Impacts caused by increasing urbanization

Introduction

It is widely acknowledged that the coastal zones of the Mediterranean are coming under increasing pressure, which in turn is having serious implications for the environment and for the sustainable use of these highly valued ecosystems. All the littoral states have undertaken some measures to try and protect their coastal zones from overdevelopment, or development that is socially and environmentally damaging. The success of these measures, however, is questionable. In spite of well-reasoned and carefully drafted regulations, the pressure has continued to increase. The laws are often ignored by developers who put up illegal units. In this and other ways the regulations are ineffective in achieving the key goals of sustainable development: i.e. development that protects the environment for present and future generations to enjoy. There is ample documented evidence that the human pressure on coastal resources is increasing. Table 1 gives some basic data for the countries covered in this study. In the 30 years to 2000 densities in coastal areas increased by 49 percent, ranging from a low of 5 percent in Croatia, to a high of 112 percent in Algeria . The same period has also seen substantial increases in tourist densities in all countries except Egypt. Values for the others range from 25 percent in Spain to 73 percent in Turkey. In general the North African countries with the fast growing populations are also the ones with the highest rates of growth of coastal densities, including tourism densities (Algeria, Tunisia and Turkey). We also observe some shift in the relative densities of the population between the coastal zones and the national average. The last column of Table 1 gives the percentage change in this ratio between 1970 and 2000. It shows a relative movement outward for Croatia, France, Italy, Spain and Turkey. In Algeria, Egypt and Israel the density has increased slightly faster on average than it has in the coastal zones.

Table 1: Indicators of Coastal Zone Pressure in the Mediterranean

Country	% Increase in Coastal Residential Density 1970 to 2000	% Increase in Coastal Tourist Density 1970 TO 2000	% Change in Pop. Density in Coastal Areas Relative to Average 1970-2000
Algeria	112	34	-2
Croatia	5	n.a.	4
Egypt	104	-89	-1
France	31	38	12
Israel	92	72	-3
Italy	8	29	1
Malta	22	38	0
Spain	27	25	8
Tunisia	90	50	0
Turkey	107	73	13
All	49

Source: Plan Bleu, 1989, 2005, Attané and Courbage, 2001

In view of these strong human pressures on coastal zones, it is clear that increased regulations may be warranted to protect the resources.

Image: Percent Changes in Built Up Coastal Areas in Three Mediterranean Countries

== Values of amenities in coastal zones and of landscapes ==

Values of Coastal Landscapes for Owners or Occupiers of Property

Values of Coastal Views and Access to Non-Property Owners

The VOE Approach

A number of processes can also be used to value coastal views to non-property owners. The most common in the literature is often used to value the recreational amenity of a beach, and is known as the Value of Enjoyment (VoE) method. This is included in the ‘Yellow Manual’, produced by the Middlesex University Flood Hazard Research Centre (Penning-Rowsell et al 1992) and recommended by the UK government for valuing coastal protection (Whitmarsh et al. 1999). It elicits stated preferences by the use of a direct open question about the value placed on the enjoyment of a visit to the beach, and so does not require any payment vehicle to be expressed and avoids the possible biases that payments vehicles can bring to CVM studies (Marzetti 2003:17). In order to help frame this value, a VoE question should invite a comparison between the beach in question and alternative recreation sources. This also brings the respondent to consider the trade-off between using the beach and the alternative sites. As Whitmarsh et al. (1999: 455) conclude, “By thus focussing on choice and sacrifice, it attempts to go to the heart of the problem of economic valuation.” However, they also note that VoE results are not limited by people’s income (ibid: 461).

The best Mediterranean European data for the value of enjoyment from beach use appear to be those from Marzetti (2003) and Camp Israel (2000). The former uses Value of Enjoyment surveys for four beaches, of which only two have usable survey sizes. The beaches are Lido Di Dante on the North Adriatic Cost near Ravenna and the Barcola Seafront in Trieste. Their mean daily use values are reported in Table 3. The Israel study combines travel cost and other revealed expenditure data to estimate the value of beach visits. Its results are discussed further below.

The Marzetti study results in Table 3 show that the figures vary considerably between the two sites. The Lido Di Dante has three relatively distinct areas, varying by the levels of development – the least developed end is the most popular. Spring/ Summer values are between €25 and €32 and Autumn/ Winter values are between €4 and €20 . The standard deviations are large and do not exclude the possibility that the value may be zero for some individuals. Barcola is a crowded beach, and ‘New Beach’ is likely to be primarily used by locals. Values there are much lower – around €5 to €8 in Spring/ Summer and €5 to €6 in Autumn/Winter. Again the standard deviations are large.

Both sites have alternative beaches in the vicinity. We are not told the number of visitors to the Lido Di Dante, but we are told that there are 235,000 inhabitants of Trieste, and the survey found that 63.8 percent of residents visit the beach and that the beach is primarily used by residents, on average 20.9 days per resident. This gives an estimate of beach use of 3.1 million beach visits per year. A greater proportion of the town visits the beach in autumn/winter than spring/summer but spends a shorter time on the beach.

TABLE 3: MEAN AND STD. DEVIATION OF DAILY USE VALUES OF BEACH USE IN ITALY (€2003)

Source: Marzetti (2003)

Travel Cost and CV Approaches

The range of values given above is comparable to those found in a wider literature. Whitmarsh et al. (1999) provide a summary of their own and other studies of coastal recreation. Their valuations range from €12.42 to €15.98 for the UK and €4.27 to €52.98 per person per day for the USA (all adjusted to 2001€). The large figure in the USA was found using the Travel cost method for out-of-state visitors to Florida. The next highest US study found €15.17 per person per day. The studies give no indications of the size of the beaches or the numbers of people visiting. Landry and McConnell’s 2004 study used travel costs to estimate the value placed on recreation at two beaches in Georgia, USA. The survey was carried out over three seasons with over 2000 observations, and found valuations of €7.72-€9.16 for one beach and €17.01-€18.75 for a nearby alternative. Sohngen et al. (1999) studied visitors to two beaches in State Parks on the coast of Lake Erie, USA. One of the beaches is 1 mile (1.61km) long – the longest beach in Ohio – and both beaches have other recreational features nearby, such as hiking trails and fishing. They find that the beach with more features has a higher valuation (€31.53) than a site that is more beach-focussed (€19.09). Polomé et al (2005) summarised the literature on coastal defense, and in doing so, developed a benefit transfer function for beach recreation. They found shortcomings in the data arising from studies not presenting the total number of visitors to beaches and numbers of visits per visitor and on-site sample bias. They use 106 observations from 38 different sites in the UK, USA and the Netherlands. The studies were mainly from the 1990s but went as far back as 1975, and were predominantly VoE studies. They find that the average value is around €16 for UK beaches and €22 for US beaches (p.837, both figures have been converted to €2001). There were not enough studies to obtain a value for the Netherlands. However, there is still large uncertainty about these figures. They give the overall average value of informal recreation to be approximately €20 (€2001) per visit (p. 839). They also find that the date of the study makes little difference to the valuation, i.e. studies in the 1970s give similar valuations to later studies. On the other hand the concept of value used such as VoE, WTP etc, is highly significant in determining the result. This could mean that the benefit transfer is flawed, since different types of valuation give different results, or it could be that the differences in value are genuine – the USA studies typically used Consumer Surplus measures whilst the UK typically used VoE.

The CAMP study in Israel provides some useful additional material from another Mediterranean littoral state. Surveys of vacationers were carried out in 1982 and 1994. Based on these the researchers estimated that the 13 million annual beachgoers spent NIS98 million on travel to the sites, 25 million on entry fees and 8 million on parking. In addition another 18 million persons visited areas close to the beaches, spending NIS79 million. To this total of NIS210 million they added a consumer surplus of 70 percent, making a total willingness to pay of NIS357 million in 1999 prices. Converting to 2001 prices, and euros we get a figure of €3.5 per visitor. This is considerably lower than the EU/US values presented previously but then Israel has a lower per capita income than the countries from which the other values were obtained. The Israel study is also valuable as it is the only one that provides an estimate of the non-use value. A 1999 survey asked households what they would be willing to pay to prevent further construction on the coast. The value that emerged was NIS31/year, or around €9.4 in 2001 prices. This is significant as it applies in principle to the whole group from which the sample was drawn – i.e. the 1.6 million households in the country. Thus the gross annual WTP amounts to €15 million. Some more conjectural is converting this to a value per kilometre of coast. Of the country’s 188 km coastline 50 kilometres are used for national infrastructures and defence uses and are closed to the public. The remaining coastline has been designated as follows: 59 kilometres as municipal shores (adjacent to urban settlements), 43 kilometres for preservation as nature reserves and national parks, and 36 for open space (free of all infrastructures and facilities). Thus at present about 79 kilometres are undeveloped. The WTP then amount to €0.12 per household per kilometre per year.

Other Non-valuation Approaches

Some information on the value of landscapes affected by development can be gleaned from other landscape studies, not related to coastal landscapes. Arriaza et al (2004) carried out a survey requiring participants to rank the best and worst pictures in a series. The first few pages summarise the theoretical/ philosophical literature on what landscape is and methods of describing and comparing different landscapes. 226 people were shown 10 panels, each with 16 randomly assigned photographs of the landscape in question (Andalusia, Spain). The photos were chosen to capture the relevant features of that landscape, with and without other features (e.g. olive trees with and without other herbaceous cover, with and without ‘pretty’ buildings, with and without industrial buildings). The best 4 and the worst 4 pictures in each panel were scored from +4 to -4. These scores were used as the dependent variable in a regression. A panel of researchers assigned each picture a score based on the pictures contents e.g. amount of water, presence of positive man-made elements, and degree of wilderness according to a strict scoring system. They found that the degree of wilderness and positive man-made features have the biggest impact upon a view’s desirability. The next most influential factors are the area of water and the colour contrast. This seems to suggest that positive building, for example houses in keeping with the area, can increase the attractiveness of a view. This study uses a methodology and is well grounded in the theoretical side of landscape evaluation. However, it is unlikely that the results will be very transferable to coastal areas, since people value different landscapes for different reasons, e.g. positive manmade elements may be valuable in some agricultural landscapes such as Andalucía or the Cotswolds, but on coastlines they would be less welcome.

Another approach to valuing landscapes is that of Dramstad et al. (2001). They used the Norwegian national monitoring programme for agricultural landscapes (the 3Q programme) as a case study, focusing on biodiversity, cultural heritage and human experience of the landscapes. A total of 1474 sample squares of 1km x 1km distributed over the country in proportion to the amount of agricultural land. These are taken on a 5 year rotation, so changes are recorded after 5 years. The first round was in 1998.

Dramstad et al looked in particular at heterogeneity in landscapes as a common variable in analyzing biodiversity, cultural heritage and human experience. Heterogeneity of land types is found by dividing the 1km square into 100 sub squares and seeing how many sub squares are different in land type to their neighbours. This forms the heterogeneity index. Preferences for landscapes were found through asking people to rank photographs and text descriptions of the landscape within each square. Photographs were used to represent clearly defined levels of openness. Increasing heterogeneity was found to be a positive change for all aspects of the landscape-based values. This partially supports the Arriaza et al. finding that landscapes with some human construction can be deemed attractive, but it does not provide data directly relevant to coastal zones. Nor does it indicate which kinds of development are desirable. Nevertheless the results are a useful warning that one should not regard all man-made development as ‘bad’ and that in some cases it can enhance the value of a landscape. More work is needed on the valuation of coastal landscapes using this promising framework.

As far as coastal landscapes are concerned a couple of studies have been conducted in the UK and one in Turkey using non-economic approaches. Morgan and Williams (1998) asked coastal managers and students to rank 70 beaches in Wales. They found that the number of people on the beach did not significantly affect the scores given to different beaches, but undeveloped beaches scored better than those where anthropogenic structures were present. Beach commercialization had an impact only on the rankings of the students.

The other UK coastal study evaluated beach litter, to see which items were most offensive and which were less so (Tudrof and Williams, 2003). Not surprisingly people found items that were potentially harmful as the most offensive (syringes, gas canisters), followed by sewage related debris ( sanitary towels, condoms). Least offensive were items of natural origin, such as seaweed and driftwood.

The Turkish study (Ergin et al., 2006) develops measures of coastal scenery based on scores derived from a fuzzy logic analysis. The methodology considers 26 coastal scenic assessment parameters which cover physical and human factors. They find top preferences for beach goers in Croatia and Turkey were absence of sewage, water colour and absence of noise and buildings. Access to the beach and landscape features appeared fifth and sixth respectively in Croatia.

These kind of rankings could be linked to values of these different features of a beach but that has not been done as far as we can see.

Conclusions on Valuation of Coastal Views and Access

The value of beach access vary according to the services provides and degree of crowdedness. There appears, however to be range of between €5 and €30 per visitor per year for European studies and €5 to €15 for US studies, if we exclude some outliers. In Israel, representing a lower income country values are also lower, at about €3.5. The Israel study also provides the only non-use value of conservation of €9.4 per household per year. While the numbers obtained above are useful, they leave a lot or questions unanswered. We do not know the value of an uninterrupted beach view when simply visiting a coastal area, and how this value is affected by coastal development or other factors relating to the beach. Some of the non-valuation studies provide useful information but it still remains to link it to monetary values. We also do not know the impact on beach visits when access to the nearest beach is impeded. Do individuals go to another beach further away (thus losing welfare) or do they go the same beach but incur a higher cost?

Conclusions and Recommendations for Regulation

The pressure on coastal resources from ‘artificialization’ or conversion of natural habitats into man-made ones is growing. This pressure has been increasing steadily, at least since 1970 and probably from before then. Even since the 1990s when the problem has been recognized and attention devoted to tackling it, the rate of urban development along the coasts has continued to increase in most countries. The integrated coastal zone management is rarely effective in its implementation. Legislation is now in place in several countries that purports to provide the right regulatory framework, but it is being hampered by a lack of coordination between the regulating authorities (e.g. those responsible for land and sea and those responsible for different levels of government). The presence of specific coastal legislation does not appear to guarantee a better performance in terms of coastal protection. Lack of compliance is a problem, although the full extent of it is not known, except for a few countries. Illegal construction is a frequent phenomenon and is encouraged by modest fines, the granting of amnesties for dwellings that have been in place for a number of years and the practice of applying a statute of limitations on legal proceedings against violators. It is not possible from the data available to establish how effective the different instruments such as setback policies and other regulations have been in protecting coastal zones. A detailed assessment of the extent of violation of the setback rule therefore is needed. But even that would provide only a fraction of the information that should be collected. With a small setback area, at most a few hundred meters, a policy of intense development close to the sea is feasible and can result in a coastal zone that is substantially developed. Thus a wider assessment of the effectiveness of regulations by measuring outcomes is required. Some limited evidence that is presented is not encouraging – it does indicate continued and increasing pressure on coastal natural resources. The experience so far indicates that a stricter regime is needed to protect overdevelopment of coastal resources. The practice of amnesties for illegal construction must stop and illegal units should be more frequently subject to demolition. The use of normal planning regulations for land use needs to be buttressed by special conditions that apply to littoral zones that extend beyond the common range of 100-200 metres. In these zones construction should be completely banned. A second zone, perhaps up to one or even two kilometres, should be subject to special permission from an authority that is responsible of integrated coastal zone management and that supersedes other planning authorities. Decisions on permitting development in this zone should be part of a strategic plan. One possible regulatory tool could be the use of transferable development rights. An authority that restricted development in one area would compensate those who lost value as a result of such a restriction by allocating rights in other areas. Such systems have been an effective planning tool in municipalities and districts in the US and elsewhere. Alternatively authorities that were given coastal development rights could share the benefits with those where the rights were denied. Such a system applies in Italy (the so-called ‘perequazione urbanistica’). The system has allowed areas to be protected by arranging the transfer of benefits from other areas from as long ago as the early 1980s. (See Box 1).

Perequazione Urbanistica in Italy The idea behind the Perequazione Urbanistica is to share the benefits and costs of changes in land use status across communities and individuals. So, if one community or person is given the rights to develop land from agricultural or recreational use to use for dwellings, and another community is restricted not to develop land in this way, the two communities may share the benefits from the increased development. The scheme works by allocating to all residents in a given area the right to develop a part of their land. Then planning laws are introduced which in effect prohibit the exercise of this right in some places. These laws also define certain areas of land for public use – roads, parks etc. Those who cannot exercise their right by virtue of the planning regulations can sell these rights to others so that they can develop more of their land than their right allocation allows. Where the state needs to acquire land for public use, it does so at the agricultural value of that land, but this still allows the owner to sell the rights to development to another person who needs more than he or she has. In this way no one suffers from a planning restriction. The scheme has been applied in Italy specially to acquire land for public services with resorting to compulsory purchase under an Eminent Domain law or its equivalent. But it has also been applied to ecologically oriented uses. An example is the case of Cantù (near Como) where it has been used to preserve some Greenfield areas. Another is the case of Chiavari (near Genoa) where further development of the hills above the resort town have been deprived of development rights but these can be exercised elsewhere.

Another important instrument that can protect coastal development is land taxation. It may be possible to tax increased land values when development rights are accorded for coastal areas and use the revenues for the protection of other areas, including transfers to these areas to make up for restricting development. This serves a similar purpose as the perequazione urbanistica in Italy, except it uses a tax instrument. In general the authorities should seek to use fiscal instruments such as the above where possible. Given the difficulties in policing development, and the very strong incentives that individuals have to break the law by undertaking building in violation of planning regulations, it makes it much easier for the authorities to achieve their goals if costs of conservation are shared equitably. That said, some degree of protection of the coasts will always be needed. This can only be achieved if the political will is there. In any plan for coastal protection there will be positive and negative externalities to account for. The data available are limited and more needs to be collected on the value of beaches with and without development, the value of coastal landscapes without development and with different types of development, the costs of limited access to beaches and the ways in which beach users respond to increased development. However, the evidence is strongly in favour of conservation for plausible cases. The benefits to owners and developers of beachfront developments are often smaller than the plausible losses to beach users. Taking account of important non-use values will make the case for conservation even stronger. Finally we note that the losses are much greater from ribbon development than for cluster development. All these results need, however, to be strengthened with further research.

Literature and further readings

GENERAL EEA (2006): The changing faces of Europe's coastal areas, relazione AEA n. 6/2006, Agenzia Europea Per l'Ambiente Copenhagen.

Plan Bleu (1989): Futures for the Mediterranean Basin. The Blue Plan. Oxford University Press. Plan Bleu (2005): A Sustainable Future for the Mediterranean: The Blue Plan’s Environment and Development Outlook. Earthscan: London. VALUATION OF COASTAL LANDSCAPES Abelson, P. and A. Markandya. (1985) "The Interpretation of Capitalised Hedonic Prices in a Dynamic Environment", Journal of Environmental Economics and Management 12, 195 206.

Arriaza, M., J.F Cañas-Ortega, J.A Cañas-Madueño, P. Ruiz-Aviles (2004) “Assessing the Visual Quality of Rural Landscapes.” Landscape and Urban Planning 69 115-125 Attané I., Courbage Y. (2001) “ La démographie en Méditerranée – Situation et Projections.” Les Fascicules du Plan Bleu 11, Economica, 249 p.

Bell, F.W and V R Leeworthy, (1990) “Recreational demand by tourists for saltwater beach days”, Journal of Environmental Economics and Management, 18(3) 189-205. Benson, E.D, J.L Hansen, A.L Schwartz Jr. and G.T Smersh (1998) “Pricing Residential Amenities: The Value of a View.” Journal of Real Estate Finance and Economics 16(1) 55-73 Bond, M.T, V.L Seiler and M.J Seiler (2002) “Residential Real Estate Prices: A Room with a View”. Journal of Real Estate Research 23(1/2) 129-137 Dramstad, W.E, G. Fry, W.J Fjellstad., B. Skar, W. Hellisksen., M-L.B Sollund, M.S Tveit, A.K Geelmuden and E Framstad (2001) “Integrating Landscape-Based Values – Norwegian Monitoring of Agricultural Landscapes.” Landscape and Urban Planning 57 257-268 Ergin, A., A.T. Williams and A. Metcalf (2006) “Coastal Scenery : Appreciation and Evaluaton” Journal of Coastal Research, 22, 958-964. Fraser, R. and G. Spencer (1998) “The Value of an Ocean View: an Example of Hedonic Property Amenity Valuation.” Australian Geographical Studies 36(1) 94-86 Landry, C. E. and K. E. McConnell, (2004) "Hedonic Onsite Model of Recreation Demand", Paper presented at the Southern Economics Association 74th Annual Conference, New Orleans, LA 2004. Leeworthy, V.R and N.F Meade (1989-1990) A Socioeconomic Pro,le of Recreationists at Public Outdoor Recreation Sites in Coastal Areas: Vols. 1-5, Public Area Recreation Visitors Survey, National Oceanic and Atmospheric Administration, US Department of Commerce, Rockville, MD. Luttik, J. (2000) “The Value of Trees, Water and Open Space as Reflected By House Prices in the Netherlands” Landscape and Urban Planning 48 161-167. Marzetti Dell’Aste Brandolini, S. (2003) Economic Valuation of the Recreational Beach Use: The Italian Case-Studies of Lido Di Dante, Trieste, Ostia and Pellestrina Island. Final Report for the DELOS project. Available online at http://www.delos.unibo.it/Docs/Deliverables/D28A.pdf. (19/1/06) Milton, J., J. Gressel and D. Mulkey (1984) “Hedonic Amenity Valuation and Functional Form Specification” Land Economics 60(4) 378-387 Morgan, R. and A.T. Williams (1998) “Video Panorama Assessment of Beach Landscape Aesthetics on the Coast of Wales”, Journal of Coastal Conservation, 5 (1), 13-22. Muriel, T., Abdelhak, N., Gildas, A., and F. Bonnieux (2006) “Evaluation des bénéfices environnementaux par la méthode des prix hédonistes: une application au cas du littoral”. Paper presented at Les 1ères Rencontres du Logement de L'IDEP Marseille 19-20 October 2006. Available online at www.vcharite.univ-mrs.fr/idep/secteurs/logement/rencontres/document/papier/Travers.pdf

Parsons, G.R. and Y. Wu (1991) "The Opportunity Cost of Coastal Land Use Controls: An Empirical Analysis" Land Economics 67(3) 308-316

Penning-Rowsell, E.C, C.H Green, P.M Thompson, A.M Coker, S.M Tunstall, C. Richards and D.J Parker, (1992) The Economics of Coastal Management, Belhaven Press, London, 380pp. Polomé, P., S. Marzetti and A. van der Veen (2005) “Economic and Social Demands For Coastal Protection” Coastal Engineering 52 819-840. Silberman, J. and M. Klock, (1988) “The recreation benefits of beach nourishment”, Ocean and Shoreline Management, 11 73-90

Sohngen, B., F.Lichtkoppler and M. Bielen, (1999)"The Value of Lake Erie Beaches", FS-078 Ohio State University Tudorf, D.T. and A.T. Williams (2003) “Public perception and Opinion of Visible Beach Aesthetic Pollution: The Utilisation of Photography” Journal of Coastal Research, 19, 1104-1115. Whitmarsh, D., J. Northen and S. Jaffry (1999) Recreational benefits of coastal protection: a case study Marine Policy 23(4) 453-464

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