SITES

Greatham, Teesside, UK
West Site, Billingham, UK
Grimsby, Humberside, UK
Calais, France
Huelva, Spain
Scarlino, Italy
Habitats on the Scarlino Site
Insects
Reptiles and Amphibians
Birds
Mammals
Montioni Landfill
Biodiversity Management
Teluk Kalung, Malaysia
Umbogintwini, South Africa
Lake Charles, USA
Burnie, Tasmania

Index by Category

Appendices

References

 

 

 

 

Scarlino, Italy

Habitats on the Scarlino Site

The wild areas form a network of important wildlife habitats across the site and include:

  • Wetlands, which can be subdivided into, (i) reedbeds, mainly of Phragmites australis, (ii) open water of various depths, (iii) canals and rivers, (iv) seasonal rain flooded areas (v) effluent lagoons.
  • Grassland of varying sward, length and diversities of associated herbaceous plants.
  • Scrub areas of small shrubs and associated herbs.
  • Tree and shrub areas.
  • Open areas with sparse or no vegetation cover.

These habitats are of varying degrees of importance for wildlife, although each of them supports particular species which are either rare or absent from the other habitats. Overall the wildlife value of the different habitats both in terms of biodiversity and degree of conservation concern for the species present is:
Wetlands > Grassland > Scrub > Trees and shrubs > Open ground

Wetlands [see Areas “C”, “H” and “K” in Figure 21]
The Phragmites reedbeds and associated open water areas are the most important wildlife habitats on the sites both in terms of biodiversity and the international conservation importance of the species present. However, as with most other habitats on the site this assessment is based mainly on bird populations. With further studies of other taxa, especially invertebrates, some of the present assessments of the relative ecological importance of the various habitats might need to be revised.

The ecological importance of reedbed habitats, especially for birds, has been studied in many parts of Europe. These include southern Spain (Valverde 1958), the Camargue in southern France (Hoffmann 1958), Hungary (Vajada 1998) and the UK (Bibby & Lunn 1982, Hawke & Jose 1996, Brookhouse 1998, Lefeuere 1998). The utilisation of the reedbeds and wetlands at Scarlino is shown in Figure 22 and the feeding zones recorded for four important species of waterbirds, Black-winged Stilt, Squacco Heron, Little Egret and Purple Heron in Figure 23.

With regard to the other wetland habitats on the site, the canalised Pecora River (Area “K”, Figure 21) that flows into the Padule di Scarlino supports a number of bird species, especially Acrocephalus Warblers (see Section Birds). However, the canal running along the western boundary of the site, based admittedly on limited surveys, seems to be of low value for birds although dragonflies are numerous and in July 2000 large numbers of Bee-eaters were exploiting this food source. The canal also holds large numbers of fish, principally Grey Mullet (Mugil labeo) [G. Best pers. comm.]. The canal receives the treated and buffered (to pH 8.5) effluent from the site that is eventually discharged to the sea. No effluent enters the Pecora that discharges directly into the Scarlino marshlands. Another river, the Airvoe, also flows through the site and discharges into the sea. It is canalised on the site and, although it receives no site effluents, its wildlife value (based on very limited data) appears to be low.

Temporary wet areas resulting from surface water run off from other parts of the site - such as those to the north of the settling lagoons - appear to have limited value for bird life, although one or two Little Egrets were observed resting (but not feeding) in such areas during 26-28 May 1998. During migration periods and in the winter months, small numbers of waders and wildfowl are occasionally seen in these habitats (M. Caramelli pers. comm.).

The only other wetland areas on the site are the active effluent settling lagoons. Between 26-28 May 1998 and during a very brief visit in October 1992, these lagoons were devoid of bird life with the exception of a few Yellow-legged Gulls resting on the surface. In July 2000 however, 12 Greater Flamingos were recorded on these lagoons, although it was unclear whether the birds were actually obtaining food from the site.

Grasslands
The majority of the grassland areas on the Scarlino site are the result of vegetating old red gypsum spoil heaps (Areas “A”, “B”, “F” & “J” in Figure 21). Experiments began in the late 1980s with trials using sown grass and legume seed mixes and in some areas planting trees and shrubs. Mainly indigenous species were used, but some exotic species have been included. The gypsum areas were first treated with sewage sludge and straw and then seeded with grass and wildflower mixtures. These earlier planted grassland areas are now well established and some of the species present are listed in Table 28.

Sheep graze the grassland areas of the site and this appears to keep the vigorous species under control and encourages a higher diversity of plant life. This grazing is good for maintaining the ecological value of the site. The grazing regime seems to suit Skylark that is common on the site. Skylark is a bird of conservation concern in Europe (see Section Birds).

Sheep also act as biological monitors - the wool, milk and flesh are regularly analysed for heavy metals to ensure that these potentially toxic substances are not bioaccumulating in the food chain.

The banks of the old gypsum disposal sites, especially along the edges of site roads have developed a diverse and colourful flora. A particularly rich area is along the track bordering the western edge of the marshland (Area “J”, Figure 21). Yellow chamomile (Anthemis tinctoria), common mallow (Malva sylvestris), common poppies (Papaver rhoeas), the scarlet flowered Italian sainfoin (Hedysarum coronarium) and various thistles and vetches are found here. Several species of birds such as Goldfinches, Serins and Turtle Doves are associated with these floral rich banks that also supported large populations of butterflies (see Section Insects).

Faunal communities appear to be less diverse in the grass dominated sites, although butterflies such as Meadow Brown (Manida jurtina) - the larvae of which feed on various grasses - are quite abundant and several species of grasshoppers are known to occur. Skylark is an important bird of the grasslands and White Wagtails (Montacilla alba) were frequently found feeding where the grass was relatively short and on areas where sewage sludge had been deposited. The birds were feeding on the insects that were attracted by the sludge.

Trees and Shrubs
Trees and shrubs have been planted in several parts of the site, mainly in
Areas “E” and “J” in Figure 21, and more plantings are planned as part of the overall site environmental improvement project. These future planting schemes will also take into account other habitats important for the conservation of biodiversity such as grasslands, meadows and wetlands.

There is a fairly extensive tree planted area towards the south of the site and bordering raised open grassland adjacent to the Padule di Scarlino (Area “E”). A detailed botanical survey of these wooded areas has not yet been carried out but characteristic Mediterranean species such as Tamarix sp. and Aleppo pine (Pinus halepensis) are well established. The Aleppo pine is a widespread tree around the Mediterranean and, being very drought resistant, thrives on rocky ground in coastal sites. The trees in Area “E” grade into a relatively small maquis or garrigue habitat zone (Area “G”) that is characteristic of hot, dry Mediterranean landscapes (Polunin & Walters 1985). Typical plants of maquis habitats are found in this zone on the Scarlino site. These include Cistus (probably C. monspeliensis), tree heather (Erica arborea), rosemary (Rosmarinus officinalis), and strawberry tree (Arbutus undeo). However, at Scarlino, vegetation in this habitat does not form the dense thickets that are often associated with such plant communities in other parts of the Mediterranean (Polunin & Huxley 1978). At Scarlino the scrub communities tend towards more garrigue type habitat, with less dense vegetation interspersed with open areas of bare soils. Characteristic plants of this type of community include the tongue orchids (Serapias spp.), of which at least one species - probably S. parviflora - is quite common on the Tioxide site in Area “G”.

The Serapias have a very specialised reproductive biology, since they produce no nectar to attract pollinators. To compensate, the narrow tube (formed largely by the sepal hood) has an average temperature 1°-3°C higher than the ambient air temperature. On cool days several species of hymenoptera (mainly solitary bees and wasps) have been seen to congregate in these slightly warmer areas. When they leave the flower, these insects carry pollen with them and this eventually passes on to other blooms (Delforge 1995). The scrub vegetation grades into open grassland habitat towards the west similar to those previously described (Area “F”).

Goldfinches (Carduelis carduelis) and Turtle Doves (Streptopelia turtur) were amongst the most numerous birds of the tree areas. Magpies (Pica pica) were also common together with Italian Sparrows (Passer demesticus italia) in some sections. Serin (Serinus serinus) and Spotted Flycatcher (Muscicapa striata) were less common.
Stonechats (Saxicola torquata) and Whinchats (S. rubetra) were present in the scrub areas with the former feeding fledged young. The bird life of the scrub areas, however, was rather disappointing. Such habitats in the Mediterranean region usually hold diverse bird populations. Various scrub warblers (Sylvia spp.) are often well represented (this is the case at the Tioxide site at Huelva, Spain. Smith 1994b, 1995) together with shrikes (Laniidae) and, in the less vegetated areas, various larks (Alaudidae). Such bird communities do occur on other sites along the coast of Tuscany (Gusting et al. 1994) so it might be that this habitat type at Scarlino is not yet large enough to support viable populations. However, as more scrub habitat is created as part of the environmental amelioration programme for the site, the characteristic bird communities will almost certainly become established.

Butterflies and other insects are well represented in the scrub zone habitats and, although as yet largely unstudied, lizards are numerous and snakes also occur.

Bare and Open Ground
These are the least diverse habitats on the Scarlino site. They occur as non-vegetated landfill areas, tracks and bare banks. Vegetation is characteristically much reduced or absent, which allows rapid warming of the ground. Such conditions are much favoured by lizards, especially early in the day, and these reptiles are especially numerous on the Scarlino site.

The Little Ringed Plover (Charadrius dubius) prefers very bare sites for nesting and several other species of birds often feed in very open areas. At Scarlino these include White Wagtail, Hoopoe (Upupa epops) and Black-eared Wheatear (Oenathe hispanica).
The use of the various habitats on the Scarlino site are summarised in Figure 22.