The long-term effect of initial restoration intervention, landscape composition, and time on the progress of Pannonic sand grassland restoration

Abstract To help upscale ecological restoration of degraded lands, landscape factors and longer time scales should be considered when assessing restoration efforts. We evaluated the impact of initial restoration intervention, landscape composition, and elapsed time since the restoration began on the...
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Autor*in:	Reis, Bruna Paolinelli [verfasserIn] Szitár, Katalin Kövendi-Jakó, Anna Török, Katalin Sáradi, Nóra Csákvári, Edina Halassy, Melinda

Format:	E-Artikel
Sprache:	Englisch

Erschienen:	2022

Schlagwörter:	Long-term monitoring Seeding Mowing Carbon amendment Invasion Vegetation recovery

Anmerkung:	© The Author(s) 2022

Übergeordnetes Werk:	Enthalten in: Landscape and ecological engineering - Tokyo [u.a.] : Springer, 2005, 18(2022), 4 vom: 08. Juni, Seite 429-440
Übergeordnetes Werk:	volume:18 ; year:2022 ; number:4 ; day:08 ; month:06 ; pages:429-440

Links:	Volltext

DOI / URN:	10.1007/s11355-022-00512-y

Katalog-ID:	SPR048211729

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100	1		\|a Reis, Bruna Paolinelli \|e verfasserin \|0 (orcid)0000-0001-6431-1906 \|4 aut
245	1	4	\|a The long-term effect of initial restoration intervention, landscape composition, and time on the progress of Pannonic sand grassland restoration
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520			\|a Abstract To help upscale ecological restoration of degraded lands, landscape factors and longer time scales should be considered when assessing restoration efforts. We evaluated the impact of initial restoration intervention, landscape composition, and elapsed time since the restoration began on the long-term progress of Pannonic sand grassland restoration. Treatments (seeding, mowing, and carbon amendment) were implemented for 6–7 years and monitoring lasted up to 23 years after the first treatment applications in eight experimental blocks belonging to three field experiments. The abundance of target/neophyte species, and distance from primary grasslands and plantations (as major source of target/neophyte species) were estimated in 500 m landscape buffers around each block to characterize landscape composition. Restoration progress was calculated as the difference between the relative cover of target/neophyte species in treatment and control plots. Restoration intervention and neophyte abundance in the landscape had a significant effect on the restoration progress, but time did not. Seeding had the highest positive effect on target species and also prevented invasion by neophyte species. Higher abundance of neophytes in the landscape and the proximity to plantations increased the cover of neophytes in treatment plots. We conclude that restoration interventions may have a greater impact on restoration progress in the longer term than landscape factors or elapsed time. Seeding proved to be the best method in restoring sand grasslands by both favoring target species and controlling invasion. From the landscape factors, the abundance of neophyte species and distance to plantations should be considered when prioritizing areas and efforts for restoration.
650		4	\|a Long-term monitoring \|7 (dpeaa)DE-He213
650		4	\|a Seeding \|7 (dpeaa)DE-He213
650		4	\|a Mowing \|7 (dpeaa)DE-He213
650		4	\|a Carbon amendment \|7 (dpeaa)DE-He213
650		4	\|a Invasion \|7 (dpeaa)DE-He213
650		4	\|a Vegetation recovery \|7 (dpeaa)DE-He213
700	1		\|a Szitár, Katalin \|0 (orcid)0000-0002-8810-540X \|4 aut
700	1		\|a Kövendi-Jakó, Anna \|0 (orcid)0000-0001-7081-6548 \|4 aut
700	1		\|a Török, Katalin \|0 (orcid)0000-0002-5910-7027 \|4 aut
700	1		\|a Sáradi, Nóra \|4 aut
700	1		\|a Csákvári, Edina \|0 (orcid)0000-0002-1089-7603 \|4 aut
700	1		\|a Halassy, Melinda \|0 (orcid)0000-0001-8523-3169 \|4 aut
773	0	8	\|i Enthalten in \|t Landscape and ecological engineering \|d Tokyo [u.a.] : Springer, 2005 \|g 18(2022), 4 vom: 08. Juni, Seite 429-440 \|w (DE-627)482837772 \|w (DE-600)2182123-9 \|x 1860-188X \|7 nnns
773	1	8	\|g volume:18 \|g year:2022 \|g number:4 \|g day:08 \|g month:06 \|g pages:429-440
856	4	0	\|u https://dx.doi.org/10.1007/s11355-022-00512-y \|z kostenfrei \|3 Volltext
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912			\|a GBV_ILN_65
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912			\|a GBV_ILN_95
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912			\|a GBV_ILN_101
912			\|a GBV_ILN_105
912			\|a GBV_ILN_110
912			\|a GBV_ILN_120
912			\|a GBV_ILN_138
912			\|a GBV_ILN_150
912			\|a GBV_ILN_151
912			\|a GBV_ILN_152
912			\|a GBV_ILN_161
912			\|a GBV_ILN_170
912			\|a GBV_ILN_171
912			\|a GBV_ILN_187
912			\|a GBV_ILN_213
912			\|a GBV_ILN_224
912			\|a GBV_ILN_230
912			\|a GBV_ILN_250
912			\|a GBV_ILN_281
912			\|a GBV_ILN_285
912			\|a GBV_ILN_293
912			\|a GBV_ILN_370
912			\|a GBV_ILN_602
912			\|a GBV_ILN_636
912			\|a GBV_ILN_702
912			\|a GBV_ILN_2001
912			\|a GBV_ILN_2003
912			\|a GBV_ILN_2004
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_2011
912			\|a GBV_ILN_2014
912			\|a GBV_ILN_2015
912			\|a GBV_ILN_2020
912			\|a GBV_ILN_2021
912			\|a GBV_ILN_2025
912			\|a GBV_ILN_2026
912			\|a GBV_ILN_2027
912			\|a GBV_ILN_2031
912			\|a GBV_ILN_2034
912			\|a GBV_ILN_2037
912			\|a GBV_ILN_2038
912			\|a GBV_ILN_2039
912			\|a GBV_ILN_2044
912			\|a GBV_ILN_2048
912			\|a GBV_ILN_2049
912			\|a GBV_ILN_2050
912			\|a GBV_ILN_2055
912			\|a GBV_ILN_2056
912			\|a GBV_ILN_2057
912			\|a GBV_ILN_2059
912			\|a GBV_ILN_2061
912			\|a GBV_ILN_2064
912			\|a GBV_ILN_2065
912			\|a GBV_ILN_2068
912			\|a GBV_ILN_2088
912			\|a GBV_ILN_2093
912			\|a GBV_ILN_2106
912			\|a GBV_ILN_2107
912			\|a GBV_ILN_2108
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912			\|a GBV_ILN_4333
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952			\|d 18 \|j 2022 \|e 4 \|b 08 \|c 06 \|h 429-440

Indexfelder

author_variant	b p r bp bpr k s ks a k j akj k t kt n s ns e c ec m h mh
matchkey_str	article:1860188X:2022----::hlntrefcoiiiletrtoitretolnsaeopstoadienhporso
hierarchy_sort_str	2022
publishDate	2022
allfields	10.1007/s11355-022-00512-y doi (DE-627)SPR048211729 (SPR)s11355-022-00512-y-e DE-627 ger DE-627 rakwb eng Reis, Bruna Paolinelli verfasserin (orcid)0000-0001-6431-1906 aut The long-term effect of initial restoration intervention, landscape composition, and time on the progress of Pannonic sand grassland restoration 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s) 2022 Abstract To help upscale ecological restoration of degraded lands, landscape factors and longer time scales should be considered when assessing restoration efforts. We evaluated the impact of initial restoration intervention, landscape composition, and elapsed time since the restoration began on the long-term progress of Pannonic sand grassland restoration. Treatments (seeding, mowing, and carbon amendment) were implemented for 6–7 years and monitoring lasted up to 23 years after the first treatment applications in eight experimental blocks belonging to three field experiments. The abundance of target/neophyte species, and distance from primary grasslands and plantations (as major source of target/neophyte species) were estimated in 500 m landscape buffers around each block to characterize landscape composition. Restoration progress was calculated as the difference between the relative cover of target/neophyte species in treatment and control plots. Restoration intervention and neophyte abundance in the landscape had a significant effect on the restoration progress, but time did not. Seeding had the highest positive effect on target species and also prevented invasion by neophyte species. Higher abundance of neophytes in the landscape and the proximity to plantations increased the cover of neophytes in treatment plots. We conclude that restoration interventions may have a greater impact on restoration progress in the longer term than landscape factors or elapsed time. Seeding proved to be the best method in restoring sand grasslands by both favoring target species and controlling invasion. From the landscape factors, the abundance of neophyte species and distance to plantations should be considered when prioritizing areas and efforts for restoration. Long-term monitoring (dpeaa)DE-He213 Seeding (dpeaa)DE-He213 Mowing (dpeaa)DE-He213 Carbon amendment (dpeaa)DE-He213 Invasion (dpeaa)DE-He213 Vegetation recovery (dpeaa)DE-He213 Szitár, Katalin (orcid)0000-0002-8810-540X aut Kövendi-Jakó, Anna (orcid)0000-0001-7081-6548 aut Török, Katalin (orcid)0000-0002-5910-7027 aut Sáradi, Nóra aut Csákvári, Edina (orcid)0000-0002-1089-7603 aut Halassy, Melinda (orcid)0000-0001-8523-3169 aut Enthalten in Landscape and ecological engineering Tokyo [u.a.] : Springer, 2005 18(2022), 4 vom: 08. Juni, Seite 429-440 (DE-627)482837772 (DE-600)2182123-9 1860-188X nnns volume:18 year:2022 number:4 day:08 month:06 pages:429-440 https://dx.doi.org/10.1007/s11355-022-00512-y kostenfrei Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 18 2022 4 08 06 429-440
spelling	10.1007/s11355-022-00512-y doi (DE-627)SPR048211729 (SPR)s11355-022-00512-y-e DE-627 ger DE-627 rakwb eng Reis, Bruna Paolinelli verfasserin (orcid)0000-0001-6431-1906 aut The long-term effect of initial restoration intervention, landscape composition, and time on the progress of Pannonic sand grassland restoration 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s) 2022 Abstract To help upscale ecological restoration of degraded lands, landscape factors and longer time scales should be considered when assessing restoration efforts. We evaluated the impact of initial restoration intervention, landscape composition, and elapsed time since the restoration began on the long-term progress of Pannonic sand grassland restoration. Treatments (seeding, mowing, and carbon amendment) were implemented for 6–7 years and monitoring lasted up to 23 years after the first treatment applications in eight experimental blocks belonging to three field experiments. The abundance of target/neophyte species, and distance from primary grasslands and plantations (as major source of target/neophyte species) were estimated in 500 m landscape buffers around each block to characterize landscape composition. Restoration progress was calculated as the difference between the relative cover of target/neophyte species in treatment and control plots. Restoration intervention and neophyte abundance in the landscape had a significant effect on the restoration progress, but time did not. Seeding had the highest positive effect on target species and also prevented invasion by neophyte species. Higher abundance of neophytes in the landscape and the proximity to plantations increased the cover of neophytes in treatment plots. We conclude that restoration interventions may have a greater impact on restoration progress in the longer term than landscape factors or elapsed time. Seeding proved to be the best method in restoring sand grasslands by both favoring target species and controlling invasion. From the landscape factors, the abundance of neophyte species and distance to plantations should be considered when prioritizing areas and efforts for restoration. Long-term monitoring (dpeaa)DE-He213 Seeding (dpeaa)DE-He213 Mowing (dpeaa)DE-He213 Carbon amendment (dpeaa)DE-He213 Invasion (dpeaa)DE-He213 Vegetation recovery (dpeaa)DE-He213 Szitár, Katalin (orcid)0000-0002-8810-540X aut Kövendi-Jakó, Anna (orcid)0000-0001-7081-6548 aut Török, Katalin (orcid)0000-0002-5910-7027 aut Sáradi, Nóra aut Csákvári, Edina (orcid)0000-0002-1089-7603 aut Halassy, Melinda (orcid)0000-0001-8523-3169 aut Enthalten in Landscape and ecological engineering Tokyo [u.a.] : Springer, 2005 18(2022), 4 vom: 08. Juni, Seite 429-440 (DE-627)482837772 (DE-600)2182123-9 1860-188X nnns volume:18 year:2022 number:4 day:08 month:06 pages:429-440 https://dx.doi.org/10.1007/s11355-022-00512-y kostenfrei Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 18 2022 4 08 06 429-440
allfields_unstemmed	10.1007/s11355-022-00512-y doi (DE-627)SPR048211729 (SPR)s11355-022-00512-y-e DE-627 ger DE-627 rakwb eng Reis, Bruna Paolinelli verfasserin (orcid)0000-0001-6431-1906 aut The long-term effect of initial restoration intervention, landscape composition, and time on the progress of Pannonic sand grassland restoration 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s) 2022 Abstract To help upscale ecological restoration of degraded lands, landscape factors and longer time scales should be considered when assessing restoration efforts. We evaluated the impact of initial restoration intervention, landscape composition, and elapsed time since the restoration began on the long-term progress of Pannonic sand grassland restoration. Treatments (seeding, mowing, and carbon amendment) were implemented for 6–7 years and monitoring lasted up to 23 years after the first treatment applications in eight experimental blocks belonging to three field experiments. The abundance of target/neophyte species, and distance from primary grasslands and plantations (as major source of target/neophyte species) were estimated in 500 m landscape buffers around each block to characterize landscape composition. Restoration progress was calculated as the difference between the relative cover of target/neophyte species in treatment and control plots. Restoration intervention and neophyte abundance in the landscape had a significant effect on the restoration progress, but time did not. Seeding had the highest positive effect on target species and also prevented invasion by neophyte species. Higher abundance of neophytes in the landscape and the proximity to plantations increased the cover of neophytes in treatment plots. We conclude that restoration interventions may have a greater impact on restoration progress in the longer term than landscape factors or elapsed time. Seeding proved to be the best method in restoring sand grasslands by both favoring target species and controlling invasion. From the landscape factors, the abundance of neophyte species and distance to plantations should be considered when prioritizing areas and efforts for restoration. Long-term monitoring (dpeaa)DE-He213 Seeding (dpeaa)DE-He213 Mowing (dpeaa)DE-He213 Carbon amendment (dpeaa)DE-He213 Invasion (dpeaa)DE-He213 Vegetation recovery (dpeaa)DE-He213 Szitár, Katalin (orcid)0000-0002-8810-540X aut Kövendi-Jakó, Anna (orcid)0000-0001-7081-6548 aut Török, Katalin (orcid)0000-0002-5910-7027 aut Sáradi, Nóra aut Csákvári, Edina (orcid)0000-0002-1089-7603 aut Halassy, Melinda (orcid)0000-0001-8523-3169 aut Enthalten in Landscape and ecological engineering Tokyo [u.a.] : Springer, 2005 18(2022), 4 vom: 08. Juni, Seite 429-440 (DE-627)482837772 (DE-600)2182123-9 1860-188X nnns volume:18 year:2022 number:4 day:08 month:06 pages:429-440 https://dx.doi.org/10.1007/s11355-022-00512-y kostenfrei Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 18 2022 4 08 06 429-440
allfieldsGer	10.1007/s11355-022-00512-y doi (DE-627)SPR048211729 (SPR)s11355-022-00512-y-e DE-627 ger DE-627 rakwb eng Reis, Bruna Paolinelli verfasserin (orcid)0000-0001-6431-1906 aut The long-term effect of initial restoration intervention, landscape composition, and time on the progress of Pannonic sand grassland restoration 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s) 2022 Abstract To help upscale ecological restoration of degraded lands, landscape factors and longer time scales should be considered when assessing restoration efforts. We evaluated the impact of initial restoration intervention, landscape composition, and elapsed time since the restoration began on the long-term progress of Pannonic sand grassland restoration. Treatments (seeding, mowing, and carbon amendment) were implemented for 6–7 years and monitoring lasted up to 23 years after the first treatment applications in eight experimental blocks belonging to three field experiments. The abundance of target/neophyte species, and distance from primary grasslands and plantations (as major source of target/neophyte species) were estimated in 500 m landscape buffers around each block to characterize landscape composition. Restoration progress was calculated as the difference between the relative cover of target/neophyte species in treatment and control plots. Restoration intervention and neophyte abundance in the landscape had a significant effect on the restoration progress, but time did not. Seeding had the highest positive effect on target species and also prevented invasion by neophyte species. Higher abundance of neophytes in the landscape and the proximity to plantations increased the cover of neophytes in treatment plots. We conclude that restoration interventions may have a greater impact on restoration progress in the longer term than landscape factors or elapsed time. Seeding proved to be the best method in restoring sand grasslands by both favoring target species and controlling invasion. From the landscape factors, the abundance of neophyte species and distance to plantations should be considered when prioritizing areas and efforts for restoration. Long-term monitoring (dpeaa)DE-He213 Seeding (dpeaa)DE-He213 Mowing (dpeaa)DE-He213 Carbon amendment (dpeaa)DE-He213 Invasion (dpeaa)DE-He213 Vegetation recovery (dpeaa)DE-He213 Szitár, Katalin (orcid)0000-0002-8810-540X aut Kövendi-Jakó, Anna (orcid)0000-0001-7081-6548 aut Török, Katalin (orcid)0000-0002-5910-7027 aut Sáradi, Nóra aut Csákvári, Edina (orcid)0000-0002-1089-7603 aut Halassy, Melinda (orcid)0000-0001-8523-3169 aut Enthalten in Landscape and ecological engineering Tokyo [u.a.] : Springer, 2005 18(2022), 4 vom: 08. Juni, Seite 429-440 (DE-627)482837772 (DE-600)2182123-9 1860-188X nnns volume:18 year:2022 number:4 day:08 month:06 pages:429-440 https://dx.doi.org/10.1007/s11355-022-00512-y kostenfrei Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 18 2022 4 08 06 429-440
allfieldsSound	10.1007/s11355-022-00512-y doi (DE-627)SPR048211729 (SPR)s11355-022-00512-y-e DE-627 ger DE-627 rakwb eng Reis, Bruna Paolinelli verfasserin (orcid)0000-0001-6431-1906 aut The long-term effect of initial restoration intervention, landscape composition, and time on the progress of Pannonic sand grassland restoration 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s) 2022 Abstract To help upscale ecological restoration of degraded lands, landscape factors and longer time scales should be considered when assessing restoration efforts. We evaluated the impact of initial restoration intervention, landscape composition, and elapsed time since the restoration began on the long-term progress of Pannonic sand grassland restoration. Treatments (seeding, mowing, and carbon amendment) were implemented for 6–7 years and monitoring lasted up to 23 years after the first treatment applications in eight experimental blocks belonging to three field experiments. The abundance of target/neophyte species, and distance from primary grasslands and plantations (as major source of target/neophyte species) were estimated in 500 m landscape buffers around each block to characterize landscape composition. Restoration progress was calculated as the difference between the relative cover of target/neophyte species in treatment and control plots. Restoration intervention and neophyte abundance in the landscape had a significant effect on the restoration progress, but time did not. Seeding had the highest positive effect on target species and also prevented invasion by neophyte species. Higher abundance of neophytes in the landscape and the proximity to plantations increased the cover of neophytes in treatment plots. We conclude that restoration interventions may have a greater impact on restoration progress in the longer term than landscape factors or elapsed time. Seeding proved to be the best method in restoring sand grasslands by both favoring target species and controlling invasion. From the landscape factors, the abundance of neophyte species and distance to plantations should be considered when prioritizing areas and efforts for restoration. Long-term monitoring (dpeaa)DE-He213 Seeding (dpeaa)DE-He213 Mowing (dpeaa)DE-He213 Carbon amendment (dpeaa)DE-He213 Invasion (dpeaa)DE-He213 Vegetation recovery (dpeaa)DE-He213 Szitár, Katalin (orcid)0000-0002-8810-540X aut Kövendi-Jakó, Anna (orcid)0000-0001-7081-6548 aut Török, Katalin (orcid)0000-0002-5910-7027 aut Sáradi, Nóra aut Csákvári, Edina (orcid)0000-0002-1089-7603 aut Halassy, Melinda (orcid)0000-0001-8523-3169 aut Enthalten in Landscape and ecological engineering Tokyo [u.a.] : Springer, 2005 18(2022), 4 vom: 08. Juni, Seite 429-440 (DE-627)482837772 (DE-600)2182123-9 1860-188X nnns volume:18 year:2022 number:4 day:08 month:06 pages:429-440 https://dx.doi.org/10.1007/s11355-022-00512-y kostenfrei Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 18 2022 4 08 06 429-440
language	English
source	Enthalten in Landscape and ecological engineering 18(2022), 4 vom: 08. Juni, Seite 429-440 volume:18 year:2022 number:4 day:08 month:06 pages:429-440
sourceStr	Enthalten in Landscape and ecological engineering 18(2022), 4 vom: 08. Juni, Seite 429-440 volume:18 year:2022 number:4 day:08 month:06 pages:429-440
format_phy_str_mv	Article
institution	findex.gbv.de
topic_facet	Long-term monitoring Seeding Mowing Carbon amendment Invasion Vegetation recovery
isfreeaccess_bool	true
container_title	Landscape and ecological engineering
authorswithroles_txt_mv	Reis, Bruna Paolinelli @@aut@@ Szitár, Katalin @@aut@@ Kövendi-Jakó, Anna @@aut@@ Török, Katalin @@aut@@ Sáradi, Nóra @@aut@@ Csákvári, Edina @@aut@@ Halassy, Melinda @@aut@@
publishDateDaySort_date	2022-06-08T00:00:00Z
hierarchy_top_id	482837772
id	SPR048211729
language_de	englisch
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author	Reis, Bruna Paolinelli
spellingShingle	Reis, Bruna Paolinelli misc Long-term monitoring misc Seeding misc Mowing misc Carbon amendment misc Invasion misc Vegetation recovery The long-term effect of initial restoration intervention, landscape composition, and time on the progress of Pannonic sand grassland restoration
authorStr	Reis, Bruna Paolinelli
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topic_title	The long-term effect of initial restoration intervention, landscape composition, and time on the progress of Pannonic sand grassland restoration Long-term monitoring (dpeaa)DE-He213 Seeding (dpeaa)DE-He213 Mowing (dpeaa)DE-He213 Carbon amendment (dpeaa)DE-He213 Invasion (dpeaa)DE-He213 Vegetation recovery (dpeaa)DE-He213
topic	misc Long-term monitoring misc Seeding misc Mowing misc Carbon amendment misc Invasion misc Vegetation recovery
topic_unstemmed	misc Long-term monitoring misc Seeding misc Mowing misc Carbon amendment misc Invasion misc Vegetation recovery
topic_browse	misc Long-term monitoring misc Seeding misc Mowing misc Carbon amendment misc Invasion misc Vegetation recovery
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title	The long-term effect of initial restoration intervention, landscape composition, and time on the progress of Pannonic sand grassland restoration
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title_full	The long-term effect of initial restoration intervention, landscape composition, and time on the progress of Pannonic sand grassland restoration
author_sort	Reis, Bruna Paolinelli
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author_browse	Reis, Bruna Paolinelli Szitár, Katalin Kövendi-Jakó, Anna Török, Katalin Sáradi, Nóra Csákvári, Edina Halassy, Melinda
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author-letter	Reis, Bruna Paolinelli
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title_sort	long-term effect of initial restoration intervention, landscape composition, and time on the progress of pannonic sand grassland restoration
title_auth	The long-term effect of initial restoration intervention, landscape composition, and time on the progress of Pannonic sand grassland restoration
abstract	Abstract To help upscale ecological restoration of degraded lands, landscape factors and longer time scales should be considered when assessing restoration efforts. We evaluated the impact of initial restoration intervention, landscape composition, and elapsed time since the restoration began on the long-term progress of Pannonic sand grassland restoration. Treatments (seeding, mowing, and carbon amendment) were implemented for 6–7 years and monitoring lasted up to 23 years after the first treatment applications in eight experimental blocks belonging to three field experiments. The abundance of target/neophyte species, and distance from primary grasslands and plantations (as major source of target/neophyte species) were estimated in 500 m landscape buffers around each block to characterize landscape composition. Restoration progress was calculated as the difference between the relative cover of target/neophyte species in treatment and control plots. Restoration intervention and neophyte abundance in the landscape had a significant effect on the restoration progress, but time did not. Seeding had the highest positive effect on target species and also prevented invasion by neophyte species. Higher abundance of neophytes in the landscape and the proximity to plantations increased the cover of neophytes in treatment plots. We conclude that restoration interventions may have a greater impact on restoration progress in the longer term than landscape factors or elapsed time. Seeding proved to be the best method in restoring sand grasslands by both favoring target species and controlling invasion. From the landscape factors, the abundance of neophyte species and distance to plantations should be considered when prioritizing areas and efforts for restoration. © The Author(s) 2022
abstractGer	Abstract To help upscale ecological restoration of degraded lands, landscape factors and longer time scales should be considered when assessing restoration efforts. We evaluated the impact of initial restoration intervention, landscape composition, and elapsed time since the restoration began on the long-term progress of Pannonic sand grassland restoration. Treatments (seeding, mowing, and carbon amendment) were implemented for 6–7 years and monitoring lasted up to 23 years after the first treatment applications in eight experimental blocks belonging to three field experiments. The abundance of target/neophyte species, and distance from primary grasslands and plantations (as major source of target/neophyte species) were estimated in 500 m landscape buffers around each block to characterize landscape composition. Restoration progress was calculated as the difference between the relative cover of target/neophyte species in treatment and control plots. Restoration intervention and neophyte abundance in the landscape had a significant effect on the restoration progress, but time did not. Seeding had the highest positive effect on target species and also prevented invasion by neophyte species. Higher abundance of neophytes in the landscape and the proximity to plantations increased the cover of neophytes in treatment plots. We conclude that restoration interventions may have a greater impact on restoration progress in the longer term than landscape factors or elapsed time. Seeding proved to be the best method in restoring sand grasslands by both favoring target species and controlling invasion. From the landscape factors, the abundance of neophyte species and distance to plantations should be considered when prioritizing areas and efforts for restoration. © The Author(s) 2022
abstract_unstemmed	Abstract To help upscale ecological restoration of degraded lands, landscape factors and longer time scales should be considered when assessing restoration efforts. We evaluated the impact of initial restoration intervention, landscape composition, and elapsed time since the restoration began on the long-term progress of Pannonic sand grassland restoration. Treatments (seeding, mowing, and carbon amendment) were implemented for 6–7 years and monitoring lasted up to 23 years after the first treatment applications in eight experimental blocks belonging to three field experiments. The abundance of target/neophyte species, and distance from primary grasslands and plantations (as major source of target/neophyte species) were estimated in 500 m landscape buffers around each block to characterize landscape composition. Restoration progress was calculated as the difference between the relative cover of target/neophyte species in treatment and control plots. Restoration intervention and neophyte abundance in the landscape had a significant effect on the restoration progress, but time did not. Seeding had the highest positive effect on target species and also prevented invasion by neophyte species. Higher abundance of neophytes in the landscape and the proximity to plantations increased the cover of neophytes in treatment plots. We conclude that restoration interventions may have a greater impact on restoration progress in the longer term than landscape factors or elapsed time. Seeding proved to be the best method in restoring sand grasslands by both favoring target species and controlling invasion. From the landscape factors, the abundance of neophyte species and distance to plantations should be considered when prioritizing areas and efforts for restoration. © The Author(s) 2022
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container_issue	4
title_short	The long-term effect of initial restoration intervention, landscape composition, and time on the progress of Pannonic sand grassland restoration
url	https://dx.doi.org/10.1007/s11355-022-00512-y
remote_bool	true
author2	Szitár, Katalin Kövendi-Jakó, Anna Török, Katalin Sáradi, Nóra Csákvári, Edina Halassy, Melinda
author2Str	Szitár, Katalin Kövendi-Jakó, Anna Török, Katalin Sáradi, Nóra Csákvári, Edina Halassy, Melinda
ppnlink	482837772
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doi_str	10.1007/s11355-022-00512-y
up_date	2024-07-03T17:44:34.649Z
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The long-term effect of initial restoration intervention, landscape composition, and time on the progress of Pannonic sand grassland restoration

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