Einde inhoudsopgave
1996 Protocol to the Convention on the Prevention of Marine Pollution by Dumping of Wastes and Other matter, 1972
Annex 2 Assessment of wastes or other matter that may be considered for dumping
Geldend
Geldend vanaf 15-01-2023
- Bronpublicatie:
07-10-2022, Trb. 2022, 143 (uitgifte: 29-12-2022, regelingnummer: LP.6(17))
- Inwerkingtreding
15-01-2023
- Bronpublicatie inwerkingtreding:
07-10-2022, Trb. 2022, 143 (uitgifte: 29-12-2022, regelingnummer: LP.6(17))
- Vakgebied(en)
Milieurecht / Algemeen
Internationaal publiekrecht / Bijzondere onderwerpen
General
1
The acceptance of dumping under certain circumstances shall not remove the obligations under this Annex to make further attempts to reduce the necessity for dumping.
Waste prevention audit
2
The initial stages in assessing alternatives to dumping should, as appropriate, include an evaluation of:
- .1.
types, amounts and relative hazard of wastes generated;
- .2.
details of the production process and the sources of wastes within that process; and
- .3.
feasibility of the following waste reduction/prevention techniques:
- .1.
product reformulation;
- .2.
clean production technologies;
- .3.
process modification;
- .4.
input substitution; and
- .5.
on-site, closed-loop recycling.
3
In general terms, if the required audit reveals that opportunities exist for waste prevention at source, an applicant is expected to formulate and implement a waste prevention strategy, in collaboration with relevant local and national agencies, which includes specific waste reduction targets and provision for further waste prevention audits to ensure that these targets are being met. Permit issuance or renewal decisions shall assure compliance with any resulting waste reduction and prevention requirements.
4
For dredged material, the goal of waste management should be to identify and control the sources of contamination. This should be achieved through implementation of waste prevention strategies and requires collaboration between the relevant local and national agencies involved with the control of point and non-point sources of pollution. Until this objective is met, the problems of contaminated dredged material may be addressed by using disposal management techniques at sea or on land.
Consideration of waste management options
5
Applications to dump wastes or other matter shall demonstrate that appropriate consideration has been given to the following hierarchy of waste management options, which implies an order of increasing environmental impact:
- .1.
re-use;
- .2.
off-site recycling;
- .3.
destruction of hazardous constituents;
- .4.
treatment to reduce or remove the hazardous constituents; and
- .5.
disposal on land, into air and in water.
6
A permit to dump wastes or other matter shall be refused if the permitting authority determines that appropriate opportunities exist to re-use, recycle or treat the waste without undue risks to human health or the environment or disproportionate costs. The practical availability of other means of disposal should be considered in the light of a comparative risk assessment involving both dumping and the alternatives.
Chemical, physical and biological properties
7
A detailed description and characterization of the waste is an essential precondition for the consideration of alternatives and the basis for a decision as to whether a waste may be dumped. If a waste is so poorly characterized that proper assessment cannot be made of its potential impacts on human health and the environment, that waste shall not be dumped.
8
Characterization of the wastes and their constituents shall take into account:
- .1.
origin, total amount, form and average composition;
- .2.
properties: physical, chemical, biochemical and biological;
- .3.
toxicity;
- .4.
persistence: physical, chemical and biological; and
- .5.
accumulation and biotransformation in biological materials or sediments.
Action list
9
Each Contracting Party shall develop a national Action List to provide a mechanism for screening candidate wastes and their constituents on the basis of their potential effects on human health and the marine environment. In selecting substances for consideration in an Action List, priority shall be given to toxic, persistent and bioaccumulative substances from anthropogenic sources (e.g., cadmium, mercury, organohalogens, petroleum hydrocarbons, and, whenever relevant, arsenic, lead, copper, zinc, beryllium, chromium, nickel and vanadium, organosilicon compounds, cyanides, fluorides and pesticides or their by-products other than organohalogens). An Action List can also be used as a trigger mechanism for further waste prevention considerations.
10
An Action List shall specify an upper level and may also specify a lower level. The upper level should be set so as to avoid acute or chronic effects on human health or on sensitive marine organisms representative of the marine ecosystem. Application of an Action List will result in three possible categories of waste:
- .1.
wastes which contain specified substances, or which cause biological responses, exceeding the relevant upper level shall not be dumped, unless made acceptable for dumping through the use of management techniques or processes;
- .2.
wastes which contain specified substances, or which cause biological responses, below the relevant lower levels should be considered to be of little environmental concern in relation to dumping; and
- .3.
wastes which contain specified substances, or which cause biological responses, below the upper level but above the lower level require more detailed assessment before their suitability for dumping can be determined.
Dump-site selection
11
Information required to select a dump-site shall include:
- .1.
physical, chemical and biological characteristics of the water-column and the seabed;
- .2.
location of amenities, values and other uses of the sea in the area under consideration;
- .3.
assessment of the constituent fluxes associated with dumping in relation to existing fluxes of substances in the marine environment; and
- .4.
economic and operational feasibility.
Assessment of potential effects
12
Assessment of potential effects should lead to a concise statement of the expected consequences of the sea or land disposal options, i.e., the ‘Impact Hypothesis.’ It provides a basis for deciding whether to approve or reject the proposed disposal option and for defining environmental monitoring requirements.
13
The assessment for dumping should integrate information on waste characteristics, conditions at the proposed dump-site(s), fluxes, and proposed disposal techniques and specify the potential effects on human health, living resources, amenities and other legitimate uses of the sea. It should define the nature, temporal and spatial scales and duration of expected impacts based on reasonably conservative assumptions.
14
An analysis of each disposal option should be considered in the light of a comparative assessment of the following concerns: human health risks, environmental costs, hazards, (including accidents), economics and exclusion of future uses. If the assessment reveals that adequate information is not available to determine the likely effects of the proposed disposal option then this option should not be considered further. In addition, if the interpretation of the comparative assessment shows the dumping option to be less preferable, a permit for dumping should not be given.
15
Each assessment should conclude with a statement supporting a decision to issue or refuse a permit for dumping.
Monitoring
16
Monitoring is used to verify that permit conditions are met — compliance monitoring — and that the assumptions made during the permit review and site selection process were correct and sufficient to protect the environment and human health — field monitoring. It is essential that such monitoring programmes have clearly defined objectives.
Permit and permit conditions
17
A decision to issue a permit should only be made if all impact evaluations are completed and the monitoring requirements are determined. The provisions of the permit shall ensure, as far as practicable, that environmental disturbance and detriment are minimized and the benefits maximized. Any permit issued shall contain data and information specifying:
- .1.
the types and sources of materials to be dumped;
- .2.
the location of the dump-site(s);
- .3.
the method of dumping; and
- .4.
monitoring and reporting requirements.
18
Permits should be reviewed at regular intervals, taking into account the results of monitoring and the objectives of monitoring programmes. Review of monitoring results will indicate whether field programmes need to be continued, revised or terminated and will contribute to informed decisions regarding the continuance, modification or revocation of permits. This provides an important feedback mechanism for the protection of human health and the marine environment.