Title: DIPTARKAPALYE
1Inventory of Hazardous Material
2Hongkong Regulation
3EU Ship Recycling Regulation 1257/2013
4The Legislation
5Guidelines for development of the
IHM(MEPC.269(68))
Class Surveyor undertakes Verification Survey
IHM Report Submit to Class verification
Approvals
Shipowner Appoints IHM Service Supplier
Class Surveyor checks IHM against items onboard
Issue SoC with Validy of 5 Years
IHM Service Supplier Documentation Sampling, Lab
sample Testing Final report
Review by Class Intital Approval
6HKC EUSSR
- Additional Perfluoro octane Sulfonic Acid - PFOS
in (Table A) - Hexabromocyclododecane HBCDD in (Table B) for
the EU ship recycling regulation.
7Newbuild Vessel Compiling Part-1
8Existing Ship Compiling Part-1
9Visual Sampling Check Plan
- The presence of material for Table A B is
likely, either on the basis of documentary
evidence or the expert opinion of the person(s)
developing the plan. - Documentation is not specific as to whether
material are present and material of uncertain
composition were used. - The Visual/Sampling check plan should be based on
the following three lists - List of equipment, system and/or area for visual
check - List of equipment, system and/or area for
Sampling check - List of equipment, system and/or Classes as
Potentially containing hazardous material.
10Maintaining Part-1
- All containing hazardous material to recorded.
11Marking in GA
- Recorded hazardous material to Marked in GA.
12Asbestos
- Asbestos is the generic commercial designation
for a group of naturally occurring mineral
silicate fibres of the serpentine and amphibole
series. - Threshold value 0.1
- Where it is found?
13Asbestos
- Possible location of hazardous material
14Asbestos Health Effects
- Asbestosis (lung scarring)
- Lung cancer
- Mesothelioma (cancer of pleura ( Brustfell)
- Pleural changes (thickening)
- The time lag between exposure and potential
illness is extremely long (20 50 year) - All types of asbestos are considered dangerous
- In general, the risk to develop asbestos related
diseases are related to the exposure of asbestos
15Polychlorinated biphenyls (PCBs)
- Polychlorinated biphenyls (PCBs) are a class of
synthetic chlorinated organic compounds
(chlorinated hydrocarbons) with biphenyl as the
basic structural unit. - Generally, globally phased out between mind
1970-1980 - Ships built after 1992 unlikely to contain PCBs
- Threshold value 50 mg/kg
- Possible location of hazardous material
16PCB Health Effects
- Acute toxicity
- Enlargement of the liver
- Damage of the immune system
- Chloric acne
- Chronic toxicity
- Cause cancer
17Ozone depleting substances(ODS)
- ODS is a compound that contributes to
stratospheric ozone depletion. - Restricted / banned to use by Montreal Protocol
since 1989 - At the end of 2018, the United Nations confirmed
in a scientific assessment that the ozone layer
is recovering - Possible location of hazardous material
18ODS Health Effects
- Ozone depleting substances cause no direct harm
to mankind, they have the ability to reduce ozone
and have a climate effect large than that of
carbon dioxide.
19Anti-fouling systems containing organotin
compounds
- Organotin compounds tin with hydrocarbon
substituents - Tributyl tins (TBT), Tributyl tin oxide (TBTO),
Triphenyl tins (TPT). - Possible location of hazardous material
- Hull Painting Coating
- Top Side Painting Coating
- Threshold value 2500 mg/kg
20Organotin compounds-Health Effect
- The lowest concentration inhaled from the air
that causes toxicity in humans is 20 ppm for
three minutes and 10 ppm for five minutes - Underwear treated with TBT has caused severe skin
irritation. - Shipyard workers exposed to TBT dust and vapors,
while repairing a submarine, developed breathing
problems, irritated skin, headaches, colds, flu,
fatigue, dizziness and stomach aches - TBT exposure can also irritate the eye, skin, and
mucous membranes and prolonged exposure may cause
liver and kidney damage
21Perfluoro octane Sulfonic Acid (PFOS)
- Perfluorooctanesulfonic acid (PFOS) (conjugate
base perfluorooctanesulfonate) is an
anthropogenic fluorosurfactant and
global pollutant. - Threshold value 10 mg/kg
- Possible location of hazardous material
- Foam Liquid
- Floor Covering Adhesive
22Cadmium Compound
- Cadmium is a silver-white metal. It melts at
321C. When heated above this temperature in air,
poisonous cadmium oxide fumes are emitted.
However, cadmium is most frequently used in the
form of compounds, such as cadmium oxide brown
crystals cadmium selenide brown or red powder
and cadmium sulphide yellow/orange crystals. - Possible location of hazardous material
- Cadmium and its compounds are used in many
processes and products including - Nickel-cadmium battery manufacturing
- Paints
- Threshold value 100 mg/kg
23Hexavalent Chromium and Hexavalent Chromium
Compounds
- Chromium and its compounds form a large and
varied group of chemicals. The hazards depend on
the chemical forms encountered. - Possible location of hazardous material
- Pigments for paint and coating
- Threshold value 1000 mg/kg
24Lead Lead Compound
- Possible location of hazardous material
- Batteries
- Lead-acid batteries
- General Purpose Emergency Generator, Life boats
Batteries - Corrosion resistant primer, paints (especially
outdoor paints) - Threshold value 1000 mg/kg
25Mercury Compound
- Possible location of hazardous material
- Mercury is used in many different applications
- In fluorescent light bulbs and mercury arc lamp
- Electrical switches
- Gyro Compass
- Ballast gauge systems, anodes.
- Thermometers.
- Threshold value 1000 mg/kg
26Polybrominated Biphenyls PBBs
- Polybrominated biphenyls (PBBs), also called
brominated biphenyls or polybromobiphenyls, are a
group of manufactured chemicals, of the
polyhalogenated compounds. - Possible location of hazardous material
- Non-flammable plastics
- Insulation in cables
- Cellular rubber
- Threshold value 50 mg/kg
27PBBs- Health Effect
- Pre- and post-natal exposure to PBB in girls
leads to menarche at an earlier age. - Cancer
28Polybrominated Diphenyl Ethers PBDEs
- Polybrominated diphenyl ethers or PBDEs, are
organ bromine compounds that are used as flame
retardant. They are structurally similar to the
PCBs and other polyhalogenated compounds,
consisting of two halogenated aromatic rings. - Possible location of hazardous material
- Non-flammable plastics
- Insulation in cables
- Cellular rubber
- Threshold value 1000 mg/kg
29PBDEs- Health Effect
- Reduce fertility in humans
- PBDEs bio accumulates in blood, breast milk, and
fat tissues - Increasing PBDE levels have been detected in the
blood of marine mammals such as harbor seals.
30Polychlorinated naphthalene PCN
- Polychlorinated naphthalene (PCN) products are
made by chemically reacting chlorine with
naphthalene, a soft, pungent solid made from coal
or petroleum. - Possible location of hazardous material
- Paint, Lubricating oil
- Insulating coatings for electrical wires
- Threshold value 50 mg/kg
31PCN Health Effect
- Severe skin rashes
- Chronic exposure increases risk of liver disease
that led to deaths - Chloral-acne
- Increased cancer risks
32Radioactive substances
- Radioactive source means radioactive material
permanently sealed in a capsule or closely bonded
and in a solid form that is used as a source of
radiation (not radioactive residues or
contamination) - Radioactive sources should be included in the
Inventory, regardless of the number, the amount
of radioactivity or the type of radionuclide. - Possible location of hazardous material
- Ionization chamber smoke detectors
- Radioactive level gauges
- Radioactive dredger gauges
- Radioactive conveyor gauges
- Radioactive spinning pipe gauges
33Certain short chain chlorinated paraffin (SCCP)
Chlorinated paraffin (CPs) is a complex group of
manmade compounds. They present an important
class of chlorinated straight-chained
hydrocarbons in the carbon range of C10 to C30.
- Possible location of hazardous material
- Non-flammable plastics.
- Floor Covering.
- Paint Coating
- Rubber, adhesives, sealants and plastics.
- Threshold value 1
34Short Chain Chlorinated paraffins (SCCP)-Health
Effect
35Hexabromocyclododecane (HBCDD)
- HBCDD is a brominated flame retardant, used to
establish fire safety in foams, plastics and
textile coatings. - Possible location of hazardous material
- Cryogenic insulation, such as for liquefied gas
tanks (LGT). - Refrigerated areas.
- Thermal insulation boards (i.e. foam materials).
- rubber and plastic materials (i.e. cable
sheaths, PVC flooring) - Threshold value 100mg/kg
36IHM Maintenance
The IHM maintenance process is divided in three
line of defenses
Purchase and procurement control
Vessel control
Technical Department.
- Verify the receipt of MD and or SDoC and quantity
of items/components as per indicative list. - Weekly report Appendix C shall be filled up by
Ship staff for any item received onboard and to
be sent to Technical department and designated
IHM Expert Company.
- A guidance document on the Indicative list
(Appendix B) of all possible Ship equipment,
components or items which may contain HM shall be
shared with Suppliers to identify and prohibit
supply of hazardous materials listed in Appendix
D. - MDs (Material declaration) and SDoC (Supplier of
declaration of conformity) shall be obtained for
all general item or components of equipment,
system that may be installed, applied, or
modified to the vessels.
37IHM Maintenance Process
Vessel raise requisition for spare parts.
Supplier share all relevant documents for spare
parts
Purchase and procurement
Upon receipt of quotation. Such list of supply
along with MD or and SDoC or hazardous
declaration shall be shared or followed up with
the Ship staff for necessary onboard verification
of items being supply onboard.
Technical department
Ship staff shall verify the receipt of MD and or
SDoC and quantity of items/components. Update
monthly report and send to Technical department
and DP.
Ship Responsibility DP
38IHM Record
Designated person on Ship shall maintain
following records respective to their department
in a single file called IHM register
01
04
IHM initial survey and inspection reports along
with all relevant Laboratory test reports
Statement of Compliance or IHM certificate
02
05
Additional sampling or Random sampling report
Supplement to IHM part1
Update/Changes in The Inventory confirmed by IHM
designated person ashore and related supporting
documents MD or SDoC
03
06
Repair facility work report or HM disposal report
39Survey and certification
an initial survey Ensures IHM Part I complies
with the requirements of the Regulation
An additional survey must ensure that any
change, replacement, or significant repair of the
structure, equipment, systems, and material,
which has an impact on the IHM, has been made in
a manner that ensures that the ship continues to
comply with the requirements of the Regulation,
and that Part I of the IHM is amended as
necessary.
a renewal survey Ensures IHM Part I complies
with the requirements of the Regulation
Final survey must verify that the IHM (Parts I,
II and III) and the ship recycling plan comply
with the requirements of the Regulation and that
the ship recycling facility where the ship is to
be recycled is included in the European List
40IHM Monthly Report
Report to vessel manager, and follow for
obtaining the MD and SDoC
Spares received with No HM as per indicative
list - appendix B
No
Update IHM Report in System Easy to Download
via Software
No
Share all MD and SDoC with vessel manager and
responsible IHM expert company
Nil Declartion
Identify the Items .Is the Material declaration
(MD) or Supplier declaration SDoC received with
the item.
Does The spares , stores, component ,system
being serviced by external party has any item as
mentioned under IHM indicative list i.e Appendix
B
No
Did vessel receive any spares, stores, component
.
Yes
Yes
Yes
41IHM Record Book
- Sorting Sdoc Mdoc Categorize wise
- Zero MD
- Below threshold MD
- Above threshold MD
Supplier to shares Mdoc Sdoc for each PO
Uploading in Software
Vessel Manager Issues PO for Spare Part Supplier
Update IHM Record book will be sent in 3 working
days
If Contained, then update in IHM Part-1
Verifying Mdoc Sdoc received from Supplier
42Handling Precautions
- The Hazardous detected in vessel is mainly in
gasket installed between various piping flanges.
These gaskets are not exposed to the crew onboard
during normal course of operation. - Other Items such as brake pads of winches and
Cranes and packing, gasket and insulation fitted
in Auxiliary Boiler/composite Boiler/Incinerator.
These items are also not exposed to the crew
onboard during normal course of operation. - The crew will handle such equipment where
Contained or PCHM identified only during any
emergency repair, crew will use required tools,
PPE and removed item will be handle as per the
procedure. - In No circumstance other than emergency repair
the item will be handle by crew, removal of
Contained and PCHM will be handled by expert
company. - For removal of Contained and PCHM in brake pad
and insulation, wet method to be used as minimum.
43Monitoring
- All the item which are identified as Contained or
PCHM, these items are not exposed to the crew. - Gasket where asbestos is identified is fitting
between pipe flanges, where asbestos identified
in packing same is provided between two metal
enclosure, similarly insulation of chamber in
auxiliary Boiler/composite boiler/incinerator are
covered by metallic sheet. No action to be taken
in case if no deterioration in the condition of
these items
44Selection and use of Tools
- It is important to select the correct tools to
minimise the generation of airborne fibres.
Manually operated (non-powered) hand tools should
be used wherever possible. If they will not
provide sufficient physical force to perform the
required operation, low-speed battery-powered
tools which are able to be used in conjunction
with wet methods for dust control are preferred.
mainly Spray Bottle, duct tape, suitable waste
container, disposable wet cleaning rags , wet
wipes. - Note- High-speed abrasive power and pneumatic
tools such as angle grinders, sanders and saws
and high-speed drills must never be used.
Compressed air must never be used to clean dust
from a brake assembly.
45Selection and Use of personal protective
equipment (PPE).
- Personal protective equipment may need to be
used, in combination with other effective control
measures, when working with containing Hazardous
materials. - The ease of decontamination should be one of the
factors considered when choosing PPE. Where
possible, disposable equipment should be used.
All disposable PPE should be disposed off. - The PPE are mainly
- Coveralls - Clothing should be made from material
capable of providing adequate protection against
fibre penetration and disposable type. - Disposable coveralls with fitted hoods and cuffs
should be worn. Coveralls with open pockets
and/or Velcro fastenings should not be used,
because these features can be easily contaminated
and are difficult to decontaminate. Fitted hoods
should always be worn over the straps of
respirators, and loose cuffs should be sealed
with tape. - Footwear and gloves- Laced boots should be
avoided, as they can be difficult to clean and
Hazardous dust can gather in the laces and
eyelets. Lace less boots, such as gumboots, are
preferred where practicable, and boot covers
should be worn where necessary. - If significant amounts of Hazardous material
fibres may be present, disposable gloves should
be worn. Protective gloves can be unsuitable if
dexterity is required. Workers must clean their
hands and fingernails thoroughly after work, and
any gloves used they must be disposed of as
asbestos waste. - N-95 type mask shall be used as a minimum while
dealing with Non friable asbestos.
46Maintenance and service area including
establishing barrier where required.
- Before commencing the task, plastic sheeting may
need to be placed on the floor and any other
surfaces that may become contaminated with
asbestos dust. At a minimum, heavy-duty thick
plastic sheeting should be used for this purpose.
- Wet wiping of surface that is to be worked on may
also be necessary before commencing the task, to
minimise the disturbance of Hazardous fibres on
the surface.
47Maintenance and service area including
establishing barrier where required.
- Techniques that prevent or minimise the
generation of airborne hazardous fibres include - The wetting of Containing Hazards using
surfactants or wetting agents, such as detergent
water. - Performing the task in a controlled environment
(i.e., a ventilated enclosure). - The work area should be clearly defined to ensure
that non-essential people do not enter and warn
persons that work is being carried out (e.g.,
through the placement of barriers and signs or
other warning devices). - Potential entry points to the All barriers and
warning signs should remain in place until a
clearance to re-occupy has been granted
48Decontamination of Tools, Personnel and working
area.
- Decontamination to be performed again depending
upon whether ACM and PCHM are Friable or Non-
friable type, all contaminated materials,
including cleaning rags, plastic sheeting, and
PPE etc, must be disposed of waste. - Decontamination of working area
- Any Hazardous dust or debris must be collected in
a safe manner and the asbestos work area
decontaminated, paying attention to all walls,
ledges, fittings, and furnishings.
Decontamination is either by wet method or Dry
method. - Wet Method - involves the use of damp rags to
wipe down contaminated areas. Cleaning rags
should only be used once, although they may be
re-folded to expose a clean surface. The rags
should be used flat and should not be wadded. If
a bucket of water is used, the rags should not be
re-wetted in the bucket, as this will contaminate
the water. - Dry method- should be only used where wet methods
are not suitable or pose a risk because of other
hazards such as electricity or slipping. Dry
decontamination procedures include carefully
rolling or folding up and sealing plastic
sheeting and/or vacuuming the asbestos work area
with an asbestos vacuum cleaner. Large pieces of
asbestos debris should be wetted and picked up by
hand rather than vacuumed.
49Decontamination of Tools
- All tools, equipment and reusable respirators
used during the maintenance or service task
should be dismantled (where appropriate) and
decontaminated, using either the wet or dry
decontamination procedures described above before
they are removed from the asbestos work area. - If tools and equipment cannot be decontaminated
in the Hazardous work area or are to be reused at
another Hazard work area, they should be tagged
to indicate Hazardous contamination and double
bagged in Hazardous waste bags before being
removed from the work area. This equipment and
tools must remain sealed until decontamination or
the commencement of the next maintenance or
service task where the equipment can be taken
into the work area and reused under full control
conditions. - PPE should be worn when opening the bag to clean
or re-use the equipment or tools, and
decontamination should only be performed in a
controlled environment. - Bags containing asbestos contaminated equipment
and tools should be clearly labelled with an
appropriate warning statement.
50Personal decontamination
- Personal decontamination must be undertaken each
time workers leave the Hazardous work area and at
the completion of the Hazardous maintenance or
service work. Personal decontamination should be
done within the Hazardous work area where
re-contamination cannot occur. - PPE should not be transported outside the work
area except for disposal purposes. - Disposable coverall, footwear cover shall be
disposed, and Double seal plastic bin and the
footwear should also be wet wiped. - Any PPE used while carrying out Hazardous work
must not be taken beyond working area without
decontamination. - Personal hygiene and careful washing are
essential. Particular attention should be paid to
the hands, fingernails, face and head.
51Personal decontamination
- A competent person may decide, that the following
personal decontamination procedure can safely be
used - First, all visible hazardous dust/residue is
removed from protective clothing, using an vacuum
cleaner and/or wet wiping. - Second, the disposable coveralls are taken off
(while still using a respirator), placed in an
hazardous waste bag and disposed of as hazardous
waste - Respiratory protective equipment should be used
until all contaminated disposable coveralls and
clothing has been vacuum cleaned and/or removed
and bagged for disposal, and personal washing has
been completed. - After removing the respirator if used, workers
should wash their head, face and hands, paying
particular attention to their fingernails.
52Waste removal
- Hazardous waste, including contaminated PPE and
cleaning materials (e.g., cleaning rags and
plastic sheeting used to cover surfaces in the
asbestos work area), should always be removed and
disposed of by a competent person or expert
company. - It may be collected and disposed of in hazardous
waste bags and/or in a solid, sealable hazardous
waste container, such as a bin or drum. - Controlled wetting of hazardous waste should be
used to reduce the possibility of dust emissions
during the bagging or containment of the waste.
53Waste bags
- Hazardous waste should be collected in heavy-duty
200 µm (minimum thickness) polythene bags that
are no more than 1,200 mm long and 900 mm wide. - The bags should be labelled with an appropriate
warning, clearly stating that they contain
asbestos and that dust creation and inhalation
should be avoided. - An example of a warning statement which might be
used is - CAUTION
- DO NOT DAMAGE OR OPEN BAG
- DO NOT INHALE DUST
- CANCER AND LUNG DISEASE HAZARD
54Waste drums and bins
- All drums or bins used for the storage and
disposal of hazardous waste should be in a good
condition, with lids and rims in good working
order, and free of hazardous residues. - The drums or bins should be lined with plastic
(minimum 200 µm thickness), and labels warning of
the asbestos waste should be placed on the top
and side of each drum or bin, with the words,
Danger asbestos. Do not break seal or a
similar warning. - If the drum or bin is to be re-used, the
hazardous waste must be packed and sealed so that
when the drum or bin is emptied there is no
residual asbestos contamination.
55Disposal
- All hazardous waste should be removed by a
competent person and transported and disposed of
in accordance with all relevant State or
Territory legislation and guidelines for the
transport and disposal of asbestos waste. - Further information on the transport and disposal
of asbestos waste, including licensing
requirements and designated hazardous waste
dumps, may be obtained from local ports or the
relevant environmental protection authority or
waste disposal authority. - Note In No circumstance other than emergency
repair the item will be handle by crew, removal
of Contained and PCHM will be handled by expert
company only.
56Recommended references
- MEPC 269 (68)
- https//www.dropbox.com/s/cptlt3a7l6cxd6i/MEPC_Res
olution_26968.pdf?dl0 - EU SRR EMSA guidance
- https//www.dropbox.com/s/vqybpcccvs9d1oe/EMSA20G
uidance20on20IHM.pdf?dl0 - GESCO IHM manual
- https//www.dropbox.com/s/ab27xxwort8qcqm/IHM20pr
ocedure.pdf?dl0 - Asbestos Management Plan
- https//www.dropbox.com/sh/870gu38dx2jbdyn/AAAw7Z0
AZa6_5jirSeHLNB-3a?dl0 - Note Asbestos management plan is only for vessel
Containing Asbestos.
57Thank You
- Integri Marine and Offshore Services Pvt Ltd
- Address C1210/11, Kailash Business Park,
Vikhroli (W) Mumbai -400079 Maharashtra, India - Contact no. 919820719814, 919819126713
- Email support_at_integrimarin.com
- Website www.integrimarine.com