Fifth Re-Examination of the Permanent Vegetation Quadrats on Little Barrier Island

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Fifth Re-Examination of the Permanent Vegetation Quadrats on Little Barrier Island TANE 28,1982 FIFTH RE-EXAMINATION OF THE PERMANENT VEGETATION QUADRATS ON LITTLE BARRIER ISLAND by C.J. West* and P.J. Bellingham * Department of Botany, University of Auckland, Private Bag, Auckland t School of Forestry, University of Canterbury, Private Bag, Christchurch SUMMARY Two permanent vegetation quadrats established in 1954 and last examined in 1971 were re-examined in 1981. While there has been comparatively little change in the frequency and density of species in Quadrat 1, there has been considerable change in Quadrat 2 with Agathis australis now the most abundant species. Several species are recorded for the first time in Quadrat 2.The frequency of species in the ground cover and epiphytic vegetation is recorded for the first time. Diameters of poles and saplings (Quadrat 1) and poles (Quadrat 2) are included for use in later examinations of these quadrats. INTRODUCTION In May 1954 two permanent quadrats were established in a regenerating Leptospermum ericoides stand along the Thumb Track on Little Barrier Island in order to quantitatively assess changes in vegetation with time. Since their establishment the quadrats have been examined in August 1958 (Percy 1958), August 1963 (English and Brock 1964), August 1967 (Parris and Keen 1968) and April 1971 (Parris 1971). The present examination took place in August 1981. Details of the location of the quadrats are given by Bellingham and Percy (1954) and Parris and Keen (1968). However, the marker pegs referred to, on the track, have'been removed and the quadrats were relocated by reference to clues given in these two papers. No pegs were available to replace the removed markers so additional information is supplied. Both quadrats are on the eastern side of the track. Quadrat 1 is above the 200 ft altitude marker and is 31.4 m up the track from the edge of the "Moss Clearing". Peg number 4 (see Fig. 1) is approximately 1.5 m from the edge of the track at this point, and is concealed behind a Leptospermum ericoides trunk. All four corner pegs are present (Fig. 1). Quadrat 2 is below the 600 ft altitude marker. This quadrat was relocated using the compass bearing of 126° from the only large Agathis australis on the western side of the track which fitted the description given by Bellingham and Percy (1954). Corner peg number 1 (see Fig. 1) 7 8 is located near a 1.5 m tall Cyathea dealbata. Peg number 2 is near a clump of Collospermum hastatum while peg number 3 is missing altogether. There is a mature Knightia excelsa between the western edge of the quadrat and the track (Fig. 1). SAMPLING METHODS An altered version of English and Brock's (1964) method of sampling was used. The vegetation was divided as follows: Poles. Greater than 10 cm D.B.H. (diameter at breast height = 1.4 m above ground level on the highest side of the tree). Saplings. Between 2.5 and 10.0 cm D.B.H. which were further subdivided into: A. 7.5 to 10.0 cm D.B.H. B. 5.0 to 7.5 cm D.B.H. C. 2.5 to 5.0 cm D.B.H. Striplings. Less than 2.5 cm D.B.H. and taller than 30 cm. These were further subdivided into height classes: A. 3.0 to 4.5 m B. 1.5 to 3.0 m C. 30cm to 1.5 m Seedlings. Dicotyledons (excluding Metrosideros perforata), gymnosperms and tree ferns less than 30 cm in height. Ground cover and Epiphytes. Cryptogams (excluding tree ferns) and monocotyledons. Density was not recorded for this category. Canopy heights were assessed but not measured. Quadrat 1 is a square (30 ft x 30 ft) while Quadrat 2 is a rectangle (60 ft x 30 ft). Each quadrat was divided into 6 ft* plots which were sampled separately as above. Because of the missing corner peg and the more variable terrain of Quadrat 2, 55 such plots were sampled instead of 50. There was certainly no overlap of plots. Thus the results obtained from the re-examination of this quadrat are not strictly comparable with previous, results. Fig. 1 shows the layout of the plots within the quadrats. Except where otherwise referenced, nomenclature follows Allan (1961) for lycopods, ferns and dicotyledons, Moore and Edgar (1970) for native monocotyledons and Healy and Edgar (1980) for exotic monocotyledons. RESULTS The raw data obtained per plot, have been lodged at the University of Auckland and can be made available on request. Pole and sapling diameters are recorded in Appendices I and II. 9 Frequency (F) and density (D) were calculated as follows :- F = plots in which species occurs x 100 total no. of plots D = total no. of individuals of a given species total area of quadrat (yd2) In Table 1 and Table 2 the above parameters have two values each. The value in parenthesis indicates the total frequency and density of each species. The first value in each instance excludes seedling numbers and is therefore comparable with previous work. For some species, e.g. Coprosma rhamnoides (Table 1) and C. spathulata (Table 2), the inclusion of seedlings in frequency and density values greatly increases the ranking of these species within each quadrat. Density could not be recorded for epiphytes and ground cover species because individual plants are often very difficult to define although frequency was recorded by the number of plots in which a plant was rooted. Frequency should be recorded in later examinations of the permanent quadrats in view of the large number of new, non-ephemeral species recorded since 1971 (Table 3, Table 4). DISCUSSION Quadrat 1 The canopy is formed by approximately 12 m tall Leptospermum ericoides with a subcanopy at about 4 m comprised of Coprosma arborea, Pittosporum umbellatum and Myrsine australis. There is a very sparse understorey mostly of M. australis with some Melicytus ramiflorus. Ground cover is largely Doodia media with scattered, quite large Asplenium oblongifolium. Leptospermum ericoides remains the canopy species but there has been a decline to nearly half the number originally present (Table 1); there are several fallen trees at the lower side (south-east) of the quadrat. Coprosma arborea remains the largest contributor to the sapling category, but Pittosporum umbellatum appears to be assuming greater importance in this category. Both species are actively growing through the sapling size classes and may form a low canopy when the remaining Leptospermum ericoides dies out. Myrsine australis is still the most abundant in the stripling category. Overall, though, there has been a marked decline in numbers of most species present; Pittosporum tenuifolium is no longer present and Geniostoma ligustrifolium, recorded as seedlings by Parris (1971), has failed to become established. However, the first recorded appearance of Rhopalostytis sapida and Pseudopanax crassifolius x 10 Table 1. Species found in Quadrat 1 arranged in order of density. Figures in parenthesis for density and frequency include seedlings. DENSITY FREQUENCY SAPLINGS STRIPLINGS SPECIES YEAR POLES A B C ABC SEEDLINGS Nestegis lanceolata 1954 0.01 2 1963 0.03 10 1 1 2 - - - 1967 0.04 14 1 1 2 3 _ 1971 0.04 14 1 2 - - Spars- e 18(22) 2 2 2 4 4 1981 0.04 (0.05) 1 3 2 - Nothofagus truncata 1954 0.02 6 - _ (1958) Present -1 -2 1963 0.02 6 - _ 1967 0 .0! h _ _ 1 3 -Present 1971 0.02 6 - _ 3 Absent 1981 0.03(0.04) 13(20) 2 1 1 7 3 Knightia excelsa 1954 _ _ _ _ - (1958) present x x 1963 0.03 10 2 2 1 - 1967 I .03 8 -1 2 2 1 - 2 -Sparse 1971 0.04 8 1 . 1981 0.02(0.03) 7(16) -1 3 12 1 5 Geniostoma Ligustrifolium 1954 0.05 16 - - - 1963 0.02 8 4 1967 0.05 18 -1 B - 1971 0.05 16 1 e Absen- t 1981 0.01(0.03) 7(13) 2 2 4 Pseudopanax discolor 1954 0.01 2 . _ 1963 0.02 6 1 2 1967 0.03 4 1 2 - 1971 D.0J 2 ; - 1981 0.01(0.02) 2(9) - 4 '• Corokia buddleoides 1954 0.01 2 _ _ 1963 0.01 2 i 1[)67 0.01 2 i - 1971 0.01 2 ; Absen- t 1981 0.01(0.01] 4(4) Absent 3 Beilschmiedia taua 1954 0.01 2 - (1958) Present 1963 0.02 4 i 2 1967 0.02 4 1 2 - 1971 0.01 4 1 1 -Absent 1981 0.01(0.01) 2(2) - I Absent Pittosporum cornifolium 1981 0.01(0.01) 4(4) 1 1 4(4) Absent Toronia toru (Johnsons Briggs 1981 0.01(0.01) .: 1975) Pseudopanax lessonii 1981 0.01(0.01) 2(2) ! 1 Leptospermum scoparium 1981 0.01(0.01) 2(2) 1 Absent Dysoxylum spectabile 1981 x (0.01) x(4) 2 Clematis paniculata 1961 x (0.01) x(2) 1 Nestegis cunninghami 1954 0.01 2 . (Johnson 1959) 1963 0.04 12 - 2 2 1 1 - 1967 0.02 6 2 1 _ - 1971 0.02 6 1 1 1 1 _ Absent 1981 Absent * x Coprosma lucida 19 54 0.01 2 - - 196 3 0.01 2 1967 0.01 2 1971 0.01 _ Absent 1981 2 * x Pseudopanax crassifolius 1954 0.02 4 1963 0.01 2 1 1967 x ... 1971 x X Absent 1981 z Absent x * Cyathea medullaris 1954 0.03 10 1963 X X 1967 X X Absent 1 07 1 X * Absent 1981 X Numbers in each class as * 1963 4.5 3.0 5.0 6.5 1.6 11.1 68 5 of total number 1967 4.0 2.1 4.3 4.7 1.3 11.7 71 9 1971 5.8 3.9 5.6 6.7 1.7 15.0 61 4 1981 (excluding seedlings) 3.5 2.4 1.7 4.0 4.1 16.4 67 7 1.8 1.3 0.9 2.1 2.3 8.6 35 5 47.6 x = not recorded.
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