Difference between revisions of "Testpage5"
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This article gives an overview of plant species that contribute to strengthening the shore protection function of dune coasts. The focus is on plants that can cope with the saline, nutrient-poor and harsh hydro-sedimentary conditions in the zone between the high waterline and the more stable backshore. These are species that can settle in shifting sands, that have a strong sand-binding capacity due to an extensive root system and that favor sand accumulation with their foliage. | This article gives an overview of plant species that contribute to strengthening the shore protection function of dune coasts. The focus is on plants that can cope with the saline, nutrient-poor and harsh hydro-sedimentary conditions in the zone between the high waterline and the more stable backshore. These are species that can settle in shifting sands, that have a strong sand-binding capacity due to an extensive root system and that favor sand accumulation with their foliage. | ||
− | The overview has not the pretention to be exhaustive. There are hundreds of plant species occurring along the shores of different continents that are adapted to nearshore conditions. The inventory (Table 1) focuses on species with a high shore protection capacity and that are common to shores | + | The overview has not the pretention to be exhaustive. There are hundreds of plant species occurring along the shores of different continents that are adapted to nearshore conditions. The inventory (Table 1) focuses on species with a high shore protection capacity and that are common to shores on different continents. Shore vegetation with a low sand-binding capacity is not included. The selection is probably biased towards species that are well described in the literature and may ignore some important less common and less-studied species. |
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These functions increase the sand volume of the upper beach and foreshore. This sand also nourishes further aeolian inshore transport and increases the sand volume of the dunes behind. | These functions increase the sand volume of the upper beach and foreshore. This sand also nourishes further aeolian inshore transport and increases the sand volume of the dunes behind. | ||
− | The sand-binding function of vegetation is not only because roots retain the sand, but also because roots improve the soil structure, by bringing in organic material and moisture and by stimulating the sand aggregation function of microorganisms and fungi<ref name=F></ref>. Experiments show that vegetation increases the stability of dunes during wave attack<ref>Silva, R., Martinez, M.L., Oderiz, I., Mendoza, E. and Feagin, R.A. 2016. Response of vegetated dune–beach systems to storm conditions. Coastal Engineering 109: 53–62</ref>. However, vegetation is usually not strong enough to prevent beach and dune erosion under extreme storm conditions. It is the sand mass of the entire dune complex that should be large enough to provide protection against flooding of the hinterland by preventing breach of the dune belt (see [[Dune erosion]]). Recolonization of eroded parts of the beach and foredunes by vegetation stimulates beach restoration<ref name=F></ref>. However, after-storm beach restoration depends primarily on sand supply from the surf zone to the beach by hydrodynamic processes, in particular wave-induced onshore sand transport and longshore drift (see [[Shoreface profile]]). In case of insufficient sand supply (beaches subjected to ongoing shoreline retreat), beach restoration requires artificial sand nourishment. The beach width can also be restored by dune retreat, which may happen naturally unless the backshore is a hard cliff or protected by a hard structure | + | The sand-binding function of vegetation is not only because roots retain the sand, but also because roots improve the soil structure, by bringing in organic material and moisture and by stimulating the sand aggregation function of microorganisms and fungi<ref name=F></ref>. Experiments show that vegetation increases the stability of dunes during wave attack<ref>Silva, R., Martinez, M.L., Oderiz, I., Mendoza, E. and Feagin, R.A. 2016. Response of vegetated dune–beach systems to storm conditions. Coastal Engineering 109: 53–62</ref>. However, vegetation is usually not strong enough to prevent beach and dune erosion under extreme storm conditions. It is the sand mass of the entire dune complex that should be large enough to provide protection against flooding of the hinterland by preventing breach of the dune belt (see [[Dune erosion]]). Recolonization of eroded parts of the beach and foredunes by vegetation stimulates beach restoration<ref name=F></ref>. However, after-storm beach restoration depends primarily on sand supply from the surf zone to the beach by hydrodynamic processes, in particular wave-induced onshore sand transport and longshore drift (see [[Shoreface profile]]). In case of insufficient sand supply (beaches subjected to ongoing shoreline retreat), beach restoration requires artificial sand nourishment. The beach width can also be restored by dune retreat, which may happen naturally unless the backshore is a hard cliff or protected by a [[Hard coastal protection structures|hard structure]] <ref name=MD>McLachlan, A. and Defeo, O. 2018. Coastal Dune Ecosystems and Dune–Beach Interactions. In The Ecology of Sandy Shores (Third Edition) 309-329. Academic Press</ref>. No major difference in vegetation type is observed between prograding and retreating coasts<ref>Konlechner, T.M., Kennedy, D.M., Cousens, R.D. and Woods, J.L.D. 2019. Patterns of early-colonising species on eroding to prograding coasts; implications for foredune plant communities on retreating coastlines. Geomorphology 327: 404–416 </ref>. |
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− | The exchange of sand between sea and land takes place in the shore zone above the mean HW line up to the foredune that is attacked by waves under heavy storm conditions. Most important for shore protection are therefore species that bind and accumulate sand in this zone | + | The exchange of sand between sea and land takes place in the shore zone above the mean HW line up to the foredune that is attacked by waves under heavy storm conditions. Most important for shore protection are therefore species that bind and accumulate sand in this zone. The European Habitats Directive (Natura2000) distinguishes the following habitats (see Fig. 1): |
− | # Annual vegetation of drift lines (1210) | + | # Annual vegetation of drift lines (habitat 1210) |
− | # Embryonic shifting dunes (2110) | + | # Embryonic shifting dunes (habitat 2110) |
− | # Shifting dunes along the shoreline with ''Ammophila arenaria'' (2120) | + | # Shifting dunes along the shoreline with ''Ammophila arenaria'' (habitat 2120) |
The last zone is often designated as 'foredune zone', 'yellow dunes' or 'white dunes'. An overview of common species occurring in these habitats is presented in Table 1. Only species with a sand-binding or dune-building function are considered. | The last zone is often designated as 'foredune zone', 'yellow dunes' or 'white dunes'. An overview of common species occurring in these habitats is presented in Table 1. Only species with a sand-binding or dune-building function are considered. | ||
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===Embryo-dune zone=== | ===Embryo-dune zone=== | ||
− | Dune formation starts higher up on the dry beach. The development of embryo dunes is mainly due to plants with erect stems that are capable to capture sand that is blown by the wind over the beach. Most of these plants are grasses such as ''Elymus'', ''Leymus'', ''Ammophilla'' (in cold/temperate climates), ''Spinifex'', ''Uniola'', ''Panicum'', ''Carex'' (in warm climates). ''Elymus'', ''Leymus'' and ''Spinifex'' are primary colonizers, whose growth is stimulated by sand burial. After the development of an initial dune | + | Dune formation starts higher up on the dry beach. The development of embryo dunes is mainly due to plants with erect stems that are capable to capture sand that is blown by the wind over the beach. Most of these plants are grasses such as ''Elymus'', ''Leymus'', ''Ammophilla'' (in cold/temperate climates), ''Spinifex'', ''Uniola'', ''Panicum'', ''Carex'' (in warm climates). ''Elymus'', ''Leymus'' and ''Spinifex'' are primary colonizers, whose growth is stimulated by sand burial. After the development of an initial dune they are partially replaced after some time by foredune species. Dune formation is also initiated by brushes such as ''Acacia'' and ''Tamarix'' that are adapted to a warm, arid climate. Embryo dunes are further stabilized and developed by smaller plants that form dense communities. Species of the genera ''Honckenya'', ''Sporobulus'', ''Anthemis'', ''Carpobrotus'', ''Medicago'', ''Eryngium'', ''Zygophyllum'' occur widespread on embryo dunes. |
===Foredune zone=== | ===Foredune zone=== | ||
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===Muddy shores=== | ===Muddy shores=== | ||
− | In temperate climate zones, muddy shores occur mainly in sheltered areas within bays, lagoons and estuaries. The dominant vegetation species is ''Sporobulus'' (often called ''Spartina''), which stabilizes mudflats and contributes to the development of salt marshes, see [[Dynamics, threats and management of salt marshes]]. In subtropical and tropical climate zones, muddy shores occur also on the open ocean. An important coastal protection function is accomplished by mangroves that attenuate waves and currents and favor sedimentation, see the article [[Mangroves]]. Protection against erosion by waves and currents can also be provided by ''Chrysopogon'' (Vertiver grass), that binds soil with very large deep roots. Vertiver grass is planted in many subtropical and tropical countries along water courses for the protection of shore and river banks. | + | In temperate climate zones, muddy shores occur mainly in sheltered areas within bays, lagoons and estuaries. The dominant vegetation species is ''Sporobulus'' (often called ''Spartina''), which stabilizes mudflats and contributes to the development of salt marshes, see [[Dynamics, threats and management of salt marshes]]. In subtropical and tropical climate zones, muddy shores occur also on the open ocean. An important coastal protection function is accomplished by mangroves, that attenuate waves and currents and favor sedimentation, see the article [[Mangroves]]. Protection against erosion by waves and currents can also be provided by ''Chrysopogon'' (Vertiver grass), that binds soil with very large deep roots. Vertiver grass is planted in many subtropical and tropical countries along water courses for the protection of shore and river banks. |
==Climate zones== | ==Climate zones== | ||
[[Image:WorldDuneDistribution.jpg|thumb|600px|center|Fig. 2. World distribution of coastal dunes. Adapted from Martinez et al. (2003)<ref>Martínez, M.L., Psuty, N.P. and Lubke, R.A. 2003. A Perspective on Coastal Dunes. In: (Eds. Martínez M. L. and Psuty N. P.) Coastal Dunes; Ecology and Conservation. Springer</ref>]] | [[Image:WorldDuneDistribution.jpg|thumb|600px|center|Fig. 2. World distribution of coastal dunes. Adapted from Martinez et al. (2003)<ref>Martínez, M.L., Psuty, N.P. and Lubke, R.A. 2003. A Perspective on Coastal Dunes. In: (Eds. Martínez M. L. and Psuty N. P.) Coastal Dunes; Ecology and Conservation. Springer</ref>]] | ||
− | Dune coasts are present along coasts worldwide, in all climate zones, see Fig. 2. Each climate zone has its own typical vegetation. Some vegetation species have a wide climate tolerance, but species that are | + | Dune coasts are present along coasts worldwide, in all climate zones, see Fig. 2. Each climate zone has its own typical vegetation. Some vegetation species have a wide climate tolerance, but species that are adapted to specific climate conditions generally prevail<ref>Doing, H. 1985. Coastal fore-dune zonation and succession in various parts of the world. Vegetatio 61: 65-75</ref>. Species that thrive under a broad range of conditions are species of the genera ''Ammophila'', ''Cakile'', ''Arctotheca'', ''Salsola'', ''Calistegia''. In temperate and Mediterranean climates the dominant dune-building species is ''Ammophila arenaria'' (marram grass); a similar species exists in N. America, ''Ammophila breviligulata''. In warmer climate zones (southern US, Mexico, Caribbean) ''A. Brevigulata'' is replaced by ''Uniola paniculata''. In colder climates ''A. arenaria'' is replaced by ''Elymus farctus'' and ''Leymus arenarius''. The major dune-building species in East Asia is ''Carex kobomigi'', which has become an invasive species in the US. |
In temperate climatic zones, wind and sand-catching grasses produce dunes with a stronger relief than dunes in warm climatic zones. On subtropical and tropical sandy coasts ''Spinifex littoreus'' and ''Scaevola plumieri'' contribute to dune-building, but creeping vegetation of the genera ''Ipomoea'' and ''Canavalia'' is often dominant<ref>Hesp, P.A. 2003. Coastal Dunes in the Tropics and Temperate Regions: Location, Formation, Morphology and Vegetation Processes. In: (Eds. Martínez M. L. and Psuty N. P.) Coastal Dunes; Ecology and Conservation. Springer</ref>. | In temperate climatic zones, wind and sand-catching grasses produce dunes with a stronger relief than dunes in warm climatic zones. On subtropical and tropical sandy coasts ''Spinifex littoreus'' and ''Scaevola plumieri'' contribute to dune-building, but creeping vegetation of the genera ''Ipomoea'' and ''Canavalia'' is often dominant<ref>Hesp, P.A. 2003. Coastal Dunes in the Tropics and Temperate Regions: Location, Formation, Morphology and Vegetation Processes. In: (Eds. Martínez M. L. and Psuty N. P.) Coastal Dunes; Ecology and Conservation. Springer</ref>. | ||
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* disturbance (trampling by visitors, sand mining) | * disturbance (trampling by visitors, sand mining) | ||
Examples are given in the articles on sand dunes in European countries, see [[:Category:Sand dunes]]. | Examples are given in the articles on sand dunes in European countries, see [[:Category:Sand dunes]]. | ||
− | In several countries (European Union, some states in the US) legal prescriptions have been issued for the protection of dune ecosystems. Many other countries have defined setback areas (see [[Setback area]]), but enforcement is often inadequate. Monitoring the status of the dune vegetation is essential to detect deterioration in time, to find out what the causes are and to | + | In several countries (European Union, some states in the US) legal prescriptions have been issued for the protection of dune ecosystems. Many other countries have defined setback areas (see [[Setback area]]), but enforcement is often inadequate. Monitoring the status of the dune vegetation is essential to detect deterioration in time, to find out what the causes are and to implement appropriate dune management measures. |
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| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Pioneer species in coastal sand dunes. Shrub, 0.5-3 m tall, 10-15 m wide. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Pioneer species in coastal sand dunes. Shrub, 0.5-3 m tall, 10-15 m wide. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Native to South Australia. Introduced to New Zealand, South Africa, Spain and Portugal. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Native to South Australia. Introduced to New Zealand, South Africa, Spain and Portugal. | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Salt tolerant. | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Humid or warm humid temperate climate, extending into the Mediterranean climate. Frost resistant down to -6°C and drought resistant, but needs at least 550 mm of rainfal<ref>Werner, C., Zumkier, U., Beyschlag, W. and Máguas, C. 2010. High competitiveness of a resource demanding invasive acacia under low resource supply. Plant Ecology 206 :83-96</ref>. Salt tolerant. |
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Various types of mobile sandy soils. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Various types of mobile sandy soils. | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | By seeds or vegetatively (branches root when touching the ground). | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | By seeds or vegetatively (branches root when touching the ground). Fire stimulates germination<ref> Marchante, H., Freitas, H. and Hoffmann, J.H. 2011. Post-clearing recovery of coastal dunes invaded by Acacia longifolia: is duration of invasion relevant for management success? Journal of Applied Ecology 48: 1295-1304</ref>. |
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Can be established from seedlings or by direct seeding (pre-soaked for 12 hours in warm water). | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Can be established from seedlings or by direct seeding (pre-soaked for 12 hours in warm water). | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Fixes nitrogen. Most Acacia plants die after 8-10 years. Can be an aggressive invasive species, altering indigenous vegetation. | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Fixes nitrogen. Most Acacia plants die after 8-10 years. Can be an aggressive invasive species, altering indigenous vegetation. |
|- | |- | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Ammophila arenaria'' (Marram grass, European beach grass) [[Image:AmmophilaArenaria.jpg|110px|center]] | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Ammophila arenaria'' (Marram grass, European beach grass) [[Image:AmmophilaArenaria.jpg|110px|center]] | ||
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| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Seeds can be wind-dispersed and also spread by ocean currents. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Seeds can be wind-dispersed and also spread by ocean currents. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | From seeds or from soft-tip cuttings made in spring and during the growing season. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | From seeds or from soft-tip cuttings made in spring and during the growing season. | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Invasive species in Australia, competing with native plants such as "Spinifex sericeus", by binding sand more efficiently. |
|- | |- | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Cakile Maritima'' (Searocket) [[Image:CakileMaritima.jpg|110px|center]] | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Cakile Maritima'' (Searocket) [[Image:CakileMaritima.jpg|110px|center]] | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Pioneer species settling close to the high-water line. Forms low erosion-sensitive hummocky dunes. Single or clumped plants accumulate sand and add organic matter to the soil, thus providing more amenable habitats for the establishment of secondary colonizers. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Pioneer species settling close to the high-water line. Forms low erosion-sensitive hummocky dunes. Single or clumped plants accumulate sand and add organic matter to the soil, thus providing more amenable habitats for the establishment of secondary colonizers. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Cakile maritima'' native to Europe and N. Africa. Introduced in Australia, New Zealand, Japan. ''Cakile edentula'' native to USA. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Cakile maritima'' native to Europe and N. Africa. Introduced in Australia, New Zealand, Japan. ''Cakile edentula'' native to USA. | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Wide-range of climatic conditions. Resistant to salt spray. |
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Grows best on moist or wet beaches, alkaline preferred. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Grows best on moist or wet beaches, alkaline preferred. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Species with seed dormancy. Efficient settling of seedlings, rapid growth, ability to flower under a range of photoperiods. Large numbers of fruits, short life cycle. Seeds can be dispersed by currents. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Species with seed dormancy. Efficient settling of seedlings, rapid growth, ability to flower under a range of photoperiods. Large numbers of fruits, short life cycle. Seeds can be dispersed by currents. | ||
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| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Seeds can float considerable distances in the sea, thereby explaining the wide distribution. Can also root from nodes at the stems. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Seeds can float considerable distances in the sea, thereby explaining the wide distribution. Can also root from nodes at the stems. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Can be grown from seed (soaked in water for several hours to speed up germination.) | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Can be grown from seed (soaked in water for several hours to speed up germination.) | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Used as drug. | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Used as a drug. |
|- | |- | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" |''Carex kobomugi'' (Asiatic sand sedge) <ref>Lea, C. 2005. Fact sheet: asiatic sand sedge. National Park Service, Washington, DC https://www.invasive.org/alien/fact/pdf/cako1.pdf</ref> [[Image:CarexKobomugi.jpg|110px|center]] | | style="border:2px solid lightblue; font-size: 11px; text-align:center" |''Carex kobomugi'' (Asiatic sand sedge) <ref>Lea, C. 2005. Fact sheet: asiatic sand sedge. National Park Service, Washington, DC https://www.invasive.org/alien/fact/pdf/cako1.pdf</ref> [[Image:CarexKobomugi.jpg|110px|center]] | ||
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| style="border:2px solid lightblue; font-size: 11px; text-align:center" | The native range extends throughout Southeast Asia, Northern Australia and the Pacific Islands. Introduced to the southern USA, West and South Africa, India, southern China and Brazil. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | The native range extends throughout Southeast Asia, Northern Australia and the Pacific Islands. Introduced to the southern USA, West and South Africa, India, southern China and Brazil. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Tropical (subtropical) climate. Tolerant to extreme environmental conditions such as drought, low nutrient availability, salt and salt spray and burial by sand. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Tropical (subtropical) climate. Tolerant to extreme environmental conditions such as drought, low nutrient availability, salt and salt spray and burial by sand. | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Tolerates calcareous soils | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Tolerates calcareous soils, granitic soils, poor soil, drought and waterlogging. |
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Casuarina'' propagates naturally by seed. | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Casuarina'' propagates naturally by seed. Protracted reproductive season and wide seed dispersal. |
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | By direct seeding or with seedlings elevated in a nursery. Can also be propagated vegetatively by cuttings (shoots). | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | By direct seeding or with seedlings elevated in a nursery. Can also be propagated vegetatively by cuttings (shoots). | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Highly competent invader; colonizes newly disturbed and nutrient-poor sites because of high fecundity | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Highly competent invader; colonizes newly disturbed and nutrient-poor sites because of high fecundity. Tendency to form monospecific stands. Fire-sensitive. |
|- | |- | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Chrysopogon zizanioides'' (also ''Vetiveria zizanioides'', vertiver grass) [[Image:ChrysopogonZizanioides.jpg|110px|center]] | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Chrysopogon zizanioides'' (also ''Vetiveria zizanioides'', vertiver grass) [[Image:ChrysopogonZizanioides.jpg|110px|center]] | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Planted to stabilize stream banks and to provide protection against erosion by currents and waves. Also used to block water runoff, to increase water infiltration. Vertiver stimulates sediment deposition; when silt builds up behind the plant new roots grow out of buried nodes to match the new soil surface level. |
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Origin: South India. Distributed to tropical countries around the world. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Origin: South India. Distributed to tropical countries around the world. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Tropical, subtropical climate. Full sun exposure. Temperature in the range -15 ºC to +55 ºC; optimum growth at 25 ºC. Medium to high annual precipitation. Salt tolerant. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Tropical, subtropical climate. Full sun exposure. Temperature in the range -15 ºC to +55 ºC; optimum growth at 25 ºC. Medium to high annual precipitation. Salt tolerant. | ||
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| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Native to Northern and Western Europe and temperate Asia. The closely related species ''Thinopyrum junceiforme'' was introduced to Australia. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Native to Northern and Western Europe and temperate Asia. The closely related species ''Thinopyrum junceiforme'' was introduced to Australia. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Cold and temperate climate. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Cold and temperate climate. | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Grows on low embryo dunes, less frequently on white dunes | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Sandy substrate rich in chlorides, with a neutral or alkaline pH. Grows on low embryo dunes, less frequently on white dunes. |
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | By seeds and by rhizomes. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | By seeds and by rhizomes. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | | ||
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| style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Euphorbia paralias'' (sea spurge) [[Image:EuphorbiaParalias.jpg|110px|center]] | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Euphorbia paralias'' (sea spurge) [[Image:EuphorbiaParalias.jpg|110px|center]] | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Highly efficient sand binder anchored by a deep taproot with several lateral roots. Colonizes bare sand and native dune vegetation, from the high water mark into the dunes, grows through accumulating sand on beach fronts. Also found on rocky foreshores, steep back dunes and mouths of coastal lakes and estuaries. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Highly efficient sand binder anchored by a deep taproot with several lateral roots. Colonizes bare sand and native dune vegetation, from the high water mark into the dunes, grows through accumulating sand on beach fronts. Also found on rocky foreshores, steep back dunes and mouths of coastal lakes and estuaries. | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Native to many countries of Europe, northern Africa, and western Asia. Introduced to Australia. | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Native to many countries of Europe, northern Africa, and western Asia. Introduced to Australia. ''E terracina'' has characteristics similar to ''E. paralias''. |
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Temperate and semi-arid regions. Sunny exposure. Tolerant to salt and drought. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Temperate and semi-arid regions. Sunny exposure. Tolerant to salt and drought. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Bare, well-drained organic-poor sandy soil. Withstands moderate sand burial. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Bare, well-drained organic-poor sandy soil. Withstands moderate sand burial. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Produces large numbers of buoyant salt-tolerant seeds which survive a number of years dispersed on ocean currents. Spreads rapidly once established. Propagation also by root fragments. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Produces large numbers of buoyant salt-tolerant seeds which survive a number of years dispersed on ocean currents. Spreads rapidly once established. Propagation also by root fragments. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Invasive environmental weed in Australia, reducing floral and structural diversity. Toxic: sap in the leaves and stem is irritant and | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Invasive environmental weed in Australia, reducing floral and structural diversity. Toxic: sap in the leaves and stem is irritant and poisonous. |
|- | |- | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Ficinia spiralis'' / ''Desmoschoenus spiralis'' (Pingao, Golden sand sedge) [[Image:FiciniaSpiralis.jpg|110px|center]] | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Ficinia spiralis'' / ''Desmoschoenus spiralis'' (Pingao, Golden sand sedge) [[Image:FiciniaSpiralis.jpg|110px|center]] | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Good sand-binding properties, grows in | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Good sand-binding properties, grows in mobile sand at the dune front. Moderate sand trapping due to the density of its foliage and morphology. Creates active sand dunes (allowing some sand movement). |
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | New Zealand. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | New Zealand. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Salt tolerant. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Salt tolerant. | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Moderate sand movement promotes growth, excessive accumulation or erosion causes dieback. Well-established stands can be excavated by high persistent winds and may die back leaving exposed rhizomes and roots. | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Moderate sand movement promotes growth, excessive accumulation or erosion causes dieback. Well-established stands can be excavated by high persistent winds and may die back, leaving exposed rhizomes and roots. |
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | By stolons and seeds. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | By stolons and seeds. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Can be reproduced from seeds or vegetatively from stolons. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Can be reproduced from seeds or vegetatively from stolons. | ||
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|- | |- | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Medicago marina'' (coastal medick, sea medick)<ref> Small, E. 2011. Alfalfa and relatives: evolution and classification of "Medicago". NRC Research Press, Ottawa, 727 pp.</ref> [[Image:MedicagoMarina.jpg|110px|center]] | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Medicago marina'' (coastal medick, sea medick)<ref> Small, E. 2011. Alfalfa and relatives: evolution and classification of "Medicago". NRC Research Press, Ottawa, 727 pp.</ref> [[Image:MedicagoMarina.jpg|110px|center]] | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Sand-binding pioneer species with an extensive root system that settles in loose sand close to the sea. | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Sand-binding pioneer species with an extensive root system that settles in loose sand close to the sea. The roots have nodules containing bacteria that fix nitrogen, available also to other plants that contribute to further dune stabilization. |
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Native to the Mediterranean region, distributed worldwide. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Native to the Mediterranean region, distributed worldwide. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Sunny exposure. Is tolerant of wind and salt spray and can survive severe drought. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Sunny exposure. Is tolerant of wind and salt spray and can survive severe drought. | ||
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| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Propagation by rhizomes . Self- and cross-pollinating plant. Seeds fall close to the mother plant; dispersal by wind. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Propagation by rhizomes . Self- and cross-pollinating plant. Seeds fall close to the mother plant; dispersal by wind. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Essential oil is extracted from the dried aerial parts of ''M. marina''. |
|- | |- | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Oenothera drummondii'' (beach evening primrose) [[Image:OenotheraDrummondii.jpg|110px|center]] | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Oenothera drummondii'' (beach evening primrose) [[Image:OenotheraDrummondii.jpg|110px|center]] | ||
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| style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Scaevola plumieri'' / ''Scaevola taccada'' <ref>CABI 2019. Invasive Species Compendium. www.cabi.org/isc/datasheet/48817</ref> [[Image:ScaevolaPlumieri.jpg|110px|center]] | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Scaevola plumieri'' / ''Scaevola taccada'' <ref>CABI 2019. Invasive Species Compendium. www.cabi.org/isc/datasheet/48817</ref> [[Image:ScaevolaPlumieri.jpg|110px|center]] | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Sand-binding pioneer plant on beaches | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Sand-binding pioneer plant on beaches, sand dunes, sandbanks, tropical atolls, mangroves and seagrape habitats. Tolerates sand burial and contributes to dune building. ''S. plumieri'' and ''S. taccada'' are similar species. |
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Scaevola taccada'' native to South Asia, East Africa, Pacific islands; ''Scaevola plumieri'' native to East and South Africa, Ceylon. Introduced to (sub)tropical America south of Florida. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Scaevola taccada'' native to South Asia, East Africa, Pacific islands; ''Scaevola plumieri'' native to East and South Africa, Ceylon. Introduced to (sub)tropical America south of Florida. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | (Sub)tropical monsoon climate. Grows within in the salt spray area. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | (Sub)tropical monsoon climate. Grows within in the salt spray area. | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Well-drained light/medium shallow sandy soils, seasonally waterlogged. Alkaline/neutral pH. | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Well-drained light/medium shallow sandy soils, seasonally waterlogged. Alkaline/neutral pH. Preference for coral sand. |
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Fast dispersal along the coast line, canal banks, mangroves, and inland shorelines by fruits that can float for up to one year. Plant fragments or stems may be dispersed on vegetation rafts. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Fast dispersal along the coast line, canal banks, mangroves, and inland shorelines by fruits that can float for up to one year. Plant fragments or stems may be dispersed on vegetation rafts. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | The species also grows from cuttings. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | The species also grows from cuttings. | ||
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| style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Tamarix nilotica'' (Nile Tamarisk) [[Image:TamarixNilotica.jpg|110px|center]] | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Tamarix nilotica'' (Nile Tamarisk) [[Image:TamarixNilotica.jpg|110px|center]] | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Shrub (2-5 m), sand binder for its extensive root system. Wind-blown sand comes to rest at the foot of the shrub, stimulating its growth and gradually creating a hummock. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Shrub (2-5 m), sand binder for its extensive root system. Wind-blown sand comes to rest at the foot of the shrub, stimulating its growth and gradually creating a hummock. | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Southeast Mediterranean region and east Africa. Also in the Nile valley. Other Tamarix species (T. aphylla, etc.) with similar characteristics around the Mediterranean and in the Middle East. | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Southeast Mediterranean region and east Africa. Also in the Nile valley. Other Tamarix species (''T. aphylla'', etc.) with similar characteristics around the Mediterranean and in the Middle East. |
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Adapted to arid subtropical climate, salt tolerant, capable to extract moisture from the underlying saline substrate. It tolerates temperatures from -10 to +50°C and frequent droughts. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Adapted to arid subtropical climate, salt tolerant, capable to extract moisture from the underlying saline substrate. It tolerates temperatures from -10 to +50°C and frequent droughts. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" |Wide variety of soils, loamy soil preferred. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" |Wide variety of soils, loamy soil preferred. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Tamarix can spread both in vegetative mode, by roots or submerged stems, and sexually, by seeds. Seeds can be dispersed by wind and by water. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Tamarix can spread both in vegetative mode, by roots or submerged stems, and sexually, by seeds. Seeds can be dispersed by wind and by water. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Salt excreted | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Salt excreted in the form of litter or 'tears', through the glands in the leaves, causes soil salinization, reducing the growth of plants nearby<ref> Abdelgawad, A.A.M. 2017. Tamarix nilotica (Ehrenb) Bunge: A Review of Phytochemistry and Pharmacology. J. Microb. Biochem. Technol. 9: 544-553. doi: 10.4172/1948-5948.1000340</ref>. |
|- | |- | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Uniola paniculata'' (Sea Oats) [[Image:UniolaPaniculata.jpg|110px|center]] | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | ''Uniola paniculata'' (Sea Oats) [[Image:UniolaPaniculata.jpg|110px|center]] | ||
Line 381: | Line 381: | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Contributes to beach stability due to a strong root system; retains embryo dunes. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Contributes to beach stability due to a strong root system; retains embryo dunes. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Western Sahara countries, Macaronesia, northeast Africa. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Western Sahara countries, Macaronesia, northeast Africa. | ||
− | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Sunny exposure. Can withstand intense drought. Requires regular salt spray. | + | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Mediterranean arid climate. Sunny exposure. Can withstand intense drought. Requires regular salt spray. |
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | Grows best in coarse, calcareous sandy brackish soils on the dunes; also on rocky soils. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | Grows best in coarse, calcareous sandy brackish soils on the dunes; also on rocky soils. | ||
| style="border:2px solid lightblue; font-size: 11px; text-align:center" | By seeds. | | style="border:2px solid lightblue; font-size: 11px; text-align:center" | By seeds. |
Revision as of 15:23, 25 June 2020
Shore protection vegetation
This article gives an overview of plant species that contribute to strengthening the shore protection function of dune coasts. The focus is on plants that can cope with the saline, nutrient-poor and harsh hydro-sedimentary conditions in the zone between the high waterline and the more stable backshore. These are species that can settle in shifting sands, that have a strong sand-binding capacity due to an extensive root system and that favor sand accumulation with their foliage.
The overview has not the pretention to be exhaustive. There are hundreds of plant species occurring along the shores of different continents that are adapted to nearshore conditions. The inventory (Table 1) focuses on species with a high shore protection capacity and that are common to shores on different continents. Shore vegetation with a low sand-binding capacity is not included. The selection is probably biased towards species that are well described in the literature and may ignore some important less common and less-studied species.
Contents
Shore protection function
Shore vegetation contributes to shore protection in two complementary ways[1][2]:
- by decreasing wave runup, due to the frictional effect of stems and foliage;
- by decreasing sand loss to the wave backwash, due to the effect of plant roots on sand aggregation and fixation.
These functions increase the sand volume of the upper beach and foreshore. This sand also nourishes further aeolian inshore transport and increases the sand volume of the dunes behind.
The sand-binding function of vegetation is not only because roots retain the sand, but also because roots improve the soil structure, by bringing in organic material and moisture and by stimulating the sand aggregation function of microorganisms and fungi[1]. Experiments show that vegetation increases the stability of dunes during wave attack[3]. However, vegetation is usually not strong enough to prevent beach and dune erosion under extreme storm conditions. It is the sand mass of the entire dune complex that should be large enough to provide protection against flooding of the hinterland by preventing breach of the dune belt (see Dune erosion). Recolonization of eroded parts of the beach and foredunes by vegetation stimulates beach restoration[1]. However, after-storm beach restoration depends primarily on sand supply from the surf zone to the beach by hydrodynamic processes, in particular wave-induced onshore sand transport and longshore drift (see Shoreface profile). In case of insufficient sand supply (beaches subjected to ongoing shoreline retreat), beach restoration requires artificial sand nourishment. The beach width can also be restored by dune retreat, which may happen naturally unless the backshore is a hard cliff or protected by a hard structure [4]. No major difference in vegetation type is observed between prograding and retreating coasts[5].
Adaptations
In order to withstand the harsh conditions prevailing on the open shore, species have developed several specific physiological traits. Typical are the following adaptations[6]:
- to salinity and salt spray: development of succulence, leave wax, thick cuticles, osmotic adaptation and glands that exude salt;
- to drought: development of succulence, hairy leaves, leave rolling, uptake of dew, roots that reach to the water table and stomata that can be closed;
- to sand burial: burial provides an incentive to increased development of roots, rhizomes, stolons and shoots, to increased seed production and to the development of 'smart' germination strategies; survivorship of seedlings and adult plants under sand burial is a major selective force in the evolution of dune vegetation[7].
- to nutrient deficiency: development of root nodules that produce nitrogen compounds, use of P and N from rhizosphere bacteria and fungal activity in the soil;
- to washing away by swash: rapid recolonization through efficient dispersal of seeds by wind and currents, delay of seed germination until conditions are favorable (so-called 'dormancy').
All species that thrive in the shore zone have at least some of these adaptations. However, some species are better adapted than others. When species are displaced from their regions of origin to other regions, native species can be outcompeted. This has consequences for the biodiversity as well as for the morphology of the dune landscape[8][9].
Habitats
The exchange of sand between sea and land takes place in the shore zone above the mean HW line up to the foredune that is attacked by waves under heavy storm conditions. Most important for shore protection are therefore species that bind and accumulate sand in this zone. The European Habitats Directive (Natura2000) distinguishes the following habitats (see Fig. 1):
- Annual vegetation of drift lines (habitat 1210)
- Embryonic shifting dunes (habitat 2110)
- Shifting dunes along the shoreline with Ammophila arenaria (habitat 2120)
The last zone is often designated as 'foredune zone', 'yellow dunes' or 'white dunes'. An overview of common species occurring in these habitats is presented in Table 1. Only species with a sand-binding or dune-building function are considered.
Drift-line zone
The drift line is the location where floating debris are left behind by waves running up the beach. In reality it is not a line but a zone around the maximum wave run-up. Most of the species in this zone are so-called pioneers. In fact, they are not really the primary colonizers, because their settlement is facilitated by micro-organisms and fungi, who aggregate sand particles in small clumps in which moist and nutrients are incorporated[4]. Symbiose of plant roots with vesicular–arbuscular mychorrhizal fungi is crucial to the development of pioneer species[10]. A special adaptation of drift-line species is their ability to feed on material - litter and wrack - washed ashore by waves. Plants are adapted to the high mobility of the substrate by an extensive root system. However, they generally do not resist storm waves and are therefore short living. Survival of the species is ensured by a high production and efficient spreading and germination of seeds. Listed species (Table 1) commonly found in different parts of the world near the drift line include the genera: Cakile, Honckenya, Salsola, Sevusium, Calystegia, Canavalia, Atriplex, Medicago, Scaevola, Glaucum, Eryngium, Ipomoea.
Embryo-dune zone
Dune formation starts higher up on the dry beach. The development of embryo dunes is mainly due to plants with erect stems that are capable to capture sand that is blown by the wind over the beach. Most of these plants are grasses such as Elymus, Leymus, Ammophilla (in cold/temperate climates), Spinifex, Uniola, Panicum, Carex (in warm climates). Elymus, Leymus and Spinifex are primary colonizers, whose growth is stimulated by sand burial. After the development of an initial dune they are partially replaced after some time by foredune species. Dune formation is also initiated by brushes such as Acacia and Tamarix that are adapted to a warm, arid climate. Embryo dunes are further stabilized and developed by smaller plants that form dense communities. Species of the genera Honckenya, Sporobulus, Anthemis, Carpobrotus, Medicago, Eryngium, Zygophyllum occur widespread on embryo dunes.
Foredune zone
The foredunes of non-vegetated coasts generally have a gentle slope, while vegetated coasts have a steeper foredune slope[4]. This holds in particular for dunes vegetated with Ammophila, which is a very effective sand binder and dune builder that prevents downslope sand transport even on steep slopes. Ammophila arenaria and Ammophila breviligulata are European and American beach grasses that have been introduced in many regions worldwide. In some regions, Ammophila arenaria can be an aggressive invader, for example in California, where it replaces the native foredune vegetation and greatly reduces species diversity[11]. Many other species also contribute to the stabilization and further growth of embryo dunes by forming a dense vegetation cover. Sand-binding species common to front dunes in several regions around the world include the genera: Eryngium, Euphorbia, Carpobrotus, Calystegia, Oenothera, Anthemis, Ficinia, Paspalum, Casuarina, Medicago, Zygophyllum.
Muddy shores
In temperate climate zones, muddy shores occur mainly in sheltered areas within bays, lagoons and estuaries. The dominant vegetation species is Sporobulus (often called Spartina), which stabilizes mudflats and contributes to the development of salt marshes, see Dynamics, threats and management of salt marshes. In subtropical and tropical climate zones, muddy shores occur also on the open ocean. An important coastal protection function is accomplished by mangroves, that attenuate waves and currents and favor sedimentation, see the article Mangroves. Protection against erosion by waves and currents can also be provided by Chrysopogon (Vertiver grass), that binds soil with very large deep roots. Vertiver grass is planted in many subtropical and tropical countries along water courses for the protection of shore and river banks.
Climate zones
Dune coasts are present along coasts worldwide, in all climate zones, see Fig. 2. Each climate zone has its own typical vegetation. Some vegetation species have a wide climate tolerance, but species that are adapted to specific climate conditions generally prevail[13]. Species that thrive under a broad range of conditions are species of the genera Ammophila, Cakile, Arctotheca, Salsola, Calistegia. In temperate and Mediterranean climates the dominant dune-building species is Ammophila arenaria (marram grass); a similar species exists in N. America, Ammophila breviligulata. In warmer climate zones (southern US, Mexico, Caribbean) A. Brevigulata is replaced by Uniola paniculata. In colder climates A. arenaria is replaced by Elymus farctus and Leymus arenarius. The major dune-building species in East Asia is Carex kobomigi, which has become an invasive species in the US.
In temperate climatic zones, wind and sand-catching grasses produce dunes with a stronger relief than dunes in warm climatic zones. On subtropical and tropical sandy coasts Spinifex littoreus and Scaevola plumieri contribute to dune-building, but creeping vegetation of the genera Ipomoea and Canavalia is often dominant[14].
In arid climates, Tamarix can stabilize shifting sands and create hummocky dunes, called nabkhas.
Dune management
Along many shores, dunes have a crucial function for protecting coastal settlements (or the low-lying hinterland) from flooding in case of extreme storm surges. If this protection is not sufficient, hard protection structures can be necessary to raise the protection function to the required level. However, hard protection structures modify the sand distribution along the coast, creating or aggravating erosion (see for example Human causes of coastal erosion and other Coastal Wiki articles on hard structures). Artificial sand nourishment avoids this problem, but is often a costly solution. Another option is to strengthen a coastal-defense dune through the incorporation of a hard concrete or rocky core[15]. The need for engineering interventions can be reduced – generally not excluded, however – by stimulating natural dune building processes. This can be done with sand-trapping fences; fences stimulate dune growth in height (but not necessarily in volume[16]). Compared to other options, dune reinforcement by stimulating natural vegetation growth or planting has many advantages: it is relatively inexpensive to implement and maintain, it offers the best resilience and it strengthens natural and scenic values[1].
Lack of understanding - why certain species may or may not prosper under existing conditions - is an important issue in dune vegetation programs. It is most naturel to use native species in coastal vegetation (or revegetation) programs, and in some countries (EU, US) there are legal regulations in this regard. However, more effective dune-building species might be wanted in some cases (more effective in terms of sand fixation, dune-building, soil improvement, adaptation to local conditions, etc.). Introducing non-native species has not always been successful; in some cases the species did not settle and in some other cases the propagation went out of control and altered the entire dune flora[8]. The success of vegetation programs using native species is equally uncertain[17]. Before introduction, one should find out why the species is not there yet and remove any obstacles that may be responsible for this. Experimental testing should be part of the vegetation programs.
The causes for the degradation of dune vegetation are multiple. Common causes are[9]:
- loss of dune surface area (urbanization, conversion to agriculture, shoreline retreat)
- soil degradation (water extraction and eutrophication, mainly through atmospheric deposition of nitrogen)
- disturbance (trampling by visitors, sand mining)
Examples are given in the articles on sand dunes in European countries, see Category:Sand dunes. In several countries (European Union, some states in the US) legal prescriptions have been issued for the protection of dune ecosystems. Many other countries have defined setback areas (see Setback area), but enforcement is often inadequate. Monitoring the status of the dune vegetation is essential to detect deterioration in time, to find out what the causes are and to implement appropriate dune management measures.
Name (popular name) | Shore protection | Regions | Environmental conditions | Soil type | Propagation | Planting | Other properties |
---|---|---|---|---|---|---|---|
Acacia longifolia subsp. sophorae (Coastal Wattle) | Pioneer species in coastal sand dunes. Shrub, 0.5-3 m tall, 10-15 m wide. | Native to South Australia. Introduced to New Zealand, South Africa, Spain and Portugal. | Humid or warm humid temperate climate, extending into the Mediterranean climate. Frost resistant down to -6°C and drought resistant, but needs at least 550 mm of rainfal[18]. Salt tolerant. | Various types of mobile sandy soils. | By seeds or vegetatively (branches root when touching the ground). Fire stimulates germination[19]. | Can be established from seedlings or by direct seeding (pre-soaked for 12 hours in warm water). | Fixes nitrogen. Most Acacia plants die after 8-10 years. Can be an aggressive invasive species, altering indigenous vegetation. |
Ammophila arenaria (Marram grass, European beach grass) | Pioneer species with great sand-binding and sand-trapping capacity. Initiates foredune growth on flat beaches. Roots extend one to several meters deep. Stimulates the development of high/steep foredunes vulnerable to erosion and blow-outs. | Native to southern/western Europe. Introduced: N. America, S. Africa and Australia. A similar species Ammophila breviligulata (American beach grass) is native to N. America. | Resistant to frost and temperatures up to 50ºC. Tolerates moderate salt spray, drought and low water table. | Well-drained, poor, mobile sandy soils, calcareous preferred. Growth stimulated by sand burial (<1 m/year). Declines in absence of new sand supply. | Rhizomes spreading horizontally and vertically. | Seedlings in dry sand with moist at about 10 cm below surface. Minimum planting depth about 30 cm. Period: late fall, winter, and early spring months; temperature between 0 and 15 ºC. | Invasive species in some countries where it inhibits growth of native plants. Fixes nitrogen. In stabilized dunes, Ammophila is replaced by other species, such as Festuca rubra (red fescue grass). |
Anthemis maritima (seaside chamomile) | Pioneer species that contributes to stabilization of mobile dunes, adapted to resist damage from wind-blown sand. | Native to the Mediterranean region, distributed to southwest Asia and W. Africa. | Sunny exposure, salt tolerant. | Lives generally on alkaline well-drained nutrient-poor beach sand, occasionally on sea cliffs and shingle beaches. | Self-pollinating plant. Seeds fall close to the mother plant. | Extraction of essential oil for aromatic and medicinal use. | |
Arctotheca populifolia (beach daisy) | Pioneer species of beach and dunes. Highly effective sand binder that forms hummocks ("nabkha's") by collecting wind-blown sand around it. Often associated with Gazania rigens. | Native to South Africa. Introduced to Australia. Similar species A. calendula introduced in southwestern Europe. | Mediterranean climate, salt tolerant. | Bare sand; variety of soils. | Seeds can be wind-dispersed and also spread by ocean currents. | From seeds or from soft-tip cuttings made in spring and during the growing season. | Invasive species in Australia, competing with native plants such as "Spinifex sericeus", by binding sand more efficiently. |
Cakile Maritima (Searocket) | Pioneer species settling close to the high-water line. Forms low erosion-sensitive hummocky dunes. Single or clumped plants accumulate sand and add organic matter to the soil, thus providing more amenable habitats for the establishment of secondary colonizers. | Cakile maritima native to Europe and N. Africa. Introduced in Australia, New Zealand, Japan. Cakile edentula native to USA. | Wide-range of climatic conditions. Resistant to salt spray. | Grows best on moist or wet beaches, alkaline preferred. | Species with seed dormancy. Efficient settling of seedlings, rapid growth, ability to flower under a range of photoperiods. Large numbers of fruits, short life cycle. Seeds can be dispersed by currents. | By seeding or by cuttings. | Invasive species. The plants are sensitive to fungi and are consumed by a variety of phytophagous insects and vertebrates; in response, Cakile manufactures glucosinolates that provides some protection. |
Calystegia soldanella (beach morning glory, shore bindweed) | Sand-binding pioneer species with a wide-spreading, branching rhizomatous rootstock. Adapted to sand drift, best developed on a buried flood mark and resistant to incidental saltwater flooding | China, Korea, Russia, Africa, Asia, Australia, Europe, North America, Pacific Islands, South America. | Tolerant to salt spray, sand burial and droughty conditions. Sunny exposure, sensitive to frost. | Along sandy shorelines, also in shell banks, fine gravel or pumice. The plant prefers well-drained light moist soils. | Flowers are pollinated by insects; the plant produces large seeds that can be dispersed by seawater. | From seed or rooted plant fragments. | |
Canavalia maritima (Sea bean) | Spontaneous sand binder on beaches, cliffs, and dunes. Climber plant that creeps over other coastal plants. Bacteria that form nodules on the roots fix atmospheric nitrogen, made available also to other plants. | South Atlantic and Gulf coast US, Mexico, West Indies, Central America, South America, and the South Asia. | Tropics and subtropics. | Dry well-drained nutrient-poor sandy soils, highly salt tolerant. | Seeds can float considerable distances in the sea, thereby explaining the wide distribution. Can also root from nodes at the stems. | Can be grown from seed (soaked in water for several hours to speed up germination.) | Used as a drug. |
Carex kobomugi (Asiatic sand sedge) [20] | Dune-stabilizing species, found on the upper parts of ocean beaches, on primary dunes, back-dunes, inter-swale areas. Sand burial stimulates the growth of rhizomes. | Native to China, Japan, Korea, Taiwan. Introduced in northeastern USA. | Temperate climate: Warm average temp. > 10°C, Cold average temp. > 0°C. Wet or dry summer. Grows in semi-shade (light woodland) or full sun. Tolerates maritime exposure. | All types of soil, with preference for moist or wet soil. | Spreads primarily by vegetative means, through production of rhizomes. Long-distance dispersal of salt-tolerant seeds or plant fragments by ocean currents | Replanting of large clumps. Seed-sow in situ in the spring in a moist soil in light shade. | Invasive species, prohibited in several US states. |
Carex pumila (dwarf sand sedge) [21] | Sand-binding species of the foreshore, cliff base or sea inlets [22]. | Australia, New Zealand, Chile, China, Japan and Korea. | Full sun, salt tolerant. | All types of freely draining sandy or gravely soils. | By rhizomes. It often regenerates naturally from seed spread by (fresh) water. | Sand sedge can be easily grown from seed and planted along the toe of foredunes near stream mouths. | |
Carpobrotus glaucescens (pigface) | Pioneer species growing on the front of sand dunes. Sandbinder allowing more effective sand-trapping species (e.g. Spinifex) to take a hold. The plant can survive sand burial, growing upwards and producing a new plant mat over the old one. | Native to Australia. Similar species C. edulis and C. virescens are native to S. Africa and distributed to other continents. | Mediterranean climate. Sunny or semi-shade exposure. Can tolerate drought. Is able to withstand salt spray, strong winds and sand blast. | Any well-drained light (sandy) or medium (loamy) soils. | The species is hermaphrodite (has both male and female organs). Propagates by seeds and by roots that develop at nodes along the stems. | Can be grown either from seed or from cuttings. | |
Casuarina equisetifolia (Australian pine tree, Filao) | Tree, stabilizer of upper beach and coastal sand dunes, by forming dense stands on coastal foreshores. | The native range extends throughout Southeast Asia, Northern Australia and the Pacific Islands. Introduced to the southern USA, West and South Africa, India, southern China and Brazil. | Tropical (subtropical) climate. Tolerant to extreme environmental conditions such as drought, low nutrient availability, salt and salt spray and burial by sand. | Tolerates calcareous soils, granitic soils, poor soil, drought and waterlogging. | Casuarina propagates naturally by seed. Protracted reproductive season and wide seed dispersal. | By direct seeding or with seedlings elevated in a nursery. Can also be propagated vegetatively by cuttings (shoots). | Highly competent invader; colonizes newly disturbed and nutrient-poor sites because of high fecundity. Tendency to form monospecific stands. Fire-sensitive. |
Chrysopogon zizanioides (also Vetiveria zizanioides, vertiver grass) | Planted to stabilize stream banks and to provide protection against erosion by currents and waves. Also used to block water runoff, to increase water infiltration. Vertiver stimulates sediment deposition; when silt builds up behind the plant new roots grow out of buried nodes to match the new soil surface level. | Origin: South India. Distributed to tropical countries around the world. | Tropical, subtropical climate. Full sun exposure. Temperature in the range -15 ºC to +55 ºC; optimum growth at 25 ºC. Medium to high annual precipitation. Salt tolerant. | Wet sandy loam soils preferred. Drought tolerant due its deep roots (3-4 m). Accepts large range of soil pH. | Neither stolons nor rhizomes. Propagated by clump subdivision. | Soil stabilization by planting one or several hedgerows, forming a long-lasting terrace where sediment is trapped. Low-cost, labor-intensive technique for civil works protection, claimed to have a high benefit/cost ratio. | Non-fertile, non-invasive. Not strongly affected by pests and diseases, not acting as host for pests or diseases that might attack crop or garden plants. The roots are used for many purposes. Vertiver oil is used in oriental fragrances. |
Elymus farctus subsp. boreoatlantica / Elytrigia juncea / Agropyron junceum (sand couch-grass) | Sand-trapping pioneer species; initiates the formation of embryo dunes but rarely a new dune ridge. Can accommodate considerable ongoing accretion by upward growth; partial recovery after temporary burial[23]. | Native to Northern and Western Europe and temperate Asia. The closely related species Thinopyrum junceiforme was introduced to Australia. | Cold and temperate climate. | Sandy substrate rich in chlorides, with a neutral or alkaline pH. Grows on low embryo dunes, less frequently on white dunes. | By seeds and by rhizomes. | Suffers from recreational use of beaches. | |
Eryngium maritimum (Sea Holly) [24] | Pioneer species of the upper beach, growing on low mobile dunes and binding sand with roots up to 5 m long. High sand accumulation (> 0.2 m/year) is unfavorable for development. Grows typically on sand and shingle beaches, foredunes and yellow dunes. | Native to Europe and adjacent parts of northern Africa and Middle East (shores of the Atlantic Ocean, the Baltic, the Mediterranean, and Black and Azov Seas). Introduced into parts of eastern North America and to Australia. | Mediterranean–
Atlantic climate, mild winters. Grows on open spaces in full sun. |
Well-drained poor sandy soil (low silt/clay content), slightly enriched with nutrients from sea spray, carbonates from shells and material blown from the driftline. | Vegetative reproduction by offshoots from rhizomes or root fragments, dispersed by the sea over short-distances. In Mediterranean regions, reproduction mainly through seeds. | Vegetative reproduction is used in horticulture, where root cuttings are taken in winter. | E maritimum is unable to withstand competition from faster and more densely growing plant species (e.g., Carex arenaria) and suffers from recreational use of beaches. |
Euphorbia paralias (sea spurge) | Highly efficient sand binder anchored by a deep taproot with several lateral roots. Colonizes bare sand and native dune vegetation, from the high water mark into the dunes, grows through accumulating sand on beach fronts. Also found on rocky foreshores, steep back dunes and mouths of coastal lakes and estuaries. | Native to many countries of Europe, northern Africa, and western Asia. Introduced to Australia. E terracina has characteristics similar to E. paralias. | Temperate and semi-arid regions. Sunny exposure. Tolerant to salt and drought. | Bare, well-drained organic-poor sandy soil. Withstands moderate sand burial. | Produces large numbers of buoyant salt-tolerant seeds which survive a number of years dispersed on ocean currents. Spreads rapidly once established. Propagation also by root fragments. | Invasive environmental weed in Australia, reducing floral and structural diversity. Toxic: sap in the leaves and stem is irritant and poisonous. | |
Ficinia spiralis / Desmoschoenus spiralis (Pingao, Golden sand sedge) | Good sand-binding properties, grows in mobile sand at the dune front. Moderate sand trapping due to the density of its foliage and morphology. Creates active sand dunes (allowing some sand movement). | New Zealand. | Salt tolerant. | Moderate sand movement promotes growth, excessive accumulation or erosion causes dieback. Well-established stands can be excavated by high persistent winds and may die back, leaving exposed rhizomes and roots. | By stolons and seeds. | Can be reproduced from seeds or vegetatively from stolons. | Suffers from competition with introduced marram grass and animal grazing. Leaves are used as weaving material. |
Honckenya peploides (sea wort grass) | Coastal pioneer plant and sand binder, close to the tidemark and on embryo dunes. Forms mats on sand beaches and gravel beaches. Long-branched rootstocks grow quickly under the sand; finely-branched shoot roots anchor the plant firmly in the sand. After sand burial the plant can send new shoots back up to the surface without having to produce new shoots. | Coasts of temperate and arctic regions of Eurasia, including Britain, and N. America. | Sunny, maritime exposure. Tolerant to frost and to short periods of immersion in salt water. | Light (sandy) and medium (loamy) well-drained dry or moist soils, can grow in nutritionally poor soil. Suitable pH: acid, neutral and basic (alkaline) soils. | Hermaphrodite species, pollinated by insects, wind and wind-blown sand. The plant is self-fertile. | The rootstock produces an abundance of buds from which new shoots grow. | Sea sandwort stabilizes and fertilizes the land, thereby helping settlement of more demanding sea-shore plants. It changes the conditions in a way that it eventually finds itself in retreat from the increasing competition. |
Ipomoea imperati (Beach morningglory, fiddle-leaf morningglory) | Colonizer species on the frontal dunes; binds shifting sands by forming mats. Used for dune restoration. Ipomoea pes-caprae has similar characteristics. | Ipomoea imperati occurs on all continents. Ipomoea pes-caprae is a common species of coasts around the Indian ocean. | Tropical and subtropical regions. Drought and salt water tolerant; cannot withstand frequent inundations. | Moist, well-drained, nutrient-poor sandy soils, without humus. Grows in unconsolidated substrate (upper beach), also on the high marsh. | Rapid propagation with vines that spread up to 10 m and roots at the nodes (points where leaves arise). Seed dispersal by flowing in seawater. | Growth from cuttings. Seeds of railroad vine are physically dormant and must be scarified in order to germinate. | |
Leymus arenarius (sand ryegrass, sea lyme grass, lyme grass) [25] | Pioneer species on beach, embryo dunes and foredunes; dune-building grass, stabilizing drifting sands and eroding fronts. Thrives on sand deposition; replaced by other species when sand deposition ceases. Strong similarities with Elymus farctus. | Native to the coasts of northern and western Europe and Iceland. Closely related to Leymus mollis of the northern coasts of North America. | Prefers cool climate but tolerant of hot weather. Highly salt tolerant. Sunny exposure or half-shade. | Grows on low embryo dunes, on a sandy substrate , loam (silt) or clay. | By rhizomes. | Sowing of seeds in sheltered fertilized areas. | Takes up nitrogen into its root system. Changes soil conditions and microclimate, which become more suitable for later successional species. Invasive species in some countries. |
Medicago marina (coastal medick, sea medick)[26] | Sand-binding pioneer species with an extensive root system that settles in loose sand close to the sea. The roots have nodules containing bacteria that fix nitrogen, available also to other plants that contribute to further dune stabilization. | Native to the Mediterranean region, distributed worldwide. | Sunny exposure. Is tolerant of wind and salt spray and can survive severe drought. | It will grow on most soils, even very poor and polluted soil. | Propagation by rhizomes . Self- and cross-pollinating plant. Seeds fall close to the mother plant; dispersal by wind. | Essential oil is extracted from the dried aerial parts of M. marina. | |
Oenothera drummondii (beach evening primrose) |
Mat-forming sand stabilizer that appears after the primary colonizers. It can grow in drifting sand, but also in (semi-)stabilized dunes and on rock cliffs. |
Native to northern Mexico and southern USA. Introduced to Australia, New Zealand, South Africa, China, Egypt, Spain. | Mediterranean climate, sunny exposure. Adapted to moderate salinity and sand movement. | Prefers well-drained slightly moist neutral soil, but can cope with dry conditions due to efficient water use. | Spreads readily by seed into dune areas. | From seed or by root division. | Medicinal use for treating sore throat and eye diseases. |
Panicum amarum (Bitter panicum, coastal panicgrass) | Stabilizer of semi-mobile dunes. Extensive fibrous root and rhizome system holds the sand in place. | USA South Atlantic and Gulf coast. | Mediterranean climate. Tolerates moderate saline overspray. | Well-drained poor sandy soil. Strongest growth with moderate sand accumulation around the plants. Replaces Ammophila in warmer regions. | By stolons or rhizomes. | Planting of young tillers, with some roots and rhizomes attached, preferably early spring. Should be mixed with other grasses, e.g. American beachgrass and sea oats. | |
Paspalum vaginatum (Seashore paspalum) | Excellent shoreline protector; spreads rapidly, forming dense stands that anchor soil particles and dissipate wave energy. Less suited for dune building. | Origin: Americas. Worldwide occurrence. | Tropical and subtropical zones. Tolerance of a wide range of conditions such as drought, saline or recycled water, varying soil pH, extended periods of low light intensity, flooding or extended wet periods. | Best suited to compacted inorganic marsh soils of moderate salinity. | Spreads by its rhizomes and stolons, forming a thick turf. | Nursery-raised plants or vegetative propagation. On dry sites: pieces of sod or rooted transplants; on wetter sites: bare-rooted rhizomes. It can be planted and grow where other species would not survive. | Good resistance to insects and diseases. |
Poa macrantha (dune bluegrass, seashore bluegrass[27]) | Sand-binding grass, with stolons and an extensive, strong rhizomatous root system. Stabilizes blowing and moving sand of foredunes. | Pacific coast of N. America from Alaska to California. Similar species: Poa douglasii in southern California and Poa billardierei (Sand tussock) in New Zealand. | Temperate climate. Sunny exposure. | Well drained sand soil. | By seeds and rhizomes. | Nursery-raised plants from locally collected seed, also by division of plants. | |
Salsola kali (common saltwort) | Pioneer species in the driftline and upper-beach zones. Roots, rhizomes and buried shoots reduce dune erosion under a swash regime[28]. | Native to northern and western Europe, from Norway to Portugal, including northern Russia. Introduced to America, Australia and New Zealand. | S. kali habitats include cool, temperate, desert, steppe, subtropical, arid life zones. It tolerates a very high range of annual rainfall and annual temperatures and saline soils[29]. | Organic-poor soils. Found in disturbed areas, including shingle and sand beaches. | Self-seeding annual plant; seeds remain viable for 6-12 months and are dispersed by wind, small rodents and birds. | Invasive species; where introduced it displaces native plants and competes for space, water and nutrients. | |
Scaevola plumieri / Scaevola taccada [30] | Sand-binding pioneer plant on beaches, sand dunes, sandbanks, tropical atolls, mangroves and seagrape habitats. Tolerates sand burial and contributes to dune building. S. plumieri and S. taccada are similar species. | Scaevola taccada native to South Asia, East Africa, Pacific islands; Scaevola plumieri native to East and South Africa, Ceylon. Introduced to (sub)tropical America south of Florida. | (Sub)tropical monsoon climate. Grows within in the salt spray area. | Well-drained light/medium shallow sandy soils, seasonally waterlogged. Alkaline/neutral pH. Preference for coral sand. | Fast dispersal along the coast line, canal banks, mangroves, and inland shorelines by fruits that can float for up to one year. Plant fragments or stems may be dispersed on vegetation rafts. | The species also grows from cuttings. | Invasive species in Florida and Caribbean region. Occurs often together with Ipomoea. |
Sesuvium postulacastrum (shoreline purslane) | Pioneer sand-colonising plant that grows on the upper beach and seaward slope of the frontal dune or beach ridge. It traps and holds wind-blown sand and tends to form small ridges or mounds. It does not survive complete burial under wind-blown sand. It also grows well in more protected littoral locations. | Native to Africa, Asia, Australia, North America and South America. | Worldwide in tropical and subtropical regions. Full sun exposure, very tolerant of salty conditions and very drought tolerant (established plants). | Well-drained poor sandy soil, sandy clay, coastal limestone and sandstone, tidal flats and salt marshes The plant tolerates acidic and alkaline soils. No irrigation or fertilizer needed. | The thick stems form roots at the nodes. | From herbaceous stem cuttings. | Was used medicinally to treat scurvy (vitamin C deficiency) and is sold in Asia as a vegetable. Also used for desalination and phytoremediation (soil cleaning by bioaccumulation of toxic substances). |
Spinifex sericeus / Spinifex littoreus | Pioneer species, highly efficient deep-rooting foredune builder. The upright shoots aid in reducing surface wind velocity and accumulate sand with frequent burial of stems and leaves. A spinifex-dominant dune has typically a low-angle dune face without blow-outs. | "Spinifex sericeus": Australia, New Zealand. "Spinifex littoreus": New Guinea, Indonesia, Malaysia, Philippines, Indochina, Indian Subcontinent, China, Japan. | Fast growth in summer, favored by warm conditions. Tolerant to high winds and salt spray. Withstands extreme temperatures and drought. | Establishes in raw sand. Stimulates sand deposition that in return favors growth. | By stolons (growth 5 m/year) and rhizomes. | 1) Seeds buried 10 cm in moist sand, after prior brush matting (high mortality rate). 2) Runners or tip cuttings of 0.5 m long planted in temperate season on a 1 m grid into moist sand at a depth of 25 cm. | Tolerant to swash. |
Sporobolus pumilus (Spartina patens, Saltmeadow Cordgrass) | Shore stabilizing grass once it is firmly settled. Most common in marshland, but also found in the dunes. | N America Atlantic coast from Newfoundland to Mexico. | Low drought tolerance; high salt tolerance. | Salty, wet habitat: marshland, moist dune sites. Highly adaptable to a range of soil conditions (loam, organic, sandy, clay). | Reproduces both through seed and vegetative rhizomatous roots. | Multi-stemmed transplants from uncrowded nursery stands. Plants 20 cm deep in moist zone. | |
Sporubolus virginicus (Seashore Dropseed) | Dune stabilizer on wind-eroded shorelines. Also used for stream bank and roadside slope stabilization. | Tropical zones of Africa, eastern Asia, Australasia, the Pacific, Caribbean, North and South America. | Tropical zones. Adapted to low rainfall and high salinity. | Moist, alkaline, nutrient-poor soil. Sandy or muddy seashores (often below high tide mark) and saline marshes. | Reproduces asexually by use of both stolons and rhizomes. | From rhizomes sections planted in a sterile, well drained medium in a greenhouse. | Grazing plant for cattle. |
Tamarix nilotica (Nile Tamarisk) | Shrub (2-5 m), sand binder for its extensive root system. Wind-blown sand comes to rest at the foot of the shrub, stimulating its growth and gradually creating a hummock. | Southeast Mediterranean region and east Africa. Also in the Nile valley. Other Tamarix species (T. aphylla, etc.) with similar characteristics around the Mediterranean and in the Middle East. | Adapted to arid subtropical climate, salt tolerant, capable to extract moisture from the underlying saline substrate. It tolerates temperatures from -10 to +50°C and frequent droughts. | Wide variety of soils, loamy soil preferred. | Tamarix can spread both in vegetative mode, by roots or submerged stems, and sexually, by seeds. Seeds can be dispersed by wind and by water. | Salt excreted in the form of litter or 'tears', through the glands in the leaves, causes soil salinization, reducing the growth of plants nearby[31]. | |
Uniola paniculata (Sea Oats) | Beach/dune grass with good sand-binding and dune-building capacity. Slow initial settlement. Very persistent. | USA South Atlantic and Gulf coast, Mexico. | Mediterranean, subtropical climate. Once established, low water requirement and resistant to salt spray. | Well-drained poor sandy soil. Growth stimulated by sand deposition. | By rhizomes. | Transplantation from wild stocks or nursery-grown 2-year old plants. Planting similar to Ammophila and Panicum; young plants require moist soil and low salinity. | |
Zygophyllum fontanesii / Tetraena fontanesii (sea grape) | Contributes to beach stability due to a strong root system; retains embryo dunes. | Western Sahara countries, Macaronesia, northeast Africa. | Mediterranean arid climate. Sunny exposure. Can withstand intense drought. Requires regular salt spray. | Grows best in coarse, calcareous sandy brackish soils on the dunes; also on rocky soils. | By seeds. | Seeds are very tolerant of salt water, but slow to germinate. Propagation by cuttings. |
Further reading
- Martínez M. L. and Psuty N. P. (Eds.) 2003. Coastal Dunes; Ecology and Conservation. Springer, 386 pp.
- Doody, J.P. 2013. Sand Dune Conservation, Management and Restoration. Coastal Research Library, Vol. 4, Springer, 303 pp.
References
- ↑ 1.0 1.1 1.2 1.3 Feagin, R. A., J. Figlus, J. C. Zinnert, J. Sigren, M. L. Martínez, R. Silva, W. K. Smith, D. Cox, D. R. Young, and G. Carter. 2015. Going with the flow or against the grain? The promise of vegetation for protection beaches, dunes, and barrier islands from erosion. Frontiers in Ecology and the Environment 13: 203–210
- ↑ Bryant, D.B., Anderson-Bryant, M., Sharp, J.A., Bell, G.L. and Moore, C. 2019. The response of vegetated dunes to wave attack. Coastal Engineering 152, 103506
- ↑ Silva, R., Martinez, M.L., Oderiz, I., Mendoza, E. and Feagin, R.A. 2016. Response of vegetated dune–beach systems to storm conditions. Coastal Engineering 109: 53–62
- ↑ 4.0 4.1 4.2 McLachlan, A. and Defeo, O. 2018. Coastal Dune Ecosystems and Dune–Beach Interactions. In The Ecology of Sandy Shores (Third Edition) 309-329. Academic Press
- ↑ Konlechner, T.M., Kennedy, D.M., Cousens, R.D. and Woods, J.L.D. 2019. Patterns of early-colonising species on eroding to prograding coasts; implications for foredune plant communities on retreating coastlines. Geomorphology 327: 404–416
- ↑ Hesp, P.A. 1991. Ecological processes and plant adaptations on coastal dunes. Journal of Arid Environments 21: 165-191
- ↑ Maun, M.A. 1998. Adaptations of plants to burial in coastal sand dunes. Canadian Journal of Botany 76: 713–738. doi: 10.1139/b98-058
- ↑ 8.0 8.1 Wiedemann, A.M. and Pickart, A.J. 2003. Temperate Zone Coastal Dunes. In: (Eds. Martínez M. L. and Psuty N. P.) Coastal Dunes; Ecology and Conservation. Springer
- ↑ 9.0 9.1 Doody, J.P. 2013. Sand Dune Conservation, Management and Restoration. Coastal Research Library, Vol. 4, Springer, 303 pages. Cite error: Invalid
<ref>
tag; name "D" defined multiple times with different content - ↑ Maun, M.A. 1994. Adaptations enhancing survival and establishment of seedlings on coastal dune systems. Vegetatio 111: 59–70
- ↑ Barbour, M., and Johnson, A.F. 1977. Beach and dune. In Barbour, M. and J. Major (eds.), Terrestrial vegetation of California. John Wiley and Sons, New York. Pages 223-270
- ↑ Martínez, M.L., Psuty, N.P. and Lubke, R.A. 2003. A Perspective on Coastal Dunes. In: (Eds. Martínez M. L. and Psuty N. P.) Coastal Dunes; Ecology and Conservation. Springer
- ↑ Doing, H. 1985. Coastal fore-dune zonation and succession in various parts of the world. Vegetatio 61: 65-75
- ↑ Hesp, P.A. 2003. Coastal Dunes in the Tropics and Temperate Regions: Location, Formation, Morphology and Vegetation Processes. In: (Eds. Martínez M. L. and Psuty N. P.) Coastal Dunes; Ecology and Conservation. Springer
- ↑ Oderiz, I., Knochelmann, N., Silva, R., Feagin, R.A., Martínez, M.L. and Mendoza, E. 2020. Reinforcement of vegetated and unvegetated dunes by a rocky core: A viable alternative for dissipating waves and providing protection? Coastal Engineering 158, 103675
- ↑ Nordstrom, K.A., Jackson, N.L., Freestone, A.L., Korotky, K.H. and Puleo, J.A. 2012. Effects of beach raking and sand fences on dune dimensions and morphology. Geomorphology 179: 106–115
- ↑ Hanley, M.E., Hoggart, S.P.G., Simmonds, D.J., Bichot, A., Colangelo, M.A., Bozzeda, F., Heurtefeux, H., Ondiviela, B., Ostrowski, R., Recio, M., Trude, R., Zawadzka-Kahlau, E. and Thompson, R.C. 2014. Shifting sands? Coastal protection by sand banks, beaches, and dunes. Coast. Eng. 87: 136–146
- ↑ Werner, C., Zumkier, U., Beyschlag, W. and Máguas, C. 2010. High competitiveness of a resource demanding invasive acacia under low resource supply. Plant Ecology 206 :83-96
- ↑ Marchante, H., Freitas, H. and Hoffmann, J.H. 2011. Post-clearing recovery of coastal dunes invaded by Acacia longifolia: is duration of invasion relevant for management success? Journal of Applied Ecology 48: 1295-1304
- ↑ Lea, C. 2005. Fact sheet: asiatic sand sedge. National Park Service, Washington, DC https://www.invasive.org/alien/fact/pdf/cako1.pdf
- ↑ de Lange, P.J. 2020. Carex pumila Fact Sheet. New Zealand Plant Conservation Network. https://www.nzpcn.org.nz/flora/species/carex-pumila/
- ↑ Jung, S.H., Kim, A.R., Lim, B.S., Seol, J.W. and Lee, C.S. 2019. Spatial distribution of vegetation along the environmental gradient on the coastal cliff and plateau of Janggi peninsula (Homigot), southeastern Korea. J. Ecology and Environment 43: 14 https://doi.org/10.1186/s41610-019-0110-y
- ↑ Harris, D and Davy, A.J. 1986. Strandline colonization by Elymus farctus in relation to sand mobility and rabbit grazing. Journal of Ecology 74: 1045-1056
- ↑ Isermann, M. and Rooney, P. 2014. Biological Flora of the British Isles: Eryngium maritimum. Journal of Ecology 102: 789–821
- ↑ Greipsson, S. and Davy, A.J. 1994. Leymus arenarius. Characteristics and uses of a dune-building grass. Icel. Agr. Sci. 8: 41–50
- ↑ Small, E. 2011. Alfalfa and relatives: evolution and classification of "Medicago". NRC Research Press, Ottawa, 727 pp.
- ↑ Oakes, A.J. 1990. Ornamental grasses and grasslike plants. Van Nostrand Reinhold publ., New York
- ↑ De Battisti, D, and Griffin, J.N. 2020. Below-ground biomass of plants, with a key contribution of buried shoots, increases foredune resistance to wave swash. Ann Bot. 125: 325-334. doi: 10.1093/aob/mcz125
- ↑ CABI. Invasive Species Compendium, https://www.cabi.org/isc/datasheet/50297
- ↑ CABI 2019. Invasive Species Compendium. www.cabi.org/isc/datasheet/48817
- ↑ Abdelgawad, A.A.M. 2017. Tamarix nilotica (Ehrenb) Bunge: A Review of Phytochemistry and Pharmacology. J. Microb. Biochem. Technol. 9: 544-553. doi: 10.4172/1948-5948.1000340