Preparing Florida Pasture for Grassland Restoration : Seedling Establishment after Herbiciding and Tilling

ABSTRACT Nonnative pasture grasses established for agriculture and livestock husbandry have replaced countless acres of natural habitat in the last century of Florida history. Many endemic species, such as cutthroat grass (Coleataenia abscissa), are now endangered and may not return to areas until t...

Ausführliche Beschreibung

Bibliographische Detailangaben
Veröffentlicht in:Natural Areas Journal. - Natural Areas Association. - 37(2017), 1, Seite 39-48
1. Verfasser: Tucker, Rebecca C. (VerfasserIn)
Weitere Verfasser: Rothermel, Betsie B., Daskin, Joshua H.
Format: Online-Aufsatz
Sprache:English
Veröffentlicht: 2017
Zugriff auf das übergeordnete Werk:Natural Areas Journal
Schlagworte:bahiagrass habitat restoration pasture seed bank tilling
LEADER 01000caa a22002652c 4500
001 JST134485580
003 DE-627
005 20240625175106.0
007 cr uuu---uuuuu
008 230311s2017 xx |||||o 00| ||eng c
035 |a (DE-627)JST134485580 
035 |a (JST)90009253 
040 |a DE-627  |b ger  |c DE-627  |e rakwb 
041 |a eng 
100 1 |a Tucker, Rebecca C.  |e verfasserin  |4 aut 
245 1 0 |a Preparing Florida Pasture for Grassland Restoration  |b Seedling Establishment after Herbiciding and Tilling 
264 1 |c 2017 
336 |a Text  |b txt  |2 rdacontent 
337 |a Computermedien  |b c  |2 rdamedia 
338 |a Online-Ressource  |b cr  |2 rdacarrier 
520 |a ABSTRACT Nonnative pasture grasses established for agriculture and livestock husbandry have replaced countless acres of natural habitat in the last century of Florida history. Many endemic species, such as cutthroat grass (Coleataenia abscissa), are now endangered and may not return to areas until the dominant pasture grass has been removed. To determine the best strategy for native revegetation, we examined the effects of two soil preparations (tilling and no tilling) in pasture plots dominated by bahiagrass (Paspalum notatum) on the Archbold Reserve in south-central Florida. In preparation for the experiment, the No-Till and Till plots were first herbicided with glyphosate and burned to remove bahiagrass cover and expose the seed bank, then the Till plots were disked to a depth of 5–10 cm. Reference plots were left undisturbed to provide a pre-restoration baseline. The pre-tilling herbicide application and burn reduced bahiagrass cover in experimental plots to an average of 24% compared to 80% in reference plots. In the first year following tilling, overall plant community composition differed between tillage treatments, with 52 and 38 plant taxa found in the No-Till and Till plots, respectively, compared to only 14 in the reference plots. Importantly, native species richness was significantly higher in the No-Till treatment, and tilling resulted in minimal reduction of cover of bahiagrass and other exotic grasses. Seedling species composition differed among experimental blocks, suggesting soil moisture or other local abiotic conditions may significantly influence seedling establishment and restoration outcomes regardless of mechanical soil preparations. 
650 4 |a bahiagrass 
650 4 |a habitat restoration 
650 4 |a pasture 
650 4 |a seed bank 
650 4 |a tilling 
655 4 |a research-article 
700 1 |a Rothermel, Betsie B.  |e verfasserin  |4 aut 
700 1 |a Daskin, Joshua H.  |e verfasserin  |4 aut 
773 0 8 |i Enthalten in  |t Natural Areas Journal  |d Natural Areas Association  |g 37(2017), 1, Seite 39-48  |w (DE-627)594779146  |w (DE-600)2486532-1  |x 21624399  |7 nnas 
773 1 8 |g volume:37  |g year:2017  |g number:1  |g pages:39-48 
856 4 0 |u https://www.jstor.org/stable/90009253  |3 Volltext 
912 |a GBV_USEFLAG_A 
912 |a SYSFLAG_A 
912 |a GBV_JST 
912 |a GBV_ILN_11 
912 |a GBV_ILN_20 
912 |a GBV_ILN_22 
912 |a GBV_ILN_24 
912 |a GBV_ILN_31 
912 |a GBV_ILN_39 
912 |a GBV_ILN_40 
912 |a GBV_ILN_60 
912 |a GBV_ILN_62 
912 |a GBV_ILN_63 
912 |a GBV_ILN_65 
912 |a GBV_ILN_69 
912 |a GBV_ILN_70 
912 |a GBV_ILN_73 
912 |a GBV_ILN_100 
912 |a GBV_ILN_101 
912 |a GBV_ILN_110 
912 |a GBV_ILN_120 
912 |a GBV_ILN_285 
912 |a GBV_ILN_374 
912 |a GBV_ILN_702 
912 |a GBV_ILN_2001 
912 |a GBV_ILN_2003 
912 |a GBV_ILN_2005 
912 |a GBV_ILN_2006 
912 |a GBV_ILN_2007 
912 |a GBV_ILN_2008 
912 |a GBV_ILN_2009 
912 |a GBV_ILN_2010 
912 |a GBV_ILN_2014 
912 |a GBV_ILN_2015 
912 |a GBV_ILN_2018 
912 |a GBV_ILN_2020 
912 |a GBV_ILN_2021 
912 |a GBV_ILN_2026 
912 |a GBV_ILN_2044 
912 |a GBV_ILN_2050 
912 |a GBV_ILN_2056 
912 |a GBV_ILN_2107 
912 |a GBV_ILN_2190 
912 |a GBV_ILN_2949 
912 |a GBV_ILN_2950 
912 |a GBV_ILN_4012 
912 |a GBV_ILN_4027 
912 |a GBV_ILN_4028 
912 |a GBV_ILN_4035 
912 |a GBV_ILN_4037 
912 |a GBV_ILN_4046 
912 |a GBV_ILN_4112 
912 |a GBV_ILN_4125 
912 |a GBV_ILN_4242 
912 |a GBV_ILN_4305 
912 |a GBV_ILN_4307 
912 |a GBV_ILN_4309 
912 |a GBV_ILN_4310 
912 |a GBV_ILN_4314 
912 |a GBV_ILN_4316 
912 |a GBV_ILN_4317 
912 |a GBV_ILN_4319 
912 |a GBV_ILN_4323 
912 |a GBV_ILN_4325 
912 |a GBV_ILN_4335 
912 |a GBV_ILN_4346 
912 |a GBV_ILN_4393 
951 |a AR 
952 |d 37  |j 2017  |e 1  |h 39-48