2 Recommended procedure for sampling
2.1 In order to evaluate the contents of the discharge water and its effects, it is
recommended that samples be analysed for the parameters listed under paragraph 2.4.1
of this appendix.
2.1 Preparation
2.1.1 This section describes preparations recommended prior to any sampling.
2.1.2 The EGCS should be equipped with sampling points for sampling of the following
water streams:
-
.1 inlet water (for background);
-
.2 water after the EGC unit after treatment (if applicable) but before any
kind of dilution; and
-
.3 discharge water after treatment and dilution.
2.1.3 Preparation for sampling, handling and transport
2.1.3.1 Sampling equipment
The sampling equipment and pre-prepared sample containers should be made ready prior
to sampling. The equipment can be ordered from the laboratory performing the
analysis. The equipment should be ordered well before the sampling takes place,
taking into consideration the itinerary of the ship.
The table below lists the recommended physical properties of the sampling bottles
needed. It takes ISO 5667-3 and the appropriate analytical standard into account,
but other equivalent standards can also be used. The table furthermore informs how
the samples should be stored when drawn and when at the latest they need to reach
the laboratory for analysis.
Parameter
|
Bottle material
|
Volume
|
Method specifying sampling bottle requirements
|
Preservative
|
Storage temperature
|
Maximum time until analysis
|
NO2-/NO3-
|
PE
|
250 mL
|
ISO 10304-1
|
No preservative
|
Frozen (≤ -18°C)
|
8 days
|
Total Metals
|
PE
|
500 mL
|
ISO 17294-2
|
HNO3 Acid
|
Cooled (4°C) / dark
|
1 month
|
Dissolved Metals
|
PE
|
500 mL
|
ISO 17294-2
|
No preservative
|
Cooled (4°C) / dark
|
1 month
|
PAHs
|
Amber-glass with PTFE seal
|
2 L (OL), 1 L (CL)
|
DIN EN 16691 or EPA 8270
|
No preservative
|
Cooled (4°C) / dark
|
7 days
|
Hydrocarbon oil index (GC-FID
analysis)
|
Glass
|
1L
|
ISO 9377-2
|
Mineral acid pH<2
|
Cooled (4°C) / dark
|
4 days
|
It is practical to label sampling bottles before sampling. Identify each bottle such
that it can be tracked back to sampling point, sampling parameter, EGCS operation
mode and EGCS load.
2.1.3.2 Preparation for storage and holding of samples
To ensure proper storage and holding, crew need to appoint an appropriate space on
board for samples and ice packs, preferably in an enclosed container in a cool space
without direct sunlight.
2.1.3.3 Preparation for transport
If samples need to be transported with ice packs, the ice packs should be deep-frozen
at least 48 h prior to sampling.
It is recommended to arrange shipping of the samples in advance with the port agent
of the destination port.
2.1.3.4 Preparation of personnel conducting the sampling
To ensure the health and safety of the personnel, it is recommended to wear the
following equipment:
-
2.1.3.4.1 Protective eyeglasses/goggles, ear protection, gloves,
protective clothing and safety shoes
2.1.3.5 Personnel qualifications and responsibilities.
It is important that the personnel taking the samples are well trained. They should
be aware of:
The personnel should be competent in drawing samples and should know the location of
the sampling points and how to safely dispose of the collected flushing water.
2.1.3.6 Information prior to sampling
It is recommended to complete the templates under 3.1 prior to sampling.
2.2 Collection
2.2.1 Sample time schedule
It is recommended to prepare a sampling time plan in advance in agreement with the
crew, considering when at the latest the samples need to be analysed at laboratory.
The sampling plan should contain information that can identify which bottle contains
which water (OL/CL, inlet/outlet, etc.) and at which hour the sample was drawn. In
this manner, continuous recorded EGCS control parameters can be retrieved at a later
stage. Sampling should be undertaken with the EGCS operating above 50% of maximum
exhaust gas flow (4.2.2.1.2.1 / 5.6.1.2.1).
2.2.2 Filling the sampling bottle
To prevent contamination during sampling, the following practices are recommended:
-
.1 use sampling bottles prepared by the laboratory;
-
.2 the water flow and thus the engine load(s) should be steady before and
during sampling;
-
.3 the sampling valve should be flushed with a minimum of 10 litres of
sampling water before samples are taken and it should not be closed or
touched after flushing or before the sampling is done;
-
.4 if more than one bottle is filled, the sampling valve should not be closed
in between;
-
.5 the use of any hydrocarbon-based cleaning agents at the sampling point
should be avoided; and
-
.6 fill the sampling bottles to the brim and close firmly to avoid air in the
bottles.
2.2.3 Information while sampling
It is recommended to complete the template under 3.2 while sampling.
2.3 Transportation
Sampling equipment to be used during transportation should meet provisions under
2.1.3.1 above.
2.3.1 Transportation container
For transportation an insulated and leak-proof container should be used. The
transportation container should be provided by the laboratory. It should be able to
hold a sufficient quantity of ice packs.
2.3.2 Shipping to the laboratory
Samples should be shipped to the laboratory as fast as possible. The transportation
container should be labelled in accordance with local requirements for shipping and
handling of water samples.
Immediately before handing over the samples to the port agent, the ice packs should
be put into the box.
2.3.3 Chain of custody
A formal chain of custody process is required, with records.
Usually it is not necessary to include a customs declaration as these are water
samples of zero commercial value.
2.3.4 Information from the laboratory
Take into consideration any information provided by the laboratory.
2.4 Sample preparation and analysis
Analysis should be undertaken by ISO 17025-accredited laboratories using EPA, ISO or
equivalent test procedures. Methods used in the laboratories need to be within the
scope of ISO 17025 accreditation of the laboratory.
2.4.1 To ensure comparability of laboratory results, the following methods are
recommended:
Parameter
|
Recommended method for sample
analysis
|
Recommended method for sample
preparation
|
Polycyclic Aromatic Hydrocarbons
(PAH):
|
|
|
16 EPA PAHs:
|
|
|
Acenaphthene
|
|
|
Acenaphthylene
|
EN 16691:2015
|
*
|
Anthracene
|
|
|
Benzo-a-anthracene
|
or
|
|
Benzo-a-pyrene
|
|
|
Benzo-b-fluoranthene
|
ISO 28540:2011
|
*
|
Benzo-g,h,i-perylene
|
(recognizing EN 16691 as
ISO is currently under consideration)
|
|
Benzo-k-fluoranthene
|
|
Chrysene
|
|
Dibenzo-a,h-anthracene
|
|
|
Fluoranthene
|
or
|
|
Fluorene
|
|
|
Indeno-1,2,3-pyrene
|
EPA 8270
|
EPA 3510;
|
Naphthalene
|
|
or
|
Phenanthrene
|
|
EPA 3511;
|
Pyrene
|
|
or
|
Sum of 16 PAHs
|
|
EPA 3520.
|
Oil detailed GC FID analysis
|
ISO 9377-2:2000
|
*
|
Determination of Hydrocarbons Oil
Index
|
|
|
Nitrate and nitrite
(NO3-/NO2-)
|
ISO 10304-1:2007
or
|
*
|
|
ISO 15923-1:2013
or
|
*
|
|
ISO 13395:1996
or
|
*
|
|
EPA 353.2
|
*
|
Total Metals:
|
ISO 17294-2:2016
|
ISO
15587-1:2002
|
- - Cd
- - Cu
- - Ni
- - Pb
- - Zn
- - As
- - Cr
|
or
|
|
EPA 200.8
or
|
*
|
EPA 200.9
|
*
|
Dissolved
Metals:
- - Cd
- - Cu
- - Ni
- - Pb
- - Zn
- - As
- - Cr
- - V
- - Se
|
ISO 17294-2:2016
or
|
ISO 17294-2:2016 and
filtration on 0.45 μm + HNO3
|
EPA 200.8
or
|
EPA 200.8 and filtration on 0.45 μm +
HNO3
|
EPA 200.9
|
EPA 200.9 and filtration on 0.45 μm +
HNO3
|
Discharge water pH should be determined
by instant onboard measurements
|
Record pH immediately on board
|
Record pH immediately on board
|
* Preparation method is included in the analytical method.