Removal of invasive Scotch broom increases its negative effects on soil chemistry and plant communities

Oecologia ◽  
2022 ◽  
Author(s):  
Robert A. Slesak ◽  
Timothy B. Harrington ◽  
Anthony W. D’Amato ◽  
David H. Peter
2021 ◽  
Author(s):  
Robert Slesak ◽  
Timothy Harrington ◽  
Anthony D'Amato ◽  
David Peter

Abstract Scotch broom is an aggressive invasive species of major concern in coast Douglas-fir forests of the Pacific Northwest USA. Control efforts are common, but potential for ecosystem recovery following Scotch broom removal is unclear. We assessed the potential for ecosystem recovery following broom removal at two sites that contrasted strongly in soil quality (i.e., texture and nutrient pool size) in western Washington and Oregon. Comparisons were made among replicated plots where Scotch broom was never present (uninvaded), retained, or removed. Microclimate (photosynthetically active radiation (PAR), soil temperature and moisture), soil properties, and vegetation were monitored during 2013 to 2017. Scotch broom removal increased PAR and soil temperature at both sites but had limited effects on soil moisture. Concentrations of Ca, Mg, K, and P were significantly lower with Scotch broom removal compared to the uninvaded and retained treatments, with the effect being most pronounced at the low-quality site. NMS ordinations indicated that the treatments differed in vegetation composition, with limited evidence for recovery in the removal treatment. Nonnative and native species varied inversely in their abundance responses, where nonnative species abundance was greatest in the removal treatment, intermediate in the retained treatment, and lowest in the uninvaded treatment, indicating occurrence of a secondary invasion following removal. As with the soil response, effects were more pronounced at the low-quality site. Our findings indicate that Scotch broom removal exacerbates negative effects on soil and plant communities, with little evidence of ecosystem recovery over our study period. These findings highlight the importance of controlling Scotch broom invasions immediately after the species establishes, especially at low-quality sites that are more susceptible to Scotch broom invasion and negative legacy effects.


Koedoe ◽  
1997 ◽  
Vol 40 (2) ◽  
Author(s):  
C.M. Smit ◽  
G.J. Bredenkamp ◽  
N. Van Rooyen ◽  
A.E. Van Wyk ◽  
J.M. Combrinck

A vegetation survey of the Witbank Nature Reserve, comprising 847 hectares, was conducted. Phytosociological data were used to identify plant communities, as well as to determine alpha and beta diversities. Eleven plant communities were recognised, two of these are subdivided into sub- communities, resulting in 14 vegetation units. These communities represent four main vegetation types, namely grassland, woodland, wetland and disturbed vegetation. Grassland communities have the highest plant diversity and wetland vegetation the lowest. Floristic composition indicates that the vegetation of the Rocky Highveld Grassland has affinities to the grassland and savanna biomes and also to the Afromontane vegetation of the Great Escarpment. An ordination scatter diagram shows the distribution of the 14 plant communities or sub-communities along a soil moisture gradient, as well as along a soil depth/surface rock gradient. The sequence of communities along the soil moisture gradient is used for calculating beta-diversity indices. It is concluded that the relatively small size of the Witbank Nature Reserve is unlikely to have significant negative effects on the phytodiversity of the various plant communities. This nature reserve is therefore of considerable importance in conserving a representative sample of the Rocky Highveld Grassland.


2018 ◽  
Vol 21 (4) ◽  
pp. 1055-1073 ◽  
Author(s):  
David R. Carter ◽  
Robert A. Slesak ◽  
Timothy B. Harrington ◽  
David H. Peter ◽  
Anthony W. D’Amato

Ecology ◽  
2012 ◽  
Author(s):  
Paul A. Keddy ◽  
James Cahill

Competition is generally understood to refer to the negative effects on plant growth or fitness caused by the presence of neighbors, usually by reducing the availability of resources. Competition can be an important factor controlling plant communities, along with resources, disturbance, herbivory, and mutualisms. Since all plants require a few basic elements, the resource involved is generally light, water, nitrogen, or phosphorus, depending upon the species and the location. The effects of competition are widespread and easily observed in mixtures of crops and managed forests, which is why weeding and thinning are practiced. Competition is also widespread in native habitats, from deserts to wetlands, and is known to have important—indeed crucial—effects upon recruitment, growth, and reproduction. In the late 1800s, Darwin wrote extensively about the importance of competition in nature, particularly its role in driving natural selection. Thereafter, interest in the phenomenon grew. Many experiments with both crops and wild species were conducted. Models of competitive interactions were also constructed, with the number and size of the models increasing rapidly with the advent of computers in the 1970s. Because the word competition has a common usage in English, what it represents in biological systems is frequently assumed, rather than explicitly stated, leading to misunderstanding. Care must be taken in using or interpreting the word without specifying what kind of competition is being investigated, as different forms of competition can have different types of consequences. For example, competition may be looked at from the perspective of an individual, a population, or a species, it may be symmetric or asymmetric, and it can occur among single or multiple species simultaneously. Experimental design carries its own assumptions, which are often not stated in published articles. One of the most difficult tasks in exploring published studies is the need to sift through large numbers of experiments in which investigators have haphazardly selected (a pair of) species and grown them in mixture, without adequately justifying their choice of species or the experimental design. Another difficult task is distinguishing between models that, at least in principle, have measurable inputs or make measurable predictions (or both) and those that do not and cannot be tested. Overall, the very ease of growing plants in mixture, as well as the ease of making new models, may have made some people careless, with the result that basic questions are remaining unaddressed. Ongoing issues of importance include mechanisms of competition, types of competition, effects of competition on plant coexistence, and the intensity of competition under different sets of conditions.


Oecologia ◽  
2018 ◽  
Vol 188 (3) ◽  
pp. 821-835 ◽  
Author(s):  
Douglas J. McCauley ◽  
Stuart I. Graham ◽  
Todd E. Dawson ◽  
Mary E. Power ◽  
Mordecai Ogada ◽  
...  

Author(s):  
N. A. Popov ◽  
V. Yu. Sidorova

In the State Forest Fund and forests of rural territories of the Russian Federation the areas of hayfields and pastures are 4,3 and 2,3 million hectares. Annually, 22,5 million tons of herbage are harvested on forest lands, which is 4,5 million tons of hay. Forest soils of the Moscow region are characterized by high acidity, low content of nutrients, they need regular fertilization. In the Moscow region according to the type of soils they are divided into gray forest soils, which make up 6,1 % of all soils and sod-podzolic – 43,4 %. When livestock manure enters the soil during grazing, the pH of the soil becomes alkaline 8,0–9,0. Six-month compost of livestock manure with a moisture content of 80 %, left on forest pastures, exceeds the leaves’ litter in the amount of dry matter by 2,6 times, N (in % for absolutely dry matter) by 6,5 times, the amount of cement carbon (C) by 1,6 times, the amount of total nitrogen (N) by 16,8 times, but is inferior in the content of C (in % for absolutely dry matter) by 1,6 times. Deoxidation of soils promotes accelerated vegetation. The impact of livestock grazing on forest resources has both positive and negative effects on increasing the biodiversity of plant communities. Livestock grazing causes both harm and benefit to forest biological diversity. The harm is caused by unregulated use, the benefit of grazing brings as a source of organic fertilizers, restoring the cycle of C, P, N. Cattle also contributes to the loosening of the soil, the destruction of ticks, and it participates in the change of the plant composition of the forest to more valuable types of trees and shrubs.


2018 ◽  
Author(s):  
Sofia J. van Moorsel ◽  
Terhi Hahl ◽  
Owen L. Petchey ◽  
Anne Ebeling ◽  
Nico Eisenhauer ◽  
...  

AbstractUnderstanding factors that increase ecosystem stability is critical in the face of environmental change. Experiments simulating species loss from grassland ecosystems have shown that losing biodiversity decreases the ability of ecosystems to buffer negative effects of disturbances. However, as the originally sown experimental communities with reduced biodiversity develop, plant evolutionary processes or the assembly of interacting soil organisms may allow them to develop stability and resilience over time. We explored such effects in a long-term grassland biodiversity experiment with plant communities with either a history of co-occurrence (selected communities) or no such history (naïve communities) over a four-year period in which a major flood disturbance occurred.We found selected communities had temporally more stable biomass than the same communities of naïve plants, especially at low species richness. Furthermore, selected communities showed greater short-term biomass recovery after flooding, resulting in more stable post-flood productivity. In contrast to a previous study, the positive diversity–stability relationship was maintained after the flooding. Our results were consistent across three soil treatments simulating the presence or absence of co-selected microbial communities. We suggest that prolonged exposure of plant populations to a particular community context and abiotic site conditions can increase ecosystem temporal stability and resistance to disturbance. We argue that selection during the course of a biodiversity experiment is the most parsimonious explanation for these effects. A history of co-occurrence can in part compensate for species loss, as can high plant diversity in part compensate for the missing opportunity of such adaptive adjustments.


2019 ◽  
Vol 9 (1) ◽  
Author(s):  
Zhenhong Wang ◽  
Alessandro Chiarucci ◽  
Juan F. Arratia

Abstract The relationship between plant productivity and species richness is one of the most debated and important issues in ecology. Ecologists have found numerous forms of this relationship and its underlying processes. However, theories and proposed drivers have been insufficient to completely explain the observed variation in the forms of this relationship. Here, we developed and validated integration models capable of combining twenty positive or negative processes affecting the relationship. The integration models generated the classic humped, asymptotic, positive, negative and irregular forms and other intermediate forms of the relationship between plant richness and productivity. These forms were linked to one another and varied according to which was considered the dependent variable. The total strengths of the different positive and negative processes are the determinants of the forms of the relationship. Positive processes, such as resource availability and species pool effects, can offset the negative effects of disturbance and competition and change the relationship. This combination method clarifies the reasons for the diverse forms of the relationship and deepens our understanding of the interactions among processes.


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