Biophysical Changes Resulting from 16 Years of Riparian Forest Rehabilitation: An Example from the Southern Ontario Agricultural Landscape

2008 ◽  
pp. 13-26 ◽  
Author(s):  
Maren Oelbermann ◽  
Andrew M. Gordon ◽  
Narinder K. Kaushik
Keyword(s):  
Agricultural Landscape ◽  
Riparian Forest ◽  
Southern Ontario ◽  
Biophysical Changes ◽  
Forest Rehabilitation

scholarly journals Pollination Potential of Riparian Hardwood Forests—A Multifaceted Field-Based Assessment in the Vistula Valley, Poland

Forests ◽  
2021 ◽  
Vol 12 (7) ◽  
pp. 907
Author(s):  
Andrzej N. Affek ◽  
Edyta Regulska ◽  
Ewa Kołaczkowska ◽  
Anna Kowalska ◽  
Katarzyna Affek
Keyword(s):  
Agricultural Landscape ◽  
Riparian Forest ◽  
Field Measurements ◽  
Threshold Value ◽  
Early Spring ◽  
Hardwood Forests ◽  
Floral Resources ◽  
Vistula River ◽  
Pollinator Abundance ◽  
Nesting Sites

Riparian forests with oaks, ashes and elms, now highly fragmented and rare in Europe, are considered hotspots for ecosystem services. However, their capacity to provide pollination seems to be quite low, although reports from in-situ research supporting this view are scarce. Our goal was therefore to thoroughly assess their pollination potential based on multifaceted field measurements. For this, we selected six test sites with well-developed riparian hardwood forests, located in the agricultural landscape along the middle Vistula River in Poland. We used seven indicators relating to habitat suitability (nesting sites and floral resources) and pollinator abundance (bumblebees and other Apoidea) and propose a threshold value (AdjMax) based on value distribution and Hampel’s test to indicate the level of pollination potential for this type of riparian forest. The obtained AdjMax for bumblebee density was 500 ind. ha−1, for Apoidea abundance—0.42 ind. day−1, while for nectar resources—200 kg ha−1. We demonstrate that the investigated small patches of the riparian hardwood forest have a higher pollination potential than reported earlier for riparian and other broadleaved temperate forests, but the indicators were inconsistent. As forest islands in the agricultural landscape, riparian hardwood forests play an important role in maintaining the diversity and abundance of wild pollinators, especially in early spring when there is still no food base available elsewhere.

scholarly journals Determinants of bird assemblage composition in riparian vegetation on sugarcane farms in the Queensland Wet Tropics

2015 ◽  
Vol 21 (1) ◽  
pp. 60 ◽  
Author(s):  
Anita F. Keir ◽  
Richard G. Pearson ◽  
Robert A. Congdon
Keyword(s):  
Riparian Vegetation ◽  
Wildlife Conservation ◽  
Agricultural Landscape ◽  
Riparian Zone ◽  
Riparian Forest ◽  
Agricultural Landscapes ◽  
Generalist Species ◽  
Assemblage Composition ◽  
Bird Assemblages ◽  
Wet Tropics

Remnant habitat patches in agricultural landscapes can contribute substantially to wildlife conservation. Understanding the main habitat variables that influence wildlife is important if these remnants are to be appropriately managed. We investigated relationships between the bird assemblages and characteristics of remnant riparian forest at 27 sites among sugarcane fields in the Queensland Wet Tropics bioregion. Sites within the remnant riparian zone had distinctly different bird assemblages from those of the forest, but provided habitat for many forest and generalist species. Width of the riparian vegetation and distance from source forest were the most important factors in explaining the bird assemblages in these remnant ribbons of vegetation. Gradual changes in assemblage composition occurred with increasing distance from source forest, with species of rainforest and dense vegetation being replaced by species of more open habitats, although increasing distance was confounded by decreasing riparian width. Species richness increased with width of the riparian zone, with high richness at the wide sites due to a mixture of open-habitat species typical of narrower sites and rainforest species typical of sites within intact forest, as a result of the greater similarity in vegetation characteristics between wide sites and the forest proper. The results demonstrate the habitat value for birds of remnant riparian vegetation in an agricultural landscape, supporting edge and open vegetation species with even narrow widths, but requiring substantial width (>90 m) to support specialists of the closed forest, the dominant original vegetation of the area.

Changes in streamside riparian forest canopy and leaf litter nutrient flux to soils during an emerald ash borer infestation in an agricultural landscape

2020 ◽  
Vol 22 (6) ◽  
pp. 1865-1878 ◽  
Author(s):  
David Kreutzweiser ◽  
David Dutkiewicz ◽  
Scott Capell ◽  
Paul Sibley ◽  
Taylor Scarr
Keyword(s):  
Leaf Litter ◽  
Forest Canopy ◽  
Agricultural Landscape ◽  
Riparian Forest ◽  
Emerald Ash Borer ◽  
Nutrient Flux

scholarly journals Past and present land use influences on tropical riparian zones: an isotopic assessment with implications for riparian forest width determination

2016 ◽  
Vol 16 (2) ◽  
Author(s):  
Luiz Felippe Salemi ◽  
Silvia Rafaela Machado Lins ◽  
Elizabethe de Campos Ravagnani ◽  
Marcelo Magioli ◽  
Melissa Gaste Martinez ◽  
...  
Keyword(s):  
Land Use ◽  
Organic Matter ◽  
Agricultural Landscape ◽  
Riparian Forest ◽  
Stream Water ◽  
Agricultural Landscapes ◽  
Riparian Areas ◽  
Stream Water Quality ◽  
Exotic Grasses ◽  
Forest Act

Abstract In this article, by using carbon stable isotopes, we assessed the past and present land use influences that riparian areas are subject within agricultural landscapes. Emphasis is given to the understanding of the effects of the 2012 Brazilian Forest Act on such areas. We selected five riparian areas within a highly C4 dominated agricultural landscape. Three of them had 30 meters native riparian forest buffer (NRFB) and two of them had 8 meter and no NRFB. We used three 100 meter-transects located 5, 15 and 30 meters relative to stream channel to obtain soil samples (0 - 10 cm). All riparian areas presented soil carbon isotopic signatures that are not C3 (native forests) irrespective of having or not 30 meters NRFB. Two cases presenting less than 30 meters NRFB had higher C4 derived carbon contribution. All of the other three areas that followed the 30 meters NRFB presented, to some degree, C4 derived carbon, which was attributed to C4 organic matter deposition originated from cultivated areas and, in one case, to the persistence of former exotic grasses. With the 2012 Forest Act allowing narrower buffers (< 30 meters), we expect C4 contributions to soil organic matter to remain high in riparian areas and streams within agricultural landscapes dominated by C4 plants where 30 meter NRFB is no longer required. Such contributions will likely continue to have detrimental effects on stream water quality and biota.

Modification and Assessment of an Index of Biotic Integrity to Quantify Stream Quality in Southern Ontario

1988 ◽  
Vol 45 (3) ◽  
pp. 492-501 ◽  
Author(s):  
Robert J. Steedman
Keyword(s):  
Land Use ◽  
Brook Trout ◽  
Forest Cover ◽  
Riparian Forest ◽  
Spatial Scales ◽  
Index Of Biotic Integrity ◽  
Biotic Integrity ◽  
Southern Ontario ◽  
Stream Quality ◽  
Watershed Urbanization

A multivariate measure of stream quality, the Index of Biotic Integrity (IBI), was adapted to southern Ontario and calibrated to watershed land use on a variety of spatial scales. The fish fauna at 209 stream locations on 10 watersheds near Toronto, Ontario, was sampled with a backpack electrofisher in the summers of 1984 and 1985 to provide biological information for the IBI. Watershed urbanization, forest cover, and riparian forest were measured from 1:50,000 scale topographic maps and related to IBI estimates by linear regression. Of the biological measures tested, species richness, local indicator species (brook trout (Salvelinus fontinalis) and Rhinichthys spp.), abundance of large piscivores, fish abundance, and incidence of blackspot disease were found to contribute significantly to IBI estimates. Variation in IBI estimates at the same location ranged from 0 to 8% within the sample season and from 0 to 24% between years. Linear models based on measures of watershed urbanization and forest cover accounted for 11–78% of the variation in IBI scores, depending on the spatial scale of the analysis. Significant IBI/land use relationships were found with whole-basin IBI estimates and for IBI estimates from individual stream reaches. Land use immediately upstream of sample stations was most strongly associated with stream quality as measured by the IBI.

scholarly journals Temporal and spatial resource use by female three-toed sloths and their young in an agricultural landscape in Costa Rica

2018 ◽  
pp. 1743-1755
Author(s):  
Oscar Ramirez ◽  
Christopher Vaughan ◽  
Geovanny Herrera ◽  
Raymond Guries
Keyword(s):  
Costa Rica ◽  
Home Range ◽  
Tree Species ◽  
Agricultural Landscape ◽  
Riparian Forest ◽  
Habitat Type ◽  
Riparian Forests ◽  
Home Ranges ◽  
Secondary Forests ◽  
Use Of Resources

The information on ecological behavior of wild sloths is very scarce. In this study we determined the home ranges and resources used by three adult female three-toed sloths (Bradypus variegatus) and their four young in an agricultural matrix of cacao (Theobroma cacao), pasture, riparian forests and living fencerows in Costa Rica. Births occurred during November-December and the young became independent at five to seven months of age. Initially, mothers remained fixed in one or a few trees, but expanded their use of resources as young sloths became independent from them. Mothers initially guided the young to preferred food and cover resources, but they gradually left their young in small nucleus areas and colonized new areas for themselves. Home range sizes for young sloths (up to seven months of age) varied between 0.04-0.6 hectares, while home range sizes for mothers varied from 0.04-25.0 hectares. During the maternal care period, 22 tree species were used, with the most common being Cecropia obtusifolia (30.9%), Coussapoa villosa (25.6%), Nectandra salicifolia (12.1%), Pterocarpus officinalis (5.8%) and Samanea saman (5.4%). However, young sloths used only 20 tree species, with the most common being C. villosa (18.4%), S. saman (18.5 %) and N. salicifolia (16.7%). The cacao agroforest was used only by mother sloths and never by their young following separation. However, in the riparian forest, both mother sloths and young used the tree species. A total of 28 tree species were used by the mother sloth; including the food species: C. obtusifolia, C. villosa, N. salicifolia and P. officinalis. However, the young used 18 trees species in this habitat with N. salicifolia and S. saman most commonly used, although they rested and fed during the day in C. obtusifolia, C. villosa and O. sinnuata. The cacao agroforest with adjacent riparian forests and fencerows provides an important habitat type that links the smaller secondary forests and other patches.

Bird assemblages of a fragmented agricultural landscape and the relative importance of vegetation structure and landscape pattern

2007 ◽  
Vol 34 (3) ◽  
pp. 185 ◽  
Author(s):  
Matthew Johnson ◽  
Paul Reich ◽  
Ralph Mac Nally
Keyword(s):  
Landscape Pattern ◽  
Riparian Vegetation ◽  
Agricultural Landscape ◽  
Riparian Forest ◽  
Landscape Context ◽  
Forest Patches ◽  
Bird Assemblages ◽  
Eastern Australia ◽  
Mosaic Landscapes ◽  
Agricultural Areas

Many of the world’s agricultural areas have greatly reduced levels of natural vegetation. This results in highly fragmented mosaic landscapes with multiple land-use types. We examined the importance of vegetation and landscape pattern by comparing the bird assemblages of riparian zones, non-riparian forest patches, and pasture in a fragmented agricultural landscape in south-eastern Australia. Bird surveys were conducted every four weeks at 27 sites in the Goldfields region of central Victoria for one year. The landscape context (position and shape of patches) and vegetation attributes were measured for each site. We found that bird assemblages strongly differed among these landscape elements. Mean abundance was significantly greater at forested patches, and there was a three-fold reduction in species richness at pasture sites. Bird assemblage structure was influenced substantially more by vegetation than by the landscape context of sites. Our results indicate that riparian vegetation is a key element for avian diversity, even in massively altered landscapes. The restoration of riparian vegetation and its connectivity with adjacent forest types would greatly benefit bird assemblages in agricultural areas.

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