# Review of Plant Species Diversity in Managed Forests in Japan

Authors: Takuo Nagaike
Journal: ISRN Forestry
 (2012)

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## Abstract

The effects of conifer plantation management and forest fragmentation on plant species diversity in Japan were reviewed. While most studies have demonstrated that the practice of thinning in coniferous plantations can enhance species diversity of naturally regenerated trees, such as broad-leaved trees, some have shown that thinning reduces plant species diversity through the direct physical disturbance to forests. In addition, plant species diversity in plantations has also been shown to be dependent on the distance from seed sources. Extensive forest fragmentation due to land use changes has occurred, particularly in forests near urban and suburban areas. Although the number of species per unit area in abandoned coppice forests is not clearly related to the extent of forest fragmentation, most species attributes (such as rare species) are negatively influenced by forest fragmentation. Some of the forests owned by shrines and temples in urban areas are similar to island forests and are relatively well protected from human disturbance. To more clearly understand and evaluate changes in biodiversity through forest management, elucidating the interactions between management and plant species diversity, species composition, and the ecological traits of various species is therefore necessary.


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## Body

## 1. Introduction

Forest management typically has a marked affect on plant species diversity, which is an important ecological indicator (e.g., [1]). Understanding the effects of forest management practices on plant species diversity is important for achieving ecologically sustainable forest management [2]. Most of the forests that cover Japan’s surface are managed; these include plantations, coppices, and selection or selectively cut forests [3]. The plant species diversity of these managed forests is thus important for maintaining, conserving, and restoring biodiversity in Japan. Globally, forest management policy has changed in response to changes in public awareness of the multiple functions of forests [4]. In Japan, studies of plant species diversity in the managed forests of the country have increased markedly since 2000 [5, 6].Species diversity is an important index in community ecology (e.g., [7]). Although species richness and diversity are useful indicators of the effects of forest management practices, species diversity per se is also important in biodiversity. For example, forest stands with relatively higher species richness or diversity are not always much better for biodiversity, as undesirable species (e.g., invasive or exotic species), which frequently comprise a high proportion of early successional species [8, 9], can contribute toward a marked increase in diversity [10–12]. A comprehensive understanding of plant species diversity, species composition, and the ecological traits of species (i.e., plant functional types [13]) is thus considered necessary in order to understand and evaluate the quality of biodiversity ([3, 6], but see [14]).This paper reviewed studies on plant species diversity and species composition within the context of forest management (i.e., plantations and forest fragmentation) that have been published, primarily in Japan, over the past 20 years. Since some of these studies have only been published in Japanese (with English summaries), much of the information they contain cannot be accessed by the international audience. The primary aim of this study was therefore to introduce these papers to the international audience.


## 2. Studies on Plant Species Diversity and Species Richness in Plantations

Plantations account for approximately 40% of Japanese forests (66% of land area). The most extensively planted species in Japan are the indigenous evergreen conifersCryptomeria japonica (Japanese ceder, 4.5 million ha, 43% of area under plantation) and Chamaecyparis obtusa (Hinoki cypress, 2.6 million ha, 26% of area under plantation). Since the function of plantations has changed from being single purpose (i.e., timber production) to multipurpose (e.g., habitats for wild animals and plants), studies of plant species diversity [15, 16] as well as ecosystem services and goods [17] provided by plantations have increased markedly (Table 1). In a meta-analysis of plant species richness in plantations compared to other land cover types (e.g., primary and secondary forest), Bremer and Farley [15] showed that plantations were more likely to contribute to biodiversity when established in degraded lands than when they replaced natural forest, grassland, and shrubland ecosystems. The reduction of plant species diversity in exotic plantations [12] and the invasion of exotic species into natural forests [18, 19] are issues that need to be considered in plantation management.Table 1
Effects of management regime on plant species richness and diversity in plantations in Japan.
Management regime
Change in plant species richness or diversity
Increasing
No change
Decreasing
Line cutting
Sakuta et al. [25]
Ito et al. [26]
Yamagawa et al. [27]
Hanada et al. [30]
Thinning
Ishii et al. [31]
Nagai and Yoshida [33]
Hirata et al. [32]
Rotation frequency
Hino and Hiura [36]
Age
Ito et al. [43]
Nagaike et al. [50]
Nagaike et al. [48]
Distance from seed sources
Gonzales and Nakashizuka [54]  (seedling)
Takahashi and Kamitani [51]Gonzales and Nakashizuka [54]  (saplings)
Utsugi et al. [55]  (seedlings and saplings in unthinned, seed fall and seed bank in thinned)
Utsugi et al. [55]  (seedlings and saplings in thinned)The trees in plantations should be harvested when they attain a size that is suitable for timber. To maximize the economic efficiency of timber harvesting in plantations, the final cut is usually a clearcut [20]. Among final cutting practices, clearcutting has the biggest effect on microclimate (i.e., soil and air temperature, humidity, and light intensity) and consequently plant species diversity [21]. For example, the diversity of forest floor plants in a subtropical forest in southern Japan did not recover well after the forest was clearcut [22, 23]. Similarly, the species composition of most plantations and coppice forests in the cool-temperate zone in central Japan that were clearcut at least once, did not revert to primary forest conditions after management was abandoned [24]. As a consequence, alternative methods of clearcutting, line cutting, or strip cutting have been introduced in Japan [25]. However, in C. japonica and C. obtusa plantations in southern Japan, species diversity (Shannon’s H′) in the cut strips was similar to that in the clearcut plantation [26]. To find a way of combining effective timber production with effective management of species diversity, Yamagawa et al. [27] clarified the effects of small-scale clearcutting and suggested that managing different-aged stands using an optimal spatiotemporal arrangement of patches was well suited to maintaining the various understory types, and that such an approach could be used to maximize species diversity through effective patch management.Tending plantations (e.g., weeding and thinning) is necessary for producing high-quality timber. Appropriate tending, particularly thinning, has been lacking in Japanese plantations because of the lack of economic incentives for forest owners to do so [24]. Since a lack of thinning creates a very dark understory with sparse vegetation, the risk of soil erosion is enhanced [4, 28]. As a result, studies on the effects of thinning on restoring or rehabilitating plant species diversity are increasing. These studies have shown that thinning enhanced the species richness of broad-leaved trees in plantations of Abiessachalinensis [29] and Larixkaempferi [30] in northern Japan, and in C. japonica plantations in western [31] and central [32] Japan. However, Nagai and Yoshida [33] showed that thinning of Piceaglehnii plantations in northern Japan reduced plant species diversity because of the direct effect of physical disturbance associated with the activity. Line thinning in C. japonica plantations in central Japan contributed little toward the regeneration of hardwood species [32], and thinning intensity increased understory species diversity in Larixleptolepis plantations four years after thinning in central South Korea [34].To avoid converting natural forests into plantations, the practice of planting a second (or more) rotation crop in plantations is increasing [35]. Since this practice will increase the area of second or multiple-rotation plantations, it is important to understand whether such practices could potentially decrease plant species diversity or future plantation productivity, either directly or indirectly. In a study of species diversity and above-ground productivity of understory plants in plantations, Hino and Hiura [36] showed that the Simpson index decreased as the rotation frequency of plantations increased, with the effects of disturbance on species diversity persisting for 20–80 years in a cool-temperate forest in northern Japan. In a loblolly pine (Pinus taeda) plantation in the USA, Jeffries et al. [9] showed overall similarities in the herbaceous layer from year 22 of the second rotation to year 18 of the third rotation, however, these authors were unable to clarify whether species diversity increases, decreases, or remains constant over multiple rotations.Stand age is a key attribute of plantations because it directly affects the quantity and log size of timber produced, as well as the cutting rotation employed in a landscape. In Japan, long-rotation management is becoming increasingly widespread as it results in the production of larger and more valuable timber and is a way of hedging against fluctuations in the price of timber [37, 38]. Long-rotation plantations have been observed to maintain and increase species diversity and develop stand structure better than standard-rotation plantations [39, 40]. An aged C. japonica plantation was observed to develop a multilayered structure, with planted trees constituting the upper layer and broad-leaved trees forming the lower layers [41]. Plant community composition and diversity is significantly related to vertical stand structure, and the development of stand structure has been shown to contribute toward increasing the diversity of plant species in mature and old-growth stands [42]. Stand age has also been shown to be positively correlated to plant species diversity in C. japonica plantations in southern Japan [43] and Picea plantations in Canada [44]. Ramovs and Roberts [45] identified a gradient in cover of forest-habitat species which ranged from being lowest in old-field plantations, intermediate in cut-over plantations and young, naturally regenerated stands, and highest in mature, naturally regenerated stands. Nagaike [46] showed that the species diversity of snags (standing dead trees), which are an important structural attribute of forest ecosystem diversity [1, 47], was positively correlated to stand age in L. kaempferi plantations, supporting the positive correlation between tree species diversity and species richness with stand age [48]. Conversely, in the herb layer of the study plots examined by Nagaike et al. [48], plant species diversity was not correlated with stand age, but the attributes of some species (e.g., weed species) were negatively correlated with stand age and the occurrence frequency of species. Conversely, bird-dispersed seeds were positively correlated with stand age [49, 50].Within the context of ecological restoration, the spatial configuration of stands, particularly the range of seed dispersal by species used in restoration, is considered to be particularly important. Consequently, the relationship between the extent of colonization by plant species in plantations and the distance from seed sources has also been extensively studied in Japan [51] and elsewhere (e.g., [52, 53]). Gonzales and Nakashizuka [54] demonstrated that although there were no marked or general trends in the frequency and species diversity (Shannon’s index) of saplings of naturally regenerated broad-leaved species in relation to distance from old-growth forest in C. japonica plantations in central Japan, the frequency and species richness of seedlings decreased as distance from the old growth forest increased. Utsugi et al. [55] clarified the interactive effects of distance from hardwood forests and thinning on species diversity and abundance of hardwoods in C. japonica plantations in northern Japan and showed that the interactive effects did not decrease the diversity of seedlings and saplings, probably due to distance-independent improvements in environmental conditions resulting from thinning. However, most of these studies were only conducted at the stand level; these effects need to be examined at the landscape level to more accurately reflect the practical management conditions of forested landscapes. Soil seed banks can also contribute to the recovery of vegetation after clearcutting or thinning plantations. For example, high red: far-red light ratios and/or the large temperature fluctuations associated with thinning in C. japonica plantations markedly increased seed germination in the understory [56]. However, since the number of late-successional species in the soil seed bank of C. obtusa plantations is low in southwestern Japan, their contribution to the recovery of natural vegetation was also low [57].


## 3. Effects of Forest Fragmentation on Plant Species Diversity

The effects of forest fragmentation on plant species diversity and richness are a major research topic in conservation biology and forest management (e.g., [58–60]). In Japan, forest fragmentation, resulting from land use change, has been severe, particularly in areas adjacent to urban and suburban areas. In abandoned coppice forests in central Japan, several studies have shown that the number of species per unit area is not clearly related to the extent of forest fragmentation [61–63]. Although forest fragmentation does not decrease overall species richness, some species (e.g., rare species) have been shown to be particularly sensitive to habitat fragmentation [61, 62]. For example, the number of species with distributions that were biased toward primeval and natural forests was positively correlated with the patch area of these primeval and natural forests [63]. Ishida et al. [64] showed that, compared to secondary forests, the number of species with distributions that tended toward primeval and natural forests was strongly and positively correlated with forest patch area for these two forest types, implying that forest fragmentation decreases species richness in lucidophyllous forests in western Japan. In a subtropical forest in southern Japan, recovery from clear-cutting was greater in stands surrounded by mature forest than in isolated stands or stands surrounded by immature forest [65].Some of the forests, owned by shrines and temples in urban areas, have survived as forest islands and are relatively well protected from human disturbance. In a study to clarify the relationship between the lucidophyllous plant diversity and area of these fragmented forests, a strong positive correlation was found between the number of species and species that were generally more common in smaller forests [66]. Tamura and Shimano [67] concluded that shrine forests, consisting of cool-temperate species, play an important role as habitats for a variety of native plants (e.g., forest-interior species) in city environments in central Japan. Using umbrella species selected by a focal species approach, Murakami et al. [68] presented planning guidelines for conserving tree species, by selecting the umbrella species, using “focal species approach,” in fragmented shrine forests. In this way, such urban forests could contribute to maintaining plant species diversity in highly altered forested landscapes.Traditionally, coppice forests in Japan were continuously managed for charcoal and firewood production [69]. However, the management of these coppice forests ceased after the advent of fossil fuels such as gas and oil, resulting in these areas becoming increasingly fragmented by conversion to other land use. Matsumura et al. [70] reported that, while the cover of evergreen species (including summer-green species) and species in the herb layer of abandoned coppice forests in western Japan increased after coppice management ceased, both were negatively correlated with overall species abundance in all forest layers.Dwarf bamboo in the understory markedly affects plant species diversity and tree regeneration (e.g., [71]) as well as forest fragmentation and management. Tomimatsu et al. [72] showed that Sasa chartacea was more abundant in smaller forest fragments and also that the species richness of forest herbs was strongly and negatively related to S. chartacea density. Indeed, variations in species richness could, more clearly, be attributed to S. chartacea density than to the distance from the nearest forest edge. Forest floor plant diversity was low in areas where Pleioblastus chino, another species of dwarf bamboo, was well established [61]. Since species richness of summer-green perennials was low where coppicing management practices had been interrupted for extended periods [73], traditional continuous management practices are considered to have maintained species richness. However, since the economic incentives for such management methods have been lost, ensuring that they will continue to be applied will be difficult. As an alternative, numerous urban residents have been encouraged to volunteer their services to manage areas in order to maintain plant diversity [74].


## 4. Future Research Directions

Since plant species diversity is known to be markedly affected by spatial scale, sampling procedures should consider the appropriate scale at which to examine plant species diversity within the context of the specific objectives of the study [11]. Moreover, while an increase in biological diversity has been observed in mixed-species production stands, no such increase exists in coniferous monocultures [75]. To accurately assess the multifunctional roles of forests, the important relationship between productivity and species diversity should therefore be examined further. Consequently, this relationship is currently being carefully elucidated in experimental mixed plantations (e.g., [76, 77]). Jobidon et al. [78] showed that the variation in species diversity along the gradient of hardwood abundance in a Picea mariana plantation in Canada had a “hump” shape, which is considered characteristic of the classic disturbance-diversity hypothesis. However, the intensity of previous vegetation control measures was weakly predictive of plant species diversity. Forest managers should therefore consider the long-term effects of management history in order to maintain the plant diversity of the forest understory [36, 79]. Also, plant species diversity and composition would play an important role for ecological function and services. Such kind of studies in managed forest is strongly necessary [17, 80].



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