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Spatial and functional niche overlap between invasive Ligustrum lucidum and native woody species in an urban shrine forest in Japan

Ishii, H. Roaki Hara, Chinatsu Kashiwagi, Keita Okabe, Momoko Noguchi, Yuiko Hirobe, Muneto 神戸大学

2022.01

概要

Preventing invasion of exotic species into urban forests is important for sustaining native species diversity. In Japan, Ligustrum lucidum, an invasive tree, has become widespread in urban areas. Here, we investigated the spread of L. lucidum in a semi-natural, urban shrine forest to infer which native species' preferred habitats may be affected. L. lucidum was most abundant near the artificially created forest edge where canopy trees are pruned regularly. Spatial distribution of L. lucidum overlapped with those of two native species (Cinnamomum japonicum, Quercus glauca), but was segregated from the other three native species. We also compared leaf functional traits between L. lucidum and the native species to infer functional niche overlap. L. lucidum exhibited greater plasticity of leaf functional traits compared to native species and its leaf functional traits were similar with Ci. japonicum, Ilex rotunda and Q. glauca, but not with Camelia japonica and Ternstroemia gymnanthera. Our results suggest that, currently, the preferred habitat and realized functional niche of L. lucidum overlaps with those of Ci. japonicum and Q. glauca. High plasticity of leaf functional traits contributing to shade tolerance may allow L. lucidum to expand its spatial distribution in this forest, affecting other native species in the future. Our results emphasize the importance of removing invasive species during early stages of invasion while their distribution is still relatively confined and negative effects on native species are limited.

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参考文献

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Table 1. Sizes and light environments of the sample trees (n = 5~6 for each species) and total

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number of individuals in the research plot and for each species. Species are listed in order of

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increasing distance of spatial distribution from forest edge (Fig. 3).

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Species

DBH (cm)

Height (m)

Canopy openness (%)

Total individuals

L. lucidum

4.13~7.83

4.43~9.04

5.4~26.4

58

Ci. japonicum

2.76~5.90

3.09~10.05

6.48~21.41

84

Q. glauca

2.45~6.78

3.30~10.66

5.51~17.12

166

T. gymnanthera

3.03~8.42

3.96~10.12

4.95~14.48

112

Ca. japonica

3.79~9.01

4.05~10.52

6.30~18.51

206

I. rotunda

2.31~6.23

3.43~10.15

6.88~24.15

55

All measurements were taken in 2019.

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Table 2. Leaf functional traits (mean ± one standard error) of the study species.

Species

Thickness (mm)

LMA (g m-2)

Amax (µmol m-2 s-1)

Nmass (%)

L. lucidum

0.34 ± 0.01 bc

103.4 ± 3.9 b

8.58 ± 0.57 a

2.89 ± 0.09 a

Ci. japonicum

0.24 ±0.01 d

102.8 ± 4.5 b

4.76 ± 0.67 b

2.00 ± 0.11 b

Q. glauca

0.33 ± 0.01 c

101.9 ± 4.0 b

6.00 ± 0.61 b

1.97 ± 0.09 b

T. gymnanthera

0.45 ± 0.01 a

112.8 ± 4.7 ab

6.61 ± 0.72 b

1.12 ± 0.11 c

Ca. japonica

0.39 ± 0.01 b

125.4 ± 4.0 a

4.14 ± 0.58 b

1.35 ± 0.10 c

I. rotunda

0.26 ± 0.01 d

67.2 ± 4.9 c

8.85 ± 0.70 a

2.09 ± 0.12 b

Means with the same letter are not significantly different (ANOVA, P < 0.05)

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Figure captions

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Fig. 1. Aerial view and map of Nishinomiya Shrine in southeastern Hyogo Prefecture, Japan. The

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evergreen broadleaved forest is located on the north and west sides of the shrine grounds. A 0.65 ha

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contiguous research plot was established comprising 65 sub-plots (10 × 10 m). Of these tree locations

367

were mapped for the 40 × 100 m area (filled squares).

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Fig. 2. Stem map (all trees taller than 1.3 m) of the 40 × 100 m area of the shrine forest.

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Fig. 3. Box-whisker plot of the distance of individual trees of each species from the intensively

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managed, western forest edge. Box length is the inter-quartile range. Lines and X inside boxes

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represent median and mean distances, respectively. Bars represent 10 and 90 percentiles. Circles are

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trees outside this range. Species are listed in order of increasing mean distance from forest edge.

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Letter indicate significantly different means (P < 0.05, ANOVA and Tukey’s HSD).

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Fig.4. Spatial distribution pattern of each species in the shrine forest (solid lines). The horizontal line

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indicates g(r) = 1. Dotted lines indicate 95% confidence interval for null hypothesis of for Poisson

379

random distribution. Positive and negative deviations outside the confidence intervals indicate

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clustered and regular distribution patterns, respectively. Species order follows that of Fig. 3.

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Fig. 5. Spatial distribution pattern of L. lucidum in relation to each of the five native species (solid

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lines). Dotted lines indicate 95% confidence interval for null hypothesis of for Poisson random

384

distribution. Positive and negative deviations outside the confidence intervals indicate sympatric and

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exclusive distribution patterns, respectively. Species order follows that of Fig. 3.

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Fig. 6. Leaf traits in relation to canopy openness for L. lucidum and five native species. Data points

388

for Nmass, LMA and thickness are the mean of five leaves at each sampling position, while Amax is the

389

mean of ten measurements taken at light saturation for one leaf. All standard errors were less than 3%.

390

Lines indicate significant regressions (P < 0.05).

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Fig.7. Results of principle component analysis of leaf functional traits of L. lucidum and the five

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native species. Arrows indicate correlation vectors showing correlation coefficients of each trait in

394

relation to PC1 and PC2.

19

Road

Figure

Shrine grounds

10m

10m

Houses

Fig. 1

X L. lucidum

□ Ci. japonicum

◊ Q. glauca

+ T. gymnanthera

Δ Ca. japonica

○ I. rotunda

Distance (m)

X Others

Distance (m)

Fig. 2

Distance from forest edge (m)

L. lucidum

Ca. japonica

Q. glauca

Ci. japonicum T. gymnanthera

I. rotunda

Fig. 3

L. lucidum

10

Ci. japonicum

yabuni

tou

10

Q. glauca

g(r)

T. gymnanthera

ara

mokk

10

Ca. japonica

I. rotunda

kuro

tsuba

10

r (m)

10

Fig. 4

Ci. japonicum

-1 0

10

-2

-3

L(r)

Q. glauca

-1 0

10

-1 0

-2

-2

-3

-3

Ca. japonica

-1 0

T. gymnanthera

10

I. rotunda

10

-1 0

-2

-2

-3

-3

r (m)

10

Fig. 5

X L. lucidum

□ Ci. japonicum

◊ Q. glauca

+ T. gymnanthera

0.4

LMA (g m2)

Leaf thickness (mm)

○ I. rotunda

200

0.6

0.2

100

16

10

20

Canopy openness (%)

30

12

10

20

30

Canopy openness (%)

Nmass (%)

Amax (µmol m-2 s-2)

Δ Ca. japonica

10

20

Canopy openness (%)

30

10

20

Canopy openness (%)

30

Fig. 6

PC 2

I. rotuna

L. lucidum

T. gymnanthera

Q. glauca

Amax

Thickness

Nmass

-4

-3

-2

-1

PC 1

LMA

-1

Ca. japonica

-2

Ci. japonicum

-3

-4

Fig. 7

...

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