
Vegetation and Climate in the Dunedin District
[Received by the Editor, August 19, 1955.]
Abstract
This paper presents some results of a survey of vegetation and climate on the hills near Dunedin which provide evidence of vegetation changes shortly preceding those for which European settlement has been responsible, and reveal some difficulties in correlating rainfall, evaporation and temperature records at selected sites with the type of vegetation they carry to-day. A map is presented which shows the distribution of indigenous coniferous forest, silver-beech, and snow-tussock, and the areas over which log remains of Podocarpus hallii and Dacrydium biforme and surface dimpling provide evidence that the snow-tussock has recently replaced forest. Most existing silver-beech forests are shown to be regenerating vigorously and tending to encroach upon snow-tussock and coniferous forest, while regeneration rates of the conifers appear generally low. The snow-tussock is subject to invasion by shrubs and trees or fescue-tussock, particularly if heavily grazed after burning.
Rainfall and evaporation records for numerous temporary stations established over the area are also mapped The 45in isohyet is shown to lie to the west of a line joining Flagstaff and Silver Peak, while land above 2,000ft on Maungatua receives over 40in of rain annually. Temperatures fall with altitude and evaporation tends to do likewise. Frost temperatures are recorded which show that marked inversion patterns develop in grassland areas. Persistence of forest (and particularly of D. biforme) on the summit of Mt. Cargill is correlated with high rainfall (54in), low evaporation rate, and frequent sea-fogs, but the upper slopes of the tussock-covered Swampy Hill and Maungatua have not proved drier than their seaward faces on which forest persists. It is suggested that these areas of snow-tussock replaced forest that would have remained had it not been destroyed by fires of Maori origin. In the northern part of the district, however, there are indications that dry N-W winds may be directly responsible for treelessness.
In this paper an attempt is made to elucidate the relative importance of present and past climate and human intervention in determining the pattern of vegetation on the hills near Dunedin. Brief accounts of the flora and plant communities of this area have been published (Simpson and Scott-Thomson 1928, 1938; D.N.F.C., 1932) and fuller descriptions prepared in the course of the present survey have been deposited in the library of the Otago University (Wardle, 1953; Mark, 1954).
Methods
1.Estimation of rainfall
A few official rain-gauges have contributed to the records presented on Map I, but most of the data are from improvised apparatus (Fig. 1) read at intervals of 4–6 weeks, either over the period September, 1952 to August, 1953, or April, 1953 to March, 1954. A spirit level was used to adjust each funnel in the field, and the exact area of its mouth was measured with a planimeter. In the beginning each can was primed with that quantity of water which it retained when inverted with the funnel removed. The reliability of these instruments was tested in two ways.
(a) Gauges were maintained alongside official ones at Lake Mahinerangi and at Musselburgh. The annual total recorded by the improvised gauge at Lake Mahinerangi was 31.54ins, while the official record was 31.18ins. At Musselburgh, the mean of two improvised gauges was 29.40ins and the official record 31.62ins. This larger discrepancy was undoubtedly due to the cans being placed on the surface of the lawn where they were subject to heating by the sun. At Lake Mahinerangi and in the field, cans were set in the ground and a cairn built about the base of the funnel. This protected them from heating and from freezing.
(b) In four localities two gauges were sited close together. The differences over the year were .01, .01, .65, and 1.30ins. Such differences are unimportant.
Rainfall figures entered upon Map I are suggested annual means Over the northern hills, where the records were taken between September, 1952, and August, 1953, they are the actual measurements made since all official stations in the district had recorded a rainfall over that period very close to their mean for the last ten years. But the corresponding means for Lake Mahinerangi and Taieri Airport, the two official stations nearest to Maungatua, were 1.2 times

the totals they recorded from April, 1953, to March, 1954, while the measurements upon Maungatua were being made. Maungatua readings have, therefore, all been multiplied by this factor before, being mapped.
Estimation of Evaporation.
Evaporation figures enclosed in square brackets were obtained from instruments of the pattern used by Barker (1953) and are at each station the average from a group of three or four since preliminary tests revealed considerable, somewhat inconsistent differences in their water consumption under uniform conditions. Measurements in this series are not directly comparable with those of the second series, enclosed in round brackets, which are for a summer period only (20/11/53—10/3/54) and are from cylindrical porous porcelam atmometers (Braun Blanquet 1932, p. 139) used singly and always placed in an entirely unprotected position. They were tested before and after service in the field and proved to give entirely consistent readings to which only small correction factors needed to be applied to make records from each instrument comparable with the rest. The porcelam cylinders were obtained from water-filter candles, and were 4.5 inches long and 1.9 inches in diameter. They were kept free of algae by occasional wiping with a cloth soaked in dilute mercuric chloride solution.
There is an open-pan evaporimeter at Lake Mahmerangi, and its records have given Precipitation/Evaporation ratios that fall below unity only from September until March The atmometers have thus been operated over most of the period in which evaporation is likely to be ecologically significant.
Temperature measurements
The thermometers used were mainly high-grade Zeal Horizontal Pattern minimum thermometers 0–120° F. which agreed closely in their readings and were used to calibrate the U-pattern maximum and minimum thermometers. They were placed either on the ground or on the south side of a cross-bar fastened to an angle-iron standard 3ft 6in above ground level. Compared with the thermometers at Musselburgh, mounted according to standard meteorological practice, they gave grass minima that were usually 1°–2° F. higher and air minima usually 1–3° F. lower than the official record, these differences depending, no doubt, upon the degree to which the bulbs were protected by their mountings.
Identification of log remains
Initially, representative log specimens were compared microscopically with known woods, papers by Garratt (1924), Phillips (1941) and Orman and Reid (1946) were studied, and the opinion of the Forestry Research Institute at Rotorua was sought on a series of samples It proved, with practice, easy to identify the four principal types in the field—i e, Nothofagus menziesii; Podocarpus hallii and Podocarpus totara; Dacrydium biforme and D. bidwilln; and Libocedrus bidwillii. But it was impracticable to separate the species in Podocarpus and Dacrydium since even microscopically this separation is difficult. Mr. H. R. Orman, of the Forest Research Institute, considered that two specimens which he studied closely were both P. hallii. D. bidwillii is only a shrub, so most Dacrydium log remains are probably D. biforme.
The Vegetation Map
To eliminate complications introduced by European settlement it has been necessary to decide what territory was occupied by each of the principal types of vegetation about the year 1850 (Map 2). Fortunately, the main boundaries between forest and grassland lie above 1,500ft, where the poor quality of the forest and of the pasture that can be established in its place have discouraged exploitation. Accordingly, the present forest edge has been accepted as valid in most places for 1850. The only large area of upland forest destroyed since this date is on Mt. Cargill. Here, the many dead trees that are still standing, the large proportion that are of non-durable kaikawaka (Libocedrus bidwillii), and the absence of snow-tussock all contrast with the situation at similar elevations on Swampy Hill and Maungatua, where well-established snow-tussock (Danthonia flavescens) contains fragments only of durable totara (mainly Podocarpus hallii) and pink pine (Dacrydium biforme) testifying to a much earlier deforestation.
The extent of these forests, which disappeared some time prior to European settlement, is indicated on Map 2 by showing the distribution in grassland areas of ancient log remains and of forest dimples, but the latter have been mapped only on gently rolling country on Maungatua, since on steeper slopes there is danger of confusing them with the effects of soil slumping.
The accuracy of this map has been checked by a study of early records in the Hocken Library, particularly those of Shortland (1843), Monro (1844), Tuckett

(1844), Wakefield (1844) and Kettle (1847) and from information recorded by Shaw & Farrant (1949). Tuckett's evidence confirms pre-European origin of grassland between Mihiwaka and Waitati, and Simpson & Scott-Thomson (1929) provided some of the records of silver beech (Nothafagus menziesii) forest in the main lowland forest area.
Rainfall, Evaporation, Fog and Temperature
Measurements of rainfall and evaporation rate at numerous stations on the area are recorded on Map I. The rainfall figures are assumed annual means, and the atmometer readings are for the summer, of 1953–54, except those in square brackets, which were made in the previous year with different apparatus and are thus comparable only among themselves.
This map also shows the average inland limit of the sea-fogs on the northern hills. These fogs, which normally come from the north-east and have their base at about 1,000ft are important because during the warmer months they produce a saturated atmosphere and heavy fog-drip on the land they cover when relative humidity west of the fog limits may be comparatively low. For instance, over a period of 34 days beginning on December 17, 1952, sea-fogs, unaccompanied by rain, developed on fourteen days, and on five of these the relative humidity at Taieri Airport at noon was below 60%, while on all but two of the remainder it was below 80%. Maungatua is only occasionally affected by these sea-fogs, and here the normal fog-base is higher (about 2,000ft). During a period of 75 days beginning December 25, 1953, sea-fogs covered both Mt. Cargill and Swampy Hill on twenty occasions, while Maungatua was covered only five times. Southerly fogs also occur (nine during this period), but these cover the northern hills and Maungatua equally, and are normally accompanied by rain.
The effect of aspect differences on local distribution of rainfall was investigated. The figures in Table I show that in most cases, the type of site chosen for the gauge did not greatly affect its reading The fact that the rainfall figures recorded over the northern hills show only a gradually changing pattern accords with this. But the last two pairs of readings which are from Maungatua establish that aspect some-times substantially affects the rainfall on this mountain. In both instances, the two sites were within a quarter mile of one another.
[The section below cannot be correctly rendered as it contains complex formatting. See the image of the page for a more accurate rendering.]
| Altitude (ft) | Site | Aspect | Rainfall | Greatest Diff. as % of lowest reading |
|---|---|---|---|---|
| 2,400 | Steep slope | N | 48.55 | |
| 2,350 | Small basin | S | 50.24 | 9.5% |
| 2,150 | Gully-side | W | 51.62 | |
| 1,950 | Flattish spur | S | 47.18 | |
| 2,000 | Moderate slope | SE | 42.21 | |
| 1,900 | Moderate slope | W | 44.09 | 7.2% |
| 1,850 | Moderate slope | S | 41.13 | |
| 1,450 | Moderate slope | E | 36.99 | |
| 1,700 | Moderate slope | N | 39.02 | 5.5% |
| 1,800 | Gentle slope | S | 36.64 | |
| 1,800 | Gentle slope | N | 37.27 | 1.73% |
| 300 | Flat valley bottom | – | 30.22 | |
| 400 | Flat spur | – | 27.58 | 9.6% |
| 1,000 | Flattish summit | – | 31.12 | |
| 800 | Flat ridge-top | – | 29.30 | 14.7% |
| 500 | Moderate slope | N | 33.60 | |
| 2,100 | Flat summit | – | 29.84 | |
| 2,050 | Gentle slope | S | 31.18 | 4.5% |
| 850 | Moderate slope | SE | 32.39 | |
| 850 | Steep slope | N | 30.50 | 6.2% |
| 2,700 | Steep slope | NW | 35.60 | |
| 2,750 | Steep slope | SE | 29.48 | 20.7% |
| 1,600 | Moderate slope | SE | 30.10 | |
| 1,800 | Hill crest | – | 20.60 | 46.1% |

The temperature records that have been kept have been intermittent readings mainly with a calibrated series of minimum and maximum-minimum thermometers. Monthly air (i.e., 3 ½ ft above the ground) maxima and minima were recorded for a full year for two stations near the Trig on Maungatua, both on open spurs at 2,400ft—one on the main seaward face (S.E.), and the other on the main inland face (N.W.), and about 1½ miles further from the sea. These did not differ consistently and never by more than 3° F. The extremes were 84° F. (Feb.) and 22° F. (Sept.). Records kept on Maungatua from March to June at four stations along a grassy ridge leading up the seaward face to the summit showed a steady fall of the monthly maximum with altitude with a range in June of 15° F. between 600ft and the Trig. In general, the monthly air minimum at the summit was about 6° F. lower than at 600ft. These records seem sufficient to establish that temperature climates are differentiated by altitude in a normal way and that there is not an east-west gradation sufficient to increase materially the temperature range of the climate of inland faces. The flat treeless summit of Maungatua does, however, experience severe ground frosts. A minimum thermometer on the ground at 2,900ft recorded in May 8° F., in June 3° F., and in July 12° F.
Several tests were made for the presence of frost pockets and inversion patterns. A series of clear grassy sites were selected for minimum thermometers at different altitudes on Mt. Cargill, Mt. Misery and Maungatua. In all cases during frosty nights an inversion pattern developed. The point of reversal on Mt. Cargill was normally below 550ft, but on Maungatua it was usually between 600ft and 1,100ft. The most intense inversion detected was in open tussock country near Bendoran during August. Misery Creek and Orbell Creek are narrow valleys separated by the spur on which Bendoran is situated.
| 1,600ft | Bendoran, hillside | Air | min. | 32.3 | Ground | min. | 27.0 |
| 550ft | Misery Creek, valley side | Air | min. | 23.3 | Ground | min. | 22.2 |
| 550ft | Misery Creek, valley bottom | Air | min. | 20.8 | Ground | min. | 15.6 |
| 1,250ft | Orbell Creek, spur | Air | min. | 27.5 | Ground | min. | 19.0 |
| 850ft | Orbell Creek, valley bottom | Air | min. | 18.0 | Ground | min. | 14.0 |
It is clear that in this tussock country inversion patterns are pronounced, and the flats in the narrow valley bottoms experience severe frosts.
In forest country that has been partly cleared at Lee Creek, Mill Creek and Mt. Cargill the inversion patterns that developed on deforested sites were less striking while thermometers set up inside the forest showed them weakly or not at all. It was always warmer within the forest than at adjacent stations in the open, and differences between air and ground minima were usually less than 1° F. The lowest ground temperature registered in a forest clearing was 22° (Mill Creek valley bottom alt. 200ft). In the adjacent beech forest both air and ground minima were 28°, and this was the lowest reading obtained in forest.
Stability of the Vegetation
Silver Beech (Nothofagus menziesii).
As Simpson and Scott-Thomson (1929) have recorded, the small patches of old silver beech enclosed in the main podocarp forest area are invaded by small tree, shrub and herb layers of that forest, and in consequence do not contain a sufficient number of vigorous saplings and poles to maintain the stands. But further from the coast clearings which develop through decline of old beech trees become filled with young beech, and in addition, considerable areas of comparatively even-aged pole beech usually accompany these all-age stands. These suggest a recent advance into new territory. Closer study of the pole stands on Maungatua, however, showed that for the most part they merely repaired damage to the existing forest. Some are where, according to settlers' records, fires had swept in from the adjacent grassland and ring counts have confirmed this by showing the trees to be

Table 2. Forest Regeneration.
Number of Individuals Per ¼ Acre (0.1 hectare) in the Order:—
Germinated Seeds: Seedlings: Saplings: Poles: Living Trees + Dead Trees (Libocedrus only).
Figures to the Nearest Whole Number. p = present but below 0.5 per ¼ Acre. α = large number not accurately counted.
[The section below cannot be correctly rendered as it contains complex formatting. See the image of the page for a more accurate rendering.]
| Forest Type | District | Timber Removal | Rimu (Dacrydius cupressinum) | Miro (Podocarpus ferrugineus) | Mt. Totara (Podocarpus hallii) | Kaikawaka (Libocedrus bidwillii) | Broadleaf (Griselinia littoralis) | Various |
|---|---|---|---|---|---|---|---|---|
| Kaikawaka | Mt. Cargill | none | p:0:0:0:0 | 0:2:2:10:7 | 0:16:0:3:30 | α:7:0:0:13 | 0:11:0:2:8A | |
| 1800′ | +12 | 0:4:1:3:4B | ||||||
| Kaikawaka | S. Waikouaiti R. | |||||||
| 1500 | none | 0:37:0:0:25 | α:α:0:0:28 | 0: 3:0:0:3B | ||||
| +12 | ||||||||
| Kaikawaka- | Leith-Waitati | partial | 0:0:0:1:5 | p:4:1:1:5 | 0:1:p:2:3 | 0:4:2:3:14 | 16:64:31:16:15 | 1:0:0:0:2C |
| rimu | 1250–1500′ | +6 | ||||||
| Rimu | Main Podocarp | Matai (Podocarpus spicatus) | ||||||
| area 700–800′ | partial | 0:0:0:1 | 1:p:p:0:2 | 0:2:3: 3:2 | 0:p:0:0:p | α:α:6:2:11 | ||
| Mt. totara-broadleaf | Bell's Gully 1400′ | 3:10:8:18:5 | 3:3:0:0:45 | 0:22:5:0:5D | ||||
| Totara (Podocarpus totara) | ||||||||
| Rimu-totara- | Woodside | |||||||
| matai | 300–1000′ | partial | 0:p:0:0:2 | p:4:0:0:p | 0:18:5:1:1 | 4:28:1:p:1 | not recorded | p:11:0:0:0E |
| Totara-matai | N. Waikouaiti R. | none | 0:0:0:1 | 0:60:16:3:5 | 1:51:0:1:4 | 3:2:1:0:4 | 0:10:2:0:1D | |
| 400′ | 0:1:1:0:0E | |||||||
| 0:0:0:0:1C | ||||||||
| A = pink-pine (dacrydium biforme) | C = pokaka (Elaeocarpus hookerianus) | E = kahikatea (Podocarpus dacrydioides) | ||||||
| B = mt. totatoa (Phyllocladus alpinus) | D = kowhai (Sophora microphylla) |

of appropriate age. But the pole stands along ridge crests in the Mill Creek catchment are between 100 and 140 years old. They are on exposed sites marked with forest dimples and occasional traces of old beech stumps and are, therefore, believed to occupy old windthrows. The seedlings and saplings that are usually present at the junction of beech forest with shrubland or grassland are often not backed by any substantial number of poles, indicating that though there is a tendency to slow marginal advance it is periodically nullified by fires sweeping along the forest edge. However, in a few places there are well-established marginal pole stands which do not appear to be on land recently in beech. One at 1,500ft above Woodside occupies what 50 years ago is stated to have been a snow-tussock spur, and still contains moribund plants of flax. The Silver Peak forest has, in places, a pole stand 2–3 chains in width at its margin.
In the South Waikouaiti R. there are areas of pole beech containing large numbers of dead and moribund broadleaf (Griselinia littoralis) and kaikawaka indicating a recent advance of beech into kaikawaka forest, and beech seedlings can be found in gaps in podocarp forest where the two adjoin. In the Silver Peak beech forest also there are moribund kaikawaka trees, but they are surrounded by old beech. It appears here that beech has been dominant continuously, but the forest has passed through a phase favourable to a limited invasion by the conifer. We can conclude that, outside the main coastal block of podocarp forest, silver beech is and has for over a century at least been capable of vigorous regeneration and of slow marginal extension usually into snowgrass, but in some areas into coniferous forest.
Conifers and accompanying Dicotyledonous Trees.
Table II indicates the regenerative capacity of the dominant species of podocarp-dicotyledonous forest by listing the average number of germinated seeds, seedlings, saplings, poles and living trees occurring per ¼-acre (0.1 hectare). The series of sample plots on which these figures are based were not standardized in shape or area but were chosen to convey as fair a picture as possible of the general situation. Their total area was about six acres.
These figures suggest that both the mountain and the true totara are maintaining, perhaps even increasing their density, and that matai is vigorous in the establishment of seedlings but poorly represented in the young tree classes. But over the wetter part of the lowland forest the principal podocarps have been rimu (Dacrydium cupressinum) and miro (Podocarpus ferrugineus). They now exist as widely spaced emergents above a continuous canopy of broadleaf and smaller dicotyledonous trees. Partial milling accounts for much of this thinning—at Woodside, for instance, where the original stands are said to have been dense—but it is questionable whether it accounts for all of it. The present inadequate regeneration rate may be of long standing.
A feature of all kaikawaka stands is that there are nearly half as many still identifiable dead trees as live ones. As this small tree is not particularly durable it is clear that the stands have recently been thinning fast. Seedlings are common, but an impression that the species is migrating to a lower altitude is given by the fact that sapling and pole classes are absent except in the belt transitional with wet lowland forest. Here there is vigorous regeneration of broadleaf and some of miro.
Though old logs of pink pine are widespread in the snow-tussock country living trees occur only east of Leith Saddle—i.e., in the Mt. Cargill area. Here it appears to be stable, as does the mountain toatoa (Phyllocladus alpinus) whose main occurence is in this region also.
Broadleaf is the most widely ranging of the larger dicotyledonous trees, and is nowhere failing to establish seedlings though outside the 35in isohyet these are not plentiful. However, saplings and poles are not always present. Nowhere have seedlings or saplings of the pokaka been observed. This suggests that it is becoming extinct locally and that the rarity of kamahi (Weinmannia racemosa) and complete

absence of southern rata (Meterosideros umbellata) from the Dunedin district illustrate other phases of the reduction of the regional tree flora.
Kowhai (Sophora microphylla) has entered two of the forests sampled (Bell's Gully and N. Waikouaiti R.), both where a low rainfall (approximately 30in) has thinned the subordinate strata, particularly the ground ferns (Blechnum capense and B. discolor are both absent), thus admitting much light to the forest floor when a break in the canopy develops. In places, kowhai is accompanied by kanuka (Leptospermum ericoides). Perhaps the fairly extensive stands of kowhai and kanuka in the middle reaches of the Silverstream Valley have originated from similar forest in which regeneration of the podocarps had failed completely.
Shrubland and Grassland.
In 1850 the grassland was probably almost wholly snow-tussock (Danthonia flavescens) since even now it only includes substantial amounts of low tussock (Poa caespitosa and Festuca novae-zealandiae) where it has been much burnt and grazed. It occurred under all climatic regimes of the district and shared margins with every forest association. This suggests that it was in large part an entrenched non-climax community, and its behaviour under the grazing and burning practices of the last century confirms this view. Large areas lying between 1,000–2,000ft have been invaded by the unpalatable and light-demanding seedlings of kanuka (Leptospermum ericoides) and particularly manuka (L. scoparium) whose spread in periodically burnt areas is probably favoured by the greater protection from heat that the larger capsule affords to the seed. Early records prove the derivation from tussock of some of the present Leptospermum communities, the most extensive being in the Silver-stream Valley, where ring counts show their age to be about 70 years. More recent extensions often reveal their origin through containing persistent specimens of the grassland flax (Phormium colensoi). On the other hand, some replacement of snow-tussock by kanuka appears to have pre-dated European settlement, since about 160 growth rings have been counted in the very large L. ericoides (about 40ft high and 18in in diameter) that sometimes intervenes between forest and grassland—e.g., between Misery Creek and Bendoran). Even above 2,000ft on Maungatua the snow-tussock is not stable, but the shrubs which tend to invade it at these altitudes are different principally Dracophyllum longifolium, Hebe buxifolia and Cassinia fulvida).
Leptospermum seedlings are so strongly light-demanding that regeneration does not occur until the ground is almost bare. Failing destruction by fire or felling there is thus normally only one generation upon a site, on which it provides protection for shade-tolerant seedlings of a more permanent community. The older Leptospermum stands now contain seedlings of the components of coniferous-dicotyledonous forest or silver beech to an extent depending mainly upon the proximity of parent trees. Young conifers have not been observed more than 2 chains from mature trees. Rimu seedlings and poles are plentiful along with silver beech in a succession occurring between the two main tributaries of the S. Waikouaiti R. at 1,200ft elevation and under a rainfall of 45in. Rimu seedlings were even found under Leptospermum in the N. Waikouaiti Valley with a rainfall of 30 inches and only stunted mature trees surviving. Holloway (1954, p. 391) draws attention to the fact that this species will establish itself in Leptospermum in areas where it fails to regenerate in forests. But the mountain totara promises to be the most conspicuous podocarp in these new forests.
Discussion
The meteorological records set forth in Map I show in general an increase in rainfall and a fall in evaporation rate with altitude so that all high land in the Mt. Cargill, Flagstaff, Silver Peak area receives between 47–56 inches of rain and has relatively low evaporation rates. The Maungatua area is drier, but the same principle holds—above 2,000ft the mean rainfall is 41in, and the mean of the

evaporation values is 4.6 litres, while corresponding figures between 2,000ft and 1,000ft are 36in and 5.8 litres. Temperature climates have proved to depend mainly on altitude, and inversion patterns on frosty nights to be marked only in grassland. The distribution of some species appears well-correlated with these climatic values. Most of the lowland forest trees have a well-defined upper limit lying, in the case of rimu, miro and pokaka, between 1,300ft and 1,600ft. The distribution of the montane conifers can be correlated with meteorological data thus:—
| Rainfall (annual) inches | Evaporation (summer) litres | Sea-fogs (75 days) | Mt. totara (P. hallii) | Kaikawaka (L. bidwillii) | Pink-pine (D. biforme) | |
|---|---|---|---|---|---|---|
| Mt. Cargill | 54 | 3.1 | 20 | Living | Living | Living |
| Swampy Hill (E. face) | 53 | 3.9 | 20 | Living | Living | Logs only |
| Maungatua (E. face) | 41 | 4.6 | 5 | Living | No trace | Logs only* |
The relative distribution of forest and grassland is not, however, readily explained. The great humidity of Mt. Cargill could explain the persistence of forest right to its summit and also why, where this forest has been recently destroyed, it has been scrub or Juncus caespiticius rather than snow tussock that has taken its place. What the rainfall and evaporation records fail to show is why forest, which can now occur on the lower seaward slopes of Flagstaff and Swampy Hill (where it consists of kaikawaka, mt. totara, and broadleaf) and Maungatua (where it is beech), does not extend to their summits. The sites are drier than Mt. Cargill, but there is no tendency for rainfall to fall further or for evaporation to increase on the snow-tussock slopes above these forests. Indeed the reverse is indicated. A series of stations on Swampy Spur, the lowest just above the forest edge, show this clearly. The following data are for the summer (November 20, 1953 to March 10, 1954) months.
| Altitude | Rainfall | Evaporation |
|---|---|---|
| 1,700ft | 11.4in | 4.13 litres |
| 2,000ft | 11.5in | 3.90 litres |
| 2,250ft | 11.5in | 3.80 litres |
It is difficult to believe that decline in temperature with altitude is proving an effective barrier because of the low altitudes involved and because even in this district the absolute altitude of both kaikawaka and beech is much higher—for kaikawaka, 2,200ft on Mt. Cargill, for silver-beech, 2,400ft on Silver Peak. A sufficient fogtolerance in both species is also demonstrated by these occurrences.
It is clear that the present forest-grassland margins were mainly established over a century ago by a process of deforestation of which log remains and dimples in the grassland provide abundant evidence. It seems likely that the deforestation was aided by a change in climate unfavourable to some tree species, but actually effected by repeated fires of Maori origin. These fires, via an inflammable grassland, always resting against the forest edge, ultimately carried deforestation into parts of this district where forest would otherwise have persisted—though its composition might have changed. Mountain totara, broadleaf, and beech would probably have increased in importance while kaikawaka, pink-pine and mountain toatoa declined. These fires would in general spread from the north-west and have therefore eliminated forest less completely on southern and eastern faces than elsewhere. Holloway accepts the probability of widespread fires (p. 373) and the likelihood of their carrying deforestation into stable forest (p. 378).
However, a possibility that needs to be assessed is that contemporary climate records give no true indication of the climate of these uplands at the time when they became grassland and for most of the ensuing period. Holloway (p. 407) offers some evidence that the South Island climate may recently have become warmer but none that it is wetter. The indifferent regenerative capacity of most existing conifers, and particularly the high proportion of standing dead kaikawaka seem to deny the existence of any recent amelioration of climate, as does the evidence in the
[Footnote] * A few bushes of D. bidwillii persist in bogs on the summit.

S. Waikouaiti catchment of recent advance of beech into kaikawaka forest. Examination of the longest series of rainfall records available at any single station in this district (Botanic Gardens, since 1913) has revealed no definite trend. There thus seems to be no reason to suspect that present-day measurements are substantially misleading.
The capacity of grassland that is frequently burnt to hold indefinitely areas with a forest climate has been established in other countries (e.g., Beilmann & Brenner, 1951; Richards, 1952, p. 342, p. 350), and if we assume that the grassland has been

extended by fire into areas climatically suited for forest, important recent changes are easily understood—namely, the marginal pole stands of beech at Silver Peak and Woodside; the rapid spread of scrub into tussock in the Silverstream Valley; and the very general tendency for this process to occur elsewhere. These successions have been able to begin, partly through cessation of burning (e.g., Silverstream Valley is now a Fire District) but mainly because browsing animals hitherto absent have retarded the recovery of burnt tussock and reduced the competitive advantage which its resilience after fire had hitherto conferred upon it. This is discussed more fully in another paper (Mark, 1955).
Certain forest species are often conspicuous among the snow-tussock, noticeably Cyathea colensoi, Polystichum vestitum, Blechnum minor and Fuchsia colensoi, and probably wherever they occur they indicate that the climate would support forest It is noteworthy that these, and invading manuka become inconspicuous or absent in the valleys of the north-west where the rainfall declines to about two-thirds of that on Silver Peak while judging by the single station established, the evaporation rate increases by about 70 per cent. In this country dry north-west winds are more frequent and more violent than they are nearer Dunedin city, and their responsibility for disappearance of the forest may be more direct.
Acknowledgments
We are indebted to Professor G. T. S. Baylis for much assistance and advice, and to the Research Fund of the University of New Zealand for a grant to cover travelling and equipment. The co-operation of many others in matters referred to them is also gratefully acknowledged, particularly Mr. H. R. Orman, of the Forest Research Institute, the Director and Mr. J. Finkelstein of the Meteorological Office, and many residents or former residents of the district.
References
Barker, A. P., 1953. An ecological study of tussock grassland, Hunters Hills, South Canterbury. N. Z. Dept. Sci. Ind. Res. Bull. 107, 58 pp.
Beilmann, A. P., and Brenner, L. G., 1951. The recent intrusion of forests in the Ozarks Ann. Mo Bot. Gard. 38, 283–291.
Braun-Blanquet, J., 1932. Plant Sociology. Trans. by G. D. Fuller and H. S. Conard, 439 pp., New York.
Dunedin Naturalists' Field Club, 1932. Catalogue of the indigenous, and introduced flowering plants, ferns, and seaweeds occurring in the Dunedin district, 41 pp., Dunedin.
Garratt, G. A., 1924. The identification of some New Zealand woods. Circular, N. Z. State Forest Service.
Holloway, J. T., 1954. Forests and climates in the South Island of New Zealand. Trans. Roy. Soc. N.Z., 82, 329–410.
Mark, A. F., 1954. A study of the vegetation of the Maungatua Range. Thesis, Otago University Library.
—— 1955. Shrubland and grassland of Maungatua, Otago. N.Z. Journ. Sc. Tech., A37, 349–366.
Orman, H. R. and Reid, J. S., 1946. Wood anatomy of New Zealand Dacrydium species. N. Z. Jour. For., 5, 215–219.
Phillips, E. W. J., 1941. The identification of coniferous woods by their microscopic structure. J. Linn. Soc. Bot., 259–320.
Richards, P. W., 1952. The Tropical Rain Forest. 450 pp., Cambridge.
Shaw, M. and Farrant, E. D., 1949. The Taieri Plain—tales of the years that have gone. 238 pp., Dunedin.
Simpson, G. and Scott-Thomson, J., 1929. On the occurrence of silver southern-beech in the neighbourhood of Dunedin. Trans. N.Z. Inst., 59, 326–342.
—— 1938. The Dunedin sub-district of the South Otago botanical district. Trans. Roy. Soc. N.Z., 67, 430–442.
Wardle, P., 1953. An ecological survey in the hill country north of Dunedin. Thesis, Otago University Library.
P. Wardle,
Botany School,
Downing Street,
Cambridge, England.
A. F. Mark,
Department of Botany,
Duke University,
North Carolina, U.S.A.

