Academic literature on the topic 'Protea roupelliae'

AbstractMajor components of most southern African archaeological sites are stone, bone, and charcoal. A new technique for climate reconstruction utilizes measurements of vessel size and frequency in the cross-sectional xylem anatomy of archaeological charcoal from Collingham Shelter and Mhlwazini Cave in the Natal Drakensberg. Previous wood anatomical studies have shown that links exist among vessel diameter, vessel frequency and climate. The present study demonstrates that in relation to rainfall, vessel diameter in the species Protea caffra and Protea roupelliae correlated positively, whereas vessel frequency correlated negatively. In P. roupelliae, mean vessel diameter increases from 46 to 62 μm along a rainfall gradient ranging from 760 to 1665 mm. The significant correlations between rainfall and tangential vessel diameter for a charred sample of P. roupelliae suggest that such measures on an archaeological charcoal sample may be used to reconstruct rainfall patterns through time. Using nine assemblages of archaeological charcoal, generalized patterns of wetter and drier periods can be postulated. Comparison with contemporary values indicates that at 200 and 2400 yr B.P. the area near the archaeological sites was wetter than at present. A dry phase occurred between 1300 and 300 yr B.P. Values for the contemporary wood sample are the lowest observed, indicating that present conditions are much drier than those at any time within the last ca. 2000 yr. Dating resolution however, is insufficient to allow more-detailed interpretation of rainfall conditions over the past 2000 yr.

In a taxonomic study of yeasts recovered from nectar of flowers and associated insects in South Africa, 11 strains were found to represent two novel species. Morphological and physiological characteristics and sequence analyses of the large-subunit rRNA gene D1/D2 region, as well as the actin, RNA polymerase II and elongation factor 2 genes, showed that the two novel species belonged to the genus Metschnikowia. Metschnikowia drakensbergensis sp. nov. (type strain EBD-CdVSA09-2T = CBS 13649T = NRRL Y-63721T; MycoBank no. MB809688; allotype EBD-CdVSA10-2A = CBS13650A = NRRL Y-63720A) was recovered from nectar of Protea roupelliae and the beetle Heterochelus sp. This species belongs to the large-spored Metschnikowia clade and is closely related to Metschnikowia proteae, with which mating reactions and single-spored asci were observed. Metschnikowia caudata sp. nov. (type strain EBD-CdVSA08-1T = CBS 13651T = NRRL Y-63722T; MycoBank no. MB809689; allotype EBD-CdVSA57-2A = CBS 13729A = NRRL Y-63723A) was isolated from nectar of Protea dracomontana, P. roupelliae and P. subvestita and a honeybee, and is a sister species to Candida hainanensis and Metschnikowia lopburiensis. Analyses of the four sequences demonstrated the existence of three separate phylotypes. Intraspecies matings led to the production of mature asci of unprecedented morphology, with a long, flexuous tail. A single ascospore was produced in all compatible crosses, regardless of sequence phylotype. The two species appear to be endemic to South Africa. The ecology and habitat specificity of these novel species are discussed in terms of host plant and insect host species.

Aerial photography provides historic record of features at the time the photograph was captured, and can assist with exploring changes in the habitat of threatened species. The host-plant of the Critically Endangered, endemic Pennington’s Protea butterfly Capys penningtoni, the Common Sugarbush Protea caffra Meisn. subsp. caffra, is a resprouter after fire which eventually dies if burnt too frequently. Six sites (Marwaqa Nature Reserve, Impendle Nature Reserve, Clairmont Mountain Nature Reserve, Lotheni Nature Reserve, Lot 93 1821 near Mkhomazi River [Nxamalala Traditional Council] and Mt Le Sueur) where the butterfly species had been previously recorded were selected to estimate the number of adult P. caffra subsp. caffra trees present using aerial photographs (2009). Protea trees in the vicinity of the C. penningtoni butterfly collection sites were point-digitised off aerial photographs. Polygons were digitised around coverages of protea trees using a distance of 50 m between trees to determine the outer margin of each coverage. The imagery data were ground-truthed by verifying the location and identities of P. caffra subsp. caffra trees at each site, using a sample of the total number of digitised trees. The ground-truthing enabled the separation of P. caffra subsp. caffra trees from Silver Protea Protea roupelliae trees, and the separation of P. caffra subsp. caffra trees with overlapping canopies. Contemporary presence of P. caffra subsp. caffra trees in relation to presence in 2009 was determined. Fire frequency data for each site was obtained via landsatlook viewer (USGS). We found that the protea savanna at most of the sampled sites was burnt about once every year between July and September. This project indicated the potential utility of aerial photographs and aerial imagery for the purposes of assessing the status of P. caffra subsp. caffra and H. axyridis in the habitat of the Critically Endangered and endemic C. penningtoni and for directing the placement of sampling plots in the field.

Abstract A description is provided for Teratosphaeria maculiformis. Information is included on the disease caused by the organism, its transmission, geographical distribution, and hosts. HOSTS: Protea amplexicaulis, P. burchelli, P. caffra, P. compacta, P. compacta × magnifica cv. Pink Duke, P. cordata, P. cynaroides, P. eximia, P. gaguedi, P. grandiceps, P. lorifolia, P. magnifica, P. magnifica × susannae cv. Susara, P. neriifolia, P. nitida, P. obtusifolia, P. obtusifolia × magnifica cv. Shelia, P. punctata, P. roupelliae, P. simplex, P. speciosa, P. stokoei, P. susannae × eximia cv. Sylvia, P. repens, Protea spp. DISEASE: Leaf spot. GEOGRAPHICAL DISTRIBUTION: South Africa. TRANSMISSION: Wind borne ascospores.

The critically endangered Protea roupelliae ssp. hamiltonii persists as a single population (of 124 individuals in 2005) within the 26ha Dr Hamilton Reserve in Mpumalanga province, South Africa. Between 2000 and 2005, no recruitment had been observed. In order to aid the recovery of this species, aspects of its reproduction and conservation were studied, namely; (a) the relationship between the demographics and the reproductive capacity of the population, (b) the relationship between achene mass and germination, (c) methods of propagating the species ex-situ, (d) the ex-situ seed storage of the species and (e) methods of establishing seedlings in-situ (the reserve) in order to augment the small population. The reason for the decline of the species has been attributed to the reported high levels of herbivory before an antelope proof fence was erected. The survival and reproductive capacity of the species is sensitive to herbivory as browsing decreases canopy size and both achene production and germination were found to be significantly related to canopy size. The number of cones produced per plant (R2= 0.532; P<0.005), number of achenes filled with embryos (filled achenes) (R2=0.178; P=0.014), the mass of the achenes produced within a cone (R2=0.127; P=0.041) and the germination percentage of filled achenes (R2=0.200; P=0.009) increased with the plant canopy area. While the number of days for 50% of the achenes to germinate (T50) (R2=0.231; P=0.005), peak day of germination (R2=0.208; P=0.008) and mean days until germination (R2=0.270; P=0.002) decreased with plant canopy area. However, the percentage of filled achenes (seed set) did not increase with plant canopy area (R2=0.044; P=0.241). Each plant had a degree of autonomy in the mass of the achenes produced which was significantly different between plants (P<0.05). The mass of individual achenes from various plants was not related to the germination (rate or viability) of that achene. However, the germination percentage of filled achenes (R2=0.133; P=0.037), the peak value of germination (Czabator 1962) (P.V.) (R2=0.403; P<0.001), the T50 (R2=0.209; P=0.0074) and the mean number of days for achenes to germinate (R2=0.178; P=0.014) were all significantly related to the mean mass of the achenes produced within cones harvested from different plants. The achenes not filled with an embryo had a higher variation in mass and were significantly lighter than filled achenes (P<0.05). Mean seed set (n=33 cones) was 36.08±2.31% (±S.E) filled achenes per cone. By sorting achenes using a simple achene mass based selection method, a sample containing 93.67±1.46% filled achenes was selected per plant. Overall, the filled achenes had high germination percentages ranging from 57.67% to 97.00%, however, germination was sensitive to various pre-treatments. Soaking achenes in water for 48 hours before germination decreased the P.V. from 3.69 to 1.22 and germination percentage from 94.06% to 82.11% compared with un-soaked achenes. However, when embryos were excised from the seed coat after 48 hours soaking, both the P.V. and the germination percentage increased further to 6.03 and 97.00% respectively. Excised embryos did not germinate normally in-vitro when plated on various media but dedifferentiated into callus on all media tested (including growth regulator free media). The most effective regeneration via adventitious somatic embryogenesis (but not statistically significant) occurred on a growth regulator free medium (containing 2.21g.l-1 Murashige & Skoog (1962) salts with vitamins, 30.00g.l-1 sucrose and 3.00g.l-1 Gelrite® with a pH of 4.20) producing a mean of 4.66±1.09 (±S.E.) embryos per explant. Secondary somatic embryogenesis also occurred on a growth regulator free medium (containing 2.21g.l-1 Murashige & Skoog (1962) salts with vitamins, 30.00g.l-1 sucrose and 3.00g.l-1 Gelrite® with a pH of 5.20). The somatic embryos developed into plantlets (generally un-rooted) on media containing a high gibberellic acid to cytokinin ratio (3:1 by mass) and a growth regulator free medium (containing 2.21g.l-1 Murashige & Skoog (1962) salts with vitamins, 30.00g.l-1 sucrose and 3.00g.l-1 Gelrite® with a pH of 5.20). Limited success (5.77%) was achieved in rooting shoots (from somatic embryos) and transferring them to a greenhouse environment. Other vegetative propagation techniques were attempted, including the rooting of stem cuttings and direct shoot organogenesis but these were unsuccessful. As the achenes of Protea species are not long lived in-situ, the ex-situ conservation of achenes (and therefore the species) was tested. Achenes had low water contents (9.27±0.10%) and were therefore categorised as orthodox seeds (Roberts 1973). Germination percentages were high in all tested storage regimes (Ambient, 25°C, 4°C, -70°C and -196°C), including those at ultra-low storage temperatures and after 18 months ranged between 86.81% and 92.23%. Evidence of loss of germination vigour was found in achenes from the Ambient and 25°C storage regimes. After 12 months of storage, the quality of stored achenes under all storage regimes was thoroughly tested. Those achenes germinated successfully and produced seedlings that grew well under greenhouse conditions. Those seedlings were of high enough quality to be transplanted back into the Dr Hamilton Reserve, where growth and survival continued successfully. This showed convincingly that seed storage is an effective tool in the future ex-situ conservation of Protea roupelliae ssp. hamiltonii. Population augmentation was effective when planting achenes directly in-situ or transplanting ex-situ propagated seedlings in-situ (transplants), but varied between the two methods. Planted achenes had a low seedling emergence (less than an estimated 10% of planted, viable achenes emerged) and survival after one year was 76.41% and 69.81% after two years. However, 96.44% of the transplants survived after the first year and 95.37% after the second year. Additionally the leaf production rate of transplanted seedlings was superior to seedlings that originated from planted achenes. Through this project 1707 Protea roupelliae ssp. hamiltonii transplants have been planted into the Dr Hamilton Reserve. Although these individuals have not yet reached a reproductive size, the population numbers in-situ have increased considerably. Intensive intervention has worked in aiding the recovery of the Protea roupelliae ssp. hamiltonii population in-situ, however new threats to the population have been identified and still need to be mitigated. Key words: critically endangered species, propagation, reproductive output, population augmentation, seed storage.