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The species investigated: (a) Hypoxis spp. corms; (b) Merwilla plumbea bulbs; (c) Scabiosa columbaria roots; (d) Dianthus mooiensis roots; (e) Eucomis autumnalis bulbs; (f ) Drimia elata bulbs. 

The species investigated: (a) Hypoxis spp. corms; (b) Merwilla plumbea bulbs; (c) Scabiosa columbaria roots; (d) Dianthus mooiensis roots; (e) Eucomis autumnalis bulbs; (f ) Drimia elata bulbs. 

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Commercial harvesting of perennial herbs and geophytes for the medicinal plant trade has resulted in significant levels of resource depletion for several of the species concerned. One way to quantify the impacts is to estimate the number of bulbs harvested annually. Using records of bulb diameters sold in the Witwatersrand traditional medicinal pla...

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... collecting for the medicinal plant trade is a major cause of resource depletion (Cunningham, 1988), the impact of which is partly dependent on the plant part removed and the level of harvesting effort and gatherer ‘ efficiency ’ . Plant populations can be driven to extinction if increases in harvesting effort chase an ever-diminishing yield (Begon et al., 1986). Damage assessments to tree populations have been based on the presence of debarked trunks (e.g. Botha et al., 2004; Geldenhuys, 2004; Twine, 2004), but for bulbous plants often little sign remains of their former presence in a locality (Cunningham, 1988). Hence, estimates on the extent of resource depletion based on population off-take are difficult to evaluate, especially if there is a paucity of data on plant population sizes and structures as well. Whole plants, roots and bulbs account for ≈ 50% of the N 500 species and 48% of the volume of plants sold in the Faraday market for traditional medicine in Johannesburg (Williams, 2003). While data on the estimated volume of plants purchased by the traders informs the magnitude of resource depletion, the sustainability of harvesting and the scale of cultivation required to substitute wild-collected stocks would benefit from knowing how many individual plants are extracted. The intention of this paper was to quantify the negative impact of commercial harvesting by investigating and estimating the number of plants harvested annually using the concept of ‘ individual equivalents ’ . ‘ Individual Equivalents ’ is a concept conceived specifically to estimate the number of individual plants harvested, and the potential condition of the resource base, directly from trade and market information (Williams et al., in press). In the case of trees, estimates of the number of individual debarked stems were derived from the bark quantity traded and the number of individual trees that had a stem diameter and bark thickness equivalent to similarly sized individuals for which harvestable bark mass per stem was determined (Williams et al., in press). In this paper, estimates of the number of individual geophytes harvested were based on the number of individuals equivalent in size (i.e. bulb diameter) to the plants for which the number of individual bulbs per bag was determined. For example, if one 50-kg size bag contained ≈ 138 bulbs, each 8 cm in diameter, and ten 50-kg bags were known to be sold over a period of time, then the equivalent number of individual 8 cm bulbs estimated to be harvested is 1380 ‘ individual equivalents ’ . If, however, a bag contained ≈ 282 bulbs, each 6 cm in diameter, then the number of ‘ individual equivalents ’ would be 2820 bulbs. Trade data for six selected perennial herbs were acquired during three surveys of traditional medicine vendors in Johannesburg between 1995 and 2001 (Williams, n.d.). From the bulb diameter and mass records for four bulbous geophytes, the relationship between bulb diameter and mass was correlated, the most prevalent size-classes sold by vendors was established, the change in diameter size-classes over a six-year period was investigated, and the number of ‘ individual equivalent ’ bulbs extracted annually from the source populations was estimated. A perennial herb is defined here as a vascular plant whose life span extends over more than 2 years, that does not produce persistent above-ground woody tissue but may have under- or partially above-ground storage organs (such as bulbs, corms, rhizomes or rootstock) (Van Wyk and Malan, 1988; Von Ahlefelt et al., 2003). Of the perennial herbs investigated, three species are bulbous, one is rhizomatous/cormous and two species have woody rootstocks with long, persistent, carrot-like roots (Table 1) (Fig. 1). Drimia spp. are the most popular bulbs, and refer to at least two species traded in the markets by the common names skanama or isiKlenama . In Johannesburg, at least 60% of the Drimia spp. bulbs are the reddish-coloured D. elata Jacq. The remaining 40% are D. altissima (L.f.) Ker Gawl. (Also known as white skanama ). Eucomis autumnalis (Mill.) Chitt. and Merwilla plumbea (Lindl.) Speta (formerly Scilla natalensis Planch.), known as uMathunga and inGuduza respectively, are also in high demand. Hypoxis spp. refers to H. colchicifolia Bak. and H. hemerocallidea Fisch. and Mey., known as iLabatheka or iNkomfe. The species investigated that have persistent woody rootstocks are Scabiosa columbaria L. (iBheka) and Dianthus mooiensis F.N. Williams (Tjanibeswe). In KwaZulu-Natal, a similar species to D. mooiensis , namely Dianthus zeyheri Sond. (iNingizimu), tends to be used. Depending on the size, bulbs are sold in handfuls equivalent to 6 ± 2.3 bulbs (Williams, 2003) whereas S. columbaria and D. mooiensis are sold in bundles consisting of ≈ 25 individual plants. The prevalence of the bulbous and perennial herbs of varying sizes sold by medicinal plant vendors was determined from three studies conducted between 1995 and 2001. Between April and October 1995, the six species were measured in 27 traditional medicine shops on the Witwatersrand. The Witwatersrand is an extensively urbanised area within the province of Gauteng, with Johannesburg located approximately at the centre of this region. Quantities of the species equivalent in volume to a typical retail sale to a customer were weighed and measured. Bulb diameter was measured using a Vernier calliper across the widest point along the horizontal axis. The bulbs were weighed using a portable digital scale accurate to 5 g. The length of the woody rootstock was measured from the leaf base to root tip. Additionally, traders were asked how many bags per annum of each species they purchased. In a second study between July and September 1995, plant samples were purchased on ten visits to the Faraday market. Faraday is a large, informal wholesale and retail street market in Johannesburg with currently more than 200 vendors. The plants were weighed and measured in the same way as the shop survey, but no data were collected on the annual volume sold. In January 2001, an extensive semi-quantitative study of Faraday was conducted on behalf of the provincial Directorate for Nature Conservation within the Department of Agriculture, Conservation and Environment in Gauteng (Williams, 2003, 2004). One hundred traders were interviewed and a quantitative inventory of every plant sold by each trader was compiled, including the quantity of each species present in the market and the estimated size of the plant part. Given time constraints and the number of species in the market ( N 500) (Williams, 2003), it was not practical to accurately weigh and measure each individual bulb. Instead, bulbs that were generally representative of the size of the stock on sale were selected and bulb diameter was visually estimated and categorised into 1 cm diameter size-classes. None of the plants were weighed, and the length of woody rootstocks was not measured. Traders were also asked how often they purchased plant stock equivalent in volume to a 50-kg maize bag. Medicinal plants are usually transported to the markets in 50-kg size bags. The actual mass of the contents of a bag depends on the plant part (e.g. bulbs or leaves) and its density and moisture content. The number of individuals in any bag depends on the size dimensions of the plant part. The annual quantity of plants purchased by the shops in 1995 was estimated by determining the mean number of bags purchased per trader per annum (bags a − 1 ), and then multiplying this by the proportion of shops selling the species. The annual quantity purchased by the traders in Faraday in 2001 was calculated slightly differently. The frequency with which the traders purchased one bag of the species was determined, and then the number of bags that would have been bought annually was calculated depending on the proportion of traders who sold the species. Bulbs range in size in the markets, and the bulb diameters used to calculate the numbers of ‘ Individual Equivalent ’ bulbs harvested annually were standardized to be equivalent to the modal bulb diameters sold by vendors in a specific year. From raw data for seven bulbous listed in Cunningham (1988, Table 5, page 31) on the mean number of bulbs of a mean specified size contained in a 50-kg bag, regression analysis was used to plot the relationship between bulb size and the number of bulbs per bag. Thereafter, the number of bulbs of a standardized size harvested annually was estimated from the number of bulbs per bag and the number of bags purchased per annum. Bulb populations may suffer varying degrees of damage depending on the popularity of the species, the intensity of harvesting and the ...

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... Many plant species traded at muthi markets were already showing signs of unsustainable harvesting in the late 1990s (Mander, 1998). For example, numerous species of bulbs displayed in the markets were becoming progressively smaller in diameter, strongly suggesting that the larger individuals had already been removed from the populations, and that only smaller ones remained in the wild (Williams et al., 2007a). Similar trends could be occurring with smaller succulent species, such as E. bupleurifolia. ...
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