• Tidak ada hasil yang ditemukan

Journal of Tropical Forest Science 20(2): 132–138 (2008) 132

N/A
N/A
Protected

Academic year: 2024

Membagikan "Journal of Tropical Forest Science 20(2): 132–138 (2008) 132"

Copied!
7
0
0

Teks penuh

(1)

Journal of Tropical Forest Science 20(2): 132–138 (2008)

132

(2)

Journal of Tropical Forest Science 20(2): 132–138 (2008) 133

(3)

Journal of Tropical Forest Science 20(2): 132–138 (2008) 134

Retention (kg/m3)*

Treatment

5% solution 1% solution 0.1% solution

Tetraguanidinium ellagate in water 28.1 (0.8) 5.7 (1.1) 0.6 (4.4)

Tetracholine ellagate in water 29.7 (0.6) 5.9 (0.7) 0.6 (0.8)

Tetrakis-benzyltrimethylammonium ellagate in water 30.5 (0.5) 5.9 (0.2) 0.6 (1.4)

Tetrakis-tetramethylammonium ellagate in water 29.5 (0.9) 6.1 (1.0) 0.6 (0.8)

Ellagic acid in N-methylpyrrolidone 29.5 (2.3) 6.1 (1.3) 0.6 (0.7)

2,3,4,2’,3’,4’-hexamethoxy-6,6’-diisocyanato-diphenyl in dioxane 31.2 (2.1) 6.3 (1.2) 0.6 (0.8)

*Percent variance in parentheses

Solvent uptakes for water (593 l/m3), N-methylpyrrolidone (601 l/m3) and dioxane (606 l/m3) were noted.

Table 1 Mean preservative retention (kg/m

3

) of wafers

(4)

Journal of Tropical Forest Science 20(2): 132–138 (2008) 135

Water repellent effectiveness (%WRE)*

Treatment

5% solution 1% solution 0.1% solution

Tetraguanidinium ellagate in water 24 (13.0) 18 (12.2) 22 (11.9)

Tetracholine ellagate in water 24 (8.4) 25 (12.4) 22 (13.1)

Tetrakis-benzyltrimethylammonium ellagate in water 32 (3.7) 25 (10.9) 24 (11.8)

Tetrakis-tetramethylammonium ellagate in water 31 (5.0) 25 (10.4) 25 (9.5)

Ellagic acid in N-methylpyrrolidone -13 (12.9) -18 (10.8) 6 (10.4)

2,3,4,2’,3’,4’-hexamethoxy-6,6’-diisocyanato-diphenyl in dioxane -5 (4.1) -17 (9.6) -19 (7.7)

*Percent variance in parentheses

The water repellent effectiveness of the N-methylpyrrolidone and dioxane blanks were -5 (7.1%) and -3 (12.0%) respectively.

Table 2 Water repellent effectiveness (%WRE) of treated wafers

(5)

Journal of Tropical Forest Science 20(2): 132–138 (2008) 136

Dimensional stability (%ASE)*

Treatment

5% solution 1% solution 0.1% solution

Tetraguanidinium ellagate in water 31 (9.4) 25 (8.4) 25 (9.1)

Tetracholine ellagate in water 40 (9.5) 29 (5.7) 27 (12.8)

Tetrakis-benzyltrimethylammonium ellagate in water 30 (12.2) 33 (7.6) 29 (8.8)

Tetrakis-tetramethylammonium ellagate in water 42 (10.8) 32 (8.6) 31 (10.6)

Ellagic acid in N-methylpyrrolidone 25 (12.8) 21 (15.7) 18 (13.6)

2,3,4,2’,3’,4’-hexamethoxy-6,6’-diisocyanato-diphenyl in dioxane 25 (9.7) 24 (10.2) 20 (13.4)

*Percent variance in parentheses

The dimensional stability of the N-methylpyrrolidone and dioxane blanks were 19 (13.3%) and 30 (2.0%) respectively.

Table 3 Dimensional stability (%ASE) of treated wafers

(6)

Journal of Tropical Forest Science 20(2): 132–138 (2008) 137

(7)

Journal of Tropical Forest Science 20(2): 132–138 (2008)

138

Referensi

Dokumen terkait

The Table 1 shows that the mean of inhibition zone of roselle infusions of 5, 10, 20, and 40% is larger than the mean of inhibitions zones of katuk leaf infusion against

However, the emphasis of this research is that composite materials produced from readily available local materials such as Bamboo and Recycled HDPE should be developed for

Based on the mean objective functions from simulation results, the performance of the proposed methods for all images is better than the original of metaheuristic,

Mengacu pada Peraturan Daerah Provinsi Kalimantan Timur Nomer 02 Tahun 2011, nilai Baku Mutu pada kelas 3 (Keperluan perikanan) adalah 3 mg/L, terlihat

Table 2: Analysis of the mean of school factors School Environment Mean 1 My school is located in a very conducive environment 3.02 2 The classrooms in my school are very spacious

Table 2 The annual mean concentrations g/kg DM of water soluble carbohydrate WSC, crude protein CP and neutral detergent fibre NDF in three cultivars of perennial ryegrass in

Table of Contents MAPPING TSUNAMI HAZARD LEVELS IN PACITAN BEACH USING REMOTE SENSING METHODS Zahrotin Jamilah, Amien Widodo, Nita Ariyanti Department of Geophysical Engineering,

Anodonta woodiana were maintained in water tub that treated with lead II nitrate exposure PbNO32 0, 15, 25, 35 mg.L-1 for 7 days to determine the alteration of the damaged structure of