Tukey (HSD) pairwise comparisons of

Tukey (HSD) pairwise comparisons of yearly mean numbers showed rehabilitated plots were not
significantly different (means of log values were
1.48 for 7-year-old plots and 1.39 for 5-year-old
plots), while control plots had significantly lower
numbers of species (mean of log value 0.46).
There was no significant difference between sites in
average density of forest species (F2,8 = 1.68, P =
0.2951, df 2), but significant differences between
years and controls (F2,8 = 13.37, P = 0.0169, df 2).
Tukey (HSD) pairwise comparisons of yearly mean
density showed that the rehabilitated plots were not
significantly different (means of log values were 0.67
for 7-year-old plots and 0.50 for 5-year-old plots)
while control plots had significantly lower numbers
of recruited species than the 7-year-old plots (mean
of log value was 0.10), but similar numbers to the 5-
year-old plots. If the rate of recruitment is reflected in
both the number of species and density of seedlings
then both the preceding analyses suggest that it is
greater in plantations than in controls. There were
significant negative correlations between abundance
and cover (r = −0.2447, n = 82, P , 0.05) and also
between diversity and cover, (r = −0.2381, n = 82,
P , 0.05).
Birds were important as dispersal vectors, especially
in fragmented landscapes where foraging may be required over larger areas. Higher proportions of
water dispersed species were recorded at the riparian
sites (Mulgrave, Eubenangee, and Backshall’s) (Fig. 4).
There was a dominance of small-seeded taxa in
all plots, but the trend was particularly evident in
the control plots and the isolated site, (Fig. 5, cf.
Appendix B). Eighty-two percent of the colonising
species had small seeds (,10 mm diameter), 17%
of species had intermediate size seeds (10–20 mm
diameter), and 1% had large seeds (.20 mm).
Growth forms were well represented in the tree and
vine categories, with canopy trees being less common
in the controls and the isolated site (Table 1). Grasses
and herbs were more abundant in the control plots.

Results (Indonesian) 1:

Tukey (HSD) pairwise perbandingan jumlah rata-rata tahunan menunjukkan direhabilitasi plot bukanlahsecara signifikan berbeda (berarti log adalah nilai-nilai1,48 untuk 7-tahun plot dan 1.39 untuk 5 tahunPlot), sementara plot kontrol telah secara signifikan lebih rendahJumlah spesies (berarti nilai log 0,46).Ada tidak ada perbedaan yang signifikan antara situs dirata-rata kepadatan spesies hutan (F2, 8 = 1,68, P =0.2951, df 2), tapi perbedaan yang signifikan antaratahun dan kontrol (F2, 8 = 13,37, P = 0.0169, df 2).Tukey (HSD) perbandingan pairwise berarti tahunankepadatan yang menunjukkan bahwa plot direhabilitasi tidaksecara signifikan berbeda (berarti nilai log itu 0,67untuk plot 7 tahun dan 0,50 untuk plot 5 tahun)Sementara plot kontrol telah secara signifikan lebih rendah nomorspesies yang direkrut dari plot 7 tahun (rata-ratalog nilai adalah 0,10), tetapi angka-angka serupa untuk 5 -Plot tahun. Jika tingkat rekrutmen tercermin dalamnomor kedua spesies dan kepadatan bibitkemudian kedua analisis sebelumnya menunjukkan bahwa itu adalahlebih besar di perkebunan daripada di kontrol. Terdapatkorelasi negatif yang signifikan antara kelimpahandan penutup (r = −0.2447, n = 82, P, 0,05) dan jugaantara keragaman dan penutup, (r = −0.2381, n = 82,P, 0,05).Burung itu penting sebagai vektor penyebaran, terutamalanskap terfragmentasi mana mencari makan mungkin diperlukan atas area yang lebih besar. Proporsi yang lebih tinggi darispesies tersebar air tercatat di ripariansitus (Yokohama, Eubenangee dan Backshall) (gambar 4).Ada dominasi taksa kecil-unggulan diSemua plot, tetapi tren ini terutama nyata dalamPlot kontrol dan situs terisolasi, (gambar 5, cf.Lampiran B). Delapan puluh dua persen dari menjajahispesies mempunyai biji kecil-kecil (, diameter 10 mm), 17%spesies mempunyai biji ukuran menengah (10-20 mmdiameter), dan 1% memiliki besar biji (.20 mm).Pertumbuhan bentuk diwakili dengan baik di pohon danKategori anggur, dengan kanopi pepohonan yang kurang umumdalam kontrol dan situs terisolasi (Tabel 1). Rumputdan herbal lebih berlimpah di plot kontrol.