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Page 1: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

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Appendix I

Details of the Eucalypt Species studied in this thesis

Main eucalypt alliances on the Northern Tablelands.

Alliance Suballiance Mainassociation

Minorassociation

Species formingecotonal

associations

E. melliodora - E. melliodora E. bridgesiana E. albensE. blakelyi E. blakelyi E. conica E. caliginosa

• E. viminalisE. sideroxylon

E. pauciflora E. pauciflora E. pauciflora E. acaciiformis E. stellulataE. viminalis

E. stellulata E. stellulata E. pauciflora. E. viminalis

E. nova-anglica

E. dalrympleana E. dalrympleana E. andrewsii§ E. caliginosa E. radiata

E. paucifloraE. acaciiformis

E. viminalis E. viminalis E. viminalis E. obliquaE. pauciflora

•E. laevopineaE. caliginosaE. dalrymplearuE. dalrymplecuuE. nova-anglicaE. stellulataE. melliodora

E. radiata E. acachformisE. dalrympleanaE. youmanii

E. nova-anglica E. nova-anglica E. stellulataE. acaciiformisE. viminalisE. paucifloraE. melliodoraE. bridgesiana

E. laevopinea - E. laevopinea E. laevopinea Wetter.E. caliginosa - E. laevopinea E. paucifloraE. youmanii E. cameronii E. viminalis

- E. obliquaE. salignaE. deaniiE. dalrympleanDrier:E. macrorhyru

, - • •

E. bridgesianaE. caliginosa

E. caliginosa E. caliginosa E. melliodoraE. caliginosa - E. blakelyi

E. nicholii E. bridgesianaE. laevopinea

, E. youmaniiE. dalrymplecui

Based on information in Beadle (19811_* Not included: E. obliqua - E. fastigata alliance; E. macrorhyncha - E. rossii alliance;

E. cypellocarpa alliance; E. youmanii suballiance; E. camvanulata alliance; E.andrewsii alliance.

§ E. dalrympleana in all cases is ssp. heptantha.

244

a

ha

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Details of the Eucalypt Species 245

Blakely's Red Gum (Eucalyptus blakelyi Maiden)

SUBGENUS: SYMPHYOMYRTUS SECTION : EXSERTARIA (Red Gums) SERIES : TERETICORNES

GENERAL APPEARANCE

Medium sized tree, 10-24m high. Trunk diameter 70-100 cm.

Short trunk, large crown, often drooping branches.

Typical "gum" bark - shed in irregular patches, greyish colour.

DISTRIBUTION

Widespread on inland side of dividing range in

N.S.W. -lower levels of Southern Tablelands;

higher levels of Northern Tablelands;

Western Slopes and edges of Western Plains.

In Victoria on gentle slopes of N.E. area.

Also Qld, as an extension of N.S.W. range.

Altitudes 170-1200 m.

Common and widespread on N. Tablelands -

replaced by E. amplifolia in Eastern areas and

by E. caliginosa on ridges.

TOPOGRAPHY

Gentle - moderate slopes usually. Not upper slopes, steep country or

river banks. Mid to low slopes on N. Tablelands.

GEOLOGY AND SOILS

Granite, slate or sedimentary rocks. Variety of soils. Usually deep

soils and compact loams of moderate quality. Not basalt soils

usually.

CLIMATE

Inland climate, cool winters (frosts and occasional snow).

Warm to hot summers (over 40° at times).

Rainfall not as reliable as coastal areas..450-750 mm per year.

Frost and drought resistant species.

ECOLOGY

Open forests and woodlands.

With Boxes and Ironbarks and occasionally Stringybarks.

COMMON ASSOCIATES ON THE NORTHERN TABLELANDS

Most common with :E. melliodora, E. bridgesiana, Angophora

floribunda. In Western areas: E. macrorhyncha, E. sideroxylon, E.

hemiphloia, E. caleyi, E. dealbata, E. youmannii, E. bancroftii etc.

In Inverell area with: E. albens, A. floribunda.

On basalt and sedimentary rocks with E. melliodora, E. nova-anglica.

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Details of the Eucalypt Species 246

On granite in central and eastern area with: E. caliginosa, E.

melliodora.

GENERAL

Most closely related to E. tereticornis, E. dwyeri, E. dealbata, E.

camaldulensis. Likely to hybridize with the last two.

Timber similar to other red gums - hard, durable, interlocking

grain. Useful for construction work, fence posts. Not milled to a

great extent because long lengths of timber are hard to obtain,

though is grown for timber in N.Z.

Also useful for shade, shelter, honey and firewood.

DIEBACK ON THE NORTHERN TABLELANDS

Had severe dieback over much of its range on the N. Tablelands. One

of the worst affected species, and in many places large proportions

of trees died. Less affected in western areas.

Also severely affected in other areas eg. Central Tablelands.

Apple Box (Eucalyptus bridgesiana R.T. Baker ssp bridgesiana)

(= E. bridgesiana RT Baker, = E. stuartiana F. Muell)

SUBGENUS: SYMPHYOMYRTUS SECTION : MAIDENARIA (Gums) SERIES : VIMINALES (White

Gums, Apple Boxes etc)

GENERAL APPEARANCE

Medium sized tree, 8-25 m high.

Trunk 0.5 - 1 m diameter.

Short bole, large drooping crown.

Bark greyish, typical "box" type, corky and persistent to the

branches.

DISTRIBUTION

Similar to E. melliodora.

N.S.W. - Western slopes and parts of the

tablelands.

Vic - eastern areas at low to medium

altitudes.

Also a short way into S.E. Qld.

Altitude : Low to intermediate, 170 -

1200 m.

Wide distribution on the N. Tablelands.

TOPOGRAPHY

Flats, lower slopes and rises. Moist sites.

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Details of the Eucalypt Species 247

GEOLOGY AND SOILS

Granites, fine grained sedimentary rocks (eg. slates and cherts).

Deep soils and heavy alluvial soils.

CLIMATE

As with E. melliodora...hot summers, cold frosty winters.

Rainfall 625 - 1125 mm. Occasional snow at higher altitudes.

ECOLOGY

Woodlands and open forests. Not usually a dominant.

Grows with Boxes, Ironbarks and Gums.

COMMON ASSOCIATES ON THE NORTHERN TABLELANDS

Most common with E. melliodora, E. blakelyi.

GENERAL

Closely related to E. angophoroides which is coastal in southern

N.S.W. and eastern Victoria. Also closely related to E. bridgesiana

ssp malacoxylon.

Shade tree, good honey (regular flowerer). Soft brittle wood of

little commercial value.

DIEBACK ON THE NORTHERN TABLELANDS

Variable susceptibility. Some areas very badly affected or the worst

affected species in a stand. In better condition west of divide

where dieback is less severe. Also one of the worst affected species

on the Central Tablelands.

Yellow Box (Eucalypus melliodora A. Gunn. ex Schauer)

SUBGENUS: SYMPHIOMYRTUS SECTION : ADNATARIA (Boxes) SERIES : MELLIODORAE

GENERAL APPEARANCE

Medium tree 12-30 m high. Trunk diameter 70-100 cm.

Trunk a third to a half of the tree height. Large spreading crown.

Bark yellow-brown, between a "gum" and a "box" type - flakey,

fibrous, coming off in small strips higher up to reveal smooth bark

underneath.

DISTRIBUTION- •

Similar to E. blakelyi.

N.S.W.- widespread on inland side of

divide, western slopes an N. Tablelands.

Vic - widespread, inland side of divide

and a little on the coastal side andc"northern foothills of the divide. Also

extends into S.E. Qld.

Altitude mainly 700-1140 m.

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Details of the Eucalypt Species 248

TOPOGRAPHY

Gentle slopes and foothills. Usually mid to lower slopes. On western

edge of occurrance grows on flats near watercourses.

GEOLOGY AND SOILS

Variety of rocks: granite, sedimentary rocks and basalts sometimes.

Soils light to moderate heavy alluvial soils, loarns, sandy foams.

Not poor sands. Indicates better class agricultural soils, thus

extensively cleared.

CLIMATE

Warm dry summers, cool frosty winters.

Annual rainfall 375-900 mm. Frost and drought resistant.

ECOLOGY

Woodlands, sometimes in open dry sclerophyll forest. Usually with

other Boxes, Ironbarks, E. macrorhyncha, and E. blakelyi.

COMMON ASSOCIATES ON THE NORTHERN TABLELAND

Commonly with E. blakelyi, E. bridgesiana, Angophora floribunda.

In western areas on basalt also with: E. albens, E. melanophloia,

Callitrus and on granite with: E. macrorhyncha, E. andrewsii, E.

dealbata, E. bancroftii. With E. caliginosa and E. viminalis on

Tenterfield plateau and with E. nova-anglica on basalt and red soils

in central and eastern areas.

GENERAL

Most closely related to E. sideroxylon (with which it hybridizes)

and E. polyanthemos.

Wood yellow/brown - hard, strong and durable. Heavy construction,

fence posts. Excellent firewood and honey tree. Attractive, fast

growing. Useful for shade and shelter.

DIEBACK ON THE NORTHERN TABLELANDS

Severely affected but not usually as bad as E. blakelyi with which

it commonly grows. Large proportions dead in many areas.

Also affected in other areas eg. Central Tablelands, where it is

usually less affected than associated species.

New England Peppermint (Eucalyptus nova-anglica H. Deane et Maiden

SUBGENUS: SYMPHYOMYRTUS SECTION : MAIDENARIA (Gums) SERIES : VIMINALES

GENERAL APPEARANCE

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Details of the Eucalypt Species 249

Small to medium tree, 15-20 m high, sometimes 30 m.

Not a true Peppermint. Bark Rough, fibrous, deeply furrowed on trunk

and smooth on upper branches.

Distinct blue/grey juvenile foliage.

DISTRIBUTION

Limited to N. Tablelands of N.S.W.and the

high country of S.E. Qld. Common near

Armidale. Chiefly east and north parts of

Tablelands - not much in western areas.

Altitude 500-1500 m

TOPOGRAPHY

Frosty valley floors and lower slopes. Prefers high moisture and

conditions and frequently grows in badly drained places.

GEOLOGY AND SOILS

Granite and basalt. Moderately heavy soils eg. clay loams.

Because it is on better soils in valleys it is common in settled

areas and consequently is heavily cleared often.

CLIMATE

Warm summers, cold frosty winters.

Annual rainfall 625-875 mm.

ECOLOGY

Woodlands, dry sclerophyll forests. Often in pure stands.

COMMON ASSOCIATES

Frequently with E. paucifiora, E. stellulata, E. blakelyi, E.

melliodora, E. viminalis, E. caliginosa and various Peppermints.

GENERAL

Most closely related to E. cinerea.

Useful for shade and shelter. Wood is light red and not highly

regarded, though sometimes used for fencing etc.

DIEBACK

Worst affected species on the N. Tablelands and was the first to

suffer. By 1970 large proportions were dead in Salisbury Plains and

Guyra Plateau areas. Often was the only species affected. Not

affected over its entire range, and in western and southern areas it

is in better health. In cultivation in Central Tablelands it is

reported to be in good health.

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Details of the Eucalypt Species 250

Snow Gum or White Sally (Eucalyptus paucifiora

Sieber ex Sprengel ssp paucifiora)

SUBGENUS: MONOCALYPTUS SECTION : RENANTHERIA SERIES : OBLIQUAE (Ashes and Sallees)

APPEARANCE

Small to medium tree, 10-20 m high. In higher altitudes has a shrub

or mallee habit. In lower altitudes is a short boled tree, much

branched and with a spreading crown.

Trunk 0.5 - 1 m diameter.

Smooth white "gum" bark.

DISTRIBUTION

High country of N.S.W., Vic, Tas, and

S.E. Qld.

Altitude 1700-3000m, extends from

sea-level in parts of Tas and Vic.

Largely alpine to subalpine.

Widespread on N. Tablelands, in central

and eastern areas, in higher or frosty

areas.

I

TOPOGRAPHY

Varied. Mountain slopes, exposed ridge tops, broad valleys.

GEOLOGY AND SOILS

Various. Shallow rocky soils on ridge tops and moderate quality

drier type alluvials from basalts, granites etc.

CLIMATE

Cool summers, cold winters..frost and snow frequent. Moderate

rainfall 625 - 1250 mm - usually reliable.Winter rainfall in southern

areas and summer rainfall in northern

ECOLOGY

Woodlands, often in pure stands.

COMMON ASSOCIATES ON THE NORTHERN TABLELANDS

Often with E. stellulata on cold exposed sites. Also with E.

viminalis, E. nova-anglica, E. dives in different areas.

GENERAL

Most closely related to E. niphophila (=E. paucifiora ssp

niphophylla), E. paucifiora ssp debeuzevillei) and E. stellulata.

Timber little used though valued locally for fencing and firewood.

Good for shade and shelter. Low density honey. Prevents erosion in

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Details of the Eucalypt Species 251

alpine areas.

DIEBACK ON THE NORTHERN TABLELANDS

Suffered over extensive areas. Shows some resistance compared with

associated species, eg. E. blakelyi, E. melliodora, E. nova-anglica,

E. viminalis. Was worst affected where it grew on exposed frosty

sites.

Also showed some resistance on the Central Tablelands.

Manna Gum or White Gum or Ribbon Gum (Eucalyptus viminalis Labill.)

SUBGENUS: SYMPHYOMYRTUS SECTION : MAIDENARIA (Gums) SERIES : VIMINALES (White

Gums etc)

APPEARANCE

2 forms. Medium to tall tree of tall woodlands and grassy forest and

a taller form of wet sclerophyll forest.

Commonly 30-40 m high and with a trunk diameter of 1 m but may reach

60 m with a 1.7 m diameter trunk.

Open spreading crown.

Typical "gum" bark, smooth, white, coming off in ribbons. Often

rough at base.

DISTRIBUTION

Wide distribution in S.E. Aust.

N.S.W.- scattered through Northern and

Southern Tablelands on well watered cold

sites.

Vic-common in N.E. area.

S.E. Qld and Mt Lofty Ranges of S.A.

also.

N. Tablelands-common and widespread above

900m.

Altitude range sealevel (S.A.) to 1500m

(Northern N.S.W.)

GEOLOGY AND SOILS

Variety of rocks; basalts, granites etc. Prefers good soils, moist

and well drained alluvial or sandy podzolics.

CLIMATE

Wide range. Mostly mild summers and cool to cold winters with

frosts. Snow rare. Winter rainfall in south, summer rainfall in

north of its range. Rainfall 625-1375 mm.

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Details of the Eucalypt Species 252

ECOLOGY

Tall woodlands, grassy forests, wet scleophyll forests. In WSF may

be associated with E. regnans, E. delegatensis, E. fastigata, E.

obliqua and various Peppermints.

COMMON ASSOCIATES ON THE NORTHERN TABLELANDS

E. pauciflora, E. melliodora, E. blakelyi, E. nova-anglica.

GENERAL

Similar to E. dalrympeana, E. rubida in appearance.

Related to E. aromaphloia, E. pryoriana, E. nova-anglica. Hybrid

swarms of it and E. nova-anglica sometimes called E. huberiana.

Wood pale, moderately hard, but not strong or durable. Grain open

and straight. Useful for posts and rails. Reports vary on wood

quality, dependant on site. Some say it twists and warps while

others say it seasons well and is useful for boards, light

construction, panelling etc.

Young trees used for pulp and fibreboard.Koalas eat the leaves.

Coppices readily. Grows well in the nursery, fast growing, responds

to fertilizer. Manna collected from leaves. Can be propagated from

cuttings. Good honey, nectar and pollen tree.

Clinal variation in drought and frost resistance.

DIEBACK ON THE NORTHERN TABLELANDS

Suffered over extensive areas. Variable susceptibility. Did not

suffer until most recent outbreak (1975-80). Generally not as badly

affected as E. blakelyi or E. melliodora.

Amongst the worst affected species on the Central Tablelands.

Rough Barked Apple (Angophora floribunda (Sm.)Sweet)

APPEARANCE

Medium tree. Rough, fibrous bark - persistant to upper branches.

Twisted gnarled appearance.

DISTRIBUTION

Widespread in N.S.W. (particularly Western Slopes).

Also Qld and Vic.

Occurs near coast in east Vic and southern N.S.W., while is more

inland in northern N.S.W.

On N. Tablelands is common at altitudes below 1100m.

Scattered over central and western areas.

TOPOGRAPHY

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Details of the Eucalypt Species 253

Often on flats. Sometimes on hills.

GEOLOGY AND SOILS

Usually slates and alluvium. Favours deep soils and alluvial soils.

CLIMATE

Similar to E. melliodora.

ECOLOGY

Woodlands

COMMON ASSOCIATED ON NORTHERN TABLELANDS

Usually grows with E. blakelyi and E. melliodora

GENERAL

Closely related to A. bakeri, A. subvelutina and hybridizes with

both.

Good shade tree and often seeked out by stock for this purpose.

Profuse flowering.

DIEBACK ON THE NORTHERN TABLELANDS

Sometimes heavily defoliated. Usually recovers well. Severe dieback

in places, but generally not as bad as E. blakelyi or E. melliodora

but occassionally worse, eg. Kingstown area.

REFERENCES USED TO COMPILE APPENDIX Ib

Some of these references give a good overview of species, while others may only be useful for one or two bits

of information. The better reference books have been maked with *.

Anderson (1956)

Beadle (1976-1987)

Beadle Carolin and Evans (1976)

Blake and Roff (1958)

Chippendale and Wolf (1981) - Distribution

*Costermans (1981) - General

Morgan (1981b) - Distribution and ecology of N. Tablelands species

*Hall, Johnston and Marryatt (1963) - Distribution etc.

*Hall, Johnston and Chippendale (1975) - Complete information for

each species

Kelly (1974) - Illustrations

Penfold and Willis (1961) - general

Pratten C. - personal communication on dieback on the Central

Tablelands of N.S.W.

Pryor and Johnson (1971) - classification

Williams (198i) - Eucalypts of the N. Tablelands.

*Williams and Nadolny (1981) - Distribution of dieback on the

Northern Tablelands.

**************************************************

Page 44: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

Appendix II

Dieback Vitality Scale

This scale is the same as used by Christopher Nadolny (see Nadolny 1984 for full details). It is

modified from E. Hoult (1970).

0 Dead (certain), heavy twig loss, bark splitting

1 Completely defoliated with no live foliage, but tree

relatively intact; possibility of sprouting new growth from

branches or bole; often dead leaves remaining on tree.

2 Epicormic growth no higher than main trunk; no mature

foliage.

3 Epicormic growth no higher than lower branches; no mature

foliage.

4 Foliage predominantly epicormic (usually no higher than upper

branches) or greater than 75% of twigs on primary crown

apparently dead.

5 Between 50-75% of twigs on primary crown apparently dead.

6 25-50% of twigs on primary crown apparently dead.

7 Less than 25% of twigs on primary crown dead, but not

completely healthy; substantial epicormic growth or defoliation;

little reproductive activity.

8 Apparently healthy.

254

Page 45: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

Appendix III

Data Sheets and Calculations of Phenological Data:1985-88

Phenological Data

Trees were chosen with low branches, where possible. For higher trees binoculars were used

and occasional destructive sampling. The different stages of the flowering cycle are illustrated

in Figure 2 and Plate 6.1.

Explanation of Data Sheet

The classification "young buds" was later disregarded as being too subjective. Seed and chaff

were put on a separate data sheet (Figure 3 below). "Health ratings" are explained in Appendix

II. "Notes" included when seed traps were installed, what defoliation was experienced, and notes

on the flowering stages. Relative sizes of . flower or fruit crops, leaf growth, or beetle attack are

illustrated in Subsection 6.3.1. The following code was used in recording

3 very light crop - fruit or buds sporadic over tree

not easy to find.

/3 moderate crop fruit or buds distinct and common

on tree, easy to find.

high crop - fruit or buds dense throughout

the crown - most possible sites are occupied.

Arrows between dates indicate the progress of each flower crop.

Seed Trap DataInflorescence buds, flower buds, immature and mature fruit, seed, and chaff were all counted.

Values for seed and chaff were added and the mean taken over the two seed traps. This figure

was converted to seed plus chaff per m 2 using the following formula:n lo,000 = seed + chaff 111-2453

where n = mean value of seed + chaff over the two seed traps. and 453 = the area of each

seed trap.

255

Page 46: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

Phenological Data 256

The arising value was then divided by the number of months over which the seed fall had

taken place giving a value of average amount of seedfall per m2 per month:

Young leaves, leaves, sticks, and unclassifiable fragments and dust were all weighed when dry

and added together to give a value of litter fall. Insects were counted, classified, and weighted

and the insect frass was weighed. These values were also converted to an amount per m2 per

month.

6176• B,;-(4,„iet (zb) 4covE: 2 0,vi51""l'es: Etc. viman a It's

Nooks" 3

DAZMI.id

R.',6.1,

1.bvis

us fl,„.. .14

fi,.y(„,:i-

ti. r--cru;&

0 2...,,; t-

L41

P.4ilea, 5.1

1

ci4fi an

NO TES

3 . 7-35 111 WA Q‘-'fr.rowffm•

4ftig44-0. 1111 Seeot -Iry s ,.s AA/

11 . 1 . 35 Ed IN= g no recr“ ;-bint e6s.,-

V

,,e4

q .1,1145. Bill Mai _ g s..e L...$4.4f1,44- C)

0...36 . NMI 11111110111 – 822 . 44, lirialli i EMI / /1•1o•14 ITINIMAINURIMIRIII r En spri .14 S $ ,,,.. c....r .

Ii.u . r. 11111/111111 la r

WM

0%

■111322IMMIIIIM"

in

. s..,..-ir1 4' • 4::' ' i " 'wt.

of,y " J u,i4t...le .•.. s

6,34 FilM il v" S.

6 .07 ile II g

I •11.1 NE II/ g

1544 ME 333 I q 1 g Iii J.,* ve, ile ' 1,. 4 .

. .

,

Figure 1: Data Sheet for Phenological Observations

Page 47: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

opiin 541,tiollOrt 5t4;t* Se cc)

Ch^4F,

a I• at,.• •

APO

Frow.... 84, 01)13.hh

Phenological Data 257

Figure : Stages of Fruit Development in Blakely's red gum (E. blakelyi)

Ice:

atfc.

kcl.bvds.

11:,bud

Ws Froweis pftrtIll . ° Idfioweis

J"J

fig 4"64.44.

i•

$WIS CilafF" kali*CS)

)

le".i

Sid*(

*NA'(i)

Li Ik'6)

_14skts

4'`143)

enA.

(3)

11 -

. .

Figure .3: Data Sheet for Seed Trap Contents

Page 48: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

Appendix IV

Design of Seed Traps

The seed traps used as part of the phenology studies from 1982-1984 (Chapter 6.3) were based

on a design by Margaret French who was working on seedfall in rainforests from the Botany

Department of the University of Sydney.

Seed traps were 0.1 m2 in area, with inside lengths of 25 cm X 40 cm. The frame was

constructed with 50 x 25 min pieces of hardwood held together with bent strips of 2 cm wide

metal strapping.

A fine nylon mesh was stapled to the bottom of the trap and joins were sealed with silicone

sealant. The mesh was a Swiss Silk bolting cloth with a mesh count of 24.4 per cm. This was

fine enough to catch the very finest particles but allowed passage of water.

[Nylon mesh: Nytal Nylon Monofilament ASTM 60-250 u, Type 2188 Thread 160 u]

Chicken wire was nailed to the top of the trap to prevent damage to the mesh from falling

twigs. The traps were suspended from a lower branch of a tree with wire.

These traps proved to be too shallow and unstable to collect and hold sufficient numbers of

seeds so the design was modified. New traps were made from plastic buckets with their bottoms

cut out and replaced with the same fine nylon mesh as before, held in place with two doughnut

shaped pieces of galvanized iron, pop rivetted through the bucket and sealed with silastic sealant.

The traps were secured between two steel fence posts with wire and chicken wire was placed

over the top to prevent damage from falling branchlets.

258

Page 49: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

bucket

fi. ne ny 1 on gauze

metal rims, poprivettet! together

Seed Traps 2E9

Top diameter bucket = 24cm Collecting area of one bucket = 453 cm 2 Height off ground

about 1.5 in Two seed traps per tree. Total collecting are per tree of 905cm2

seal ant

Bucket seed trap

Not to scale.

deed trap and portable vacuum cleaner.

Page 50: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

Appendix V

Phenology graphs of selected eucalypt trees

IE • 14ev 0 pin e,t #2- Pei - a 61.' 1185 MG i /7 7 Ifirr

3"i

6s ow DIFti Anra-ksoNIDn-FriAtiJS A 5 0 AlP t jfeal Av

1 ykotj fr,,, 9 V* tiollihrmici,r 4-._ith 4.ft,1 L _ _ -fike . ‘-'

Re/Jaw./ ktfpils PREPARED f OR ‘AcH 7A6t MOAJITOKCP

C loo AGO.

260

Page 51: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

Appendix VI261

Total area and trees established and monitored inthe project

SI1E

Area(ha)

No. treesMonitored

forphenology

No. treesPlanted

No. treessurvivingApril '88

% treessurvivingApril '88

Mean ht(m)

April '88

Areasown(ha)

No. Mean htseedlings (m)April '88 April '88

No. Euc.seedlings

Regenerated(Approx.)

No. Acaci •and shrubs

Regenerated* •

Mean ht(m)

naturalegeneration

BELHAVEN (la) 1 0 336 ('83) 118 36 2.0 - - -1

BELHAVEN (lb) 0.3 0 0 - - - 0.3 39 i 0.2 1 - 0.1(1985,86)

BIRRAHLEE (2a) 2.9 0 0 - - - 0 - - 500 14,500 7

BIRRAHLEE (2b) 3.5 8 0 - - - 0.03 440 1.3 9 21 1.3

EASTLAKE (3a) 11 6 0 - - 0 - - 4,300 2,200

EASTLAKE (3b) 3 12 0 - - - 0.02 ('86) 4 0.4 70 30 1.0

EASTLAKE (3c) 0.2 0 0 - - - 0.08 (87) 168 0.1 0 0 -

EASTLAKE (3d) 0.2 0 0 - - - 0.09 ('87) 324 0.2 0 0 -

EASTLAKE (3e) 0.09 0 0 - - - 0.09 ('86) 43 7 0 0 -

EASTLAKE (3f) 0.06 0 0 - - - 0.06 ('86) 12 ? 0 0 -

EUROPAMBELA (4a) 4 3 0 - - - 0 - - 7 , ?EUROPAMBELA (4b) 1 0 0 - - - 0.5 37 (841 2.0 25 10. . 1.0

62 (85 1.59 (8 0.6

MALPAS DAM (5) 45 0 12,193 11,949 96.8 0.5(approx.)

- 7

MIRAMOONA (6a) 0.45 7 - - 0.06 ('85) 18 0.4 2 0 0.554 ('86) 4 8 0.9 0.07 ('86) 143 o.

MIRAMOONA (6b) 1.8 3 154 ('85) 10 7 0.7 - - 12 0 0.7332 ('87) 276 83 0.10 (87) 38 0.2

MIRAMOONA (6c) 0.35 0 54 ('85) 17 32 0.7 - - - - - -

PETAL! (8a) 7.2 12 0 - - - 0.02 ('86) 0 - 73 160 0.3

PETALI (8b) 5.8 0 0 - - - 0 - - 7 0 ?

PETAL! (8c) 4 3 0 - - - 0 - - 7

RUBY HILLS (9a) 8.6 14 0 - - - 1.00 ('85) 0 - 90 170 1.00.03 ('86) 1,4360.05 (87) 610

RUBY HILLS (9b) 0.1 0 192 83 43 7 0 - - 0 0 -

SALISBURY COURT (10) 4.8 6 456 ('85) 99 22 0.6 0.20 ('85) 58 0.3 7 0 0.7332 ('87) 295 89 7 0.02 ('86) 21 0.1

TERRIBLE VALE (12a) 1.2 3 0 - - - 0 - - 264 360 1.8

TERRIBLE VALE (12b) 3.3 6 132 1 0.8 1.5 0.4 30 0.2 . 0 0 -('85, '86)

THE HILL (13) 8.8 0 0 - - - 0 - - 7 7 . 7

WOODPARK (15a) 10 3 0 - - - 0 - - 0 0 -

WOODPARK (15b) 5 2 332 302 91 7 0 - - 7 ? ?

YALGOO (16a) 3 6 0 - - - 0 - - 1,500 90 ?

YALGOO (16b) 10.6 10 0 - - - 0.80 (85) 0 - 0 0 -0.40 (86) 207 0.8 .

YALGOO (16c) 2.6 0 386 (85) 52 14 0.7 1.30 (85) 0 - 3 0 0.5401 (87) 308 77 1.0

TOTAL 150 100 15,354 13,514 88 Approx. 5.7 3,700 Approx. 6,800 17,500 1-21 0.5

.

Figures in () = sowing or planting dates.

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262

Appendix VII

Details of Study Sites

Property1(a) I (lb)

Belhaven2(a) I 2(b)

Birrahlee •3(a) I 3(b)

Eastlake

Eng: Bloomfield family Rob and Sally Taylor Williams familyLocation 15km NE Armidale 5km SE Kentucky 26km SE UrallaProperty Size, 1,240 ha. 1,320 ha.Land= Sheep and cattle grazing Sheep and cattle grazing Sheep and cattle grazing

SNOW GUM HILLijeology Granite Basalt Porphyritic Palaeozoic Palaeozoic Palaeozoic

leucodamellite metamorphic metasediments metasediments withsediments ("Trap") tertiary stream and

gravel remnants.

Soil Grey lateritic podzal Chocolate podzolic Sandy Grey-brown podzolic Red podzolic Not classifiedintergrade

Slope 3-4. 2. 5-10° 2-5. 15. 2-3.

Position on slope Midslope Midslope Crest to upper slope Crest to mid slope Crest to mid slope Crest to mid slope

Aspect South North South, east, west South and west North, west West

Plant Community GrasslandIsolated trees nearby

GrasslandIsolated trees nearby

Sclerophyll shrubwoodland

Grassy woodland Grassy woodland Grassy woodland

Pasture Tvpe Natural Native None Highly improvedpasture

Native pasture Natural pasture

Density of trees + 0 0 Sparse 292/ha Sparse 48/ha Sparse 27/ha Sparse 89/haDensity of shrubs 0 0 Dense 5000/ha None 0 Sparse 204/ha Isolated plants 9/haEucalypt Regeneration 0 Isolated plants 3/ha Sparse 167/ha Isolated plants 2.6/ha Sparse 388/ha Sparse 23/haAcacia Regeneration 0 0 0 Isolated clumps 6.0/ha Isolated plants Isolated plants 0.3/hr

Main Trees and Shrubs E. melliodora nearby E. dalrympleana near- * E. pauciflora * E. stellulata * E. laevopinea * E. nova -anglicain order of abundance by * L. brevipes * E. viminalis E. melliodora E. pauciflora(,* are dominant) Callitris endlicheri Angophora floribundc E. blakelyi E. dairympleana

Exocarpus cupressy"ormis E. dalrympleana A. dealbata E. blakelyiProstanthera nivea A. dealbata A. implexa E. radiataA. melanoxylon E. bridgeslana Lissanthe strigosa E. laevopineaA, filicifolia Daviesia genistifolia Daviesia genistifoliaLomatia fraseri + planted Pinus radiates Crataegus monogynaJacksonia scopaha Lissantha strigosa

Main herbaceous * Eragrostis sp. Eragrostis leptostachya Poa sieberana * Festuca arundinacea * Poa sieberana Pinus radiataspecies * Sporobolus elongotus Panicum effusum Rhagodia hastata * Marrubium vulgare Stipa sp. * Poa sieberrutain order of abundance Acetocella angiocarpa Pteridium esculeturn * Cirsium vulgare Microlaena stipoides

are dominant) Poa sieberana Lomandra long(/blia * Cynodon dactylonBothriochloa macroHypochaeris radiata

Health of site All trees removed. All trees removed. Most trees good over- Many trees removed. Many trees removed. Many trees removed.',Tree condition scaletee Table 8.18)

all health. (3) 17% dead, 40% poor,43% good. (2)

27% dead.Most other treesgood. (3)

46% trees dead.Most other treesgood. (3)

Area of site (ha) 1 0.3 2.9 3.5 11 ha. 3 ha.Studies carried out Tree planting trial Direct sowing trial Regeneration Phenology. Regenera- Phenology. Regenera- phenologv. Regal-

observation tion. Direct sowing fllon • eration. Directsowing

Previous history Had been cleared. Fenced off 1982. Fenced 1984. Rung Had not been Fenced for regenera-ask Unsupered sward of Was part of a 300 ac. 1920's;30's leaving supered since 1981 don Winter 1985.

native pasture. Had paddock, rarely used belts of trees. Fenced 1983 for •been a low intensity by stock. Rung Regrowth-->existing regeneration. Pinessheep camp. 1920's and 30's.

Aerially supered withrest of paddock.

small trees. Pastureimprovement since1960's. Sown pasture

planted in 1983 (NEcorner), 1984 (Wfence line) 1985 (S &

Since fencingvigorous regeneration.

fertilizer raised stockstock from 1 to 3.5sheep/ac.

E fence lines). ,

Short description "Island" of thickshrubby regenerationamidst heavilycleared pasture.

Improved pasture witha moderate number oftrees and littleregeneration.

Unproductive rockyhill fenced forregeneration and stockprotection.

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263

Property4(a) I 4(b)

Europambela5

Malpas Dam6(a) I 6(b)

Miramoona

Owner Fenwick family (Mngr - McNeil family)10km E. Walcha3,200 ha.Sheep and cattle

(foreshore)

Armidale City Council27km NE Armidale150 ha. approximately.Water catchment(foreshore)

Barnet family161cm NW Walcha1,796 ha.Sheep and cattle grazing

LocationProperty sizeLand use

THE CAVES SOWING SITE BERALA WOOKOOGeology, Fine grained

palaeozoic meta-Basalt and Sediment-ary

Palaeozoic meta-morphic. Grey wacke

Sediments ("Trap")

Soil Lithosol Lithosol Red and yellowpodzolic, chocolate,prairie, gravel

Red podzolic - not classified

Slope 1-50° 7-10° 1-2° 5°Position on slope Crest - lower slope Crest - mid-slope Upper slope to Crest Crest to mid-slopeAspect West North, South, East depression North,

South, East,WestEast and West East and South

Plant Community Shrub woodland and Isolated clump of Grassland (all wood- Isolated clump of Isolated clump ofopen woodland trees land cleared) trees trees

Pasture Type Natural Natural Natural pasture Improved pasture Improved pasture

Density of trees Mid.dense Isolated clump 23/ha. Isolated Isolated clump (50/ha) Isolated clump 9/ha.Density of shrubs Dense Very sparse 8/ha. Isolated 0 0Eucalypt Regeneration Very sparse Very sparse 25/ha. Isolated Isolated 4/ha. Isolated clump 7/ha.Acacia Regeneration Very sparse Very sparse 10/ha. Isolated 0 0

Main Trees & Shrubs * E. radiata * E. viminalis * E. nova-anglica * E. melliodora * E. viminalisin order of abundance ' Casuarina littoralis A. filicifolia * S. siliculiformis * E. blakelyi(* are dominant) E. viminalis Crataegus monogyna Daviesia genistifolius

*Olearia viscidula Rosa rubiginosa Nearby are:* Leptospermum brevipes E. paucifloraA. dealbata E. stellulataA. falciformisCassinia quinquenervia stellulata

E. caliginosa xstellulata I

Indigofera australis E. viminalisMain herbaceous *Poa sieberana Marrubium vulgare *Poa sieberana *Hordeum leporinum *Marrubium vulgarespecies Pteridium esculentum Cirsium vulgare *Conyza bonariensis *Lolium sp *Bromus molliformi:in order of abundance Rhagodia hastata Trifolium repens Verbascum *Bromus molliformis *Lolium sp(* are dominant) Conyza bonariensis Lepidum hyssopifolia Hordeum vulgare

Phalaris aquatica Cirsium vulgare Cynodon dactylonAsperula conferta Marrubium vulgare Festuca arundinacea

Trifolium repens Conyza bonariensis

Health of site • Few trees removed Many trees removed. Some trees badly Many trees removed. Most trees removed.Existing trees None dead. None dead. affected - most good. A few dead. None dead.

Most trees in good or Most trees good. Most trees good. Most trees good.very good health. (4) (3) - (3) Some poor. (2) (3)

Area of site 4 ha. approximately 1 ha. Approx. 45 ha. 0.45 ha. 1.8 ha.Studies carried out ' Phenology, Regenera- Direct sowing Tree planting Phenology, Regenera- Phenology, Regener

tion Regeneration • tion Direct seeding tion, Direct seeding,Planting

Previous history Settled in 1834. Most Part of a larger padd- Heavily cleared earlyof site of property cleared

1860-70. This siteock - fenced for trees1985. Pines planted

this century. Areanearby pasture

uncleared because ofsteepness and rocks.

in other sections 1985.Some native treesplanted on site 1985.

improved. Watercatchment 1985 -stock excluded sincethen.

Short description Island of scrub onrocky hillside,surrounded by pasture.

Small outcrop of treesin cleared country.

Reafforestation ofMalpas Dam fore-shores.

Remnant trees in improved pasture.

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264

property7(a)

University of New England10km North Armidale

sheep and cattle grazing.

7(b)klewholme

7(c) 8(a)

Oppehheimer family17ktn N.W. Walcha1,200 ha.Sheep and cattle grazing.

8(b)Fetali

8(c)

OwnerLocationProperty sizeLand use

"Sheep Camp"

"Creek"

'Central Woodlot"

"Dam Paddock"

"House"

"Possum"

Geology Adamellite, 10%rock outcrop

Grey-brown podzolic,scattered alluvial sand

Adamellite 10%rock outcrop

Sandy

Adamellite 10%rock outcrop

Grey-brown podzolic

Palaeozoic meta-sediments

Yellow podzolic

palaeozoic meta-sediments - chert

Yellow podzolic

Palaeozoic meta-sediments - greywackes

Not classifiedSoil,

Slope Flattish 5-6° slope Drainage line and flat 2-5°, gentle 5-10° 6° Approximately 2-5°area beside creek

Position slope Mid slope Mid-lower slope Crest to mid slope Mid-slope Mid-slope

Aspect North West East East

Plant Community Grassy woodland Grassy woodland Grassy woodland Grassy sclerophyllforest

Grassy woodland Grassy woodland

Pasture type Natural pasture Natural pasture Native pasture Natural pasture Natural pasture Natural pasture

Density of trees sparse sparse sparse Mid dense (45/ha) sparse (28/ha) sparseDensity of shrubs Virtually none 0 Virtually none Very sparse (21/ha) 0 sparseEucalypt regeneration 0 sparse Isolated clump Very sparse (10/ha) sparse clumps sparse clumpsAcacia regeneration 0 0 0 Isolated (2/ha) 0 0

Main trees and_s_linibs E. blakelyi * E. nova-anglica * E. blakelyi * E. melliodora * E. blakelyi • * E. blakelyiin order of abundance * E. melliodora * E. melliodora * E. laevopinea * E. melliodora * E. melliodora(* are dominant) Rosa rubiginosa E. bridgesiana * E. blakelyi E. viminalis E. viminalis

E. bridgesiana E. bridgesianaE. viminalis nearby E. dalryrnpleana

Lissanthe strigosaA. dealbataA. ulicifolia

Main herbaceot4 Exotic herbs adopted Native tussock grasses Vulpia bromoides * Poa sieberana * Bromus molliformis * Poa sieberana5pecies to sheep camps. dominated by Aristida Vulpia sp. Poa sieberana Asperula confertain order of abundance Native tussock grasses ramosa Danthonia sp. Vulpia sp.(* are dominant) toward edge of camp

eg. Aristida ramosaBromus mollifortnis Lepidium

hyssoptfolia

Health of site Badly affected. 74% Damage relatively mild 50% trees dead. The Many trees removed Many trees removed Many trees removed.standing trees dead. Most trees less than rest suffering from 50% dead. Most 30% trees dead. Most Most remaining treesAll of remaining trees 50% damaged (DB6-8) dieback. Many trees remaining good. remaining good. good. "badly defoliated (2) quite healthy. (3) (3) (3)(DB4-8). (3)

(1)

Area of site Approximately 2 ha. Approximately 3 ha. Approximately 3 ha. 7.2 ha. 5.8 ha. Approximately 5 ha.

Studies canied out Phenology (1982-84) Phenology (1982-84) Phenology (1982-84) Phenology, Regenera- RegeneratioR Plienology,tion. Direct sowing Regeneratioq

Previous history Sheep camp - heavily Fenced off from stock Grazed by cattle and Fenced 1985, grazed Probably never cleared Never been cleared -of site grazed - unfenced. to all regeneration, sheep. Is a small

patch of grassy wood-land amidst cleared

prior to that. Beginn-ing to get badly affect-ed by dieback and

Some ringbarkingdone in early days.

always semi-woodecFenced posts takenout from time to

paddocks.Unfenced.

mistletoe. Fenced - time. Pastureimprovement since1950's ie. aerialsuper and seeding.Fenced-

Short description Sheep camp, S.E.cnr. of property (Land

Creek, E. part ofproperty (Land Unit 5

Central part ofproperty (Land Unit 1

Remnant forest fencedoff for regeneration.

Remnant woodland,light grazing to

Woodland fenced oftfor regeneration.of site

Unit 4 Sandy Creek of Sandy Creek of Sand Creek encourage regenera-Ecological Manage-ment Area).

Ecological Manage-ment Area).

Ecological Manage-ment Area).

don.

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265

9(a) I 9(b)Ruby Hills

10,Salisbury Court

11Spy way

12(a) I 12(b)Terrible Vale

13The Hilt

Burgess family Croft family Curtis family Fred Taylor and family John & Vicki Taylor10km West Walcha 10km SE Uralla 5km SE Armidale 5km SE Kentucky 5km SE Kentucky2,080 ha. 600 ha. 0.1 ha. 960 ha.Sheep and cattle grazing Sheep and cattle House Sheep and cattle grazing Sheep and cattle

grazing •"Woodlot" "Dam" "Snow Gum Hill" "Stingybark Hill"

Palaeozoic meta- Palaeozoic meta- Basalt Palaeozoic meta- Palaeozoic meta- Palaeozoic meta-morphic sediments - morphic sediments - morphic sediments. morphic sediments sediments - schist,Phyllites and chert("Trap")

chert mixed withgranite

("trap") ("Trap") jasper, chert.

Lithosol Gley Podzolic Yellow podzolic soil Black earth Lithosol (rocky) Yellow Earth

1 ° on flat: 7°011 slope Flat 20 Flat 18-20° 7-100

Crest - mid-slope Lower slope Crest and upper slope Crest Crest to upper slope Crest to upper slope Crest to vale

West North East and West East West South and East East

Grassy schloerphyllforest

Grassland Open woodland Isolated clump Isolated clump Grassy woodland Open woodland

Natural pasture Improved pasture Natural pasture Natural Native pasture Improved pasture Natural

Mid-dense (44/ha) 0 Very sparse 6/ha Isolated clump Isolated clump 18/ha sparse 27/ha sparseVery sparse (20/ha) 0 0 0 sparse 228/ha 0 Isolated clumpsVery sparse 11/ha 0 Isolated clump 1/ha 0 sparse 220/ha 0 Isolated clumpssparse 102/ha 0 0 0 sparse 97/ha 0

* E. caliginosa None * E. blakelyi E. blakelyi * E. pauciflora * E. caliginosa * E. stellulata* E. radiata Nearby are: * E. viminalis * A. dealbata Angophora E. laevopinea* A. dealbata E. stellulata * Jacksonia scoparia floribunda. E. paucifloraE. pauciflora E. nova-anglica Pimelia linifolia . E. dalrympleanaE. stellulata E. paucVlora Hibbertia linearis A. dealbataE. bridgesianaE. nicholii

Brachylomadaphnoides

E. pauciflora xradiata '

Cryptandra amaraDillwynia retorta

Poa sieberana * Phalaris aquatica * Poa sieberana Poa sieberana * Themeda australia * Silybum marianum * Marrubium vulgarePteridium esculentum * Vulpia bromoides * Eragrostis Phalaris aquatica * Poa sieberana * Lolium perenneMicrolaena stipoides Cirsium vulgaris leptostachya * Dichelachne sciurea * Hordeum leporinum

Cynodon dactylon * Vulpia bromoides * Marrubium vulgare* Bromus molliformis * Vulpia bromoidesAsperula confena * Trifolium repens

Few trees cleared. All trees removed. Many trees removed. Most trees removed. Most trees removed. Many trees removed. .Few trees dead.Most trees in good

80% dead, 10% good,10% poor - very poor.

Few dead.Most poor - good.

50% trees dead.Remaining trees good.

25% dead.Most remaining trees

health. Many verygood.

(1) (2) (3) good (some poor).(3)

(4)

8.6 ha. 0.1 ha. 4.8 ha. 0.1 ha. 1.2 ha. 3.3 ha. 8.8 ha.

Phenology. Regnera- planting phenology, Regenera-lion. Direct sowing,

Direct sowing 1982- Phenojogy. Regenerg- Phenology. Regenerg- Phenologv,lion. Direct sowing 14.1 &a tion._ Direct sowing, Regeneration

Planting

Purchased 1962. Massof regrowth and rabbits

Completely cleared,open pasture, fenced

Heavily cleared andgrazed for sheep.

Originally timberedCleared since 1940's.

Was a sheep camp.Never excessively

Fenced off 1982 atthe end of the

and poor stocking. for a large dam. Fenced 1982 for Trees gradually rung, trees removed drought for regener-Cleared 1962-64 allyoung timber. 1970's

sowing trials, removed over time.Supered with other

gradually. Supered1 cwt/ac/gr over 15.

ation. Pines andother exotics planted

cleared out dead timber- nothing killed after

sites. Fenced May '85to allow regeneration.

years and aeriallysown to clover.

on all edges of site.

1962. Present tree - May 1985. •

Regrowth has declined Exposed windy site Remnant trees in bad Remnant trees in bad Snow gum hill, fenced Remnant trees in 1 Remnant trees in

since super (1964onwards). Regener-ating grassy forest.

beside irrigationdam.

dieback area. dieback area. to regenerate. improved pasture. improved pasture forregeneration.

r,1

Page 56: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

266

14University ofNew England

Amidale

15(a) 15(b)Woodpark

Steve Falconer and Karen Payten (manager)2km west of Annidale

16(a) 16(b) 16(c)Yalgoo

Nivison family101cm NW of Walcha

Approximately 200 ha. 3,200 ha.Goat grazing. Sheep and cattle grazing.

"Goat Paddock" "Regeneration Paddock' "Stringybark Hill" "Hudson's E" "Black Ash"

Basalt Armidale sedimentaries Palaeozoic meta-morphic sedimentswith quartz veins.

Palaeozoic meta-morphic sediments.

Palaeozoic meta-morphic sediments.

Lateritic podzolic soils Yellow earth. Lateritic podzolic. Lateritic podzolic.

Approximately 10° Approximately 2-5° Approximately 2-5° 2-8° 2° Flat 1-2°Crest-midslope Upper to lower slopes Crest to lower slope Crest to mid slope Lower slope Lower slopeSouth North, west North and east N,S,E,W East East and South

Grassy woodland Isolated trees Grassy woodland -grassland

Grassy sclerophyllforest

Grassy woodland Isolated clump

Natural pasture Natural pasture Natural pasture Natural pasture Improved pasture Improved pasture

Sparse Isolated clumps Sparse Mid dense (342/ha) Very sparse (47/ha) Isolated clump (53/ha)Very sparse 0 clumped, dense Very sparse (31/ha) 0 0Sparse 0 Sparse Isolated clumps (500/ha) 0 Isolated (1/ha)) 0 Sparse Isolated clumps 0 0

(20/ha)

E. viminalis * E. blakelyi * E. blakelyi * E. laevopinea * E. nova-anglica E. nova-anglicaE. blakelyi E. viminalis Angophora E. blakelyi E. stellulataE. melliodora E. melliodora floribunda E. melliodora E. paucifloraAng. floribunda Crataegus monogyna E. viminalis E. bridgesianaE. pauciflora E. melliodora E. viminalis .

Hawthorn, Blackberry, Lespedezia,Briar Rose, Cassiniaquinquenervia, Jack-sonia scoparia,Cryptandra amara

A. dealbata .Exocarpus

cupressiformisIndigofera australisCassiniaquinquenervia

Vulpia bromoides . Poa sieberana * Cirsium vulgare Phalaris aquaticaBothriochloa macra s ' stipoides,Microlaena * Bromus molliformis Festuca arundinaceaChloris truncata * Marrubium vulgare Polygonum avicularePanicum effusum Cynodon dactylonPoa sieberana Hordeum leporinumSporobolus elongatus Trifolium repens

Badly 70% dead; 8% very About 40% trees dead. Few removed. Many trees removed Many removed.poor, 22% poor; 0% Remaining trees badly Few dead. Few dead. Most Few dead. Mostgood. Many treesremoved.

affected by dieback. Most in good health. remaining trees ingood health.

remaining trees ingood health.

(1) (2) (3) (3) (3)

3 ha. 10.6 ha. 2.6 ha.Phenology 1982-84 Phenology and natural regeneration (1982-84) Phenology and Phenology. Regenera- Direct Sowing,

Unfenced Tree planting trial, Regeneration tion. Direct sowing Planting

Continuous sheep and Fenced off from stock Probably cleared about Paddock cleared about Cleared and grazedgoat grazing for many to allow regeneration 30 years ago and 30 years ago and let go and .pasture improved.years. Highly cleared 1978. allowed to regenerate. since. Wooded Fenced from stockand badly affected bydieback.

Existing trees wouldbe coppice from then.Grazed since then.Fenced to allowregeneration July 1984

previously. Rung,suckers cleared.Present trees regrowthfrom then. Fencedfrom stock June 1984.

July 1984. Planted400 trees, most diedor killed by mistake.

Grassy forest remnantallowed to regenerate.

Grazing continuedfrom time to time.

Page 57: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

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Page 58: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

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Page 59: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

Appen

dix V

III S

eed viability data for the species u

sed in th

e direct

sowin

g trials

SpeciesProvenance

Mean N

o.viableseed/g

Mean seed/g

Range viable

seed/g

Acacia baileyanaC

AE Am

iidale42

4242

A. dealbataW

alcha74

7474

A. filicifoliaN

.P.W

.S.

3852

38-51

Eastlake67

Arding51

A. fimbriata

N.P

.W.S

.41

4141

A. m

elanoxylonN

.P.W.S

.79

44-79

Whitfield, V

ic.44

62

Angophora floribundaK

entucky0.8

0.80.8

Casuarinacunningham

ianaB

lue hole196

196196

C. littoralis

Eastlake242

298242-352

Eastlake352

E. blakelyi15km

W.

299431

290-592Am

iidale

Miram

oona398

U.N

.E.

337

Petali592

Puddledock (1)570

Puddledock (2)290

Miram

oona/535

Petali

E. caliginosaArm

idale96

1259-154

Eastlake154

E. laevopineaEastlake

2937

22-64

Petali64

Miram

oona32

Eastlake22

SpeciesProvenance

Mean N

o.viableseed/g

Mean seed/g

Range viable

seed/g

E. melliodora

Eastlake224

13749-224

Armidale

49

E. nicholii

Eastlake534

534534

E. obliquaN

.P.W.S

.26

2626

E. paucifloraSalisbury Plain

3785

37-123

Yalgoo94

Eastlake123

E. radiataEastlake

191177

125-234

Ruby H

ills159

Eastlake125

Yalgoo234

E. stellzdataR

uby Hills

62122

62-251

Yalgoo251

Kentucky81

Yalgoo170

E. viminalis

Kentucky124

280134-572

Salisbury Court134

Walcha

259

Miram

oona309

Eastlake572

E. youmanni

Walcha

5050

50

Leptospermum

brevipesKentucky

3,8823,882

3,882

L. flavescensPuddledock

1,1901,190

1,190

Page 60: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

Appendix IX

Details of individual direct sowing trials: sowingdetails and results

GRADED TREATMENTS

270

■■•■■■4-■••••■••••

Site: Petali (8a) - Natural pasture. Sown: 6.10.1986

Preparation: Graded bare, about lm wide.

win: Seed sprinkled over graded area by hand.

Bulked with: Sand. Ara:

160 x lm =160m2 Total length: 160m

Species and ProvenanceSowin;

gin/inRate

seed/m1 month after

seedlings/msowing% survival

5seedlings/m

months after sowing% survival Mean ht.(m)

E. hlakelyi 1.25 740 0 0 0 0 -(Petali 2.8.1986)

E. laevopinea 0.88 56 0 0 0 0 -(Petali 5.6.1985)

TOTAL 2.1 796 0 0 0 0 -

Site:

Ruby Hills (9a) - Natural pasture. Sown: 5.9.1986

Preparation: Graded off topsoil; chisel ploughed.

win : Seed sprinkled along row by hand and lightly covered with soil by hand.

Bulked with: Rice hulls (1 bucket). Am: 86 x 3m = 260m2

Total length: 86m

Species and ProvenanceSowin;

gm/mRate

seed/m8 months after

seedlings/insowing% survival

19seedlings/m

months after sowing% survival Mean ht.(m)

Acacia dealbata 19.8 12.1 61 9.5 49 1.2(Walcha 1/1986)

E. caliginosa 5.8 1.5 26 0.7 12 0.4(Ruby Hills)

E. pauciflora 7 7 7 0.1 7 0.6

E. radiata 16.3 3.1 19 1.4 9 . 0.4(Ruby Hills)

Total Eucalypt 22.1 4.6 21 2.2 10

TOTAL 41.9 16.7 40 11.7 28 •

Site: Ruby Hills (9a) - Natural pasture. .Sow

18.9.1987

Treatment: As above.

Sowing: as above, same seed lot except for addition of E. youmanni.

Am:

100 x 5m = 500m2Total length: 85m

Species and ProvenanceSowin;

gm/mRate

seed/m7 months after

seedlings/insowing% survival Mean ht.(m)

A. dealbata 17 5.3 31 0.2(Walcha 1/1986)

E. caliginosa 5 0.2 4 0.2(Ruby Hills)

E. radiata 14 0.1 0.7 0.2(Ruby Hills)

E. youmannii (20m) 150 0.5 0.3 0.1(Walcha)

Total Eucalypt 169 0.8 0.5 •

TOTAL 186 6.1 3.3 .

Page 61: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

GRADED 7E,A,TMENT

Europambela (4b) - Natural pasture. Sown: July 1984

Treatment: Top soil graded July 1984, for width of 2m and Ripline down centre.

Sowing: Seed sprinkled in row.

Bulked with: Sand. Am: 3 x 30m = 90m2Total length: 90m

Species and ProvenanceSowin;

gm/mRate

seed/m24 months after

seedlings/msowing

mean ht.(m)46 months after

seedlings/msowing

mean ht.(m)

A. dealbata ? 1 0.02 1.2 0.02 1.3(Europambla)

A. filicifolia • 0.36 1.0 0.37 2.1(Armidale)

Casuarina cunninghamiana 0 - 0 -(Apsley)

C. littoralis 0 - 0 -(Europambela)

E. blakelyi 0 - 0 -(Annidale)

E. laevopinea 0 - 0 -(Inglebar)

E. pauciflora 0.02 0.3 0.02 2.0(Europambela)

E. stellulata 0 - 0 _(Inglebar)

Leptospermum brevipes 0 - 0 -(Europambela)

'DOTAL 0.40 0.41

Europambela (4b) - Natural pasture. October 1985

Treatment: Graded in July 1984. Any weed growth was sprayed just prior to sowing..

Sowing: Spot sown - spots about lm apart.

Ate:

6 x 30m =180m2Total length: 180m

Species and ProvenanceNo. of

spots sownlength

(m)4 months after

seedlings/m-

sowing% of spots with

seedlings

29seedlings/m

months after sowingTo spots mean ht.(m)

A. filicifolia 143 100 0.7 14 0.6 13 1.5

C. cunninghamiana 143 100 0 0 0 0 -

C. littoralis 143 100 0 0 0 0 -

E. globulus bicostata 143 100 0 0 0 0 -

E. laevopinea 143 100 0.02 0.7 0 0 -

E. nova-anglica 19 13 0 0 0 0 ' -

E. pauciflora 19 13 0 0 0 0 -

E. radiata 86 47 0 0 0 0 -L. brevipes 19 13 0 0 0 0 -

271

Page 62: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

CULT TNATED TREATMENTS

Site: Salisbury Court - Natural pasture Sown: 10.10.1985

Preparation: Deep ripped to 60cm depth. Worked several times with discs.

Sowing: Hand sown. 2 rows: seed sprinkled along row and raked with back of rake, 5 rows spot sown - spots 1.5m and pressed by foot. Depth ofsowing lcm or less.

Bulked with: Coarse sand, 1 bucket.

Species and Provenance

Sowing

gm/m

Rate

seed/m

5Line Sowing

seed/m

Months after

%survival

sowingSpot Sowing

seed/m %survival

seedlings/m

Line Sowing%

survival

30 months

meanht.(m)

after sowing

seedlings/m

Spot Sowing%

survivalmeanht.(m)

A. baileyana 0.15 6.3 .48 7.6 .94 14.9 .004 .06 .1 .007 .1 .2(Armidale 1984)

Ang. floribunda 0.2 0.16 0 0 .02 12.5 0 0 - 0 0 -(Kentucky 1985)

E. blakelyi 0.2 60 .02 .03 .5 .03 .05 .4(15km W. Armidale 1983)

E. melliodora 0.06 13 .04 .28 .4 .02 .15 .3(Eastlake, Uralla 1985)

Total Eucalypt 0.26 73 .8 1.1 .76 1.0 .06 .08 .05 .07

Total 0.61 80 1.28 1.6 1.72 2.2 .064 .08 .057 .07

Site:

Salisbury Court (as above)

Sown: 30.10.1986

Preparation: Disced several times to depth of 15cm. Soil scraped away manually, forming a trench with partitions to prevent wash.

Sowing: Spot sowing. Seed covered lightly and trodden in by foot. Each spot staked, 0.5m apart.

Bulked with: 1 bucket dry sand. Area: 1 row, 100m long by lm = 100m2

Total length: 100m

Species and ProvenanceSowing

gm/mRate

seed/m6 Months after

seedlings/msowing% Survival

17Seedlings/m

Months after sowing% Survival Mean ht.(m)

A. filicifolia 0.80 41 0.6 1.5 0.18 0.44 0.2(Arding 1986)

E. blakelyi 0.90 358 0.03 0.008 0.02 0.006 0.2(Miramoona 1985)

E. pauciflora 0.90 33 0 0 0 0 -(Salisbury Plain 1986)

E. viminalis 0.08 11 0.02 0.19 0.01 0.09 0.1(Salisbury Court 1986)

Total Eucalypt 1.88 402 0.05 0.01 0.03 0.008 0.2

TOTAL 2.68 443 0.65 0.15 .21 0.05

272

Area sown: 7 rows, 140m long = 0.4ha

Total length: 1000m

Page 63: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

RIPPED WITH MULCHING BLADE

Site: Belhaven (lb) - Native pasture Sown: November 1984, November 1985, May 1986 and August 1986.

Preparation: No treatment; a normal sward of native pasture. Never been supered. Line ripped with chisel tyne fitted with a mulching blade. Tyne penetrated20cm, blade was 5cm deep and cut under grasses on each side of row.

Sowing: Seed spread by hand into row immediately behind plough and loosely covered by foot.

Bulked with: Coarse sand; 1-2 buckets. Area: 0.5 ha

Species and Provenance

NovemberSowin3

gm/m

1984 sowingRate

seed/m

(3120m)% survival12 months

Sowinggm/m

Rateseed/m

November 1985 sowing% survival20 months

(360m)Mean ht.

(m) 20 months

A. dealbata .005 0.4 0 .04 3.6 .03 0.2(Canberra 1984)

A. melanoxylon .001 0.05 0 .009 0.4 0 -(NE Victoria 1983)

C. cunninghamiana .0006 0.1 0 .005 1.0 0 -(Blue hole 1982)

E. melliodora .018 4.1 0 0.15 35.9 .08 0.2(20km W. Armidale 1983)

L.flavescens .0005 0.2 0 .004 1.9 0 -(Ebor 1982)

Total Eucalypts .018 4.1 0 .015 35.9 .08

TOTAL .03 5 0 0.2 42.8 .01

November 1985 sowing (370m) May 1986 sowing (290m) August 1986 sowing (96m)Sowing rate 20 months Sowing rate 12 months Sowing rate 9 months

% mean % mean % meanSpecies and Provenance gm/m seed/m survival ht.(m) gm/m seed/m survival ht.(m) gm/m seed/m survival ht.(m)

A. filicifolia 0.1 4 1.0 .1 0.1 5 1.0 0.1 .4 15 0.4 0.1(Armidale)

A. firnbriata 0.1 4 .6 .1 0.1 5 0.8 0.1 .4 16 0.3 0.17

A. melanoxylon 0.01 1 0 - 0.01 1 0 - .04 3 0 -

E. blakelyi 0.1 36 0 - 0.1 41 0 - 0.4 124 0 -(Armidale 1985)

•E. caliginosa 0.06 5 0 - 0.06 6 0 - 0.2 19 0 -(North of Armidale 1983)

E. obliqua 0.04 1 0 - 0.06 1 0 - 0.2 4 0 -

L.flavescens 0.02 28 0 - 0.04 45 0 - 0.1 136 0 -(Belhaven 1984)

Total Eucalypts 0.2 43 0 - 0.2 49 0 - 0.8 148 0 -

TOTAL 0.4 79 .08 0.5 104 .08 1.7 317 0.03

273

Page 64: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

HERBICIDE TREATMENTS 27451e: Birrhalce (2b) - Improved pasture. am_vn: 11.9.1985

Preparation: Grass eaten short. Boom sprayed with Roundup (31/ha) over whole site one week before sowing.

Sowing: Begg sod seeder. Blocked every second tyne to give 8 rows 35cm apart. Furrow 3cm deep, seed sprinkled on surface and soil and leaf materialfell on top - depth about 1cm.

Bulked with: 14kg bran plus 14kg wheat to aid flow. &a: Sha. Total length: 16,600m.

Species and ProvenanceSowing

grtitniRate

seed/m6 months after

seedlings/msowing% survival

A. dealbata 0.002 0.2 0 0

Angophora floribunda 0.01 0.008 0 0

E. stellulata 0.008 0.35 0 0

Leptospennum brevipes 0.001 3.9 0 0

TOTAL 0.02 4.5 0 0

,Bile: Ruby Hills (9a) - Natural pasture. Sown: 18.9.1985

Preparation: Sprayed Roundup (4 L/ha) plus Dicamba (1.8 L/ha) June and Roundup (3.5 L/ha) September.

Sowing: Gyral air seeder, 2.5m wide with lucerne points, chisel tyne. Width between rows 20cm.

Bulked with: 15kg rice hulls. AtraI: lha. Mall:oar 3,333m

Species mid ProvenanceSowing

gni/mRate

seed/m6 months a

seedlings/mter sowing

% survival

A. dealbata 0.01 0.9 0 0E. calignosa 0.03 2.9 0 0

E. radiata 0.04 6.6 0 0

E. stellulata 0.01 0.7 0 0

TOTAL 0.09 11.1 0 0

Site:Yalgoo (16b and c) - Improved pasture. &Bo: 26.9.1985

Preparation: Site 16b grazed flat, sprayed Roundup (6 Ulm) 4 weeks before sowing. Site 16c, burnt August, sprayed Roundup (6 L/ha) 4 weeks beforesowing. Burnt again the following day (accidentally). Ploughed twice (discs) in week before sowing.

Sowing: Duncan 734 multi seeder 2.5m wide. 15 tynes 15cm apart. Machine cuts groove, 2 wheels open groove, seed falls in soil closes over. Depth 1-2cm.

Lam: (both sites pooled): l.9ha. Total length: 7,600m.Bulked with: 20kg rice hulls.

Species and ProvenanceSowing

gm/mRate

seed/m6 months after

seedlings/msowing% survival

A. baileyana 0.01 0.6 0 0

E. blakelyi 0.03 10.6 0 0E. stelhdata 0.004 1.0 0 0

Leptospermum flavescens 0.05 5.7 0 0TOTAL 0.05 17.9 0 . 0

Silt: Yalgoo (16b) - Improved pasture. Sown: 20.10.1986

Preparation: Sprayed Roundup 2 months (August) and 3 weeks (early October) before sowing.

Sowing: Duncan 734 multisecder. All tynes blocked except 3 spaced 1.5m apart. Depth about 1cm.

Bulked with: 5 L rice hulls. 150 x 3m = 450m2

Follow up: Hand weeding December; Mown and Roundup wiped in February.

Total length: 450m

Species and ProvenanceSowing

gm3InRate

seed/m8 months after

seedlings/msowing% survival

29seedlings/m

months after sowing% survival Mean ht.(m)

A./I/Walla 0.3 13.6 0.49 3.6 0.4 2.6 ' 1.8(Arding 1/1986)

E. pauciflora ' 0.07 6.3 0.002 0.04 0.004 0.07 1.5(Yalgoo 5/1986)

E. radiata 0.2 57.2 0.0004 0.008 0 0 -(Yalgoo 2/1986)

E. stellulata 0.04 7.6 0.007 0.09 0 0 -(Yalgoo 5/1986)

Total Eucalypts 0.36 71.0 0.01 0.02 0.004 0.006

TOTAL 0.62 84.6 0.51 0.6 0.4 0.42

Ere: Eastlake - Natural pasture. Sown: 22.9.1986

Preparation: Slashed areas 1 and 3 in February. All 3 areas sprayed Roundup in April and again 2 weeks after sowing.

Bossin g : Machine built by G. & J. Williams. Coulter blade to make a cut, a flange to open the trench, a Baker's Boot seeding foot, a bolt dragged behindto cover the seed and a seedbox on top (Plate 10.1). Single row sowing.

Bulked with: 321.. laying mesh, ltsp Terrasorb 1005 graphite seed coating, ltsp diazanone insecticide.

Total arca: 2ha.Ares: Area 1: 405m long; Area 2: 106m long; Area 3: 300m long. Total length: 810m.

Species and ProvenanceSowing

g /mRate

seed/m7 months after

seedlings/msowing% survival

34seedlings/m

months after sowing% survival I Mean ht.(m)

A. filicifolia 0.13 9.0 .13 1.5 .06 .7 1.5

C. &torahs 0.03 7.3 0 0 0 0 -E. laevopinea 0.15 4.3 .003 .09 .001 .03 1.0

E. radiata 0.31 39.1 .001 .02 .006 .02 1,0

Total Eucalypts 0.46 43.4 .004 .03 .007 .02 1.0

TOTAL 0.59 59.7 .13 .22 .07 .12

Page 65: 07 Bibliography-Appendix IX Curtis · In: Revegetation Workshop - Proceed-ings of a Workshop held in Adelaide. 27-29 March 1985. 43-46 (ed.) J. Venning Dept. Environment and Planning,

BURNT TREATMENTS

Site: Europambela (4b) - Natural pasture, October 1986.

Preparation: Site burnt the day before sowing. Thick sward of dead thistles, grass, horehound, verbascum.

Sowing: Spot sown using 'pepper pot'. Individual spots staked. Fruit containing brush laid on some.

Area: 0.5ha.

Species and provenance .No. spots

sown

AT% spots

with seedlings

3 MONTHSTotal no.seedlings

% survivalof seedlings

% spotswith seedlings

AT 17 MONTHSTotal No.seedlings

% survivalof seedlings

Meanht.(m)

E. radiata (brush) 4 0 0 0 0 0 0 -(Europambela)

Casuarina littoralis (brush) 3 0 0 0 0 0 0 -(Europambela)

E. viminalis (brush) 1 0 0 0 0 0 0 -(Europambela)

Eucalypt and Casuarina mix 28 11 10 ? 0 0 0 -C. cunninghamiana

(Apsley)C. littoralisE. blakelyi

(Miramoona)E. globulus bicostataE. laevopineaE. paucifloraE. radiataE. stellulataE. viminalisHakea eriantha .L. brevipes

A. filicifolia 12 spots 100 114 1.9 58 9 0.15 0.6(6120 seeds)

TOTAL 48

275