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At the pine site, by contrast, mulching had no obvious effect.
The proposed methods are experimented on airborne visible infrared imaging sensor (AVIRIS) data of Indian Pine Site.
Favourable interactions between genotype, site and silviculture are desired for growing radiata pine, site and silviculture being two components of environment.
Arguably, however, more important differences between the two study sites were those in fire severity, resulting in an elevated litter cover prior to mulching at the pine site but not at the eucalypt site, and in experimental design, with eight bounded erosion plots of 16 m2 installed at the eucalypt site as opposed to only four at the pine site (due to its limited size).
The results show that chloride depositions in canopy areas are significantly higher than those in the adjacent open field with 28% enhancement at the eucalyptus site and 89% at the pine site.
For example, Germain et al. (2016) reported white pine site index (dominant/codominant height at base age 50 in m) values of 25 and 16 for HWF and PDF respectively.
At continental or montane sites, EWUEGPP was around zero in winter and fluctuated greatly during the active growing season when GPP increased more than ET. At the semi-arid US-Me2 pine site, EWUEGPP increased steadily as drought progressed in summer and EWUEGPP peaked in early September when drought stress peaked.
Harvested sites (particularly retention cuts) were primarily preferred, and dry pine sites had a distinct fauna.
Composition and structure of forests on mixed-conifer sites were very similar to those on ponderosa pine sites.
Regeneration scenarios were based on empirical data from Savage and Mast [29], indicating that 50% of ponderosa pine sites investigated following a stand-replacing fire did not regenerate.
To address the need for such information we sampled 25 reference and 29 altered mixed-pine sites in a wetland-upland landscape mosaic representative of eastern Upper Michigan.
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