scholarly journals Forest plantations reduce soil functioning in terrestrial ecosystems from South Africa

Pedobiologia ◽  
2021 ◽  
pp. 150757
Author(s):  
Adenike Eunice Amoo ◽  
Manuel Delgado-Baquerizo ◽  
Olubukola Oluranti Babalola
Bothalia ◽  
2017 ◽  
Vol 47 (2) ◽  
Author(s):  
Alan R. Wood

Background: Fungi are a major component of the functioning of all terrestrial ecosystems. Objectives: To increase awareness of fungi as drivers of ecosystem processes, including invasion biology. Method: Here, I reviewed the information available regarding fungal invasions of native ecosystems in South Africa in the context of the National Status Report on Biological Invasions. Results: Only seven fungal species are regulated as invaders (all category 1b) under the National Environmental Management: Biodiversity Act (NEM:BA) AIS regulations. Four of these species are not yet known to occur in South Africa. Similarly, under the NEM:BA AIS regulations, two of the four species listed as prohibited (i.e. not present in the country but which would pose a threat if introduced) are already present in the country. The actual number of alien fungi in South Africa is much greater. A preliminary listing of alien fungal species is made, with a total of 9 pathogenic species known to attack indigenous plants, 11 saprotrophic species, 1 fish pathogen, 23 host-specific pathogens of listed alien terrestrial plants, 61 ectomycorrhizal species and 7 host-specific pathogens deliberately introduced as biological control agents. The majority of fungal species were introduced to South Africa most likely via the introduction of crop plants as passengers, although there are as yet very little details available on pathways of introduction into South Africa. Conclusion: For almost all aspects considered, it is concluded that there is simply not sufficient data to begin to understand the role and impact of fungal invasions in South Africa.


2010 ◽  
Vol 76 (2) ◽  
pp. 402
Author(s):  
M. Rouget ◽  
T. Smith ◽  
A. Driver

2003 ◽  
Vol 112 (1-2) ◽  
pp. 63-85 ◽  
Author(s):  
Mathieu Rouget ◽  
David M Richardson ◽  
Richard M Cowling ◽  
J.Wendy Lloyd ◽  
Amanda T Lombard

Bothalia ◽  
1983 ◽  
Vol 14 (3/4) ◽  
pp. 661-667 ◽  
Author(s):  
P. J. Weisser ◽  
R. Müller

Dune vegetation changes were studied qualitatively with the aid of air photos taken in 1937, 1957 and 1976.Results were transferred to 1:10 000 scale maps. In 1937 roughly 80% of the dune forest habitat was occupied by planted fields and post cultivation serai stages such as Secondary Grasslands and Dwarf Shrubland, Secondary Scrub and Acacia karroo Woodland. In three areas, the vegetation cover had been completely destroyed and drift sands had formed. In the 1950’s the trend of vegetation degradation was changed by the implementation of an afforestation programme by the Department of Forestry. The 1976 air photos indicate that the post cultivation serai stages of 1937 had been largely replaced by forest plantations. In secondary, unafforested areas the vegetation is evolving rapidly towards a Secondary Dune Forest.


2010 ◽  
Vol 30 (9) ◽  
pp. 1181-1195 ◽  
Author(s):  
Ndeke Musee

This paper attempts to quantify the potential risks posed by engineered nanomaterials (ENMs) to the aquatic and terrestrial ecosystems from cosmetic-based nanoproducts. The predicted environmental concentrations (PEC) were modelled for the silver (nAg) and titanium dioxide (nTiO2) nanoparticles embedded in cosmetic nanoproducts. The Johannesburg Metropolitan City (JHB City), in South Africa, was used as the reference study area. A mathematical model was applied to compute the quantities of ENMs flows from the cosmetic nanoproducts into the JHB City aquatic and terrestrial ecosystems. The risk quotient (RQ) of the nanoscale materials were evaluated as a ratio of PEC to the predicted no effect concentrations (PNEC). RQ values showed wide variance due to factors like; the quantities of ENMs, the fate and pathways of ENMs in the aquatic and terrestrial ecosystems, efficiency of the wastewater treatment plants (WWTP) as well as the economic and demographic data for South Africa and Switzerland. For the aquatic environment, the PEC values of nAg ranged from 2.80 × 10−3 to 6.19 × 10−1 μg L−1 whereas for nTiO2 the values ranged from 2.7 0 × 10−3 to 2.70 × 10−1 μg L−1 under the realistic dilution factor of 1 with the WWTP functioning at high removal efficiency regime. The RQ values in the aquatic ecosystems were mostly >1, indicating the potential risk of both nAg and nTiO2 but <<<1 in the terrestrial ecosystems. Our results provide the first quantification of ENMs potential risk into the environment Johannesburg City in a developing country’s natural and technical settings.


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