Weed control is challenging for Mississippi peanut producers. Research was established during 2017 and 2018 at the Delta Research and Extension Center in Stoneville, Mississippi, to evaluate herbicide programs for weed control and reducing weed seed production in Mississippi peanut production. Treatments were combinations of acetochlor, clethodim, flumioxazin, lactofen, paraquat, and S-metolachlor with their respective adjuvants if needed. Treatments were applied: PRE, early-POST (EPOST), and/or mid-post (MPOST). All treatments included a PRE application followed by (fb) application of EPOST and/or MPOST application. Flumioxazin PRE fb lactofen plus clethodim MPOST provided greatest weed control and peanut yield. This treatment provided 88 to 100% control of barnyardgrass, hemp sesbania, Palmer amaranth, pitted morningglory, and prickly sida. Additionally, this treatment reduced total weed seed production 88% compared to the nontreated control. Flumioxazin PRE fb lactofen plus clethodim EPOST fb acetochlor MPOST provided similar weed control and peanut yield as flumioxazin PRE fb lactofen plus clethodim MPOST. This treatment provided 88 to 100% control of all weed species present and reduced total weed seed production 93%. Sequential applications of PRE, EPOST, and/or MPOST herbicide treatments provided the best season-long control of weeds and weed seed suppression in Mississippi peanut.

A robust ecosystem requires a functionally heterogeneous community of organisms with a wide range of traits that permits broad resource partitioning. Understanding community diversity patterns can help investigate drivers of community assembly and how different metrics reflect the success of restoration in grassland or weed control in cropland. The objectives of my study were to identify assembly drivers influencing community taxonomic, phylogenetic, and functional diversity. The first study examined the effect of different ecotypes of dominant species on grassland community diversity along a spatial aridity gradient during restoration. This study showed that ecotype significantly affected species richness and shaped taxonomic, phylogenetic, and functional diversity. Accordingly, restorations should consider ecotypic variation as a critical biological filter to community assembly in grassland ecosystems. Given the community response across the tallgrass prairie, restoration practitioners should draw attention to regional sources of dominant species because ideal ecotypic sources can affect species richness and even sustain the phylogenetic and functional patterns. The restoration efficacy of existing ecosystems should be evaluated to large-scale diversity patterns to detect gaps and limitations that will reveal which diversity components to highlight for further restoration investment. The second study investigated temporal variations in diversity metrics among dominant species ecotypes and a drought treatment on the importance of external and internal filters in shaping the assembly of grassland communities. In this study, species richness decreased significantly during the early stages of restoration while phylogenetic and functional diversity was maintained over eight years. I also found no significant effect of experimental drought treatment on community biodiversity. Moreover, ecotypic variation as an internal filter played a key role in grassland assembly but the external filter was less strong because of high trait overlap among species within a community. In general, this study highlighted the consequence of integrating both interspecific and intraspecific trait variabilities and the value of concentrating on functional traits to comprehend better how trait variability is coupled with species coexistence. Future investigations are necessary to examine the distinctive origins of variability in plant traits and how they contribute to grassland community assembly. The third study focused on whether weed management tactics such as a glyphosate-resistant (GR) cropping system were beneficial to control weed diversity in the soil seedbank of the agroecosystem. Both phylogenetic and functional diversity of the soil seedbank was relatively stable with different GR cropping systems across six years. The neutral assembly of the soil seedbank may imply that the belowground weed community could be restrained by stochastic mechanisms, such as dispersal and demographic stochasticity of seeds, during agricultural activities. Therefore, I recommend integrated weed management with a sustainable perspective to fight against the evolutionary feedback due to weed herbicide resistance. While the GR cropping system still seems beneficial, future weed control cannot overlook the extensive impact of GR systems on biodiversity variations, the shifts in weed composition, and the resistance evolution of weed species to herbicides in the agroecosystem.

<p>  </p> <p>Annual bluegrass (<em>Poa annua</em> L.) is the most troublesome weed in turfgrass systems and the second most troublesome weed across all grass crops. Controlling annual bluegrass is exceptionally complicated due to its high genetic adaptability to new environments. Additionally, prolific seed production allowed the rapid development of herbicide resistance to 12 herbicide modes of action. Experiments were initiated with the goal to better understand annual bluegrass ecology and resistance to ethofumesate. A dose-response experiment was initiated in 2022 to determine the potential level of ethofumesate resistance in annual bluegrass collected from seed production systems. Seed from 55 annual bluegrass populations was obtained from three sources: seed production fields (31 populations), seed cleaning process (6 populations), and seed testing prior to retail distribution (18 populations). </p> <p>Individual seedlings (2–3 tillers) were treated with ten doses of ethofumesate: 0, 0.6, 1.1, 2.8, 5.6, 8.4, 11.2, 16.8, 22.4, and 44.8 kg ai ha−1; with 1.1 to 2.2 kg ha−1 as the label application rates for perennial ryegrass (<em>Lolium perenne</em> L.). The resistance to susceptible ratio of populations across all sources ranged from 0.48 to 5.48. The most resistant populations from production fields, removed during the seed cleaning process, or found in seed testing lots had ED50 values of 12.1, 13.1, and 9.4 kg ai ha−1, respectively. Further, 68% of the populations found in production fields had ED50 higher than 6 kg ai ha−1, which indicates that annual bluegrass resistance is common in grass seed production. A garden study was initiated in November 2020 to assess the development, reproduction, and survival of ten annual bluegrass populations in Indiana. Annual bluegrass plants were maintained in the absence of turf competition and not subjected to typical turfgrass management practices including irrigation, mowing and fertilization. Data collected in included growth rate, biomass production, ground cover, morphology, flowering time, seed production and morphology, and both winter survival and subsequent summer survival of plants. Principal component analysis indicated that certain populations grouped together based on their development, morphology, stress tolerance, and seed production. Plants from the cooler climates (OR, PA, and IN) were characterized by higher growth rates and biomass compared to southern ecotypes. These three populations survived the longest during the summer, with the PA population averaging the highest ground cover of 276 cm2 on 23 July 2021. Plants from warm climates (AL, FL, NC, SC, TN, TX) had poor summer survival. Additionally, the FL population had the highest winterkill of 68%, followed by TX at 45%. The NJ population was distinct from other populations, and plants had robust aboveground biomass and high seed production. The results indicate that the development, reproduction, and survival of different annual bluegrass biotypes are dependent on the climate of origin. A third experiment was designed to understand patterns of germination and seed longevity in populations from five climates across the U.S. at two depths of burial. Seed was retrieved in 6-month intervals up to 24 months. Seed viability by depth (surface vs. 5-cm deep) of burial differed only 18 months after the initiation of the study. However, seed viability did differ among populations on each date of seed retrieval. Viability was low ranging from 0.21 to 0.91%, and populations originating from cool climates (New Jersey, Pennsylvania, and Oregon) generally had higher viability than populations originating from warmer climates. Annual bluegrass seed tested in this study typically had low levels of survival (<0.5%); however, all populations retained some level of viability 24 months after burial, which would allow future reproduction of this troublesome weed. Overall, this research determined that herbicides alone will likely be ineffective at controlling annual bluegrass and that knowledge of the development, reproduction, and survival of local annual bluegrass populations should be factored into an integrated weed management strategies created for each site. </p> <p>  </p>