IMPEL-TFS
Seaport Project Detects Hundreds of Illegal Waste Shipments;
Second Phase To Continue Through June 2006
By Nancy Isarin, VROM Project Manager. Email: nancy.isarin@minvrom.nl
Inspectors in the six seaports in Belgium, Germany,
United Kingdom, Poland, Latvia, and the Netherlands
participating in the IMPEL-TFS Seaport project carried
out nearly 50 inspections in the past year and discovered
more than 100 illegal shipments of hazardous waste.
In a period between September 2003 and March 2004,
inspectors checked 1,230 shipments, of which 508 contained
waste. Inspectors determined that 103 of those waste
shipments were illegal. For example, thousands of tons
of domestic waste were shipped illegally from Ireland
to India, hundreds of refrigerators containing CFC's
from Germany and France to Africa, electronic waste
from England to Pakistan and cable waste from the Netherlands
to China. In most of these cases, the required CCIC
certificates or other needed documents were not present
with the waste shipments.
The final report of the Seaport project was published
in June 2004 and was presented during the IMPEL-TFS
Meeting in Malta. In September 2004 it was presented
to the Director-General of the DG Environment of the
European Commission and representatives of all EU member
states.
The main aim of the seaport project was to stimulate
the joined enforcement of European waste shipment regulation
259/93 and to level enforcement pressures within the
member states. The project is carried out under the
umbrella of the European network IMPEL, specifically
the IMPEL cluster TFS (Transfrontier shipments). See
europa.eu.int/comm/environment/impel/
for more information.
For the operational phase of the seaport project, the
six participating authorities made agreements regarding
the inspection methods, number of inspections, priorities
of waste streams and destinations and the exchange of
information, inspectors, signals and experiences.
The outcomes of the project emphasized that cooperation
in enforcement of European waste shipment regulation
is needed to protect the environment. Illegal waste
shipments and infractions have been detected in almost
every inspection. The final report of the project also
gives an overview of involved enforcement structures.
The differences between these structures, such as differences
in available enforcement capacity, priority for transfrontier
waste shipments, legal powers and means, create possibilities
for companies to choose the line of the least resistance
for waste streams to be disposed of or exported. Furthermore,
a manual and standard forms for inspections were developed,
and experiences and information were exchanged. Cooperation
with other authorities, mainly with customs, has been
set up or further intensified.
To extend and improve international and national cooperation,
a European enforcement strategy for waste shipment regulation
is recommended. Due to the surplus value of this European
enforcement project, a second IMPEL-TFS Seaport project
will start in September 2004. Agreements for this second
project will be made during a start meeting in Latvia
from 13-15 September. To date, 12 member states are
participating: Ireland, United Kingdom, Sweden, the
Netherlands, Germany, Belgium, Poland, Latvia, Portugal,
Malta, and Spain. France will announce its decision
on whether to participate in early 2005. The second
Seaport project will conclude in June 2006.
Transition to Integrated
Permitting in Eastern Europe, Caucasus, and Central
Asia
By Krzysztof Michalak, Organization for Economic Cooperation
and Development. Email: Krzysztof.MICHALAK@oecd.org
Several countries in the region of Eastern Europe,
Caucasus, and Central Asia (EECCA) have expressed their
desire to progressively move toward an integrated environmental
permitting system for large industrial installations,
using as a benchmark the Integrated Pollution Prevention
and Control (IPPC) Directive of the European Union.
The development of Integrated Environmental Permitting
Guidelines for government agencies and industry is a
major part of the REPIN Secretariat's 2003-2006 work
programme adopted at the 5th annual meeting in October
2003 in Kiev, Ukraine.
As part of this programme, an expert meeting on the
Development of Integrated Environmental Permitting Guidelines
for EECCA region was held on 24-25 May 2004 at the OECD
Headquarters in Paris.
The meeting brought together EECCA and OECD environmental
policy-makers and experts to discuss the draft Guidelines
and issues related to reforming environmental permitting
systems in EECCA countries. The expert meeting reviewed
progress in the preparation of the Permitting Guidelines
since the REPIN meeting of October 2003 and discussed
the new draft of the Guidelines, particularly the recently
developed model application and permit forms with instructions.
The participants also discussed principal steps as part
of a strategy for gradual transition toward integrated
environmental permitting for large industry and the
role of the forthcoming Permitting Guidelines and other
related activities of the EAP Task Force Secretariat
in this process.
The participants broadly supported the development
of the Permitting Guidelines, which seek to assist EECCA
officials and experts to carry out environmental permitting
reforms. The Guidelines incorporate a model administrative
procedure for issuing an integrated permit and a model
permit application form and a model permit form with
user-friendly instructions. The report also provides
guidance on the combination of the Environmental Quality-Based
and Technique-Based approaches in Integrated Permitting
for Large Industrial Installations and on the setting
of emission limit values in permits. The guidelines
also present a strategy for the gradual transition to
integrated permitting for Large Industry as well as
Small and Medium Size Enterprises.
The development of these products is based on approaches
applied in the European Union and draws from experience
of the accession countries of Central Europe, but the
recommended approaches will be adapted to EECCA conditions.
The preparation of the Permitting Guidelines is supported
by projects in individual EECCA countries, including
Belarus and Ukraine. For more information on the Guidelines,
contact Eugene Mazur, OECD, e-mail: eugene.mazur@oecd.org.
OECD, REPIN Launch
Study On Meeting Costs of Regulatory Compliance
By Angela Bularga, OECD. Email: angela.bularga@oecd.org
Financing of environmental compliance assurance activities
is one of the key challenges faced by Environmental
Enforcement Agencies around the world. Even though enforcement,
as part of the application of the rule of law, is receiving
increasing attention, the resources available for compliance
assurance and compliance promotion efforts are inadequate
to achieve established objectives, even in the most
developed OECD countries.
The situation is much more difficult in transition
and developing economies where governments face serious
budgetary constraints and the inspectorates have to
scale down their operations due to lack of funds. At
the same time, in countries where economies start to
recover from economic depression or crisis, there are
strong pressures to reduce inspection activities as
part of deregulation and lifting barriers to investment.
In many countries, inspectors' operations have been
reduced to a minimum and in some cases compliance monitoring
systems have collapsed. Since a certain minimum level
of compliance assurance has to be maintained, enforcement
officials recognized an urgent need to work out effective
mechanisms for increasing funding for enforcement actions
ensuring, at the same time, that inspectors operations
are performed efficiently and effectively.
To address these concerns the OECD, in the context
of the work of the Regulatory Environmental Programme
Implementation Network (REPIN) in Eastern Europe, Caucasus,
and Central Asia, launched a study which reviews international
practice in assessing and meeting costs of regulatory
compliance assurance It discusses the challenges in
funding compliance assurance faced by environmental
enforcement authorities in OECD countries and in the
transition economies, as well as presents the results
of an analysis of the principles for funding enforcement
efforts.
The study describes the sources of funding and the
ways in which funds are allocated and managed. It also
presents approaches to address gaps in funding environmental
compliance assurance activities by effectively using
existing means and introducing innovative sources of
funding. One of the main issues discussed in the report
is whether the application of Polluter Pays and User
Pays principles implies that industry and beneficiaries
should pay inspectors for the costs of their activities.
Some countries accept Polluter Pays principle and inspectorates
require fees to be paid by industry for their operations.
However, the question arises over requiring administrative
costs to reflect actual or potential pollution (or other
impacts on the environment which can be difficult to
establish). Some countries argue that issuing permits
and inspections are part of the general costs of administration
so they have to be funded from the general budgets to
which companies contribute by paying taxes. It can even
be argued that the "users" in this regard
are the public and, therefore, general taxation (derived
from the public) is the most appropriate means to fund
regulatory authorities. The widespread requirement in
many countries for self-monitoring by industry (of emissions
and even of the ambient environment) is also often justified
by reference to the Polluter Pays principle, although
again the costs of such monitoring are not necessarily
a reflection on the levels of pollution caused.
The report discusses other principles which can be
applied to the funding of inspectors' work. They include
the precautionary principle, the principle of preventative
action - used to differing extents in the development
in environmental legislation, and other related approaches
such as the full cost accounting and performance-oriented
budgeting approaches/principles. The latter is only
possible through proper assessments of the delivery
of objectives, targeting budget provision to priority
areas based on efficiency assessments of those work
areas.
Prevention of conflicts of interest is another concept
discussed in the report. While some countries charge
installations for the cost of inspection activities,
others do not, on the grounds that this may lead to
a conflict of interest. It is clear that some inspectors
may feel uncomfortable with the idea of being paid by
the company that they are inspecting. They could feel
obliged to provide results that are acceptable to the
company and reliance on income from the company could
result in a reticence to take severe enforcement action
(e.g. seeking closure) which would then result in loss
of income for the inspectorate. Some countries get around
this by not levying inspection charges directly, but
having this as part of permit fees, and some make the
distinction between inspection costs per se, and the
specific associated costs of testing, monitoring, and
laboratory services which they do charge for even if
no direct charge is in place for the inspection.
The report, however, does not attempt to cover all
issues for all countries; rather it focuses on examples
and insights that were readily obtainable. Overall,
the report offers case examples and insights that may
be of interest and relevance to the inspectorates/enforcement
agencies in many countries. It looks at the existing
funding patterns of environmental inspectorates in light
of their responsibilities, to what they allocate funds,
and looks at how funding gaps are assessed and addressed.
On the latter point the report looks at approaches for
raising the efficiency of compliance assurance programmes,
reducing demand (e.g. through redistribution of burdens,
out-sourcing), increasing synergies with other authorities
and programmes, and developing revenue sources. For
more information about the findings of the report, contact
Angela Bularga, OECD, e-mail: angela.bularga@oecd.org.
Basel Convention
Compliance Mechanism
By Constanza Martinez, Environmental Law Consultant,
UNEP. Email: Constanza.MARTINEZ@unep.ch
Nearly two years after adopting the Compliance Mechanism
for Promoting Implementation and Compliance with the
Basel Convention, the seventh meeting of the Conference
of the Parties of the Basel Convention in October 2004
will provide attendees an opportunity to assess the
new mechanism.
After more than three years of negotiations, the Conference
of the Parties of the Basel Convention (COP) adopted
the Compliance Mechanism for Promoting Implementation
and Compliance with the Basel Convention at its sixth
meeting held in Geneva in December 2002.
After much debate, the Parties agreed that the mechanism
would aim to assist them to "comply with their
obligations under the Convention and to facilitate,
promote, monitor and aim to secure the implementation
of and compliance with the obligations under the Convention."
The mechanism is "non-confrontational, transparent,
cost-effective and preventive in nature, simple, flexible,
non-binding."
A Compliance Committee comprised of 15 members nominated
and elected at the COP will administer the mechanism.
The Committee will reflect an equitable geographic distribution,
with five members (one from each region) elected for
one term, and ten members (two from each region) elected
for two terms. The mechanism seeks to ensure compliance
through several means. Parties unable to comply with
the terms of the Convention may request assistance from
the committee. The Secretariat, or parties who are affected
by the noncompliance of a third party, may also refer
to the Committee for assistance.
Before referring to the Committee, the Secretariat
or a Party preparing a submission about a third Party
must consult with that Party.
Through the mechanism's Facilitating Procedure, the
committee can provide the Party facing compliance difficulties
with different types of assistance, such as nonbinding
recommendations and information on strengthening regulatory
regimes, financial and technical assistance, compliance
action plans, or help with reporting arrangements. The
committee can, under Paragraph 12, also make recommendations
to the COP.
After arduous negotiations on submission of information
to the Committee by entities other than the Parties
and the Secretariat, it was agreed that "a Party
may also consider and use relevant and appropriate information
provided by civil society on compliance difficulties."
(Paragraph 17)
The Basel Convention Compliance Mechanism was adopted
following a compromise between those countries aiming
for a strong system with some monitoring and enforcement
power and those interested in a mechanism that would
respond to specific needs of Parties, particularly of
developing countries, to increase capacity for implementing
the obligations under the Basel Convention.
The nature and scope of the submissions to the Committee
will shape the mechanism, particularly those submitted
at an early stage, as they will set the precedent on
which approach to take with future cases of non-compliance.
At the occasion of the seventh meeting of the COP,
Parties to the Convention will to appoint the members
of the Committee that serve for only one term. In addition,
the Committee will submit a report on its activities
to the COP.
Parties may come to the meeting prepared to discuss
specific cases or, more likely, to endorse proposals
for a wide mandate to carry out activities that would
increase the capacity of developing countries to implement
the convention and to fulfill the reporting requirement.
The text of the Mechanism for Promoting Implementation
and Compliance with the Basel Convention and other related
documents can be found in the following Web site: www.basel.int.
Dutch Environment Agency
Develops New Approach To Manage Abandoned Industrial
Sites
The Environmental Inspectorate of the Netherlands has
developed a structured approach to managing the environmental
risks caused by abandoned industrial sites that has
worked well in the Netherlands and can be applied by
local or regional authorities in other countries.
The Environmental Inspectorate identified 69 potentially
hazardous sites in the Netherlands in 2003, and visited
and assessed 47 of them. Of these 47, there were 7 sites
classified as high risk and 7 as medium risk. By the
fall of 2004, remedial measures have been taken at 5
of these sites.
The risk to the environment stems largely from hazardous
materials that remain on industrial sites after they
have been abandoned that can leak from the aging and
deteriorating storage containers. Abandoned sites are
also targeted for illegal dumping of hazardous waste
by third parties. Aging infrastructure can also pose
risks as buildings begin to decay and possibly collapse
or catch fire. This is particularly dangerous when the
site is not adequately fenced off, as these areas can
attract children.
The Environmental Inspectorate's approach consists
of three steps: (1) to identify all potentially hazardous
sites; (2) conduct site visits and risk assessments;
and (3) perform remedial measures at sites classified
as high risk.
For the first step, the Environmental Inspectorate
used local permit records, agency data on historic buildings,
industrial consultants, local media, and direct surveys
of selected industrial areas. In the northern areas
of the Netherlands, the Environmental Inspectorate was
able to find several factories that produced potato
starch, strawboard, and dairy products that had been
inactive since the 1960s.
Sites are classified as high risk when there is widespread
contamination in and around buildings or when the structural
integrity is severely affected, and when public safety
or health is directly at risk. All sites classified
as high or medium risk require appropriate follow up.
In performing remedial measures, specialists make detailed
assessments of the contamination, danger of structural
collapse, and fire safety. If appropriate, samples are
taken for more detailed analysis.
Where possible, the last owner/operator of the abandoned
site will be forced to pay for any clean up. In cases
where the last owner/operator is bankrupt or does not
have the resources to pay for a clean up, the local
authorities must pay for the clean up themselves, though
in some cases they can apply for redevelopment or conservation
funding.
For more information, please contact Kees Huizinga
kees.huizinga@minvrom.nl
or Henk Ruessink henk.ruessink@minvrom.nl.
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