Infection of heartwood by decay fungi (heartrot) is a concern for growers of Acacia mangium for solidwood products as the incidence can be high in some regions of Indonesia. Variation of heartrot incidence for different provenances of A. mangium was determined using two field trials in Sumatra, Indonesia. In a Riau Province trial of 21 provenances, the effect of provenance was statistically significant for natural heartrot incidence, which ranged from 1.6% to 27.2%. In a smaller trial using artificial inoculation in South Sumatra, heartwood infection incidence ranged from 39.4% to 70.8% across six provenances and both wound type and provenance were statistically significant factors. There was also significant variation in sapwood infection length related to provenance. Wood extractives (yield, total phenols, protein-precipitable tannin and 2,3-trans-3,4¢,7,8-tetrahydroxyflavanone) were quantified from a subsample of trees for each trial. However, no significant differences in extractive concentration were detectable according to provenance and evidence for a relationship between heartwood extractives and heartrot incidence was generally poor. While further studies need to be completed to establish the basis for heartrot incidence, results from these trials allow for recommendations on provenance selection to reduce heartrot incidence and provide information for further genetic selection programmes.

Biodiversity loss can be drastically aggravated by mining activities. Opened pit mining removes all material, including vegetation, above the ore deposit. Cement industries always implement opened mining as they process all rocks into cement. Restoration is known as the best human interference to drive the damaged ecosystem to recover. This study aimed to observe vegetation that was naturally grown under Pinus sp after 20 years of planting on ex-cement mining. The study was conducted in Sukabumi District, in three sites that were distributed in Cicantayan (2 sites) Sub District and Cibadak Sub District. Each location disses ivided into three points to conduct analysis vegetation in transects, for trees 2 units (10 x 10 m), shrubs 4 units (5 x 5 m), and grasses 5 units (1x1 m). The study resulted after 20 years of planting with Pinus (3 x 3 m) the sites recorded have been inhabited by 13 new species. They are 4 woody trees species, 4 species of shrubs, and 5 species of under-story (grasses). Tree stratum new inhabitants are Ficus spp, Macaranga gigantea, Schima wallichii, and Hibiscus tilliaceus, with the important value index (IVI) 57.83%; 53.67%; 33.17 %, 26.5%; respectively. Shrub’s stratum is inhabited by Mimosa invisa (IVI 76.66%); Eupatorium odoratum (IVI 76.66 %); Melastoma malabathricum (IVI 73.83%); and Clibadium suninamensis (IVI 72.837%). Whereas grasses stratum inhabited by Imperrata cyllindrica (IVI 98.77%); Brachiaria decumbens (IVI 98.60%); Themedia gigantea (IVI 43.11%); Setaria spp (IVI 31.83%), Cymbophogon citratus (IVI 27.69%). Shortly, restoration has encouraged natural colonization even acid mine drainage on the body waters remains occurred.