Rhizophora apiculata

Evaluation and Planning of Mangrove Restoration Programs in Sedari Village of Kerawang District, West Java: Contribution of PHE-ONWJ Coastal Development Programs

Background

The authors described a mangrove restoration project in Sedari Village of Kerawang District, West Java. According to the article, the main cause for mangrove degradation in this region is due to brackish water fish ponds called “tambak”. The authors described and evaluated the first four of six project phases through mangrove survivability and soil structure. 

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Preliminary assessment of post-Haiyan mangrove damage andshort-term recovery in Eastern Samar, central Philippines

Background

In this study, authors examined the natural ability of mangrove trees to recover after major storms and supertyphoons in the Philippines. Coastal mangroves are important for reducing the damage from these storms.

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Human Hydrographical Changes Interact with Propagule Predation Behaviour in Sri Lankan Mangrove Forests

Background

This article describes the relation between propagule predators and vegetation structure and environmental factors on a forest path. It also considers how human influence affects these interactions.

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A review of the floral composition and distribution of mangroves in Sri Lanka

Background

The article reviews literature on the numbers and distributions of Sri Lankan mangrove species and highlights the causes of overestimation. It also attempts to provide an accurate count based on standardized fieldwork over a 4-year period along the coast between Palatupana and Puttalam, Sri Lanka. The authors name some examples of mischaracterized or misidentified species from previous studies and address the importance of clearly defining the terms for mangroves.

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Reforestation of Mangroves after Severe Impacts of Herbicides during the the Viet Nam War: The Case of Can Gio

background

This article describes the detrimental impacts of chemicals used in the Viet Nam war on mangroves with a focus on the reforestation efforts of the mangroves of the Can Gio district. In the 1980s, poor management, combined with stress from fuelwood collection and conversion to shrimp ponds, limited the success of mangrove restoration. Between 1978 and 1989,29,583 ha of Rhizophora apiriculata were planted; however, due to a lack of technical experience and a very high planting density, by 1990 only 18,125 ha remained. 35,000 ha of mangrove were replanted by 1996 and, in 2001, about 20,000 ha still survived.

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Local Mangrove Planting in the Philippines: Are Fisherfolk and Fishpond Owners Effective Restorationists?

background

This paper evaluates ecological characteristics of mangrove plantations planted by local communities in the Philippines and compares them to natural mangrove forests nearby. 

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Community Based Ecological Mangrove Rehabilitation (CBEMR) in Indonesia

Background

While large-scale wetland/mangrove restoration projects have been successful worldwide efforts in Indonesia have largely failed. This is due to technical issues but also tenure issues. Considering pass projects and attempts, Ecological Mangrove Rehabilitation (EMR) has been identified as a potential best practice for Indonesia.  

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Mangrove reforestation in Vietnam: the effect of sediment physicochemical properties on nutrient cycling

Background

Mangrove forests depend on unique physicochemical properties found in tidal coastal sites. One of the main reasons why mangrove reforestation fails is due to changes in the sediment properties that occurred under deforestation conditions. The iron sulphides common in mangrove sediments are oxidated to sulphuric acid, drastically lowering the sediment pH. Other changes also take place as nutrients leach. This study assesses the effects of pH and redox potential on phosphorus and nitrogen cycling in reforested mangrove stands in southern Vietnam.

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