INFORMATION KIT
STOCKHOLM 2001
CONFERENCE OF
PLENIPOTENTIARIES FOR THE STOCKHOLM CONVENTION ON PERSISTENT
ORGANIC POLLUTANTS
22 to 23 May 2001 Stockholm, Sweden
Contents
Produced by UNEP
Chemicals and UNEPs Information Unit for Conventions.
For use of the media only;
not an official document.
PRESS
RELEASE
Governments finalize
Persistent Organic Pollutants treaty
Johannesburg,
10 December 2000 Diplomats from 122 countries have finalized the text of a legally
binding treaty that will require governments to minimize and eliminate some of the most
toxic chemicals ever created.
Persistent
organic pollutants threaten the health and well-being of humans and wildlife in every
region of the world, said John Buccini, the
Canadian government official who chaired the talks. This new treaty will protect
present and future generations from the cancers, birth defects, and other tragedies caused
by POPs.
Executive Director Klaus
Töpfer of the United Nations Environment Programme, which organized the negotiations,
applauded the strong international regime that has been established for promoting global
action on POPs.
This is a sound and
effective treaty that can be updated and expanded over the coming decades to maintain the
best possible protection against POPs, he said.
The treaty sets out
control measures covering the production, import, export, disposal, and use of POPs.
Governments are to promote the best available technologies and practices for replacing
existing POPs while preventing the development of new POPs. They will draw up national
legislation and develop action plans for carrying out their commitments.
The control measures will
apply to an initial list of 12 chemicals. A POPs Review Committee will consider additional
candidates for the POPs list on a regular basis. This will ensure that the treaty remains
dynamic and responsive to new scientific findings.
A financial
mechanism will help developing countries and countries with economies in
transition meet their obligations to minimize and eliminate POPs. New and
additional funding and technical assistance will be provided.
Most
of the 12 chemicals are subject to an immediate ban. However, a health-related exemption
has been granted for DDT, which is still needed in many countries to control malarial
mosquitoes. This will permit governments to protect their citizens from malaria a
major killer in many tropical regions until they are able to replace DDT with
chemical and non-chemical alternatives that are cost-effective and environmentally
friendly.
Similarly, in the case of
PCBs, which have been widely used in electrical transformers and other equipment,
governments may maintain existing equipment in a way that prevents leaks until 2025 to
give them time to arrange for PCB-free replacements. Although PCBs are no longer produced,
hundreds of thousands of tons are still in use in such equipment. In addition, a number of
country-specific and time-limited exemptions have been agreed for other chemicals.
Governments agree to
reduce releases of furans and dioxins, which are accidental by-products and thus more
difficult to control, with the goal of their continuing minimization and, where
feasible, ultimate elimination.
Other national measures
required under the treaty relate to reporting, research, development, monitoring, public
information and education.
The meeting in
Johannesburg was the fifth and final POPs negotiating session and was attended by some 600
participants. The treaty will be formally adopted and signed by ministers and other
plenipotentiaries at a Diplomatic Conference in Stockholm on 22 23 May 2001.
Governments must then ratify, and when 50 have done so the treaty will enter into force;
this process normally takes several years.
Of all the pollutants released into the environment every year by human activity,
POPs are among the most dangerous. They are highly toxic, causing an array of adverse
effects, notably death, disease, and birth defects, among humans and animals. Specific
effects can include cancer, allergies and hypersensitivity, damage to the central and
peripheral nervous systems, reproductive disorders, and disruption of the immune system.
These highly stable
compounds can last for years or decades before breaking down. They circulate globally
through a process known as the "grasshopper effect". POPs released in one part
of the world can, through a repeated (and often seasonal) process of evaporation, deposit,
evaporation, deposit, be transported through the atmosphere to regions far away from the
original source.
In
addition, POPs concentrate in living organisms through another process called
bioaccumulation. Though not soluble in water, POPs are readily absorbed in fatty tissue,
where concentrations can become magnified by up to 70,000 times the background levels.
Fish, predatory birds, mammals, and humans are high up the food chain and so absorb the
greatest concentrations. When they travel, the POPs travel with them. As a result of these
two processes, POPs can be found in people and animals living in regions such as the
Arctic, thousands of kilometers from any major POPs source.
Fortunately, there are
alternatives to most POPs. The problem is that high costs, a lack of public awareness, and
the absence of appropriate infrastructure and technology often prevent their adoption.
Solutions must be tailored to the specific properties and uses of each chemical, as well
as to each country's climatic and socio-economic conditions.
The 12 initial POPs include eight pesticides (aldrin, chlordane, DDT, dieldrin,
endrin, heptachlor, mirex, and toxaphene), two industrial chemicals (PCBs and
hexachlorobenzene, which is also a pesticide), and two unwanted by-products of combustion
and industrial processes (dioxins and furans).
Note to journalists: For
more information, please contact Michael Williams in Johannesburg (GMT + 2 hours) on
Sunday until 13h at +27-11-508-1559 and during the afternoon at +41-79-409-1528, or in
Geneva from Tuesday a.m. at +41-22-917-8242, or Michael.williams@unep.ch. See also www.chem.unep.ch/pops/
POPs are organic chemical
substances, that is, they are carbon-based. They
possess a particular combination of physical and chemical properties such that, once
released into the environment, they:
As a result of releases to
the environment over the past several decades due especially to human activities, POPs are
now widely distributed over large regions (including
those where POPs have never been used) and, in some cases, they are found around
the globe. This extensive contamination of
environmental media and living organisms includes many foodstuffs and has resulted in the
sustained exposure of many species, including humans, for periods of time that span
generations, resulting in both acute and chronic toxic
effects.
Twelve specific POPs have
been recognized as causing adverse effects on humans and the ecosystem and these can be
placed in 3 categories:
Specific effects
can include cancer, allergies and hypersensitivity, damage to the central and peripheral
nervous systems, reproductive disorders, and disruption of the immune system. Some POPs
are also considered to be endocrine disrupters, which, by altering the hormonal system,
can damage the reproductive and immune systems of exposed individuals as well as their
offspring; they can also have developmental and carcinogenic effects.
In addition, POPs
concentrate in living organisms through another process called bioaccumulation. Though not
soluble in water, POPs are readily absorbed in fatty tissue, where concentrations can
become magnified by up to 70,000 times the background levels. Fish, predatory birds,
mammals, and humans are high up the food chain and so absorb the greatest concentrations.
When they travel, the POPs travel with them. As a result of these two processes, POPs can
be found in people and animals living in regions such as the Arctic, thousands of
kilometers from any major POPs source.
* Aldrin A pesticide applied to
soils to kill termites, grasshoppers, corn rootworm, and other insect pests, aldrin can
also kill birds, fish, and humans. In one incident, aldrin-treated rice is believed to
have killed hundreds of shorebirds, waterfowl, and passerines along the Texas Gulf Coast
when these birds either ate animals that had eaten the rice or ate the rice themselves. In
humans, the fatal dose for an adult male is estimated to be about five grams. Humans are
mostly exposed to aldrin through dairy products and animal meats. Studies in India
indicate that the average daily intake of aldrin and its byproduct dieldrin (see below) is
about 19 micrograms per person. The use of aldrin has been banned or severely restricted
in many countries.
* Chlordane
Used extensively to control termites and as a broad-spectrum insecticide on a range of
agricultural crops, chlordane remains in the soil for a long time and has a reported
half-life of one year. The lethal effects of chlordane on fish and birds vary according to
the species, but tests have shown that it can kill mallard ducks, bobwhite quail, and pink
shrimp. Chlordane may affect the human immune system and is classified as a possible human
carcinogen. It is believed that human exposure occurs mainly through the air, and
chlordane has been detected in the indoor air of residences in the US and Japan. Chlordane
is either banned or severely restricted in dozens of countries.
* DDT Perhaps the most
infamous of the POPs, DDT was widely used during World War II to protect soldiers and
civilians from malaria, typhus, and other diseases spread by insects. After the war, DDT
continued to be used to control disease, and it was sprayed on a variety of agricultural
crops, especially cotton. DDT continues to be applied against mosquitoes in several
countries to control malaria. Its stability, its persistence (as much as 50% can remain in
the soil 10-15 years after application), and its widespread use have meant that DDT
residues can be found everywhere; residual DDT has even been detected in the Arctic.
Perhaps the best
known toxic effect of DDT is egg-shell thinning among birds, especially birds of prey. Its
impact on bird populations led to bans in many countries during the 1970s. Thirty-four
countries have banned DDT, while 34 others severely restrict its use. Nonetheless, it has
been detected in food from all over the world. Although residues in domestic animals have
declined steadily over the last two decades, food-borne DDT remains the greatest source of
exposure for the general population. The short-term acute effects of DDT on humans are
limited, but long-term exposures have been associated with chronic health effects. DDT has
been detected in breast milk, raising serious concerns about infant health.
* Dieldrin Used principally
to control termites and textile pests, dieldrin has also been used to control insect-borne
diseases and insects living in agricultural soils. Its half-life in soil is approximately
five years. The pesticide aldrin rapidly converts to dieldrin, so concentrations of
dieldrin in the environment are higher than dieldrin use alone would indicate. Dieldrin is
highly toxic to fish and other aquatic animals, particularly frogs, whose embryos can
develop spinal deformities after exposure to low levels. Dieldrin residues have been found
in air, water, soil, fish, birds, and mammals, including humans. Food represents the
primary source of exposure to the general population. For example, dieldrin was the second
most common pesticide detected in a US survey of pasteurized milk.
* Dioxins
These chemicals are produced unintentionally due to incomplete combustion, as well during
the manufacture of pesticides and other chlorinated substances. They are emitted mostly
from the burning of hospital waste, municipal waste, and hazardous waste, and also from
automobile emissions, peat, coal, and wood. There are 75 different dioxins, of which seven
are considered to be of concern. One type of dioxin was found to be present in the soil 10
- 12 years after the first exposure. Dioxins have been associated with a number of adverse
effects in humans, including immune and enzyme disorders and chloracne, and they are
classified as possible human carcinogens. Laboratory animals given dioxins suffered a
variety of effects, including an increase in birth defects and stillbirths. Fish exposed
to these substances died shortly after the exposure ended. Food (particularly from
animals) is the major source of exposure for humans.
* Endrin This insecticide is
sprayed on the leaves of crops such as cotton and grains. It is also used to control
rodents such as mice and voles. Animals can metabolize endrin, so it does not accumulate
in their fatty tissue to the extent that structurally similar chemicals do. It has a long
half-life, however, persisting in the soil for up to 12 years. In addition, endrin is
highly toxic to fish. When exposed to high levels of endrin in the water, sheepshead
minnows hatched early and died by the ninth day of their exposure. The primary route of
exposure for the general human population is through food, although current dietary intake
estimates are below the limits deemed safe by world health authorities.
* Furans These compounds are
produced unintentionally from many of the same processes that produce dioxins, and also
during the production of PCBs (see below). They have been detected in emissions from waste
incinerators and automobiles. Furans are structurally similar to dioxins and share many of
their toxic effects. There are 135 different types, and their toxicity varies. Furans
persist in the environment for long periods, and are classified as possible human
carcinogens. Food, particularly animal products, is the major source of exposure for
humans. Furans have also been detected in breast-fed infants.
* Heptachlor
Primarily
used to kill soil insects and termites, heptachlor has also been used more widely to kill
cotton insects, grasshoppers, other crop pests, and malaria-carrying mosquitoes. It is
believed to be responsible for the decline of several wild bird populations, including
Canadian Geese and American Kestrels in the Columbia River basin in the US. The geese died
after eating seeds treated with levels of heptachlor lower than the usage levels
recommended by the manufacturer, indicating that even responsible use of heptachlor may
kill wildlife. Laboratory tests have also shown high doses of heptachlor to be fatal to
mink, rats, and rabbits, with lower doses causing adverse behavioral changes and reduced
reproductive success. Heptachlor is classified as a possible human carcinogen, and some
two dozen countries have either banned it or severely restricted its use. Food is the
major source of exposure for humans, and residues have been detected in the blood of
cattle from the US and from Australia.
* Hexachlorobenzene
(HCB) First introduced in 1945 to treat seeds, HCB kills fungi that affect food
crops. It was widely used to control wheat bunt. It is also a byproduct of the manufacture
of certain industrial chemicals and exists as an impurity in several pesticide
formulations. When people in eastern Turkey ate HCB-treated seed grain between 1954 and
1959, they developed a variety of symptoms, including photosensitive skin lesions, colic,
and debilitation; several thousand developed a metabolic disorder called porphyria
turcica, and 14% died. Mothers also passed HCB to their infants through the placenta and
through breast milk. In high doses, HCB is lethal to some animals and, at lower levels,
adversely affects their reproductive success. HCB has been found in food of all types. A
study of Spanish meat found HCB present in all samples. In India, the estimated average
daily intake of HCB is 0.13 micrograms per kilogram of body weight.
* Mirex This insecticide is used
mainly to combat fire ants, and it has been used against other types of ants and termites.
It has also been used as a fire retardant in plastics, rubber, and electrical goods.
Direct exposure to mirex does not appear to cause injury to humans, but studies on
laboratory animals have caused it to be classified as a possible human carcinogen. In
studies mirex proved toxic to several plant species and to fish and crustaceans. It is
considered to be one of the most stable and persistent pesticides, with a half life of up
to 10 years. The main route of human exposure to mirex is through food, particularly meat,
fish, and wild game.
*
Polychlorinated Biphenyls (PCBs) These compounds are used
in industry as heat exchange fluids, in electric transformers and capacitors, and as
additives in paint, carbonless copy paper, and plastics. Of the 209 different types of
PCBs, 13 exhibit a dioxin-like toxicity. Their persistence in the environment corresponds
to the degree of chlorination, and half-lives can vary from 10 days to one-and-a-half
years. PCBs are toxic to fish, killing them at higher doses and causing spawning failures
at lower doses. Research also links PCBs to reproductive failure and suppression of the
immune system in various wild animals, such as seals and mink.
Large numbers of
people have been exposed to PCBs through food contamination. Consumption of
PCB-contaminated rice oil in Japan in 1968 and in Taiwan in 1979 caused pigmentation of
nails and mucous membranes and swelling of the eyelids, along with fatigue, nausea, and
vomiting. Due to the persistence of PCBs in their mothers' bodies, children born up to
seven years after the Taiwan incident showed developmental delays and behavioral problems.
Similarly, children of mothers who ate large amounts of contaminated fish from Lake
Michigan showed poorer short-term memory function. PCBs also suppress the human immune
system and are listed as probable human carcinogens.
* Toxaphene
This insecticide is used on cotton, cereal grains, fruits, nuts, and vegetables. It has
also been used to control ticks and mites in livestock. Toxaphene was the most widely used
pesticide in the US in 1975. Up to 50% of a toxaphene release can persist in the soil for
up to 12 years. For humans, the most likely source of toxaphene exposure is food. While
the toxicity to humans of direct exposure is not high, toxaphene has been listed as a
possible human carcinogen due to its effects on laboratory animals. It is highly toxic to
fish; brook trout exposed to toxaphene for 90 days experienced a 46% reduction in weight
and reduced egg viability, and long-term exposure to levels of 0.5 micrograms per liter of
water reduced egg viability to zero. Thirty-seven countries have banned toxaphene, and 11
others have severely restricted its use.
THE INTERNATIONAL
COMMUNITY'S RESPONSE TO POPs
Over
the past few decades, as the risks posed by POPs became of increasing concern in many
countries, various actions to protect human health and the environment have been taken at
the national, regional and international levels.
More than three
decades ago, Rachel Carsons "Silent Spring" highlighted the risks of DDT
and other pesticides by evoking the haunting image of a springtime without birds. The
resulting media attention led to legal action by several countries to ban or severely
restrict the use of DDT in the early 1970s. Governments moved to ban or restrict other
chemical compounds as well in response to growing scientific evidence that they too were
toxic to humans and animals.
Since then, many
countries have adopted national legislation to regulate the production and use of
hazardous chemicals. However, because POPs circulate globally, no country acting alone can
protect its citizens or its environment from them. United action by the international
community is essential.
Fortunately, there
are alternatives to most POPs. The problem is that high costs, a lack of public awareness,
and the absence of appropriate infrastructure and technology often prevent their adoption.
Therefore, to minimize the need for using POPs, the international community will have to
exploit all the tools at its disposal, including education, incentives, regulations, and,
when necessary, bans.
Solutions must be
tailored to the specific properties and uses of each chemical, as well as to each
country's climatic and socio-economic conditions. But action must be taken quickly: the
persistence of these chemicals in water and soil and their accumulation in living tissue
means that each year that passes without a solution will result in decades of additional
exposures.
In 1992,
governments met at the Rio Earth Summit and adopted Agenda 21, which includes Chapter 19
on the "Environmentally Sound Management of Toxic Chemicals Including Prevention of
Illegal International Traffic in Toxic and Dangerous Products". This chapter called
for the creation of an Intergovernmental Forum on Chemical Safety (IFCS) to promote the
coordination of international work on chemicals. Since being established in 1994, the IFCS
has provided policy guidance and strategies for harmonizing risk assessment methods and
chemical classification. It has also contributed to strengthening information exchange,
risk reduction, chemicals management capacity-building, and so forth.
Meanwhile, the
Inter-Organization Programme on the Sound Management of Chemicals (IOMC) was established
to promote coordination among international organizations involved in implementing Chapter 19 of Agenda 21. The IOMCs current
membership includes UNEP, ILO, FAO, WHO, the UN Industrial Development Organization
(UNIDO), the UN Institute for Training and Research (UNITAR), and the OECD.
Steps to regulate
international trade in hazardous chemicals started with the FAOs International Code
of Conduct on the Distribution and Use of Pesticides (as amended in 1989) and UNEPs
London Guidelines for the Exchange of Information on Chemicals in International Trade
(amended 1989). Together, these instruments led to the creation of the voluntary Prior
Informed Consent (PIC) Procedure, which is jointly administered by FAO and UNEP.
The Prior Informed
Consent (PIC) procedure is a means for formally obtaining and disseminating the decisions
of importing countries as to whether they wish to receive future shipments of a certain
chemical and for ensuring compliance to these decisions by exporting countries. The aim is
to promote a shared responsibility between exporting and importing countries in protecting
human health and the environment from the harmful effects of such chemicals. The voluntary
PIC procedure has covered 22 pesticides and five industrial chemicals among which
are seven of the 12 POPs.
The voluntary PIC
system has worked well, and 154 countries have participated in the procedure. By the
mid-1990s, however, governments saw the need for a legally binding treaty to govern trade
in these hazardous chemicals. Treaty negotiations began in 1996 and the Convention on the
Prior Informed Consent Procedure for Certain Hazardous Chemicals and Pesticides in
International Trade was adopted and signed at a Conference of Plenipotentiaries in
Rotterdam on 10 - 11 September. To date 13 countries have ratified the Rotterdam
Convention.
In May 1995,
UNEPs Governing Council called for an international assessment of the 12 recognized
POPs (Decision 18/32). In response, the Inter-Organization Programme on the Sound
Management of Chemicals summarized the scientific literature on POPs and consolidated the
available information on their chemistry, toxicity, environmental dispersion, and other
relevant properties and established an UNEP/IFCS ad hoc Working Group on POPs.
The
Intergovernmental Forum on Chemical Safety concluded in June 1996 that there was
sufficient evidence that international action including a global legally binding
instrument was needed to reduce the risks posed by POPs to human health and the
environment. These recommendations were forwarded to UNEPs Governing Council and
WHOs World Health Assembly.
In February 1997, at the
Governing Council of UNEP (and later in May at the World Health Assembly of the WHO),
governments agreed:
It also called for
work on developing and sharing information; evaluating and monitoring response strategies;
determining alternatives to POPs; identifying and inventorying PCBs; quantifying the
available capacity for incinerating or destroying unwanted stocks; and identifying sources
of dioxin and furan emissions.
The negotiations
of the UNEP POPs convention began in Montreal on June 29, 1998, and after a total of five
sessions, concluded on December 10, 2000 in Johannesburg. The sessions were held as
follows; the first in Montreal, Canada, 29 June to 3 July 1998, the second in Nairobi,
25-29 January 1999, the third in Geneva, 6-11 September 1999, the fourth in Bonn, Germany,
20-25 March 2000 and the fifth and final in Johannesburg, South Africa, 4-9 December 2000.
In Johannesburg countries agreed on the text of the convention and they also agreed to
name it the Stockholm Convention on POPs.
Below are some highlights
of what will be known as the Stockholm POPs Convention.
The main provisions of the Convention may be briefly summarized under four
headings:
1)
Control Provisions:
·
the
goal for all is the elimination of production and use
·
country-specific
exemptions for eight of the 10 have been identified
·
countries
have until the opening of the Conference of Plenipotentiaries in Stockholm to
amend the list
·
the
Secretariat will keep a public register for all country-specific exemptions
·
a
country-specific exemption may be withdrawn by a Party at any time
·
an
exemption is valid for five years
·
the
COP will review a request for renewing an exemption
·
Parties
with exemptions shall take measures to prevent or minimize human exposure and
releases to the environment
·
When
all countries have withdrawn their exemptions for a specific substance, the
Conference of the Parties may delete that exemption from the Annex.
For PCBs:
·
all
Parties have agreed to cease production
·
the
use of in-place equipment is exempted for all Parties, with conditions
·
the
intent is to phase equipment out by 2025
·
no
trade is allowed in PCB equipment, except for the purpose of environmentally sound
waste management
·
Parties
should establish environmentally sound management of PCB wastes as soon as
possible, and at the latest by 2028
·
Parties
should report on their activities every five years, and the Conference of the Parties
should review progress at five-year intervals
With regard to DDT:
·
a
special regime is included, involving Acceptable Purposes
·
production
or use is only allowed to meet requirements for disease vector control
programs according to WHO guidelines (malaria, etc.)
·
the
Secretariat will keep a specific public register that will identify Parties that use DDT
·
registered
Parties will report every three years on use, etc.
·
registered
Parties should develop national action plans, including measures to reduce
reliance on DDT
·
all
Parties should seek alternatives to DDT for the purposes of vector control
·
the
Conference of the Parties will review the situation every three years to ascertain
whether there is a continued need for DDT use
·
specific
exemptions are also allowed, but there are only two of these (related to
intermediate use of DDT in the manufacturing
of other substances)
Trade in the ten
intentionally produced POPs will be restricted as
follows:
·
In
general, imports and exports are limited to
°
the
environmentally sound disposal of the substances
°
Parties
with specific exemptions or acceptable purposes
·
Exports to non-Parties may take place, but with conditions and accountability
·
take
measures to regulate, with the aim of preventing, the production and use of
new
POPs (N.B. Precautionary measure)
·
consider
the screening criteria for candidates for addition to the Convention in conducting
assessments of in-use substances.
·
the
goal is to reduce the total releases from anthropogenic sources to achieve
continuing
minimization and, where feasible, ultimate elimination
·
Parties
are to develop action plans within two years of entry into force of Convention and
also to implement the plan, which should inter alia contain actions to:
°
evaluate
current and projected releases (source inventories, release estimates)
°
evaluate
efficacy of laws and policies to manage such releases
°
develop
strategies, and promote education and training on them
°
review
success of strategies every five years and report to the COP
°
develop
schedule for implementation of action plan
·
promote
measures to achieve realistic and meaningful level of release reduction or source
elimination
·
promote
the development and, where appropriate, require the use of substitute or
modified materials, products and processes to prevent the formation and release of
by-
product POPs
·
promote,
and as provided for in an action plan, require the use of Best Available
Technology (BAT) for new sources within specified source categories in (Part II of)
Annex C, and phase in BAT requirements for new sources in Part II of Annex C within
four years of the entry into force of the Convention for a Party
·
for
identified new source categories, Parties shall promote the use of Best Environmental
Practice (BEP)
·
promote
the use of BAT and BEP for existing sources within identified source categories
and for new sources which are not otherwise addressed
·
the
COP will develop guidance on BAT and BEP
For POPs in stockpiles and wastes, the goal is to ensure the sound management of stockpiles, wastes, products and articles upon becoming wastes that consist of, contain or are contaminated by POPs. To this end Parties shall:
·
develop
and implement strategies to identify the stockpiles, products and articles
containing POPs
·
manage
stockpiles in a safe, efficient and environmentally sound manner until they are
deemed to be wastes
·
take
measures to handle, collect, transport and store wastes in an ESM, and dispose of in
a way that destroys the POP content, or otherwise in an ESM taking into account
international rules, standards and guidelines.
·
not
allow recovery, recycle, reclamation, direct reuse or alternative uses of POPs
·
not
transport across international boundaries without taking into account international
rules, etc (e.g. Basel Convention)
·
develop
strategies for identifying contaminated sites and if remediation is attempted, do
in an ESM
Parties must develop an
action plan within two years, involve all relevant stakeholders in doing so, and endeavour
to implement, review and update the plan on a periodic basis.
Parties shall designate a
National Focal Point to permit the exchange of information on production, use and release
of POPs and on alternatives to POPs.
Parties shall promote and
facilitate:
·
awareness
among policy- and decision-makers on POPs
·
provision
of up-to-date information to the public
·
development
of educational and public awareness programs
·
public
participation in addressing POPs
·
training
and development programs for all stakeholders
Parties shall encourage
and/or undertake research, development, monitoring and cooperation on all aspects of POPs,
including aspects relating to their environmental releases, presence, transformation,
effects, socio-economic impacts, and release reduction and/or elimination.
In
the future, the COP will evaluate the effectiveness of the Convention in reducing and/or
eliminating the releases of POPs by establishing a mechanism to acquire monitoring data on
POPs using available scientific information. This
mechanism will tap into existing networks and sources of information to achieve this, and
will be addressed in the future by the first COP.
The POPs convention will be
a living instrument and provision has been made for addition of new POPs through
application of scientific criteria and an agreed process for evaluation of candidates that
will be nominated in the future. Criteria include:
·
persistence in different media with
numerical cut-off values
·
bioaccumulation in organisms with
numerical cut-off values
·
potential for long-range
environmental transport
·
adverse effects
The proposing Party shall
also provide a statement of the reasons for concern. The process for the evaluation of
candidates proceeds in several steps and incorporates precaution in a number of ways to
ensure that all possible candidate POPs are thoroughly considered and evaluated on the
basis of available scientific data to see if they possess the properties that would
indicate POPs behaviour to a degree sufficient to warrant inclusion in the treaty. A POPs Review Committee will be set up to advise
the COP on the application of the criteria and process and there are safeguards in the
process to ensure that all Parties have the opportunity to get a full hearing on any
nominated candidate.
One
of the key features of the Convention reflects the recognition that developing countries
and countries with economies in transition will need technical and financial assistance in
order to meet their obligations as Parties to the Convention. The developed countries have undertaken to provide
technical assistance and new and additional financial resources to meet these needs, and
the Global Environment Facility has been named as an interim financial mechanism to handle
the funding of capacity building and other related activities.
The
next step is the Conference of Plenipotentiaries for the Stockholm Convention on POPs.
Countries will have the opportunity to adopt and sign the convention. When 50 countries
have ratified the convention, it will come into force.
Based on past conventions, this is not expected to occur before 2004 or 2005.
However,
that does not mean that action on POPs will not take place for another three or four
years: far from it! The process of
negotiation has stimulated wide spread interest and concern about the effects of POPs and
much action has already taken place. UNEP has
developed a master list of actions that reports that over 108 countries have already taken
or are taking action of some sort of action on POPs.
During the negotiation process, environmental groups established an International
POPs Elimination Network (IPEN) that has now grown to include over 300 ENGOs, and
they are promoting action on POPs around the world.
There will also be a number of resolutions on interim measures and arrangements for consideration and adoption by the Conference of Plenipotentiaries. These resolutions will set the stage for activities that will take place between the Stockholm Conference and the first COP. It is foreseen that the INC will continue to meet to review interim activities and to prepare for the first COP. Governments are also encouraged to implement the obligations under the convention on a voluntary basis.
THE POPs NEGOTIATIONS: A
GLOSSARY
This glossary contains some of the most
common acronyms and jargon that has been used throughout the negotiations and which are
likely to be encountered in Stockholm.
I) The Players
II) The action (meetings, documents,
process)
III) The issues