BS ISO 13073-1:2012
Current
The latest, up-to-date edition.
Ships and marine technology. Risk assessment on anti-fouling systems on ships Marine environmental risk assessment method of biocidally active substances used for anti-fouling systems on ships
Hardcopy , PDF
English
30-11-2012
Foreword
Introduction
1 Scope
2 Terms and definitions
3 Application
4 Structure and procedure of environmental
risk assessment
5 Exposure assessment
6 Hazard assessment
7 Risk characterization
8 Risk assessment report
Annex A (informative) - Systems for estimation of
release rates of biocidally active substances
from antifouling paints
Annex B (normative) - Details of risk characterization
process of an environmental risk assessment
for organic biocidally active substances used
in anti-fouling systems on ships
Annex C (normative) - Issues to be considered for risk
characterization for inorganic biocidally active
substances used in anti-fouling systems on ships
Annex D (informative) - Examples of guidance for
determining data quality
Annex E (informative) - Examples of testing methods
Annex F (informative) - Setting of assessment factors (AF)
Annex G (normative) - Minimum information required for
the risk assessment report
Annex H (informative) - Previously validated models for
predicting environmental concentrations
Bibliography
Describes a risk assessment method that protects the marine environment from the potential negative impacts of biocidally active substances that are intentionally used in the anti-fouling system applied to a ship during its service life.
Committee |
SME/32
|
DevelopmentNote |
Supersedes 11/30213205 DC. (11/2012)
|
DocumentType |
Standard
|
Pages |
62
|
PublisherName |
British Standards Institution
|
Status |
Current
|
Supersedes |
This part of ISO13073 specifies a risk assessment method that protects the marine environment from the potential negative impacts of biocidally active substances that are intentionally used in the anti-fouling system applied to a ship during its service life. This method can also be modified for use in freshwater environments.
This part of ISO13073 does not provide a specific test method for evaluating the hazard and toxicity or usage restrictions of certain substances. This also does not provide an efficacy-evaluation method for an anti-fouling system using a specific substance.
The following are not covered by this part of ISO13073:
-
the risk assessment of biocidally active substances in anti-fouling systems during their application and removal during vessel maintenance and repair, new building or ship recycling;
-
use of anti-fouling systems intended to control harmful aquatic organisms and pathogens in ships’ ballast water and sediments according to the International Convention for The Control and Management of Ships’ Ballast Water and Sediments, 2004;
-
anti-fouling systems applied to fishing gear, buoys and floats used for the purpose of fishing, and to equipment used in fisheries and aquaculture (nets/cages etc);
-
test patches of anti-fouling systems on ships for the purpose of research and development of anti-fouling products;
-
the assessment of risk of biocidally active substances in cases of accidental releases, such as spillage during ocean transport or releases into the sea from rivers and/or coastal facilities.
Standards | Relationship |
ISO 13073-1:2012 | Identical |
ISO/IEC 17025:2005 | General requirements for the competence of testing and calibration laboratories |
ISO 15181-3:2007 | Paints and varnishes — Determination of release rate of biocides from antifouling paints — Part 3: Calculation of the zinc ethylene-bis(dithiocarbamate) (zineb) release rate by determination of the concentration of ethylenethiourea in the extract |
ISO 10890:2010 | Paints and varnishes — Modelling of biocide release rate from antifouling paints by mass-balance calculation |
ISO 15181-2:2007 | Paints and varnishes — Determination of release rate of biocides from antifouling paints — Part 2: Determination of copper-ion concentration in the extract and calculation of the release rate |
ISO 14592-2:2002 | Water quality — Evaluation of the aerobic biodegradability of organic compounds at low concentrations — Part 2: Continuous flow river model with attached biomass |
ISO 15181-1:2007 | Paints and varnishes — Determination of release rate of biocides from antifouling paints — Part 1: General method for extraction of biocides |
ISO 15181-4:2008 | Paints and varnishes Determination of release rate of biocides from antifouling paints Part 4: Determination of pyridine-triphenylborane (PTPB) concentration in the extract and calculation of the release rate |
ISO 15181-6:2012 | Paints and varnishes — Determination of release rate of biocides from antifouling paints — Part 6: Determination of tralopyril release rate by quantitation of its degradation product in the extract |
ISO 11348-3:2007 | Water quality Determination of the inhibitory effect of water samples on the light emission of Vibrio fischeri (Luminescent bacteria test) Part 3: Method using freeze-dried bacteria |
ISO 10253:2016 | Water quality — Marine algal growth inhibition test with Skeletonema sp. and Phaeodactylum tricornutum |
ISO 14669:1999 | Water quality — Determination of acute lethal toxicity to marine copepods (Copepoda, Crustacea) |
ISO 14592-1:2002 | Water quality — Evaluation of the aerobic biodegradability of organic compounds at low concentrations — Part 1: Shake-flask batch test with surface water or surface water/sediment suspensions |
ISO 15181-5:2008 | Paints and varnishes Determination of release rate of biocides from antifouling paints Part 5: Calculation of the tolylfluanid and dichlofluanid release rate by determination of the concentration of dimethyltolylsulfamide (DMST) and dimethylphenylsulfamide (DMSA) in the extract |
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