MAL008 - Is-Salini
Description
Is-Salini Special Area of Conservation (SAC) is found within Salini Bay, which is located on the northeast coast of Malta between Naxxar and St. Paul’s Bay. Is-Salini is one of the last remaining salt marshes in the Maltese Islands. It is characterised by an estuary whereby sea water meets and mixes with rainwater originating from a complex of valley systems leading to Is-Salini. The Salini estuary is dynamic and dependent on the build-up of dead sea grass foliage. The consistent presence of freshwater makes this marshland unique to other similar habitats in the Maltese Islands and consequently the marshland supports several endemic species as well as a relatively large number of rare, endangered, and/or locally threatened species. It is the largest extant marshland in the Maltese Islands, though it used to be considerably larger before parts of it were reclaimed for health reasons, for salt harvesting, or for agriculture. Other parts of the site were later built over or afforested and turned into a recreational area (Kennedy Grove). One of the major features in the area is the seventeenth century salt harvesting complex, which was built in the inner reaches of Salina Bay and is now flanked on all except the seaward side by the remnants of the original marshland, which has been restricted to a canal-like feature, known as Is-Sokkorsu. The habitats of importance in this SAC (listed in the Habitats Directive under Annex I) include: • Coastal lagoons (Habitat 1150*) ; • Large shallow inlets and bays (Habitat 1160); • Salicornia (Twiggy Glasswort) and other annuals (plants that complete their lifecycle within one year) colonising mud and sand (Habitat 1310); • Mediterranean salt meadows (subject to flooding by sea water) (Habitat 1410); • Mediterranean and thermo-Atlantic halophilous scrubs perennial vegetation of marine saline muds) (Habitat 1420); • Garrigue/phrygana dominated by the Shrubby Kidney Vetch and Wild Thyme (Habitat 5410); and • Southern riparian galleries and thickets which are dominated by Tamarisk trees and Chaste trees growing along the valley watercourse (Habitat 93D0). The salt marsh is highly diverse in habitat composition and it is often difficult to distinguish between the different habitat types. Despite the number of habitat types recorded, however, it should be noted that Salini has been subjected to continual significant disturbance, which has obliterated the character of the original communities. Is-Salini was known to be the only or one of few remaining localities in the Maltese Islands for a number of plant species such as the Marsh Couch, Beaked Tassel Pondweed, Saltmarsh Bindweed, Slender sea hard-grass, and the Drooping Broomrape. It is also ecologically important for the fauna it supports. Most of these are typical of salt marsh areas and some have only been recorded at this site including molluscs, arthropods, moths and other invertebrates. The Tas-Sokkorsu canal is an important habitat for the brackish water native fish, the Killifish, an Annex II species (Habitats Directive). Notably, is-Salini provides ideal habitat for migratory bird species. In addition, a small breeding population of the Reed Warbler makes use of the reed bed at this site. A number of activities exert pressure on the ecology of the site. The site experienced significant negative effects with the development at Ta’ Mattew as a result of which, the freshwater spring as well as garrigue habitat were lost. Other interventions in more recent years have included the dredging and removal of the sediment that had accumulated in the southern branch of the canal over the years. This action resulted in the removal of certain vegetation communities inside and along the banks of the canal. This would also have impacted on the blue carbon storage of the site. Other pressures include impacts from agricultural runoff which is likely to be causing eutrophication of the watercourse as well as potential contamination from pesticides. Issues related to site abandonment have also impacted the site including dumping, vandalism, disturbance to accessible areas such as the reed bed and the introduction of invasive and non-native plant species. Poaching and trapping also result in negative impacts.
Wetland data
Basic information
Wetland location: | Marine/Coastal |
Wetland type: | Artificial |
Wetland area: | 14.10 Ha |
Hydrological interaction: | Yes |
Water salinity: | Brackish (5.0-18.0 g/l) |
Type of fresh water input: | Catchment area (precipitation) |
Surface water runoff | Other |
Open water area (%): | 76 - 95 |
Hydroperiod: | Permanent |
Geographic information
Census district: | Northern |
Island: | Malta |
Local council: | San Pawl Il-Bahar |
Longitude: | 14.422650 East |
Latitude: | 35.946000 North |
Biological significance
Biological significance: | High |
Ramsar wetland type
Type | Coverage (%) |
5 -- Salt exploitation sites; salt pans, salines, etc. |
Property status
Public |
Protection status category | Protection status subcategory | Area's name | Code | Coverage area (%) | Legislation |
National | Area of Ecological Importance | Sigar f'Kennedy Grove, is-Salini, limiti ta' San Pawl il-Bahar u n-Naxxar | 14777 | 22 | Development Planning Act (Act VII of 2016) |
National | Area of Ecological Importance/Site of Scientific Importance | Bur salmastru, Xaghri, Masgar u Steppa fis-Salini, limiti ta' San Pawl il-Bahar u n-Naxxar | 194409 | 100 | Development Planning Act (Act VII of 2016) |
National | Bird Sanctuary | Il-madwar ta' Kennedy Grove u s-Salini | 194412 | 100 | Environment Protection Act (Act I of 2016) |
International | Special Areas of Conservation - International Importance | Is-Salini | 330719 | 99 | Environment Protection Act (Act I of 2016) |
International | Special Protection Areas | Il-Bahar ta' madwar Ghawdex | 555589829 | 7 | Environment Protection Act (Act I of 2016) |
International | Transitional waters | Is-Salini | MT TW 01 | 100 | Water Framework Directive |
CDDA protection status
CDDA code | CDDA category |
MT01 | Area of Ecological Importance |
MT02 | Area of Ecological Importance/Site of Scientific Importance |
MT03 | Bird Sanctuary |
MT11 | Special Areas of Conservation - International Importance |
MT13 | Special Protection Areas |
Ecosystem services
Type of ecosystem service | Ecosystem service | Scale of Βenefit (%) | Importance |
Cultural services | Cultural heritage | ||
Regulatory services | Erosion regulation | ||
Regulatory services | Flood hazard regulation | ||
Supporting services | Nutrient cycling | ||
Supporting services | Provision of habitat | ||
Cultural services | Recreation and tourism | ||
Regulatory services | Storm hazard regulation | ||
Regulatory services | Water purification |
Activities on wetland
Activity | Intensity |
010 = Habitat conservation | High |
020 = Resource conservation | High |
030 = Species conservation | High |
040 = Land restoration | High |
161 = forest planting | Low |
243 = trapping poisoning poaching | Low |
340 = Salt works | High |
610 = Interpretative centres | High |
830 = Canalisation | High |
910 = Silting up | High |
952 = eutrophication | High |
Activities on catchment area
Activity | Intensity |
010 = Habitat conservation | Low |
020 = Resource conservation | Low |
030 = Species conservation | Low |
040 = Land restoration | Low |
100 = Cultivation | High |
110 = Use of pesticides | High |
120 = Fertilisation | High |
130 = Irrigation | High |
161 = forest planting | Medium |
220 = Leisure fishing | Low |
243 = trapping poisoning poaching | Low |
401 = continuous urbanisation | High |
430 = Agricultural structures | Low |
502 = roads motorways | High |
710 = Noise nuisance | High |
810 = Drainage | High |
Impacts
Impact | Intensity |
FCP = Introduction of animal pests | High |
PS- = Sewage pollution | High |
Habitat types
Type | Coverage (%) |
1150 * Coastal lagoons | 76 - 95 |
1160 Large shallow inlets and bays | 5 - 25 |
1310 Salicornia and other annuals colonizing mud and sand | 5 - 25 |
1410 Mediterranean salt meadows (Juncetalia maritimi) | 5 - 25 |
1420 Mediterranean and thermo-Atlantic halophilous scrubs (Sarcocornetea fruticosi) | 5 - 25 |
92D0 Southern riparian galleries and thickets (Nerio-Tamaricetea and Securinegion tinctoriae) | 5 - 25 |
Vegetation types
Type | Coverage (%) |
Halophytic | |
Emergent | |
Other | |
Ammophilous | |
Wet meadow | |
Shrubby / Arborescent | |
Submerged |
Flora
Species | Presence status | References |
Arthrocnemum macrostachyum | ||
Arundo donax | ||
Asparagus aphyllus | ||
Aster squamatus | ||
Atriplex prostrata | ||
Atriplex sp. indet, | ||
Avena sterilis | ||
Calystegia sepium | ||
Capparis orientalis | ||
Chenopodium album | ||
Cressa cretica | ||
Cynodon dactylon | ||
Elymus flaccidifolius | ||
Equisetum ramosissimum | ||
Hordeum leporinum | ||
Jacobaea crithmoides | ||
Juncus acutus | ||
Juncus subulatus | ||
Lolium spp. | ||
Lythrum junceum | ||
Melilotus messanensis | ||
Orobanche cernua | ||
Parapholis filiformis | ||
Phalaris minor | ||
Phragmites australis | ||
Polygonum aviculare | ||
Polypogon monspeliensis | ||
Populus alba | ||
Portulaca oleracea | ||
Potentilla reptans | ||
Ruppia maritima | ||
Salicornia ramosissima | ||
Salsola soda | ||
Suaeda maritime | ||
Suaeda vera | ||
Tamarix Africana |
Fauna
Mammals | Presence status in wetland | References | |
Erinaceus algirus (Lereboullet, 1842) | |||
Myotis blythii (Tomes, 1857) | |||
Pipistrellus pipistrellus (Schreber, 1774) | |||
Plecotus austriacus (Fischer, 1829) | |||
Suncus etruscus (Savi, 1822) | |||
Birds |
Number of individuals |
Nesting |
References |
Circus aeruginosus (Linnaeus, 1758) | |||
Pandion haliaetus (Linnaeus, 1758 ) | |||
Anas acuta (Linnaeus,1758) | |||
Anas clypeata (Linnaeus,1758) | |||
Anas crecca (Linnaeus, 1758) | |||
Anas penelope (Linnaeus, 1758) | |||
Anas platyrhynchos (Linnaeus, 1758) | |||
Anas querquedula (Linnaeus, 1758) | |||
Anas strepera (Linnaeus, 1758) | |||
Anser albifrons (Scopoli, 1769) | |||
Aythya ferina (Linnaeus, 1758) | |||
Aythya marila (Linnaeus, 1758) | |||
Aythya nyroca (Gűldenstädt, 1770) | |||
Cygnus olor (Gmelin, 1789) | |||
Marmaronetta angustirostris (Ménétriés, 1832) | |||
Netta rufina | |||
Tadorna ferruginea (Linnaeus, 1764) | |||
Tadorna tadorna (Linnaeus, 1758) | |||
Apus affinus (JE Gray, 1830) | |||
Apus apus (Linnaeus, 1758) | |||
Apus pallidus (Shelley, 1870) | |||
Actitis hypoleucos (Linnaeus, 1758) | |||
Alca torda (Linnaeus, 1758) | |||
Alle alle (Linnaeus, 1758) | |||
Arenaria interpres (Linnaeus,1758) | |||
Calidris alba (Pallas, 1764) | |||
Calidris alpina (Linnaeus, 1758) | |||
Calidris canutus (Linnaeus, 1758) | |||
Calidris ferruginea (Pontoppidan, 1763) | |||
Calidris maritima (Brünnich, 1764) | |||
Calidris minuta (Leisler, 1812) | |||
Calidris temminckii (Leisler, 1812) | |||
Charadrius alexandrinus (Linnaeus, 1758) | |||
Charadrius dubius (Scopoli, 1786) | |||
Charadrius hiaticula (Linnaeus, 1758) | |||
Childonias niger (Linnaeus, 1758) | |||
Chlidonias hybrida (Pallas, 1811) | |||
Chroicocephalus genei (Linnaeus, 1766) | |||
Fratercula arctica (Linnaeus, 1758) | |||
Gallinago gallinago (Linnaeus, 1758) | |||
Gallinago media (Latham, 1787) | |||
Gelochelidon nilotica (Gmelin, 1789) | |||
Glareola pratincola (Linnaeus, 1766) | |||
Haematopus ostralegus (Linnaeus, 1758) | |||
Himantopus himantopus (Linnaeus, 1758) | |||
Larus fuscus (Linnaeus, 1758) | |||
Larus michahellis (Pallas, 1811) | |||
Larus minutus ( Pallas, 1776) | |||
Larus ridibundus (Linnaeus, 1766) | |||
Limosa limosa (Linnaeus, 1758) | |||
Lymnocryptes minimus (Brünnich, 1764) | |||
Numenius arquata (Linnaeus, 1758) | |||
Numenius tenuirostris (Vieillot, 1817) | |||
Phalaropus lobatus (Linnaeus, 1758) | |||
Philomachus pugnax (Linnaeus, 1758) | |||
Pluvialis squatarola (Linnaeus, 1758) | |||
Recurvirostra avosetta (Linnaeus, 1758) | |||
Scolopax rusticola (Linnaeus, 1758) | |||
Sterna sandvicensis (Latham, 1787) | |||
Sternula albifrons (Pallas, 1764) | |||
Tringa erythropus (Pallas, 1764) | |||
Tringa glareola (Linnaeus, 1758) | |||
Tringa nebularia (Gunnerus, 1767) | |||
Tringa ochropus (Linnaeus, 1758) | |||
Tringa stagnatilis (Bechstein, 1803) | |||
Tringa totanus (Linnaeus, 1758) | |||
Vanellus vanellus (Linnaeus, 1758) | |||
Xenus cinereus (Güldenstädt, 1775) | |||
Ardea alba (Linnaeus, 1758) | |||
Ardea cinerea (Linnaeus, 1758) | |||
Ardea purpurea (Linnaeus, 1766) | |||
Ardeola ralloides (Scopoli, 1769) | |||
Botaurus stellaris (Linnaeus, 1758) | |||
Bubulcis ibis (Linnaeus, 1758) | |||
Bubulcis ibis (Linnaeus, 1758) | |||
Ixobrychus minutus (Linnaeus, 1766) | |||
Nycticorax nycticorax (Linnaeus, 1758) | |||
Platalea leucorodia (Linnaeus, 1758) | |||
Plegadis falcinellus (Linnaeus, 1766) | |||
Streptopelia decaocto (Frivaldszky, 1838) | |||
Alcedo atthis (Linnaeus, 1758) | |||
Merops apiaster (Linnaeus, 1758) | |||
Upupa epops (Linnaeus, 1758) | |||
Cuculus canorus (Linnaeus, 1758) | |||
Coturnix coturnix (Linnaeus, 1758) | |||
Fulica atra (Linnaeus, 1758) | |||
Gallinula chloropus (Linnaeus, 1758) | |||
Porphyrula martinica (Linnaeus, 1756) | |||
Porzana parva (Scopoli, 1769) | |||
Porzana porzana (Linnaeus, 1766) | |||
Porzana pusilla (Pallas, 1776) | |||
Rallus aquaticus (Linnaeus, 1758) | |||
Acrocephalus arundinaceus (Linnaeus, 1758) | |||
Acrocephalus melanopogon (Temminck, 1823) | |||
Acrocephalus schoenobaenus (Linnaeus, 1758) | |||
Acrocephalus scirpaceus (Hermann, 1804) | |||
Acrocephalus scirpaceus (Hermann, 1804) | |||
Anthus campestris (Linnaeus, 1758) | |||
Anthus cervinus (Pallas, 1811) | |||
Anthus novaseelandiae (Gmelin, 1789) | |||
Anthus pratensis (Linnaeus, 1758) | |||
Anthus trivialis (Linnaeus, 1758) | |||
Cecropis daurica (Laxman, 1769) | |||
Cettia cetti (Temminck, 1820) | |||
Cisticola juncidis (Rafinesque, 1810) | |||
Delichon urbicum (Linnaeus, 1758) | |||
Emberiza calandra (Linnaeus, 1758) | |||
Emberiza schoeniclus (Linnaeus, 1758) | |||
Erithacus rubecula (Linnaeus, 1758) | |||
Ficedula albicollis (Temminck, 1815) | |||
Ficedula hypoleuca (Pallas, 1764) | |||
Ficedula parva (Bechstein, 1792) | |||
Hippolais icterina (Vieillot, 1817) | |||
Hirundo rustica (Linnaeus, 1758) | |||
Lullula arborea (Linnaeus, 1758) | |||
Luscinia megarhynchos (C.LinnaeusBrehm, 1831) | |||
Luscinia svecica (Linnaeus, 1758) | |||
Motacilla alba (Linnaeus, 1758) | |||
Motacilla cinerea (Tunstall, 1771) | |||
Motacilla flava (Linnaeus, 1758) | |||
Muscicapa striata (Pallas, 1764) | |||
Oenanthe hispanica (Linnaeus, 1758) | |||
Oenanthe oenanthe (Linnaeus, 1758) | |||
Oriolus oriolus (Linnaeus, 1758) | |||
Passer hispaniolensis (Temminck, 1820) | |||
Phoenicurus ochruros ( S.G. Gmelin, 1774) | |||
Phoenicurus phoenicurus (Linnaeus, 1758) | |||
Phylloscopus bonelli (Vieillot, 1819) | |||
Phylloscopus collybita (Vieillot, 1817) | |||
Phylloscopus sibilatrix (Bechstein, 1793) | |||
Phylloscopus trochilus (Linnaeus, 1758) | |||
Prunella modularis (Linnaeus, 1758) | |||
Remiz pendulinus (Linnaeus, 1758) | |||
Riparia riparia (Linnaeus, 1758 ) | |||
Saxicola rubetra (Linnaeus, 1758) | |||
Saxicola torquatus (Linnaeus, 1766) | |||
Sturnus vulgaris (Linnaeus, 1758) | |||
Sylvia atricapilla (Linnaeus, 1758) | |||
Sylvia borin (Boddaert, 1783) | |||
Sylvia cantillans (Pallas, 1764) | |||
Sylvia communis (Latham, 1787) | |||
Sylvia melanocephala (J.F. Gmelin, 1789) | |||
Turdus iliacus (Linnaeus, 1766) | |||
Turdus philomelos (C.LinnaeusBrehm, 1831) | |||
Phalacrocorax aristotelis (Linnaeus, 1758) | |||
Phalacrocorax carbo (Linnaeus, 1758) | |||
Phoenicopterus roseus (Pallas, 1811) | |||
Jynx torquilla (Linnaeus, 1758) | |||
Podiceps cristatus (Linnaeus, 1758) | |||
Podiceps nigricollis (C.Linnaeus Brehm, 1831) | |||
Tachybaptus ruficollis (Pallas, 1764) | |||
Calonectris diomedea (Scopoli, 1769) | |||
Hydrobates pelagicus (Linnaeus, 1758) | |||
Puffinus mauretanicus (Lowe, 1921) | |||
Puffinus yelkouan (Acerbi, 1827) | |||
Asio flammeus (Pontopiddan, 1763) | |||
Otus scops (Linnaeus, 1758) | |||
Reptiles |
Presence status in wetland |
References |
|
Chalcides ocellatus (Forskal, 1775) | |||
Chamaeleo chamaeleon (Linnaeus, 1758) | |||
Coluber viridiflavus carbonarius (Bonaparte, 1833) | |||
Hemidactylus turcicus (Arnold, 1980) | |||
Podarcis filfolensis maltensis (Mertens, 1921) | |||
Tarentola mauritanica (Linnaeaus, 1758) | |||
Zamenis situla (Linnaeus, 1758) | |||
Amphibians |
Presence status in wetland |
References |
|
Discoglossus pictus (Otth, 1837) | |||
Fishes |
Presence status in wetland |
References |
|
Aphanius fasciatus (Valenciennes, 1821) | |||
Invertebrates |
Presence status in wetland |
References |
|
Pisaura maderiana (Kulczyński, 1895) | |||
Neaetha membrosa (Simon, 1868) | |||
Tetragnatha extensa (Linnaeus, 1758) | |||
Cyclodinus constrictus (Curtis, 1838) | |||
Cyclodinus humilis (Germar, 1824) | |||
Acupalpus elegans (Dejean, 1829) | |||
Anisodactylus virens winthemi (Dejean, 1829) | |||
Pogonus chalceus (Marsham, 1802) | |||
Achenium striatum (Latreille, 1804) | |||
Brachygluta globulicollis aubei | |||
Anisolabis maritima (Bonelli, 1832) | |||
Labidura riparia (Pallas, 1773) | |||
Nemotelus anchora (Loew, 1846) | |||
Ligyrocoris spp. | |||
Mesostenus grammicus (Gravenhorst, 1829) | |||
Eumenes dubius (Saussure, 1852) | |||
Oecogonia delluccai | |||
Megacraspedus lativalvellus (Amsel, 1954) | |||
Agdistis melitensis (Amsel, 1954) | |||
Apatema fasciata melitensis (Stainton, 1859) | |||
Symmoca melitensis (Amsel, 1954) | |||
Orthetrum brunneum (Fonscolombe, 1837) | |||
Gammarus aequicauda (Martynov, 1931) | |||
Heleobia (Semisalsa) stagnorum (Gmelin, 1791) | |||
Hydrobia acuta (Draparnaud, 1805) | |||
Hydrobia ventrosa (Montagu, 1803) | |||
Tudorella melitensis (G.B. Sowerby II, 1843) | |||
Melanoides tuberculata (O. F. Müller, 1774) | |||
Trochoidea spratti (L. Pfeiffer, 1846) | |||
Muticaria macrostoma (Cantraine, 1835) |
Adi Associates Environmental Consultants Ltd (2012b) PA 03883/08 & PA 03758/09 Reconstruction and Upgrading of Coast Road from Junction NA11 and NA10 & Widening and Realignment of Coast Road from Bahar Ic-Caghaq, Naxxar to St Paul’s Bay. Environmental Impact Statement.
Adi Associates Environmental Consultants Ltd (2012c) 03883/08 & PA 03758/09 Reconstruction and Upgrading of Coast Road from Junction NA11 and NA10 & Widening and Realignment of Coast Road from Bahar Ic-Caghaq, Naxxar to St Paul’s Bay. Appropriate Assessment.
Adi Associates (2012d) Salini Rehabilitation Project: Conservation & Management Framework, Version 3. San Gwann, October 2012; vi + 52pp.
Adi Epsilon Consortium (2014c) Is-Salini – Natura 2000 Management Plan (SAC). Prepared for the Malta Environment and Planning Authority under CT3101/2011. San Gwann, Malta, pp. 112 + Annex
Deidun, A., Diacono, I., Tigano, C. & Schembri, P.,(2002) Present distribution of the threatened killifish Aphanius fasciatus (Actinopterygii, Cyprinodontidae) in the Maltese Islands. Central Mediterranean Naturalist, 3(4), pp. 177-180.
ERA (2015) The 2 nd Water Catchment Management Plan for the Malta Water Catchment District 2015 - 2021