Abstract:As invasive species become increasingly abundant in forests, their presence may influence a number of key nutrient cycling processes. For example, Chinese privet has become well established in southeastern forests and continues to spread. Two studies, a multisite field investigation and a controlled approach on a single site, were conducted to examine the role of Chinese privet (Ligustrum sinense) on decomposition within riparian forests of the Georgia Piedmont. The field study also investigated the effects of… Show more
“…For example, Stone (1997) has shown that practicing site preparation procedures such as hand-pulling seedlings and mowing and/or cutting stems larger than 2.5 m can successfully reduce Chinese privet invasion in relatively small areas, such as nature preserves [29]. Chinese privet has been shown to inhibit reproduction and growth of trees through altering the occurrence of arbuscular mycorrhizal fungi in the resident soil [30] and influencing a number of key nutrient cycling processes [31]. In addition, a combination of shading and some allelopathic effect of adult leaf leachate inhibit the growth of other plants under a canopy of Chinese privet and contribute to a reduction in plant diversity after invasion [32].…”
Chinese privet (Ligustrum sinense) was the most prevalent invasive shrub in the forestlands of Eastern Texas in 2006. We analyzed extensive field data collected by the Forest Inventory and Analysis Program of the U.S. Forest Service to quantify the range expansion of Chinese privet from 2006 to 2011. Our results indicated the presence of Chinese privet on sampled plots increased during this period. Chinese privet spread extensively in the north. Results of logistic regression, which classified 73% of the field plots correctly with regard to species presence and absence, indicated probability of invasion was correlated positively with elevation, adjacency (within 300 m) to water bodies, and site productivity, and was correlated negatively with stand age, site preparation (including clearing, slash burning, chopping, disking, bedding, and other practices clearly intended to prepare a site for regeneration), artificial regeneration (which refers to planting or direct seeding that results in at least 50% of the stand being comprised of stocked trees), and distance to the nearest road. Habitats most at risk to further invasion (likelihood of invasion > 40%) under current conditions occurred primarily in Northeast Texas. Practicing site preparation and artificial regeneration reduced the estimated probabilities of further invasion.
“…For example, Stone (1997) has shown that practicing site preparation procedures such as hand-pulling seedlings and mowing and/or cutting stems larger than 2.5 m can successfully reduce Chinese privet invasion in relatively small areas, such as nature preserves [29]. Chinese privet has been shown to inhibit reproduction and growth of trees through altering the occurrence of arbuscular mycorrhizal fungi in the resident soil [30] and influencing a number of key nutrient cycling processes [31]. In addition, a combination of shading and some allelopathic effect of adult leaf leachate inhibit the growth of other plants under a canopy of Chinese privet and contribute to a reduction in plant diversity after invasion [32].…”
Chinese privet (Ligustrum sinense) was the most prevalent invasive shrub in the forestlands of Eastern Texas in 2006. We analyzed extensive field data collected by the Forest Inventory and Analysis Program of the U.S. Forest Service to quantify the range expansion of Chinese privet from 2006 to 2011. Our results indicated the presence of Chinese privet on sampled plots increased during this period. Chinese privet spread extensively in the north. Results of logistic regression, which classified 73% of the field plots correctly with regard to species presence and absence, indicated probability of invasion was correlated positively with elevation, adjacency (within 300 m) to water bodies, and site productivity, and was correlated negatively with stand age, site preparation (including clearing, slash burning, chopping, disking, bedding, and other practices clearly intended to prepare a site for regeneration), artificial regeneration (which refers to planting or direct seeding that results in at least 50% of the stand being comprised of stocked trees), and distance to the nearest road. Habitats most at risk to further invasion (likelihood of invasion > 40%) under current conditions occurred primarily in Northeast Texas. Practicing site preparation and artificial regeneration reduced the estimated probabilities of further invasion.
“…It has become widely naturalized in the southeastern United States and is reported to have invaded thousands of acres (Mitchell et al 2011;Ward 2002). It generally has multiple stems and a shrub-like growth form, with heights ranging from 1.5 to 3.6 m (5 to 12 ft), although it occasionally becomes treesized (Greene and Blossey 2011).…”
mentioning
confidence: 99%
“…Much of the previous research on CHP has focused on growth characteristics, response to flooding, dispersal rates, impacts on native plants and forest regeneration, and influences on decomposition and nutrient availability (Hanula et al 2009;Merriam and Feil 2002;Mitchell et al 2011;Morris et al 2002). Research in the Piedmont region of the United States has indicated that CHP invasion suppresses herbaceous understory, causing decreases in plant species richness and diversity (Greene and Blossey 2011;Merriam and Feil 2002;Wilcox and Beck 2007).…”
mentioning
confidence: 99%
“…Research in the Piedmont region of the United States has indicated that CHP invasion suppresses herbaceous understory, causing decreases in plant species richness and diversity (Greene and Blossey 2011;Merriam and Feil 2002;Wilcox and Beck 2007). CHP litter has a lower C : N ratio than most of the understory vegetation that it displaces, which results in accelerated nutrient mineralization, especially during summer months (Mitchell et al 2011). The rapid rate at which CHP spreads impedes the ability of native pine (Pinus spp.…”
mentioning
confidence: 99%
“…Their analyses, however, did not include soils, nor did their study design incorporate within-stand variables such as microsite differences in slope, litter depth, etc. However, studies conducted with other species have indicated that factors such as soil texture, nutrient concentrations, landscape, slope, and terrain shape correlate strongly with invasion (Mitchell et al 2011). Determining how site characteristics such as these are related with CHP invasion could be an important management tool in deterring its spread, prioritizing resources for early detection and control, and maintaining understory and overstory diversity in southeastern forests (Wang and Grant 2012).…”
There is a limited understanding about the ecological mechanisms that enable certain plant species to become successful invaders of natural areas. This study was conducted to determine the soil and landscape characteristics that correlate with invasion of Chinese privet (CHP), and to develop a model to predict the probability of CHP invasion in Piedmont forests. A landscape ecosystem classification (LEC) system—based on the percentage of clay in the B horizon, depth to maximum clay (cm), exposure, terrain shape, and aspect (degrees)—was used to determine the soil moisture characteristics of invaded and uninvaded plots. Additional measurements included the cover classes of CHP and other species, litter depth (cm), slope (degrees), overstory basal area (m2 ha−1), and soil chemical properties. CHP invasion was negatively correlated with overstory basal area and slope and positively with litter depth and pH. A stepwise logistic regression model containing these four variables was highly sensitive, with an overall accuracy of 78%. Given the accuracy of this model, we propose that it can be used to calculate the probability of invasion in a given area, provided that some basic, readily obtainable site characteristics are known.
The objectives of this study were to evaluate the allelopathic effects of Chinese privet (Ligustrum sinense Lour.) extract on native seeds and cuttings and to assess the survivability of native plants in a flooded riparian corridor. Field sites occupied the Trinity River floodplain in southeast Dallas County, Texas. Eight native species were evaluated. They were soapberry, red mulberry, persimmon, elderberry, beautyberry, coralberry, mustang grape, and heartleaf peppervine. From this study, we concluded that:
Truncating privet at ground level and applying equal parts of glyphosate and water to the stump effectively kills the plant;
Once removed, privet does not curtail establishment of native plants;
A 60‐day (d) flood killed most plants, with red mulberry being the most resilient;
A 1% leaf and berry extract from privet significantly reduced soapberry seed germination; and
A 1% extract from various parts of privet did not significantly affect root growth from cuttings.
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