Environmental Management Journal
Band 339,
1. August 2023
, 117892
Author links open the overlay panel, , , , , ,
Abstract
Mountain landscapes are very heterogeneous due to topography, particularly location along slopes and slope forms that control ecosystem mechanisms. We hypothesize that tree dieback is driven by topography, selecting productive and less diverse communities on the lower slopes and more diverse and stress-resistant communities on the upper slopes. Understanding how this heterogeneity affects vegetation patterns should provide benchmarks for managing the montane forest ecosystems they dominatewhite oak. Timber communities were sampledagainstkonkave Topography (d. h. Gratagainsttalweg) and with measurements of the severity of tree dieback, environmental variables (depth of leaf litter, soil composition, rocky outcrop), stand structure (canopy cover, mistletoe infestation, tree diameter and height, differentiation of diameter and height, number of oaks). from shoot groups or seed origin) and biodiversity. Tilt position was the most important determinant affecting all variables except uniformity. Dieback severity was higher on the slopes and hilltops and lower on the lower slopes, where the trees were more productive: taller, larger, more homogeneous, and largely seed-derived.ChainShape affected diversity and dieback severity, both of which were higher in valley trails, but had no impact on environmental variables and little on stand structure. The results show that the greatest variety ofwoody plantsFound on upper slopes, they support a community resilient to stress associated with increased dieback and infection from mistletoe, likely because frugivating birds are attracted to the fruit of the shrubs. Management of semi-arid forests should take into account the ecosystem heterogeneity of the formed slopes by preserving ridges that are most vulnerable to tree dieback and naturally supporting biodiversity. Remediation measures on the lower fertile slopes could be implemented by planting oak trees or seedlings under shrub canopies to counteract the effects of dieback and environmental stress. In addition, at lower altitudes, forest management measures to convert coppice forests to tall oak forests can be undertaken to potentially consider moderate silviculture.
introduction
In mountains, forest structure and diversity are determined by microscale factors such as slope, orientation, elevation, bedrock or moisture (Kovács et al., 2017; Luo et al., 2019; Michalet et al., 2021; Woldu et al., 2020; Deák et al., 2021; Carcaillet et al., 2022). Understanding these natural patterns and the mechanisms involved provides valuable benchmarks for ecosystem management, which aims to reduce the gap between natural and managed landscapes to ensure the long-term preservation of ecosystem functions and thus the preservation of socio-economic benefits (Führer, 2000; Gauthier et al., 2009; Heckwolf et al., 2021). This is useful given that global montane forest decline, such as tree dieback or biodiversity erosion, is leading to degradation of ecosystem services (Foley et al., 2007; Laigle et al., 2021; Kaushal et al ., 2021).
The phenomenon of tree death manifests itself in reduced growth and reduced vitality and ultimately in a higher mortality rate. Tree diebacks vary in severity, particularly in temperate and Mediterranean forests, and are altering community composition and ecosystem functions (Ogaya et al., 2020; Puchi et al., 2021; Sánchez-Moreno and Yuste, 2022). Tree dieback has increased in drought-prone areas in recent decades (Gazol et al., 2020). There are now a million hectares of Zagros forests with the landmarkwhite oakLindl. (Brant oak) has been declining in semi-arid areas of western Iran (Shiravand and Hosseini, 2020; Ghanbari Motlagh et al., 2020), while the factors driving this die-off crisis and reducing ecosystem values remain a knowledge gap.
Probably this affects the dying of trees, the location on the slope seems to be decisive due to trophic processes on the mountain. A series of different locations along a slope and successive surface roughnesses is referred to as a "catena" (Wells et al., 2018; Fayyadh et al., 2021). A catena modulates spatial biotic patterns by controlling its surroundings and environmental responses (Fazlollahi Mohammadi et al., 2022). Along the slope, landscape heterogeneity may be caused by microscale variability in soil quality and moisture, which is partly controlled by altitude. at higher altitude, lower temperature, higher humidity and shallower soil depth (see also López-Marcos et al., 2020). These variations can be crucial for plant structure, productivity and diversity (Fazlollahi Mohammadi et al., 2022) as well as the frequency of biotic and abiotic disturbances (Hosseini et al., 2017; Kagezi et al., 2018). Trees can experience drought stress, sometimes exacerbated by thermal stress or biotic disturbances (Schwantes et al., 2018; Zandalinas et al., 2021; Pascual et al., 2022). The topographical structure mitigating these stresses would serve as shelter for trees (Hampe et al., 2013).
The severity of tree dieback varies by species, stand structure and environmental conditions (Hevia et al., 2019; Lakkana et al., 2022). Soil moisture and nutrient availability, stand structure, competition, tree age, extreme heat and frequent droughts have been found to be effective in causing dieback to occur (Turner and Lambert, 2005; Gazol et al., 2018; Taccoen et al., 2021). ). ). Trees with small crown and root systems would be more vulnerable due to less access to water and nutrients (Scott et al., 2013; Hosseini et al., 2014). In addition, it has been found that larger trees suffer less from dieback thanks to their deeper root system for access to soil resources (Mensforth et al., 1994). In contrast, studies have found a higher risk of larger trees dying due to declining vigor with age (Worrall et al., 2008), unless the problem is with tree height: trees that are taller would be due to taller trees Cost of vulnerable maintenance of breathing (Lavigne and Ryan, 1997; Tang et al., 2014; Housset et al., 2021). Forest dieback tends to be more severe in densely populated stands due to competition between trees for resources (Mensforth et al., 1994; Fensham and Fairfax, 2007). Along a dieback severity gradient, taxonomic diversity and stand structure are strongly correlated (Karami et al., 2022). However, tree dieback may not be related to stand characteristics, but to floodplain location, where dieback decreased with increasing water availability (Cunningham et al., 2010), underscoring the role of site quality. The overview presented above shows that tree decline is a complex phenomenon resulting from multiple factors and their interactions in space and time (McDowell et al., 2008; Gazol et al., 2020). Because the processes appear to be ecosystem-specific, managers should use the environmental or biotic factors per ecosystem as an early warning signal to identify and predict site typologies that are most at risk of die-off.
What is new about the present study is that we analyzed a wide range of potential factors attributable to tree dieback in a heterogeneous mountain environment. Our aim is to assess the relationship between the severity of oak dieback and the ecological properties of forest stands in different landforms in a semi-arid oak ecosystem in western Iran, where the severity of oak dieback varies over the years. Landscapes (Hosseini et al., 2017; Pourhashemi et al., 2017). ; Zarafshar et al., 2020). It is known that tree dieback in such forests depends on large-scale primary factors such as drought, increased temperatures and reduced precipitation, and increased intensity and duration of particulate matter storms (Shiravand and Hosseini, 2020; Yaghmaei et al., 2022). However, we hypothesize that not only macroscale but also multiple microscale factors control the severity of Brants oak dieback, specifically plant diversity through interspecific interactions and stand structures throughout the tree. Our detailed analysis of environmental conditions and their relationship to the spatial distribution of oak dieback can support the establishment of appropriate forest management policies in mountainous areas. In this context, we tested the relationship between the severity of oak dieback and the biotic and abiotic properties of forest stands. In particular, we tested the ecological and environmental characteristics of Brant oak stands in different shapes and canopy positions on slopes and examined how biotic and abiotic factors influence oak dieback patterns.
section cutouts
description of the place
Zagros Forest is one of the five ecological regions of Iran and covers 40% of Iran's forests. Protecting soil and water resources and securing the livelihood of the human population are key functions of these semi-arid forests. The study was conducted on the north slope of Shalem Mountain (46°29′-46°30′E, 33°36′-33°37′N; Fig. 1), a protected area in the department of Calle der Environment. The study extends from 1750 to 2180 m above sea level. M. Above sea level (asl) and the slope varies between 15 and 15 m
Shape of the catena, position of the slope and surroundings and structure of the stand
All environmental variables were significantly influenced by the location on the slopes (Page<0.01), but not by catena forms (Table S2). However, the SQI was significantly influenced both by the position on the slopes and by the interaction between the shape of the catena and the position on the slopes (Page<0.05; Table S2). LD and SQI were significantly higher in the toe-tilt (TS) position (Page<0.01) and their values decreased significantly with altitude along the slope, particularly at the summit (SU) and shoulder (SH).
discussion
The results of the study showed that oak dieback was positively correlated with woody plant diversity, mistletoe infection, differentiation between tree forms, tree regrowth, and the occurrence of significant ledges. Oak dieback correlated well with catena shape and slope position, and some of these factors interacted. Topography appears to be an important driver of ecosystem diversity, structure and processes. These results support our working hypothesis assuming that the topography is a
Diploma
The present study showed that the topography in the forests of the Zagros Mountains controls the susceptibility of oak trees to dieback. This control interacts with plant composition and diversity, canopy structure and soil quality. We have found that the position of the escarpment is a key factor controlling all variables except the shape of the catena, the ridgeagainsttalweg is less important and mainly concerns diversity measurements and variables related to tree dieback. The severity of die-off was significantly higher in concave catenas and
Statement of Authorship Contribution
Mehdi Heydari,Javad Cheraghi, Reza Omidipour: conceptualization, methodology, data curation, resources, formal analysis, software, visualization, monitoring, writing - original draft, writing - proofreading and editing; Mahmood Rostaminia, Yahya Kooch,Orsolya Valko, Christopher Carcaillet: Writing, revising and editing.
Declaration of Competing Interests
The authors declare that they have no competing financial interests or known personal relationships that may have influenced the work described in this article.
Thanks
This work was supported byLam University, Ilam, Iran.
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Forest Ecology and Management, Volume 537, 2023, Article 120950
Conserving the biodiversity of softwood and deciduous trees in riparian and mountainous areas is of increasing interest to foresters. For example, the input of softwood and hardwood into streams increases structural diversity and affects the accumulation of aquatic and terrestrial organisms, and the presence of both components in stands can have a positive effect on post-disruption resilience. Investigating the effects of density and weed control on the establishment of red alder (with rotorBong.) and western hemlock (Tsuga heterophylla(Raf.) Sarg.) Combined Nelder plots and replacement series were established at three sites in western Oregon. The species ratio of hemlock to alder was 100:0, 75:25, 50:50, 25:75 and 0:100, with densities ranging from 988 to 85,400 tons per hour. Measurements were available after 24 years for two locations and after 14 years for one location. Weed height and diameter increased at lower densities, especially in the early years. As the canopy closed, the effects of weed control diminished over time, but were still visible on some plots after 24 years. Increased red alder density resulted in decreased survival and growth of both species. The density of the hemlock had no effect on the growth of the red alder for 24 years. Although the mixed stocks resulted in higher volume in the early years, this did not hold up in later years. The higher juvenile growth rates of red alder compared to western hemlock led to a dominance of alder over hemlock in early years, particularly at higher alder densities and ratios. Cultivation of hemlock with a lower alder density has maintained a co-dominance with alder and will become dominant as alder growth rates decline. The density of the alder must be low enough for the hemlock to survive and grow. Density, location, species ratio, animal damage, and the presence of other competing vegetation resulted in different dominance scenarios of hemlock and alder, making it difficult to accurately predict long-term outcomes.
investigative article
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Forest Ecology and Management, Volume 537, 2023, Article 120911
Climate models predict more frequent droughts and more severe fire events. Although wildfires in wet forests are historically rare, they can have catastrophic effects on forest values and services. Therefore, it is important to ask whether climate change is increasing the frequency of fires in wet forests. Long-term fire progression and weather records in wetlands were compared.EucalyptusForests supplying water to Melbourne, Australia to identify the combination of dry weather and fire causing stand-replacing fires. The impact of climate change on the frequency of stock renewal was predicted using reduced regional climate change projections for RCP4.5 and RCP8.5.
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investigative article
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Environmental Management Magazine, Band 339, 2023, Artikel 117933
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investigative article
Population decline in a Pleistocene refugium: drought-related gradual death of a South Australian gum
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Refugia can facilitate species persistence under long-term environmental change, but it is unclear whether Pleistocene refugia will continue to function as anthropogenic climate change progresses. Die-offs in populations where refuge is restricted therefore raise concerns about their long-term persistence. Using repeated field studies, we investigated die-off in an isolated populationEukalyptus Macrorhynchaduring two periods of drought and discuss the prospects for their continued existence in a Pleistocene refuge. We first confirm that Clare Valley in South Australia has provided a long-term sanctuary for the species, although the population is genetically very different from other conspecific populations. However, the population lost more than 40% of individuals and biomass due to drought, with mortality being just under 20% after the Millennium Drought (2000–2009) and almost 25% after the Great Drought (2017–2019). The best predictors of mortality differed after each drought. While north orientation of a sampling site was a significant positive predictor after both droughts, biomass density and slope were significant negative predictors only after the Millennium Drought, and distance to the northwest corner of the population, which intercepts hot, dry winds, was a significant one positive predictor only after the Great Drought. This suggests that while more marginal low-biomass sites and sites on flat plateaus were initially more vulnerable, heat stress was an important factor in die-offs during the Great Drought. Therefore, the causative causes of die-offs may change as the population declines. The regeneration took place mainly on the south and east side, where the solar radiation was lowest. Although this protected area population is experiencing sharp declines, some ravines with less sun exposure appear to be harboring relatively healthy and regenerating stands of red fibrous bark, offering hope for continued existence in small pockets. Monitoring and managing this herd during future droughts will be critical to ensure the continued existence of this isolated and genetically unique population.
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Regreening by Seeding or Planting: A Systematic Map of the World
Environmental Management Magazine, Band 337, 2023, Artikel 117713
Around the world, approximately 2 billion hectares of land are degraded and in need of ecological restoration. Active recovery often involves revegetation, leading to the question of direct sowing or planting seedlings from nurseries. Choice of reclamation method can regulate plant survival and performance, with economic implications that ultimately affect our ability to carry out reclamation. We follow a peer-reviewed protocol to develop a systematic map that collects, describes, and catalogs available studies on how seeding versus planting compares to achieve recovery goals. We create a database with the characteristics of all surveys retrieved, which can be searched to identify surveys on specific sites and habitats, restoration targets, plant material, technical aspects and measured results. The search was conducted in eight languages and returned 3,355 publications, of which 178 were retained. The systematic map identifies research gaps, such as missing studies in the Global South, in rainforests and over a long period of time offers opportunities for expanding fieldwork. In addition, many studies have overlooked reports of important technical aspects such as seed origin and nursery culture methods, and others, such as irrigation or seedling protection, have been applied more often to planting than to sowing, limiting our ability to learn from previous research. Most studies measured outcomes in the context of target crops, but avoided measuring overall recovery outcomes or economics. This represents a major research gap, as the choice of revegetation method is largely based on economics, and achieving recovery goals goes beyond plant establishment. Finally, we identified a significant body of studies conducted in temperate regions and over short time periods (0-5 years). This research group needs further in-depth synthesis, possibly through meta-analysis, to show the overall balance between sowing and planting and to assess whether the answer to this question is mediated by species traits, environmental traits or technical aspects. The systematic mapping database allows managers not only to identify clusters and research gaps, but also to find the most relevant scientific literature on plant suitability.against. Planting for specific conditions, such as specific species or habitats.
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