Growth and provenance of Norway maple (Acer platanoides) in lowland Britain

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Growth and provenance of Norway
 maple (Acer platanoides) in lowland
 Britain
GARY KERR1 AND JOHN NILES2
1
    Forestry Commission Research Agency, Alice Holt Lodge, Wrecclesham, Farnham, Surrey, GU10 4LH,
    England

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2
    Believer, May Road,.Turvey, Bedford, MK43 8DT, England

Summary
The results of an experiment to investigate the early growth and form of ten different prove-
nances of Norway maple (Acer platanoides L.) are described. Two sites were planted and after 8
years survival was 88 per cent and 95 per cent and height increment was 402 cm and 201 cm;
confirming the potential of Norway maple to be a productive forest tree. Provenances that per-
formed well were from Germany, the Netherlands, Denmark and Yugoslavia; exact locations
were not known for all seed collections. A provenance from Russia was included, material from
this far east has rarely been tested in Britain. However, as expected, its performance was rela-
tively poor. The main constraint to further planting of Norway maple is the palatability of the
bark to grey squirrels (Sciurus carolinensis Gmelin.). However, it is a useful tree for high pH and
heavy soils and as an alternative species to sycamore (Acer pseudoplatanus L.).

                                                        The earliest cultivation of Norway maple in
Norway maple (Acer platanoides L.) is the most       Britain was probably at Edinburgh Botanic
widespread native maple in Europe (Santamour         Garden when George Sutherland included
and McArdle, 1982) ranging from southern             Norway maple 'Laciniatum' in his Hortius
Scandinavia and the Ural Mountains south-            Medicus Edinburgensis of 1683 (Hadfield,
wards over the greater part of Europe (not west-     1957). The date of its arrival is therefore usually
ern France or the British Isles) to northern         quoted as 'pre 1683' as in Mitchell (1981).
Spain, northern Italy and Greece, extending into     Because of its vigorous early growth, desirable
the Caucasus Mountains, Asia Minor and               form and size, capacity to tolerate urban
northern Iran (Figure 1). Its natural range is       impacts, the fact that it transplants well and
similar to that of sycamore (Acer pseudopla-         grows on a variety of soils, and withstands ice
tanus L.), the notable difference being that the     and snow damage better than other maples, it
natural range of sycamore does not extend as         has become a popular urban tree in Britain and
far north. The two species are very similar in       North America (Nowak and Rowntree, 1990).
their silvicultural characteristics.                 Many of these species characteristics would
C Institute of Chartered Foresters, 1998                                            Forestry, Vol. 71, No. 3 , 1998
220                                           FORESTRY

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                               Figure \. Native range of Acer platanotdes.

indicate a wider use in Britain but sycamore has     very tolerant of exposure and calcareous soils
been much preferred. In the Census of                (Moffat and McNeil, 1994). The ability to tol-
Woodlands and Trees 1979—82, sycamore was            erate high pH led Kerr and Evans (1993) to rec-
reported to be a major forest species covering       ommend that it is one of a small number of
49426 ha but Norway maple, although recorded         species meriting wider consideration for chalk
as a separate species was not reported on indi-      downland planting.
vidually (Locke, 1987). In Forestry Commission          Evans (1984) rates Norway maple as having
woodlands sycamore forms 1560 ha whereas             considerable potential as a forest tree in Britain,
Norway maple is recorded in a mere 65 ha (J.         suggesting that in 30—40 years it can reach 18—22
Gilbert, personal communication); although           m in height and, if thinned correctly, achieve a
these figures do not include its presence in         stem diameter of 40 cm in 40 years. This view is
mixed woodland.                                      well supported by the few published studies in
   The optimum sites for Norway maple are            Britain that have included Norway maple.
deep, fertile, moist soils which are adequately      Williamson et al. (1992) describe an experiment
drained and have a pH in the range 5.5-6.5.          on thin (30 cm) silty loam soil of pH 7.9 over
Evans (1984) states it is probably less demand-      chalk in which Norway maple grew over 1 m in
ing than sycamore regarding soil fertility and       the first 2 years. Willoughby {personal commu-
also appears to be able to tolerate drier soils.     nication) reported that after 4 years the same
These tolerances have made the species one that      trees were 3.4 m tall with maintenance of 100
can be recommended for planting on disturbed         per cent weed-free conditions. Good growth has
land. It is intolerant of acidic soils, moderately   also been reported by Buckley et al. (1981). The
tolerant of air pollution and heavy soils, and       timber of Norway maple is similar to sycamore
GROWTH AND PROVENANCE OF NORWAY MAPLE IN LOWLAND BRITAIN                                             221

in colour, grain and texture but is marginally             Randomized block experiments were established
harder and heavier (Brazier, 1990). Therefore              at two sites, Hatch and Centenary Wood in
there is a strong body of evidence to suggest that         Bedfordshire. At Hatch there were two blocks
it could be a major forest tree. However, the              and each of the 10 provenance plots contained
Achilles' heel of the species, in common with              16 trees, and at Centenary Wood there were
sycamore, is that the bark is very attractive to           four blocks and each plot contained 25 trees.
grey squirrels (Sciurus carolinensis Gmelin.).             The trees were planted in February 1989 at 2 X
Although effective methods of grey squirrel con-           2 m spacing. The heights of a random sample of
trol exist, the lack of a co-ordinated, consistent         trees were measured from each provenance after
approach to its control means that it is one of            planting and subsequently the height of each
the main problems of producing quality timber              tree planted was measured in February 1992,
from broadleaved woodlands in Britain (Kerr                then annually until April 1997. In addition, in
and Evans, 1993).                                          April 1997, the length of the longest branch was
   There is little, if any, published information          measured to enable form to be compared.
on the effects of provenance on the growth and                The Hatch site (NGR TL159481) is flat, lying

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early form of Norway maple in Britain. The                 at 25 m a.s.l. and sheltered by a large hedge on
main purpose of this paper is to describe the              the east side. The soil is a well drained loam
results of a provenance experiment, planted at             derived from river terrace gravels with a pH
two sites, to investigate the early growth and             6.0-7.8. The Centenary Wood site (NGR
form of 10 provenances of Norway maple.                    TL061348) is a light clay soil (pH 7.4-8.1) devel-
                                                           oped from chalky boulder clay with gently slop-
                                                           ing ground and a southern aspect lying at 75 m
                                                           a.s.l.
Materials and methods                                         All results were subject to analysis of vari-
Ten provenances from five European countries               ance. Survival data were transformed by arcsine
were supplied from four nurseries (Table 1).               before analysis, but actual percentages are

Table 1: Survival, growth and form of 10 provenances of Norway maple

                                                                                            Mean         Mean
                                                                               Mean       length of     height:
                                            Survival (%)         Mean          height      longest      branch
                 Location                                        height      increment     branch       length
                  of seed                        Centenary        (cm)          (cm)        (cm)         ratio*
Country          collection      Codet   Hatch    Wood          Both sites   Both sites   Both sites   Both sites
Germany        8°3
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          1992           1993                           1995           1996           1997
                                            Year assessed

                      Figure 2. Norway maple trials: mean height of trees at Hatch.

presented for clarity. Survival data are shown       with a mean height increment of 402 cm (50.3
for each site separately but height, height incre-   cm a"1) compared with 201 cm at Centenary
ment and form data were combined for both            Wood (25.1 cm a"1). Over both sites, three
sites to improve the precision of the analyses.      provenances HI, H2 and D2, were generally
                                                     taller than the others although only significantly
                                                     (P
GROWTH AND PROVENANCE OF NORWAY MAPLE IN LOWLAND BRITAIN                                  223

branch showed that four provenances (Dl, R,               (1984) could be achieved. Growth has also been
Hu and Y) had short branches, but that only Dl            relatively good at Centenary Wood which has a
and R were significantly shorter (P
224                                           FORESTRY

(HI) and worst (Hu) of these seven provenances        References
would be of some importance if the tree were          Brazier, J.D. 1990 The timbers of farm woodland
being grown commercially. There were few dif-           trees. Forestry Commission Bulletin No 91. HMSO,
ferences in form between provenances except             London, 8pp.
that the shorter provenances also tended to have      Buckley, C.P., Chilton, K.G. and Devonald, V.G.
small branches.                                         1981 The influence of sward control on the estab-
   It is unfortunate that the exact location of all     lishment and early growth of ash (Fraxinus excel-
the seed collections was not recorded as coun-          sior L.) and Norway maple {Acer platanoides L.).
try-wide recommendations for provenance are             J. Environ. Manage. 13, 223-240.
subject to large variation, for example the con-      Evans, J. 1984 Silviculture of broadleaved woodland.
                                                        Forestry Commission Bulletin No 62. HMSO,
trasting performance of Dl and D2, both from
                                                        London, 232pp.
Denmark. These results are also of interest as        Hadfield, M. 1957 British Trees, A Guide for
planting material from as far east as Russia has        Everyman. J.M. Dent, London, 468pp.
rarely been tested in Britain. It would be            Kerr, G. and Evans, J. 1993 Growing broadleaves for
expected to perform poorly and this is                  timber. Forestry Commission Handbook No 9.

                                                                                                             Downloaded from http://forestry.oxfordjournals.org/ by guest on March 23, 2015
confirmed for Norway maple by the poorer sur-           HMSO, London, 95pp.
vival and growth of the Russian provenance.           Locke, G.M.L. 1987 Census of woodlands and trees
However, the experiments reported here demon-           1979-92. Forestry Commission Bulletin No 63.
strate that good growth and form of Norway              HMSO, London, 123pp.
maple can be achieved from a wide range of            Mitchell, A.F. 1981 The native and exotic trees in
                                                        Britain. Arboriculture Research Note 29/81/S1LS.
sources in Europe.
                                                        AAIS, Farnham, Surrey, 4pp.
                                                      Moffat, A. and McNeil, J. 1994 Reclaiming disturbed
Acknowledgements                                        land for forestry. Forestry Commission Bulletin No
                                                        110. HMSO, London, 103pp.
The authors would like to thank Bedfordshire County   Nowak, D.J. and Rowntree, R.A. 1990 History and
Council who established and maintained the experi-      range of Norway maple. / . Arboric. 16, 291-296.
ments and Pamela Stephenson for help with assess-     Santamour, F.S. and McArdle, A.J. 1982 Checklist of
ments. Dave West and staff of the Forestry              cultivated maples III. Acer platanoides L. J.
Commission Research Agency's Technical Support          Arboric. 8, 241-246.
Unit carried out the final assessment and Tracy       Williamson,     D.R.,     McDonald,      H.G. and
Houston and Juliet Streeter analysed the data.          Nowakowski, M.R. 1992 Vegetation management
                                                        during the establishment of farm woodlands.
                                                        Aspects Appl. Biol. 29, 203-210.

                                                      Received 23 September 1997
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