Cultural landscapes affiliated with the Indigenous Sámi of the northern boreal forests are laden with cognitive elements of social and religious significance. Here, the authors focus on trees bearing incised markings and use an archaeological and ethnohistoric interpretive framework to explore the significance of such trees in Sámi landscapes. Intensive forestry is destroying culturally modified trees at an alarming rate, and their significance as the bearers of culture and history is being stripped from forest landscapes. As a step towards understanding their importance, this work makes a plea for the documentation, interpretation and protection of the remaining trees.

This article examines the sylvan political ecology of late colonial New Spain and the colonial government's attempt to address deforestation through the Council on Forests, the first body in the kingdom's history dedicated to the conservation of natural resources. Drawing primarily from the corpus of documents produced by and remitted to the council, this article gives a trans-regional perspective on colonial forest use and argues that the Spanish crown's usurpation of indigenous communities’ eminent domain over forests was the first step in a process that over centuries progressively severed the cultural ties that bound communities and forests by converting common-pool resources into open-access commons. The catastrophic mortality of the Spanish invasion was the second step, which rendered conservation measures seemingly unnecessary among both woodcutters and officials. But it was during the eighteenth century that older Habsburg notions of protectionism intersected with economic and political changes associated with Bourbon rule to further compel this cultural severance. While previous works have studied the ecological impacts of mining, ranching, and flood control, this article moves beyond the study of a single industry to suggest some of the larger ecological consequences of Spanish colonialism.

Deadwood tree stems scattered above treeline on tephra-covered slopes of Whitewing Mtn (3051 m) and San Joaquin Ridge (3122 m) show evidence of being killed in an eruption from adjacent Glass Creek Vent, Inyo Craters. Using tree-ring methods, we dated deadwood to AD 815–1350 and infer from death dates that the eruption occurred in late summer AD 1350. Based on wood anatomy, we identified deadwood species as Pinus albicaulis, P. monticola, P. lambertiana, P. contorta, P. jeffreyi, and Tsuga mertensiana. Only P. albicaulis grows at these elevations currently; P. lambertiana is not locally native. Using contemporary distributions of the species, we modeled paleoclimate during the time of sympatry to be significantly warmer (+3.2°C annual minimum temperature) and slightly drier (−24 mm annual precipitation) than present, resembling values projected for California in the next 70–100 yr.

Given the difficulty of separating the three Picea species—P. glauca, P. mariana, and P. rubens (white, black, and red spruce)—in the pollen record, little is known about their unique histories in eastern North America following deglaciation. Here we report the first use of a classification tree analysis (CART) to distinguish pollen grains of these species. It was successfully applied to fossil pollen from eight sites in Maine and one in Massachusetts. We focused on the late glacial/early Holocene (14,000 to 8000 cal yr B.P.) and the late Holocene (1400 cal yr B.P. to present)—the two key periods since deglaciation when Picea has been abundant in the region. The result shows a shift from a Picea forest of P. glauca and P. mariana in the late glacial to a forest of P. rubens and P. mariana in the late Holocene. The small number of P. rubens grains identified from the late glacial/early Holocene samples (<5%) suggests that that species was either absent or rare at most of the sites. The occurrence and distribution of the three species do not reveal any geographic or temporal trend during late glacial time, but the data suggest that they were distributed in local patches on the landscape. The results of this study indicate that the recent population expansion of Picea (1000 to 500 cal yr B.P.) was likely the first time since deglaciation that P. rubens was abundant in the region.

Picea is an important taxon in late-glacial pollen records from eastern North America, but little is known about which species of Picea were present. We apply a recently developed palynological method for discriminating the three Picea species in eastern North America to three records from New England. Picea glauca was dominant at ∼ 14,500–14,000 cal yr BP, followed by a transition to Picea mariana between ∼ 14,000 and 13,500 cal yr BP. Comparison of the pollen data with hydrogen isotope data shows clearly that this transition began before the beginning of the Younger Dryas Chronozone. The ecological changes of the late-glacial interval were not a simple oscillation in the position of a single species' range, but rather major changes in vegetation structure and composition occurring during an interval of variations in several environmental factors, including climate, edaphic conditions, and atmospheric CO2 levels.

This paper documents a continuous ∼ 44,000-yr pollen record derived from the Mfabeni Peatland on the Maputaland Coastal Plain. A detailed fossil pollen analysis indicates the existence of extensive Podocarpus-abundant coastal forests before ∼ 33,000 cal yr BP. The onset of wetter local conditions after this time is inferred from forest retreat and the development of swampy conditions. Conditions during the last glacial maximum (∼ 21,000 cal yr BP) are inferred to have been colder and drier than the present, as evidenced by forest retreat and replacement of swampy reed/sedge communities by dry grassland. Forest growth and expansion during the Holocene Altithermal (∼ 8000–6000 cal yr BP) indicates warm, relatively moist conditions. Previous records from Maputaland have suggested a northward migration of Podocarpus forest during the late Holocene. However, we interpret a mid-Holocene decline in Podocarpus at Mfabeni as evidence of deforestation. Forest clearance during the mid-Holocene is supported by the appearance of Morella serrata, suggesting a shift towards more open grassland/savanna, possibly due to burning. These signals of human impact are coupled with an increase in Acacia, indicative of the development of secondary forest and hence disturbance.

Changes in habitat affect the distribution of species at different spatial and temporal scales. Our aim was to assess the use of several retrospective methods when determining habitat history and its influence on species distribution, using the pendent lichen Usnea longissima Ach. as a model organism. The study was carried out in a Norway spruce dominated forest, located in the middle boreal zone of northern Sweden. Historical sources (including forest inventories and maps) and dendrochronology were combined with field surveys to determine past stand characteristics with a high spatial precision. Also, present stand characteristics were thoroughly surveyed and the relationship between distribution of U. longissima and past and present habitat characteristics were evaluated. Our results showed that, despite the fact that historical logging was unevenly distributed within the study area, similarities in stand structure exist today. Several essential factors affecting the distribution of U. longissima could be related to changes in past stand structure, especially the extent and intensity of previous logging operations and the subsequent stand development during the last c. 150 years. Our results also showed that U. longissima was favoured by a continuous old age structure with canopy openness preserved. The importance of detailed reconstructions of specific habitat components is highlighted when relating species presence to habitat change. It is suggested that the use of retrospective methods presented in this study can be helpful in clarifying possible causes for the complex distribution of certain organisms.

The authors present a unique long record of inner bark use by the Sami people of northern Scandinavia extending back to 2800 BP. Consistent patterns with respect to the direction and size of bark peeling scars shows that common values and standards were early applied. They further conclude that inner bark was important as a regular food and a vitamin C source at these northern latitudes. Bark-peeled trees as biological artefacts in forests also provide important data to understand subsistence strategies and spatial patterns of land use unique to areas with long winter seasons.

Historical research has enhanced understanding of past human influences on forests and provides insights that can improve current conservation efforts. This paper presents one of the first detailed studies of mangrove forest history. Historical changes in mangroves and their use were examined in Bais Bay and Banacon Island, Philippines. Cutting to make space for fish ponds and residential settlement has dramatically reduced the distribution of mangroves in Bais, although forest has expanded rapidly near the mouth of the largest river where soils from nearby deforested hillsides have been deposited as sediments along the coast. Heavy cutting of mangroves for commercial sale of firewood occurred under minor forest product concessions in Bais and Banacon between the late 1930s and 1979. Cutting for domestic consumption of fuel and construction wood by local people has been widespread in both areas, although rates of cutting have varied in space and over time as a result of changing demographic pressures and in response to cutting restrictions imposed by firewood concessionaires, fish pond owners and government officials. People in both Bais and Banacon have responded to declining local forest availability by planting mangroves. Early motivations to plant reflected the desire to have a ready supply of posts for construction of fish weirs. Many have also planted to protect fishpond dykes and homes from storm damage, and increasing numbers now plant as a means to establish tenure claims over mangrove areas. However, planted stands have tended to be species monocultures and to bear only limited resemblance to natural mangrove forests. In contrast to many upland forests, opportunities for protection and restoration of mangroves are limited by virtue of a highly restricted natural distribution and by competing land uses that are likely to intensify in the future. Understanding historical patterns of change can be instructive to conservationists, but the future remains laden with uncertainties.