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Establishing native wildflower habitats in urban settings on a low budget


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INTRODUCTION

The goal of enhancing the visual appeal of roadsides and public spaces through planting wildflowers falls within the concept of sustainability. Wildflower plantings support pollinators and other beneficial insects. Flower meadows in urban settings increase their aesthetic quality in public perception (Lindermann-Matthies and Brieger, 2016; Hoyle et al., 2017) while even limited flower plantings such as flower borders increase public emotional health (Lambert et al., 2016; Zhuang et al, 2021). Public perception of urban plantings positively correlates with the perceived insect benefits (Hoyle et al., 2017). The synergy between aesthetics and ecosystem diversity supports the planting of wildflowers in public spaces. Such spaces often have soils unsuitable for ornamental plantings, and native wildflowers offer a low-cost alternative for managing public space, contributing to the preservation of biodiversity and species conservation (Bretzel et al., 2009). However, funding submissions require quantification of the costs for establishing wildflower plantings. The use of transplants (also called ‘plugs’) in wildflower planting offers an alternative to seeding. Although it requires additional labour and, at some stages of establishment, different equipment, transplants eliminate the risk of seeds being washed away during intensive rainfall and a failure for wildflowers to germinate in the intended area. Possible bird predation involving scratching and exposing sprouted seeds to the elements is also avoided. Compared to seed mixes, plugs also effectively control the mix of native species in the planted area as establishment of individual species is more predictable. Another feature of this project is planting wildflower meadows in the urban setting on barren land, and poor soil is being offered for that purpose by a private entity. Ultimately, the parcel planted with native wildflowers has reduced exposure to water and wind erosion, while providing refuge for pollinators and other beneficial insects, and also providing aesthetic experiences for the public at large. In a broader context, the involvement of a private company reflects the global trend of corporate governance adopting behaviour consistent with sustainable environmental outcomes (Karim et al., 2021; Alkaraan et al., 2023).

The added economic benefit involves the reduced need for maintenance such as mowing (Mody et al., 2020), contributing to air and noise pollution reduction. Maintenance of roadside plantings with woody vegetation can cost up to five times more than the costs of roadside wildflower plantings, although converting a roadside covered with woody plants to wildflowers requires substantial upfront investment that is recouped in several years (Mody et al., 2020). For example, the state of Florida in the United States spends at least $33.5 million annually to maintain 186,121 acres along the state highways (Harrison, 2014). Mowing accounts for 25% of the maintenance costs. Limiting mowing provides other direct ecoservices by reducing air pollution and greenhouse gases (GHG) emissions. Additionally, the exposure of workers and drivers to accident risk is lowered by less mowing. In the United States, 64% of right-of-way vegetation along the National Highway System is turfgrass (Harrison, 2014) and even converting some of that acreage could provide sizable ecological and economic benefits.

Planting wildflowers has been advocated so as to maintain and increase biodiversity (Grass et al., 2016; Campbell et al., 2019; Griffiths-Lee et al., 2022). Flower-rich habitats have been subsidised in the United States and the European Union to promote ecoservice delivery and support biodiversity (Grab et al., 2018). Increased pollinator numbers support commercial soft fruit production (Feltham et al., 2015). Planting strips of wildflowers has also been advocated to increase the biodiversity threatened by agricultural intensification (Grass et al., 2016; Grab et al., 2018). Planting wildflowers revegetates degraded soils, especially common in urban areas, creates aesthetically pleasing areas, creates conservation habitats and protects insect biodiversity (Bretzel et al., 2016). The loss of natural wildflower meadows is viewed as a national emergency situation in England (Jarvis, 2014). Wildflower strips are established within agri-environmental programmes to enhance biodiversity in continental Europe (Haaland et al., 2011). Incorporating native herbaceous plants in green space attracts pollinators thus, creating an alternative to lawns in urban China (Yang et al., 2019).

The use of seeds has several advantages. Planting from seeds allows treatment of a large area and is generally intended to supplement the existing vegetation with wildflowers to increase the diversity of plants and create visual appeal. Low sowing densities seem suitable for unproductive soil in urban environments (Jiang and Hitchmough, 2022). Large area wildflower seeding allows for substantial labour savings, which can be of concern to public institutions such as local governments. However, large area plantings sometimes seed red or white clover, which as a non-native plant has been observed to eventually be displaced by other plants in the United States. The cost of wildflower seeds could be one reason for choosing to plant relatively less expensive clover in some parts of the United States. The visual appeal of clover is excellent but short-lived as the repeated bloom is limited and seasonal weather (e.g. drought) may eliminate it altogether. Some concern has been expressed about the potential to support a variety of arthropods by wildflower planting and that seed mixes may not assure consistent floral display and variety (Williams et al., 2015). Failure to flower adds to the cost of seed mixes and could exclude species particularly beneficial to pollinators and arthropods (Pickett and Derek, 2017).

In the case of seeding, acquiring ecotypic seeds of native wildflowers from reliable sources is preferred to reduce the potential for weed seed and transmitting pests or diseases (Jarvis, 2014). Planting wildflower strips and harvesting their seeds for sale offer incentives for farmers to adopt such practices (Delphia et al., 2019). Recommended seeding rates for commercial wildflower seed mixes vary with regard to the intended character of the wildflower plot and local conditions (Jarvis, 2014; Pickett and Derek, 2017). When seeding involved a mix of forbs and grasses, the result was a higher density of forbs in experimental conditions (Love et al., 2016). Many commercial seed mixes lack information regarding purity, germination rate and species composition by weight (Pickett and Derek, 2017). However, germination rates of seed mixes are erratic (Weaner, 1996; Milstein, 2005; Hoyle et al., 2017).

Plugs are seedlings typically grown in a controlled environment (greenhouse or cold frame). Seedlings are obtained from seeds and grown for a period of time, and the risk of non-viable seed, and/or low-vigour seedling, is absorbed by the producer. By seeding under controlled conditions, the grower precisely selects the quantity and species that are ecoregion-specific (ecotypic) and sustainably sourced. Compared to direct seeding in an outdoor area, this production approach assures a large volume of marketable plant material ready at specific dates throughout the year. The control of growing conditions also allows the production of a wide variety of native wildflowers, which can be important for propagating species that are rare and/or difficult to propagate. The ecotypic seed or site soil-specific mix of species (Weaner, 1996; Jarvis, 2014) assures good establishment and extended bloom throughout the season, which in turn can support an abundant and diverse suite of beneficial arthropods. Using transplants offers an opportunity to compose a native wildflower plot and is an attractive option for landscape architects whose design plans typically call for specific species. However, plugs are more expensive than seeds and require different planting techniques that are labour-intensive. Those characteristics narrow the practical use of transplants to carefully selected sites that are of limited size. As such, establishing native wildflower plots can appeal to urban and suburban locations and create visually appealing, even if not fine-grained, islands at cross-roads, roundabouts and green spaces accepted by the public (Hoyle et al., 2017; Jiang and Yuan, 2017). The sites will still provide ecosystem services with lower maintenance costs. Furthermore, non-road machinery with combustion engines increase anthropogenic air pollution (Waluś et al., 2018). Reduced mowing has been identified as a benefit of establishing wildflower areas (Harrison, 2014; Fernandes et al., 2023).

Results provide the much-needed knowledge of what it costs to establish native wildflower flower beds and enable civic entities, local government, land managers and public road authorities to compare the costs of plantings and budget accordingly. The aesthetic value of native wildflower beds enhances life quality and generates a positive public response. The major environmental benefit is the value provided by pollinators and other beneficial arthropods, which can thrive in the wildflower habitat. The use of native species adapted to local soil and climatic conditions applies the concept of sustainability and enhances resilience to climate change. The current study’s objective is to consider the direct costs of establishing wildflower habitats from transplants and under two soil treatments to control weeds.

MATERIALS AND METHODS

The expenses of the two applied methods involve the initial establishment of the plot since those costs are essential in the decision to invest in a native wildflower plot. Direct expenses are of primary importance in the calculus of municipal authorities or volunteer organisations, as indirect costs are already part of the authority operation or are not considered by volunteers.

Experimental design, plot layout and treatments

The total area of the study site was approximately 0.065 ha (0.16 acre), and it was selected in consultation with the private owner (details below). The plot was divided into three blocks with eight plots in each block. On each block, four plots received a dazomet treatment with tillage, and the other four plots received a no-till and glyphosate treatment. The plot area was approximately 16 m2 (square shape of 3.96 m × 3.96 m) and separated on all sides by a 1.52 m buffer. The two chemicals used were dazomet (commercial product: Basamid G, active ingredient: dazomet 99%, AMVAC Chemical Corporation, Newport Beach, CA, USA) and glyphosate (commercial product: Ranger Pro, active ingredient: glyphosate 41%, Southern Agricultural Insecticides, Inc., Palmetto, FL, USA). The study was conducted from March 2020 to April 2022.

Site location and its characteristics

Site selection for wildflower plantings by public entities such as the state department of transportation or local governments involves the land that is available or that can be adopted for wildflower establishment. Therefore, the cost of land can be ignored from consideration in establishing a wildflower plot. For example, the strips along a divided highway cannot be developed or farmed. The nature of publicly owned land limits the site selection and affects the relative importance of ecosystem services that the wildflower plot provides. The shift emphasises the aesthetic benefits to the public rather than the measurable gains from, for example, pollination services (part of ecosystem services) provided by insects supported by the wildflower plot. Pollination services can be provided by foraging insects if a plot on public land is located near the farmland.

In the case of this study, the selected site was located at a multiple road crossing. The plot was covered with vegetation and occasionally mowed. The area was located in a mixed industrial–residential neighbourhood without any farmland nearby in an urban environment of the Atlanta metropolitan area in Georgia. The plot was property owned by Trilith Studios (461 Sandy Creek Rd, Fayetteville, GA 30214, Fayette County, USA; 33.4731086, -84.5099865; USDA Plant Hardiness Zone 8a-b) and within the range of sites used for wildflower plantings (Aldrich, 2002). The company volunteered to offer the site for the study. The site was previously used as rangeland and has remained fallow for at least two decades. The study site was an open field that extended 30 m at a slope of <5° towards a major roadway. The site was partly barren and partly covered in grass and weeds that would compete with the planted transplants.

Soil preparation

To reduce weed competition, the plots were subjected to three separate applications of 1.5% glyphosate spray. Besides organic soil-preparation techniques such as grazing, solarisation, and burning, herbicide applications have been typical means of soil preparation, with glyphosate being the standard non-selective herbicide used to clear all vegetation in preparation of wildflower plantings (Johnston et al., 2015). Glyphosate targets actively growing plants (Kanissery et al., 2019) and is rapidly inactivated in soil (Quinn et al., 1988). Dazomet is a broad-spectrum pre-plant soil fumigant that has been used widely to control weeds and soil-borne pathogens in a wide variety of horticulture crops (Gilreath and Santos, 2004; Fennimore et al., 2008). However, it has not been studied in wildflower applications. For the glyphosate, the plots were sprayed using a hand pressurised backpack sprayer (Lesco 61840, Cleveland, OH, USA), with the first application until runoff. The first application yielded unsatisfactory results and was followed by two more applications. To enhance the effectiveness of treatment, the glyphosate mix concentration was increased to 5%. All three applications were performed prior to planting transplants on untilled soil. For the dazomet treatment, plots were roto-tilled with the attachment (Land Pride RTA3576, Salina, KS, USA) mounted on a tractor (John Deere 4600, Moline, IL, USA). The soil was tilled to a depth of 15.2 cm.

The tilling was followed by dazomet application at the manufacturer-recommended rate (181.44 kg per A) and another 15.2 cm tilling was done to incorporate it into the soil. The soil was packed using a roller (Brouwer BTR-30, Kesmac Inc., Keswick, Ontario, Canada). To activate the dazomet, the plots were irrigated with 25 mm of water as measured by randomly placed water gauges. Finally, to assure successful soil fumigation, the treated plots were covered with plastic sheeting (HDX 6 mm clear plastic sheeting, Home Depot, Atlanta, Georgia), and its edges were placed in 15.2 cm deep trenches dug around each treated plot. A compact utility loader (Toro Dingo TX-1000 Wide Track Vertical Lift, Bloomington, IN, USA) performed the tasks of digging and backfilling the trenches using a trencher attachment (Toro).

Plant material

Plant material used in the study was cultivated in-house from seeds and planted as standard size landscape plugs. Seeds were acquired from Prairie Moon Nursery (Winona, MN, USA) (Table 4). Five criteria guided the selection of the 15 herbaceous perennial species: native status in the state of Georgia or the southeastern United States, purported pollinator value, suitability to grow in open areas, tolerance of wet to dry soil conditions and bloom time. A total of 15 native forb species were grown in a greenhouse at the research facility. Standard protocols for dormant seed and subsequent seedling establishment were followed. Plants (also referred to as plugs) were grown in 11.43 cm pots. Although this site used plugs raised from seed, the calculations show the plug prices listed by commercial vendors recognising that many lack the capacity to produce their own plugs and have to rely on purchases.

Plants were planted on 28 September 2020 in a triangular shape (measuring 76.2 cm) in 15.2 cm diameter holes, 25.4–30.5 cm deep dug by a soil auger diameter (Stihl, Waiblingen, Germany). A total of 720 transplants were planted, including plants – 360 for one method – applying dazomet treatment, and 360 for the other method – preparing no-till and glyphosate treatment. Each method consisted of 24 replicates of 15 wildflower species. There were 30 plants in each plot. The soil was neither amended during or after planting with nutrients or organic matter; this is the standard recommendation for native perennial plantings (Ullmann et al., 2016). Adding organic matter or soil amendments would also increase costs of establishing the wildflower plot.

The first 3 weeks after planting, plants were irrigated by a hose attached to a water truck with 25 mm per plant. No supplemental irrigation was applied beyond the initial establishment phase. Natural precipitation over the study period totalled 123 cm (October 2020 through August 2021, data extracted from Georgiaweather.net).

Labour and equipment

Labour is necessary to establishing a wildflower plot using plugs. This study estimates the labour costs using publicly available wage figures for the first year of the study. Median wages are typically used to calculate labour costs because mean wages are affected by outliers (Hara et al., 2018). Landscaping, lawn service or groundskeeping supervisors earn a median wage of $24.52 and a mean wage of $25.98 per hour (Bureau of Labor, 2020). Additionally, the average landscaping and groundskeeping worker earns a median wage of $15.26 and mean wage of $16.25 (Bureau of Labor, 2020).

The establishment of wildflower plots involves simple equipment dictated by the specific location and is commonly limited in size. Each piece of equipment used during the preparation, planting and maintenance of the beds in the current study was recorded. Pricing of the equipment was based on the average cost of each piece of equipment sourced from online databases, field representatives and retail stores. The time spent using each piece of equipment on the site was recorded. Labour costs were calculated using industry averages provided by the Bureau of Labor Statistics. All calculations were done in Microsoft Excel® (Microsoft Corporation, Redmond, WA, USA).

RESULTS AND DISCUSSION

Wildflower habitats face significant pressure from weeds often resulting in a monoculture (Easton, 2012) and necessitating renovation every two to 3 years (Perry, 2005). Weed control is essential for wildflower bed establishment (Weaner, 1996; Aldrich, 2002). Aldrich (2002) lists top-soil disturbing and non-disturbing methods of site preparation, with the former involving herbicide applications. Glyphosate, a broad spectrum non-selective herbicide, has been commonly used in wildflower bed preparation (Aldrich, 2002). Since the topsoil could possibly contain thousands of viable weed seeds (Benvenuti and Mazzoncini, 2021), the application of glyphosate involved tilling between herbicide applications (Angelella et al., 2019). However, for establishing wildflowers from transplants, tilling may provide limited benefits since the planted native wildflowers are at advanced growth stages and capable of outcompeting undesirable vegetation. Additionally, with increased tillage, weed seed is brought to the surface, which can result in increased weed pressure (Benvenuti and Mazzoncini, 2021). Some studies applied post-emergence herbicides in establishing wildflower plots (Love et al., 2016) but the options are limited (Angelella et al., 2019) and can have harmful effects on some species (Henry et al., 2023). Tillage also can disturb nests of ground-nesting bees (Ullmann et al., 2016).

Wildflowers have been successfully established in soils that were left untilled and treated with glyphosate compared to beds that were rotary power-tilled (Angelella and O’Rourke, 2017). As part of a larger study, the current project studies wildflower establishment from transplants under two soil treatments designed to control weeds: a no-till method and tillage using a soil fumigant. Both alternatives have been considered for wildflower planting (Aldrich, 2002), but the fumigation is followed by the use of plastic sheeting and is subsequently described.

The two scenarios involved application of different chemicals (herbicide and soil fumigant) with and without tilling. Additionally, the plastic sheathing was used under one scenario. The specific scenario directly affected the needs for labour, the key input in establishing wildflower sites.

Scenario 1: Till + dazomet application

Dazomet use requires the presence of a certified applicator (Basamid G Label) and specialised machinery. A team of two landscaping workers and one supervisor was required to properly till the soil and apply the dazomet. In this study, the three workers required 5 hr and 40 min to till the treated beds, incorporate the dazomet, repeat the till, apply supplemental irrigation and cover the soil with plastic sheeting to seal in the active ingredient (Figure 1). Dazomet application and sealing the treated surface with the plastic sheathing were particularly labour-intensive.

Figure 1.

Time spent on tasks required in Scenario 1 with dazomet treatment. Notes: The total time of all tasks is 5 hr and 40 min. Glyphosate rates were calculated using Excel on a cell phone; herbicide was measured using a graduated cylinder and water in a back sprayer, which was used to apply the mix.

The cost of dazomet involves only the amount applied at the site. Manufactured by AMVAC Chemical Corporation, dazomet is sold under the commercial name of Basamid G. Given the expected amount needed for application, a 22.68 kg container with N active ingredient dazomet 99% was most suitable for the experiment. With a price of $400 per bag (AI 90% dazomet), only 8.44 kg were applied at the cost of $148.98.

Using the Bureau of Labor Statistics wage data, the median wage rates were applied in the calculations since the average wage rate could be distorted by the most extreme (lowest and highest) rates. The labour cost associated with the treatment method involving dazomet application was $311.52. To illustrate the total labour cost (the hourly cost of performing tasks listed in Figure 1), an industry standard overhead of 30% was added yielding the total labour costs of $404.97 (Table 3).

Table 1 shows the equipment necessary for the scenario applying dazomet and the required soil tilling. Two pieces of equipment, a wide track and a tractor, accounted for the majority of equipment costs. The addition of two attachments supplemented the most expensive pieces of machinery. The source of the price information about the machinery was a popular hardware and horticulture store chain.

Equipment needed for tillage and dazomet treatment and its listed price.

Manufacturer Model Price Source
Toro Dingo TX-1000 Wide Track Vertical Lift, Model #22328 $32500 www.machinerytrader.com
Toro Trencher Attachment $6300 Keystone Outdoor Power Equipment
Kesmac, Inc. Brouwer BTR-30 Roller $9553.78 Site One Landscape Supply
AcuRite Magnifying 5″ Rain Gauge (need two) $3.98 each Home Depot
Scotts Whirl Hand Powered Spreader $13.49 Home Depot
John Deere 4600 Tractor $25100 www.tractordata.com
Land Pride RTA3576 Tiller Attachment $8500 www.marketbook.ca
HDX 6 mil clear plastic sheeting (need two) $103 each Home Depot
Total cost - $82181.23 -
Scenario 2: No-till + glyphosate application

The initial time-consuming task involved the measurement and mixing of the herbicide in the tank. The first application of herbicide mix was critical and its implementation required a full hour (Figure 2). The two subsequent applications of glyphosate required only one half the time used in the first application. Glyphosate spraying, applied prior to plot tilling, required 3 hr and 30 min of labour for three applications. Glyphosate was applied using a backpack sprayer. The use of a backpack sprayer involved physical effort, but the method eliminated emission drift that was risked with the use of a tractor.

Figure 2.

Time spent on tasks required in Scenario 2 ‘no-till and glyphosate treatment’. Notes: A total time of all tasks is 3 hr and 30 min. Glyphosate rates were calculated using Excel on a cell phone; herbicide was measured using graduated cylinder and water in a back sprayer, which was used to apply the mix.

The labour costs associated with the glyphosate application and no-till approach to plot preparation (Scenario 2) were less than in the case of the dazomet treatment and involved only one worker. Direct labour costs estimated at $53.41 were calculated using figures provided by the Bureau of Labor Statistics. Adding the industry standard overhead of 30% established the total labour costs of three glyphosate applications as $69.43 (Table 3). The difference in labour costs under Scenario 2 is substantial and may appeal to those who would like to establish wildflower plots but may lack adequate labour resources.

The implementation of Scenario 2 (‘no-till and glyphosate’) requires a minimal amount of simple equipment (Table 2). The scenario’s implementation required 3 hr and 30 min (Figure 2). The mixed herbicide is applied using a backpack sprayer. The application also requires the purchase of a retail size container of glyphosate, but only a portion of the purchased volume is applied given the size of the plot. Given specific locations, the party establishing a wildflower plot may select a different size of the herbicide container to avoid the need for storing the unused portion.

Equipment and herbicide costs for no-till and glyphosate treatment (assuming all equipment was purchased as new).

Manufacturer Model/Product Retail price Quantity used Total cost
Lesco Backpack sprayer, Product #61840 $91.594 1 $91.59
Southern Agricultural Insecticides Ranger Pro Glyphosate Grass & Weed Herbicide Concentrate, 2.5 gal., active ingredient glyphosate 41% $96.495 56.75 ounces $17.11
Expense comparison of scenarios

Table 3 shows the summary of the labour and chemical costs of both scenarios. Scenario 2 offers lower costs than Scenario 1 for establishing wildflower plots using transplants. The primary cause of cost difference is the choice of equipment. The use of the backpack sprayer in the current study is justified by the size of the plot and applicable only to small sites.

Comparison of costs for Scenario 1 ‘tillage + dazomet’ and Scenario 2 ‘no-till + glyphosate’ in the preparation of the site for wildflower plot using plugs.

Scenario 1 Scenario 2
Input Till + dazomet No-till + glyphosate
Labour $311.52 $53.41
Labour overhead $93.45 $16.02
Equipment $82181.23 $91.59
Herbicide $148.98 $17.11
Total cost $82735.18 $178.13

Choosing Scenario 1 is practical if the services associated with the plot preparation can be performed using rented equipment. Outsourcing to a landscape firm could also offer savings if the firm has trained workers and specialised equipment. Knowledgeable civic organisations could also volunteer their services in establishing wildflower plots. The calculations presented in the current study serve as a benchmark in choosing a course of action.

The cost difference between the two different treatments does not account for several additional factors. First, the equipment used in both treatments can be used repeatedly for a number of years for other projects. In 1988, a study found that tractor repair costs equal 80% of the tractor’s initial purchase price after 10,000 hr of use (Morris, 1988). To reach a 10,000-hr limit, a tractor would have to be used 50 hr a week for 200 straight weeks. Technology has advanced considerably since 1988 and with care and regular maintenance, equipment lasts for many years. Tractors, tillers and backpack sprayers required for dazomet applications should be considered investments that are paid off over time through repeated use. Second, the choice of the scenario implies the use of different herbicides. Dazomet costs more than glyphosate. Additionally, dazomet requires the presence of a certified applicator to supervise its application. A certified applicator must complete advanced training in the United States and the labour cost could be higher given their expertise, increasing Scenario 1 labour costs.

Each of the 24 replicate plots was planted with two plants of 15 wildflower species each as 11.43 cm plugs, for a total of 30 plants per plot. The plugs were evenly divided and planted in plots treated with dazomet and plots treated with glyphosate. Plugs cost $519.25 per treatment, using the listed prices from commercial vendors and assuming the investor in the wildflower site lacks the capacity to raise plugs from seed (Table 4). The price per plug includes the cost of labour involved in planting and care during growth, plug packaging and shipping and distribution. The risk premium for having non-viable seed, loss or damage prior to delivery is embedded in the price and cannot be isolated as a separate cost item. It appears that the transfer of that risk to the plug supplier is advisable.

List of species used in the study and total cost of plugs planted.

Species Price per plug September 2020, in $ Total cost, per 48 plugs in $
Agastache foeniculum 1.38 66.24
Allium cernuum 1.43 68.64
Anemone virginiana 1.70 81.60
Asclepias tuberosa 1.54 73.92
Boltonia asteroides 0.91 43.68
Eryngium yuccifolium 1.38 66.24
Helenium autumnale 1.38 66.24
Penthorum sedoides 1.65 79.20
Rudbeckia fulgida 1.43 68.64
Salvia lyrata 0.97 46.56
Sisyrinchium albidum 2.00 96.00
Symphyotrichum laeve 1.35 64.80
Symphyotrichum pilosum 1.25 60.00
Vernonia angustifolia 1.76 84.48
Zizia aptera 1.53 73.44
Total cost - 1039.68

The planting of plugs involved drilling holes to a depth of approximately 25.4 cm using a Stihl BT131 auger with a 15.2 cm drill bit by one landscaper. Another landscaper randomly selected a plug and manually planted it in the drilled hole. The method required 4.5 hr per landscaper to complete planting at $68.67 per worker. After the addition of 30% overhead costs the estimated labour cost is $178.54.

All 15 species established well and experienced significantly reduced weed pressure under the dazomet treatment. Additionally, over 90% of the transplants grown under Scenario 1 (till + dazomet) were still viable by the conclusion of the current study, while 85% of the transplants were alive under Scenario 2 (no-till + glyphosate). The pairwise test on difference between till vs. no till treatments confirmed the statistical difference between them with p-value = 0.0001454 and α = 0.05. Though the statistically significant, in practical terms, 85% survival is acceptable. While the higher growth indices under the former treatment were attributed to increased rootable soil volume (due to tillage), plant survival rates under both treatments were achieved with no additional maintenance after the initial planting and watering, without any fertiliser, mulch application or manual weeding. Limited maintenance and fertilisation reduces CO2 emissions (Marshall et al., 2023). Therefore, both planting approaches are consistent with the goal of sustainability and low-cost maintenance once the urban wildflower plots were established.

CONCLUSIONS

This study considered two methods of establishing low-maintenance wildflower plots on an urban site with poor soil offered for that purpose by a private owner. The establishment scenarios involved the use of plugs of 15 native wildflower species and the preparation of plots using 2 alternative herbicides.

The expense differences between the two scenarios resulted from the price difference of the herbicides, equipment and hours of labour. Retail-size herbicide containers did not match the exact needs for their application given the size of the plots. It is advisable to check the area of the site or sites prior to determining the amount of a specific herbicide and consider additional uses if the container volume exceeds immediate needs. With the exception of the backpack sprayer, which is relatively inexpensive and can have alternative uses, other equipment can be possibly rented. Renting may not apply if the wildflower plot is established by a municipal government with a public ground maintenance unit, or if the service of establishing the wildflower plot is outsourced. The provided estimate of expanses offers a benchmark for consideration of similar scenarios for wildflower plantings.

Both considered scenarios involve herbicides approved for use in the United States. Since the regulatory regimes differ across countries, the specific scenario may have to be modified to meet local conditions. The literature provides examples of the use of pre- and post-emergence herbicide application in wildflower plantings (Love et al., 2016). Perhaps, the least desired feature is the use of plastic sheeting in Scenario 1. Once used, the sheeting needs to be discarded. Recycling plastic sheeting is an option, but may require additional direct costs for removing soil particles, or paying for collection of the recyclable material. Finally, the recent period of accelerated inflation across the world calls for location-specific updates of the identified expenses of labour and materials.

In terms of practical applications, Scenario 2 ‘no-till and glyphosate’ is considerably less expensive because there is no need for specialised equipment to prepare soil prior to planting transplants. That scenario also requires less labour, which can be an important factor because labour costs can be high in some areas. The transplant planting could be accomplished by groups of volunteers guided by a knowledgeable horticulturalist. The transplant option would be recommended where specific species may not be available from seed, on slopes where planting risks loss of seed, situations where pressure from perennial weeds is high and in smaller spaces where the cost of labour and materials is justified by the project scope. Additionally, it would be a good fit for urban areas with high visibility and when immediate results are desired.

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