 7.0 0 0 52.72 2 25.29 528 9.0 1 1 41.35 4 14.14 529 9.8 1 1 41.35 4 13.89 530 10.0 1 1 41.35 4 13.83 531 4.0 0 0 52.72 2 26.20 532 6.9 0 0 52.72 2 25.32 533 5.9 0 0 52.72 2 25.62 534 5.6 0 0 52.72 2 25.71 535 5.5 0 0 52.72 2 25.74 536 5.3 0 0 52.72 2 25.81 537 7.4 0 0 52.72 2 25.16 538 5.7 0 0 52.72 2 25.68 539 5.7 0 0 52.72 2 25.68 540 4.0 0 0 52.72 2 26.20 541 6.0 0 0 52.72 2 25.59 542 7.0 0 0 52.72 2 25.29 543 7.0 0 0 52.72 2 25.29 544 4.6 0 0 52.72 2 26.02 545 8.3 1 0 30.38 4 11.10 546 9.4 1 1 41.35 4 14.02 547 8.5 1 0 30.38 4 11.04 237

548 7.2 0 0 52.72 2 25.22 549 6.0 0 0 52.72 2 25.59 550 7.9 0 0 52.72 2 25.01 551 9.5 1 1 41.35 4 13.98 552 7.4 0 0 52.72 2 25.16 553 7.9 0 0 52.72 2 25.01 554 8.4 1 0 30.38 4 11.07 555 7.7 0 0 52.72 2 25.07 556 6.1 0 0 52.72 2 25.56 557 6.6 0 0 52.72 2 25.41 558 7.3 0 0 52.72 2 25.19 559 8.9 1 1 41.35 4 14.17 560 9.1 1 1 41.35 4 14.11 561 11.4 1 1 41.35 4 13.40 562 12.2 1 1 41.35 4 13.16 563 11.2 1 1 41.35 4 13.46 564 8.0 1 0 30.38 2 7.15 565 9.5 1 1 41.35 4 13.98 566 7.3 0 0 52.72 2 25.19 567 7.1 0 0 52.72 2 25.26 568 7.0 0 0 52.72 2 25.29 569 9.4 1 1 41.35 4 14.02 570 10.3 1 1 41.35 4 13.74 571 10.3 1 1 41.35 4 13.74 572 7.4 0 0 52.72 2 25.16 573 6.4 0 0 52.72 2 25.47 574 9.0 1 1 41.35 4 14.14 575 8.3 1 0 30.38 4 11.10 576 4.3 0 0 52.72 2 26.11 577 5.0 0 0 52.72 2 25.90 578 9.0 1 1 41.35 4 14.14 579 7.0 0 0 52.72 2 25.29 580 3.6 0 0 52.72 2 26.33 581 6.7 0 0 52.72 2 25.38 582 7.0 0 0 52.72 2 25.29 583 7.0 0 0 52.72 2 25.29 584 8.3 1 0 30.38 4 11.10 585 6.5 0 0 52.72 2 25.44 586 6.5 0 0 52.72 2 25.44 587 5.6 0 0 52.72 2 25.71 588 6.7 0 0 52.72 2 25.38 589 5.3 0 0 52.72 2 25.81 238

590 7.6 0 0 52.72 2 25.10 591 8.6 1 0 30.38 4 11.01 592 7.5 0 0 52.72 2 25.13 593 7.2 0 0 52.72 2 25.22 594 6.9 0 0 52.72 2 25.32 595 9.6 1 1 41.35 4 13.95 596 9.0 1 1 41.35 4 14.14 597 8.7 1 1 41.35 4 14.23 598 4.0 0 0 52.72 2 26.20 599 4.0 0 0 52.72 2 26.20 600 5.4 0 0 52.72 2 25.78 601 4.4 0 0 52.72 2 26.08 602 7.8 0 0 52.72 2 25.04 603 4.9 0 0 52.72 2 25.93 604 4.0 0 0 52.72 2 26.20 605 3.0 0 0 52.72 2 26.51 606 10.9 1 1 41.35 4 13.56 607 3.8 0 0 52.72 2 26.27 608 4.2 0 0 52.72 2 26.14 609 3.0 0 0 52.72 2 26.51 610 5.9 0 0 52.72 2 25.62 611 6.5 0 0 52.72 2 25.44 612 4.4 0 0 52.72 2 26.08 613 4.4 0 0 52.72 2 26.08 614 3.7 0 0 52.72 2 26.30 615 4.3 0 0 52.72 2 26.11 616 3.5 0 0 52.72 2 26.36 617 4.1 0 0 52.72 2 26.17 618 4.0 0 0 52.72 2 26.20 619 4.2 0 0 52.72 2 26.14 620 4.8 0 0 52.72 2 25.96 621 5.8 0 0 52.72 2 25.65 622 6.7 0 0 52.72 2 25.39 623 5.9 0 0 52.72 2 25.62 624 11.3 1 1 41.35 4 13.43 625 8.9 1 1 41.35 4 14.17 626 11.3 1 1 41.35 4 13.43 627 8.2 1 0 30.38 4 11.13 628 10.8 1 1 41.35 4 13.59 629 4.8 0 0 52.72 2 25.96 630 4.2 0 0 52.72 2 26.14 631 5.0 0 0 52.72 2 25.90 239

632 5.2 0 0 52.72 2 25.84 633 5.4 0 0 52.72 2 25.78 634 5.0 0 0 52.72 2 25.90 635 4.3 0 0 52.72 2 26.11 636 4.8 0 0 52.72 2 25.96 637 6.3 0 0 52.72 2 25.50 638 5.7 0 0 52.72 2 25.68 639 6.8 0 0 52.72 2 25.35 640 4.0 0 0 52.72 2 26.20 641 5.0 0 0 52.72 2 25.90 642 3.3 0 0 52.72 2 26.42 643 11.3 1 1 41.35 4 13.43 644 9.0 1 1 41.35 4 14.14 645 7.4 0 0 52.72 2 25.16 646 9.3 1 1 41.35 4 14.05 647 7.5 0 0 52.72 2 25.13 648 9.7 1 1 41.35 4 13.92 649 7.0 0 0 52.72 2 25.29 650 10.9 1 1 41.35 4 13.56 652 9.4 1 1 41.35 4 14.02 653 11.2 1 1 41.35 4 13.46 654 10.2 1 1 41.35 4 13.77 655 11.7 1 1 41.35 4 13.31 656 8.3 1 0 30.38 4 11.10 657 8.3 1 0 30.38 4 11.10 658 11.3 1 1 41.35 4 13.43 659 9.2 1 1 41.35 4 14.08 660 8.8 1 1 41.35 4 14.20 661 8.3 1 0 30.38 4 11.10 662 11.5 1 1 41.35 4 13.37 663 8.4 1 0 30.38 4 11.07 664 11.3 1 1 41.35 4 13.43 665 11.0 1 1 41.35 4 13.53 666 11.0 1 1 41.35 4 13.53 667 12.3 1 1 41.35 4 13.13 668 12.0 1 1 41.35 4 13.22 669 8.4 1 0 30.38 4 11.07 670 11.0 1 1 41.35 4 13.53 671 7.5 0 0 52.72 2 25.13 672 4.2 0 0 52.72 2 26.14 674 6.5 0 0 52.72 2 25.44 675 7.0 0 0 52.72 2 25.29 240

676 3.0 0 0 52.72 2 26.51 677 4.8 0 0 52.72 2 25.96 678 3.8 0 0 52.72 2 26.27 679 8.8 1 1 41.35 4 14.20 680 8.2 1 0 30.38 4 11.13 681 6.3 0 0 52.72 2 25.50 682 6.5 0 0 52.72 2 25.44 683 10.0 1 1 41.35 4 13.83 684 8.0 1 0 30.38 2 7.15 685 4.6 0 0 52.72 2 26.02 686 3.4 0 0 52.72 2 26.39 687 2.7 0 0 52.72 2 26.60 688 3.7 0 0 52.72 2 26.30 689 5.3 0 0 52.72 2 25.81 690 4.7 0 0 52.72 2 25.99 691 5.2 0 0 52.72 2 25.84 692 3.0 0 0 52.72 2 26.51 693 7.4 0 0 52.72 2 25.16 694 7.2 0 0 52.72 2 25.22 695 8.5 1 0 30.38 4 11.04 696 7.7 0 0 52.72 2 25.07 697 6.7 0 0 52.72 2 25.38 698 13.0 1 1 41.35 4 12.91 699 12.0 1 1 41.35 4 13.22 700 9.2 1 1 41.35 4 14.08 701 4.0 0 0 52.72 2 26.20 702 5.0 0 0 52.72 2 25.90 703 5.0 0 0 52.72 2 25.90 704 4.0 0 0 52.72 2 26.20 705 10.0 1 1 41.35 4 13.83 706 8.2 1 0 30.38 4 11.13 707 12.0 1 1 41.35 4 13.22 708 7.4 0 0 52.72 2 25.16 709 10.2 1 1 41.35 4 13.77 710 6.0 0 0 52.72 2 25.59 711 4.8 0 0 52.72 2 25.96 712 3.0 0 0 52.72 2 26.51 713 4.0 0 0 52.72 2 26.20 714 6.9 0 0 52.72 2 25.32 715 4.3 0 0 52.72 2 26.11 716 5.2 0 0 52.72 2 25.84 717 4.7 0 0 52.72 2 25.99 241

718 4.9 0 0 52.72 2 25.93 719 9.7 1 1 41.35 4 13.92 720 4.9 0 0 52.72 2 25.93 721 7.7 0 0 52.72 2 25.07 722 9.4 1 1 41.35 4 14.02 723 8.3 1 0 30.38 4 11.10 724 5.8 0 0 52.72 2 25.65 725 8.0 1 0 30.38 2 7.15 726 3.6 0 0 52.72 2 26.33 727 11.5 1 1 41.35 4 13.37 728 11.3 1 1 41.35 4 13.43 729 6.5 0 0 52.72 2 25.44 730 8.8 1 1 41.35 4 14.20 731 9.3 1 1 41.35 4 14.05 732 11.3 1 1 41.35 4 13.43 733 7.0 0 0 52.72 2 25.29 734 5.0 0 0 52.72 2 25.90 735 5.5 0 0 52.72 2 25.74 736 4.1 0 0 52.72 2 26.17 737 11.0 1 1 41.35 4 13.53 738 11.1 1 1 41.35 4 13.50 739 9.0 1 1 41.35 4 14.14 740 4.1 0 0 52.72 2 26.17 741 4.5 0 0 52.72 2 26.05 742 4.0 0 0 52.72 2 26.20 743 3.3 0 0 52.72 2 26.42 744 4.3 0 0 52.72 2 26.11 745 3.7 0 0 52.72 2 26.30 746 3.8 0 0 52.72 2 26.27 747 10.3 1 1 41.35 4 13.74 748 7.6 0 0 52.72 2 25.10 749 7.3 0 0 52.72 2 25.19 750 9.3 1 1 41.35 4 14.05 751 10.3 1 1 41.35 4 13.74 752 8.8 1 1 41.35 4 14.20 753 9.4 1 1 41.35 4 14.02 754 7.4 0 0 52.72 2 25.16 755 8.7 1 1 41.35 4 14.23 756 6.6 0 0 52.72 2 25.41 757 8.8 1 1 41.35 4 14.20 758 11.4 1 1 41.35 4 13.40 759 9.4 1 1 41.35 4 14.02 242

760 12.4 1 1 41.35 4 13.10 761 10.0 1 1 41.35 4 13.83 762 7.9 0 0 52.72 2 25.01 763 8.2 1 0 30.38 4 11.13 764 4.5 0 0 52.72 2 26.05 765 10.4 1 1 41.35 4 13.71 766 8.3 1 0 30.38 4 11.10 767 11.5 1 1 41.35 4 13.37 768 4.0 0 0 52.72 2 26.20 769 8.3 1 0 30.38 4 11.10 770 11.3 1 1 41.35 4 13.43 771 4.0 0 0 52.72 2 26.20 772 7.0 0 0 52.72 2 25.29 773 7.5 0 0 52.72 2 25.13 774 5.6 0 0 52.72 2 25.71 775 5.3 0 0 52.72 2 25.81 776 5.3 0 0 52.72 2 25.81 777 6.6 0 0 52.72 2 25.41 778 6.5 0 0 52.72 2 25.44 779 5.4 0 0 52.72 2 25.78 780 7.9 0 0 52.72 2 25.01 781 7.9 0 0 52.72 2 25.01 782 10.0 1 1 41.35 4 13.83 783 10.2 1 1 41.35 4 13.77 784 12.0 1 1 41.35 4 13.22 785 7.0 0 0 52.72 2 25.29 786 12.0 1 1 41.35 4 13.22 787 12.2 1 1 41.35 4 13.16 788 7.8 0 0 52.72 2 25.04 789 10.0 1 1 41.35 4 13.83 790 11.6 1 1 41.35 4 13.34 792 11.2 1 1 41.35 4 13.46 793 6.9 0 0 52.72 2 25.32 794 8.3 1 0 30.38 4 11.10 795 9.1 1 1 41.35 4 14.11 796 10.0 1 1 41.35 4 13.83 797 7.0 0 0 52.72 2 25.29 798 6.0 0 0 52.72 2 25.59 799 7.4 0 0 52.72 2 25.16 800 9.3 1 1 41.35 4 14.05 801 8.6 1 0 30.38 4 11.01 802 6.4 0 0 52.72 2 25.47 243

803 5.0 0 0 52.72 2 25.90 804 9.3 1 1 41.35 4 14.05 805 4.9 0 0 52.72 2 25.93 806 4.6 0 0 52.72 2 26.02 807 4.0 0 0 52.72 2 26.20 808 4.1 0 0 52.72 2 26.17 809 12.0 1 1 41.35 4 13.22 810 5.0 0 0 52.72 2 25.90 811 5.0 0 0 52.72 2 25.90 812 4.8 0 0 52.72 2 25.96 813 8.7 1 1 41.35 4 14.23

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Appendix D: Questionnaire

This questionnaire will be used in accompany with several others to collect expert opinions in order to determine which kind of recreational boating impacts on Kosterhavets National park the government should give the highest priority. Please note that 1 boating season is assumed 100 days. And all boats are considered to be using either gasoline or diesel.

Please have a look at the summary of recreational boating processes, possible emissions, and possible impacts assessed in the project. This will then be followed by a table. In this table, a scoring is to be given. The rest of the instructions will be given in each section. Please reply electronically if possible. The diagrams and data shown in this questionnaire is a replica from the project’s report. Once the project is completed, the report is available upon request.

Section A - Boating Process

Recreational boating includes boats that are less than 12 meters long. However, in case of errors when studying the length overalls of boats, all boats in Koster that have been counted are less than 13 meters long. The amount of boats is estimated from an aerial photograph taken randomly on a summer day. Below is the conceptual diagram of boating processes and its subprocesses with their emissions.

SO HC CO NO

Metals

H2O • Recreation • Electric Power Generation Biocid • Antifouling

Air • Combustion within boat

Engines Fuel

Etc.

HC PM Metals Oil Biocid Etc.

Fig y. Conceptual Model summarizing the Recreational Boating Process, sub processes, and inventories

The 4 subprocesses include Recreation, Electric Power Generation, Antifouling, and Combustion. • Recreation – This is the boating itself and other activities associated with boating. The use of motor powered PWCs (i.e. jet skis) are not considered. • Electric power generation – this is the means of power generation on yachts for electronical devices. Since this process has just been recently founded, not much data on it is obtained. • Antifouling – the use of antifoulants on boats • Combustion – This is mainly from the engines creating various environmental problems

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Section B – Environmental Impact Summary

Recreation There are various environmental impacts associated with recreational activities. This include disturbance to the wild population, where studies in North America have found relocation of habitats to be a possible result of disturbance. Other physical impacts vary from erosion via boat waves to the propeller action which can cut macroalgae and cause severe uprooting and its side effects. Boat waves can also remove epifauna living on seagrass. Evidences have shown boat outboard motors cutting through seagrass areas. Other emissions are from human sewage. The table below summarizes the estimated amount of N, P, and carbohydrate release due to recreation in 1 season. These may lead to the likelyhood increase of eutrophication.

Total Calculated Sewage Release Electric Power Generation For this process, nothing much can be said since the Emission Total (kg) process has just been recently found through various Nitrogen 193,02 yacht and boat sales. Various means of generating Phospherous 23,79 electricity on board exists and further study on this Carbohydrates 95,16 matter is required.

Antifouling The use of TBT and Cu as antifoulants have been prohibited by the Swedish law. However, recent Antifouling Contamination experimental studies from Stockholm University Contaminants Total (mg) has found levels of TBT and Cu on top sediment MBT 104,65 layers in Stockholm. It is assumed that this is DBT 644 probably because people painted over the TBT and TBT 3220 Cu layer, which is released during boat cleaning at the end of the season. An estimate of TBT and Irgarol 2334,5 other metal leachates for Koster per season is given Cu 241500 in the table to the right. These are toxic to various Zn 805000 marine life at high concentrations. Pb 2415 Sn 5635

Combustion Combustion releases various pollutants. If we follow the ideal stoichiometric combustion, a lot of CO2 would result, which in itself has problems with climate change and ocean acidification. However, because the efficiency of combustion is not 100%, NOx, COx, and HCs are also being emitted. Total estimates of these emissions are given in the table below. Furthermore, the engine design and the nature of the combustion process also creates loud noises which enhances further disturbances in recreational boating.

Total Nox (kg) Total CO (kg) Total HC (kg) Total CO2 (kg) 3151,73 116065,49 36055,73 867937,63

NOx and HCs lead to generation of photochemical smog and acid rain. A majority of HCs are VOCs and some are released with the water exhaust which has been found to be highly toxic for marine life.

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Section C – Scoring In this section, please give a score to which process do you think should be given highest priority for Kosterhavets Marine National park. The scoring is given by rank, where a 4 is given if the matter should be given the highest priority and 1 for the least priority in according to various kinds of impacts. It is considered that all of these impacts should be given priority but it is the objective of the project to determine which subprocess of boating should be given the highest priority. The reason behind this is because the nature of the problem varies accordingly.

Electric power Recreation Antifouling Combustion Marine environments Air Quality Biota Nearby environments , i.e. Goteborg archipelagos, Stromstad, Tjarno, and the Norwegian Coast

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TRITA-IM 2009:16 ISSN 1402-7615

Industrial Ecology, Royal Institute of Technology www.ima.kth.se