USDA Forest Service, 920 Main Campus Dr. Suite 300, Raleigh, NC 27606, United States.
USDA Forest Service, 920 Main Campus Dr. Suite 300, Raleigh, NC 27606, United States.
Sci Total Environ. 2017 Dec 15;605-606:376-390. doi: 10.1016/j.scitotenv.2017.06.147. Epub 2017 Jun 29.
A field experiment was established in a high elevation red spruce (Picea rubens Sarg.) - balsam fir (Abies balsamea) forest on Mount Ascutney Vermont, USA in 1988 to test the nitrogen (N) saturation hypothesis, and to better understand the mechanisms causing forest decline at the time. The study established replicate control, low and high dose nitrogen addition plots (i.e., 0, 15.7 and 31.4kgNHCl-Nhayr). The treatments began in 1988 and continued annually until 2010, but monitoring has continued to present. During the fertilization period, forest floor C:N, net in situ N mineralization, spruce foliar Ca%, and live spruce basal area decreased with increasing N addition, while foliar spruce N% and forest floor net nitrification increased with increasing N addition. The control plots aggraded forest floor N at a rate equal to the sum of the net in situ N mineralization plus average ambient deposition. Conversely, N addition plots lost forest floor N. Following the termination of N additions in 2010, the measured tree components returned to pre-treatment levels, but forest floor processes were slower to respond. During the 30year study, site surface air temperature has increased by 0.5°C per decade, and total N deposition has decreased 5.5 to 4.0kgNhayr. There have also been three significant drought years and at least one freeze injury year after which much of the forest mortality on the N addition plots occurred. Given that there was no control for the air temperature increase, discussion of the interactive impacts of climate and change and N addition is only subjective. Predicted changes in climate, N deposition and other stressors suggest that even in the absence of N saturation, regeneration of the spruce-fir ecosystem into the next century seems unlikely despite recent region-wide growth increases.
1988 年,在美国佛蒙特州阿斯科特尼山的高海拔红云杉(Picea rubens Sarg.)-香脂冷杉(Abies balsamea)森林中建立了一个田间实验,以检验氮(N)饱和假说,并更好地了解当时导致森林衰退的机制。该研究建立了重复对照、低氮和高氮添加处理区(即 0、15.7 和 31.4kgNHCl-Nhayr)。这些处理从 1988 年开始,一直持续到 2010 年,但监测一直持续到现在。在施肥期间,林下地被物 C:N、原位净氮矿化、云杉叶片 Ca%和活云杉基部面积随氮添加量的增加而减少,而叶片云杉 N%和林下地被物净硝化随氮添加量的增加而增加。对照区的林下地被物以等于原位净氮矿化加上平均环境沉降之和的速率积累氮。相反,氮添加区失去了林下地被物氮。2010 年停止氮添加后,测量的树木组成部分恢复到预处理水平,但林下地被物过程恢复较慢。在 30 年的研究期间,站点地表空气温度每十年上升 0.5°C,总氮沉积减少了 5.5 至 4.0kgNhayr。此外,还发生了三次严重干旱年和至少一次冻害年,此后,氮添加区的大部分森林死亡。考虑到没有对气温升高进行控制,因此,关于气候和变化以及氮添加的交互影响的讨论仅具有主观性。预测的气候变化、氮沉积和其他胁迫因素表明,即使没有氮饱和,在下个世纪,云杉-冷杉生态系统的再生似乎也不太可能,尽管最近该地区的生长有所增加。