Printer Friendly
The Free Library
22,719,120 articles and books

Management of Eucalyptus grandis coppice regeneration of seedling parent stock in Zululand, South Africa.



Introduction

Plantation forestry carried out in the Zululand region is of great importance as it contributes 18% of the total eucalypts grown for hardwood pulpwood pulp·wood  
n.
Soft wood, such as spruce, aspen, or pine, used in making paper.


pulpwood
Noun

pine, spruce, or any other soft wood used to make paper

Noun 1.
 in South Africa South Africa, Afrikaans Suid-Afrika, officially Republic of South Africa, republic (2005 est. pop. 44,344,000), 471,442 sq mi (1,221,037 sq km), S Africa.  (Directorate Forest Policy 2000). One of the notable attributes of Eucalyptus species This is a list of 746 Eucalyptus species.

Binomial Name Common name(s)
Eucalyptus abdita
Eucalyptus absita Badgingarra Box
Eucalyptus acaciiformis Wattle-leaved Peppermint
Eucalyptus accedens Powder-barked Wandoo
 is their ability to survive and produce new growth following adverse environmental conditions (Florence 1996). This is largely a function of the bud systems of the genus. Although four types of buds are recognised in eucalypts, coppice regrowth Re`growth´   

n. 1. The act of regrowing; a second or new growth.
The regrowth of limbs which had been cut off.
- A. B. Buckley.
 in Eucalyptus grandis Eucalyptus grandis, Flooded gum, Rose gum, is a medium to tall tree with smooth bark, rough at the base fibrous or flaky, grey to grey-brown.

Leaves are stalked, lanceolate to broad lanceolate, discolorous, to 15 x 3 cm, glossy dark green.
 following felling is confined to development from epicormic buds, which are situated in the live bark, or cambium cambium (kăm`bēəm), thin layer of generative tissue lying between the bark and the wood of a stem, most active in woody plants. The cambium produces new layers of phloem on the outside and of xylem (wood) on the inside, thus increasing , at the base of the tree (Penfold and Willis 1961). This survival mechanism is exploited in commercial plantations for reestablishment following felling. For E. grandis the coppice shoots can be selectively thinned over time and managed as a coppice stand for the production of pulpwood (MacLennan and Schonau 1991; Little 2000).

Previous research on coppice management in South Africa focused primarily on the effects of the number of stems remaining on the stump campaigning for public office; running for election to office.

See also: Stump
, and on the effects of frequency and timing of coppice reduction (thinning of the shoots) on timber volume and properties. This produced recommendations which are still used today (Schonau 1980, 1990; Stubbings and Schonau 1980; Bredenkamp 1991).

In terms of the timing of reduction operations, these recommendations state that coppice should be reduced in two operations: first to two or three stems per stump when the dominant shoot height is 4 m, and later to the original stocking when the dominant shoot height is 8 m. However, an experiment on the reduction of coppice of E. grandis in Zululand indicated that first coppice could be reduced to two shoots per stump when the shoots were under 3 m in height (Bredenkamp 1991). That study also questioned the value of fertiliser application and weed control Weed control is the botanical component of pest control, stopping weeds from reaching a mature stage of growth when they could be harmful to domesticated plants and livestock by physical and chemical methods.  in managed coppice stands, and the potential to apply herbicide herbicide (hr`bəsīd'), chemical compound that kills plants or inhibits their normal growth. A herbicide in a particular formulation and application can be described as selective or nonselective.  instead of manually removing secondary coppice regrowth using axes.

The present trial has been undertaken to investigate the effects of early reduction of first coppice, chemical control of secondary coppice regrowth, fertiliser application and weed control on final yield.

Materials and methods

The trial was located in Southern Area, Zululand, on a SAPPI SAPPI South African Pulp and Paper Inc.  plantation at 28[degrees]40'S and 32[degrees]03'E. The climate is sub-tropical, with mean annual precipitation of 1089 mm and temperature of 21.6[degrees]C. There is good rainfall distribution, 35-40% occurring in winter, and this combined with mild winters allows trees to grow throughout the year (Schulze 1997). The trial was situated at an altitude of 50 m on a deep Fernwood 1210 soil (using the taxonomic system for South Africa, Soil Classification Working Group 1991). The parent material of the soil (as for most of the Zululand region) is aeolian Ae·o·li·an  
adj.
1. Of or relating to Aeolis or its people or culture.

2. Greek Mythology Of or relating to Aeolus.

3. aeolian Variant of eolian.

n.
1.
 in origin, and as such contains little organic carbon (<0.5%) or clay (<6%). The growth rate of E. grandis for this region of Zululand is considered to be good, with mean annual increments of up to 55 [m.sup.3] [ha.sup.-1] being recorded when optimum planting densities are coupled with fertiliser application and weeding during establishment (Coetzee et al. 1996). The site had been planted to E. grandis for pulpwood and was felled in June 1992. The trees had been planted at 2.9 m x 2.9 m spacing, resulting in a stocking of about 1185 stems [ha.sup.-1].

Six treatments (Table 1), replicated eight times, were laid out in a randomised Adj. 1. randomised - set up or distributed in a deliberately random way
randomized

irregular - contrary to rule or accepted order or general practice; "irregular hiring practices"
 complete block design. Each treatment plot consisted of 7 x 8 trees, of which only the inner 3 x 4 trees were measured. The initiation and timing of events for the different treatments are listed in Table 2. Weed growth in the weed-free treatment (Treatment 6 in Table 2) was controlled on three occasions with glyphosate glyphosate

herbicide and desiccant for grains. Heavy doses to birds cause soft shells on their eggs.
 sprayed at 4 L [ha.sup.-1]. Weed control beyond 21 mo was not necessary due to the effect of shading following canopy closure, which reduced the growth of competing vegetation. Initial weed growth in the remainder of the treatments was dominated by Panicum maximum Jacq., and as for Treatment 6, weed growth following canopy closure was negligible. The foliage of the secondary coppice regrowth (Treatments 3 and 4 in Tables 1 and 2) was sprayed with the appropriate herbicides until runoff, using a solid-cone nozzle. Care was taken not to spray the foliage of the selected coppice stems.

Coppice height was measured regularly during the first 20 months after felling in order to determine the timing for reduction operations, and then again just before the trees were felled (8 y). Diameter at breast height Diameter at breast height, or DBH, is a standard method of expressing the diameter of the trunk of a tree.

The trunk is measured at the height of an adult's breast; this is defined differently in different situations, with foresters measuring the diameter at 1.
 was first measured at 7 mo after felling and then on an annual basis. These diameter measurements, together with the number of stems per treatment plot, were used to calculate basal area on a treatment plot basis. As a suitable volume equation for E. grandis coppice could not be found, the merchantable volume per tree was first calculated using Bredenkamp's (2000) tree volume equation for E. grandis, before merchantable volume on a hectare basis was determined. Merchantable volume refers to the underbark volume to a small-end diameter of 7.5 cm. Analysis of variance, appropriate for a randomised complete block design, was used to test for treatment effects. Prior to all analyses, Bartlett's Test Bartlett's test (Snedecor and Cochran, 1983) is used to test if k samples have equal variances. Equal variances across samples is called homoscedasticity or homogeneity of variances.  (Snedecor and Cochran 1956) was used to test for homogeneity of variance, an assumption which must be met for a valid analysis of variance. Assessments of the weed growth were scheduled to be carried out when coppice growth responses to competition were detected. No significant differences were detected between treatments, so no vegetation assessments were carried out for the duration of the trial.

Results and discussion

Although the site had been selected to include only that part of the compartment within which there was good tree stocking, high mortality after felling resulted in the survival of only 885 coppice-bearing stumps [ha.sup.-1]. Similar stump mortality after felling (30%) was recorded by Bredenkamp (1991) for E. grandis in Zululand. To reach the original stocking of about 1185 stems [ha.sup.-1], two stems were left on certain stumps to compensate for those that were missing. This resulted in a mean stocking of 1247 stems [ha.sup.-1] after the final reduction (at a height of 8 m) at 20 mo. Further stem mortality over time left a final stocking of 1140 stems [ha.sup.-1], a 4% reduction from the original stocking (Table 3).

No significant differences were detected for any of the variates measured, either for the duration of the trial or at the last measurement. The mean height for the trial at eight years was 21.3 m, the mean diameter at breast height 18.6 cm, the mean basal area 30 [m.sup.2] [ha.sup.-1] and the merchantable volume 276 [m.sup.3] [ha.sup.-1]. Bearing in mind that these results are based on the data of one trial only and are particular to the conditions under which the trial was conducted, the non-significant results obtained nonetheless indicate the possibility for alternative coppice management practices as outlined in the objectives.

Neither weeding nor fertiliser application produced any benefit in terms of coppice growth when compared to the control. The application of fertiliser to seedlings immediately following planting (60 kg N [ha.sup.-1]) has yielded significant gains on similar sites in the same region (du Toit 1995), a response attributed to enhanced nutrient supply during the period before tree roots thoroughly colonise Verb 1. colonise - settle as a colony; of countries in the developing world; "Europeans colonized Africa in the 17th century"
colonize

annex - take (territory) as if by conquest; "Hitler annexed Lithuania"
 the site. In another study on a similar site, however, an application of fertiliser (70-140 kg N [ha.sup.-1]) to seedling crops, three to six months after establishment, yielded no significant response (Noble 1992). Post-establishment applications of fertiliser (80 kg N [ha.sup.-1]) have been beneficial on only the most infertile in·fer·tile
adj.
Not capable of initiating, sustaining, or supporting reproduction.


infertile,
adj unable to produce offspring.
 sites of the coastal plain, which had been burned and tilled extensively under previous shifting agricultural use (du Toit et al. 2001). In two E. grandis coppice trials conducted on sites where tree performance is enhanced through the application of phosphorus, Schonau et al. (1981) were able to show that coppice growth responded positively to the application of fertiliser, but the subsequent high cost of weeding and fertiliser at the rates applied made this operation a doubtful proposition.

In the present trial the lack of response to the fertiliser applied (94 kg N [ha.sup.-1]) or weed control may be in part attributed to the use of the existing and well-established root system of the stump by the coppice shoots (Tschaplinski and Blake 1989). Young coppice shoots may be able to obtain necessary nutrients and moisture from a larger soil resource than that available to newly-planted seedlings. In addition, some of the necessary nutrients and water may come from resources already existing in the stumps and associated roots (Bamber and Humphreys 1965). An additional reason for the lack of response to fertiliser could be that the first coppice reduction treatment, immediately prior to fertiliser application, decreased the size of the sink that existed for nutrient uptake in the above-ground biomass. The rapid initial growth of the coppice shoots when compared to seedlings (Blake 1980; Taylor et al. 1982), combined with their slightly elevated position on the stumps, may also have contributed to the lack of weed competition detected. This lack of response to weed control has been confirmed in a subsequent Eucalyptus coppice trial (Little 1998), and in a Eucalyptus hybrid post-establishment weed control trial (Little and Rolando 2002). It is recommended, though, that woody and invasive weeds be controlled. This will help to reduce under-canopy fuel loads and risks of uncontrolled fires, reduce the seed bank of unwanted vegetation and prevent its reestablishment, and improve access for silvicultural operations (Denny and Schumann 1993).

There was no significant difference in yield between carrying out an early reduction of first coppice at a height of 1.5 m, and the control (reduction of first coppice to two stems at a height of 4 m). The rationale for early reduction includes the potential saving of labour required to carry out the reduction operation due to the smaller size of the stems, and a possible growth benefit resulting from the channelling of plant resources into the selected stems at an earlier age. The lack of significant differences between these two treatments may in part be explained by selective thinning, at 8 m in height, to the original stocking, by removing the smaller of the two stems per stump. Apart from the potential benefits (which did not materialise in this trial), disadvantages may include an increase in the incidence of windthrow due to the poor attachments of the coppice shoots to the stump, the inability to accurately select shoots of suitable stem form when they are only 1.5 m in height, and the production of more secondary coppice regrowth following reduction.

No increased incidence of windthrow following an early reduction was detected in this trial, as indicated by the lack of significant treatment differences obtained for the final stocking. The nature of the trial design might not have lent itself to the detection of differences in windthrow between treatments due to the sheltering effect of adjacent treatments. Much larger plots should be used in any test of susceptibility to windthrow. The reduction to two stems per stump when the coppice was 1.5 m high was not based on the selection of dominant shoots, as most of the shoots were of equal size. In subsequent trials, the early reduction of coppice has been delayed until the shoots have a dominant top height of 2 m to minimise this problem (Little 1997, 1998). Although it was not tested in this trial, data from subsequent trials have shown that the early reduction of first coppice leads to increased regrowth of secondary coppice requiring more frequent control in order to avoid a loss of growth (Little 1997, 1998). The timing of the first reduction operation in the selected management regime will depend on economic benefits arising from the timing, number and cost associated with each operation, rather than benefits from improved growth.

Regrowth of secondary coppice following the initial coppice reduction treatments was controlled either by manually removing it with a bushknife or by spraying it with herbicides (glyphosate at 0.6% or paraquat paraquat /para·quat/ (par´ah-kwaht) a poisonous compound, some of whose salts are used as contact herbicides. Contact with concentrated solutions causes irritation of the skin, cracking and shedding of the nails, and delayed healing of  at 0.4%). Of the two herbicides tested, glyphosate gave far better control (sprayed on two occasions) than either manual removal or spraying with paraquat (removed or sprayed on four occasions). Glyphosate, a systemic herbicide, resulted in the death of the coppice regrowth following translocation of the active ingredient An active ingredient, also active pharmaceutical ingredient (or API), is the substance in a drug that is pharmaceutically active. Some medications may contain more than one active ingredient.  without negatively affecting the performance of the remaining coppice stems. This result has been confirmed in a subsequent trial carried out on E. grandis x E. camaldulensis hybrid clones in Zululand (Little 1998). In contrast, paraquat, a contact herbicide, resulted only in the desiccation des·ic·ca·tion
n.
The process of being desiccated.



desic·ca
 of the sprayed foliage, leaving the epicormic buds to re-sprout. As there was no significant difference in coppice volume between these methods of controlling secondary regrowth and the control, spraying with glyphosate would seem the logical choice. Besides the economic benefits, damage to the remaining stems or bark through manual control will also be alleviated.

Acknowledgements

SAPPI and their foresters who have been involved with this trial are acknowledged for their support and the use of their property. Sincere thanks also go to the technical staff of the ICFR ICFR Internal Control Over Financial Reporting (SOX compliance, financial reporting)
ICFR Institute for Commercial Forestry Research (South Africa) 
 for their help in establishing and maintaining the trial, and to Lauren MacLennan and Carol Rolando for their constructive comments.

Revised manuscript received 22 August 2002

References

Bamber, R.K. and Humphreys, RR. (1965) Variations in sapwood sapwood, relatively thin, youngest, outer part of the woody stem of a tree, the part that conducts water and dissolved materials. In the cross section of a tree, the sapwood is recognizable by its texture and color; it is softer and lighter than the inner heartwood.  starch levels in some Australian forest species. Australian Forestry 29, 15-23.

Blake, T.J. (1980) Effects of coppicing For the locality in Oldham, see Coppice, Greater Manchester.

Coppicing is a traditional method of woodland management in which young tree stems are cut down to near ground level.
 on growth rates Growth Rates

The compounded annualized rate of growth of a company's revenues, earnings, dividends, or other figures.

Notes:
Remember, historically high growth rates don't always mean a high rate of growth looking into the future.
, stomata sto·ma·ta  
n.
A plural of stoma.
] characteristics and water relations in Eucalyptus camaldulensis Dehn. Australian Journal of Plant Physiology 7, 81-87.

Bredenkamp, B.V. (1991) Results of an Eucalyptus grandis Coppice Reduction Trial in Zululand. CSIR CSIR Council for Scientific and Industrial Research (Ghana)
CSIR Council of Scientific and Industrial Research (India)
CSIR Centre for Scientific and Industrial Research
 Report No. FOR 38. CSIR, Pretoria, South Africa.

Bredenkamp, B. (2000) Volume and mass of logs and standing trees. In: Owen, D.L. (ed.) Forestry Handbook. V and R Printers, Pretoria, pp. 167-174.

Coetzee, J., Chiswell, K., Storey, E and Arbuthnot, A. (1996) The Final Results of the E. grandis Spacing Trial, Kwambonambi, for Age Two to Ten Years. ICFR Bulletin 10/96. ICFR, Pietermaritzburg, South Africa. 31 pp.

Directorate Forest Policy (2000) Revised commercial timber resources and roundwood Roundwood (Irish: An Tochar, meaning The Causeway) is a village in County Wicklow, Ireland. It was listed as having a population of 518 in the census of 2002.  processing in SA 1997/98 and commercial timber resources and roundwood processing in SA 1998/99. Director-General, Water Affairs and Forestry, Pretoria, South Africa.

Denny, R.P. and Schumann, A.W. (1993) Weed control. In: van der Sijde, H.A. (ed.) Forestry Handbook. The Southern African Institute of Forestry, pp. 219-230.

du Toit, B. (1995) Nutrition research. Section II: Coastal Zululand. ICFR Annual Research Report 1995. ICFR, Pietermaritzburg, South Africa, pp. 143-152.

du Toit, B., Arbuthnot, A., Oscroft, D. and Job, R.A. (2001) The effects of remedial fertilizer treatments on growth and pulp properties of Eucalyptus grandis stands established on infertile soils of the Zululand Coastal Plain. Southern African Forestry Journal 192, 9-18.

Florence, R.G. (1996) Ecology and Silviculture silviculture: see forestry.  of Eucalypt Forests. CSIRO Publishing, Collingwood. 413 pp.

Little, K.M. (1997) Vegetation management. ICFR Annual Research Report 1997. ICFR, Pietermaritzburg, South Africa, pp. 87-88.

Little, K.M. (1998) Vegetation management. ICFR Annual Research Report 1998. ICFR, Pietermaritzburg, South Africa, p. 80.

Little, K.M. (2000) Eucalypt coppice management. ICFR Technical Innovations 2000101. ICFR, Pietermaritzburg, South Africa.

Little, K.M. and Rolando, C.A. (2002) Post-establishment vegetation control in a Eucalyptus grandis X E. camaldulensis stand. Southern African Forestry Journal 193, 77-80.

Maclennan, L.A. and Schonau, A.P.G. (1991) Eucalypt Coppice Regeneration and Management. ICFR Pamphlet 1991. ICFR, Pietermaritzburg, South Africa.

Noble, A.D. (1992) Nutrition of Eucalypts on the Zululand Sands. ICFR Bulletin 29/92. ICFR, Pietermaritzburg, South Africa. 46 pp.

Penfold, A.R. and Willis, J.L. (1961) The Eucalypts. Interscience Publishers, New York New York, state, United States
New York, Middle Atlantic state of the United States. It is bordered by Vermont, Massachusetts, Connecticut, and the Atlantic Ocean (E), New Jersey and Pennsylvania (S), Lakes Erie and Ontario and the Canadian province of
, pp. 33-38.

Schonau, A.P.G. (1980) Timber density of planted parent trees and first generation coppice of Eucalyptus grandis. Wattle wattle, in botany: see acacia.  Research Institute Report for 1979-1980. ICFR, Pietermaritzburg, South Africa, pp. 107-110.

Schonau, A.P.G. (1990) Growth, yield and timber density of short rotation coppice Short Rotation Coppice (SRC) is grown as an energy crop for use in power stations, alone or in combination with other fuels such as coal. Species used
SRC uses high yield varieties of poplar and willow.
 stands of Eucalyptus grandis. In: Proceedings of the 19th IUFRO IUFRO International Union of Forestry Research Organizations  World Congress, August 1990, Montreal, 4, 14.

Schonau, A.P.G., Boden, D.I., Herbert, M.A. and Brice Bruce, A.P. (1981) Fertilizing coppice. Wattle Research Institute Report for 1980-1981. ICFR, Pietermaritzburg, South Africa, p. 57.

Schulze, R.E. (1997) South African Atlas of Agrohydrology and Climatology climatology

Branch of atmospheric science concerned with describing climate and analyzing the causes and practical consequences of climatic differences and changes. Climatology treats the same atmospheric processes as meteorology, but it also seeks to identify slower-acting
. Water Research Commission, Pretoria, Report TT82/ 96.

Snedecor, G.W. and Cochran, W.G. (1956) Statistical Methods Applied to Experiments inAgriculture and Biology. The Iowa State College Press, Iowa, pp. 265-268.

Soil Classification Working Group (1991) Soil Classification. A Taxonomic System for South Africa. Memoirs on the Agricultural Natural Resources of South Africa No. 15. Department of Agricultural Development, Pretoria. 258 pp.

Stubbings, J.A. and Schonau, A.P.G. (1980) Management of short rotation coppice crops of Eucalyptus grandis Hill ex Maiden. Southern African Forestry Journal 115, 38-46.

Taylor, J.S., Blake, T.J. and Pharis, R.P. (1982) The role of plant hormones and carbohydrates in the growth and survival of coppiced Eucalyptus seedlings. Physiologia Plantarum 55, 421-430.

Tschaplinski, T.J. and Blake, T.J. (1989) Photosynthetic reinvigoration of leaves following shoot decapitation Decapitation
See also Headlessness.

Antoinette, Marie

(1755–1793) queen of France beheaded by revolutionists. [Fr. Hist.: NCE, 1697]

Argos

lulled to sleep and beheaded by Hermes. [Gk. Myth.
 and accelerated growth of coppice shoots. Physiologia Plantarum 75, 157-165.

Keith M. Little and Ben du Toit

Institute for Commercial Forestry Research, PO Box 100281, Scottsville, Pietermaritzburg 3209, South Africa. Email: keith@icfr.unp.ac.za
Table 1. Coppice management treatments implemented
on Eucalyptus grandis in Zululand, South Africa

              Height of
              coppice when    Silvicultural input + method of
Treat. No.    reduced (1)     secondary coppice regrowth control

1 (control)   4 m + 8 m      Manual removal of secondary coppice
                               regrowth when 0.75 m high
2             1.5 m + 8 m    Manual removal of secondary coppice
                               regrowth when 0.75 m high
3             4 m + 8 m      Secondary coppice regrowth sprayed
                               with glyphosate CP 0.6% when 0.75
                               m high
4             4 m + 8 m      Secondary coppice regrowth sprayed
                               with paraquat CP 0.4% when 0.75 m
                               high
5             4 m + 8 m      Broadcast application of 321 kg
                               [ha.sup.-1] of fertiliser as
                               4:1:1 (N:P:K)
                             This equates to 94 kg N [ha.sup.-1],
                               23 kg P [ha.sup.-1] and 23 kg K
                               [ha.sup.-1]
                             Manual removal of secondary coppice
                               regrowth when 0.75 m high
6             4 m + 8 m      Chemical control of all vegetation
                               with glyphosate CP 4 L [ha.sup.-1]
                             Manual removal of secondary coppice
                               regrowth when 0.75 m high

(1) The coppice was reduced in a stepwise manner: the first reduction
(when 1.5 or 4 m high) was to two stems per stump and the second
(when 8 m high) to the original stocking.

Table 2. The initiation and timing of events
for the various coppice management treatments

Treatments        Date of event
affected (1)      (months after felling)    Action taken

                  June 1992                 Trees felled

2                 October 1992 (4 mo)       1st coppice reduction
                                            to 2 stems per stump

1, 3, 4, 5 and 6  January 1993 (7 mo)       1st coppice reduction
                                            to 2 stems per stump

5                 January 1993 (7 mo)       Broadcast application of
                                            fertiliser to the inner
                                            6 x 5 trees

All treatments    February 1994 (20 mo)     2nd coppice reduction to
                                            original stems [ha.sup.-1]

6                 January + April 1993;     Complete weed control
                  March 1994 (7, 10         through the broadcast
                  and 21 mo)                application of glyphosate

1, 2, 5 and 6     February, June, October   Secondary coppice
                  1993; March 1994 (8, 12,  regrowth manually
                  16 and 21 mo)             removed when 0.75 m high

3                 February and June 1993    Secondary coppice regrowth
                  (8 and 12 mo)             sprayed with glyphosate
                                            when 0.75 m high

4                 February, June, October   Secondary coppice regrowth
                  1993; March 1994 (8, 12,  sprayed with paraquat when
                  16 and 21 mo)             0.75 m high

All treatments    June 2000 (96 mo/8 y)     Last measurement before
                                            trees felled

(1) Refer to Table 1 for treatment description.

Table 3. Summary of data when the trees were felled at 8 y of age

Data                                   Initial       Final stocking
                                       stocking          (stems
                                       (stumps        [ha.sup.-1])
                                     [ha.sup.-1])

Grand mean                          885              1140
Unit coefficient of variation (%)    15.6              18.4
Standard error of the difference     69               105
Bartlett's Test for homogeneity       0.849 (ns)        0.235 (ns)
of variance (P < 0.05)

Data                                  Basal area      Merchantable
                                      ([m.sup.2]         volume
                                     [ha.sup.-1])      ([m.sup.3]
                                                      [ha.sup.-1])

Grand mean                          30               276.3
Unit coefficient of variation (%)   19.5              20.9
Standard error of the difference     2.9              28.9
Bartlett's Test for homogeneity      0.706 (ns)        0.784 (ns)
of variance (P < 0.05)

Note: ns denotes non-significance at P < 0.05.
COPYRIGHT 2003 Institute of Foresters of Australia
No portion of this article can be reproduced without the express written permission from the copyright holder.
Copyright 2003 Gale, Cengage Learning. All rights reserved.

 Reader Opinion

Title:

Comment:



 

Article Details
Printer friendly Cite/link Email Feedback
Author:Little, Keith M.; du Toit, Ben
Publication:Australian Forestry
Article Type:Report
Geographic Code:6SOUT
Date:Jun 1, 2003
Words:3487
Previous Article:Efficacy of atrazine and simazine applications over harvest residue in Queensland's subtropical softwood plantations.
Next Article:Mycosphaerella leaf disease reduces growth of plantation-grown Eucalyptus globulus.
Topics:



Related Articles
Effect of seedling characteristics at planting on browsing of Eucalyptus globules by rabbits.
Effects of thinning and coppice control on stand productivity and structure in a silvertop ash (Eucalyptus sieberi L.Johnson) forest.
Population differentiation within Eucalyptus obliqua: implications for regeneration success and genetic conservation in production forests.
Post-wildfire seedling colonisation patterns in a Eucalyptus delegatensis (Myrtaceae) windthrow site at Snowy River National Park, Victoria.
Physical and nutritional characteristics and performance after planting of Eucalyptus globulus Labill. seedlings from ten nurseries: implications for...
Mammalian browsing in the Mt Cole State Forest: defining a critical browsing level and assessing the effect of multiple browsing events.
Seed fall and flowering in white box (Eucalyptus albens Benth.) trees near Cowra, New South Wales.
Achievements in forest tree genetic improvement in Australia and New Zealand 3: tree improvement of Eucalyptus dunnii Maiden.
Feeding preferences of the Christmas beetle Anoplognathus chloropyrus (Coleoptera: Scarabaeidae) and four paropsine species (Coleoptera:...
Impact of repeated defoliation on jarrah (Eucalyptus marginata) saplings.

Terms of use | Copyright © 2014 Farlex, Inc. | Feedback | For webmasters