Appendix 3 - Discharge Water Data Collection
Clasification Society 2024 - Version 9.40
Statutory Documents - IMO Publications and Documents - Resolutions - Marine Environment Protection Committee - Resolution MEPC.340(77) - 2021 Guidelines for Exhaust Gas Cleaning Systems - (adopted on 26 November 2021) - Appendix 3 - Discharge Water Data Collection

Appendix 3 - Discharge Water Data Collection

 1 Introduction

1.1 The discharge water quality criteria are intended to act as initial guidance for implementing EGCS designs. The criteria should be reviewed in the future as more data become available on the contents of the discharge and its effects, taking into account any advice given by GESAMP.

1.2 Administrations should therefore invite the collection of relevant data. To this end, shipowners in conjunction with the EGCS manufacturer are invited to sample and analyse samples of EGCSs, taking into account section 2 and section 3 of this appendix, as appropriate.

1.3 The sampling could be conducted during approval testing or shortly after commissioning and at about 12-monthly intervals.

 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:

  • .1 how the system is working and where the sampling points are located; and

  • .2 how to dispose of the flushing water collected during flushing.

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.

 3 Recommended template for submitting sampling data

When submitting sampling data to the Administration, the data should include information according to paragraphs 1 and 2 as well as the results from the analyses as described under paragraph 2.4.

When submitting sampling data to the Administration, the following template is recommended.

3.1 Data Template Part 1
Information prior to sampling
Parameter Value Unit
3.1.1 Ship information
Ship's name    
IMO number    
Ship build date   dd.mm.yyyy
3.1.2 Combustion unit(s) details
Engine questions should be answered for every fuel-burning facility connected to the EGCS
Number of combustion units connected to EGCS    
Combustion unit(s) manufacturer(s)    
Type of combustion unit(s) (ME, AE, 2/4-stroke, boiler)    
EGCS capacity in MW    
3.1.3 EGCS general    
Name of manufacturer    
Name of system    
Number of streams single/multiple  
System operation mode open/closed/hybrid  
Type of washwater treatment    
EGCS retrofit or new building    
Installation date    
ETM scheme A or B approval    
Additional notes:

3.2 Information in conjunction with sampling for each operation mode (OL and/or CL)
Parameter Value Unit
3.2.1 Ship information during sampling
Cruise speed   knots
Start of sampling date and time   UTC
Stop of sampling date and time   UTC
Ship's position start of sampling   GPS
Ship's position end of sampling   GPS
Weather conditions (during sampling)   calm/rough
3.2.2 EGCS operation
Approx. EGCS load   %
System operation mode open/closed  
Type of washwater treatment, if any    
Added chemicals for treatment   Name
Dosage rate of added chemicals for treatment during sampling   l/m³
Average washwater flow rate to EGCS during sampling period   m³/h
Average dilution water flow rate during sampling period, if given or relevant   m³/h
3.2.3 Combustion unit(s) operation
Approx. total combustion unit(s) load to EGCS   MW
Total fuel consumption   t/h
Fuel sulphur content (according BDN)    
Fuel viscosity if available    
Additional notes:

3.2.4 Online monitoring readings during sampling, for each sampling point
Monitoring unit pH PAHphe μg/L or ppb Turbidity FNU or NTU
Inlet (if available), average during sampling period      
Discharge point, average during sampling period (outlet)   NA NA
Before dilution, average during sampling period NA    
3.2.5 Results to be reported by the laboratory
Question Answer Comments
Satisfactory temperature at arrival Yes/No  
Sampling bottles and transportation container prepared by laboratory Yes/No  
Methods within the scope of ISO 17025 accreditation of the laboratory Yes/No  
Date and time samples arrived at laboratory    
Date and time of analyses    
Parameter Bottle ID Preparation method Analytical method Result + unit
Polycyclic Aromatic Hydrocarbons (PAH):

16 EPA PAHs:

Acenaphthene

Acenaphthylene

Anthracene

Benzo-a-anthracene

Benzo-a-pyrene

Benzo-b-fluoranthene

Benzo-g,h,i-perylene

Benzo-k-fluoranthene

Chrysene

Dibenzo-a,h-anthracene

Fluoranthene

Fluorene

Indeno-1,2,3-c,d-pyrene

Naphthalene

Phenanthrene

Pyrene

       
Hydrocarbon Oil Index GC-FID analysis        
Nitrate and nitrite (NO3-/NO2-)        
Total Metals:
  • - Cd
  • - Cu
  • - Ni
  • - Pb
  • - Zn
  • - As
  • - Cr
  • - V
  • - Se
       
Dissolved Metals:
  • - Cd
  • - Cu
  • - Ni
  • - Pb
  • - Zn
  • - As
  • - Cr
  • - V
  • - Se
       

3.2.6 List of bottle IDs or chain of custody (COC)

Sampling point Parameter PAH Parameter Metals Parameter X
Inlet Bottle #1 + time stamp Bottle #2 + time stamp Etc.
discharge point Bottle # + time stamp Bottle # + time stamp Etc.
Etc. Etc. Etc. Etc.
       
       

Copyright 2022 Clasifications Register Group Limited, International Maritime Organization, International Labour Organization or Maritime and Coastguard Agency. All rights reserved. Clasifications Register Group Limited, its affiliates and subsidiaries and their respective officers, employees or agents are, individually and collectively, referred to in this clause as 'Clasifications Register'. Clasifications Register assumes no responsibility and shall not be liable to any person for any loss, damage or expense caused by reliance on the information or advice in this document or howsoever provided, unless that person has signed a contract with the relevant Clasifications Register entity for the provision of this information or advice and in that case any responsibility or liability is exclusively on the terms and conditions set out in that contract.