Louis Calder Center, Biological Field Station, Department of Biological Sciences and Center for Urban Ecology, Fordham University, P.O. Box 887, Armonk, New York, 10504, USA.
Wildlife Conservation Society, 2300 Southern Boulevard, Bronx, New York, 10460, USA.
Ecol Appl. 2017 Jan;27(1):297-308. doi: 10.1002/eap.1444.
Plant survivorship depends on biotic and abiotic factors that vary at local and regional scales. This survivorship, in turn, has cascading effects on community composition and the physical structure of vegetation. Survivorship of native plant species is variable among populations planted in environmentally stressful habitats like urban roofs, but the degree to which factors at different spatial scales affect survivorship in urban systems is not well understood. We evaluated the effects of biotic and abiotic factors on survivorship, composition, and physical structure of two native perennial species assemblages, one characterized by a mixture of C grasses and forbs (Hempstead Plains, HP) and one characterized by a mixture of C grasses and forbs (Rocky Summit, RS), that were initially sown at equal ratios of growth forms (5:1:4; grass, N-fixing forb and non-N-fixing forb) in replicate 2-m plots planted on 10 roofs in New York City (New York, USA). Of 24 000 installed plants, 40% survived 23 months after planting. Within-roof factors explained 71% of variation in survivorship, with biotic (species identity and assemblage) factors accounting for 54% of the overall variation, and abiotic (growing medium depth and plot location) factors explaining 17% of the variation. Among-roof factors explained 29% of variation in survivorship and increased solar radiation correlated with decreased survivorship. While growing medium properties (pH, nutrients, metals) differed among roofs there was no correlation with survivorship. Percent cover and sward height increased with increasing survivorship. At low survivorship, cover of the HP assemblage was greater compared to the RS assemblage. Sward height of the HP assemblage was about two times greater compared to the RS assemblage. These results highlight the effects of local biotic and regional abiotic drivers on community composition and physical structure of green roof vegetation. As a result, initial green roof plant composition and roof microclimate may have long-term effects on community dynamics, ecosystem function, and urban biodiversity.
植物的存活率取决于在局部和区域尺度上变化的生物和非生物因素。这种存活率反过来又对群落组成和植被的物理结构产生级联效应。在像城市屋顶这样的环境压力生境中种植的本地植物物种的存活率在种群之间是不同的,但不同空间尺度的因素对城市系统中存活率的影响程度还不太清楚。我们评估了生物和非生物因素对两种本地多年生植物群落存活率、组成和物理结构的影响,一种以 C 草和杂类草的混合物为特征(Hempstead Plains,HP),另一种以 C 草和杂类草的混合物为特征(Rocky Summit,RS),最初以生长形式的相等比例(5:1:4;草、固氮植物和非固氮植物)播种在纽约市(美国纽约州)的 10 个屋顶上的 2m 重复小区中。在安装的 24000 株植物中,有 40%在种植 23 个月后存活下来。屋顶内因素解释了存活率变化的 71%,生物因素(物种身份和群落)占总体变化的 54%,非生物因素(生长介质深度和小区位置)占 17%。屋顶间因素解释了存活率变化的 29%,太阳辐射增加与存活率降低相关。尽管屋顶之间的生长介质特性(pH 值、养分、金属)不同,但与存活率无关。盖度和草层高度随存活率的增加而增加。在低存活率下,HP 群落的盖度大于 RS 群落。HP 群落的草层高度大约是 RS 群落的两倍。这些结果强调了当地生物和区域非生物驱动因素对绿色屋顶植被群落组成和物理结构的影响。因此,初始绿色屋顶植物组成和屋顶小气候可能对群落动态、生态系统功能和城市生物多样性产生长期影响。