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Great Lakes Water Quality Agreement 1978
ANNEX1 -
SPECIFIC OBJECTIVES
These Objectives are based on available information on
cause/effect relationships between pollutants and receptors to
protect the recognized most sensitive use in all waters. These
Objectives may be amended, or new Objectives may be added, by mutual
consent of the Parties.
- CHEMICAL
- Persistent Toxic Substances
- Organic
- Pesticides
Aldrin/Dieldrin
The sum of the concentration of aldrin and dieldrin in water
should not exceed 0.001 micrograms per litre. The sum of
concentrations of aldrin and dieldrin in the edible portion
of fish should not exceed 0.3 micrograms per gram (wet
weight basis) for the protection of human consumers of fish.
Chlordane
The concentration of chlordane in water should not exceed
0.06 micrograms per litre for the protection of aquatic
life.
DDT and Metabolites
The sum of the concentrations of DDT and its metabolites in
water should not exceed 0.003 micrograms per litre. The sum
of the concentrations of DDT and its metabolites in whole
fish should not exceed 1.0 microgram per gram (wet weight
basis) for the protection of fish-consuming aquatic birds.
Endrin
The concentration of endrin in water should not exceed 0.002
micrograms per litre. The concentration of endrin in the
edible portion of fish should not exceed 0.3 micrograms per
gram (wet weight basis) for the protection of human
consumers of fish.
Heptachlor/Heptachlor Epoxide
The sum of the concentrations of heptachlor and heptachlor
epoxide in water should not exceed 0.001 micrograms per
litre. The sum of concentrations of heptachlor and
heptachlor epoxide in edible portions of fish should not
exceed 0.3 micrograms per gram (wet weight basis) for the
protection of human consumers of fish.
Lindane
The concentration of lindane in water should not exceed 0.01
micrograms per litre for the protection of aquatic life. The
concentration of lindane in edible portions of fish should
not exceed 0.3 micrograms per gram (wet weight basis) for
the protection of human consumers of fish.
Methoxychlor
The concentration of methoxychlor in water should not exceed
0.04 micrograms per litre for the protection of aquatic
life.
Mirex
For the protection of aquatic organisms and fish-consuming
birds and animals, mirex and its degradation products should
be substantially absent from water and aquatic organisms.
Substantially absent here means less than detection levels
as determined by the best scientific methodology available.
Toxaphene
The concentration of toxaphene in water should not exceed
0.008 micrograms per litre for the protection of aquatic life.
- Other Compounds
Phthalic Acid Esters
The concentration of dibutyl phthalate and di (2-ethylhexyl)
phthalate in water should not exceed 4.0 micrograms per
litre and 0.6 micrograms per litre, respectively, for the
protection of aquatic life. Other phthalic acid esters
should not exceed 0.2 micrograms per litre in waters for the
protection of aquatic life.
Polychlorinated Biphenyls (PCBs)
The concentration of total polychlorinated biphenyls in
fish tissues (whole fish, calculated on a wet weight basis),
should not exceed 0.1 micrograms per gram for the protection
of birds and animals which consume fish.
Unspecific Organic Compounds
For other organic contaminants, for which Specific
Objectives have not been defined, but which can be
demonstrated to be persistent and are likely to be toxic,
the concentrations of such compounds in water or aquatic
organisms should be substantially absent, i.e., less than
detection levels as determined by the best scientific
methodology available.
- Inorganic
- Metals
Arsenic
The concentrations of total arsenic in an unfiltered water
sample should not exceed 50 micrograms per litre to protect
raw waters for public water supplies.
Cadmium
The concentration of total cadmium in an unfiltered water
sample should not exceed 0.2 micrograms per litre to protect
aquatic life.
Chromium
The concentration of total chromium in an unfiltered water
sample should not exceed 50 micrograms per litre to protect
raw waters of public water supplies.
Copper
The concentration of total copper in an unfiltered water
sample should not exceed 5 micrograms per litre to protect
aquatic life.
Iron
The concentration of total iron in an unfiltered water
sample should not exceed 300 micrograms per litre to protect
aquatic life.
Lead
The concentration of total lead in an unfiltered water
sample should not exceed 10 micrograms per litre in Lake
Superior, 20 micrograms per litre in Lake Huron and 25
micrograms per litre in all remaining Great Lakes to protect
aquatic life.
Mercury
The concentration of total mercury in a filtered water
sample should not exceed 0.2 micrograms per litre nor should
the concentration of total mercury in whole fish exceed 0.5
micrograms per gram (wet weight basis) to protect aquatic
life and fish-consuming birds.
Nickel
The concentration of total nickel in an unfiltered water
sample should not exceed 25 micrograms per litre to protect
aquatic life.
Selenium
The concentration of total selenium in an unfiltered water
sample should not exceed 10 micrograms per litre to protect
the raw water for public water supplies.
Zinc
The concentration of total zinc in an unfiltered water
sample should not exceed 30 micrograms per litre to protect
aquatic
life.
- Other Inorganic Substances
Fluoride
The concentration of total fluoride in an unfiltered water
sample should not exceed 1200 micrograms per litre to
protect raw water for public water supplies.
Total Dissolved Solids
In Lake Erie, Lake Ontario and the International Section
of the St. Lawrence River, the level of total dissolved
solids should not exceed 200 milligrams per litre. In the
St. Clair River, Lake St. Clair, the Detroit River and the
Niagara River, the level should be consistent with
maintaining the levels of total dissolved solids in Lake
Erie and Lake Ontario not to exceed 200 milligrams per litre.
In the remaining boundary waters, pending further study, the
level of total dissolved solids should not exceed present
levels.
- Non-Persistent Toxic Substances
- Organic Substances
- Pesticides
Diazinon
The concentration of diazinon in an unfiltered water sample
should not exceed 0.08 micrograms per litre for the
protection of aquatic life.
Guthion
The concentration of guthion in an unfiltered water sample
should not exceed 0.005 micrograms per litre for the
protection of aquatic life.
Parathion
The concentration of parathion in an unfiltered water sample
should not exceed 0.008 micrograms per litre for the
protection of aquatic life.
Other Pesticides
The concentration of unspecified, non-persistent
pesticides should not exceed 0.05 of the median lethal
concentration on a 96-hour test for any sensitive local
species.
- Other substances
Unspecified Non-Persistent Toxic Substances and Complex
Effluents
Unspecified non-persistent toxic substances and complex
effluents of municipal, industrial or other origin should
not be present in concentrations which exceed 0.05 of the
median lethal concentration in a 96-hour test for any
sensitive local species to protect aquatic life.
Oil and Petrochemicals
Oil and petrochemicals should not be present in
concentrations that:
- can be detected as visible film, sheen or
discoloration on the surface;
- can be detected by odour;
- can cause tainting of edible aquatic organisms; and
- can form deposits on shorelines and bottom sediments
that are detectable by sight or odour, or are deleterious
to resident aquatic organisms.
- Inorganic Substances
Ammonia
The concentration of un-ionized ammonia (NH3) should not
exceed 20 micrograms per litre for the protection of aquatic
life. Concentrations of total ammonia should not exceed 500
micrograms per litre for the protection of public water
supplies.
Hydrogen Sulfide
The concentration of undissociated hydrogen sulfide should
not exceed 2.0 micrograms per litre to protect aquatic life.
- Other Substances
- Dissolved oxygen
In the connecting channels and in the upper waters of the
Lakes, the dissolved oxygen level should not be less than 6.0
milligrams per litre at any time; in hypolimnetic waters, it
should be not less than necessary for the support of fishlife,
particularly cold water species.
- pH
Values of pH should not be outside the range of 6.5 to 9.0,
nor should discharge change the pH at the boundary of a
limited use zone more than 0.5 units from that of the ambient
waters.
- Nutrients
Phosphorus
The concentration should be limited to the extend necessary to
prevent nuisance growths of algae, weeds and slimes that are
or may become injurious to any beneficial water use. (Specific
phosphorus control requirements are set out in Annex 3.)
- Tainting Substances
- Raw public water supply sources should be essentially
free from objectionable taste and odour for aesthetic
reasons.
- Levels of phenolic compounds should not exceed 1.0
microgram per litre in public water supplies to protect
against taste and odour in domestic water.
- Substances entering the water as the result of human
activity that cause tainting of edible aquatic organisms
should not be present in concentrations which will lower the
acceptability of these organisms as determined by
organoleptic tests.
- PHYSICAL
- Asbestos
Asbestos should be kept at the lowest practical level and in any
event should be controlled to the extent necessary to prevent
harmful
effects on human health.
- Temperature
There should be no change in temperature that would adversely
affect any local or general use of the waters.
- Settleable and Suspended Solids, and Light Transmission
For the protection of aquatic life, waters should be free from
substances attributable to municipal, industrial or other
discharges
resulting from human activity that will settle to form
putrescent or otherwise objectionable sludge deposits or that
will alter the value of
Secchi disc depth by more than 10 per cent.
- MICROBIOLOGICAL
Waters used for body contact recreation activities should be
substantially free from bacteria, fungi, or viruses that may
produce enteric
disorders or eye, ear, nose, throat and skin infections or other
human diseases and infections.
- RADIOLOGICAL
The level of radioactivity in waters outside of any defined
source control area should not result in a TED50 (total
equivalent dose integrated
over 50 years as calculated in accordance with the methodology
established by the International Commission on Radiological
Protection)
greater than 1 millirem to the whole body from a daily ingestion
of 2.2 litres of lake water for one year. For dose commitments
between 1
and 5 millirem at the periphery of the source control area,
source investigation and corrective action are recommended if
releases are not as
low as reasonably achievable. For dose commitments greater than
5 millirem, the responsible regulatory authorities shall
determine
appropriate corrective action.
SPECIFIC
OBJECTIVES - SUPPLEMENT TO ANNEX 1
- General Principles
- Interim Objectives for Persistent Toxic Substances
Consistent with the policy stated in paragraph (a) of Article II
and Paragraph 2 of Annex 12 that the discharge of any or all
persistent toxic substances be virtually eliminated, the
Specific Objectives set out in Annex 1 for such substances are
adopted as interim objectives.
- Detection Levels
As used in this Annex, "absent" means that the substances are
not detectable when analyzed using the best available
technology, which may include biological indicators. Detection
levels will be subject to change as technology improves and new
levels are adopted.
- Specific Objectives Review Process
- The Parties, in consultation with State and Provincial
Governments, shall consult on or before July 1, 1988, and at
least once every two years thereafter for the purpose of
considering the adoption of proposals by the Parties, State and
Provincial Governments or recommendations of the Commission to:
- establish or modify Specific Objectives under Annex 1; and
- establish action levels under Annex 12.
The Parties, in cooperation with State and Provincial
Governments, shall ensure that the public is consulted in the
development and adoption of the Specific Objectives.
- In proposing a substance for a new Specific Objective, the
Parties, State and Provincial Governments or the Commission
shall be guided by, but not limited to, the lists prepared by
the Parties under paragraph (c), below, identifying substances
that are present or potentially present within the water,
sediment or aquatic biota of the Great Lakes System and are
believed, singly or in synergistic or additive combination with
another substance, to have acute or chronic toxic effects on
aquatic, animal or human life.
- The Parties, on or before December 31, 1988, shall compile
and maintain three lists of substances as follows:
- List No. 1 shall consist of all substances (1) believed to
be present within the water, sediment or aquatic biota of the
Great Lakes System and (2) believed, singly or in synergistic
or additive combination with another substance, to have acute
or chronic toxic effects on aquatic, animal or human life.
- List No. 2 shall consist of all substances (1) believed to
be present within the water, sediment or aquatic biota of the
Great Lakes System and (2) believed, singly, or in synergistic
or additive combination with another substance to have the
potential to cause acute or chronic toxic effects on aquatic,
animal or human life.
- List No. 3 shall consist of all substances (1) believed to
have the potential of being discharged into the Great Lakes
System and (2) believed, singly or in synergistic or additive
combination with another substance, to have acute or chronic
toxic effects on aquatic, animal or human life.
In compiling such lists, the Parties shall employ all data
available, including that resulting from activities undertaken
pursuant to Annex 12.
- Determinations regarding whether a substance, singly or in
synergistic or additive combinations with another substance, has
actual or potential acute or chronic effects or whether a
substance has the potential of being discharged into the Great
Lakes System according to paragraph (c) above, shall be made
using standard methods agreed to by the Parties in consultation
with State and Provincial Governments by April 1988.
- Lake Ecosystem Objectives.
Consistent with the purpose of this
Agreement to maintain the chemical, physical and biological
integrity of the waters of the Great Lakes Basin Ecosystem, the
Parties, in consultation with State and Provincial Governments,
agree to develop the following ecosystem objectives for the
boundary waters of the Great Lakes System, or portions thereof,
and for Lake Michigan:
- Lake Superior
The Lake should be maintained as a balanced and stable
oligotrophic ecosystem with lake trout as the top aquatic
predator of a cold-water community and the Pontoporeia hoyi as a
key organism in a food chain; and
- Other Great Lakes
Ecosystem Objectives shall be developed as the state of
knowledge permits for the rest of the boundary of the Great
Lakes System, or portions thereof, and for Lake Michigan.
ANNEX2 - REMEDIAL ACTION PLANS AND LAKEWIDE
MANAGEMENT PLANS
-
Definitions. As used in this Annex:
- "Area of Concern" means a geographic area that fails to meet
the General or Specific Objectives of the Agreement where such
failure has caused or is likely to cause impairment of
beneficial use or of the area's ability to support aquatic life.
- "Critical Pollutants" means substances that persist at
levels that, singly or in synergistic or additive combination,
are causing, or are likely to cause, impairment of beneficial
uses despite past application of regulatory controls due to
their:
- presence in open lake waters;
- ability to cause or contribute to a failure to meet
Agreement objectives through their recognized threat to human
health and aquatic life; or
- ability to bioaccumulate.
- "Impairment of beneficial use(s)" means a change in the
chemical, physical or biological integrity of the Great Lakes
System sufficient to cause any of the following:
- restrictions on fish and wildlife consumption;
- tainting of fish and wildlife flavour;
- degradation of fish wildlife populations;
- fish tumors or other deformities;
- bird or animal deformities or reproduction problems;
- degradation of benthos;
- restrictions on dredging activities;
- eutrophication or undesirable algae;
- restrictions on drinking water consumption, or taste and
odour problems
- beach closings;
- degradation of aesthetics;
- added costs to agriculture or industry;
- degradation of phytoplankton and zooplankton populations;
and
- loss of fish and wildlife habitat.
- "Point Source Impact Zone" is defined as an area of water
contiguous to a point source where the water quality does not
comply with the General and Specific Objectives of this
Agreement.
- General Principles
- Remedial Action Plans and Lakewide Management Plans shall
embody a systematic and comprehensive ecosystem approach to
restoring and protecting beneficial uses in Areas of Concern or
in open lake waters.
- Such Plans shall provide a continuing historical record of
the assessment of Areas of Concern or Critical Pollutants,
proposed remedial actions and their method of implementation, as
well as changes in environmental conditions that result from
such actions, including significant milestones in restoring
beneficial uses to Areas of Concern or open lake waters. They
are to serve as an important step toward virtual elimination of
persistent toxic substances and toward restoring and maintaining
the chemical, physical and biological integrity of the Great
Lakes Basin Ecosystem.
- The Parties, State and Provincial Governments, and the
Commission have identified Areas of Concern and the development
of the of Remedial Action Plans for them has begun. Furthermore,
the Parties and State and Provincial Governments have begun
developing lakewide strategies for Lakes Ontario and Michigan.
By incorporating an Annex for Remedial Action Plans and Lakewide
Management Plans in this Agreement, the Parties intend to
endorse and build upon these existing efforts.
- Point source impact zones exist in the vicinity of some
point source discharges. Pending the achievement of the virtual
elimination of persistent toxic substances, the size of such
zones shall be reduced to the maximum extent possible by the
best available technology so as to limit the effects of toxic
substances in the vicinity of these discharges. These zones
shall not be acutely toxic to aquatic species, nor shall their
recognition be considered a substitute for adequate treatment or
control of discharges at their sources.
- The Parties, in cooperation with State and Provincial
Governments, shall ensure that the public is consulted in all
actions undertaken pursuant to this Annex.
- Designation of Areas of Concern. The Parties, in
cooperation with State and Provincial Governments and the
Commission, shall designate geographic Areas of Concern. The
Commission, in its evaluation role, shall review progress in
addressing Areas of Concern, and recommend additional Areas of
Concern for designation by each Party.
- Remedial Action Plans for Areas of Concern
- The Parties shall cooperate with State and Provincial
Governments to ensure that Remedial Action Plans are developed
and implemented for Areas of Concern. Each plan shall include:
- a definition and detailed description of the environmental
problem in the Areas of Concern, including a definition of the
beneficial uses that are impaired, the degree of impairment
and the geographic extent of such impairment;
- a definition of the causes of the use impairment,
including a description of all known sources of pollutants
involved and an evaluation of other possible sources;
- an evaluation of remedial measures in place;
- an evaluation of alternative additional measures to
restore beneficial uses;
- a selection of additional remedial measures to restore
beneficial uses and a schedule for their implementation;
- an identification of the persons or agencies responsible
for implementation of remedial measures;
- a process for evaluating remedial measure implementation
and effectiveness; and
- a description of surveillance and monitoring processes to
track the effectiveness of remedial measures and the eventual
confirmation of the restoration of uses.
- The Parties, in cooperation with State and Provincial
Governments, shall ensure that affected State and Provincial
Governments not now covered by this Agreement will be involved
in the development of such plans and consulted on their
implementation.
- The Parties shall cooperate with State and Provincial
Governments to classify Areas of Concern by their stage of
restoration progressing from the definition of the problems and
causes, through the selection of remedial measures, to the
implementation of remedial programs, the monitoring of recovery,
and, when identified beneficial uses are no longer impaired and
the area restored, the removal of its designation as an Area of
Concern.
- The Remedial Action Plans shall be submitted to the
Commission for review and comment at three stages:
- when a definition of the problem has been completed under
sub-paragraphs 4(a)(i) and (ii);
- when remedial and regulatory measures are selected under
sub-paragraphs 4(a)(iii), (iv), (v) and (vi); and
- when monitoring indicates that identified beneficial uses
have been restored under sub-paragraphs 4(a)(vii) and (viii).
- Designation of Critical Pollutants for the Development of
Lakewide Management Plans. The Parties, in cooperation with
State and Provincial Governments and the Commission, shall
designate Critical Pollutants for the boundary waters of the Great
Lakes System or for a portion thereof. The Commission, in its
evaluative role, shall review progress in addressing Critical
Pollutants and recommend additional Critical Pollutants for
designation by the Parties. Substances on List No. 1 under Annex 1
Supplement shall be considered for designation as Critical
Pollutants.
- Lakewide Management Plans for Critical Pollutants
- The Parties, in consultation with State and Provincial
Governments, shall develop and implement Lakewide
Management Plans for open lake waters, except for Lake Michigan
where the Government of the United States of America shall have
that responsibility. Such Plans shall be designed to reduce
loadings of Critical Pollutants in order to restore beneficial
uses, Lakewide Management Plans shall not allow increases in
pollutant loadings in areas where Specific Objectives are not
exceeded.
Such Plans shall include:
- a definition of the threat to human health or aquatic life
posed by Critical Pollutants, singly or in synergistic or
additive combinations with another substance, including their
contribution to the impairment of beneficial uses;
- an evaluation of information available on concentration,
sources, and pathways of the Critical Pollutants in the Great
Lakes System, including all information on loadings of the
Critical Pollutants from all sources, and an estimation of
total loadings of the Critical Pollutants by modelling or
other identified methods;
- steps to be taken pursuant to Article VI of this Agreement
to develop the information necessary to determine the schedule
of load reduction of Critical Pollutants that would result in
meeting Agreement Objectives, including steps to develop the
necessary standard approached and agreed procedures;
- a determination of load reduction of Critical Pollutants
necessary to meet Agreement Objectives;
- an evaluation of remedial measures presently in place, and
alternative additional measures that could be applied to
decrease loadings of Critical Pollutants;
- identification of the additional remedial measures that
are need to achieve the reduction of loadings and to eliminate
the contribution to impairment of beneficial uses from
Critical Pollutants, including an implementation schedule;
- identification of the persons or agencies responsible for
implementation of the remedial measures in question;
- a process for evaluating remedial measure implementation
and effectiveness;
- a description of surveillance and monitoring to track the
effectiveness of the remedial measures and the eventual
elimination of the contribution to impairments of beneficial
uses from the Critical Pollutants;
- a process for recognizing the absence of a Critical
Pollutant in open lake waters.
- The Parties shall classify efforts to reduce Critical
Pollutants by their stages of elimination progressing from the
definition of the problem, through the selection of remedial
measures, to the implementation of remedial programs, the
monitoring of recovery, and the removal of designation as a
Critical Pollutant when it is no longer likely to cause, singly
or in synergistic or additive combination with another
substance, impairment of identified beneficial uses.
- Lakewide Management Plans shall be submitted to the
Commission for review and comment at four stages;
- When a definition of the problem has been completed under
sub-paragraphs 6(a)(i), (ii) and (iii);
- When the schedule of load reductions is determined under
paragraph 6(a)(i), (ii) and (iii);
- When remedial measures are selected under sub-paragraph 6(a)(v), (vi) and (vii); and
- When monitoring indicates that the contribution of the
Critical Pollutants to impairment of identified beneficial
uses has been eliminated under sub-paragraphs 6(a)(viii) and
(ix)
- Reporting Progress
- Point Source Impact Zones that are associated with direct
significant discharges of industrial and municipal wastes shall
be identified delineated and reported to the Commission
beginning September 30, 1989. They shall be reviewed biennially
and their limits revised to achieve the maximum possible
reduction in size and effect in accordance with improvements in
waste treatment technology and consistent with the policy of
virtual elimination of persistent toxic substances.
- The Parties shall report, by December 31, 1988, and
biennially thereafter, to the Commission on the progress in
developing and implementing the Remedial Action Plans and
Lakewide Management Plans and in restoring beneficial uses.
Information from these reports shall be included in the
Commission's biennial report under paragraph 3 of Article VII.
ANNEX 3 - CONTROL OF PHOSPHORUS
- The purpose of the following programs is to minimize
eutrophication problems and to prevent degradation with regard to
phosphorus in the boundary waters of the Great Lakes System. The
Goals of phosphorus control are:
- Restoration of year-round aerobic conditions in the bottom
waters of the Central Basin of Lake Erie;
- Substantial reduction in the present levels of algal biomass
to a level below that of a nuisance condition in Lake Erie;
- Reduction in present levels of algal biomass to below that
of a nuisance condition in Lake Ontario unleading the
International Section of the St. Lawrence River;
- Maintenance of the oligotrophic state and relative algal
biomass of Lakes Superior and Huron;
- Substantial elimination of algal nuisance growths in Lake
Michigan to restore it to oligotrophic state; and
- The elimination of algal nuisance in bays and in other areas
wherever they occur.
- The following programs shall be developed and implemented to
reduce input of phosphorus to the Great Lakes:
- Construction and operation of municipal waste treatment
facilities in all plants discharging more than one million
gallons per day to achieve, where necessary to meet the loading
allocation be developed pursuant to paragraph 3 below, or to
meet local conditions, whichever are more stringent, effluent
concentration of 1.0 milligram per litre total phosphorus
maximum for plants in the basins of Lakes Superior, Michigan,
and Huron, and of 0.5 milligram per litre total phosphorus
maximum for plants in the basins of Lakes Ontario and Erie.
- Regulation of phosphorus introduction from industrial
discharges to the maximum practicable extent.
- Reduction to the maximum extent practicable of phosphorus
introduced from diffuse sources into Lakes Superior, Michigan,
and Huron; and the reduction by 30 per cent of phosphorus
introduced from diffuse sources into Lakes Ontario and Erie,
where necessary to meet the loading allocations to be developed
pursuant to paragraph 3 below, or to meet local conditions,
whichever is more stringent.
- Reduction of phosphorus in household detergents to 0.5 per
cent by weight where necessary to meet the loading allocation to
be developed pursuant to paragraph 3 below, or to meet local
conditions, whichever are more stringent.
- Maintenance of a viable research program to seek maximum
efficiency and effectiveness in the control of phosphorus
introductions into the Great Lakes.
- The following table establishes phosphorus loads for the base
year (1976) and future phosphorus loads. The Parties, in
cooperation with the State and Provincial Governments, shall
within eighteen months after the date of entry into force of this
Agreement confirm the future phosphorus loads, and based on these
establish load allocations and compliance schedules, taking into
account the recommendations of the International Joint Commission
arising from the Pollution from Land Use Activities Reference.
Until such loading allocations and compliance schedules are
established, the Parties agree to maintain the programs and other
measures specified in Annex 2 of the Great Lakes Water Quality
Agreement of 1972.
| Basin |
1976
Phosphorus
Load in Metric Tonnes Per Year |
Future
Phosphorus Load
in Metric Tonnes
Per Year |
| Lake Superior |
3,600 |
3,400* |
| Lake Michigan |
6,700 |
5,600* |
| Main Lake Huron |
3,000 |
2,800 |
| Georgian Ban |
630 |
600* |
| North Channel |
550 |
520* |
| Saginaw Bay |
870 |
440* |
| Lake Erie |
20,000 |
11,000** |
| Lake Ontario |
11,000 |
7,000** |
| * These loadings would result
if all municipal plants over one million gallons per day
achieved an effluent of 1 milligram per litre of phosphorus.
|
| ** These loadings are required
to meet the goals stated in paragraph 1 above. |
PHOSPHORUS LOAD REDUCTION
SUPPLEMENT TO ANNEX 3 OF THE 1978 AGREEMENT BETWEEN THE UNITED
STATES OF AMERICA AND CANADA ON GREAT LAKES WATER
QUALITY
- The purpose of this Supplement is to outline measures to fulfill
the commitments undertaken pursuant to paragraph 3 of Annex 3 of the 1978 Great Lakes Water Quality Agreement which requires that:
"... The Parties, in cooperation with the State and Provincial
Governments, shall within eighteen months after the date of entry into force of this Agreement confirm the future phosphorus
loads, and based on these establish load allocations and compliance schedules, taking into account the recommendations of
the International Joint Commission arising from the Pollution from Land Use Activities Reference ..."
- Phosphorus Target Loads
Table 1 establishes the recommended phosphorus target loads which
represent planning guides for the Parties. Table 1 replaces the table contained in paragraph 3 of Annex 3 of the 1978 Great Lakes
Water Quality Agreement (GLWQA).
|
Table 1 |
| Basin |
Phosphorus
Target Loads
(metric tonnes per week) |
| Lake Superior |
(See Section 3(b)) |
| Lake Michigan |
" |
| Main Lake Huron |
" |
| Georgian Bay |
" |
| North Channel |
" |
| Saginaw Bay |
440 (Note 1) |
| Lake Erie |
11,000 (Note 2) |
| Lake Ontario |
7,000 (Note 2) |
Note 1
Target load designed to alleviate drinking water taste and
odour problems.
Note 2
Target loads proposed to meet ecosystem objectives in Annex 3.
The allocation of the phosphorus target loads between the two
countries shall be consistent with the equal rights of both
Parties in the use of their boundary waters. |
- Phosphorus Load Reduction
Table 1 establishes the recommended phosphorus target loads
which represent planning guides for the Parties.
- Lower Lakes:
Table 2 summarizes the estimated phosphorus loading that will be
discharged to the Lower Lakes basins when all municipal waste
treatment facilities over one million gallons per day achieve
compliance with the one milligram per litre (1 mg/1) effluent
concentration (on a monthly average basis) as required by
Article VI, 1(a) of the 1978 GLWQA. The table also shows the
further reductions required to meet the Phosphorus Target Loads.
Table 2 - Phosphorus Load
Reduction Targets
(metric tonnes per year) |
| Basin |
Estimated
Loadings
at 1 mg/l
(Note 1) |
Phosphorus
Target
Load |
Estimates
of Further
Reductions
Required |
| Lake Erie |
13,000 |
11,000 |
2,000 |
| Lake Ontario |
7,430 |
7,000 |
430 |
- Upper Lakes:
Load reductions for the Upper Lakes will be accomplished by
achieving the 1 mg/1 phosphorus effluent concentration (on a
monthly average) at municipal waste treatment facilities
discharging more than one million gallons per day. The Parties
further agree to maintain the present oligotrophic state of the
open waters and relative algal biomass of Lakes Superior and
Huron. In addition, the United States agrees to undertake
efforts to achieve the substantial elimination of algal nuisance
growths in Lake Michigan. Further measures will be implemented
as required for Saginaw Bay, various localized nearshore problem
areas and Green Bay.
- Table 3 presents the distribution of further reductions in
phosphorus loading required for Lake Erie (in metric tonnes/year)
in order to achieve the estimated target loads. These figures
will be used by the Parties in the development of detailed plans
for achieving further phosphorus reductions as described in 4(a)
and (b) below.
Table 3 - Allocation of
Reductions to
Meet Target Loads for Lake Erie
As Shown in Table 1 |
| Canada |
U.S. |
Total |
| 300 |
1,700 |
2,000 |
- For Lake Ontario, the Parties, in cooperation and full
consultation with State and Provincial Governments, agree to
review the
measures to achieve further phosphorus reductions in this Basin
and will, within one year, meet to allocate the further
phosphorus
reductions between the parties. Plans to achieve the required
reductions set out in Table 2 will be developed using these
figures in
accordance with procedures described in 4(a) and (b) below.
- Phosphorus Load Reduction Plans
- Phosphorus load reduction plans will be developed and
implemented by the Parties in cooperation and full consultation
with State
and Provincial governments to achieve the phosphorus reductions
for Lake Erie and Ontario described in Table 2. The plans will
include phosphorus control programs and other measures as
outlined in Section 5 and will describe any additional measures
which
will be undertaken to evaluate and review progress in achieving
the phosphorus load reductions. A staged approach,
incorporating target dates for achieving further reductions,
will be included in the plans to provide the Parties and State
and
Provincial governments with a framework for implementing and
evaluating the effectiveness of controls.
- These detailed plans shall be tabled by the Parties with the
International Joint Commission 18 months after agreement on this
Supplement to Annex 3. The Parties will provide the Commission
with progress reports and annual updates of these plans.
- Programs and Other Measures
The following phosphorus control programs and measures will be
developed and implemented by the Parties in cooperation and full
consultation with State and Provincial governments to achieve
the required reductions in accordance with the plans developed
pursuant
to Section 4. The Parties recognize that the responsibility for
the control on nonpoint sources is shared between the Parties
and the
State and Provincial governments.
- Municipal Waste Treatment Facilities
- Priority will be given to the continuation and intensification
of efforts to ensure that municipal waste treatment facilities
discharging more that one million gallons per day achieve an
effluent concentration of 1 mg/1 total phosphorus on a monthly
average.
- Where necessary, consideration will be given to operating
facilities capable of greater phosphorus reduction at higher
level
of phosphorus removal than that required in 5(a)(i).
- Where necessary, municipal waste treatment facilities designed,
built, expanded or modified after October 1, 1983 should
allow for later modification to provide for greater removal of
phosphorus than that required under 5 (a)(i).
- Detergent Phosphorus Limitation
Priority will be given to continuing efforts to limit phosphorus
in household detergents.
- Industrial Discharges
Reasonable and practical measures will be undertaken to control
industrial sources of phosphorus.
- Nonpoint Source Programs and Measures
Priority management areas will be identified and designated for
application of urban and agricultural programs and measures
which
include:
- Urban drainage management control programs where feasible
consisting of level 1 measures throughout the Great Lakes
Basin; and level 2 measures where necessary to achieve
reductions or where local environmental conditions dictate (Note
1); and
- Agricultural nonpoint source management programs where feasible
consisting of level 1 measures throughout the Basin and
level 2 measures where necessary to achieve reductions of where
local environmental conditions dictate (Note 1).
Note 1:
Level 1 nonpoint source control options include:
Agricultural: adoption of management practices such as: animal
husbandry control measures, crop residue management,
conservation tillage, no-till, winter cover-crops, crop
rotation, strip cropping, vegetated buffer strips along stream
and ditch
banks, and improved fertilizer management practices.
Urban: adoption of management practices such as: erosion
controls, use of natural storage capacities and street cleaning.
Level 2 nonpoint source controls include Level 1 plus:
Agricultural: adoption of intensive practices such as: contour
plowing, contour strip cropping, contour diversions, tile
outlet-terraces, flow control structures, grassed waterways,
sedimentation basins and livestock manure storage facilities.
Urban: adoption of practices such as: artificial detention and
sedimentation of stormwater and runoff and reduction of
phosphorus
in combined sewer overflows.
- Research
Pursuant to the provisions of paragraph 2(e) of Annex 3, the
Parties will make special efforts to assure that their research
activities
will be responsive to the Programs and Other Measures described
herein.
- Monitoring and Surveillance
The Parties will develop and implement surveillance and
monitoring measures to determine the progress of Phosphorus Load
Reduction Plans for the Lower Lakes as called for under Section
4 above, and to evaluate efforts taken by the Parties to reduce
phosphorus in the Great Lakes Basin. These measures will include
an inventory of areas treated, watershed modelling and
improved measurement of tributary loadings to the Lower Lakes
for the purpose of providing improved nonpoint source loading
estimates and the monitoring of mass loadings to the Upper Lakes
to maintain or improve the environmental conditions described
in Section 3(b).
- Review
The Parties shall meet no later than December 31, 1988, to
review the effectiveness of the programs and measures described
herein,
and any remaining load reduction measures required to achieve
the target loads.
ANNEX 4 - DISCHARGES OF OIL AND HAZARDOUS
POLLUTING SUBSTANCES FROM VESSELS
- Definition. As used in this Annex:
- "Discharge" includes, but is not limited to, any spilling,
leaking, pumping, pouring, emitting or dumping; it does not
include unavoidable direct discharges of oil from a properly
functioning vessel engine;
- "Harmful quantity of oil" means any quantity of oil that, if
discharged from a ship that is stationary into clear calm water
on a clear day, would produce a film or a sheen upon, or
discolouration of, the surface of the water or adjoining
shoreline, or that would cause a sludge or emission to be
deposited beneath the surface of the water or upon the adjoining
shoreline;
- "Oil" means oil of any kind or in any form, including, but
not limited to, petroleum, fuel oil, oil sludge, oil refuse, oil
mixed with ballast or bilge water and oil mixed with wastes
other than dredged material;
- "Tanker" means any vessel designed for the carriage of
liquid cargo in bulk; and
- "Vessel" means any ship, barge or other floating craft,
where or not self-propelled.
- General Principles. Compatible regulation shall be adopted for
the prevention of discharges into the Great Lakes System of
harmful quantities of oil and hazardous polluting substances from
vessels in accordance with the following principles;
- The discharge of a harmful quantity of oil or hazardous
polluting substance, including any such quantities as may be
contained in ballast water, shall be prohibited and made subject
to appropriate penalties; and
- As soon as any person in charge has knowledge of any
discharge, or probable discharge, of harmful quantities of oil
or hazardous polluting substances, immediate notice of such
discharge shall be given to the appropriate agency in the
jurisdiction where the discharge occurs; failure to give this
notice shall be made subject to appropriate penalties.
- Oil. The programs and measures to be adopted for the
prevention of discharges of harmful quantities of oil shall
include;
- Compatible regulations for design, construction, and
operation of vessels based on the following principles.
- Each vessel shall have a suitable means of containing on
board cargo oil spills caused by loading or unloading
operations;
- Each vessel shall have a suitable means of containing on
board fuel oils spills caused by loading or unloading
operations, including those from tank vents and overflow
pipes;
- Each vessel shall have the capability of retaining on
board oily wastes accumulated during vessel operation;
- Each vessel shall be capable of off-loading retained oily
wastes to a reception facility;
- Each vessel shall be provided with a means for rapidly and
safely stopping the flow of cargo or fuel oil during loading,
unloading or bunkering operations in the event of an
emergency;
- Each vessel shall be provided with suitable lighting to
adequately illuminate all cargo and fuel oil handling areas if
the loading, unloading or bunkering operations occur at night;
- Hose assemblies used on board vessels for oil loading,
unloading, or bunkering shall be suitably designed,
identified, and inspected to minimize the possibility of
failure; and
- Oil loading, unloading, and bunkering systems shall be
suitably designed, identified, and inspected to minimize the
possibility of failure; and
- Programs to ensure that merchant vessel personnel are
trained in all functions involved in the use, handling, and
stowage of oil and in procedures for abatement of oil pollution.
- Hazardous Polluting Substances. The programs and measures to
be adopted for the prevention of discharges of harmful quantities
of hazardous polluting substances carried as cargo shall include:
- Compatible regulations for the design, construction, and
operation of vessels using as a guide the standards developed by
the International Maritime Organizations (IM0), including the
following additional requirements:
- Each vessel shall have a suitable means of containing on
board spills caused by loading or unloading operations;
- Each vessel shall have a capability of retaining on board
wastes accumulated during vessel operation;
- Each vessel shall be capable of off-loading wastes
retained to a reception facility;
- Each vessel shall be provided with a means for rapidly and
safely stopping the flow during loading or unloading
operations in the event of an emergency; and
- Each vessel shall be provided with suitable lighting to
adequately illuminate all cargo handling areas if the loading
or unloading operations occur at night;
- Identification of vessels carrying cargoes of hazardous
polluting substances in bulk, containers, and package form, and
of all such cargoes;
- Identification in vessel manifests of all hazardous
polluting substances;
- Carriage and storage arrangements of all hazardous polluting
substances in packaged form using as a guide the International
Maritime Dangerous Goods Code; and
- Programs to ensure that merchant vessel personnel are
trained in all functions involving the use, handling, and
stowage of hazardous polluting substances; the abatement of
pollution from such substances; and the hazards associated with
the handling of such substances.
- Additional Measures. Both Parties, in cooperation
with State and Provincial Governments shall take, as appropriate, action to
ensure the provision of adequate facilities for the reception,
treatment, and subsequent disposal of oil and hazardous polluting
substances wastes from all vessels.
ANNEX 5 - DISCHARGES OF VESSEL WASTES
- Definitions. As used in this Annex:
- "Discharge" includes, but is not limited to, any spilling,
leaking, pumping, emitting, and dumping;
- "Garbage" means all kinds of victual, domestic, and
operational wastes, excluding fresh fish and parts thereof
generated during the normal operation of the ship and liable to
be disposed of continually or periodically;
- "Sewage" means human or animal waste generated on board ship
and includes wastes from water closets, urinals, or a hospital
facility;
- "Vessel" means any ship, barge or other floating craft,
whether or not self-propelled; and
- "Waste water" means water in combination with other
substances, including ballast water and water used for washing
cargo holds, but excluding water in combination with oil,
hazardous polluting substances, or sewage.
- General Principles. Compatible regulations shall be
adopted governing the discharge into the Great Lakes System of
garbage, sewage, and waste water from vessels in accordance with
the following principles:
- The discharge of garbage shall be prohibited and made
subject to appropriate penalties;
- The discharge of waste water in harmful amounts or
concentrations shall be prohibited and made subject to
appropriate penalties; and
- Every vessel operating in these waters that is provided with
toilet facilities shall be equipped with a device or devices to
contain, incinerate, or treat sewage to an adequate degree;
appropriate penalties shall be provided for failure to comply
with the regulation.
- Critical Use Areas. Critical use areas of the Great
Lakes System may be designate where the discharge of waste water
or sewage shall be limited of prohibited.
- The Parties, in cooperation with State and Provincial
Governments, shall establish regulation to control the discharge
of sewage from pleasure craft of other classes of vessels
operating in the Great Lakes System or designated areas thereof.
- Additional Measures. The Parties shall take, as
appropriate, action to ensure the provision of adequate facilities
for the reception, treatment, and subsequent disposal of garbage,
waste water, and sewage from all vessels.
ANNEX 6 - REVIEW OF POLLUTION FROM SHIPPING
SOURCES
- Review. The Canadian Coast Guard and the United States Coast
Guard shall continue to review services, systems, programs,
recommendations, standards and regulations relating to shipping
activities for the purpose of maintaining or improving Great Lakes
water quality. The reviews shall include:
- Review of vessel equipment, vessel manning, and navigation
practices or procedures, and of aids to navigation and vessel
traffic management, for the purpose of precluding casualties
which may be deleterious to water quality;
- Review of practices and procedures regarding waste water and
their deleterious effect on water quality, including, as
required, studies to determine if live fish or invertebrates in
ballast water discharges into the Great Lakes System constitute
a threat to the System;
- Review of practices and procedures, as well as current
technology for the treatment of vessel sewage;
- Review of current practices and procedures regarding the
prevention of pollution from the loading, or unloading, or on
board transfer of cargo; and
- Review of international ship safety, pollution prevention
and civil liability conventions and standards developed by the
International Maritime Organization to determine their
applicability in the boundary waters of the Great Lakes System
- Consultation. Representatives of the Canadian Coast Guard and
the United States Coast Guard, and other interested agencies,
shall meet at least annually to consider Annexes 4, 5, 6, 8 and 9
of this Agreement. A report of this annual consultation shall be
furnished to the International Joint Commission prior to its
annual meeting on Great Lakes water quality. The purpose of the
consultation shall be to:
- Provide an interchange of information with respect to
continuing reviews, ongoing studies, and areas of concern;
- Identify and determine the relative importance of problems
requiring further study; and
- Apportion responsibility, as between the Canadian Coast
Guard and the United States Coast Guard, for the studies, or
portions thereof, which were identified in subparagraph 2(b)
above.
- Studies. Where a review identifies additional areas for
improvement, the Canadian Coast Guard and the United States Coast
Guard, and other interested agencies, will undertake a study to
establish improved procedures for the abatement and control of
pollution from shipping sources, and will:
- Develop a brief study description which will include the
nature of the perceived problem, procedures to quantify the
problem, alternative solutions to the problem, procedures to
determine the best alternative, and an estimated completion
date;
- Transmit study descriptions to the International Joint
Commission and other interested agencies:
- Transmit the study, or a brief summary of its conclusions,
to the International Joint Commission and other interested
agencies; and
- Transmit a brief status report to the International Joint
Commission and other interested agencies if the study is not
completed by the estimated completion date.
- Responsibility. Responsibility for the coordination of the
review, consultation, and studies is assigned to the Canadian
Coast Guard and the United States Coast Guard.
- There shall be established, under the auspices of the Water
Quality Board, a Subcommittee on Dredging. The Subcommittee shall:
- Review the existing practices in both countries relating to
dredging activities, as well as the previous work done by the
International Working Group on Dredging, with the objective of
developing, within one year of the date of entry into force of
this Agreement, compatible guidelines and criteria for dredging
activities in the boundary waters of the Great Lakes System;
- Maintain a register of significant dredging projects being
undertaken in the Great Lakes System with information to allow
for the assessment of the environmental effects of the projects.
The register shall include pertinent statistics to allow for the
assessment of pollution loadings from dredged materials to the
Great Lakes System;
- Encourage the exchange of information relating to
developments of dredging technology and environmental research.
- The Subcommittee shall identify specific criteria for the
classification of polluted sediments of designated areas of
intensive and continuing dredging activities within the Great
Lakes System. Pending development of criteria and guidelines by
the Subcommittee, and their acceptance of the Parties, the Parties
shall continue to apply the criteria now in use by the regulatory
authorities; however, neither party shall be precluded from
applying standards more stringent than those now in use.
- The Parties shall continue to direct particular attention to
the identification and preservation of significant wetland areas
in the Great Lakes Basin Ecosystem which are threatened by
dredging and disposal activities.
- The Parties shall encourage research and investigate advances
in dredging technology and the pathways, fate and effects of
nutrients and contaminants of dredged materials.
- The Subcommittee shall undertake any other activities as the
Water Quality Board may direct.
ANNEX 8 - DISCHARGES FROM ONSHORE AND OFFSHORE
FACILITIES
- Definitions. As used in this Annex:
- "Discharge" means the introduction of polluting substances
into receiving waters and includes, but is not limited to, any
spilling, leaking, pumping, pouring, emitting or dumping; it
does not include continuous effluent discharges from municipal
or industrial treatment facilities;
- "Harmful quantity of oil" means any quantity of oil that, if
discharged into clear calm waters on a clear day, would produce
a film or sheen upon, or discoloration of the surface of the
water or adjoining shoreline, or that would cause a sludge or
emulsion to be deposited beneath the surface of the water or
upon the adjoining shoreline;
- "Facility" includes motor vehicles, rolling stock,
pipelines, and any other facility that is used or capable of
being used for the purpose of processing, producing, storing,
disposing. transferring or transporting oil or hazardous
polluting substances, but excludes vessels;
- "Offshore facility" means any facility of any kind located
in, on or under any water;
- "Onshore facility" means any facility of any kind located
in, on or under, any land other than submerged land;
- "Oil" means oil of any kind or in any form, include, but not
limited to petroleum, fuel oil, oil sludge, oil refuse, and oil
mixed with wastes, but does not include constituents of dredged
spoil.
- Principles. Regulations shall be adopted for the prevention of
discharges into the Great Lakes System of harmful quantities of
oil and hazardous polluting substances from onshore and offshore
facilities in accordance with the following principles:
- Discharges of harmful quantities of oil or hazardous
polluting substances shall be prohibited and made subject to
appropriate penalties;
- As soon as any person in charge has knowledge of any
discharge of harmful quantities of oil or hazardous polluting
substances, immediate notice of such discharge shall be given to
the appropriate agency in the jurisdiction where the discharge
occurs; failure to give this notice shall be made subject to
appropriate penalties.
- Programs and Measures. The programs and measures to be adopted
shall include the following:
- Review of the design, construction, and location of both
existing and new facilities for their adequacy to prevent the
discharge of oil or hazardous polluting substances;
- Review of the operation, maintenance and inspection
procedures of facilities for their adequacy to prevent the
discharge of oil or hazardous polluting substances;
- Development and implementation of regulations and personnel
training programs to ensure the safe use and handling of oil or
hazardous polluting substances;
- Programs to ensure that at each facility plans and
provisions are made and equipment provided to stop rapidly and
safely, contain, and
- Clean up discharges of oil or hazardous polluting
substances; and
- Compatible regulations and other programs for the
identification and placarding of containers, vehicles and other
facilities containing, carrying, or handling oil or hazardous
polluting substances; and where appropriate notification to
appropriate agencies of vehicle movements, maintenance of a
registry, and identification in manifests of such substances to
be carried.
- Implementation.
- Each Party shall submit a report to the International Joint
Commission outlining its programs and measures, existing or
proposed, for the implementation of this Annex within six months
of the date of entry into force of this Agreement.
- The report shall outline programs and measures, existing or
proposed, for each of the following types of onshore and
offshore facilities:
- land transportation including rail and road modes;
- pipelines on land and submerged under water;
- offshore drilling rigs and wells;
- storage facilities both onshore and offshore; and
- wharves and terminals with trestle or underwater pipeway
connections to land and offshore island type structures and
buoys used for the handling of oil and hazardous polluting
substances.
- The report shall outline programs and measures, existing or
proposed, for any other type of onshore or offshore facility.
- Upon receipt of the reports, the Commission , in
consultation with the Parties, shall review the programs and
measures outlined for adequacy and compatibility and, if
necessary, make recommendation to rectify any such inadequacy or
incompatibility it finds.
ANNEX 9 - JOINT CONTINGENCY PLAN
- The Plan. Annex one (CANUSLAK) of the Canada-United
States Joint Marine Contingency Plan, as amended or reviewed,
shall be maintained in force for the Great Lakes. The Canadian
Coast Guard and the United States Coast Guard shall, in
cooperation with other affected parties, identify and provide
detailed Supplements for areas of high risk and of particular
concern in augmentation of CANUSLAK. It shall be the
responsibility of the United States Coast Guard and the Canadian
Coast Guard to coordinate and to maintain the Plan and the
Supplements appended thereto.
- Purpose. The purpose of the Plan is to provide for
coordinated and integrated response to pollution incidents in the
Great Lakes System by responsible federal, state, provincial and
local agencies. the Plan supplements the national, provincial and
regional plans of the Parties.
- Pollution Incidents.
- A pollution incident is a discharge, or an imminent threat
of discharge of oil, hazardous polluting substance or other
substance or other substance of such magnitude or significance
as to require immediate response to contain, clean up, and
dispose of the material
- The objectives of the Plan in pollution incidents are:
- To develop appropriate preparedness measures and effective
systems for discovery and reporting the existence of a
pollution incident within the area covered by the Plan;
- To institute prompt measures to restrict the further
spread of the pollutant; and
- To provide adequate cleanup response to pollution
incidents.
- Funding. The costs of operations of both Parties under
the Plan shall be borne by the Party in whose waters the pollution
incident occurred, unless otherwise agreed.
- Amendment. The Canadian Coast Guard and the United
States Coast Guard are empowered to amend the Plan subject to the
requirement that such amendments shall be consistent with the
purpose and objectives of this Annex.
ANNEX 10 - HAZARDOUS POLLUTING SUBSTANCES
- The Parties shall:
- Maintain a list, to be known as Appendix 1 of the Annex
(hereinafter referred to as Appendix 1), of the substances know
to have toxic effects on aquatic and animal life and a risk of
being discharged to the Great Lakes System;
- Maintain a list, to be known as Appendix 2 of this Annex
(hereinafter referred to as Appendix 2), of substances
potentially having such effects and such a risk of discharge,
and to give priority to the examination of these substances for
possible transfer to Appendix 1;
- Ensure that these lists are continually revised in the light
of growing scientific knowledge; and
- Develop and implement programs and measures to minimize or
eliminate the risk of release of hazardous polluting substances
to the Great Lakes System.
- Hazardous polluting substances to be listed in Appendix 1
shall be determined in accordance with the following procedures:
- Selection of all hazardous substances for listing in
Appendix 1 shall be based upon documented toxicological and
discharge potential data which have been evaluated by the
Parties and deemed to be mutually acceptable.
- Revisions to Appendix 1 may be made by mutual consent of the
Parties and shall be treated as amendments to this Annex for the
purposes of Article XIII of this Agreement.
- Using the agreed selection criteria, either Party may
recommend at any time a substance to be added to the list in
Appendix 1. Such substance need not previously have been listed
in Appendix 2. The Party receiving the recommendation will have
60 days to review the associated documentation and either reject
the proposed substance or accept the substance pending
completion of appropriate procedural or domestic regulatory
requirements. Cause for rejection must be documented and
submitted to the initiating Party and may be the basis for any
further negotiations.
- The criteria to be applied to the selection of substances as
candidates for listing in Appendix 1 are:
- Acute toxicological effects, as determined by whether the
substance is lethal to:
- One-half of a test population of aquatic animals in 96
hours or less at a concentration of 500 milligrams per litre
or less; or
- One-half of a test population of animals in 14 days or
less when administered in a single oral dose equal to or less
than 50 milligrams per kilogram of body weight; or
- One-half of a test population of animals in 14 days or
less when dermally exposed to an amount equal to or less that
200 milligrams per kilogram body weight for 24 hours; or
- One-half of a test population of animals in 14 days or
less when exposed to a vapour concentration equal to or less
than 20 cubic centimetres per cubic meter in air for one hour;
or
- Aquatic flora as measured by a maximum specific growth
rate or total yield of biomass which is 50 per cent lower than
a control culture over 14 days in medium at concentrations
equal to or less than 100 milligrams per litre.
- Risk of discharge into the Great Lakes System, as determined
by:
- Gathering information on the history of discharges or
accidents;
- Assessing the modal risks during transport and determining
the use and distribution patterns;
- Identifying quantities manufactured or imported.
- Potentially hazardous polluting substances to be listed in
Appendix 2 of this Annex shall be determined in accordance with
the following procedures:
- Either Party may add new substances to Appendix 2 by
notifying the other in writing that the substance is considered
to be a potential hazard because of documented information
concerning aquatic toxicity mammalian and other vertebrate
toxicity, phytotoxicity, persistence, bio-accumulation,
mutagenicity, teratogenicity, carcinogenicity, environmental
translocation or because of documented information on risk of
discharge to the environment. The documentation of the potential
hazard and the selected criteria upon which it is based will
also be submitted.
- Removal of substances from Appendix 2 shall be by mutual
consent of the Parties.
- The Parties shall give priority to the examination of
substances listed in Appendix 2 for possible transfer to
Appendix 1.
- Programs and measures to control the risk of pollution from
transport, storage, handling and disposal of hazardous polluting
substances are contained in Annexes 4 and 8; and
- In addition to the lists of hazardous polluting substances
described in Appendices 1 and 2 to this Annex, practice and
procedures consistent with the general principles of this
Agreement shall be applied to those substances
categorized
as marine pollutants by the International Maritime Organization.
|
APPENDIX 1 - HAZARDOUS POLLUTING
SUBSTANCES |
Acetaldehyde
Acetic Acid
Acetic Anhydride
Acetone Cyanohydrin
Acetyl Bromide
Acetyl Chloride
Acrolein
Acrylonitrile
Aldrin
Allyl Alcohol
Allyl Chloride
Aluminum Sulfate
Ammonia
Ammonium Acetate
Ammonium Benzoate
Ammonium Bicarbonate
Ammonium Bichromate
Ammonium Bifluoride
Ammonium Bisulfite
Ammonium Carbamate
Ammonium Carbonate
Ammonium Chloride
Ammonium Chromate
Ammonium Citrate, Dibasic
Ammonium Fluoborate
Ammonium Fluoride
Ammonium Hydroxide
Ammonium Oxalate
Ammonium Silicofluoride
Ammonium Sulfamate
Ammonium Sulfide
Ammonium Sulfite
Ammonium Tartrate
Ammonium Thicoyanate
Ammonium Thiosulfate
Amyl Acetate
Aniline
Antimony Pentachloride
Antimony Potassium Tartrate
Antimony Tribromide
Antimony Trichloride
Antimony Trifluoride
Antimony Trioxide
Arsenic Disulfide
Arsenic Pentoxide
Arsenic Trichloride
Arsenic Trioxide
Arsenic Trisulphide
Cadmium Acetate
Cadmium Bromide
Cadmium Chloride
Calcium Arsenate
Calcium Arsenite
Calcium Carbide
Calcium Chromate
Calcium Cyanide
Calcium
Dodecylbenzenesulfonate
Calcium Hydroxide
Calcium Hypochlorite
Calcium Oxide
Captan
Carbaryl
Carbon Disulfide
Chlordane
Chlorine
Chlorobenzene
Chloroform
Chlorosulfonic Acid
Chlorpyrifos
Chromic Acetate
Chromic Acid
Chromic Sulfate
Chromous Chloride
Cobaltous Bromide
Cobaltous Foremate
Cobaltous Sulfamate
Coumaphos
Cresol
Cupric Acetate
Cupric Acetoarsenite
Cupric Chloride
Cupric Nitrate
Cupric Oxalate
Cupric Sulfate
Cupric Sulfate, Ammoniated
Cupric Tartrate
Cyanogen Chloride
Cyclohexane |
2,
4-D Acid
2, 4-D Esters
Dalapon
DDT
Diazinon
Dicamba
Dichlobenil
Dichlone
Dichlorvos
Dieldrin
Diethylamine
Dimethylamine
Dinitrobenzene (mixed)
Dinitrophenol
Diquat
Disulfoton
Diuron
Dedocylbenzenesulfonic Acid
Endosulfan
Endrin
Ethion
Ethylbenzene
Ethylenediamine
EDTA
Ferric Ammonium Citrate
Ferric Ammonium Oxalate
Ferric Chloride
Ferric Fluoride
Ferric Nitrate
Ferric Sulfate
Ferrous Ammonium Sulfate
Ferrous Chloride
Ferrous Sulfate
Formaldehyde
Formic Acid
Fumaric Acid
Furfural
Guthion
Heptachlor
Hydrochloric Acid
Hydrofluoric Acid
Hydrogen Cyanide
Isoprene
Isopropanolamine
Dodecylbenzenesulfonate
Kelthane
Lead Acetate
Lead Arsenate
Lead Chloride
Lead Fluoborate
Lead Fluoride
Lead Iodide
Lead Nitrate
Lead Stearate
Lead Sulfate
Lead Sulfide
Lead Thiocyanate
Lindane
Lithium Chromate
Malathion
Maleic Acid
Maleic Anhydride
Mercuric Cyanide
Mercuric Nitrate
Mercuric Sulfate
Mercuric Thiocyanate
Mercurous Nitrate
Methoxychlor
Methyl Mercaptan
Methyl Methacrylate
Methyl Parathion
Mevinphos
Mexacarbate
Monoethylamine
Monomethylamine
Naled
Naphthalene
Naphtenic Acid
Nickel Ammonium Sulfate
Nickel Chloride
Nickel Hydroxide
Nickel Nitrate
Nickel Sulfate
Nitric Acid
Nitrobenzene
Nitrogen Dioxide
Nitrophenol (mixed) |
Paraformaldehyde
Parathion
Pentachlorophenol
Phenol
Phosgene
Phosphoric Acid
Phosphorous
Phosphorus Oxychloride
Phosphorus Pentasulfide
Phosphorus Trichloride
Polychlorinated Biphenyls
Potassium Arsenate
Potassium Arsenite
Potassium Bichromate
Potassium Chromate
Potassium Cyanide
Potassium Hydroxide
Potassium Permanganate
Propionic Acid
Propionic Anhydride
Pyrethrins
Quinoline
Resorcinol
Selenium Oxide
Sodium
Sodium Arsenate
Sodium Arsenite
Sodium Bichromate
Sodium Bifluoride
Sodium Bisulfite
Sodium Chromate
Sodium Cyanide
Sodium Dodecylbenzenesulfonate
Sodium Fluoride
Sodium Hydrosulfide
Sodium Hydroxide
Sodium Hypochlorite
Sodium Methylate
Sodium Nitrite
Sodium Phosphate, Dibasic
Sodium Phosphate, Tribasic
Sodium Selenite
Strontium Chromate
Strychnine
Styrene
Sulfuric Acid
Sulfur Monochloride
2,4,5-T Acid
2,4,5-7 Esters
TDE
Tetraethyl Lead
Tetraethyl Pyrophosphate
Toluene
Toxaphene
Trichlorfon
Trichlorophenol
Triethanolamine
Dodecylbenzenesulfonate
Triethylamine
Thrimethylamine
Uranyl Acetate
Uranyl Nitrate
Vanadium Pentoxide
Vanadyl Sulfate
Vinyl Acetate
Xylene (mixed)
Xylenol
Zinc Acetate
Zinc Ammonium Chloride
Zinc Borate
Zinc Bromide
Zinc Charbonate
Zinc Chloride
Zinc Cyanide
Zinc Fluoride
Zinc Formate
Zinc Hydrosulfite
Zinc Nitrate
Zinc Phenolsulfonate
Zinc Phosphide
Zinc Silicofluoride
Zinc Sulfate
Zirconium Nitrate
Zirconium Potassium Fluoride
Zirconium Sulfate
Zirconium Tetrachloride
|
|
APPENDIX 2 - POTENTIAL HAZARDOUS
POLLUTING SUBSTANCES |
Acridine
Allethrin
Aluminum Fluoride
Aluminum Nitrate
Ammonium Bromide
Ammonium Hypophosphite
Ammonium Iodide
Ammonium Pentaborate
Ammonium Persulfate
Antimony Pentafluoride
Antimycin A
Arsenic Acid
Barhan
Benfluralin
Bensulide
Benzene Hexachloride
Beryllium Sulfate
Butifos
Cadmium
Cadmium Cyanide
Cadmium Nitrate
Captafol
Carbophenothion
Chlorflurazole
Chlorothion
Chlorpropham
Chromic Chloride
Chromium
Chromyl Chloride
Cobaltous Fluoride
Copper
Crotoxyphos
Cupric Carbonate
Cupric Citrate
Cupric Formate
Cupric Glycinate |
Cupric Lactate
Cupric Paraamino Benzoate
Cupric Salicylate
Cupric Subacetate
Cuprous Bromide
Demeton
Dibutyl Phthalate
Dicapthon
2,4-Dinitrochlorobenzene
p-Dinitrocresol
Dinocap
Dinoseb
Dioxathion
Dodine
EPN
Gold Trichloride
Hexachlorophene
Hydrogen Sulfide
m-Hydroxybenzoic Acid
p-Hydroxybenzoic Acid
Hydroxylamine
2-Hydroxyphenazine-1-Carboxylic Acid
Lactonitrile
Lead Tetraacetate
Lead Thiosulfate
Lead Tungstate
Lithium Bichromate
Malachite Green
Manganese Chloride, Anhydrous
MCPA
Mercuric Acetate
Mercuric Chloride
Mercury
Metam-Sodium
p-Methylamino-Phenol
|
2-Methyl-Napthoquinone
Neburon
Nickel Formate
Phenylmercuric Acetate
n-Phenyl Naphthylamine
Phorate
Phosphamidon
Picloram
Potassium Azide
Potassium Cuprocyanide
Potassium Ferricyanide
Propyl Alcohol
Pyridyl Mercuric Acetate
Rotenone
Silver
Silver Nitrate
Silver Sulfate
Sodium Azide
Sodium 2-Chlorotoluene-5-Sulfonate
Sodium Pentachlorophenate
Sodium Phosphate, Monobasic
Sodium Sulfide
Stannous Fluoride
Strontium Nitrate
Sulfoxide
Temephos
Thallium
Thionazin
1,2,4-Trichlorobenzene
Uranium Peroxide
Uranyl Sulfate
Zinc Bichromate
Zinc Potassium Chromate
Zirconium Acetate
Zirconium Oxychloride |
ANNEX
11 - SURVEILLANCE AND MONITORING
- Surveillance and monitoring activities shall be undertaken for
the following purposes:
- Compliance. To assess the degree to which
jurisdictional control requirements are being met.
- Achievement of General and Specific Objectives. To
provide definitive information on the location, severity, areal
or volume extent, frequency and duration of non-achievement of
the Objectives, as a basis for determining the need for more
stringent control requirements.
- Evaluation of Water Quality Trends. To provide
information for measuring local and whole lake response to
control measures using trend analysis and cause/effect
relationships, and to provide information which will assist in
the development and application of predictive techniques for
assessing impact of new developments and pollution sources. The
results of water quality evaluations will be used for:
- assessing the effectiveness of remedial and preventative
measures and identifying the need for the improved pollution
control;
- assessing enforcement and management strategies; and
- identifying the need for further technology development
and research activities.
- Identification of Emerging Problems. To determine the
presence of new or hitherto detected problems in the Great Lakes
Basin Ecosystem, leading to the development and implementation
of appropriate pollution control measures.
- Annex 2 Programs. To support the development of
Remedial Action Plans for Areas of Concern and Lakewide
Management Plans for Critical Pollutants pursuant to Annex 2.
- A joint surveillance and monitoring program necessary to
ensure the attainment of the foregoing purposes shall be developed
and implemented among the Parties and the State and Provincial
Governments. The Great Lakes International Surveillance Plan
contained in the Water Quality Board Annual Report of 1975 and
revised in subsequent reports shall serve as a model for the
development of the joint surveillance and monitoring program.
- The program shall include baseline data collection, sample
analysis, evaluation and quality assurance programs (including
standard sampling and analytical methodology, inter-laboratory
comparisons, and compatible data management) to allow assessment
of the following:
- Inputs from tributaries, point source discharges,
atmosphere, and connecting channels;
- Whole lake data including that for nearshore areas (such as
harbours and embayments, general shoreline and cladophora growth
areas), open waters of the Lakes, fish contaminants, and
wildlife contaminants;
- Overflows including connecting channels, water intakes and
outlets;
- Total pollutant loadings to, storage and transformation
within, and export from the Great Lakes System;
- The adequacy of proposed load reductions and schedules
contained in Lakewide Management Plans; and
- Contributions of various exposure media to the overall human
intake of toxic substances in the Great Lakes Basin Ecosystem.
- Development of Ecosystem Health Indicators for the Great
Lakes. The Parties agree to develop ecosystem health
indicators to assist in evaluating the achievement of the specific
objectives for the ecosystem pursuant to Annex 1:
- with respect to Lake Superior, lake trout and the
crustacean Pontoporeia hoyi shall be used as indicators:
- Lake Trout
- productivity greater than 0.38 kilograms/hectare;
- stable, self-producing stocks;
- free from contaminants at concentrations that
adversely affect the trout themselves or the quality of the
harvested products.
- Pontoporeia hoyi
- the abundance of the crustacean, Pontoporeia hoyi,
maintained throughout the entire lake at
present levels of 220-320/(metres)2 (depths less than 100
metres) and 30-160/(metres)2 (depths greater than 100 metres);
and
- with respect to the rest of the boundary waters of the
Great Lakes System or portions thereof, and for Lake Michigan,
the indicators are to be developed.
ANNEX
12 - PERSISTENT TOXIC SUBSTANCES
- Definitions. As used in this Annex:
- "Persistent toxic substance" means any toxic substance with
a half-life in water of greater than eight weeks;
- "Half-life" means the time required for the concentration of
a substance to diminish to one-half of its original value in a
lake or water body;
- "Early warning system" means a procedure to anticipate
future environmental contaminants (i.e., substances having an
adverse effect on human health or the environment) and to set
priorities for environmental research, monitoring and regulatory
action.
- General Principles.
- Regulatory strategies for controlling or preventing the
input of persistent toxic substances to the Great Lakes System
shall be adopted in accordance with the following principles:
- The intent of programs specified in this Annex is to
virtually eliminate the input of persistent toxic substances
in order to protect human health and to ensure the continued
health and productivity of living aquatic resources and human
use thereof;
- The philosophy adopted for control of inputs of persistent
toxic substances shall be zero discharge; and
- The reduction in the generation of contaminants,
particularly persistent toxic substances, either through the
reduction of the total volume or quantity of waste or through
the reduction of the toxicity of waste, or both, shall,
wherever possible, be encouraged.
- The Parties shall take all reasonable and practical measures
to rehabilitate those portions of the Great Lakes System
adversely affected by persistent toxic substances.
- Programs. The Parties in cooperation with the State and
Provincial Governments, shall develop and adopt the following
programs and measures for the elimination of discharges of
persistent toxic substances:
- Identification of raw materials, processes, products,
by-products, waste sources and emissions involving persistent
toxic substances, and quantitative data on the substances,
together with recommendations on handling, use and disposition.
Every effort shall be made to complete this inventory by
January, 1982;
- Establishment of close coordination between air, water and
solid waste programs in order to assess the total input of toxic
substances to the Great Lakes System and to define
comprehensive, integrated controls;
- Joint programs for disposal of hazardous materials to ensure
that these materials such as pesticides, contaminated petroleum
products, contaminated sludge and dredge spoils and industrial
wastes are properly transported and disposed of. Every effort
shall be made to implement these programs by 1980.
- Monitoring. Monitoring and research programs in support
of the Great Lakes International Surveillance Plan should be
established at a level sufficient to identify:
- Temporal and spatial trends in concentration of persistent
toxic substances such as PCB, mirex, DDT, mercury and dieldrin,
and of there substances known to be present in biota and
sediment of the Great Lakes System;
- The impact of persistent toxic substances on the health of
humans and the quality and health of living aquatic systems;
- The sources of input of persistent toxic substances; and
- The presence of previously unidentified persistent toxic
substances.
- Early Warning System. An early warning system
consisting of, but not restricted to, the following elements shall
be established to anticipate future toxic substances problems:
- Development and use of structure-activity correlations to
predict environmental characteristics of chemicals;
- Compilation and review of trends in the production, import,
and use of chemicals;
- Review of the results of environmental testing on new
chemicals;
- Toxicological research on chemicals, and review of research
conducted in other countries;
- Maintenance of a biological tissue bank and sediment to
permit retroactive analysis to establish trends over time;
- Monitoring to characterize the presence and significance of
chemical residues in the environment;
- Development and use of mathematical models to predict
consequences of various loading rates of different chemicals;
- Development of a data bank for storage of information on
physical/chemical properties, toxicology, use and quantities in
commerce of known and suspected persistent toxic substances;
- Development of data necessary to evaluate the loadings of
critical pollutants or other polluting substances identified in
the boundary waters of the Great Lakes System; and
- Further development and use of reproduction,
physiological and biochemical measures in wildlife, fish and
humans as health effects indicators and the establishment of a
data base for storage, retrieval and interpretation of the data.
- Human Health. The Parties shall establish action levels
to protect human health based on multimedia exposure and the
interactive effects of toxic substances.
- Research. Research should be intensified to determine
the pathways, fate and effects of toxic substances aimed at the
protection of human health, fishery resources and wildlife of the
Great Lakes Basin Ecosystem. In particular, research should be
conducted to determine:
- The significance of effects of persistent toxic substances
on human health and aquatic life;
- Interactive effects of residues of toxic substances on
aquatic life, wildlife, and human health; and
- Approaches to calculation of acceptable loading rates for
persistent toxic substances, especially those which, in part,
are naturally occurring.
- Reporting. The Parties shall report, by December 31,
1988 and biennially thereafter, on the progress of programs and
measures to reduce the generation of contaminants in accordance
with the principle in sub-paragraph 2(a)(iii) above.
ANNEX
13 - POLLUTION FROM NON-POINT SOURCES
- Purpose. This Annex further delineates programs and
measures for the abatement and reduction on non-point sources of
pollution from land-use activities. These include efforts to
further reduce non-point source inputs of phosphorus, sediments,
toxic substances and microbiological contaminants contained in
drainage from urban and rural land, including waste disposal
sites, in the Great Lakes System.
- Implementation. The Parties, in conjunction with
State and Provincial Governments, shall:
- identify land-based activities contribution to water
quality problems described in Remedial Action Plans for Areas of
Concern, or in Lakewide Management Plans including, but not
limited to, phosphorus and Critical Pollutants; and
- develop and implement watershed management plans,
consistent with the objectives and schedules for individual
Remedial Action Plans or Lakewide Management Plans, on priority
hydrologic units to reduce non-point source inputs. Such
watershed plans shall include a description of priority areas,
intergovernmental agreements, implementation schedules, and
programs and other measures to fulfill the purpose of this Annex
and the General and Specific Objectives of this Agreement. Such
measures shall include provisions for regulation of non-point
sources of pollution.
- Wetlands and their Preservation. Significant wetland
areas in the Great Lakes System that are threatened by urban and
agricultural development and waste disposal activities should be
identified, preserved and, where necessary, rehabilitated.
- Surveillance, Surveys and Demonstration Projects.
Programs and projects shall be implemented in order to determine:
- non-point source pollutants inputs to and outputs from
rivers and shoreline areas sufficient to estimate loadings to
the boundary waters of the Great Lakes System; and
- the extent of change in land-use and land management
practices that significantly affect water quality for the
purpose of tracking implementation of remedial measures and
estimating associated changes in loadings to the Lakes.
Demonstration projects of remedial programs on pilot urban and
rural watersheds shall be encouraged to advance knowledge and
enhance information and education services, including extension
services, where applicable.
- The Parties shall report by December 31, 1988 and
biennially thereafter, to the Commission on progress in developing
specific watershed management plans and implementing programs and
measures to control non-point sources of pollution.
ANNEX
14 - CONTAMINATED SEDIMENT
- Objectives. The Parties shall, in cooperation with
State and Provincial Governments, identify the nature and extent
of sediment pollution of the Great Lakes System. Based on these
findings, they shall develop methods to evaluate both the impact
of polluted sediments on the Great Lakes System, and the
technological capabilities of programs to remedy such pollution.
Information obtained through research and studies pursuant to this
Annex shall be used to guide the development of Remedial Action
Plans and Lakewide Management Plans pursuant to Annex 2, but shall
not be used to forestall the implementation of remedial measures
already under way. Dredging for the purpose of navigation is
addressed in Annex 7.
- Research and Studies.
- General. The Parties, in cooperation with State
and Provincial Governments, shall exchange information relating
to the mapping, assessment and management of contaminated
sediments in the Great Lakes System.
- Surveillance Programs. The Parties, in cooperation
with State and Provincial Governments shall:
- evaluate, on or before December 31, 1988 and biennially
thereafter, existing methods for quantifying the transfer of
contaminants and nutrients to and from bottom sediments for
use in determining the impact of polluted sediments on the
Great Lakes Basin Ecosystem;
- review practices in both countries regarding the
classification of contaminated sediments and establish
compatible criteria for the classification of sediment
quality;
- develop common methods to quantify the transfer of
contaminants and nutrients to and from bottom sediments. Such
methods shall be used to determine the impact of polluted
sediment of the Great Lakes System. As a first step,
biological indicators shall be developed to determine
accumulation rates in biota from polluted bottom sediments;
and
- develop a standard approach and agreed procedures for
the management of contaminated sediments by December 31, 1988.
- Technology Programs
- The Parties shall, on or before December 31, 1988 and
biennially thereafter, in cooperation with State and
Provincial Governments, evaluate existing technologies for the
management of contaminated sediments such as isolation,
capping, in-place decontamination and removal of polluted
bottom sediment.
- The Parties, in cooperation with State and Provincial
Governments shall design and implement demonstration projects
for the management of polluted bottom sediment at selected
Areas of Concern identified pursuant to Annex 2. The design
shall be based on the evaluation(s) made pursuant to
sub-paragraph (i) above, the Parties shall meet by June 20,
1988 and jointly design a demonstration program and
implementation schedule and report progress biennially
thereafter.
- Long-Term Measures. The Parties, in cooperation with
State and Provincial Governments, shall also ensure that measures
are adopted for the management of contaminated sediment
respecting:
- the construction and the long-term maintenance of
disposal facilities; and
- the use of contaminated sediment in the creation of land.
- Reporting. The Parties shall report their progress
in implementing this Annex to the Commission biennially,
commencing with a report no later than December 31, 1988.
ANNEX
15 - AIRBORNE TOXIC SUBSTANCES
- Purpose. The Parties, in cooperation with State and
Provincial Governments, shall conduct research, surveillance and
monitoring and implement pollution control measures for the
purpose of reducing atmospheric deposition of toxic substances,
particularly persistent toxic substances, to the Great Lakes Basin
Ecosystem.
- Research. Research activities shall be conducted to
determine pathways, fate and effects of such toxic substances for
the protection of the Great Lakes System. In particular, research
shall be conducted to:
- understand the processes of wet and dry deposition and
those associated with the vapor exchange of toxic substances;
- understand the effects of persistent toxic substances,
singly or in synergistic or additive combination with other
substances, through aquatic exposure routes on the health of
humans and the quality and health of aquatic life where a
significant source of these substances is the atmosphere, in
accordance with sub-paragraph 4(b) of Annex 12; and
- develop models of the intermediate and long-range
movement and transformation of toxic substances to determine;
- the significance of atmospheric loadings to the Great
Lakes System relative to other pathways; and
- the sources of such substances from outside the Great
Lakes System.
- Surveillance and Monitoring. The Parties shall:
- establish, as part of the Great Lakes International
Surveillance Plan (GLISP) instituted under Annex 11, an
Integrated Atmospheric Deposition Network in accordance with
paragraph 4 below;
- identify, by means of this Network, toxic substances and,
in particular, persistent toxic substances, appearing on List
No. 1 described in Annex 1, of those designated as Critical
Pollutants pursuant to Annex 2 and their significant sources in
accordance with sub-paragraph 4(c) of Annex 12, and to track
their movements; and
- utilize this Network in order to:
- determine atmospheric loadings of toxic substances to
the Great Lakes System by quantifying the total and net
atmospheric input of these same contaminants, pursuant to
sub-paragraph 3(a) of Annex 11;
- define the temporal and spatial trends in the
atmospheric deposition of such toxic substances in accordance
with sub-paragraph 4(a) of Annex 12; and
- develop Remedial Action Plans and Lakewide Management
Plans pursuant to Annex 2.
- Components of the Integrated Atmospheric Deposition
Network. The Parties shall confer on or before October 1,
1988, regarding;
- the identity of the toxic substances to be monitored;
- the number of monitoring and surveillance stations;
- the locations of such stations;
- the equipment at such stations;
- quality control and quality assurance procedures; and
- a schedule for the construction and commencement of the
operation of the stations.
- Pollution Control Measures.
- The Parties, in cooperation with State and Provincial
Governments, shall develop, adopt and implement measures for the
control of the sources of emissions of toxic substances and the
elimination of the sources of emissions of persistent toxic
substances in cases where atmospheric deposition of these
substances, singly or in synergistic or additive combination
with other substances, significantly contributes to pollution of
the Great Lakes System. Where such contributions arise from
sources beyond the jurisdiction of the Parties, the Parties
shall notify the responsible jurisdiction and the Commission of
the problem and seek a suitable response.
- The Parties shall also assess and encourage the
development of pollution control technologies and alternative
products to reduce the effect of airborne toxic substances on
the Great Lakes System.
- Reporting. The Parties shall report their progress
in implementing this Annex to the Commission biennially,
commencing with a report no later than December 31, 1988.
ANNEX
16 - POLLUTION FROM CONTAMINATED GROUNDWATER
The Parties, in cooperation with State and Provincial
Governments, shall coordinate existing program to control
contaminated groundwater affecting the boundary waters of the
Great Lakes System. For this purpose, the Parties shall;
- identify existing and potential sources of contaminated
groundwater affecting the Great Lakes;
- map hydrogeological conditions in the vicinity of existing
and potential sources of contaminated groundwater;
- develop a standard approach and agreed procedures for
sampling and analysis of contaminants in groundwater in order to:
- assess and characterize the degree and extent of
contamination; and
- estimate the loadings of contaminants from groundwater to
the Lakes to support the development of Remedial Action Plans
and Lakewide Management Plans pursuant to Annex 2;
- control the sources of contamination of groundwater and the
contaminated groundwater itself, when the problem has been
identified; and
- report progress on implementing this Annex to the
Commission biennially, commencing with a report no later than
December 31, 1988.
ANNEX 17 - RESEARCH
AND DEVELOPMENT
- Purpose. This Annex delineates research need to
support the achievement of the goals of this Agreement.
- Implementation. The Parties, in cooperation with
State and Provincial Governments, shall conduct research in order
to:
- determine the mass transfer of pollutants between the
Great Lakes Basin Ecosystem components of water, sediments, air,
land and biota, and the processes controlling the transfer of
pollutants across the interfaces between these components in
accordance with Annexes 13, 14, 15 and 16;
- develop load reduction models for pollutants in the Great
Lakes System in accordance with the research requirements of
Annexes 2, 11, 12 and 13;
- determine the physical and transformational processes
affecting the delivery of pollutants by tributaries to the Great
Lakes in accordance with Annexes 2, 11, 12 and 13;
- determine cause-effect inter-relationships of
productivity and ecotoxicity, and identify future research needs
in accordance with Annexes 11, 12, 13 and 15;
- determine the relationship of contaminated sediments on
ecosystem health, in accordance with the research needs of
Annexes 2, 12 and 14;
- determine pollutant exchanges between the Areas of
Concern and the open lakes including cause-effect
inter-relationships among nutrients, productivity, sediments,
pollutants, biota and ecosystem health, and to develop in-situ
chemical, physical and biological remedial options in accordance
with Annexes 2, 12, 14 and sub-paragraph 1(f) of Annex 3;
- determine the aquatic effects of varying lake levels in
relation to pollution sources, particularly respecting the
conservation of wetlands and the fate and effects of pollutants
in the Great Lakes Basin Ecosystem in accordance with Annexes 2,
11, 12, 13, 15 and 16;
- determine the ecotoxicity and toxicity effects of
pollutants in the development of water quality objectives in
accordance with Annex 1;
- determine the impact of water quality and the
introduction of non-native species on fish and wildlife
populations and habitats in order to develop feasible options
for their recovery, restoration or enhancement in accordance
with sub-paragraph 1(a) of Article IV and Annexes 1, 2, 11 and
12;
- encourage the development of control technologies for
treatment of municipal and industrial effluents, atmospheric
emissions and the disposal of wastes, including wastes deposited
in landfills;
- develop action levels for contamination that incorporate
multi-media exposures and the interactive effects of chemicals;
and
- develop approaches to population-based studies to
determine the long-term, low-level effects of toxic substances
on human health.
TERMS OF
REFERENCE FOR THE JOINT INSTITUTIONS AND THE GREAT
LAKES
REGIONAL OFFICE
- Great Lakes Water Quality Board
- This Board shall be the principal advisor to the
International Joint Commission with regard to the exercise of
all the function, powers and responsibilities (other than those
functions and responsibilities of the Science Advisory Board
pursuant to paragraph 2 of these Terms of Reference) assigned to
the Commission under this Agreement. In addition, the Board
shall carry out such other functions, related to the water
quality of the boundary waters of the Great Lakes System, as the
Commission may request from time to time.
- The Water Quality Board, at the direction of the Commission,
shall:
- Make recommendations on the development and implementation
of programs to achieve the purpose of this Agreement;
- Assemble and evaluate information evolving from such
programs;
- Identify deficiencies in the scope and funding of such
programs and evaluate the adequacy and compatibility of
results;
- Examine the appropriateness of such programs in light of
present and future socio-economic imperatives; and
- Advise the Commission on the progress and effectiveness of
such programs and submit appropriate recommendations.
- The Water Quality Board, on behalf of the Commission, shall
undertake liaison and coordination between the institutions
established under this Agreement and other institutions and
jurisdictions which may address concerns relevant to the Great
Lakes Basin Ecosystem so as to ensure a comprehensive and
coordinated approach to planning and to the resolution of
problems, both current and anticipated.
- The Water Quality Board shall report to the Commission
periodically as appropriate, or as required by the Commission,
on all aspects relating to the operation and effectiveness of
this Agreement.
- Great Lakes Science Advisory Board
- This Board shall be the scientific advisor to the Commission
and the Water Quality Board.
- The Science Advisory Board shall be responsible for
developing recommendations on all matters related to research
and the development of scientific knowledge pertinent to the
identification, evaluation and resolution of current and
anticipated problems related to Great Lakes water quality.
- To effect these responsibilities the Science Advisory Board
shall;
- Review scientific information in order to:
- examine the impact and adequacy of research and the
reliability of research results, and ensure the
dissemination of such results;
- identify additional research requirements;
- identify specific research programs for which
international cooperation is desirable; and
- Advise jurisdictions of relevant research needs, solicit
their involvement and promote coordination.
- The Science Advisory Board shall seek analyses, assessments
and recommendations from other scientific, professional,
academic, governmental or intergovernmental relevant to Great
Lakes Basin Ecosystem research.
- The Science Advisory Board shall report to the Commission
and the Water Quality Board periodically as appropriate, or as
required by the Commission, on all matters of a scientific or
research nature relating to the operation and effectiveness of
this Agreement.
- The Great Lakes Regional Office
- This Office, located in Windsor, Ontario, shall assist the
Commission and the two Boards in the discharge of the functions
specified in subparagraph (b) below.
- The Office shall perform the following functions:
- Provide administrative support and technical assistance
for the Water Quality Board and the Science Advisory Board and
their sub-organizations, to assist the Boards in discharging
effectively the responsibilities, duties and functions
assigned to them.
- Provide a public information service for the programs,
including public hearings, undertaken by the Commission and
its Boards.
- The Office shall be headed by a Director who shall be
appointed by the Commission in consultation with the Parties and
with the Co-Chairmen of the Boards. The position of Director
shall alternate between a Canadian citizen and a United States
citizen. The term of office for the Director shall be determined
in the review referred to in subparagraph (d) below.
- The Parties, mindful of the need to staff the Great Lakes
Regional Office to carry out the functions assigned the
Commission by this Agreement, shall, within six months from the
date of entry into force of this Agreement, complete a review of
the staffing of the Office. This review shall be conducted by
the Parties based upon recommendations of the Commission after
consultation with the Co-Chairmen of the Boards. Subsequent
review may be requested by either Party, or recommended by the
Commission, in order to ensure that the staffing of the Regional
Office is maintained at a level and character commensurate with
its assigned functions.
- Consistent with the responsibilities assigned to the
Commission, and under the general supervision of the Water
Quality Board, the Director shall be responsible for the
management of the Regional Office and its staff in carrying out
the functions described herein.
- The Co-Chairmen of the Boards, in consultation with the
Director, will determine the activities which they wish the
Office to carry out on behalf of, or in support of the Boards,
within the current capability of the Office and its staff. The
Director is responsible to the Co-Chairmen of each Board for
activities carried out on behalf of, or in support of such
Board, by the Office or individual staff members.
- The Commission, in consultation with the Director, will
determine the public information activities to be carried out on
behalf of the Commission by the Regional Office.
- The Director shall be responsible for preparing an annual
budget to carry out the functions of the Boards and the Regional
Office for submission jointly by the two Boards to the
Commission for approval and procurement of resources.
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