| 1.The Coastal Zone
1.1 Description of the coastal zone
1.2 Definition of the coastal zone
1.3 Setback lines policy
2. Coastal Management
2.1 Authority
2.2 Policy
2.3 Legislation
3. Spatial Planning in the Coastal Zone
3.1 Authority
3.2 Policy
3.3 Legislation
4. Coastal and Marine Environmental Policy
5. Coastal and Marine Nature Conservation Policy
5.1 Authority
5.2 Policy
5.3 Legislation
6. Economic Developments, Important Sectors and Trends
6.1 Recreation and tourism
6.2 Coastal defence
7. The Current State of Integrated Coastal Zone Management
7.1 Legal framework
7.2 Finished projects
7.3 Ongoing projects
7.4 Initiatives related to ICZM
7.5 Evaluation
8. NGOs and Other Private Stakeholders
9. References
1.The Coastal Zone
1.1 Description of the coastal zone
The total length of the Polish coastline, including the banks of
internal sea waters, i.e. the Szczecin and Vistula Lagoons, is 843
km. It is comprised of 500 km of seacoast, 241 km of the Szczecin
Lagoon and 102 km of the Vistula Lagoon. The Polish coast includes
sandbars with dunes, cliff coasts and lagoons, coastal lakes, river
estuaries and delta plains. Dune shores, related to littoral accumulation,
occupy about 71% of the length of the coast. Upland shores occupy
about 19%, the remaining 10% being low, lagoon shores and harbour
areas. The majority of shore accumulation forms occurring on the
Polish coast are threatened. It appears from Maritime Office data
that about 50% of the dune and 65% of the cliff shores have been
devastated.
1.2 Definition of the coastal zone
There is no precise legal definition of the entire coastal zone.
The variable boundaries of the Protective Belt are used for terrestrial
planning purposes. The seaward boundary of the Technical Belt is
established as ‘on the water line at mean sea level’
by regulation of the Prime Minister. The lower part of the inter-tidal
and the marine zone are thus outside this definition, although the
small tides in this part of the Baltic Sea mean that the width of
inter-tidal shore below this line is generally narrow.
1.3 Setback lines policy
The Act on Marine Areas of the Polish Republic and Maritime Administration
(1991) established a protected coastal strip running the length
of the Polish coastline, including internal marine areas, i.e. Vistula
Lagoon, Szczecin Lagoon. This strip comprises the Technical Belt
and the Protective Belt which must be marked on all Land Use Plans.
The technical belt is used for ensuring adequate safety and state
of the environment, whereas the protective belt is established in
order to control the negative impact of human activity in areas
directly adjoining the technical belt landward of the technical
belt.
The Technical Belt has been established for the whole Polish coastline
and extends up to 200m inland, according to the type of coast. In
dune areas it is up to 200m landward of the dune ridge; for cliffs
it is up to 100 m landward of the upper edge of the cliff; and for
the lagoons it is up to 200 m landward of the shore. In some areas,
it has been increased to as much as 1 km wide, but in urban areas
and along the shores of lagoons it can be much narrower. According
to the 1991 Act, it is ‘an area designed for maintaining the
coast in a state conforming with the requirements of safety and
environmental protection’. The relevant Maritime Office must
approve all uses of this strip. It is primarily intended for coastal
and environmental protection.
The Protective Belt extends generally up to 2 km inland from the
landward boundary of the Technical Belt but in some places it widens
to 5 km. In urban areas it can be much narrower. The Belt is intended
to limit the impact of human activities on the Technical Belt and
consequently there are restrictions on land use and development
to ensure they do not have a negative influence on the state of
the Technical Belt. All permissions for building within these zones
must have the approval of the relevant Maritime Office. In essence,
it is acting as a buffer zone.
2. Coastal Management
2.1 Authority
The scope of competence of maritime administration and other local
and governmental administrative bodies can be divided into three
areas:
The territorial sea and marine internal waters
Maritime Administration enjoys full competence as regards the location
and the substance of issues, with the exception of construction
permits and water supply and sewage effluent disposal consents,
i.e. the so-called water law permits. However, these require consultation
with the competent head of the maritime office within the territory.
Another exception is permits for the extraction of seabed resources
which require consultation with the Ministry of Transport and Maritime
Economy. Construction and water law permits are issued by provincial
governors. Maritime Administration is competent to issue decisions
in terms of land development and spatial management in this area.
The technical belt
Maritime Administration is responsible for the preparation and execution
of the protection of the shore and the environment, as well as for
issuing permits for all kinds of use, with the exception of construction
and water law permits and for the consultation of local spatial
management plans and decisions. Construction and water law permits
are issued by other administrative bodies on condition that they
have received the approval of a competent maritime authority.
The protective belt
Water law permits and decisions related to construction, changes
in land use, as well as the elaboration of spatial management plans,
are effected by competent ‘land’ bodies in consultation
with the competent maritime authority.
2.2 Policy
There is no national policy regarding coastal management. A new
concept of spatial planning for the coastal zone is being discussed.
At a regional level, the principles of development and conservation
are being discussed as a first step to create the Regional Strategy
of Development. On a local level, some documents are being prepared
which should function as a framework for spatial planning in the
future.
2.3 Legislation
There is no separate national legislation for coastal zone planning
and management. A number of legal instruments cover either the terrestrial
or the marine part of the coastal zone. Many of these instruments
are recent Acts that have been introduced in the course of the major
political and administrative transition in Poland.
Legislation relevant to coastal zone management:
- The Environmental Law Act, 2001
- The Act on Access to Information on the Environment and Its
Protection and on Environmental Impact Assessments, 2000
- The Act on Nature Conservation, 1991 and the changes made to
it in 2000
This describes and defines the protection of e.g. dunes.
- The Act on the Protection of Agricultural and Forest Land, 1995
- The Act on Environmental Protection and Development, 1994
This act forms the basis of current environmental legislation in
Poland.
- The Geological and Mining Law Act, 1994
- The Hunting Law, 1995
- The Act on Marine Areas of the Polish Republic and Maritime
Administration, 1991
This legal instrument regulates the administration of both marine
areas and the coastal belt. The Act also establishes the competence
of the maritime administration (Maritime Offices) and other governmental
and local authorities.
- The Water Law Act, 1974
The Act defines tasks associated with the management and protection
of water and its sources. Regional water management boards are
responsible for the strategic management of water resources. The
Act describes the terms of proper water usage and the regulatory
tool used for this purpose, the so-called water permit.
3. Spatial Planning in the Coastal Zone
3.1 Authority
There are four planning levels in Poland, i.e. national, regional,
county and local.
National
The Housing and Urban Development Office is the governmental agency
that is responsible for the general co-ordination and standardisation
of physical planning. The Government Centre for Strategic Studies
is responsible for the national physical development policy and
other kinds of planning at this level. Furthermore, the Ministry
of the Environment has guiding and control tasks in respect to environmental
issues of spatial planning.
Regional
There are 16 provinces, or voivodships, in Poland, three of which
are situated on the coast, being the West-Pomeranian, Pomeranian
and Varmian-Masurian. The voivodships are self-governing authorities.
The regional self-government, headed by the Marshal of the Vovoidship,
has full responsibility for strategic and spatial planning. The
regional body for planning is the Marshal’s Office and the
Department of Strategy and Development. Other institutions involved
in the formulation and implementation of regional plans include
regional development agencies, NGOs, foundations, etc.
County
The role of counties in public administration is an intermediary
one, with no specific planning competencies.
Local
There are 1489 communes in Poland which have substantial planning
responsibilities, however their enforcement potential is rather
weak. All local communes are obliged to prepare and approve a ‘local
comprehensive planning document’, which formulates the preconditions
and directions for physical development. National and regional goals
and directions are to be taken into account when elaborating these
plans. The detailed spatial plans are prepared as a legal instrument
for the development permits.
3.2 Policy
The 1994 Physical Development Act regulates the goals and principles
of spatial development and planning, adopting sustainable development
as a foundation. Since the mid-1990s, most of the planning and policy-forming
activities in Poland have been performed at the local and regional
level by self-governmental institutions. The basic regulation is
the Physical Development Act of 1994 but the drawback of the Polish
system is that planning, building and environmental protection issues
are regulated by completely different acts. It also must be said
that many communes have not yet enforced their local comprehensive
plans. The Ministry of the Environment is responsible for the so-called
“protection plans”, prepared for the National and Landscape
(regional) Parks. However, these plans do not belong to the category
of spatial plans in the sense of the Physical Development Act and
their provisions are binding for the regulations of the statutory
local comprehensive and detailed spatial development plans.
At the national level, the Concept of National Spatial Development
Policy is being elaborated as a strategic document (the present
document is called “Poland 2000 plus”). One of the key
components of the Concept is sustainability. Alongside the socio-economic
and environmental policy documents (strategies), it is supposed
to operate as a tool for indirect regulation of structural changes
in Poland (especially the physical space, incl. environment), during
the process of transition to a market driven economy. In this respect,
it is co-ordinated with the umbrella document of the Polish government
“Sustainable Development Strategy for Poland till 2025”.
Moreover, drafts of substantial amendments to the Physical Development
Act and the Environmental Protection Act have been submitted to
the Parliamentary Commission.
3.3 Legislation
Other regulations and legislation relevant to spatial planning are:
- The Act on Municipal Self-government, 1990,
- The Act on Marine Areas of the Polish Republic and Maritime
Administration, 1991,
- Construction Law, 1995,
- General Building Regulations, 1997
- Protected Belts Act, 1997
4. Coastal and Marine Environmental Policy
Over the last few years no national plans, programmes or strategies
have been approved at the ministerial level. One of the main problems
in this field appears to be that at the ministerial level no lobbying
bodies exist that work on coastal zone management and protection.
Although some preliminary work has been started, large-scale successes
have not yet been achieved. The new Polish Constitution states that
sustainable development shall be a basic principle of any policy
which is at least a good general platform for the introduction of
ICZM.
At present, the New National Environment Policy is formulated by
the government and being discussed in the Parliament. The document
calls for actions in the field of environmental protection and sustainable
development of Poland at the turn of the century. The principle
of sustainable development has been adopted as a leading principle
of the New National Environment Policy. The primary objective of
the state environmental policy is to ensure ecological safety for
the country, its inhabitants and natural resources by applying such
measures as legal regulations and control in reference to the use
of the environment. The transposition of the respective EU regulations
into the Polish legal system is an important element necessary for
the achievement of this objective.
5. Coastal and Marine Nature Conservation Policy
5.1 Authority
The provincial governor has the basic competencies in terms of the
introduction of certain forms of nature conservation and is authorised
to establish reserves. Boards of communes are competent to implement
different forms of individual protection, to establish protected
landscape areas and to introduce species protection. Certain rights,
related to management, organisation and supervision lie with the
head of the county. The authority regarding protective forests is
either the minister, in the case of forests that are the property
of the State Treasury, or the provincial governor, for all other
forests.
5.2 Policy
A long-term programme for coastal protection was approved in 1986
and revised in 1989. A new long-term coastal policy in under preparation
which will mainly consist of technical guidelines. Moreover, Poland
has established several parks, reserves and protected areas.
Protected areas in the coastal zone cover a total of 154,512 ha,
almost 0.5% of the country’s area. There are 2 national parks,
66 nature reserves, 5 landscape parks and 5 areas of protected landscapes.
The following tables present the basic data concerning the large
protected natural areas in the coastal zone.
Table 1: National parks and their geographical status (in hectares)
| National Park area (hectares) |
Total |
Forest |
Water |
Under strict control |
| 1. Wolinski National Park |
4,897 |
4,422 |
165 |
|
| 2. Slowinski National Park |
18,247 |
4,536 |
9,763 |
5,935 |
Table 2: Landscape parks and their geographical status (in hectares)
| Landscape Park Area |
Total |
Forest |
Agriculture |
Water |
| 1. Szczecin Landscape Park – Beach Forest |
9,096 |
6,742 |
1,616 |
241 |
| 2. Nadmorski Landscape Park |
15,493 |
3,043 |
285 |
10,345 |
| 3. Trojmiejski Landscape Park |
20,104 |
18,154 |
1,805 |
145 |
| 4. Vistula Spit Landscape Park |
4,410 |
3.330 |
186 |
269 |
| 5. Elblag Upland Landscape Park |
13,460 |
6,775 |
5,024 |
159 |
Table 3: Protected landscape areas and their total surface (in
hectares)
| Protected landscape areas |
Overall area |
| 1. Koszalin Coastal Belt |
48,330 |
| 2. Coastal Belt west of Ustka |
7,520 |
| 3. Coastal Belt east of Ustka |
3,336 |
| 4. Area of protected landscape of Vistula Lowlands |
5,320 |
| 5. Area of protected landscape of the River Bauda |
2,150 |
Two national parks protect two different types of dry coastal ecosystems
in Poland. The Wolinski National Park in the north-western cliff
zone was established in 1960, while the Slowinski National Park
on the sandy coast, with large mobile dunes, was established in
1966. The latter was nominated as a ‘Biosphere Reserve’
in 1980. Both these parks have made large scientific investigations
possible in all spheres of the national sciences. They have preserved
the most valuable landscapes with their vegetation and fauna.
Many nature reserves of different character protect special forms
of coastal landscapes, special types of soils (notably naspa soils
and classical podzolized soils), rare plants, plant communities
and animals. In the so-called ‘reserves of protected landscape’
the human impact on nature is greatly restricted. Another aspect
concerns the stabilisation of primary white dunes developing along
the beach. The main danger for the landscape, and for the coastal
vegetation, consists in the invasion of tourists and holiday-makers
as well as in the construction of different kinds of weekend houses
with camping and parking areas or even of big tourist amenities
in the direct vicinity of the coast.
5.3 Legislation
Legal Acts pertaining to environmental protection:
- The Water Law Act, 1974
- The Act on the establishment of the Ministry of Environmental
Protection, National Resources and Forestry, 1989
- The Act on Nature Conservation, 1991
- The Act on Marine Areas of the Polish Republic and Maritime
Administration, 1991
- The Act on the establishment of the State Inspection for Environmental
Protection, 1991
- The Act on Nature Conservation, 1991 and the changes made to
it in 2000
- The Act on fees for Economic Use of the Environment, 1993
- The Geological and Mining Law Act, 1994
- The Act on Environmental Protection and Development, 1994
- The Act on the Protection of Agricultural and Forest Land, 1995
- The Act on Access to Information on the Environment and its
Protection and on Environmental Impact Assessments, 2000
- The Environmental Law Act, 2001
6. Economic Developments, Important Sectors and Trends
6.1 Recreation and tourism
The coastal zone is a traditional area of mass recreation and tourism
activity. About 30% of the tourist facilities in Poland are located
along the coastal strips. Unplanned development of tourism facilities
on the Polish coast in the past has caused a concentration of recreation
places in, or close to, areas of natural beauty. A number of these
areas have experienced serious degradation, water and air pollution,
devastation of flora on sand dunes and cliffs and deterioration
of forests and open spaces. Programmes for the protection of about
100 landscape parks and many nature reserves in Poland are being
planned and implemented. To prepare for the sustainable development
of the Polish seaside, a study of the coastal zone has been made.
This study includes: documentation of the natural resources, protection
programmes, comprehensive assessments including environmental impact
assessment for recreation and health services needed; assessment
of the degradation or anthropogenic effects on the natural environment
and assessments of the environmental impacts of existing and proposed
investments and developments.
6.2 Coastal defence
Over 100 km of the Polish shoreline is now protected in some form
by means of groynes, seawalls, bulkheads, revetments and increasingly
artificial beach nourishment. The Act on the Forests (1991) describes
which forests in the coastal belt are understood as 'protective
forests'. A strategy for coastal defence is under preparation which
will mainly consist of technical guidelines.
7. The Current State of Integrated Coastal Zone Management
7.1 Legal framework
There is no national legislation that can be identified as ICZM
regulations or decrees. Since no formal mechanism has been installed
to facilitate or promote integration as regards ICZM and there is
no national policy or legislation for ICZM, overall legislation
concerning management and planning is applied. Poland has created
a framework for the development of ICZM which could be perceived
as an important international incentive for a more integrated approach
by signing numerous conventions. Moreover, Poland has engaged in
international discussions on the implementation of ICZM and accepted
international obligations to meet certain criteria and pursue a
strategy of sustainable development in numerous fields, including
coastal areas.
7.2 Finished projects
ICZM in The Baltic States and Poland
This satellite-image and GIS (Geographic Information System) based
project was executed from December 1997 to the middle of 2000. The
aim of this project was to give Estonia, Latvia, Lithuania and Poland
the opportunity to better manage their coastal resources in an environmental
and sustainable way. The specific pilot project in Poland (Coastal
Processes and Dynamics, Wladyslawowo Municipality) was located in
the Wladyslawowo area. The establishment of an Information Centre
in Gdansk, and adhering hardware and software installation and testing,
in combination with training of the Information Centre personnel
are some of the main results, next to the elaboration of the project
itself.
High Quality Tourism
The focus of this project is to improve and combine tourism and
sustainable development in regions with a large share of protected
areas. The end result was a handbook for local actors and Iinked
tourism projects within, and between, the regions.
SEBtrans (The South East Baltic Future Transport pattern
and the TEM-TER development zone)
The project aimed to establish a transport corridor as a zone of
accelerated development, TEM (Katowice-Gdynia-Karlskrona) and consisted
of four sub-projects dealing with transport corridors, modes and
technologies and regional development in the South East Baltic.
It includes transport patterns and intermodal solutions on short
sea shipping and combined transports, an impact study in the TEM/TER
development zone, a forecast of passenger traffic in the South-East
Baltic and a regional impact study to evaluate the impact of traffic
development and trade flows on a local and regional level.
7.3 Ongoing projects
Conservation of the Oder Delta
This joint demonstration project, executed by EUCC - The Coastal
Union and (EUCC) Poland, started in 1995. The main aims of the project
are to purchase strategically located land and to promote ecologically
sustainable development in the area. The goal is to integrate environmental
protection with economic development.
ICZM plan for the Oder and Vistula Lagoons
These plans have been developed under the auspices of the HELCOM
Working Group for Coastal Lagoons and Wetlands (HELCOM PITF MLW),
being the subsidiary of HELCOM PITF. Provisions included in these
plans have been incorporated into the development strategies for
Poland’s coastal provinces. Additionally, the Union of the
Vistula Lagoon is to take responsibility for the implementation
of ICZM plans for the Vistula Lagoon. A programme to support the
participation of integrated management of the Vistula Lagoon was
elaborated in 2000. The aim of the project is to provide the support
for implementation of the ICZM plan for the Vistula Lagoon by dissemination
of knowledge on ICZM among local authorities and the public, by
organising public hearings on ICZM. A similar project is to be implemented
for the Szczecin Lagoon.
Waterfront Urban Development
The objective of this project is to find solutions for downtown
and dock areas and small towns situated on the waterways in their
hinterlands where numerous cities have been turned away from the
waterfront.
SuPortNet
SuPortNet focuses on planning activities in regions of the South-
East Baltic. SuPortNet aims at implementing integrated spatial planning
and management in various locations that need improving harbour
facilities.
MATROS
This is a project on spatial (incl. environmental impact) issues
connected with the maritime transport and harbours.
WUD
This project is concerned with waterfront urban developments, coastal
zones in the towns and cities attractive for multipurpose development).
7.4 Initiatives related to ICZM
Joint Comprehensive Environmental Action Programme
for the Baltic Sea (JCP)
The JCP was adopted in 1992 to constitute a ‘Strategic Action
Plan’ for the Baltic Sea region. It provides an environmental
management framework for long-term restoration of the ecological
balance of the Baltic Sea ecosystem through a series of preventive
and curative actions to be undertaken in a phased manner in the
region. The five recipient countries, Estonia, Latvia, Lithuania,
Poland and the Russian Federation opted for Global Environment Facility
(GEF) assistance within this framework through the United Nations
Development Programme and the World Bank. Updated and strengthened
in 1998, the JCP Framework has formed a fruitful basis for further
regional projects.
7.5 Evaluation
A PROCOAST report concluded that in Poland, ‘Although nutrient
supply could be stabilised by establishing new sewage treatment
plants, eutrophication is still a problem. Changes in fish stock
composition could be observed. There are protected areas, but a
monitoring programme exists for the marine environment only. Parts
of the coasts are affected by coastal defence construction due to
the danger of flooding and erosion’. The general conclusion
that was drawn is that there is a lack of knowledge and attention
to coastal environmental issues.
8. NGOs and Other Private Stakeholders
Some of the most important NGO's concerned with nature conservation
are:
Coalition Clean Baltic (CCB)
The first environmental NGO-network established in the Baltic Sea
Region, established in 1990. Today it has 25 member organisations
in all 9 countries bordering the Baltic Sea. The main goal of CCB
is the protection and improvement of the Baltic Sea environment
and natural resources. It is gathering, producing and distributing
information about environmental problems in the Baltic Sea Area.
ECOBALTIC Foundation
The foundation aims to raise the public awareness and to conduct
ecological education in the field of nature protection and related
scientific research. It publishes materials on ecological issues.
EUCC - The Coastal Union - Poland (EUCC Poland)
An organisation concerned with sustainable use of coastal resources.
International Union of Anthropological and Ethnological
Sciences, Commission of Human Ecology (CHE/IUAES)
The CHE/IUAES is specifically concerned with support for research
in human ecology, information exchange, co-ordination of international
research programme on the bio-social status of human populations
as an indicator of environmental changes.
League for the Conservation of Nature in Poland
The organisation aims at the conservation of nature, ecological
education, especially in schools, protest group, publications, co-operation
with other organisations in Poland and abroad.
National Council for Protection of Nature in Poland
OTOP
The Polish Society for the Protection of Birds
PTOP
The North Podlasian Society for Bird Protection is active in North
Eastern Poland, and aims at protecting birds and their habitats,
documenting the current status of and the changes in the birdlife
of the North Podlasian Lowland. Another goal is to raise public
awareness of the threat to the survival of bird-life and the possibilities
of their protection.
An extensive list of nearly all NGO’s in Poland can be found
at www.rec.org.
9. References
Eeltink M, Background document ICZM National Files: Baltic Sea
Region, EUCC report, Netherlands, June 2000, p. 28/32
Ellul, Anthony, 1996. Council of Europe. Tourism and environment
in European countries.
EUCC, 1999. National report – Poland.
EUCC, 2000. Policy Instruments for ICZM in Nine Selected European
Countries – Poland. (PC 2006)
Houston, J., 1993. Coastal Management in Poland.
Ministry of the Environment, Department of Environmental Protection,
2000. Information on the Practical work on integrated coastal zone
management (ICZM) and on division of competence as regards management
and planning in the coastal areas in Poland, Poland.
PROCOAST project secretariat, Proceedings of the Interregional
Seminar on the Harmonisation of uses and interests in the Baltic
Sea Coastal Zones, October 2000
PROCOAST project secretariat, Procoast State of the art report.
Background document for Coastal Zone Planning and Management in
the Baltic Sea region, August 2000, p147/154
VASAB 2010 Compendium of spatial planning systems in the Baltic
Sea Region,
© Copyright: EUCC, 2002
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