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Correlates of yield, fecundity and survival of a wild harvested Cyclopia intermedia (honeybush) population

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Abstract

Cyclopia intermedia (honeybush) is a plant species endemic to the fynbos biome. Wild harvested populations are used commercially to produce tea. The species is a resprouter, regrowing from underground rootstock after fires, and as such resprouts once it has been cut. However, there is concern that premature cutting may be compromising rootstock recovery. We report on an initial 400 wild plants measured and monitored under different harvest regimes, including control plants. Plants were harvested once in 2018 and regrowth and survival monitored until 2021. Here, an allometric calculation is provided based on height and stem number to estimate the harvest yield. Plants in valleys or with high surrounding vegetation had the highest yield values and potential fecundity. After harvest, an increase in mortality was correlated with plant size, being higher for smaller plants, but after two years of drought high mortality was not explained by any harvesting category nor any of the site variables, suggesting drought results in high plant mortality regardless of harvest history. The study clarifies several speculative components of harvest method, demonstrates that a complete cut rather than half cut results in better potential yield, and that an ash admixture post-harvest had no measurable impact on regrowth.

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Many endemic Cape plant species are commercially valuable, but information required to manage the resources is often lacking. Here I consider the potential genetic risk that the transition to cultivation may pose for Cape endemic plants and use honeybush – which is based on the members of the Cape endemic genus Cyclopia – as an example. The honeybush industry is expanding, in part driven by the transition from wild harvesting to cultivation. This change offers substantial environmental and economic benefits but may pose risks to wild populations through genetic contamination. I discuss (1) the importance of maintaining genetic diversity and structure of wild populations, (2) the levels of genetic structuring we might expect within the members of the genus Cyclopia, (3) the potential threats to genetic diversity, (4) suggestions for minimising genetic contamination of wild populations by cultivated plantations, and (5) why these issues may be important for the honeybush industry.
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Mesic grasslands in South Africa (> 650 mm a À 1 MAP) are rich in herbaceous forbs, which outnumber grass species by more than 5 to 1. Many of these forbs are geophytes with underground storage units (USOs), such as thickened rootstocks, rhizomes, bulbs, or corms, that provide resources (non-structural carbohydrates, minerals, and water) enabling them to resprout after dry, frosty winters, and fire. However, despite their extensive biomass and reserves ostensibly protected underground, mesic grassland geophytes can be severely depleted or extirpated by chronic trampling and grazing of their aerial parts by livestock. This study examined a possible explanation for the demise of grassland geophytes in overgrazed grassland by investigating , in a pot trial, whether the growth of a geophyte and the size of its USOs are negatively affected by simulated green leaf loss. In a 2 £ 2 factorial (clipped vs. unclipped x spring regrowth in the dark vs. light), five replicate plants of Hypoxis hemerocallidea, a common mesic grassland geophyte that resprouts from a corm, were subject to six severe (clipped to 80 mm) defoliations during the growing season and regrown in spring under full or restricted light to measure stored reserve contribution to regrowth. Defoliated plants were resilient to defoliation during the growing season, matching the total biomass production of unclipped plants, though cutting reduced the number of leaves by :60% and flowers by almost 85%. Spring regrowth on stored reserves equalled that from reserves plus concurrent photosynthesis, indicating the value of USOs for regrowth. However, there was a marked carry-over effect of previous season defoliation, resulting in a one-third reduction in shoot growth and 40% fewer inflorescence in spring. Crucially, corm mass was more than halved by clipping, which resulted in lower spring biomass and inflorescence production. It was concluded that buried stored reserves are not protected from recurrent defoliation and mechanical damage to aerial plant parts and that continued diminishment of USOs under chronic disturbance by overgrazing or frequent mowing would weaken and likely eventually kill plants, reducing overall forb species richness. Lenient management by infrequent summer mowing or grazing at moderate stocking rates combined with periodic rota-tional full season resting and dormant-season burning is recommend to maintain the USOs and vigour of grassland geophytes in mesic grassland.
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Natural selection acts on phenotypic trait variation. Understanding the mechanisms that create and maintain trait variation is fundamental to understanding the breadth of diversity seen on Earth. Flower colour is among the most conspicuous and highly diverse traits in nature. Most flowering plant populations have uniform floral colours, but a minority exhibit within-population colour variation, either discrete (polymorphic) or continuous. Colour variation is commonly maintained by balancing selection through multiple pollinators, opposing selection regimes, or fluctuating selection. Variation can also be maintained by heterozygote advantage or frequency-dependent selection. Neutral processes, or a lack of selection, may maintain variation, although this remains largely untested. We suggest several prospective research directions that may provide insight into the evolutionary drivers of trait variation.
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This paper reports the dissimilar floral spectral reflection of invasive and non-invasive angiosperms. Hyper spectral floral reflectance of 22 non-invasive and 8 invasive, co-habiting and co-flowering angiosperm from Trivandrum, India were measured from 350 to 700 nm. using hand-held spectroradiometer. The ultraviolet, blue and green portions of the electromagnetic spectrum was converted to corresponding photoreceptor excitation values, and insect pollinator (bee) perceived colours respectively. The colour distance between invasive and non-invasive flowers was calculated. Spectral similarity and principal component analysis carried out on photoreceptor excitation values in the ultraviolet, blue and green region reveal the markedly different floral colour perception rendered by invasive species from that of their co-flowering, non-invasive counterparts. Floral spectral reflection in the ultraviolet and blue region was the least similar.
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Floral traits are hypothesized to evolve primarily in response to selection by pollinators. However, selection can also be mediated by other environmental factors. To understand the relative importance of pollinator‐mediated selection and its variation among trait and pollinator types, we analyzed directional selection gradients on floral traits from experiments that manipulated the environment to identify agents of selection. Pollinator‐mediated selection was stronger than selection by other biotic factors (e.g. herbivores), but similar in strength to selection by abiotic factors (e.g. soil water), providing partial support for the hypothesis that floral traits evolve primarily in response to pollinators. Pollinator‐mediated selection was stronger on pollination efficiency traits than on other trait types, as expected if efficiency traits affect fitness via interactions with pollinators, but other trait types also affect fitness via other environmental factors. In addition to varying among trait types, pollinator‐mediated selection varied among pollinator taxa: selection was stronger when bees, long‐tongued flies, or birds were the primary visitors than when the primary visitors were Lepidoptera or multiple animal taxa. Finally, reducing pollinator access to flowers had a relatively small effect on selection on floral traits, suggesting that anthropogenic declines in pollinator populations would initially have modest effects on floral evolution. This article is protected by copyright. All rights reserved
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We used locally-sourced and other relevant information to value ecosystem services provided by South Africa's terrestrial, freshwater and estuarine habitats. Our preliminary estimates suggest that these are worth at least R275 billion per annum to South Africans. Notwithstanding benefits to the rest of the world, natural systems provide a major source of direct income to poor households, and generate significant value in the economy through tourism and property markets, as well as providing considerable non-market benefits. Higher values correspond both to areas of higher biomass, which have higher capacity to supply ecosystem services, and areas of higher population densities, which generate demand as well as threats. The value of regulating services is higher for natural systems closer to population centres. Amenity values are highest in cities and protected areas, with the fragmented green open space areas within cities have among the highest values per ha. Even if the gaps are taken into account, our estimates are far lower than estimates based on average global values, but are likely to be more accurate, relevant and tractable to policymakers. Nevertheless, some services have large global values, the recognition of which is important in developing strategies for financing biodiversity conservation.
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Inflorescences and cones of serotinous (canopy-stored seed) Proteaceae are extensively harvested by the wildflower industry from natural stands in fynbos of the Agulhas Plain, South Africa. This study investigated the impacts of harvesting on seed bank size and seed set of Protea susannae Phill., P. obtusifolia Beuk ex Meisn., Leucadendron coniferum (L.) Meisn. and L. meridianum I. Williams. Harvesting of inflorescences or cones by the stem-cutting method reduced the following season's infructescence (called ‘cones') production in all species except P. susannae. Remaining current year cones of the harvested Protea spp. had greater insect predation levels, and unaltered or lower seed set, than those of unharvested plants. The seed set findings are not consistent with the hypothesis that seed numbers are nutrient-limited, since inflorescence harvesting represents a sink removal, and increased nutrients remaining in the plant would be available for increased seed set. Since repeated annual harvesting of 70% of current year inflorescences or fruit was estimated to result in severe seed bank depletion, it is suggested that lower levels of harvesting (not more than 50% of current inflorescences or cones) be performed in alternate years.
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Invasive non‐native plants form interactions with native species and have the potential to cause direct and indirect impacts on those species, as well as the functioning of invaded ecosystems. Many entomophilous invasive plants form interactions with resident pollinators; sometimes, these interactions are necessary for the reproductive success of the invader. However, the direct role native pollinators play in plant invasion is not well understood and varies according to invasive plant traits, including breeding system and pollination syndrome. The majority of studies addressing impacts on plant–pollinator mutualisms have focussed on the indirect impacts of plant invasion for native plant pollination. Fewer studies have focussed on the direct effects of invasive plants on native flower visitors. Impacts of invasive plants on native pollinators can occur at a range of scales: from the individual flower visitors (in terms of nutrition, health and fitness), to populations (size, density and growth rates), communities (richness, diversity and composition) and community‐level interactions (insect–flower interaction networks). Most research to date has focussed on community‐level impacts, with almost nothing known about the effects of invaders on native flower visitor individuals or populations. Invasive plant traits, including reward quantity and quality, spatial and temporal availability and accessibility, modulate effects on native flower visitors, and thus, different plant species have different impacts. Similarly, flower visitors do not all respond in the same way to invasive plants. Thus, generalizations are difficult to make, but understanding impacts at the individual and population level for different visitor taxa is key to explaining community‐level impacts. There have been varied approaches to determining impacts, with most studies attempting to compare invaded vs. non‐invaded habitats. The pros and cons of different approaches are discussed. Since it is impractical to study every invasive plant in every ecological context in which it occurs, we recommend a better understanding of relevant individual‐level traits to predict direct interactions between invasive plants and native pollinators. A Lay Summary is available for this article.
Code
Tools for performing model selection and model averaging. Automated model selection through subsetting the maximum model, with optional constraints for model inclusion. Model parameter and prediction averaging based on model weights derived from information criteria (AICc and alike) or custom model weighting schemes. [Please do not request the full text - it is an R package. The up-to-date manual is available from CRAN].
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No information is available on the phenological phases between and within genotypes of Cyclopia (honeybush). This information is important to understand the timing of plant development and growth, species co-existence, and growth dynamics of the genus. The study spanning 2 years determined the monthly genotypic variation, the time of the start of a growth phase, and duration of budding, flowering, fruiting, and seed dispersal in C. subternata and C. genistoides. The results indicated differences in phenology between and within species and that initiation period among individuals of a phenological phase is inversely proportional to that duration of that phenophase. Budding, flowering, fruiting, and seed dispersal peaked in the months of July, September, October, and December, respectively. Compared to C. genistoides, C. subternata genotypes had a shorter time (days) from start of observation to start of flowering (25.9 versus 51.2), fruiting (46.1 versus 61.5), and seed dispersal (96.3 versus 110.0). However, the duration (days) of flowering (13.2 versus 24.3), fruiting (45.6 versus 52.2), and seed dispersal (4.3 versus 8.9) was shorter in C. genistoides. Using observational qualitative analysis, phenology of these Cyclopia species was categorised into three groups; early, intermediate, and late. The findings serve as a platform for investigating factors affecting the reproductive phases, morphology, and physiology in these and other Cyclopia species. It will assist farmers and researches to time crop requirements and management practices, thus having practical implications in the cultivation of the species.
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Livelihood status, smallholder farming and climate change are directly interconnected in Sub-Sahara Africa. Simulations predict that yields of main crops will decrease and will be negatively impacted due to climate change within the next 30 to 40 years. The results of a simulation and survey about land use management and demography reveal the competitiveness of drought adapted pearl millet varieties concerning yields and the potential impact on sustainable smallholder farming in a semi-arid region of Kenya. We highlight the ability of adapted crops to improve livelihood through increased income generation and food security with the help of optimized farm management.
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Contrasting flower color patterns that putatively attract or direct pollinators towards a reward are common among angiosperms. In the deceptive orchid Anacamptis morio, the lower petal, which makes up most of the floral display, has a light central patch with dark markings. Within populations, there is pronounced variation in petal brightness, patch size, amount of dark markings, and contrast between patch and petal margin. We tested whether pollinators mediate selection on these color traits and on morphology (plant height, number of flowers, corolla size, spur length), and whether selection is consistent with facilitated or negative frequency-dependent pollination. Pollinators mediated strong selection for increased petal brightness (Δβpoll = 0.42) and contrast (Δβpoll = 0.51). Pollinators also tended to mediate stabilizing selection on brightness (Δγpoll = -0.27, n.s.) favoring the most common phenotype in the population. Selection for reduced petal brightness among hand-pollinated plants indicated a fitness cost associated with brightness. The results demonstrate that flower color traits influence pollination success and seed production in A. morio, indicating that they affect attractiveness to pollinators, efficiency of pollen transfer, or both. The documented selection is consistent with facilitated pollination and selection for color convergence towards co-occurring rewarding species. This article is protected by copyright. All rights reserved.
Article
Phenotypic convergence is rampant throughout the tree of life. While recent studies have made significant progress in ascertaining the proximate mechanisms underlying convergent phenotypes, less is known about the frequency and predictability with which convergent phenotypes arise via the same or multiple pathways at the macroevolutionary scale. We investigated the proximate causes and evolutionary patterns of red flower color in the tomato family, Solanaceae, using large-scale data mining and new sequence data to reconstruct a megaphylogeny of 1341 species. We then combined spectral and anatomical data to assess how many times red flowers have evolved, the relative contribution of different pathways to independent origins of red, and whether the underlying pathway is predicted by phylogenetic relatedness. We estimated at least 30 relatively recent origins of red flowers using anthocyanins, carotenoids, or a dual production of both pigments, with significant phylogenetic signal in the use of anthocyanins and dual production, indicating that closely related red-flowered species tend to employ the same mechanism for coloration. Our study is the first to test whether developmental pathways exhibit phylogenetic signal and implies that historical contingency strongly influences the evolution of new phenotypes. © 2015 The Authors. New Phytologist © 2015 New Phytologist Trust.
Article
I. II. III. IV. References SUMMARY: Floral traits often show correlated variation, both within and across species. One explanation for this pattern of floral integration is that different elements of floral phenotypes are controlled by the same genes, that is, that the genetic architecture is pleiotropic. Recent studies from a range of model systems suggest that the pleiotropy is common among the loci responsible for floral divergence. Moreover, the effects of allelic substitutions at these loci are overwhelmingly aligned with direction of divergence, suggesting that the nature of the pleiotropic effects was adaptive. Molecular genetic studies have revealed the functional basis for some of these effects, although much remains to be discovered with respect to the molecular, biochemical and developmental mechanisms underlying most quantitative trait loci (QTL) responsible for floral differences. Developing a detailed understanding of the nature of pleiotropic mutations and their phenotypic consequences is crucial for modeling how the genetic architecture of trait variation influences the tempo and trajectory of floral evolution. © 2015 The Author. New Phytologist © 2015 New Phytologist Trust.