Σάββατο 28 Δεκεμβρίου 2019

ABS New LNG Bunkering Guide

Classification society ABS has released a guide for liquefied natural gas (LNG) bunkering, which outlines requirements for the design, construction, and survey of carriers and barges fitted with dedicated LNG transfer arrangements and intended for regular LNG bunkering service. In parallel ABS has also released its GUIDE FOR LNG BUNKERING. Both documents are available to download further below.

The guide also addresses bunkering station safety, lifting and hose handling equipment, control, monitoring and Emergency Shutdown (ESD) and release safety systems.
While application of the guide is optional, the guide must be followed in order to obtain ABS’ optional LNG Bunkering notation.
“Most LNG-fuelled vessels in operation at the time of issuance of this Guide receive LNG bunkers on a relatively small scale, typically through a shore-to-ship basis by road tankers or dedicated shore side LNG tanks,” notes ABS. “ It is envisaged that greater LNG transfer rates than those typically used for refueling the current gas fueled ship fleet will be required. In order to support the further growth and development of LNG fueled vessels for short sea and international trade, ABS says more dedicated LNG infrastructure is needed, particularly in terms of small scale LNG storage and distribution centres together and dedicated LNG bunkering vessels for ship to ship LNG transfer operations.
The guide may be downloaded at,

Πέμπτη 26 Δεκεμβρίου 2019

Bunkers and bunkering - It's nothing to do with your golf swing


Introduction
Everybody who owns or drives a car has experience of bunkering. We all fill up with petrol from time to time. We do so almost without thinking about it. Fortunately, we rarely, if ever, have a problem with the quality of the fuel. And if we spill some petrol, it is not a "pollution incident".
The procedures which take place during bunkering vessels are, or should be, very different from the procedure of putting petrol into your car. Given the problems and liabilities which bunkers and bunkering can lead to, it is essential that the entire bunkering operation, from start to finish, is closely monitored by the receiving vessel. It is also vital that the quality of the (new) bunkers is checked and the bunkers are tested before they are used or mixed with other bunkers already on board.
Apart from nuclear-powered ships, all vessels have to take on bunkers from time to time. Large bulk carriers and container vessels can carry as much as 10,000 MT of fuel oil at any one time. Even the "workhorses" of the bulk trades, the Handymax and Panamax vessels, may have up to 1,000 MT of fuel oil on board after bunkering. Fuel oil is very viscous and persistent.
The problems which (good or bad) bunkers can cause
Bunkers do not need to be "bad", or, more correctly, off-specification, to cause serious claims and liabilities. A spill of bunkers from any vessel is likely to lead to a difficult and expensive clean-up operation and - depending to some extent on where the spill has occurred - to claims for damage to the environment and for losses suffered by individuals or organisations allegedly affected by the spill.
Bunker experts generally consider that overall bunker quality has deteriorated over the years, although the quality also tends to follow the price and vice-versa. However, it is often the case that, because of increased demand for high quality products such as kerosene and jet fuel, the "raw material" left behind after the crude oil has been processed is likely to lead to bunkers of a lower quality being produced. If the bunkers contain additives such as used car oil, this may well add to the problem.
Off-specification bunkers (bad bunkers) can cause many problems. At best, they may result in the main engine not performing effectively or efficiently. This may result in reduced speed and over-consumption of bunkers. In turn, either or both of these is likely to lead to a claim by charterers - a speed and consumption claim.
More importantly, the consumption of bunkers which are off-specification could well cause damage to the main engine. Relatively speaking, the age and condition of the engine is not relevant, although it is perhaps true to say that an engine in first-class condition may have a greater tolerance for bad bunkers than an engine in poor condition. Nevertheless, damage to the main engine caused by bad bunkers is likely to be a serious problem. Your hull insurers are likely to be worried.
Such main engine damage can lead to even more serious problems. If a loss of main engine power occurs at sea, there is likely to be a significant delay to the vessel while the engineers work hard to put right the problem. They may not be able to do so. Salvage assistance, or possibly a straightforward tow, may be needed. Even more seriously, a vessel with little or no main engine power could, particularly in confined waters, result in the vessel grounding or colliding with another vessel or fixed or floating object such as a jetty or dolphin. If this happens, both your hull and your P&I insurers will be very worried people. The potential claims and liabilities arising in such circumstances are very large.
Bunker spills
The International Tanker Owners' Pollution Federation (ITOPF) publishes oil pollution statistics every year. In a speech made at an oil pollution conference in London in May 2019, the managing director of ITOPF said that "about 28 per cent of the oil spills attended on site by ITOPF staff over the past fifteen years have involved bunker fuel spilled from non-tankers. In the last two years, this percentage has risen to about 50 per cent."
It is likely that for bulk carriers, the number/percentage of oil spills caused by casualties of some sort (i.e., grounding or collision) is substantially less than for tankers (which is only 14 per cent anyway) and the number/percentage of spills happening during routine operations is substantially higher.
Most bunker spills will be in the range of between 7 and 700 MT. Some will involve smaller quantities. Unless the vessel concerned is a large vessel, with a large quantity of bunkers on board, and is involved in a major casualty, such as a grounding in which more than one bunker tank is holed, few bunker spills will be more than 700 MT.
Many such spills are the result of carelessness or negligence, either on the part of those supplying the bunkers, or those on board the vessel receiving them. Even a technical problem, such as the failure of an alarm to go off, may well be the result of human error. More often, our experience is that one or more of the following are present:
     Ø  failure to agree a loading rate with the bunker barge or shore loading facility;  
     Ø  failure on the part of the bunker barge or shore facility to stick to the agreed loading rate;
    Ø  failure on the part of the vessel's crew to check that the bunkers are being loaded at the agreed rate and if they are not, failure to request the loading barge to slow down;
    Ø  failure to monitor the tank(s) into which the bunkers are being loaded; 
    Ø  failure to respond to an alarm indicating that the tank is nearly full.
    Out of all of these, Gard's experience is that most bunker spills result from an overflow of bunkers. The cause is usually one or both of the last two failures. A former deck officer once suggested that the best way of avoiding bunker spills would to be connect all the bunker tank airvents and overflow pipes to the chief engineer's cabin!
Example
A small tanker was discharging mineral oil at a berth upriver in London. Owners' safety officer was on board to assist with a vetting inspection by one of the major oil companies. During discharge from four of the vessel's tanks, the high level alarms went off. The master and chief officer were taking part in the vetting inspection and the second officer was on duty. He assumed that the alarms had been activated in the course of the vetting inspection - perhaps to show to the inspectors from the oil company that they worked properly - and took no action. In fact, they had been activated in exactly the intended way - to warn that cargo was close to overflowing from a cargo tank. A couple of minutes later, the cargo overflowed from one of the tanks. Fortunately, the crew then responded very quickly and took all the required steps to stop discharge and clean up the spill. As a result, only a very small quantity - estimated at 100 litres - went over the side. Later investigation showed that the device showing the position of the cargo valves (i.e., open or closed) was not working on almost all valves. Both the chief officer and the second officer wrongly thought that a particular valve was closed, when in fact it was open. Neither of them checked the position of the valve before starting discharge. The quantity spilled was very small. It was not spilled into the water, but on to "Thames mud", which becomes visible at times as a result of the large rise and fall of the river. Despite this, the Port of London Authority (PLA) investigated the incident, with a view to possible criminal prosecution. Ultimately, they decided not to prosecute. Instead, they issued the master with a letter of warning, which will be taken into account in a future similar incident. The potential maximum fine in such cases is GBP 250,000 in the Magistrates Court or an unlimited fine in the Crown Court.
The time and cost involved in cleaning-up spills of heavy fuel oil is usually considerable. The oil is thick and does not evaporate or disperse. Manual cleaning is often the only option. Disposal of the oil which has been collected is also a problem and can be just as difficult and expensive as the clean-up operation. If the spill has occurred in or close to an area where other ships or private boats are moored, their hulls may be oiled and require cleaning. Even more importantly, if the spill affects, or is alleged to have affected, mariculture, often fish-farming, the claims can be very significant. The local and sometimes the national, media may well take an interest in the incident. Even worse, local or national politicians may either take an interest themselves, or find themselves called upon to do so by their voters, whose pleasure boats have been oiled, or whose beach has been closed while the clean-up is carried out.
Even a small quantity of fuel oil can, if spilt, result in very large liabilities. Perhaps the best - or worst - example concerns a non-tanker - a woodchip carrier, which spilled approximately 17.5 MT of heavy fuel oil in a port in Southern California. The spill occurred during loading and was caused by the vessel making contact with a dolphin on the jetty. A bunker tank was holed and heavy fuel oil was spilt. For the first five days, the clean-up cost, per day, was approximately USD 1 million. After five days, it was possible to reduce the cost per day to about USD 500,000. By the end of 1999, the Club in question had paid approximately USD 14.3 million, mainly in respect of clean-up costs and third party claims. They were estimating a further USD 10.7 million to cover the claim for alleged natural resource damage and further legal and expert's costs. A round sum of USD 25 million!
This is the worst-case scenario - the P&I man's nightmare. Most bunker spills do not cost anything like this amount, but they are difficult and expensive to deal with. If you spill a little petrol when you are filling up your car, it is nobody's problem but yours, since you have to pay for the petrol you have lost. You do not have to clean it up. Nor do you have to pay compensation to the garage owner for "damaging" his property. Nor do you have to deal with claims from third parties - for example, people living near to the garage who may claim that they have been affected by the smell of the petrol which has been spilt. Nor are you likely to face civil and criminal proceedings, with every chance of being deemed to be guilty, which brings with it the potential for large fines and even imprisonment. In the example mentioned, criminal prosecution did not happen. However, Gard has had many cases, in various countries, where the master, usually together with the ship owner, is criminally prosecuted. Regrettably, this trend is continuing. Remember that criminal prosecution and any liability arising as a result is not covered by P&I insurance. The legal costs involved and any liability incurred may well remain with the person or company in question.
All these problems can and often do arise in a bunker spill.
Even if there is no initial bunker spill, it is very likely that, if the vessel has suffered a casualty of some kind, the first "request" (i.e., instruction) from the authorities will be: "remove the bunkers". The nature of the casualty and the quantity and location of the bunkers are often ignored. The focus - sometimes to the exclusion of almost everything else - is on the potential pollution which the bunkers could cause.
This may be good for the environment. It is certainly good business for the salvors. However, someone has to pay for it and it is likely that a ship owner will look for his P&I Club to do so, on the basis that the removal of the bunkers is mainly a measure to avoid or minimize pollution.
Over the last 20 years or so, there has been worldwide growth of environmental awareness and concern about the damage which we are all, in some way, said to be doing to the environment. These days, the publicity given by the media to an oil spill of any significance is extensive and almost always unfavorable to the ship owner, or indeed, almost anyone involved in the operation of the ship. Remember the very negative publicity which Total, the charterers of the ERIKA, received.
International conventions
With the exception of the US, a large proportion of the world's coastal states have ratified one or both of the Civil Liability Conventions (CLCs) and the International Convention on the Establishment of an International Fund for Compensation for Oil Pollution Damage (Fund Convention). These conventions essentially deal with compensation for loss and damage caused by oil pollution from tankers and are widely recognized and accepted.
The text of a new convention, specifically covering bunker spills, was agreed in March 2001 at an IMO Diplomatic Conference in London. It is unlikely to come into force for at least a couple of years, but the intention is for this latest Convention to fill the gaps left by the earlier CLCs, which effectively date back to 1969 and 1992.1

Neither the CLC 1969, nor the Protocols to the CLC of 1992, will apply to a spill of bunkers from a non-tanker, such as a bulk carrier. However, in general terms, if the bunker barge supplying the oil could be classed as a "tanker" and the spill occurred from the bunker barge, the CLC in one of its two forms would probably apply.
The fact that many countries are now focusing more closely on bunker spills can be seen from the new compulsory insurance requirements which have come into force in Australia.
As from 6th April 2001, all ships larger than 400 GT which are visiting an Australian port and are carrying oil as cargo or bunkers must have a "relevant insurance certificate". This rule does not cover oil tankers which are already required to have such insurance under the 1992 CLC. Clearly, therefore, the rule is aimed at non-tankers and by implication, at bunker pollution. Amongst other things, the "relevant insurance certificate" must state the amount of insurance cover, or other financial security, which "must be no less than the limit of any liability applicable under relevant international law". The good news is that, in most cases, the requirements should be met by carrying on board the original P&I Club certificate of entry, or a certified copy. The certificate must be produced on request.
Other problems with "good" bunkers
As can be seen from the above, bunkers do not have to be "bad" to cause serious problems. Apart from the pollution aspect, even on-specification bunkers can cause problems and damage, as can be seen from the example described below.
A purpose-built car carrier, laden with cargo for Japan and entered with Gard, was bunkering heavy fuel oil in the Far East just before Christmas 2016. The vessel was receiving bunkers into the No. 1 port and starboard bunker tanks. Because an inlet valve had been left open, bunkers leaked into the No. 4 centre heavy fuel oil tank. This tank was nearly full. Not surprisingly, it filled up and the excess oil overflowed up the ventilation pipe. Unfortunately, this pipe had a small hole, later found to have been caused by corrosion, through which fuel oil leaked out. Where did it go? Approximately 3 MT leaked out on to a car deck in No. 2 hold. Some of this ran down through lashing openings on to a further three car decks. As if this was not bad enough, a further, fortunately small, quantity of fuel oil leaked from a previously repaired part of the ventilation pipe from No. 4 centre F.O. tank. The cargo was BMW cars! Some 41 cars were badly damaged. A further 209 were slightly damaged. The estimated liability on the Club is USD 250,000. In addition, some areas of the vessel were heavily oiled and had to be cleaned. The time and expense involved in cleaning the vessel is unlikely to be covered by the P&I insurance. It is owners' responsibility to properly clean and prepare the vessel for loading and carrying cargo.
Bunker shortages
Engineers reading this article will know the difficulties involved in accurately measuring and perhaps more importantly, agreeing with the bunker supplier, the quantity of bunkers supplied. Inevitably, with a bulk liquid, there will be some minor measurement variations. Equally, however, there are examples where the difference between the bunker supplier's figures and the vessel's figures are substantial. It always seems to be the case that the supplier's figures are higher than the vessel's figures.
In a case mentioned in a recent warning issued by DNV and Intertanko, a vessel bunkered diesel and fuel oil. The responsible engineer on board the vessel recorded substantial shortages for both products. In the case of the diesel, the bunker barge's figure was 119.69 cbm , whereas the vessel's figure was 93.0 cbm, a shortage of 26.69 cbm. At the request of the vessel, the bunker barge resumed pumping diesel. Problems were also noted in relation to the fuel oil. The flow from the barge to the vessel was very slow. When the engineer commented on this, the crew of the bunker barge were seen to adjust a valve on board the barge, which resulted in the flow speeding up. Even so, on completion of bunkering, the vessel still recorded shortages of some 3 MT in relation to the fuel oil and some 19 MT in relation to the diesel.
"Bad" bunkers
We have seen how perfectly good (i.e., within specification) bunkers can cause serious problems and liabilities. Bad bunkers - bunkers which are off-specification - can cause equally difficult and expensive problems and liabilities.
Gard News issue No. 156 contains an article dealing with procedures for bunkering.2 It includes comments and suggestions in relation to sampling and testing the bunkers received, as well as practical advice, especially regarding the sampling and testing of bunkers before use. A little prevention at an early stage can avoid the need for a lot of (expensive) cure at a later date!
Speed and consumption claims
Unfortunately for ship owners and charterers and their insurers, proper sampling and testing is not always carried out. As a result, fuel which is off-specification in some way may well be supplied to the vessel. This does not mean that serious problems will automatically follow. The vessel's engine may be capable of using the fuel, albeit with a reduced power output and/or a greater consumption of fuel to produce the same power. Such circumstances are, however, likely to lead to a claim by charterers either because the vessel has burned a larger quantity of bunkers than she should have, or because she has taken longer to complete the voyage (because of the reduced power output). Often, the claim is a combination of the two aspects - what is called a speed and consumption claim.
Claims for delay
A speed and consumption claim by itself is not necessarily particularly difficult or expensive, but a long delay in the voyage will mean a delay in the delivery of the cargo. Often, this may not matter. Sometimes, however, it may be extremely important to both the seller and the buyer, especially if the price of the cargo has gone up or down during the period of delay. In such circumstances, the party who may have lost money because of the delay may well bring a claim against the vessel. Depending on the cargo and the variation(s) in price, the amount may be large. Further, the cargo itself may have suffered damage. Many fruit and vegetable cargoes have a limited shelf life and the conditions under which they are carried are calculated as precisely as they can be for the expected length of the voyage. A delay of only a few days can upset these calculations. The result can often be a claim for damage to the cargo, often the entire cargo if the vessel is carrying foodstuffs with a limited shelf life.
Conclusion
Being human, all of us will make mistakes from time to time. Fortunately, these mistakes rarely have important consequences, but from time to time, a person involved in the bunkering operation, or in the preparation and use of the bunkers on board the vessel, will make a mistake which results in a spill of bunkers, or in damage to the main engine or other machinery on board.
Clearly, it is impossible to do away with human error completely. One must accept that accidents will happen from time to time - that is what P&I insurance is for. However, by properly following well prepared and clearly explained procedures, the problems and incidents mentioned above can be avoided.

What is the cause of most bunker spills?


Over the last five policy years, 2014 to 2019, 18% of all pollution incidents handled by the Gard claims teams have been caused by bunker spills, with an average cost per incident in excess of USD 100,000. Although bunkering is a routine operation, it involves high risk. 
The two main concerns in bunker spills are firstly, the environmental impact of spills, especially from persistent oils, and secondly, the risk of crew members and/or owners facing criminal prosecution. So why do spills happen and how can they be prevented?
There can be a variety of reasons for the spills but the majority is overflow incidents. The underlying causes could be a high flow rate, incorrect line up, improper monitoring of both the tanks being bunkered and those not being bunkered, or not acting on high level alarms. The human element is very much involved. We see that bunker procedures and checklists usually contain all the necessary points to prevent such incidents from happening but what is lacking is putting them into practice. In our experience continuous monitoring of bunker tanks irrespective of whether they are being filled or not can help prevent a spillage, even in cases of incorrect line up. It is important that crew members, who have been assigned to manage a bunkering operation, are not burdened with other tasks and are well rested so that they can focus on following what is required by their procedures.
A selection of articles previously published by Gard AS may be read at,

Cargo Samples – your best defence


What’s the problem?
One of the functions of the bill of lading is that it is the evidence of receipt of the goods on board. It is the
duty of the master to ensure that the information shown on the bill of lading is accurate, including that regarding cargo quality.
However, in most cases, the ship’s staff is not able to assess the condition of the cargo on a tanker, due to loading via a closed system and limited resources on board to check the quality of the cargo. Also, although the master has every right to clause the bills, we have seen that most charterparties require a clean bill of lading. As a result, bills of lading may not be an accurate reflection of the quality of cargo on board.
Most cargo contamination claims are brought against the member at the discharge port. In most cases, the onus lies on the shipowner to prove that the contamination did not occur on board. Given the difficulties identified above, the ship becomes an easy target even if she was not at fault and the cargo was contaminated before it was loaded. Under these circumstances, sampling becomes vital as it can provide the shipowner with an important means of confuting any alleged cargo contamination claims.
When to take samples
It is very important to take samples at each of the stages of loading and discharging so that they can be compared, to identify the source of the contamination. The stages are:
1.      Shore tank sample prior to loading.
2.      Manifold sample at the start of loading, preferably with the manifold valve closed if possible; thereafter, spot checks should be carried out during the whole loading operation.
3.      Manifold samples during loading whenever there is a change in the shore tank.
4.      First foot samples from the cargo tank once cargo is received in the tanks.
5.      Final cargo tank samples after completion of loading.
6.      Cargo tank samples prior to commencement of discharge at the discharge port.
7.      Manifold samples at the start of discharge.
8.      Shore tank sample at the discharge port if there is any pre-existing cargo in the tank.

Who should take the samples?
Cargo surveyors attending at load and discharge ports are more often than not attending on behalf of the shipper and the consignee, and are not obliged to provide samples to the ship. The ship might be handed a
sample at the load port for delivery to the receiver at the discharge port.
This sample is not the property of the ship. Whether samples are provided to the ship or not, it is recommended that the ship’s crew draws samples to protect the interest of the ship owner.
Every effort should be made to get the cargo surveyor to sign and seal these samples; however, if the surveyor declines, then a senior officer should sign and seal the sample, and keep it in their safe custody. It is recommended that a ship’s officer always supervises the sampling on board to check that the correct and safe sampling procedure is  used based on the material safety data sheet (MSDS) of the cargo and that the sampling equipment and bottles are in a good and clean condition appropriate to hold the sample.
Sampling procedure
It is difficult to generalize the sampling procedure for the various liquids which are carried in bulk because of the diversity of the cargoes, the variety of loading procedures and the differing effects on human health and
the environment. Safety is vital and utmost care should be taken to avoid any exposure at the time of sampling.
Certain chemical cargoes might also require antidotes to be carried on board in case there is exposure to the chemical. The MSDS should be reviewed and the crew should have appropriate training before they undertake any activities where the risk of exposure is high. Hazards must be mitigated by the correct use of personal protective equipment and other safety equipment.
Samples should be drawn in compliance with the industry best practices as set out in publications such as:
  Ø  ASTM D 4057 – Standard Practice for Manual Sampling of Petroleum and Petroleum Products;
  Ø  ASTM E 300 – Standard Practice for Sampling Industrial Chemicals;
  Ø  BS 3195 – Methods for Sampling Petroleum Products;
  Ø  BS 5309 – Methods for Sampling Chemical Products;
  Ø  API Manual of Petroleum Measurement Standards, Chapter 8 – Standard Methods of Sampling Petroleum and Petroleum Products;
  Ø  ISO 5555 Animal and Vegetable Fats and Oils – Sampling.
In general, a ‘running’ sample taken by use of a bottle and sample cage is the preferred method; however, for nonhomogeneous cargoes, zone sampling is required to produce a representative composite sample. The properties of some chemical cargoes require that special sampling procedures be adopted such as excluding air, using specialist sample valves or ‘closed’ sampling methods due to the toxicity or flammability of the cargo. Appropriate safety procedures must be observed and the person taking the samples should always be
protected from exposure to the cargo.

Sampling equipment
Sampling equipment and bottles come in a variety of shapes, materials and sizes. Selection of the equipment and the container should be based on the product to ensure that there will be no interaction between the product and the container, which could affect the integrity of either. The following should be considered as a general guide:
  Ø  Internal surfaces should be designed to minimise corrosion, encrustation and clingage.
  Ø  Inspection cover/cap should be of sufficient size to facilitate filling, inspection and cleaning.  
  Ø  Sample containers should be clean and free from all substances (such as water, dirt, lint, washing compounds, naphtha and other solvents, soldering fluxes, acids, rust and oil) that might contaminate the cargo sample. Reuse of containers should be avoided; however, if necessary, the containers should be cleaned by a method that has been determined as acceptable for the intended use, for example, by rinsing with a suitable solvent.
  Ø  The equipment should be designed to allow safe transfer of the product both from the tank to the container and from the container to the analytical apparatus without affecting the sample product or the safety of the person handling the sample.
  Ø  The sampling equipment should be cleaned using a method that has been determined as acceptable for the intended use, for example, by rinsing with a suitable solvent.
  Ø  The sample container should be large enough to contain the required sample volume and have sufficient ullage space for expansion and mixing of the sample.
  Ø  Glass containers are suitable for many test and storage requirements. Clear glass bottles can be easily examined visually for cleanliness, and allow for visual inspection of the sample. Dark glass bottles offer protection to cargo samples that are affected by light.
  Ø  Plastic bottles may be used for certain liquids after ensuring that the sample would not be affected by problems such as solubility, contamination or loss of light components, or would not lead to failure of the sample bottle.
  Ø  Certain products can be stored in metal (tin, aluminum or stainless steel) cans. However, it is difficult to check the cleanliness of the cans prior to use. Certain products might become contaminated due to oxidation and corrosion on the can surface.
  Ø  Sample bottle closures/caps vary in their chemical resistance depending on the sealing insert. Appropriate sealing caps should be used. Waxed cardboard disc inserts are suitable for most petroleum products. Aluminum disc inserts are unsuitable for acids and alkalis.
  Ø  The master should ensure that adequate and appropriate sampling equipment and containers along with labels and seals are available on board, especially when the ship carries different grades of cargo.
Checking of samples
Ship staff might not have the means to analyse the sample, but should be able to check for:
  Ø  general physical appearance;
  Ø  colour and brightness;
  Ø  presence of water (if apparent);
  Ø  odour and taint (for non-toxic cargoes – refer to the MSDS for thecargo);
  Ø  other physical impurities visible to the eye; and
  Ø  the approximate pour point of the cargo if it is heated cargo.
Loading of cargo should be stopped immediately if the manifold samples show such apparent deviations. Further investigation should be carried out and the master should note protest. We recommend the member to also notify the club.
Labelling and storage of samples
All samples drawn should be sealed, labelled, retained and recorded. The following information should be recorded on the labels and the sample log for easy cross reference and traceability:
      1.      Ship’s name and operational status before loading, after loading and before discharge.
      2.      Product name.
      3.      Sample source – tank number, manifold number.
      4.      Sample type – top, middle, bottom, dead bottom, running, composite.
      5.      Identity of sampler/surveyor/crew member.
      6.      Date and time.
      7.      Location – port, berth, anchorage.
      8.      Seal number.
Sample bottles should be sealed in order to preserve the sample in the event of a dispute. Ship staff should ensure that the correct seal numbers are recorded in the sample log and other cargo documentation. Marked
samples should be retained in a dedicated sample locker, ideally for at least 12 months. Samples should not be exposed to extreme temperatures and should be kept in darkness. When no longer required, disposal should be by the appropriate means in accordance with MARPOL requirements. Samples of cargoes that are known to react should not be stowed together.
Conclusion
It is very important that a strict and diligent sampling procedure is adopted and included in the ship’s operations manual and that the staff are trained appropriately to follow the best practices required to carry the various grades of cargo that the ship transports.

Τετάρτη 11 Δεκεμβρίου 2019

Checklist for compliance with the 2020 sulphur cap


From 1 January 2020, the limit for sulphur in fuel oil on board ships operating outside designated Emission Control Areas (ECAs) will fall to 0.50% mass by mass (m/m). 

For this reason, the Shipowners' Club published a checklist, which may be used as a guide to compliment any operational changes that operators are planning, so as to ensure compliance with the upcoming MARPOL convention changes.


The checklist is divided into three categories. These are:
General
Ø  Have you developed a ship specific implementation plan, in accordance with guidance from the IMO?
Ø  In case that any structural modifications are necessary, have these been added to the ship specific implementation plan and approved by the flag state and/or classification society as applicable?
Ø  Has a risk assessment for compliance been conducted and is it available on board?
Ø  Has crew and shore side personnel training been carried out with appropriate records available?
Ø  If the ship is more than 400GT, is the International Air Pollution Prevention (IAPP) Certificate or related exemption documentation available on board?
Ø  Are the Oil Record Book and any other required records available and up to date?
Ø  Do records note the condition of tanks, pipelines and other associated bunkering equipment?
Ø  Do the Bunker Delivery Notes clearly verify whether the fuel oil sulphur content is above 0.50% m/m?
Ø  Have you taken precautions to avoid comingling of supplied bunkers with fuel already on board the vessel?
Ø  If comingling of fuel is unavoidable, have you made sure that clear fuel test documentation is available for each batch of fuel?
Ø  Have you made preparations for entry into Emission Control Areas (ECAs) in sufficient time to allow for complete flushing of the fuel system or effective operation of the scrubber system?
Ø  If so, are written changeover procedures available to crew and the necessary associated records available and maintained on board the vessel?
On ships where scrubbers are installed
Ø  Is the scrubber system type approved, in good working order with planned maintenance tasks up to date and monitoring devices fully operational?
Ø  Are operational and maintenance records for the scrubber system and its related equipment being maintained on board and are these available for inspection?
Ø  Do any ports restrict or have additional requirements for the discharge of open loop scrubber system wash water on the upcoming voyage(s)?
Ø  If so, have you made arrangements for specialist disposal arrangements if necessary?
Switching to a new fuel type
Ø  Have you completed a suitability assessment, including reference to manufacturer’s instructions, to establish what impacts a change in fuel type may have on existing machinery and equipment?
Ø  Have the tanks and pipelines been thoroughly flushed and cleaned to avoid cross contamination?
Ø  Do records note that segregation of fuel system tanks and pipe work has been maintained where necessary?
Ø  Have you carried out additional tests for bunkers before utilising them?
Ø  If additional tests are not practicable, are you monitoring the vessel’s filters and fuel consumption when commencing use of fresh bunkers in order to identify any problem at the earliest opportunity?
The port state control authorities will inspect the vessel posing several risk factors, such as vessel’s historic PSC performance, its age, flag, classification society and ISM manager performance.
Also, PSC may also target a vessel if they are alerted by a third party, such as a pilot, or by ‘sniffing’ devices that detect stack emissions.
#2 Inspection process
Except IMO's PSC guidance, the inspection depends on the factor whether the vessel has an exhaust gas cleaning system (EGCS) installed, and this may be different from state to state.
PSC inspectors will ask to see several documents, as:
Ø  Ship’s certificates relating to MARPOL Annex VI (e.g. IAPPC + supplement, EIAPPC)
Ø  Bunker delivery notes (BDN) retained as required
Ø  Bunker operation checklists
Ø  Bunker certificates of quality
Ø  Ship implementation plan
North alerts that if the port State believes that the vessel and its equipment are not in line with the documentation or if the crew seems unfamiliar with the operations, then a more thorough inspection will follow. In the meantime, when a ship is not equipped with an exhaust gas clean system (EGCS) or the use of it is banned form the port, then the PSC are likely to check that its fuel is compliant.
This may require testing of:
Ø  the MARPOL delivered sample (drawn at time of bunkering and retained by the vessel)
Ø  the not-in-use onboard sample (drawn from the vessel’s bunker storage tanks during inspection)
Ø  The in-use sample (drawn as close as possible to the engine inlet during inspection)
Learn more on "Preparing for PSC guidance" at,