Establishment of Avicennia marina mangroves on accreting coastline at Sungai Haji Dorani, Selangor, Malaysia
Avicennia marina saplings were established within a restoration area at Sg. Hj. Dorani, Malaysia between May and August 2010. Sapling establishment was achieved following the construction of segmented and hard breakwater as mitigating measure against coastal erosion. Geostructures known as brush fas...
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Veröffentlicht in: | Estuarine, coastal and shelf science coastal and shelf science, 2011-10, Vol.94 (4), p.334-342 |
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creator | Tamin, Noraini Mohd Zakaria, Rozainah Hashim, Roslan Yin, Yu |
description | Avicennia marina saplings were established within a restoration area at Sg. Hj. Dorani, Malaysia between May and August 2010. Sapling establishment was achieved following the construction of segmented and hard breakwater as mitigating measure against coastal erosion. Geostructures known as brush faschines were installed within the restoration area as secondary sediment and seed traps. There was a steady increase in the sand content of the soil from 5% in November 2008 to 18% in May 2010. The dominant soil content was silt but it fluctuated and declined slightly over the same period, between 80% in November 2008 and 72% in May 2010. The accreting shoreline behind the breakwater had stabilised within 18 months. Subsequently, the first batch of
A. marina wild seedlings or wildings was established on the mud surface in September 2009. Only about 10% of these wildings survived and showed high survival rate (90%) over the next eight months. Wildings that were naturally established near mother trees showed good growth performance. No wilding was established after the fruiting season in August 2010 as all seeds that were dispersed into the restoration area were washed away by September 2010. Tall,
A. marina wild saplings (1 m) planted within the restoration area showed higher survival rate (80%) compared to planted saplings of
Rhizophora apiculata (30%). Final planting of a thousand 1 m tall
A. marina wild saplings was carried out from June 2010, in clumps of 20 and in 1 m × 1 m spacing. By the end of September 2010 clusters of regenerating
A. marina mangroves about 1.5 m tall were successfully established on the accreting coastline. |
doi_str_mv | 10.1016/j.ecss.2011.07.009 |
format | Article |
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A. marina wild seedlings or wildings was established on the mud surface in September 2009. Only about 10% of these wildings survived and showed high survival rate (90%) over the next eight months. Wildings that were naturally established near mother trees showed good growth performance. No wilding was established after the fruiting season in August 2010 as all seeds that were dispersed into the restoration area were washed away by September 2010. Tall,
A. marina wild saplings (1 m) planted within the restoration area showed higher survival rate (80%) compared to planted saplings of
Rhizophora apiculata (30%). Final planting of a thousand 1 m tall
A. marina wild saplings was carried out from June 2010, in clumps of 20 and in 1 m × 1 m spacing. By the end of September 2010 clusters of regenerating
A. marina mangroves about 1.5 m tall were successfully established on the accreting coastline.</description><identifier>ISSN: 0272-7714</identifier><identifier>EISSN: 1096-0015</identifier><identifier>DOI: 10.1016/j.ecss.2011.07.009</identifier><identifier>CODEN: ECSSD3</identifier><language>eng</language><publisher>Kidlington: Elsevier Ltd</publisher><subject>accreting coastline ; Animal and plant ecology ; Animal, plant and microbial ecology ; Biological and medical sciences ; Brackish ; Brackish water ecosystems ; Breakwalls ; Coastal ; enrichment planting ; Fundamental and applied biological sciences. Psychology ; Malaysia ; mangroves ; Marinas ; Restoration ; Sand ; Seeds ; Soil (material) ; Sungai Haji Dorani ; Survival ; Synecology</subject><ispartof>Estuarine, coastal and shelf science, 2011-10, Vol.94 (4), p.334-342</ispartof><rights>2011 Elsevier Ltd</rights><rights>2015 INIST-CNRS</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c472t-3128ed30feac4e47bb45813bca2efc4e167ecec52eac4ba583b73b3b6459f8bc3</citedby><cites>FETCH-LOGICAL-c472t-3128ed30feac4e47bb45813bca2efc4e167ecec52eac4ba583b73b3b6459f8bc3</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://dx.doi.org/10.1016/j.ecss.2011.07.009$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>314,780,784,3550,27924,27925,45995</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=24492912$$DView record in Pascal Francis$$Hfree_for_read</backlink></links><search><creatorcontrib>Tamin, Noraini Mohd</creatorcontrib><creatorcontrib>Zakaria, Rozainah</creatorcontrib><creatorcontrib>Hashim, Roslan</creatorcontrib><creatorcontrib>Yin, Yu</creatorcontrib><title>Establishment of Avicennia marina mangroves on accreting coastline at Sungai Haji Dorani, Selangor, Malaysia</title><title>Estuarine, coastal and shelf science</title><description>Avicennia marina saplings were established within a restoration area at Sg. Hj. Dorani, Malaysia between May and August 2010. Sapling establishment was achieved following the construction of segmented and hard breakwater as mitigating measure against coastal erosion. Geostructures known as brush faschines were installed within the restoration area as secondary sediment and seed traps. There was a steady increase in the sand content of the soil from 5% in November 2008 to 18% in May 2010. The dominant soil content was silt but it fluctuated and declined slightly over the same period, between 80% in November 2008 and 72% in May 2010. The accreting shoreline behind the breakwater had stabilised within 18 months. Subsequently, the first batch of
A. marina wild seedlings or wildings was established on the mud surface in September 2009. Only about 10% of these wildings survived and showed high survival rate (90%) over the next eight months. Wildings that were naturally established near mother trees showed good growth performance. No wilding was established after the fruiting season in August 2010 as all seeds that were dispersed into the restoration area were washed away by September 2010. Tall,
A. marina wild saplings (1 m) planted within the restoration area showed higher survival rate (80%) compared to planted saplings of
Rhizophora apiculata (30%). Final planting of a thousand 1 m tall
A. marina wild saplings was carried out from June 2010, in clumps of 20 and in 1 m × 1 m spacing. By the end of September 2010 clusters of regenerating
A. marina mangroves about 1.5 m tall were successfully established on the accreting coastline.</description><subject>accreting coastline</subject><subject>Animal and plant ecology</subject><subject>Animal, plant and microbial ecology</subject><subject>Biological and medical sciences</subject><subject>Brackish</subject><subject>Brackish water ecosystems</subject><subject>Breakwalls</subject><subject>Coastal</subject><subject>enrichment planting</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Malaysia</subject><subject>mangroves</subject><subject>Marinas</subject><subject>Restoration</subject><subject>Sand</subject><subject>Seeds</subject><subject>Soil (material)</subject><subject>Sungai Haji Dorani</subject><subject>Survival</subject><subject>Synecology</subject><issn>0272-7714</issn><issn>1096-0015</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2011</creationdate><recordtype>article</recordtype><recordid>eNp9kE9vFDEMxSMEEkvhC3DKBXHpDEnmT2YkLlVbKFIRh8I5cryeJavZpMSzK_Xbk9FWHDlZst-z_X5CvNeq1kr3n_Y1IXNtlNa1srVS4wux0WrsK6V091JslLGmsla3r8Ub5n3p6q4xGzHf8gJ-Dvz7QHGRaZJXp4AUYwB5gBziWuIupxOxTFECYqYlxJ3EBLzMIZKERT4c4w6CvIN9kDcpQwyX8oHm4kz5Un6HGZ44wFvxaoKZ6d1zvRC_vtz-vL6r7n98_XZ9dV9ha81SNdoMtG3URIAttdb7tht04xEMTaWje0tI2Jl17qEbGm8b3_i-7cZp8NhciI_nvY85_TkSL-4QGGku_1A6shvGUXd9QVKU5qzEnJgzTe4xh5L7yWnlVrJu71aybiXrlHWFbDF9eF4PjDBPJS4G_uc0bTuaUZui-3zWUcl6CpQdY6CItA2ZcHHbFP535i_tDZDd</recordid><startdate>20111020</startdate><enddate>20111020</enddate><creator>Tamin, Noraini Mohd</creator><creator>Zakaria, Rozainah</creator><creator>Hashim, Roslan</creator><creator>Yin, Yu</creator><general>Elsevier Ltd</general><general>Elsevier</general><scope>IQODW</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>8FD</scope><scope>FR3</scope><scope>KR7</scope></search><sort><creationdate>20111020</creationdate><title>Establishment of Avicennia marina mangroves on accreting coastline at Sungai Haji Dorani, Selangor, Malaysia</title><author>Tamin, Noraini Mohd ; Zakaria, Rozainah ; Hashim, Roslan ; Yin, Yu</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c472t-3128ed30feac4e47bb45813bca2efc4e167ecec52eac4ba583b73b3b6459f8bc3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2011</creationdate><topic>accreting coastline</topic><topic>Animal and plant ecology</topic><topic>Animal, plant and microbial ecology</topic><topic>Biological and medical sciences</topic><topic>Brackish</topic><topic>Brackish water ecosystems</topic><topic>Breakwalls</topic><topic>Coastal</topic><topic>enrichment planting</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>Malaysia</topic><topic>mangroves</topic><topic>Marinas</topic><topic>Restoration</topic><topic>Sand</topic><topic>Seeds</topic><topic>Soil (material)</topic><topic>Sungai Haji Dorani</topic><topic>Survival</topic><topic>Synecology</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Tamin, Noraini Mohd</creatorcontrib><creatorcontrib>Zakaria, Rozainah</creatorcontrib><creatorcontrib>Hashim, Roslan</creatorcontrib><creatorcontrib>Yin, Yu</creatorcontrib><collection>Pascal-Francis</collection><collection>CrossRef</collection><collection>Technology Research Database</collection><collection>Engineering Research Database</collection><collection>Civil Engineering Abstracts</collection><jtitle>Estuarine, coastal and shelf science</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Tamin, Noraini Mohd</au><au>Zakaria, Rozainah</au><au>Hashim, Roslan</au><au>Yin, Yu</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Establishment of Avicennia marina mangroves on accreting coastline at Sungai Haji Dorani, Selangor, Malaysia</atitle><jtitle>Estuarine, coastal and shelf science</jtitle><date>2011-10-20</date><risdate>2011</risdate><volume>94</volume><issue>4</issue><spage>334</spage><epage>342</epage><pages>334-342</pages><issn>0272-7714</issn><eissn>1096-0015</eissn><coden>ECSSD3</coden><abstract>Avicennia marina saplings were established within a restoration area at Sg. Hj. Dorani, Malaysia between May and August 2010. Sapling establishment was achieved following the construction of segmented and hard breakwater as mitigating measure against coastal erosion. Geostructures known as brush faschines were installed within the restoration area as secondary sediment and seed traps. There was a steady increase in the sand content of the soil from 5% in November 2008 to 18% in May 2010. The dominant soil content was silt but it fluctuated and declined slightly over the same period, between 80% in November 2008 and 72% in May 2010. The accreting shoreline behind the breakwater had stabilised within 18 months. Subsequently, the first batch of
A. marina wild seedlings or wildings was established on the mud surface in September 2009. Only about 10% of these wildings survived and showed high survival rate (90%) over the next eight months. Wildings that were naturally established near mother trees showed good growth performance. No wilding was established after the fruiting season in August 2010 as all seeds that were dispersed into the restoration area were washed away by September 2010. Tall,
A. marina wild saplings (1 m) planted within the restoration area showed higher survival rate (80%) compared to planted saplings of
Rhizophora apiculata (30%). Final planting of a thousand 1 m tall
A. marina wild saplings was carried out from June 2010, in clumps of 20 and in 1 m × 1 m spacing. By the end of September 2010 clusters of regenerating
A. marina mangroves about 1.5 m tall were successfully established on the accreting coastline.</abstract><cop>Kidlington</cop><pub>Elsevier Ltd</pub><doi>10.1016/j.ecss.2011.07.009</doi><tpages>9</tpages><oa>free_for_read</oa></addata></record> |
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subjects | accreting coastline Animal and plant ecology Animal, plant and microbial ecology Biological and medical sciences Brackish Brackish water ecosystems Breakwalls Coastal enrichment planting Fundamental and applied biological sciences. Psychology Malaysia mangroves Marinas Restoration Sand Seeds Soil (material) Sungai Haji Dorani Survival Synecology |
title | Establishment of Avicennia marina mangroves on accreting coastline at Sungai Haji Dorani, Selangor, Malaysia |
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