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Rehabilitation as a method of understanding vegetation change in Paulshoek, Namaqualand.Simons, Liora-lee January 2005 (has links)
The main aim of this study was to test rehabilitation interventions in a system altered by heavy grazing, and to develop methods of monitoring these interventions.
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Rehabilitation as a method of understanding vegetation change in Paulshoek, Namaqualand.Simons, Liora-lee January 2005 (has links)
The main aim of this study was to test rehabilitation interventions in a system altered by heavy grazing, and to develop methods of monitoring these interventions.
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Mycorrhiza re-establishment on post-mined rehabilitated areas of the Brand se Baai Succulent Karoo vegetation.Ndeinoma, Albertina 12 1900 (has links)
Thesis (MSc (Botany and Zoology)--University of Stellenbosch, 2006. / Parts of the West Coast Strandveld and adjacent Succulent Karoo on the arid coast of
Namakwaland in the Western Cape of South Africa are subject to surface mining. An
understanding of mycorrhizal association of plants in the natural vegetation of this
area could contribute to the improvement of post-mining re-vegetation of the area.
This study investigated mycorrhizal association of plants in the West Coast
Strandveld, and compared mycorrhizal infection rates of soils taken from natural
vegetation to soils from post-mined rehabilitated vegetations. The study was divided
into two components.
In the first component a pot experiment was conducted in the greenhouse to assess
vesicular-arbuscular mycorrhiza (AM) infectivity of post-mined rehabilitated areas of
Brand se Baai in Namakwa Sands mining areas. Rehabilitated areas used in this study
included sites that has been strip mined for heavy minerals and then progressively
backfilled with sub-soil sand remaining after mineral extraction (tailings), topsoil and
translocated plants in an effort to restore the structure and functional aspects of the
mined site to its original (pre-mining) ecosystem. Rehabilitated sites 1 assessed in this
study included sites backfilled with: tailings + translocated plants (TP); tailing +
topsoil + translocated plants (TSP) and tailings + topsoil only (TS). Natural sites (N)
were also assessed to serve as reference points. AM infection was evaluated as
percent root colonization on wheat planted as bioassay on sterilised sand and
inoculum from rehabilitated sites in the ratio of 3:1 respectively. Results of this study
component showed that mycorrhiza infectivity of rehabilitated soils was high on TSP
and TS because mining disturbance has been remedied by topsoil with or without
translocated plant replacement. The structural and chemical components of topsoil
used as rehabilitation material favoured re-establishment of microbial activities.
Infectivity was however low on soils rehabilitated with tailings and translocated
plants (TP) because this treatment lacked topsoil which is a major source of infective
mycorrhizal propagules. Infectivity was also low in soils from undisturbed sites (N)
probably high phosphorus concentration or presence of perennial vegetation led to low mycorrhiza infection. Results showed that there was no significant effect of
mycorrhiza on plant growth rate, nutrient uptake or carbon cost of mycorrhizal plants
when related to non-mycorrhizal plants, instead the biomass production and nutrient
contents of plants were determined by chemical properties of treatment soils.
The second component of the study investigated presence of mycorrhiza on randomly
selected common indigenous species of Aizoaceae, Asparagaceae, Asteraceae,
Chenopodiaceae, Fabaceae, Lamiaceae, Mesembryanthemaceae, Restionaceae,
families growing on unmined areas of the study site. Total mycorrhiza infection was
recorded on 85% of the assessed species with percent infection level ranging from 8%
in Atriplex lindleyi and Drosanthemum hispidum to 98% in Salvia lanceolata.
Functional mycorrhizal association with arbuscule structures were however only
observed on 15% of all species assessed. Low arbuscules infection observed in
indigenous species assessed in this study could be associated with the timing of
mycorrhiza infection assessment and root competition in the soil. There was no
infection observed on four species belonging to Chenopodiaceae, Zygophyllaceae,
Sterculiaceae, and Asteraceae families, which represented 15% of all species
assessed. Most species belonging to Chenopodiaceae and Zygophyllaceae have been
reported as non-mycorrhizal in other studies, absence of mycorrhiza on the remaining
three families species observed in this study require further confirmation.
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Monitoring rehabilitation success on Namakwa Sands heavy minerals mining operations, Namaqualand, South AfricaBlood, Jeremy Russell 12 1900 (has links)
Thesis (MScConsEcol(Conservation Ecology and Entomology)--University of Stellenbosch, 2006. / Anglo American Corporation’s Namakwa Sands heavy minerals mining and beneficiation operation has
been strip-mining a heavy mineral deposit, rich in the commercially valuable minerals ilmenite, rutile and
zircon, since September 1994. The mine is located in the vicinity of Brand-se-Baai on the west coast of
South Africa, approximately 385 km north of Cape Town. Strip-mining causes total destruction of natural
ecosystems through the removal of vegetation and soil in the area where mining is being undertaken.
Namakwa Sands has been rehabilitating mined out areas as the mining front moves forward. Due to the
difficulty of rehabilitating mined out areas as a result of harsh environmental factors, Namakwa Sands has
initiated various research projects to gain an understanding of the baseline conditions and ecosystem
function in order to increase plant cover and biodiversity on post-mined areas. This on-going research
and the development of rehabilitation and mining techniques have resulted in the implementation of four
rehabilitation techniques varying in investment of topsoil replacement, seeding and plant translocation.
This study assesses the success and effectiveness of these techniques in terms of various vegetation
and soil parameters. In addition, those parameters that are considered useful for monitoring are identified.
This study indicated that topsoil replacement and plant translocation facilitate the return of similarity,
species richness, species diversity and vegetation cover to post-mined areas. The rehabilitation site that
had the greatest amount of biological input (topsoil replacement and plant translocation) appeared to be
the most successful technique in facilitating vegetation recovery similar to reference sites. In comparison,
the site that had the least amount of biological input performed the worst and requires adaptive
management, e.g. reseeding and / or plant translocation. Namakwa Sands should continue to replace
topsoil in all future rehabilitation efforts and, when possible (e.g. after sufficient winter rain), continue to
translocate species in multi-species clumps.
In terms of species selected for translocation, Othonna cylindrica, Ruschia versicolor and Lampranthus
suavissimus should be considered for future large-scale translocation projects. Zygophyllum morgsana
appears to be more difficult to re-establish under the current climatic conditions (below average rainfall).
The long-term viability of rehabilitated Z. morgsana populations needs to be determined before
considering this species for any future large-scale translocation purposes. No translocated Asparagus
spp. individuals survived and should therefore not be considered for any further translocation purposes.
The grass Ehrharta calycina, which is dominant in the site seeded, should continue to be considered for
future seeding.
Species and functional diversity appear to be the most limiting factors within all the rehabilitation sites and
Namakwa Sands will not be able to meet their long-term objective of small-stock farming if diversity and
the number of palatable species do not increase significantly. Adaptive management should seriously be
considered in order to speed up this process. Alternatively, an appropriate grazing strategy, which is
related to the Tetragonia fruticosa dominated vegetation within rehabilitation sites, would need to be
determined and adopted.More time is needed to ameliorate the rehabilitated soil profiles to the same level as in reference sites,
especially with regard to carbon, pH and sodium levels. In order to increase organic matter within
rehabilitation areas, Namakwa Sands should consider creating clumps with cleared vegetation from the
mining front.
Since the long-term rehabilitation goal has not been achieved, Namakwa Sands will need to continue to
monitor plant and soil changes until it has been achieved. The objectives of the current rehabilitation
programme are limited and Namakwa Sands should develop additional objectives relating to the structure
and function of the natural vegetation. This will give a better indication of whether rehabilitation sites are
progressing towards the desired end point and if adaptive management is required. In addition, the
current monitoring programme (vegetation survey) implemented at Namakwa Sands could be improved
by increasing the vegetation parameters to be monitored. It is recommended that the following vegetation
parameters be monitored as part of the long-term monitoring programme: species composition and
similarity, species richness, species diversity, vegetation cover, species dominance, vertical structure and
functional diversity of the vegetation (clumps and inter-clumps). It is also recommended that carbon, pH
and sodium of soil profiles be monitored as part of the long-term monitoring programme. These
parameters should not be seen as exhaustive as this study only considered various vegetation
parameters and soil chemistry between rehabilitation and reference sites. The results of other studies on
the fauna, mycorrhiza, insects, etc. should also be taken into consideration and the monitoring
parameters expanded accordingly.
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Strip mining rehabilitation by translocation in arid coastal Namaqualand, South AfricaMahood, Kirsten 03 1900 (has links)
Degree of Master of Forestry (Conservation Ecology) / Thesis (MSc)--Stellenbosch University, 2003. / Full text to be digitised and attached to bibliographic record. / ENGLISH ABSTRACT: This study investigates the use of top-soiling, irrigation and translocating indigenous plants to
facilitate the cost-effective return of a mined landscape to its former land-use (small stock
farming) in an arid winter rainfall Succulent Karoo shrub land biome on the West Coast of South
Africa.
Effects of topsoil stockpiling and subsoil mineral concentration on soil fertility and chemistry
were investigated, as soils are likely to determine rates of vegetation recovery on post-mined
areas. Results of a radish bioassay show that stockpiling topsoil and mineral concentration subsoil
decreased soil fertility. Mineral concentration decreased phosphorus, potassium, calcium,
magnesium, carbon and nitrogen levels significantly relative to other soil treatments. Sodium in
freshly deposited tailings was at potentially toxic levels and significantly higher than for all other
soil treatments. Spreading of stockpiled topsoil over tailings may ameliorate harsh conditions
created by mineral separation.
Translocation of plants from pre-mined to post-mined areas was carried out on a trial basis in an
effort to facilitate the return of natural vegetation and processes to strip-mined landscapes. Five
local indigenous plant species: Asparagus spp., Ruschia versicolor, Othonna cylindrica,
Lampranthus suavissimus and Zygophyllum morgsana were planted into multi-species clumps in
a replicated experiment. Variables examined in the translocation trial included the effects of
plant origin, soil treatment and/or irrigation on plant survival and establishment. The proportion
of O. cylindrica transplants surviving for 15 months was greater than for other species. Whole
plants survived better than salvaged plants, and Asparagus spp., R. versicolor, L. suavissimus
and Z. morgsana survived better on stockpiled topsoil spread over tailings than on tailings alone.
Irrigation had no consistent effect across species and treatment replicates. Salvaged-plant
clumps were significantly larger than whole-plant clumps at planting, however, this effect was
not observed after 12 months, indicating that whole-plant clumps grew faster than salvaged-plant
clumps. The evergreen, leaf succulent shrubs O. cylindrica, L. suavissimus and R. versicolor
appeared to be most suitable for large-scale translocation at Namakwa Sands.
The return of biodiversity and changes in soil quality 15 months after translocation trials began
were compared for combinations of top-soiling, irrigation, plant translocation and unmodified
tailings. Irrigation may reduce biodiversity and seedling densities. Over a 15-month period following back filling and topsoil spreading, sodium, potassium and calcium appeared to return
to levels observed for undisturbed soils. Magnesium remains at levels lower than in pre-mined
soil conditions. Soil conditions may be more conducive to plant establishment and rehabilitation
after back-filling of tailings and topsoil spreading. Electrical resistance increased over time
indicating a reduction of free salts and salinity on rehabilitation sites. Phosphorus did not return
to pre-disturbance levels, and carbon remained below pre-mining levels for at least 15 months
after rehabilitation began, remaining a potential limiting factor in rehabilitation.
Each rehabilitation technique that a mine employs has costs and benefits, and it is increasingly
important that insights from ecology and economics are coupled if restoration efforts are going to
succeed. A review of valuation systems indicates that Discounted Cash Flow Techniques (DCF)
are suitable for valuation of rehabilitation operations. / AFRIKAANSE OPSOMMING: Hierdie studie ondersoek die gebruik van bogrond, besproeiing en die oorplanting van inheemse
plante om die koste-effektiewe rehabilitasie van 'n stroopmynlandskap in die droë, winter reënval
streek, Vetplant Karoo aan die Weskus van Suid-Afrika, wat vroeër gebruik is vir kleinvee
boerdery, te bespoedig
Die uitwerking van bogrondopberging en minerale konsentrasie op vrugbaarheid en chemise
komposisie van grond is ondersoek, aangesien dié gronde gewoonlik die herstelspoed van
plantegroei op 'n ou myn terein bepaal. Uitslae van radys proewe toon dat berging van bogrond
en minerale konsentrasie van die onderliggende grond vrugbaarheid van grond laat afneem.
Mynaktiwiteite en die minerale konsentrasie lei tot 'n betekenisvolle verlies aan fosfaat, kalium,
kalsium, magnesium, koolstof en stikstof as die geval met ander bedrywighede. Die vlak van
natrium in oorgeblywende sand na die minerale ekstraksie is hoogs giftig en is veel hoër as na
ander bedrywighede. Die toediening van bogrond oor die oorblywende sand verbeter die
toestand wat deur die skeiding van minerale veroorsaak is.
Oorplasing van plante vanaf ongemynde na rehabilitasie gebiede is op proefbasis uitgevoer in 'n
poging om die terugkeer van natuurlike plantegroei by die strookmyn te bespoedig. Vyf plaaslike
inheemse plantspesies: Asparagus spp., Ruschia versicolor, Othonna cylindrical, Lampranthus
suavissimus en Zygophyllum morgsana is in multi-spesie groepe geplant. Veranderlikes getoets
tydens hierdie proef sluit in plantoorsprong, grond behandeling, en/of besproeiing, op die
oorlewing en vestiging van plante. 'n Groter proporsie O. cylindrical as enige ander spesie het na
15 maande oorleef. Heel plante het beter oorleef as beskadigde plante. Asparagus spp., R.
versicolor, L. suavissimus en Z. morgsana het beter oorleef op gebergde bogrond oor
oorblywende sand as op oorblywende sand self. Besproeiing het nie 'n volgehoue uitwerking
gehad op spesies of op herhaalde replisering nie. Beskadigde plantgroepe was groter as heelplant
groepe toe hulle geplant is maar na 12 maande is opgemerk dat die heel-plante vinniger gegroei
het. Die immergroen vetplante, 0. cylindrical, L. suavissimus en R. versicolor blyk die mees
geskik vir grootskaalse oorplanting by Namakwa Sands.
Herstel van biodiversiteit en veranderings in grondeienskappe 15 maande na proewe begin het, is
vergelyk m.b.t. die toediening van bogrond, besproeiing, oorplanting en onbehandelde
oorblywende sand. Besproeiing kan biodiversiteit en digtheid van saailinge verminder. Vyvtien maande na opvulling en die toediening van bogrond, het kalium, natrium en kalsium teruggekeer
na vlakke in onversteurde grond. Magnesium vlakke was nog altyd laer as dié voordat
mynaktiwiteite aangevang is. Terugplasing van sand en toediening van bogrond mag die
vestiging en rehabilitasie van plante bespoedig. Weerstand vermeerder met tyd wat 'n verlaaging
in vry soute en soutagtigheid in die grond wat gebruik is vir rehabilitasie aantoon. Fosfor het nie
teruggekeer tot vlakke van voorheen nie en vlakke van koolstofhet na 15 maande verlaag gebly,
en kan die potential tot rehabilitasie belemmer.
Elke rehabilitasie tegniek wat die myn gebruik bring kostes sowel as voordele mee. Om
restorasie pogings te laat slaag moet insigte vanaf ekologie en ekonomie saam ingespan word. 'n
Oorsig van waardasie sisteme toon dat Afslag Kontant Vloei Tegnieke geskik is vir die evaluasie
van rehabilitasie programme.
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