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Several stages of Hyptis invasion in the landscape of the study area: a early stage of Hyptis invasion, b riverine landscape heavily invaded by Hyptis, c healthy patches of Hyptis (below red line) in the area near to habitation and agriculture fields, d larger patch of landscape having invasion of Hyptis competing with Lantana, e a close view of Hyptis plant, f late summer period with sign of dried population of Hyptis

Several stages of Hyptis invasion in the landscape of the study area: a early stage of Hyptis invasion, b riverine landscape heavily invaded by Hyptis, c healthy patches of Hyptis (below red line) in the area near to habitation and agriculture fields, d larger patch of landscape having invasion of Hyptis competing with Lantana, e a close view of Hyptis plant, f late summer period with sign of dried population of Hyptis

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Biological invasion is probably one of the most serious threats to biodiversity after climate change. Landscape distinguished by the heterogeneity of structure, forms, human interferences, and environmental settings plays an important role in the establishment and spread of invasive species. We investigated the effect of the spatial heterogeneity f...

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The assessment of seed banks could provide useful hints towards ensuring restoration planning and invasive species management. In this study, the impacts of two invaders, Hyptis suaveolens and Urena lobata on the soil seed banks were investigated. We also assessed the seed characteristics of the invaders at the invaded sites. This was achieved usin...

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... In interior forest openings of the Vindhyan highlands, heavy infestations of H. suaveolens monoculture thickets have also been reported (Sharma 2007b;Sharma et al. 2009;Sharma and Raghubanshi 2009;Sharma et al. 2017). Kumar et al. (2019) advocated that habitat size, land use, and management practices affect the H. suaveolens invasive population and reported a severe infestation of H. suaveolens in open areas of water stream networks of Indian Western Himalayan regions. Studies have indicated that H. suaveolens forms dense monospecific thickets, potentially reducing light penetration to the forest floor, thus masking the growth of other herbaceous species (Raizada 2006;Sharma et al. 2009Sharma et al. , 2017Afreen et al. 2018). ...
... Spatial heterogeneity, management practices, and environmental factors such as land disturbances (Minor et al. 2009;Vilà et al. 2011;Kumar et al. 2019), species composition (Stohlgren et al. 1998), soil properties (Fukano et al. Fig. 7 Relationships between and among stand-level, seed-level, and plant-level traits of Hyptis suaveolens under sun (high-light) and shade (low-light) conditions. ...
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Background Hyptis suaveolens (L.) Poit., native to the American tropics, is a pantropical annual plant and a major invasive species throughout India. It was anticipated that the availability of sunlight, coupled with its superior reproductive potential, persistent propagule bank, and dispersal ability, could lead to an increase in the growth and spread of this invader, thus potentially impeding herbaceous growth and diversity in non-native areas. Clarifying its ecological fitness and competitive performance will be useful to manage the spread of H. suaveolens in natural ecosystems that are facing a wide range of anthropogenic pressures. Methods The present study is a three-tier experiment. In the first tier, a field study was conducted to assess the patterns of H. suaveolens abundance and herbaceous species diversity in response to light availability (sun, 842–1072 µmol m –2 s ⁻¹ and shade 253–341 µmol m – ² s ⁻¹ ) in the tropical dry deciduous ecosystems in the Vindhyan highlands, India. Furthermore, the impact of H. suaveolens abundance on the resident native and non-native species abundance and diversity was also studied. In the second tier, a randomized common garden experiment was conducted to understand the trait fitness of H. suaveolens in sun (940 µmol m –2 s ⁻¹ ) and shade (300 µmol m –2 s ⁻¹ ) conditions. In the third tier, a plant growth chamber experiment with high-light (940 µmol m –2 s ⁻¹ ) and low-light (300 µmol m –2 s ⁻¹ ) treatments was done to learn how H. suaveolens partitions its biomass between aboveground and belowground plant parts. Results The field study indicated that the sunlit areas had a higher abundance of H. suaveolens and a lower diversity of resident herbaceous species than the shaded areas. The common garden experiment showed that sun-dwelling H. suaveolens individuals performed better in germinative, vegetative, eco-physiological, and reproductive traits than the shade-dwelling individuals. The growth chamber experiment exhibited that plants grown in high-light environment had greater seed germination, seedling recruitment, and aboveground biomass than those grown in low-light environment, whereas plants grown in low-light environment exhibited a higher root mass ratio than the high-light individuals. These results suggest that H. suaveolens individuals mask the understory vegetation owing to higher seedling recruitment, relative growth rate, photosynthetic performance, resource acquisition-allocation, and reproductive output in response to high-light conditions. Conclusions The study concludes that light significantly controls the invasive population dynamics of H. suaveolens in dry deciduous forests. In high-light areas, H. suaveolens populations dominate the forest understory with suboptimal shade tolerance. In shade environment, H. suaveolens maintains a persistent soil seed bank along with ‘Oskar individuals’ that become active in response to high-light availability. The modus operandi is a ‘sit and wait’ strategy. The current study provides insights on prioritizing areas for H. suaveolens management that will potentially reduce the risk of biological invasions on the native species diversity of tropical regions.
... Resources and niches are well established but difficult to quantify concepts since they could potentially reflect an almost infinite number of factors. Thus, examinations of these hypotheses rely most often on proxies like the composition and diversity of the landscape as a potential path for decreasing interspecific competition and allowing the establishment and propagation of alien species [9][10][11]. ...
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... S.M. Haq et al. weed control and eradication plans in the region's rice agro-ecosystems. Such research is critical for managing weeds, as a lack of data on weeds is one of the most significant barriers to developing an effective weed management strategy [53]. ...
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... Evaluation of temporally dynamic abiotic and biotic processes is crucial for planning to manage and protect ecosystems and biodiversity with reference to threats from invasive species (Zurell et al. 2022). The spatial variability of topography, pattern of different land uses, current species composition, ecosystem features, and species physiology, all impact the establishment of invasive species (Khuroo et al. 2009;Kumar et al. 2019). The taxonomic and geographic parameters influencing the dynamics of invasive species are poorly understood (Jamil et al. 2022). ...
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... This provides an opportunity to investigate the weed invasion in these two different land use classes. At the same time, the information on the phenological events of weed is important for formulating effective control and management [13,14]. ...
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... Field-based observations are usually time-consuming and costly and may not be easy for difficult terrain such as mountains (Banko 1998;Martin et al. 1998). Remote sensing has widely been used in vegetation mapping using multiple approaches and using different data sets (Clerici et al. 2012;Han et al. 2004;Jin et al. 2016Jin et al. , 2017Kumar et al. 2019aKumar et al. , 2021Singh et al. 2020a, b;Stibig et al. 2003;Mishra et al. 2021). With remote sensingbased observations, it is easy to trace the spatial and temporal changes in a forested landscape as observations are available at planetary scales with repeated observations ranging from days to months. ...
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... Remote sensing satellite data and modelling techniques are valuable tools to infer ecosystem structure and processes' spatial and temporal patterns. Several researchers used these tools for vegetation characterisation (Kimothi and Dasari 2010;Munsi et al. 2010;Padalia et al. 2013;Srinet et al. 2020a;Mishra et al. 2021), forest dynamics (Joshi et al. 2011Munsi et al. 2012;Areendran et al. 2017;Kumar et al. 2021), species distribution modelling (Yang et al. 2013;Lamsal et al. 2018), spatial heterogeneity (Kumar et al. 2019), atmospheric CO 2 dynamics (Watham et al. 2021), gross primary productivity modelling (Mishra and Chaudhuri 2015;Srinet et al. 2020b), and foliar nutrients modelling (Vasudeva et al. 2021) in the Indian Siwalik region. ...
... MaxEnt modelling was used to predict the distribution of Justicia adhatoda L. (Yang et al. 2013) and some invasive plants (Lamsal et al. 2018). Further, it has been suggested that the spread of invasive plants is affected by spatial heterogeneity (Kumar et al. 2019). ...
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The Himalayan foothills or the Siwaliks have been considered as one of the most fragile ecosystems of India. The underlying cause of degradation includes natural settings (geological formation and climate change) and human-mediated pressures (sandstone mining, urbanisation and developmental activities). Since the Siwaliks is associated with the livelihood of about 20 million people, it becomes imperative to respond appropriately for sustaining this ecologically fragile region. Ecological principles have great potential to develop sustainable practices for the conservation and management of natural resources. These principles offer nature-based solutions to sustain the ecologically sensitive and degraded ecosystems such as the ‘Siwaliks’. However, there is a need for concerted research to develop data-driven decisions for effective management. Therefore, a systematic analysis was conducted to assess the current patterns and knowledge gaps about plant ecological studies in the Indian Siwalik region. This article analysed the available peer-reviewed literature using established guidelines and bibliometric analyses. We found an increasing trend in the scientific output, and most studies were concentrated in the Siwalik region belonging to the Indian state of Uttarakhand. Although studies have been conducted on plant ecology, landscape ecology and ecosystem ecology have been disproportionately focused. Our findings suggest a growing interest in the plant ecology of the region; however, these studies seem relatively small compared to the complexity and diversity of this ecosystem structural and functional attributes. Further, with advances in computer application and remote sensing satellite data availability, we observed a shift towards ecological modelling studies, though experimental evidence also needs to be addressed.
... These effects differ for different forest age classes and are subjective trait differences of native and nonnative plant species (Dillon et al. 2018). Invasive species are able to affect local biodiversity on multiple scales and diverse ways (Kumar et al. 2019c). In natural forest ecosystems, risks due to IAS comprise of hybridization, disease transmission, and competition among species (Langmaier and Lapin 2020). ...
Chapter
Forest ecosystems are one of the most important ecosystems on earth, and sustainability of the planet heavily relies on diverse ecosystem services emerging from them. In order to maintain unrestricted flow of ecosystem services in the warming world, it is essential to conserve and sustainably manage them. This necessitates an understanding of past, present, and future structural and functional pattern of forests, their functioning as well as health status. There are substantial indications that unsustainable human activities have significantly affected the structure and functioning of natural forest ecosystems. To explain the distribution of forests, their functioning, and different drivers of loss to which forests are exposed, enormous methodological and socio-ecological and governance advancements have already taken place. In the opening chapter, we elaborate on the understanding of forest ecosystems from variations in definitions and conceptualizations of forests, emerging challenges, monitoring advancements, etc. Chapter broadly covers scientific advancements for monitoring various stressors, forest degradation, inventory using advanced tools to present the fate of forest structure, and functioning in the changing world. The volume highlights drivers of deforestation and forest degradation, provides insights to innovations, and also touches advanced institutional provisions and governance framework. The thematic and cross cutting chapters bring in scientific evidence-supported information and solutions to enhance the prospects for conserving forests in the fast changing world. Apart from providing a broader overview of the book, its growing relevance, the chapter also offers a brief outline of the chapters in different sections of the book.
... This helps to ensure sustainable development and understanding of human activities' effect within and around protected areas. Geospatial data such as aerial and satellite photographs can be used to manage flora and fauna by determining the presence and distribution of vegetation and invasive species within a protected area (Kumar et al. 2019b). It helps in determining the extent of vegetation, water and food availability for animals in different seasons of the year. ...
Chapter
Geospatial assessment supported by the Geographic Information System (GIS), Remote Sensing (RS), and Global Positioning System (GPS) caters for compelling techniques of mapping, monitoring, surveying, classification, characterization, and change detection of natural resources. These techniques provide a platform for generating valuable data, creating cartographic products, and performing timely analysis to make sound sustainable development decisions. Remote sensing involves the recording of information distantly without coming in contact with the object using the various electromagnetic spectrum. It employs the use of cameras, lasers, scanners, and specialized sensors that are located on the ground or aerial platforms (Jensen and Im 2007). The principle geospatial components of a study are derived using various methods such as aerial photographs, satellite imaging, Light Detection and Ranging (LiDAR) data, Unmanned Aerial Systems (UAS)/Drone data, GPS survey, etc., based on the study’s objective. Figure 2.1 displays different remote sensing components for collecting NRM data. Remotely sensed data captured through different satellites and other platforms such as drones platforms has wide applications in natural resource management disciplines. Multiple data from various sources also serve as input for other environmental models (Melesse and Graham 2004). The combined use of GIS, remote sensing data, and GPS has enabled researchers and natural resource managers to establish management plans for various applications (Philipson et al. 2003). The rest of this chapter will focus on multiple geospatial technologies and their application in different natural resource management areas.
... Any new approach that serves the purpose of classifying the plants into PFTs would help modellers to obtain global maps of PFT which is a pre-requisite for use and development of vegetation models for climate change impact studies (Foley et al., 1996;Kumar et al., 2018aKumar et al., , 2020Prentice, 1989;Quillet et al., 2010;Rawat et al., 2020;. The recent concerns of climate change impacts manifested on forest and agriculture have augmented the efforts of using new approaches and vegetation models for the vulnerability assessment of different ecosystems (Franklin et al., 2013;Gupta et al., 2020;Kalra and Kumar, 2019;Kraft et al., 2008;Kumar et al., 2018bKumar et al., , 2019aKumar et al., , 2019bKumar et al., , 2019cLevis et al., 2017;Pandey et al., 2018;Peng, 2000;Pokhriyal et al., 2020;Rawat et al., 2020;. Different Dynamic Global Vegetation Models (DGVMs) have evolved in recent times and these models are capable of simulating transient patterns of vegetation under the influence of climate change which is much in use due to global concern of climate change (Gillison, 2019;Peng, 2000). ...
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Phenological studies involve capturing information on dates of recurrent and seasonal biological events in plants and animals. In plants, phenological events of leaf flushing, full bloom, autumn discolouration, leaf fall etc. can be used to distinguish vegetation into separate classes. We refer here such phenological distinction as Phenological Functional Types (PhFT). The PhFT can be considered as the precursor of Plant Functional Types (PFTs) where PFT uses additional traits (e.g. leaf area, tree height, leaf structure, rate of evapotranspiration and photosynthesis, etc.) to classify vegetation. The PFT classification is essentially needed for developing and running dynamic global vegetation models (DGVMs) used in studying impacts of climate change on vegetation. We used archived long time series satellite remote sensing data, Landsat 5,7 and 8 (1985–2019), for classifying a landscape into appropriate PhFT. Normalized Difference Vegetation Index (NDVI) was calculated for the given period in the Google Earth Engine (GEE). The GEE is a cloud-based platform developed for the retrieval and processing of remotely sensed images and other data. The monthly median values of NDVI for the mentioned period was used to label each pixel into appropriate PhFT classes using Random Forest (RF) algorithm in GEE to obtain four distinct classes of evergreen forest, deciduous forest, agriculture and non-forest. The comparison of PhFT map was done with reference maps of global MCD12Q1 and the forest type map of India; with an overall moderate agreement of 68.55% and 66.22%, respectively. MCD12Q1 has an accuracy of 73% for the land cover map and the forest type map of India has 75% accuracy, whereas, we achieved an overall accuracy of 78%. The PhFT classification accuracy can further be improved using additional indices and topographic variables. The methodology demonstrated in this study can be adopted for classifying a landscape into distinct PhFT/PFT classes.