Identification of Old-Growth Forest Reference Ecosystems Using Historic Land Surveys, Redwood National Park, California

2011 ◽  
Vol 20 (6) ◽  
pp. 679-687 ◽  
Author(s):  
Joy A. Fritschle
The Holocene ◽  
2015 ◽  
Vol 26 (1) ◽  
pp. 80-92 ◽  
Author(s):  
Ambroise G Baker ◽  
Marcelina Zimny ◽  
Andrzej Keczyński ◽  
Shonil A Bhagwat ◽  
Kathy J Willis ◽  
...  

1988 ◽  
Vol 64 (3) ◽  
pp. 269
Author(s):  
Kent W. Olson ◽  
Ronald L. Moomaw ◽  
Richard P. Thompson

Nova Hedwigia ◽  
2002 ◽  
Vol 74 (1-2) ◽  
pp. 25-49 ◽  
Author(s):  
Christian Printzen ◽  
Josef Halda ◽  
Zdeněk Tønsberg Palice

2014 ◽  
Vol 25 (3) ◽  
pp. 306-321 ◽  
Author(s):  
JESSICA S. CORNILS ◽  
ISABELL RIEDL ◽  
JULIAN FRICKE ◽  
MORITZ KATZ ◽  
CHRISTIAN H. SCHULZE

SummaryThe lowland forest on the southern Pacific slope of Costa Rica has an extremely diverse avifauna, including the Black-cheeked Ant-tanager Habia atrimaxillaris. The only known remaining populations of this highly range-restricted species occur in the areas of Piedras Blancas and Corcovado National Park. It is assumed that the population is decreasing due to habitat loss and fragmentation. We assessed the species’ population density in a part of the Piedras Blancas National Park using distance sampling (in February–April 2009 and November 2010–January 2011) and territory mapping (November 2010–January 2011). We also examined habitat preferences based on vegetation structure at point count locations. Black-cheeked Ant-tanagers were exclusively found in old-growth forest. The species’ likelihood of occurrence at census points increased with forest cover (within a radius of 200 m around census points), canopy closure, and density of trees (with diameter at breast height >10 cm). Average population density estimated by distance sampling was 24–27 individuals per km², which is in accordance with the population size estimated by territory mapping (17–25 birds per km²). Based on these estimates, an overall population size of 12,432–20,720 birds is predicted for the remaining 592 km² lowland forest area of the Golfo Dulce region. The Black-cheeked Ant-tanager was only recorded in old-growth forest, but not in gallery forests embedded in a human-dominated landscape matrix. Since the species appears to avoid forest edges, further forest degradation and fragmentation will have a strong negative impact and should be rapidly reduced by adequate conservation measures.


2018 ◽  
Vol 69 (1) ◽  
pp. 44-62
Author(s):  
Teele Paluots ◽  
Jerry F. Franklin ◽  
Lembit Maamets ◽  
Diana Laarmann ◽  
Ahto Kangur ◽  
...  

Abstract Diverse structural elements play an important role in sustaining biodiversity in old-growth forests. Therefore, it is important to have thorough knowledge about these habitats and their condition in protected areas. Metsakorralduse Büroo OÜ conducted a large-scale Natura 2000 forest habitat inventory that covered 60% of Lahemaa National Park (LNP) area. Western taiga habitat data (7,191 ha) from this inventory was used for analysis of forest stages. The data was grouped according to stand classes by total area and these classes were compared by deadwood occurrence and relative density. For more precise evaluation of coarse woody debris (CWD) we used 27 sample plots from the Estonian Network of Forest Research Plots (ENFRP) located in LNP. The biggest areas of Western taiga habitat were covered by mature and old stages. CWD occurrence (over 5 m3ha−1 of snags and logs) by habitat representativeness is higher in old and natural forest classes. This logical result is overshadowed by the outcome that the CWD was not substantially present on 32% of the area in the old-growth forest class. This indicates that these areas lack the potential of biological legacies to provide critical niche habitats for different species. The study shows that the CWD quantity in Estonian conditions is similar to that reported in previous studies in this region, but because many of the older forest stage classes do not have any CWD present, these areas should include ecological restoration practices in their conservation planning. By creating snags, logs and gaps in these areas, we are able to create better structural variability and include wood into different decay processes.


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