Spatial and temporal variation in farmland bird nesting ecology: Implications for effective Corn Bunting Emberiza calandra conservation

Nils Anthes, Julia Staggenborg, Markus Handschuh
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Abstract

Farmland bird populations continue to decline despite intense conservation efforts, possibly also because of incomplete knowledge on the drivers of local productivity. We therefore investigated spatial and temporal variation in nest site selection, breeding phenology, and nest survival for 225 nests of the Corn Bunting, a species of conservation concern in Central and Western Europe, in cropland-dominated, mixed, and grassland-dominated landscapes in SW Central Europe. Nesting phenology spread from April to August, started earlier at lower altitudes and progressed from grassland habitats to arable crops and eco-scheme flower fields. Most nests were placed in cultivated land, with substantial variation between landscape types but also between years within sites, so that large fractions of breeding attempts are prone to fail through land use operations in particular years. When nests were individually protected from land use, 'apparent' and 'Mayfield' survival rates differed substantially between nest habitats, with lowest survival in 2nd year flower fields and highest survival in fallow grassland. Accounting for land use survival from patch-specific mowing, harvesting, and grazing dates, 'total Mayfield nest survival' estimates dropped by about half to 21 %, 13 %, and 20 % for (hay) meadows, alfalfa / clover-grass leys, and pastures, respectively, which held about 2/3 of nests in mixed landscapes. To enhance productivity beyond the thresholds required for local population persistence, we propose refined conservation schemes that improve survival within production farmland, best coupled with the development of prolific 'Corn Bunting Landscapes'.
农田鸟类筑巢生态的时空变化:有效保护粟滨鹀(Emberiza calandra)的意义
尽管开展了大量保护工作,但农田鸟类种群数量仍在持续下降,这可能也是因为对当地生产力驱动因素的了解不够全面。因此,我们研究了中欧西南部以耕地为主、混合和草地为主的地貌中玉米鹀的 225 个巢穴在巢址选择、繁殖物候学和巢存活率方面的时空变化,玉米鹀是中欧和西欧受保护的物种。筑巢期从 4 月到 8 月,在低海拔地区开始较早,并从草地栖息地发展到耕地和生态花田。大多数巢都位于耕地中,不同地貌类型之间以及同一地点不同年份之间的差异很大,因此在特定年份中,很大一部分繁殖尝试很可能因土地使用操作而失败。当单独保护巢穴不受土地利用影响时,巢穴栖息地之间的 "表观 "存活率和 "梅菲尔德 "存活率差别很大,第二年花田的存活率最低,而休耕草地的存活率最高。考虑到特定地块除草、收割和放牧日期的土地使用存活率,"梅菲尔德巢总存活率 "估计值下降了约一半,在(干草)草甸、紫花苜蓿/苜蓿-禾本科牧场和牧场中分别为21%、13%和20%,在混合景观中,这些地块保留了约2/3的巢。为了提高生产力,使其超过当地种群持续存在所需的阈值,我们提出了完善的保护计划,以提高生产农田中的存活率,最好能与发展多产的 "玉米鹀景观 "相结合。
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