International Journal of Environmental Impacts

3 watersheds, the average increase in the maximum daily volume of flow from the treatment watershed is caused by the increase in the cut-off, respectively, from eqns (8) and (12) in eqns (9) and (13); can be considered constant regardless of the rainfall volume that produces the maximum daily runoff. When the slopes of the linear regression lines for the control and treatment periods are nearly equal, as in definitions (8) and (9) and those (12) and (13), forest land is preserved. 2, the flood mitigation function of the forest was considered degraded due to clear-cutting, avalanche and slope failure because the slopes of the linear regression lines were greater in the treatment period than in the control period (Fig. 5b) ; there was a maximum estimated daily increase in runoff relative to rainfall volume. producing the maximum daily runoff due to slope failure and transition to bare soil at 20%. The above discussion suggests that the loss of forest land associated with slope failure and avalanches causes a degradation of the flood mitigation function.

Forest vegetation may be misunderstood as having no recognized role in the flood mitigation function because degradation of the flood mitigation function may not be observed in treatment catchment areas where only the forest vegetation is affected while the forest floor is preserved, such as the Minamidani and none. nevertheless, forest vegetation contributes to flood mitigation by preserving the forest floor and enhancing slope stability with tree root systems. this effect is reflected in the deterioration of the flood mitigation function caused by slope failure in catchment no. of the three treatment catchments assessed in this report, slope failure occurred after clear-cutting in catchment no. 2, while it did not occur after a forest fire and wilting of trees in Minamidani catchment area or after clear-cutting in catchment area No. the reasons for these different outcomes are discussed at the end of this report. prior to that discussion, a forest management system to prevent collapse on slopes is briefly described [7]. While hardware is "the tool that embodies the technology in the form of a material or physical object", software is "the information base for the tool" [1].

CO 2 AND SO 2 EMISSIONS FROM THE HULENE DUMp, MUNICIpALITY OF MApUTO

Measurements were taken in the last week of each month during a 6-month period of the dry season, starting in April and ending in September 2021. The city of Maputo is in Mozambique on the western shore of Maputo Bay in the extreme south of the country, close to the South African border and Swaziland's border. These points, according to the location of the biogas measurement points in the Hulene landfill, are on the highest quota lines where the waste dumped is relatively more recent.

From the graph comparing the roof temperatures, there were higher temperatures on the upper black roof compared to the green roof, and the slope of the lines indicated the mitigating effect of the green roof on heat waves. Additionally, a mathematical model was used to determine the ceiling temperature of the Javits Center to within 3%. Additionally, the proximity of the Javits Center to the Lincoln Tunnel was considered.

For the experimental models tested in the laboratory, the heat exchange between the rainwater and the green roof material occurs in the first minutes of the storm. From the slope of the control roof and green roof hydrographs, peak flows can be determined with R2 greater than 0.9. Most of the freshwater resources are threatened by harmful algal blooms (HABs), which increase in severity in developing countries (Vilmi et al., 2015).

2, spatial distribution of low algae content was observed in the middle of the nandoni reservoir in the year.

AIR AND WATER POLLUTION 2022

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Public Perception of Government Role and Competence to Address Water-Related Problems Over a 34-Year Period in the Pacific Northwest, USA" Robert L.

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ENVIRONMENTAL IMPACTS