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1

Erickson, Britt E. "Clear-cutting increases mercury in runoff." Environmental Science & Technology 37, no. 11 (June 2003): 200A—201A. http://dx.doi.org/10.1021/es032463l.

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2

Keenan, Rodney J., and J. P. (Hamish) Kimmins. "The ecological effects of clear-cutting." Environmental Reviews 1, no. 2 (July 1, 1993): 121–44. http://dx.doi.org/10.1139/a93-010.

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Clear-cutting is a controversial practice that is widely applied in forests managed for wood production in many parts of the world. This paper aims to provide an objective synthesis of the ecological effects of clear-cutting as a basis for more informed discussion of its merits and disadvantages. A definition of clear-cutting is put forward, and its place in modern productive forestry is described. Effects on microclimate, water, soil, nutrient cycling, and the diversity and composition of plant and animal species are reviewed. The effects of clear-cutting vary considerably depending on site conditions (such as climate, geology, and topography) and on the structure and composition of the forest, the extent and distribution of harvesting, the method used to extract the logs, and the length of time before the forest is removed again. However, it is evident that many of the ecological impacts commonly ascribed to clear-cutting, in fact, result from other stages of the wood-production process, such as the quality and intensity of roading, site preparation practices (such as mechanical disturbance or slash burning), and the intensity of control of noncrop vegetation. Situations where clear-cutting is inappropriate are described. It is argued that in the right situations, with appropriate safeguards, it is an environmentally sound practice that offers many advantages in terms of the production of wood fibre.Key words: clear-cutting, environmental impacts, microclimate, hydrology, soil, forest production, nutrient cycling, wildlife.
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3

Stone, Louise. "Cutting cholesterol curbs clear cell RCC." Nature Reviews Urology 18, no. 9 (August 2, 2021): 509. http://dx.doi.org/10.1038/s41585-021-00510-z.

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4

Budiaman, A., N. F. Haneda, A. I. Nugraha, and F. Haikal. "Impacts of Clear Cutting on Diversity of Ground Ants (Hymenoptera: Formicidae) in Pine Plantation Forest in Sukabumi Forest Management Unit, West Java." Jurnal Manajemen Hutan Tropika (Journal of Tropical Forest Management) 27, no. 1 (April 4, 2021): 42–49. http://dx.doi.org/10.7226/jtfm.27.1.42.

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Clear cutting is the main source of timber production of plantation forest management in Indonesia, but this activity disrupts the lives of ground ants. It is rarely known how clear cutting affects the ground ant community in the Indonesian plantation forest. The study aimed to analyze the impacts of clear cutting on the diversity of ground ants in the pine plantation forest of Sukabumi, West Java. The study compared the community structure of ground ants before clear cutting and after clear cutting. Ground ants were collected using a pitfall trap. Trapping of ground ants was carried out six days before the clear cutting and six days after the clear cutting. The ground ants were identified to the morphospecies level and classified into their functional role. The results showed that clear cutting alters the community indices of ground ants. Abundance, morphospecies composition, diversity index, richness index, and evenness index of ground ants after clear cutting was lower compared with those before clear cutting. The clear-felled area due to clear cutting provided favorable habitat for the generalist groups of ground ants, but negatively affected the predator and forager groups of ground ants. These findings can be used as an important factor in the development of environmenllyt-friendly forest harvesting systems in Indonesian plantation forests.
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5

Molchanov, A. G., Yu A. Kurbatova, and A. V. Olchev. "Effect of clear-cutting on soil CO2 emission." Biology Bulletin 44, no. 2 (March 2017): 218–23. http://dx.doi.org/10.1134/s1062359016060121.

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6

Grønflaten, Lena, Eiliv Steinnes, and Göran Örlander. "Effect of conventional and whole-tree clear-cutting on concentrations of some micronutrients in coniferous forest soil and plants." Forestry Studies / Metsanduslikud Uurimused 48, no. 1 (January 1, 2008): 5–16. http://dx.doi.org/10.2478/v10132-011-0051-4.

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Effect of conventional and whole-tree clear-cutting on concentrations of some micronutrients in coniferous forest soil and plants Increasingly intensive and mechanized clear-cutting may deplete the forest ecosystem of essential nutrients. A clear-cut area near Växjö, southern Sweden, was investigated for changes in Mn, Cu and Zn in soil (NH4NO3 extractable and HNO3 soluble) and wavy hair grass (Deschampsia flexuosa) after conventional (CC) and whole-tree clear-cutting (WTC). The soil samples were mostly iron podzols. The area consisted of four clear-cut sites, respectively 2, 4, 6 and 8 years old, and an uncut forest reference stand. Each of the clear-cuts was split in two parts representing WTC and CC sites. Manganese showed the most definite trends after clear-cutting, exhibiting higher extractable concentrations in Oe, Oa and E horizons (4-8 years after clear-cutting) and B horizons (6-8 years after clear-cutting). The increase of exchangeable Mn in the E (2-8 years) and B (4-8 years) horizons was particularly strong. Zn concentrations tended to fluctuate with time. There was a tendency to higher Mn and Zn concentrations in the humus layer especially 2 years after CC-treatment compared with WTC, whereas the opposite trend was apparent for Cu. Mn, Cu and Zn concentrations decreased in Deschampsia flexuosa 2 years after clear-cutting, possibly due to increased soil pH.
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7

WALLENDORF, MICHAEL J., PAUL A. PORNELUZI, WENDY K. GRAM, RICHARD L. CLAWSON, and JOHN FAABORG. "Bird Response to Clear Cutting in Missouri Ozark Forests." Journal of Wildlife Management 71, no. 6 (August 2007): 1899–905. http://dx.doi.org/10.2193/2006-386.

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8

Tönnes, Susan, Eeva Karjalainen, Irja Löfström, and Marjo Neuvonen. "Scenic Impacts of Retention Trees in Clear-cutting Areas." Scandinavian Journal of Forest Research 19, no. 4 (July 2004): 348–57. http://dx.doi.org/10.1080/02827580310019284.

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9

Calbris, Geneviève. "From cutting an object to a clear cut analysis." Gesture 3, no. 1 (October 16, 2003): 19–46. http://dx.doi.org/10.1075/gest.3.1.03cal.

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The representation of the concrete world is an abstraction. The elements that are physically pertinent to reality are synthesized in a gestural, schematic and ergonomic representation. Although schematic, this representation is nuanced: the gestural variants are numerous in order to account for the way we cut things: differences in size and configuration of blades as well as in their manipulation in a single or repeated movement. Representing an abstract notion derived from the act itself, gesture evolves towards increasing simplification and integrates the representation of other notions that enrich the first: cf. the semantic nuances supplied by the plane of the hand and the orientation of the palm in order to evoke ‘cut plus division’, ‘cut plus obstacle’, etc. Moreover, on the semantic level one witnesses a process of generalization: the passage from concrete to abstract, and in the abstract world, from one domain to another: the individual knows how ‘trancher / to decide’ and is ‘tranchant / abrupt’. From the physical and symbolic comparison of the gestural variants referring to all kinds of cuts, a common percept emerges: a gap in a continuum, a representative schema explaining the cut as an interruption. The question addressed is: does gesture not directly account for the abstract schema loaded with imagery from diverse perceptual experiences (representation of acts and their results) at the basis of the concept (representation of the notion)?
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10

Mohr, Christian H., Ruben Coppus, Andrés Iroumé, Anton Huber, and Axel Bronstert. "Runoff generation and soil erosion processes after clear cutting." Journal of Geophysical Research: Earth Surface 118, no. 2 (May 24, 2013): 814–31. http://dx.doi.org/10.1002/jgrf.20047.

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11

Stiegler, Mayo H. "Airport's Clear-Cutting of Trees Deemed Destruction of Wetlands." Journal - American Water Works Association 98, no. 6 (June 2006): 44. http://dx.doi.org/10.1002/j.1551-8833.2006.tb07680.x.

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12

Pardo, L. H., H. F. Hemond, J. P. Montoya, T. J. Fahey, and T. G. Siccama. "Response of the natural abundance of 15N in forest soils and foliage to high nitrate loss following clear-cutting." Canadian Journal of Forest Research 32, no. 7 (July 1, 2002): 1126–36. http://dx.doi.org/10.1139/x02-041.

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Export of microbially produced nitrate from an ecosystem is expected to increase δ15N in the remaining soil organic matter and NH4+. To test the hypothesis that nitrification and nitrate loss induced by clear-cutting cause an increase in soil and foliar δ15N, we measured δ15N in a clear-cut watershed at the Hubbard Brook Experimental Forest, New Hampshire. δ15N ranged from –0.02‰ in the Oie horizon to 7.7‰ in the Bs2 horizon prior to clear-cutting and increased significantly by 1.3‰ in the Oie horizon and 0.9‰ in the Oa horizon 3 years after clear-cutting. Fifteen years after clear-cutting, δ15N in both O horizons decreased to near-initial values. No significant temporal changes in the Bs2 and C horizons δ15N were observed. Foliar δ15N was highest (1.7‰) the first 2 years after clear-cutting and was significantly higher than in the reference watershed (mean δ15N = –1.2‰), decreasing to 0.0‰ 3–5 years after clear-cutting and to –1.3‰ 9–11 years after clear-cutting. Increased foliar δ15N coincided with increased stream-water nitrate concentration, suggesting that the increased nitrification responsible for elevated stream-water nitrate may also have caused an enrichment of the plant-available ammonium pool. The response observed in this catchment also suggests that sampling of soil or foliar δ15N may provide a practical alternative to long time series of stream chemistry for evaluating nitrogen saturation of forested ecosystems.
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13

Elliott, Katherine J., Chelcy F. Miniat, and Andrea S. Medenblik. "The long-term case for partial-cutting over clear-cutting in the southern Appalachians USA." New Forests 51, no. 2 (July 6, 2019): 273–95. http://dx.doi.org/10.1007/s11056-019-09731-y.

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14

Hashimoto, Shoji, and Masakazu Suzuki. "The impact of forest clear-cutting on soil temperature: a comparison between before and after cutting, and between clear-cut and control sites." Journal of Forest Research 9, no. 2 (May 2004): 125–32. http://dx.doi.org/10.1007/s10310-003-0063-x.

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15

Chubbs, Tony E., Lloyd B. Keith, Shane P. Mahoney, and Michael J. McGrath. "Responses of woodland caribou (Rangifer tarandus caribou) to clear-cutting in east-central Newfoundland." Canadian Journal of Zoology 71, no. 3 (March 1, 1993): 487–93. http://dx.doi.org/10.1139/z93-070.

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Movements, sex and age structure, and habitat selection of adult woodland caribou (Rangifer tarandus caribou) were examined in relation to clear-cutting on summer range in east-central Newfoundland during 1987 – 1990. We obtained 2473 locations of 35 radio-collared caribou during at least two consecutive summers. Locations relative to clearcuts were determined for eight males and 27 females. Distances to existing clearcuts were compared with distances to those same geographic points prior to and following the summer in which clear-cutting occurred. Four males and 10 females maintained similar mean distances from clearcuts, 3 males and 12 females were farther away, and 2 females were closer. Three other females and one male were assumed to be too distant to be affected by clear-cutting. Of those found farther away from clearcuts, females were 2 – 3 times farther away than males. Among female caribou that maintained similar mean distances to clearcuts, habitat use during clear-cutting was similar to that before and afterwards. Females displaced by clear-cutting avoided open burns and hardwoods and selected mature black-spruce forest, whereas prior to cutting they used habitats in proportion to their availability. Sex and age ratios indicated that significantly fewer females and calves were present near clearcuts than elsewhere in the study area. Our results demonstrate that clear-cutting mature forests on summer range may affect the movements and distribution of woodland caribou.
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16

Lee, Cheol Min, and Tae-Sung Kwon. "Change of Butterfly Communities After Clear Cutting in Gwangneung Forest." Korean Journal of Applied Entomology 53, no. 4 (November 25, 2014): 347–54. http://dx.doi.org/10.5656/ksae.2014.09.0.042.

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17

Clabough, C. "Clear-Cutting Eden: Ecology and the Pastoral in Southern Literature." Interdisciplinary Studies in Literature and Environment 18, no. 1 (January 1, 2011): 231–33. http://dx.doi.org/10.1093/isle/isq141.

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18

Metslaid, M., T. Ilisson, M. Vicente, E. Nikinmaa, and K. Jogiste. "Growth of advance regeneration of Norway spruce after clear-cutting." Tree Physiology 25, no. 7 (July 1, 2005): 793–801. http://dx.doi.org/10.1093/treephys/25.7.793.

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19

Johnson, Chris E. "Soil nitrogen status 8 years after whole-tree clear-cutting." Canadian Journal of Forest Research 25, no. 8 (August 1, 1995): 1346–55. http://dx.doi.org/10.1139/x95-147.

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Previous research on chronosequences of even-aged northern hardwood stands has suggested that forest clearing is accompanied by large losses of nitrogen from the forest floor. The timing of the losses and the fate of a large fraction of the lost nitrogen are unclear. The purpose of this investigation was to study these questions through direct measurement of soil nitrogen concentrations and pools through time on an experimental catchment cleared in a whole-tree harvest in 1983–1984. Nitrogen losses from the forest floor at the site, the Hubbard Brook Experimental Forest, New Hampshire, were lower than predictions based on previous research. The mean forest floor nitrogen pool was 17% lower 8 years after clear-cutting of the site (P = 0.18). Predictions based on chronosequence studies suggest that 25–40% of the forest floor nitrogen would be lost after 8 years. Mechanical disturbance during logging may play a role in limiting short-term nitrogen losses. The steep midsection of the catchment experienced the greatest losses of nitrogen and carbon, while pools in the relatively flat spruce-fir zone at the upper elevations were unchanged. Carbon was preferentially lost from soil organic matter, relative to nitrogen, resulting in significant decreases in the C/N and C/organic matter ratios in the soil. The N/organic matter ratio was generally unchanged. Nitrogen losses can be limited after clear-cutting by minimizing organic matter losses and promoting rapid regrowth.
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20

Yang, Zhiqiang, Warren B. Cohen, and Mark E. Harmon. "Modeling early forest succession following clear-cutting in western Oregon." Canadian Journal of Forest Research 35, no. 8 (August 1, 2005): 1889–900. http://dx.doi.org/10.1139/x05-132.

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In the Pacific Northwest, the process of conifer development after stand-replacing disturbance has important implications for many forest processes (e.g., carbon storage, nutrient cycling, and biodiversity). This paper examines conifer development in the Coast Range Province and Western Cascades Province of Oregon using repeat interpretation of historic aerial photographs from 1959 to 1997 to examine the canopy cover change of different life forms: shrubs, hardwood trees, and conifer trees. Ninety-four stands from the Western Cascades Province and 59 stands from the Coast Range Province were photointerpreted in roughly 5-year intervals. A Chapman–Richards growth function was used to model conifer cover development for all sample stands. Based on the photo data and the Chapman–Richards function, these stands were classified into one of seven early forest successional trajectories defined by the vegetation physiognomy. Succession in the Coast Range Province and Western Cascades Province were compared using parameters derived from the Chapman–Richards growth function. Our results echo previous studies in that rates and densities of conifer regeneration varied markedly among sites; however, our results also indicate that early forest succession differs in the two study regions in terms of both trajectories and rates. Conifer regeneration in the Western Cascades Province tends to have longer delays in establishing and slower rates compared with the Coast Range Province.
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21

Pominville, Pierre, and Jean-Claude Ruel. "Effets de la coupe à blanc et de la coupe par bandes sur la régénération obtenue après 5 ans dans des pessières noires du Québec." Canadian Journal of Forest Research 25, no. 2 (February 1, 1995): 329–42. http://dx.doi.org/10.1139/x95-037.

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An experiment was conducted to compare the effects of traditional clear-cutting with those of strip cutting on regeneration of black spruce, Piceamariana (Mill.) B.S.P., stands on scarified and unscarified uplands and on lowlands. To that effect, regeneration surveys were done before cutting, in the following year, and 3 and 5 years after cutting. Five years after harvesting, strip cutting led to higher coniferous stocking than clear-cutting on scarified uplands and on lowlands. On unscarified uplands, the gain attributable to strip cutting was not significant. The coniferous stocking of strip cuts on scarified uplands was not greater than on unscarified uplands. So the efficiency of scarification could not be proved in that study. Stocking obtained after 5 years remained closely related to the one observed immediately after harvesting in the strip cufs as in the clear-cuttings. This is particularly true for balsam fir, Abiesbalsamea (L.) Mill. In the strip cuts, the balsam fir stocking was constant while the one of black spruce increased. This could have an impact on the evolution of the composition of the new stands and, consequently, on their vulnerability to spruce budworm, Choristoneurafumiferana (Clem.). The majority of the clear-cuttings were well regenerated 5 years after harvesting. Their average coniferous stocking was slightly above 60%. However, 48% of the clear-cuttings did not reach this level when only unscarified plots on uplands were considered. Advance growth was abundant in those plots but suffered high losses during harvesting. Consequently, reducing the losses during harvesting would result in a lower proportion of clear-cuttings with insufficient coniferous stocking 5 years after cutting. On the other hand, almost all the strip cuts with insufficient regeneration after harvesting were well regenerated 5 years later. Thus, strip cutting could be an interesting option on sites with insufficient advance growth and on sites well regenerated before cutting but where important losses during harvesting are anticipated.
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22

Abe, Yukiko, Hiroyuki Kurokochi, Kazutoshi Yoshitake, Ryo Yonezawa, Shuichi Asakawa, and Takeshi Tange. "Soil Bacterial Community Composition in Cryptomeria japonica Plantation at Different Times after Clear-Cutting." Forests 12, no. 6 (June 8, 2021): 754. http://dx.doi.org/10.3390/f12060754.

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To understand the mechanism of carbon release from the soil after clear-cutting, it is first necessary to understand the soil microbes, which are the decomposers of organic matter. The aim of this study was to obtain knowledge on the composition of the soil bacterial community in a Cryptomeria japonica plantation at different times after clear-cutting. We established three clear-cutting plots—CC1, CC2, and CC3—in March 2013, May 2017, and December 2017, respectively, and one unlogged plot (Control) in March 2013 in a 35–39-year-old C. japonica plantation in eastern Japan. We collected the soil in May and September 2018 and examined the soil bacterial community compositions of the plots at 5–9, 12–16, and 62–66 months after clear-cutting. The soil bacterial community composition at the phylum level showed a small difference between plots for CC1, CC2, CC3, and the Control. On the other hand, most of the taxa showed similar compositional ratios in the four plots, but some taxa, such as Proteobacteria and Acidobacteria, showed differences. Proteobacteria appeared more frequently in CC1, CC2, and CC3 than in the Control, indicating a longer period of high soil temperature due to clear-cutting. The frequency of Acidobacteria was significantly lower in CC1 and CC2 than in CC3 and the Control, which might be due to the lack of the organic layer (Ao) after clear-cutting.
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23

Sakals, M. E., and Roy C. Sidle. "A spatial and temporal model of root cohesion in forest soils." Canadian Journal of Forest Research 34, no. 4 (April 1, 2004): 950–58. http://dx.doi.org/10.1139/x03-268.

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Root cohesion is an important parameter governing slope stability in steep forested terrain. Forest harvesting impacts root cohesion, and although the temporal effects have been noted, this dynamic parameter is often assumed to be spatially uniform. A model was developed to simulate the variation in root cohesion on a hillslope resulting from various forest management treatments. The model combines physical data on the horizontal rooting distribution of Douglas-fir (Pseudotsuga menziesii (Mirb.) Franco var. menziesii) together with a temporal relation of root cohesion decay. Harvesting methods examined include clear-cutting, single-tree selection cutting, and strip-cutting. Model outputs are analysed qualitatively for regions of root cohesion minima and quantitatively for the average root cohesion within the simulated hillslope. A selection cutting simulation maintained the highest average root cohesion value, decreasing to only 81% of the preharvest condition. In contrast, the minimum root cohesion following clear-cutting declined to 38% of the preharvest value. Selection and strip-cutting scenarios resulted in smaller areas of reduced root cohesion that were adjacent to areas with high root cohesion. Such partial cutting methods shorten the period of reduced root cohesion following timber harvesting compared with clear-cutting.
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24

Byrd, Kristin B., V. Thomas Parker, Detlev R. Vogler, and Ken W. Cullings. "The influence of clear-cutting on ectomycorrhizal fungus diversity in a lodgepole pine (Pinus contorta) stand, Yellowstone National Park, Wyoming, and Gallatin National Forest, Montana." Canadian Journal of Botany 78, no. 2 (April 7, 2000): 149–56. http://dx.doi.org/10.1139/b99-171.

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Effects of clear-cutting on the ectomycorrhizal (EM) fungus community in a Pinus contorta Dougl. ex Loud. forest near Yellowstone National Park, Wyoming, U.S.A., were assessed using molecular techniques. Samples were taken by soil core in both undisturbed and clear-cut sites by randomized block design. Species overlap was compared between clear-cut and undisturbed sites and ascomycete-basidiomycete ratio was determined, using PCR-RFLP methods. Fifty species of EM fungi were detected in the clear-cut sites, the most common being Cenococcum geophilum Fr., Suillus sp., a member of the suilloid group, a Russulaceae species, and a Thelephoraceae species. Sixty-six species were detected in the undisturbed sites, which were dominated by a Suilloid species, a Tricholomataceae species, Cortinarius sp., and Cenococcum geophilum. Species composition in the clear-cut sites differed significantly from that in the undisturbed sites (P = 0.0001). However, 9 of the 14 species most commonly found in the clear-cut sites were also found in the undisturbed sites, but in much lower abundance, while species rank curves of both stand types mirrored each other. There were no significant differences in species richness, root-tip abundance, or ascomycete-basidiomycete ratio between the clear-cut and undisturbed sites. However, species richness was lower in the clear-cut sites than in the undisturbed sites. An overall loss of species richness after clear-cutting and significant changes in species composition indicate that clear-cutting can negatively alter the EM fungal community, and this may have profound effects on ecosystem function.Key words: ectomycorrhizae, community structure, clear-cutting, molecular techniques.
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25

Jurgensen, M. F., R. T. Graham, M. J. Larsen, and A. E. Harvey. "Clear-cutting, woody residue removal, and nonsymbiotic nitrogen fixation in forest soils of the Inland Pacific Northwest." Canadian Journal of Forest Research 22, no. 8 (August 1, 1992): 1172–78. http://dx.doi.org/10.1139/x92-155.

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The effect of clear-cutting and woody residue removal on soil nonsymbiotic nitrogen fixation, as estimated by the acetylene reduction technique, was investigated on a subalpine fir (Abieslasiocarpa (Hook.) Nutt.) site in western Montana and on a cedar (Thujaplicata (Donn ex D. Don) Lindl.)–hemlock (Tsugaheterophylla (Raf) Sarg.) site in northern Idaho. Nitrogen fixation in the forest floor, soil wood, and mineral soil on the subalpine fir site averaged 0.9 kg N•ha−1•year−1 in the uncut stand. This nitrogen input was reduced by 10% after clear-cutting followed by prescribed burning, and by 22% after clear-cutting followed by intensive residue removal. Nitrogen fixation in the uncut cedar–hemlock stand averaged 1.1 kg N•ha−1•year−1 and was reduced by 26% after prescribed burning. Clear-cutting only and clear-cutting followed by intensive woody residue removal had little effect on nitrogen fixation. However, large amounts of woody residue left on the cut site nearly doubled the amounts of nitrogen fixation compared with the uncut stand. Lower nitrogen fixation after harvesting on both the Idaho and Montana sites was due mostly to reductions in forest floor and large woody residue. Replacement of nitrogen losses from prescribed burning on these sites by nonsymbiotic nitrogen fixation and precipitation would take from 150 to 400 years, depending on the severity of the bum treatments.
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26

Ivanova, N. S. "Recovery of tree stand after clear-cutting in the ural mountains." International Journal of Bio-resource and Stress Management 5, no. 1 (2014): 090. http://dx.doi.org/10.5958/j.0976-4038.5.1.017.

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27

Åström, Marcus, Mats Dynesius, Kristoffer Hylander, and Christer Nilsson. "SLOPE ASPECT MODIFIES COMMUNITY RESPONSES TO CLEAR-CUTTING IN BOREAL FORESTS." Ecology 88, no. 3 (March 2007): 749–58. http://dx.doi.org/10.1890/06-0613.

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28

Johnson, Chris E., Arthur H. Johnson, and Thomas G. Siccama. "Whole-Tree Clear-Cutting Effects on Exchangeable Cations and Soil Acidity." Soil Science Society of America Journal 55, no. 2 (1991): 502. http://dx.doi.org/10.2136/sssaj1991.03615995005500020035x.

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29

Khazri, Olfa, and Pierre Lasserre. "Forest management: Are double or mixed rotations preferable to clear cutting?" Resource and Energy Economics 33, no. 1 (January 2011): 155–71. http://dx.doi.org/10.1016/j.reseneeco.2010.04.004.

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30

Kearney, Anne R. "Effects of an Informational Intervention on Public Reactions to Clear-Cutting." Society & Natural Resources 14, no. 9 (October 2001): 777–90. http://dx.doi.org/10.1080/089419201753210594.

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31

Harvey, B. D., and Y. Bergeron. "Site patterns of natural regeneration following clear-cutting in northwestern Quebec." Canadian Journal of Forest Research 19, no. 11 (November 1, 1989): 1458–69. http://dx.doi.org/10.1139/x89-222.

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Pre- and post-harvest regeneration levels were compared for Abiesbalsamea (L.) Mill. –Betulapapyrifera Marsh. –Picea spp. forests in an area of the southern clay belt of northwestern Quebec. Results revealed abundant advance softwood regeneration (mean = 65 000 stems/ha), almost entirely of Abies prior to harvest. The survey following mechanical and manual whole-tree harvesting suggested a 92% reduction of softwood regeneration and a shift from softwood to a mixed or hardwood-shrub dominated regeneration. Ninety percent of softwood seedlings collected after harvest were pre-established. Destruction of advance regeneration was generally greater on fine-textured soils. Hierarchic cluster analysis of ecological types based on softwood, hardwood, and shrub tree regeneration data as variables, revealed nine groups that could serve as a basis for operational silvicultural decision making. In general, Salix spp. and Alnusrugosa (Du Roi) Spreng. are the major competitors on poorly drained sites; Betula sp., Acerspicatum Lam., and Prunuspensylvanica L.f. dominate on thin organic deposits and coarse deposits, whereas Populustremuloides Michx. and Acerspicatum dominate on fine-textured deposits. These findings suggest that a good understanding of physical site factors can provide useful information for harvesting and silvicultural planning.
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32

McIver, J. D., G. L. Parsons, and A. R. Moldenke. "Litter spider succession after clear-cutting in a western coniferous forest." Canadian Journal of Forest Research 22, no. 7 (July 1, 1992): 984–92. http://dx.doi.org/10.1139/x92-132.

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The litter spiders of a coniferous forest in western Oregon were trapped in pitfalls to study the effects of, and recovery after, clear-cutting. Traps were placed in old-growth sites (150–450 years) and in clearcuts of three different ages (4–7, 16–19, and 22–31 years); each age-class was represented by sites that differed along a gradient of moisture availability. A total of 8905 individuals were collected over the 2-year study period, comprising 93 species, 54 genera, and 15 families. Visual pursuit hunting spiders dominated clearcuts, while "sit and wait" microweb and trapdoor spiders dominated mature forests. Most of the common forest species were reestablished in the wettest sites by 30 years after clear-cutting; species composition in dry 30-year-old clearcuts more closely resembled the fauna of shrubby wet 16-year-old clearcuts. Microenvironmental conditions and the availability and species composition of prey are the most likely factors behind variation in spider species composition among sites. Prey and microenvironment are in turn largely influenced by canopy closure and litter depth. The use of litter spiders as bioindicators of litter habitat quality and forest recovery is discussed.
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33

Rondon, Xanic J., David L. Gorchov, Robert B. Noble, and Fernando Cornejo. "Aboveground carbon dynamics following strip clear-cutting in the Peruvian Amazon." Ecological Research 30, no. 4 (May 8, 2015): 693–703. http://dx.doi.org/10.1007/s11284-015-1271-5.

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34

Schmalholz, Martin, and Kristoffer Hylander. "Succession of bryophyte assemblages following clear-cut logging in boreal spruce-dominated forests in south-central Sweden — Does retrogressive succession occur?" Canadian Journal of Forest Research 39, no. 10 (October 2009): 1871–80. http://dx.doi.org/10.1139/x09-113.

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The recovery process of boreal bryophyte communities after clear-cutting was studied in a chronosequence in south-central Sweden. We hypothesized that high initial grass cover on clearcuts, high litter cover and low light levels during canopy closure, and shortage of coarse woody substrates would constrain recovery in different ways. Instead, both epigeic and epixylic guilds (i.e., species growing on forest floor and deadwood) displayed a gradual increase in similarity over time from the clear-cut phase, perhaps because of the absence of distinct peaks in needle litter and canopy cover. Epixylic species started to recover long before the accumulation of deadwood, indicating that microclimate rather than substrate availability was the most constraining factor during the first 50 years. Since we did not find any other bottlenecks during the succession after clear-cutting, conservation measures aiming at decreasing local extinction rates during clear-cutting may also increase long-term persistence. On the other hand, as the results from the epixylic guild suggest, other factors during the forest succession, such as the development of a suitable microclimate, might be more important for some organisms, thus possibly mitigating such long-term positive effects of adjusted management during the clear-cutting operation.
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35

Duchesne, Luc C., and Suzanne Wetzel. "Effect of clear-cutting, prescribed burning and scarification on litter decomposition in an Eastern Ontario jack pine (Pinus banksiana) ecosystem." International Journal of Wildland Fire 9, no. 3 (1999): 195. http://dx.doi.org/10.1071/wf00016.

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Mass losses of litter bags containing leaf litter of Pinus banksiana Lamb., Quercus rubra L., Pteridium aquilium (L.) Kuhn, and Populus tremuloides Mchx. were compared in a jack pine ecosystem after clear-cutting, clear-cutting plus prescribed burning, and clear-cutting plus disk trenching scarification. Controls consisted of litterbags left in undisturbed plots. Mass losses were significantly affected by treatment types and litter types. The greatest differences among treatments were observed after 1 year of field incubation whereas there were considerably fewer differences among treatments after 3 years of incubation in the field. Initial decomposition of P. tremuloides and Q. rubra litter was greatest in the control plots. Scarified plots showed the slowest decomposition rates. Mass losses were not significant among treatments and litter types after 3 years incubation except for P. aquilinum litter on clear-cut and scarified plots.
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36

Pothier, David. "Ten-year results of strip clear-cutting in Quebec black spruce stands." Canadian Journal of Forest Research 30, no. 1 (February 1, 2000): 59–66. http://dx.doi.org/10.1139/x99-189.

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Regeneration of first-cut strips in a two-cut system of strip clear-cutting was compared to that of large clear-cutting in four different areas representative of the black spruce (Picea mariana (Mill.) BSP) stands of the boreal forest of Quebec. Seedlings were more evenly distributed in clearcut strips than in large clearcuts. Differences of about 10 000 black spruce seedlings per hectare and 20% of stocking were observed in favour of clearcut strips compared to large clearcuts. Black spruce stocking was about 14% larger on lowland than on upland sites but height growth was better on upland sites. A regeneration problem similar to that of large clearcuts was observed when the second strips were cut. One year after cutting these second strips, winter harvesting resulted in a 23% gain in black spruce stocking as compared to summer harvesting. Even if black spruce stocking marginally increased during the years following winter harvesting, the height advantage of the preserved advance growth justifies the application of this harvesting method. The strip clear-cutting system effectively improved the stocking of former black spruce stands but if the stocking level of advance growth is adequate, careful harvesting to preserve advance regeneration should be the preferred method since it would be more cost-efficient.
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37

Henriksen, A., and L. A. Kirkhusmo. "Effects of clear-cutting of forest on the chemistry of a shallow groundwater aquifer in southern Norway." Hydrology and Earth System Sciences 4, no. 2 (June 30, 2000): 323–31. http://dx.doi.org/10.5194/hess-4-323-2000.

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Abstract. As part of the national monitoring programme for long-range transported air pollutants, four groundwater aquifers in southern Norway were monitored for acidification trends during the period 1980 – 1995. For the monitoring station, Langvasslia in south eastern Norway, sampling continued until the end of 1999. This groundwater aquifer is about 3 km north east of the calibrated catchment Lake Langtjern. The catchment of the groundwater aquifer, covered completely by Norway spruce, was clear-cut in September 1986 and was treated with glyphosate in the summer, 1991. The chemical effects on the chemistry of the groundwater are generally similar to those observed in stream-water from clear-cut areas: increases in water runoff, water temperature, concentrations of K, NO3, and organic carbon (TOC), and decrease in SO4 concentration. In the groundwater aquifer, inorganic Al and ANC increased more than would have been expected without clear-cutting. By 1999 NO3 concentrations were nearly the same as prior to clear-cutting, whereas K still was elevated. Keywords: Groundwater; clear-cutting; water chemistry; monitoring.
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38

Phillips, M. J., and K. M. Goh. "Extractable Soil Nitrogen Following Clear-cutting and Burning in a Beech Forest." Soil Science Society of America Journal 49, no. 6 (November 1985): 1563–68. http://dx.doi.org/10.2136/sssaj1985.03615995004900060046x.

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39

Phillips, M. J., and K. M. Goh. "Extractable Soil Nitrogen Following Clear-cutting and Burning in a Beach Forest." Soil Science Society of America Journal 49, no. 6 (November 1985): NP. http://dx.doi.org/10.2136/sssaj1985.03615995004900060068x.

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40

Rebane, Sille, Kalev Jõgiste, Andres Kiviste, John A. Stanturf, and Marek Metslaid. "Patterns of Carbon Sequestration in a Young Forest Ecosystem after Clear-Cutting." Forests 11, no. 2 (January 21, 2020): 126. http://dx.doi.org/10.3390/f11020126.

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A large area of Estonian hemiboreal forest is recovering from clear-cut harvesting and changing carbon (C) balance of the stands. However, there is a lack of information about C- source/sink relationships during recovery of such stands. The eddy covariance technique was used to estimate C-status through net ecosystem exchange (NEE) of CO2 in two stands of different development stages located in southeast Estonia in 2014. Measured summertime (June–September) mean CO2 concentration was 337.75 ppm with mean NEE −1.72 µmol m−2 s−1. June NEE was −4.60 µmol m−2 s−1; July, August, and September NEE was −1.17, −0.77, and −0.25 µmol m−2 s−1, respectively. The two stands had similar patterns of CO2 exchange; measurement period temperature drove NEE. Our results show that after clear-cutting a 6-year-old forest ecosystem was a light C-sink and 8-year-old young stand demonstrated a stronger C-sink status during the measurement period.
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41

Johnson, Chris E., Arthur H. Johnson, Thomas G. Huntington, and Thomas G. Siccama. "Whole-Tree Clear-Cutting Effects on Soil Horizons and Organic-Matter Pools." Soil Science Society of America Journal 55, no. 2 (1991): 497. http://dx.doi.org/10.2136/sssaj1991.03615995005500020034x.

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42

Sorvari, Jouni, and Harri Hakkarainen. "Forest Clear-Cutting Causes Small Workers in the Polydomous Wood AntFormica aquilonia." Annales Zoologici Fennici 46, no. 6 (December 2009): 431–38. http://dx.doi.org/10.5735/086.046.0604.

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43

Maita, E., and M. Suzuki. "Change in the Monthly Water Yield after Clear-cutting in Fukuroyamasawa, Chiba." Journal of the Japanese Forest Society 89, no. 4 (2007): 278–87. http://dx.doi.org/10.4005/jjfs.89.278.

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44

Inoue, Akio, Hanako Takaoka, Nobuya Mizoue, Tetsuji Ota, Kotaro Sakuta, and Kazukiyo Yamamoto. "A Simple Model for Estimating Light Environment in Strip Clear-cutting Stands." Journal of the Japanese Forest Society 95, no. 5 (2013): 245–52. http://dx.doi.org/10.4005/jjfs.95.245.

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45

Mallik, A. U., F. W. Bell, and Y. Gong. "Regeneration behavior of competing plants after clear cutting: implications for vegetation management." Forest Ecology and Management 95, no. 1 (July 1997): 1–10. http://dx.doi.org/10.1016/s0378-1127(97)00012-1.

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46

Berthelsen, B. O., E. Steinnes, and R. Næumann. "Distribution of 137Cs in surface soils as affected by forest clear-cutting." Journal of Environmental Radioactivity 42, no. 1 (January 1999): 39–49. http://dx.doi.org/10.1016/s0265-931x(98)00029-0.

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47

Duggin, J. A., G. K. Voigt, and F. H. Bormann. "Autotrophic and heterotrophic nitrification in response to clear-cutting northern hardwood forest." Soil Biology and Biochemistry 23, no. 8 (January 1991): 779–87. http://dx.doi.org/10.1016/0038-0717(91)90149-e.

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48

Johnson, C. E., R. B. Romanowicz, and T. G. Siccama. "Conservation of exchangeable cations after clear-cutting of a northern hardwood forest." Canadian Journal of Forest Research 27, no. 6 (June 1, 1997): 859–68. http://dx.doi.org/10.1139/x96-192.

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49

Lundström, Johanna, Fredrik Jonsson, Karin Perhans, and Lena Gustafsson. "Lichen species richness on retained aspens increases with time since clear-cutting." Forest Ecology and Management 293 (April 2013): 49–56. http://dx.doi.org/10.1016/j.foreco.2012.12.027.

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50

Dahlberg, Anders, and Elna Stenström. "The effect of clear-cutting on the ectomycorrhizal flora on scots pine." Agriculture, Ecosystems & Environment 28, no. 1-4 (February 1990): 91–94. http://dx.doi.org/10.1016/0167-8809(90)90020-e.

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