Zum Hauptinhalt springen

Nutrients and non-essential metals in darkibor kale grown at urban and rural farms: A pilot study

Kim, Brent F. ; Lupolt, Sara N. ; et al.
In: PLoS ONE, Jg. 19 (2024), Heft 4
Online academicJournal

Nutrients and non-essential metals in darkibor kale grown at urban and rural farms: A pilot study  Introduction

Kale is a nutrient-dense leafy vegetable associated with wide-ranging health benefits. It is tolerant of drought and temperature fluctuations, and could thus serve an increasingly important role in providing a safe and nutritious food supply during the climate crisis, while kale's ease of cultivation and ability to be grown in a wide range of soils make it a good fit for urban agriculture. In this pilot study we explored potential differences between kale grown at urban versus rural farms. We planted kale seedlings (Darkibor variety) at three urban and four rural farms in and around Baltimore City, Maryland, instructed farmers to cultivate them using their usual growing practices, harvested the kale from fields and points of distribution, and analyzed it for concentrations of carotenoids, vitamins C and K1, ten nutritional elements, and eight non-essential metals. Although sample sizes for some analyses were in some cases too small to produce statistically significant results, we identified potentially meaningful differences in concentrations of several components between urban and rural kale samples. Compared to urban samples, mean concentrations of carotenoids and vitamins were 22–38% higher in rural field samples. By contrast, mean concentrations for eight nutritional elements were higher in urban field samples by as much as 413% for iron. Compared to rural field samples, mean concentrations of nine non-essential metals were higher in urban samples, although lead and cadmium concentrations for all samples were below public health guidelines. Some urban-rural differences were more pronounced than those identified in prior research. For six elements, variance within urban and rural farms was greater than variance between urban and rural farms, suggesting urbanicity may not be the primary driver of some observed differences. For some nutrients, mean concentrations were higher than upper ranges reported in prior estimates, suggesting kale may have the potential to be more nutrient-dense than previously estimated. The nutritive and metals composition of this important crop, and the factors that influence it, merit continued investigation given its growing popularity.

Kale (Brassica oleracea var. acephala), widely considered a "superfood," is a nutrient-dense leafy vegetable associated with antioxidant, anticancer, cardiovascular, and gastrointestinal benefits [[1]]. According to United States Department of Agriculture (USDA) FoodData Central Foundation Foods data [[2]], and relative to US Food and Drug Administration (FDA) recommended daily values (DV) [[3]], a standard serving of 65 grams of raw kale provides over 200% of the DV for vitamin K1 and over 20% of the DV for vitamin C and manganese (over 20% is considered "high in" a nutrient by FDA standards), and 10–20% of the DV for vitamin A, riboflavin, calcium, and folate (10–19% is considered a "good source"). Even among cruciferous vegetables—known for their nutrient density—kale has been reported to be exceptional in its content of many vitamins and minerals [[1]]. Beyond essential nutrients, kale contains health-promoting phytochemicals in the glucosinolates, polyphenols, and carotenoids groups [[1], [4]].

The popularity of kale has surged in recent decades. Bon Appétit magazine named 2012 the year of kale; a year later, "National Kale Day" was established in the US [[5]]. Between 1997 and 2017, US kale production and supplies nearly tripled, with per capita availability peaking at 467 grams (over one pound) per US citizen annually. Production and availability have since declined slightly but remain well above historical levels [[6]]. Countries outside the US, such as Denmark [[7]] and Australia [[8]], have reported a similar rise in demand. Kale's growing popularity extends beyond fresh and frozen products; the global market for dehydrated kale chips, for example, is projected to more than double between 2020 and 2027 [[9]]. At a more local level, according to a 2016–2017 survey of 104 urban farms and community gardens in Baltimore City, Maryland, kale was grown at 34 percent of sites and was the 3rd most frequently grown produce item after tomatoes and peppers [[10]]. It has been suggested that kale's popularity may be buoyed in part by the plant's tolerance of unfavorable agronomic conditions, making it more popular among farmers during a rapidly changing climate [[1]]. Beyond uses in human food, Brassica plants have a history of use in traditional medicine [[1]], and older kale leaves may be used as animal fodder [[11]].

The nutritive value and widespread popularity of kale are grounds for investigating the many factors that affect kale's beneficial properties. For example, studies have demonstrated that the nutrient and/or phytochemical composition of kale can vary based on cultivar [[1], [12]–[15]], species of cover crop [[16]], agrochemical use [[15]], fertilizer composition and application rate [[17]], moisture stress [[19]], short-term exposure to low temperatures [[20]], growing season, [[15], [21]], maturity stage (e.g., microgreens vs. adult leaves) [[14], [22]], time between planting and harvest [[24]], and processing method (e.g., drying) [[25]]. Leaf biomass has been shown to be influenced by many of the same factors, including cultivar [[24], [26]], moisture stress [[19]], and time between planting and harvest [[24], [26]].

Environmental factors can also impact concentrations of non-essential metals and other harmful contaminants in kale. Urban areas, for example, often have high concentrations of industrial activity, waste incineration, building demolition, lead-based paint, vehicular emissions, tire wear, and other sources of harmful metals [[27]–[31]]. Releases from these sources may contaminate growing soils via various environmental pathways, including runoff and airborne deposition [[29], [31]], and subsequently be taken up by plant tissues. Uptake rates may vary widely by compound, plant species, and the part of the plant, e.g., roots vs. leaves [[32]–[34]].

Generally, the health benefits of consuming vegetables likely outweigh any risks associated with exposure to non-essential metals and other harmful contaminants; regardless, research and monitoring are important to ensure the safety of food supplies. An assessment of produce grown in Baltimore City, Maryland found some significant differences in concentrations of essential and non-essential (arsenic (As), barium (Ba), cadmium (Cd), chromium (Cr), lead (Pb)) metals in kale samples from urban-grown sources compared to peri-urban, grocery conventional, and grocery organic sources; however, differences were too small in magnitude to have any practical significance for health, and Cd and Pb concentrations in all samples were well below public health guidelines for exposure (no guidelines are available for As, Ba, and Cr) [[35]]. A San Francisco, California study found no significant differences in Cd or Pb concentrations in kale from urban, suburban, or grocery sources, and all levels were below public health guidelines [[36]], and a North Carolina study found only 20 percent of kale samples from commercial sources had lead concentrations above their detection limits [[37]].

Despite its popularity, raw kale is not included in the FDA's Total Diet Study [[38]], which monitors levels of nutrients and contaminants in common foods (the 2018–2020 dataset for the first time added a pan-cooked version of kale).

Building upon the existing body of evidence, we conducted a pilot study to assess levels of select health-relevant nutrients, nutritional elements, and non-essential metals in kale grown at two urban and four rural farms; and to gather data about site history, farming practices, environmental conditions, and other factors that might influence the properties of kale grown at those sites. The aim of the study was to explore the degree to which concentrations of these analytes might differ between urban and rural farms, and possible reasons for those differences. The analytes of interest were carotenoids, vitamin K1, and vitamin C; nutritional elements calcium (Ca), copper (Cu), iron (Fe), magnesium (Mg), manganese (Mn), molybdenum (Mo), phosphorous (P), potassium (K), sodium (Na), and zinc (Zn); and non-essential metals As, Ba, Cd, Cr, Pb, nickel (Ni), uranium (U), and vanadium (V).

Materials and methods

Farm selection

We identified and recruited seven farms for participation in this study. Three urban farms were identified through previous inclusion in the Safe Urban Harvests Study [[10], [35]]. Four rural farms, including a farm established to research and test small-scale sustainable agricultural practices, were identified via the study team's professional networks. We distinguished urban farms from rural using 2010 Maryland population density as a rough proxy for urbanicity; urban farms were in census tracts with over 4,000 people per square mile, whereas rural farms where in tracts with fewer than 1,001 [[39]]. Urban farms were located within Baltimore City; rural farms were within one hour of driving distance from Baltimore City. All farms had previous experience growing at least two varieties of kale, e.g., Red Russian or Winterbor. For reporting results, farms were anonymized by assigning a unique identifier beginning with "U" for urban farms and "R" for rural farms.

Kale seedlings and transplanting

For the purposes of this survey study, one variety of kale, Darkibor, was selected. Organic (F1) Darkibor kale seeds were acquired from a commercial seed vendor (Johnny's Selected Seeds, Maine, US). The seeds were sown in seedling starting trays filled with Fafard growing mix (Sun Gro Horticulture, MA, US) on 25 July 2019 in a growth chamber (temperature 25°C, relative humidity 60%, in darkness) at the US Department of Agriculture (USDA) Agricultural Research Service's Beltsville Agricultural Research Center laboratory in Beltsville, MD. Germination of the seeds was first noted two days after sowing. Plants were then grown under 14h/10h light/dark with an intensity of 160 μmol per m2 second. After one month, seven trays of 32 seedlings each with similar growth were selected for use in the study.

Between 27–29 August 2019, we transplanted 32 seedlings at each farm using stainless steel trowels at a spacing of 12 inches (30 cm) in an area determined by the farmer, in configurations most suitable for the location, e.g., 1 row of 32 seedlings, 2x16, or 4x8. All plants were grown in open air, i.e., not in high tunnels/hoop houses. Farmers were otherwise instructed to grow and tend to the kale plants per usual practices for their farm (e.g., some farms applied pesticides, some installed and used row cover). Farmers were compensated $1,000 USD for the use of space, labor, and time in growing the kale.

Surveys on farm history and growing practices

At the time of transplanting, members of the study team verbally administered a baseline survey (provided in Supporting Information) to a representative at each farm. The survey included questions about farm history; prior soil testing for fertility or contaminants; and growing practices, e.g., irrigation, pest management, use of soil amendments, and USDA Organic certification.

After harvesting, a follow-up survey was emailed to the representative at each farm. The survey asked representatives to verify which practices—specifically irrigation, pest management, and use of soil amendments—had been used to grow the study kale and whether those differed from their typical kale growing practices reported in the baseline survey.

Kale harvesting and collection

After at least one farmer notified the study team that their kale was ready to harvest (approximately six to seven weeks after transplanting), four kale samples were collected directly from each farm ("field samples") between 11–18 October 2019. The 12 largest and healthiest plants at each farm, selected based on a visual assessment of size and the fewest spots and yellow leaves, were harvested, and sets of three plants were randomly selected and combined into four composite samples. Two study team members took a photo of the plants prior to harvesting, removed each plant from the ground (including roots) using a shovel, and recorded the time of harvest. Each sample was placed in a five-gallon (approximately 19-liter) bucket and promptly transported via air-conditioned vehicle to a laboratory at the Johns Hopkins Bloomberg School of Public Health (BSPH), where it was immediately processed.

During the same week, two samples of kale from each farm were collected from the point of distribution ("market samples"), i.e., farmers market, mobile market, or donation site. Farmers obtained six bunches of market-quality kale, which were then randomly assigned to two composite samples of three bunches each. The kale in the market samples was harvested, processed, and transported to the point of distribution, following the usual practices for that farm (e.g., any washing, sanitizing, use of refrigerated storage and/or delivery). The study team picked up the harvested samples at the point of distribution and transported them to the BSPH laboratory, where they were immediately processed. When study team members picked up market samples, they verbally administered a market survey (provided in Supporting Information) to a representative of each farm. The survey included questions about the date and time of harvest, processing (e.g., washing), and use of refrigeration during transport.

Kale sample processing and storage

Upon arrival at the BSPH laboratory, each sample was inspected by the study team. Leaves deemed edible by the study team (e.g., not yellow or covered in pests) were separated from the central stem and roots. Each sample (i.e., leaves without the central stem and roots) was then weighed, rinsed in deionized water, patted dry with WypAll lint-free surface wipes, laid out on a flat white surface, photographed, and weighed again.

The center rib of each leaf was removed with a stainless-steel knife on a plastic, consumer-grade kitchen cutting board. Following previously described procedures [[40]] established for analysis of produce samples for the USDA National Food and Nutrient Analysis Program [[41]] and FoodData Central Foundation Foods datatype [[42]], leaves were then placed in stainless steel bowls with liquid nitrogen, flash frozen, and broken into smaller pieces. Flash-frozen samples were weighed again. The flash-frozen samples were immediately processed in a Blixer V6 industrial food processor (Robot-Coupe USA, Inc., Ridgeland, MS) for 70 seconds or until reaching the consistency of a fine powder, adding additional liquid nitrogen if necessary to keep the material frozen. The powdered homogenate from each sample was aliquoted into multiple labeled 60-mL glass jars (pre-cleaned and certified to meet EPA guidelines for environmental sampling [[43]]) (Environmental Express, Charleston, SC), sealed, wrapped in foil to prevent light exposure, and stored in a -80°C freezer until distributed for analysis. Between each sample, all processing equipment was washed with Alconox detergent and warm water, air-dried, and rinsed with acetone and allowed to dry.

Nutrient and non-essential metals analyses

Moisture was analyzed in all samples to assess differences on a fresh and dry mass basis. Ten elements essential for human health were selected for analysis: calcium, copper, iron, magnesium, manganese, molybdenum, phosphorous, potassium, sodium, and zinc. Vitamin C, vitamin K1, and carotenoids contents were additionally analyzed since kale is recognized as a good dietary source of these nutrients, and were nutrients for which methodology and analytical precision had been established in previous studies to be sufficient for detecting meaningful sample-to-sample variability [[40], [44]]. Eight non-essential metals (contaminants of public health concern) were also selected for analysis: arsenic, barium, cadmium, chromium, lead, nickel, uranium, and vanadium. These contaminants may be present in plant tissues and/or on plant surfaces as a result of airborne deposition, soil uptake, or other pathways [[35]]. Chromium was not speciated between hexavalent chromium (a carcinogen) and trivalent chromium (an essential nutrient).

Samples were packed in dry ice after removal from the -80°C freezer at the BSPH laboratory, shipped via overnight express to designated laboratories, verified to have arrived frozen upon receipt at each laboratory, and held at -60°C storage until analyzed. Vitamin C and moisture were analyzed at Virginia Tech (Phillips laboratory), vitamin K1 at Tufts (USDA Human Nutrition Research Center on Aging at Tufts University, Boston, MA), carotenoids at Eurofins-Craft Technologies (Wilson, NC), and nutritional elements and non-essential metals at Eurofins Scientific (Madison, WI).

Analytical methods

Moisture was measured by vacuum drying 2 g subsamples to a constant weight at 635 mm Hg and 65–70°C, as adapted from Association of Official Analytical Chemists International [[46]]. Vitamin C was analyzed as total ascorbic acid after reduction of dehydroascorbic acid with tris (2-carboxyethyl) phosphine hydrochloride, by reversed-phase high-performance liquid chromatography, as previously described [[47]], using 2.0±0.1 g analytical subsamples that were weighed while still frozen. Stability of vitamin C in homogenized raw vegetables analyzed under the conditions of this study has been validated [[44]]. For carotenoids (alpha-carotene, beta-carotene, gamma-carotene, alpha-cryptoxanthin, beta-cryptoxanthin, lutein, lycopene, and zeaxanthin), samples were extracted and analyzed as previously described using high-performance liquid chromatography (HPLC) for quantitation [[48]]. For vitamin K1, extracts were prepared using hexane and purification by silica solid phase extraction, and analyzed for phylloquinone (vitamin K1), menoquinone-4, and dihydrophylloquinone using reversed-phase HPLC with fluorescence detection and with vitamin K1(25) as an internal standard [[49]]. Nine elements (Ca, Cu, Fe, K, Na, Mn, Mg, P, and Zn) were analyzed by inductively coupled plasma emission spectroscopy (ICP) after digestion with concentrated hydrochloric acid [[50]]. The remaining elements (As, Ba, Cd, Cr, Pb, Mo, Ni, U, V) were analyzed by ICP with mass spectrometry detection (ICP-MS) after digestion with concentrated nitric acid and water using a closed-vessel microwave digestion system [[51]].

Analytical quality control

For each nutrient, 10–15% of the samples were assayed in duplicate with the laboratory blinded to the sample duplicates. Additionally, well-characterized in-house control materials, developed for the USDA National Nutrient Database/Food Data Central [[42]] ("CC") and/or commercially available certified reference materials ("RM") were included in each assay batch, as follows. For vitamin K1, a mixed vegetable composite ("Vegetable III CC"), and SRM® 3232 Kelp Powder and SRM® 1869 Adult/Infant Nutritional Formula II from National Institute of Standards and Technology (NIST) (Gaithersburg, MD; [[53]]); for carotenoids, Vegetable III CC and NIST SRM® 1869; for vitamin C a mixed vegetable/fruit composite ("Mixed Vegetable II CC") and BCR CRM 421 Milk Powder [[54]] purchased from Sigma-Aldrich (St. Louis, MO); for moisture, Mixed Vegetable II CC; for nutritional elements, Vegetable III CC and NIST SRM® 2383a Baby Food; for metals and Mo NIST SRM® 1515 Apple Leaves (Ba, Cd, Cr, Mo, Ni, Pb, U, V), NIST SRM® 1570a Spinach Leaves (As, Cd, Ni), NIST SRM® 2383a Baby Food (Ba, Cr, Ni), and Vegetable III CC. The CC had established tolerance limits for quality control purposes, as described previously [[55]].

Environmental data collection

At the time of seedling transplanting and weekly thereafter until harvesting, two members of the study team visited each farm to collect data on environmental conditions, totaling six visits over five weeks. During each visit, a DustTrak portable aerosol and dust monitor (TSI, Shoreview, MN) was used to measure mean concentrations of particulate matter (PM1, PM2.5, respirable PM, PM10, and total PM) over a five-minute period. Weekly rainfall amounts, collected by consumer-grade rain gauges, were also recorded (in cm). Photographs of kale plants were taken by the study team each week and any substantial changes or observations were noted.

On the first visit after transplanting, three Bluetooth-enabled HOBO data loggers (ONSET, Bourne, MA) were installed within each kale plot. Two were installed above ground to track light intensity and ambient air temperature. One was buried at root depth to track soil temperature. Loggers recorded light and temperature data at five- to 15-minute intervals from installation until they were stopped and retrieved at the time of harvesting.

Data reporting and analyses

Data management, analysis, and visualization were performed using Python version 3.6. For some visualizations Microsoft Excel was additionally used.

For some non-essential metals (As, Ni, Pb, U, V), results for some samples were below the detection limit (5, 10, and 50 ppb for lead and uranium, vanadium and arsenic, and nickel, respectively; see S2 Table in S1 Data for results). Prior to the following analytical steps, including calculating means of duplicates, any values below the detection limit were assumed to be at the detection limit. This assumption slightly overestimates concentrations of these metals; e.g., if a value for arsenic was below the detection limit, it was assumed to be 10 ppb.

For samples analyzed in duplicate for a given component, the mean was used as the sample result.

Analyte concentrations were reported by laboratories on a per fresh weight basis, e.g., mg vitamin C per 100 g fresh kale. Results herein are also reported on a per fresh weight basis, since this is the form in which kale is typically consumed, i.e., not dehydrated. In the Supporting Information and Supporting Data Tables we additionally present results after converting to dry weight, to control for moisture content. Fresh weight concentrations were converted to dry weight using the following formula adapted from the US Environmental Protection Agency (EPA) [[56]]:

Graph

Ca,i,dry=Ca,i,fresh1-Wi

Where C is the concentration of analyte a in sample i and W is the wet fraction for sample i.

For statistical analyses, sample descriptive variables included an identifier for each farm, farm type (urban, rural), and harvest location (field, market). Two-sided Mann-Whitney U tests were used to compare analyte concentrations between groups, e.g., samples from urban vs. rural farms, samples collected from farms vs. at market, or samples from farms using a particular growing practice vs. those that did not. One-way analysis of variance (ANOVA) was also used to compare differences between urban and rural samples; although this test is more appropriate for larger sample sizes and normally distributed data, it is useful for comparing variation between urban and rural samples to variation within urban and rural samples. Potential correlations between continuous variables, such as between different analyte concentrations, were assessed using Pearson's correlation tests.

Data from individual kale samples were clustered, i.e., we would expect analyte concentrations among kale samples from the same farm to be correlated, thus kale samples were not independent. To account for clustering, for the purpose of statistical testing with kale data we used the mean value for each cluster (i.e., farm), as previously recommended [[57]].

Analyses of light and temperature were based on hourly means and included only those data that were common to every group (e.g., when checking for differences across farms, if a HOBO data logger at one farm was started 30 hours before those at the other farms, those first 30 hours were excluded from analyses). Estimates of peak hourly light and temperature for each day excluded days that did not have a full 24 hours of data, i.e., days when data loggers were either installed or removed. Wilcoxon signed-rank tests were used to compare two groups with repeated measures over time, i.e., PM concentrations, weekly collected rainfall, and mean hourly light and temperature between urban and rural farms.

With the exception of ANOVA, the aforementioned tests are all non-parametric and were used on the rationale that sample sizes were small. Light and temperature data had larger sample sizes, e.g., there were 907 mean hourly light intensity observations per farm; however, the results of Shapiro-Wilks tests indicated that the distributions of light and temperature data were non-normal and thus better suited for non-parametric testing.

Ethical considerations

The Johns Hopkins Bloomberg School of Public Health Institutional Review Board (IRB) reviewed and determined that this study did not require oversight as human subjects research.

Results

Kale yields

Thirty-two kale samples were represented in the results (Table 1). These comprised 23 field samples and nine market samples, including four field samples and two market samples from each rural farm. After harvesting four field samples from urban farm U1, there was only enough kale remaining for one market sample. Urban farm U2 had a harlequin bug (Murgantia histrionica) infestation and only had enough kale for three field samples and no market samples. A third urban farm encountered significant pest issues that inhibited kale production; no kale was harvested from this farm and their survey results were excluded from the study. Sample weight, measured after removing the central stem and roots, washing, and drying, ranged from 319–1840 grams (mean: 923 g). S1 Fig in S1 File shows photos of cultivated kale at each farm.

Graph

Table 1 Number of kale samples by farm. A third urban farm encountered significant pest issues that inhibited kale production; no kale was harvested from this farm and their survey results were excluded from the study. Farms were anonymized by assigning a unique identifier beginning with "U" for urban farms and "R" for rural farms.

Farm IDNumber of field samplesNumber of market samples
U141
U230
R142
R242
R342
R442

Farm history and growing practices

Four of the six eligible farms were established between 2009–2018, while two rural farms (R3, R4) were established in the 1980s. The urban farms were previously vacant lots with some history of residential use. The rural farms all had some history of use as a farm or garden prior to current management and their participation in this study.

Both urban farms had previously tested their soil for metals as part of their participation in the Safe Urban Harvests Study [[35]]. One urban farm (U2) reported testing their soil for metals annually. Of the rural farms, only the research farm (R4) had tested their soil for metals and repeated testing every three to four years. One urban (U2) and three rural farms (R2, R3, R4) had tested the fertility of their soil (e.g., nutrients, pH).

All farms had at least two years of experience growing kale, and all reported growing at least two different varieties of kale since the establishment of their respective farms. Only one rural farm (R3) had prior experience growing the Darkibor variety of kale. All rural farms reported using cover crops; the urban farms did not. Other crops previously grown on study plots included turnips, beets, carrots, pattypan squash, tomatoes, garlic, strawberries, eggplant, and other brassicas. All farms reported rotating crop locations each year. Only one farm (R3) was USDA-certified Organic.

Participating farms did not consistently reply to survey questions about the scale of their operations, but one rural farm (R2) reported growing 600 square feet (0.01 acres) of kale. Another rural farm (R1) reported harvesting 150 kale plants in the previous year, less than the 600 plants harvested by one of the urban farms (U2).

Prior to planting, all farms reported applying soil amendments at least once per season, including compost, feather meal, worm castings, kelp, fish emulsion, and/or minerals. During kale cultivation, both urban farms (U1, U2) and one rural farm (R3) applied compost, two rural farms applied feather meal (R2, R3), and the research farm (R4) did not apply soil amendments.

During kale growth, one urban (U2) and three rural farms (R2, R3, R4) reported using pesticides. The other urban farm (U1) relied exclusively on guardian plants (e.g., marigolds), row cover, and other non-chemical deterrents. The other rural farm (R1) used pesticides but only prior to planting. The five farms using pesticides either before or after planting used kaolin clay, neem oil, pyrethrin, spinosad, and/or Bacillus thuringiensis, all of which are generally allowed for use under Organic Materials Review Institute standards [[58]] and consequently, USDA Organic standards.

During kale cultivation, all urban farms used municipal water to irrigate. Three rural farms (R1, R2, R3) used well water and the research farm (R4) used filtered pond water. None of the urban farms and all of the rural farms used drip irrigation. Three rural farms irrigated once per week; the other farms irrigated as frequently as once per day, with variations based on weather patterns or stage of plant growth.

All farms except for the research farm (R4) identified as commercial, i.e., they grew and sold produce for profit, at least in part.

Time from kale harvest to processing, use of refrigeration

The duration of time between harvesting kale and the point at which flash-frozen homogenized samples were put into the freezer ranged from 1.8 to 6.8 hours for field samples and 2.9 to 26.4 hours for market samples. Three of the five farms with market samples (U1, R1, R3) brought kale to the respective distribution points the day after it was harvested. Of these, two rural farms noted that they kept the kale in refrigerated storage. The urban farm did not provide any information about their storage method (the survey requested information about refrigerated transport but not storage; when designing the survey we had assumed kale would be transported directly to market following harvest), but the kale was noticeably wilted upon collection by the research team. Only one farm reported using refrigerated transport.

Analytical quality control

Results for the quality control materials are summarized in S1 Table in S1 Data. All values were within the expected range for in-house control materials and the certified range for reference materials, with acceptable HorRat (≤3.0) [[59]], with most <1.0.

Among the carotenoids analyzed, lutein, zeaxanthin, and total beta-carotene are reported in this study. Beta-cryptoxanthin, lycopene, and alpha-carotene were detected at trace levels (less than ~0.1 mg/100g fresh weight), but the data had insufficient precision for quantitative results. Alpha-cryptoxanthin and gamma-carotene were also monitored but not detected (<0.01 mg/100g fresh weight) in any samples (lycopene was also <0.01 mg/100g in most samples). For vitamin K1, menoquinone-4 and dihydrophylloquinone were not detected (<0.1 μg/100 g) in any samples and thus are not reported in this study.

Differences between urban and rural field samples

Unless specified otherwise, all analyte concentrations and statistical tests reported in the manuscript and tables refer to fresh weight concentrations. Dry weight concentrations are provided in Supplementary Figures and Tables. Mean analyte concentrations for field samples, by farm urbanicity, are reported in Table 2. Results for individual farms are reported in Figs 1–3. Additional descriptive statistics and analyte concentrations for individual samples are provided in S2-S4 Tables in S1 Data.

Graph: Each dot represents one kale sample. Site identifiers (x-axis) with "U" represent urban farms, identifiers with "R" represent rural farms. P values are from Mann-Whitney U tests comparing field samples from urban and rural farms, using the mean value from each farm (N = 6).

Graph: Each dot represents one kale sample. Site identifiers (x-axis) with "U" represent urban farms, identifiers with "R" represent rural farms. P values are from Mann-Whitney U tests comparing field samples from urban and rural farms, using the mean value from each farm (N = 6). See S2 Fig in S1 File for dry weight concentrations.

Graph: Each dot represents one kale sample. Site identifiers (x-axis) with "U" represent urban farms, identifiers with "R" represent rural farms. P values are from Mann-Whitney U tests comparing field samples from urban and rural farms, using the mean value from each farm (N = 6). See S3 Fig in S1 File for dry weight concentrations. Chromium was not speciated between hexavalent chromium (a carcinogen) and trivalent chromium (an essential nutrient).

Graph

Table 2 Mean fresh weight analyte concentrations in field samples by urban/urban farms, with comparisons to prior estimates. Mean fresh weight analyte concentrations by urban/rural farm, with standard error (SE). Since there was only one market sample from urban farms, market samples are not included in means. Estimates from the current study are compared against prior estimates from the Safe Urban Harvests (SUH) study (27) and the USDA FoodData Central database entry for raw kale (NDB number 11233) (2). The SUH study included kale samples from urban farms and community gardens in Baltimore City (N = 25) and "non-urban" results that included conventional and organic kale samples from grocery stores, and samples from farmers market vendors from outside the city (N = 32). Lutein and zeaxanthin concentrations were combined for this table so they could be compared to USDA values. Chromium was not speciated between hexavalent chromium (a carcinogen) and trivalent chromium (an essential nutrient).

GroupAnalyteUnitCurrent study urban, mean ± SECurrent study rural, mean ± SESUH urban, meanSUH non-urban, meanUSDA, mean (range)
Moistureg/100g fresh wt88.2 ± 0.785.2 ± 0.4
Carotenoids & vitaminsBeta-carotenemg/100g fresh wt3.20 ± 0.265.28 ± 0.212.87 (2.16–3.83)
Lutein + zea.mg/100g fresh wt8.09 ± 0.1810.65 ± 0.326.26 (4.46–8.56)
Phylloquinonemcg/100g fresh wt228 ± 5350 ± 7390 (369–422)
Vitamin Cmg/100g fresh wt113 ± 3147 ± 493 (84–104)
Nutritional elementsCalciummg/100g fresh wt397 ± 54374 ± 11254 (203–281)
Coppermg/100g fresh wt0.07 ± 0.000.05 ± 0.000.060.270.05 (0.03–0.08)
Ironmg/100g fresh wt7.58 ± 2.021.61 ± 0.061.60 (0.77–3.61)
Magnesiummg/100g fresh wt50.3 ± 6.045.3 ± 1.232.7 (28.4–45.8)
Manganesemg/100g fresh wt0.57 ± 0.070.88 ± 0.060.380.620.92 (0.51–1.46)
Molybdenummg/100g fresh wt0.03 ± 0.000.02 ± 0.00
Phosphorousmg/100g fresh wt53.1 ± 2.152.8 ± 3.055 (47–62)
Potassiummg/100g fresh wt312 ± 15441 ± 8348 (301–389)
Sodiummg/100g fresh wt18.1 ± 3.38.6 ± 0.753 (16–107)
Zincmg/100g fresh wt0.61 ± 0.020.39 ± 0.010.430.390.39 (0.20–0.57)
Non-essential metalsArsenicppm fresh wt0.02 ± 0.000.01 ± 0.000.020.01
Bariumppm fresh wt3.82 ± 0.674.49 ± 0.333.372.08
Cadmiumppm fresh wt0.03 ± 0.010.02 ± 0.000.050.06
Chromium (total)ppm fresh wt0.17 ± 0.040.04 ± 0.000.050.05
Leadppm fresh wt0.13 ± 0.020.01 ± 0.000.040.02
Nickelppm fresh wt0.09 ± 0.020.08 ± 0.010.090.15
Uraniumppb fresh wt7.61 ± 1.525.00 ± 0.00
Vanadiumppm fresh wt0.12 ± 0.040.02 ± 0.00

Since there was only one market sample from urban farms (Table 1), market samples were excluded from statistical comparisons between urban and rural kale, i.e., comparisons were only made using field samples. Since we had to use mean values for Mann-Whitney U tests, sample sizes (N = 6 mean values for each analyte, one per farm) were too small to produce statistically significant results from urban-rural comparisons, P values are provided in Figs 1–3 and S2, S3 Figs in S1 File and may be indicative of potentially meaningful differences that could be explored in larger studies.

Stem and leaf weights

Sample weights (measured after removing the central stem and roots, washing, and drying) were generally lower in urban field samples, while the mass ratios of leaves to stems were generally higher in urban samples. Mean weights of rural field samples were nearly twice those of urban field samples; by contrast, the mean ratio of leaf mass to stem mass was 76% higher in urban samples.

Moisture

Moisture content was similar between urban and rural samples (means: 88 and 85%, respectively). Controlling for moisture content (i.e., comparing dry weight concentrations) did not meaningfully affect the overall conclusions from any statistical analyses, including differences in analyte concentrations between urban and rural samples, differences by growing practices, and correlation tests. Time between harvesting and storing processed samples in the freezer was not correlated with moisture content (P>0.05).

Nutrients and non-essential metals

Sample sizes (N = 6 mean values for each analyte, one per farm) precluded the possibility of statistically significant differences in analyte concentrations between urban and rural field samples. However, P values were as low as 0.06 for arsenic and 0.11 for all carotenoids and vitamins, copper, iron, potassium, zinc, lead, and vanadium (Figs 2 and 3). Mean concentrations of carotenoids and vitamins were generally higher in rural samples. Compared to urban field samples, mean fresh weight concentrations of carotenoids and vitamins were 22–38% higher in rural field samples. By contrast, with the exception of manganese and potassium, mean concentrations of nutritional elements were higher in urban field samples by as much as 413% for iron.

Compared to rural field samples, with the exception of barium, mean concentrations of non-essential metals were higher in urban field samples by as much as 13 times for lead and six times for vanadium (Table 2, Fig 3). That said, lead and cadmium concentrations for all samples, including urban (mean Pb: 0.13 ppm, mead Cd: 0.03 ppm) and rural (mean Pb: 0.01 ppm, mean Cd: 0.02 ppm) field samples, were below the maximum levels (Pb: 0.3 ppm, Cd: 0.2 ppm; Fig 3) specified by the Food and Agriculture Organization of the United Nations (FAO) and the World Health Organization (WHO) [[60]].

Between urban-rural variance compared to within urban-rural variance

One-way ANOVA was used to compare variance between urban and rural farms to variance within urban and rural farms (S5 Table in S1 Data). For six elements (Ba, Ca, Cd, Mg, Ni, P), variance was greater within urban and rural farms; this can also be observed in Figs 2 and 3. These results suggest that differences in production conditions among farms may in some cases have a greater influence on analyte concentrations than farm location being rural or urban. For all 17 other analytes, however, variance was greater between urban and rural farms.

Differences between field and market samples

The only market sample provided by urban farms was collected at the market 19 hours after harvest, and had much higher concentrations of six elements (Ca, Cu, Mg, K, Na, Ba), and lower moisture content, compared to field samples from the same farm (Figs 1–3). Given this sample was an outlier in many regards, and because there was only one market sample from urban farms (Table 1), urban farms were excluded from statistical comparisons between field and market samples.

There were no significant differences (P>0.05) in sample weight, leaf:stem ratio, or moisture content between the four mean field and four mean market samples (N = 8), by farm, among rural farms. There were also no significant differences in analyte concentrations between mean field and mean market samples (N = 8) among rural farms, with the exception of dry weight (and not fresh weight) concentrations of calcium (P<0.05). Compared to field samples, mean fresh weight concentrations of nutritional elements and non-essential metals by farm were higher in market samples by as much as 80% for lead and chromium. Mean carotenoid and vitamins concentrations were similar between field and market samples (6% lower to 2% higher in market samples). Differences in moisture content were less than 1%.

Correlations between mass, moisture, harvest to storage time, and analyte concentrations amon...

The leaf:stem mass ratio was significantly positively correlated with fresh weight concentrations of some carotenoids and vitamin K1, and negatively correlated with some elements and metals (Fig 4). Moisture content was significantly inversely correlated with fresh weight vitamin C and Manganese concentrations. Sample weight was not correlated with any analyte concentrations. Time between harvest and freezing samples was not correlated with concentrations of any analytes susceptible to oxidation or degradation, i.e., vitamins and carotenoids.

Graph: Levels of statistical significance for Pearson's correlations between sample properties (mass, moisture, and time to freezing; table rows) and fresh weight concentrations of nutrients and metals (table columns) in field samples, using the mean values from each farm (N = 6). See S4 Fig in S1 File for dry weight correlations.

There appeared to be some patterns in how certain groups of analytes correlated with others (Fig 5). Fresh weight concentrations of one carotenoid or vitamin, for example, consistently tracked with the others (P<0.05, top left corner of Fig 5); for example, samples high in vitamin K1 were also high in carotenoids. Similarly, concentrations of nutritional elements and non-essential metals in some cases positively correlated with one another, e.g., iron with copper, magnesium, arsenic, chromium, uranium, and vanadium (P<0.05). Potassium was positively correlated with carotenoids and vitamins, while lead and zinc were inversely correlated with most carotenoids and vitamins (P<0.05).

Graph: Levels of statistical significance for Pearson's correlations between mean fresh weight concentrations of nutrients and metals in field samples, using the mean values from each farm (N = 6). See S5 Fig in S1 File for dry weight correlations.

Differences in field samples by growing practice

Analyte concentrations in some cases differed significantly based on growing practices used (Fig 6). Carotenoid and vitamin concentrations, for example, were significantly different between field samples from farms that used drip irrigation vs. samples from farms that did not (P<0.05), with mean concentrations higher among the former. Only rural farms reported using drip irrigation, however, thus any associations between growing practices and analyte concentrations may be confounded by urbanicity. Farms that tested their soil for metals prior to planting generally had lower concentrations of carotenoids and vitamin K1, although without an obvious explanation for why this would be the case, this too is likely the result of confounding factors. No other patterns were evident.

Graph: Levels of statistical significance for Mann-Whitney U tests (N = 6) comparing mean mass, moisture, and fresh weight concentrations of nutrients and metals in field samples (table columns) from farms that used a growing practice vs. those that did not (table rows). Parenthesized values indicate the number of farms, out of six, following each growing practice. See S6 Fig in S1 File for dry weight differences.

Environmental conditions

Five-minute mean particulate matter concentrations (PM1, PM2.5, respirable PM, PM10, and total PM) are shown in in S7 Fig in S1 File. PM2.5 concentrations ranged from 0.006–0.065 ppm (mean: 0.016 ppm); concentrations during 14 different farm visits (out of 36) were at or above EPA National Ambient Air Quality Standards (NAAQS) secondary standard of 0.015 ppm [[61]]. Only one farm (U2) remained below the PM2.5 standard for all six visits. PM10 concentrations ranged from 0.008–0.132 ppm (mean: 0.026 ppm) and were below the NAAQS secondary standard of 0.15 ppm [[61]]. Secondary standards are designed to protect public welfare, including protection against damage to crops. There are currently no NAAQS standards for other PM sizes. There were no significant differences in concentrations between urban and rural farms for any of the particle sizes.

Collected rainfall ranged from 0–2.2 cm per week (mean: 0.5 cm; median: 0 cm; S8 Fig in S1 File). There were no significant differences among farms or between urban and rural farms.

Peak hourly light intensity for each day ranged from 35–7739 lumens/ft2 (S8 Fig in S1 File). Compared to urban farms, rural farms generally had higher light intensity readings before the third week after planting, and lower light intensity readings after the third week, continuing to decline thereafter. Overall, light intensity was significantly higher at urban farms compared to rural farms (difference in overall means: 138 lumens/ft2, P<0.001), although this was likely a result of light sensors at two rural farms being in the shadow of kale leaves.

Peak hourly ambient and in-ground temperatures for each day ranged from 60–142 degrees F (16–61 degrees C) and 59–114 degrees F (15–46 degrees C), respectively, and generally declined with the change in season (S8 Fig in S1 File). Differences between urban and rural farms were highly significant (P<0.001) but negligible in magnitude (difference in overall means: <1 degree F).

Discussion

Comparisons to prior estimates

Since there was only one market sample from urban farms, all comparisons to prior estimates (Table 2) are based on field samples only. The Safe Urban Harvests (SUH) study analyzed concentrations of nine metals in kale (among other produce items) from urban farms and community gardens in Baltimore City (N = 25) [[35]]. The two urban farms in this study were also part of SUH. Although mean urban cadmium concentrations were 40 percent lower in the current study, barium, lead, and chromium were 13%, 225%, and 240% higher, respectively, compared to SUH. This is not necessarily cause for concern given: 1) concentrations of lead in this study were below FAO/WHO standards [[60]] (Fig 3; cadmium levels were well below the standard, and there are no FAO/WHO standards for other metals at the time of writing); 2) levels of chromium were not speciated between hexavalent chromium (a carcinogen) and trivalent chromium (an essential nutrient), thus if the levels in kale were predominantly comprised of the latter there would be little cause for concern; and 3) this study only assessed kale from two urban farms, a small sample size that should not be used to make generalized conclusions, whereas SUH assessed kale from 25 urban farms and community gardens. Mean concentrations of the three nutritional elements assessed in SUH (copper, zinc, and manganese) were also higher (17%, 42%, and 50%, respectively) among urban farms in the current study compared to SUH.

A more direct comparison between kale from the two urban farms in this study and kale from the same two urban farms in SUH indicates metals concentrations were, with some exceptions, higher in the current study by as much as 96% for lead (farm U1); chromium was also 82% higher in this study for one of the farms (U2). These differences may be due to a wide range of factors, including changes in soil metals concentrations (and accordingly, plant uptake) between the two study periods, either due to environmental factors and/or changes in soil management practices; spatial differences in soil metals concentrations; and/or differences in plant uptake between different kale cultivars.

The SUH study also analyzed metals concentrations in conventional and organic kale samples from grocery stores, and samples from farmers market vendors from outside Baltimore City (N = 32). For five of the nine metals included in SUH, mean metals concentrations from rural farms in this study were between 20% and 81% lower compared to non-urban samples from SUH. Some differences are to be expected, in part because grocery store samples included in SUH likely represent industrial-scale farms that operate under qualitatively different conditions than those in the current study. Participating farms did not consistently reply to survey questions about the scale of their operations, but one rural farm (R1) reported harvesting 150 kale plants in a prior year compared to 600 plants from an urban farm (U2), while another rural farm (R2) reported growing 600 square feet (0.01 acres) of kale. For context, the average 2021 farm size in Maryland was 161 acres [[62]]. These data, taken together with visual observations by the study team, suggest the rural farms in this study were orders of magnitude smaller than the highly mechanized, industrial-scale farms that produce the bulk of the country's vegetable output, whether organic or conventional.

Field samples from the current study were also compared to estimates of 11 nutritional components for raw kale provided in the USDA FoodData Central Foundation Foods database [[2]] (Table 2). Mean concentrations of beta-carotene, combined lutein and zeaxanthin, vitamin C, calcium, iron, and magnesium from both urban and rural samples in this study were higher than means reported by the USDA, and were in some cases even higher than the maximum values reported by the USDA. Iron concentrations were 374% higher in urban samples from this study compared to mean USDA values. Similar to the SUH non-urban samples, USDA estimates were based on samples from five different supermarkets across the U.S., and thus likely represent farms operating under vastly different conditions than those in the current study. Furthermore, time in transit and on supermarket shelves may have reduced the nutrient density of USDA samples. As with metals, nutrients in kale likely also vary based on variety and cultivar; this study assessed the Darkibor variety, whereas neither SUH participants nor the USDA database specify which variety was grown. Taken together with the SUH comparisons of nutritional elements above, USDA comparisons suggest kale in some cases has the potential to be even more nutrient-dense than previously estimated, particularly if consumed shortly after harvest, regardless of urban or rural origins.

Differences between urban and urban samples

Although small sample size (N = 6 mean values for each analyte, one per farm) precluded the possibility of statistically significant differences between urban and rural field samples, concentrations of carotenoids and vitamins were generally higher in rural samples, while concentrations of nutritional elements and non-essential metals were generally higher in urban samples, particularly for lead and vanadium. Given element concentrations in kale from urban farms in this study were generally higher than those from prior studies, and concentrations in kale from rural farms in this study were generally lower than those from prior studies, the urban-rural differences observed in this study are to be expected. For some elements, however, ANOVA results suggest differences in production conditions within a farm or among farms may have a greater influence on some analytes than farm location being rural or urban.

Neither environmental conditions nor surveys of growing practices revealed any obvious explanation as to why these differences occurred. Urban farms' use of municipal water is unlikely to explain differences in kale metal concentrations, since the overwhelming majority of irrigation water samples from the SUH study were well below public health guidelines for nine metals [[35]]. Since the rural farms in this study reported using drip irrigation and urban farms did not, moisture stress could partly explain the lower carotenoid, vitamin, and potassium concentrations in urban kale (Fig 6), which for potassium would be consistent with a prior study suggesting concentrations of some minerals in kale decrease as a result of moisture stress [[19]]. Contrary to the prior study, however, in this study concentrations of copper and iron were higher among kale samples experiencing greater water stress (i.e., urban kale, on the hypothesis that use of drip irrigation alleviates water stress). Further research on kale could explore the effects of these and other factors or urban-rural differences, including by analyzing irrigation water samples as in Lupolt et al. [[35]].

Soil conditions could also explain urban-rural differences in kale. Urban soils may be subject to numerous factors that can decrease fertility, including compaction by buildings and heavy machinery which, in turn, can decrease porosity, suppress the activity of beneficial microbes, and inhibit the accumulation of soil organic carbon [[63]], all of which may affect the nutrient density of urban crops. Urban areas are also often associated with sources of soil contamination [[27]–[31]] which may be taken up by plant tissues or deposited on surfaces (see Introduction). We would not expect soil on the surfaces of kale plants to be a major factor in this study given samples were thoroughly washed, although soil resides may have remained in crevices of the leaves. Follow-up studies should account for these contamination pathways by analyzing soil samples, as in Lupolt et al. [[35]].

To mitigate soil quality and contamination concerns, farmers may grow crops in raised beds filled with imported growing media. Both urban farms in the current study reported using some compost, but it was unclear whether they used imported growing media exclusively, or if it was added to native soil. The overwhelming majority (95%, among the 100 farms that responded to questions about soil) of Baltimore's farms and gardens participating in SUH reported growing crops in at least some soil, compost, or mulch brought in from off-site, and two-thirds (69%) used raised beds [[10]]. Media used to fill raised beds should be of good quality and not contaminated, although even the use of clean soils does not address the potential for soil recontamination via airborne deposition [[31]]. The current study did not analyze soil samples, but the SUH study in most cases did not find a significant relationship between metals concentrations in soils and those in produce; significant linear relationships were only found between soil and plant concentrations for two metals (Cu and Mn). Furthermore, all calculated bioconcentration factors (metal concentrations in produce divided by the concentration in a soil sample collected immediately adjacent to the plant [[64]]) from the SUH study were less than 0.3 [[35]], suggesting soil element concentrations alone may be a poor predictor of concentrations in plants.

The health implications of urban-rural differences in non-essential metals are difficult to gauge without a risk assessment that would additionally consider how much kale people typically consume, among other factors. The SUH assessment of nine metals in soil, produce, and irrigation water in 104 urban farms and gardens in Baltimore City did not identify cause for concern [[35]], although metals concentrations in kale in this study were higher than those reported in SUH in many cases (Table 2). Any potential health implications associated with exposure to non-essential metals should not be considered in isolation, but rather balanced against the health benefits associated with diets higher in kale [[1]] and other vegetables.

Differences between field and market samples

Since there was only one market sample from urban farms, statistical comparisons between field and market samples were performed on rural samples only to mitigate confounding. Since field samples were transported directly to the lab for processing and freezing, kale samples harvested from the market might be expected to have lower vitamin and carotenoid concentrations due to the oxidation and/or degradation of those nutrients. There were not, however, any significant differences in levels of potentially labile nutrients (i.e., vitamins and carotenoids) between field and market samples, nor was time from harvesting to freezing correlated with concentrations of any vitamins or carotenoids.

It is also notable that the one urban market sample had much higher concentrations of six elements and lower moisture content compared to field samples from the same farm, which would be consistent with the samples losing moisture over the 19-hour period between harvest and collection at the market, concentrating the elements.

Correlations among analytes

We also observed some statistically significant relationships among analyte concentrations and other properties of the kale samples. The ratio of leaf mass to stem mass, for example, was negatively correlated with some carotenoids and vitamin K1, and positively correlated with some nutritional elements and non-essential metals. Further research could shed light on the reasons for these relationships; studies have shown that some metals, for example, tend to accumulate at higher levels in different parts of a plant, e.g., roots vs. leaves [[32]–[34]]. This could in turn inform potential recommendations for consumers, e.g., whether there may be benefits of consuming kale stems along with the leaves.

There also appeared to be patterns in how certain groups of analytes correlated with others in field samples. Fresh weight concentrations of one carotenoid or vitamin, for example, consistently tracked with the others; e.g., samples high in vitamin K1 were also high in carotenoids. Similarly, concentrations of nutritional elements and non-essential metals were in some cases correlated with one another. By contrast, concentrations of lead and zinc were negatively correlated with concentrations of carotenoids and vitamins. For lead, this is consistent with prior evidence of an inverse association between heavy metal and vitamin concentrations in plants, in part due to oxidative stress [[65]]. Furthermore, since urban farms were generally significantly lower in carotenoids and vitamins and higher in elements compared to rural farms, urbanicity—and the associated properties of urban and rural soils explained above—could be confounders that partly explain these correlations. Revisiting these patterns with a larger sample size could shed more light on any potential underlying phenomena that could explain them.

Study limitations and lessons learned

The sample size for this study was small (Table 1). Larger sample sizes would be needed to control for multiple potential confounding factors at once, including urbanicity, time between harvesting and freezing samples, and growing practices. We also had only one market sample from one urban farm (which was an outlier in moisture/element concentrations) versus two market samples from each rural farm, which could skew results, thus market samples were excluded from comparisons to prior studies and from most statistical analyses. Given the popularity of farmers markets, future research could explore the potential for nutrient loss between harvest and point of sale, with an eye toward helping producers make decisions about how best to preserve nutrient density.

Some open-ended questions for growers elicited responses that were not comparable across farms because of differences in how they may have been interpreted. In response to a question about pest management, for example, some growers mentioned row covers—which are used for pest management, but also to protect against the elements and retain moisture. Differences in how growers classify the primary use of row covers could have influenced their responses, thus we did not have reliable data on the use of these and certain other practices. Wherever possible, in lieu of open-ended questions, an expanded checklist of growing and supply chain practices (e.g., use of row covers, mulching film, and refrigerated storage for market samples) for use during both questionnaires and farm visits could aid in gathering more viable data, although this would have to be balanced against potentially longer times for survey administration.

Challenges for urban farms observed during this study, including the loss of kale plants and the exclusion of one urban farm due to pest infestations, reflect the realities of growing operations that are often under resourced, understaffed, and/or run by volunteers. More extreme temperatures due to the climate crisis, combined with heat island effects in urban areas, are likely to make urban agriculture an even more challenging endeavor. Future studies on urban agriculture should plan and account for these realities, while exploring policy interventions to help address them.

Conclusion

Kale is a hardy, resilient, and nutrient-dense crop that could serve an increasingly important role in providing an affordable, safe, and nutritious food supply, particularly within the growing urban and community farming movement, as well as in light of the climate crisis and associated effects on extreme weather patterns and food insecurity. With both urban and rural farms filling different roles and priorities in a changing food system, including climate adaptation and resilience, the safety and nutrient density of produce grown in these different environments is of critical importance. Although small sample sizes precluded statistical significance for some analyses, we observed non-significant but potentially meaningful differences between kale grown in urban and rural settings. Absent any compelling evidence to the contrary, however, the health benefits of a varied diet high in fruits and vegetables—regardless of urban or rural origins—likely outweigh any potential risks associated with exposure to non-essential metals, provided growing sites follow recommended practices for soil safety. Our findings also suggest kale in some cases may have the potential to be even more nutrient-dense than previously estimated, although those comparisons are based on a small number of fresh field samples (in this study) with retail samples (USDA) using potentially different varieties of kale. Further research with larger sample sizes could shed more light on the nutritive and metals composition of this important crop and the factors that influence it, particularly given its growing popularity.

Supporting information

S1 Data

S1-S5 Tables.

(XLSX)

S1 File

S1-S8 Figs and baseline farmer questionnaire.

(PDF)

S2 File

(DOCX)

Decision Letter 0

Sauli Elingarami Academic Editor

27 Oct 2023

PONE-D-23-29655Nutrients and Non-Essential Metals in Darkibor Kale Grown at Urban and Rural Farms: A Pilot StudyPLOS ONE

Dear Dr. Nachman,

Thank you for submitting your manuscript to PLOS ONE. After careful consideration, we feel that it has merit but does not fully meet PLOS ONE's publication criteria as it currently stands. Therefore, we invite you to submit a revised version of the manuscript that addresses the points raised during the review process.

When responding to reviewer comments, please make sure to add proper/related citations to the introduction part, including also thorough discussion of the findings in terms of differences in carotenoids and vitamins vs minerals in  rural and urban settings, respectively. Your responses should also include thorough explanations of the methodology, including indicating observed levels of nutrients/elements as seen in results.

Please submit your revised manuscript by Dec 11 2023 11:59PM. If you will need more time than this to complete your revisions, please reply to this message or contact the journal office at plosone@plos.org. When you're ready to submit your revision, log on to https://www.editorialmanager.com/pone/ and select the 'Submissions Needing Revision' folder to locate your manuscript file.

Please include the following items when submitting your revised manuscript:

If you would like to make changes to your financial disclosure, please include your updated statement in your cover letter. Guidelines for resubmitting your figure files are available below the reviewer comments at the end of this letter.

If applicable, we recommend that you deposit your laboratory protocols in protocols.io to enhance the reproducibility of your results. Protocols.io assigns your protocol its own identifier (DOI) so that it can be cited independently in the future. For instructions see: https://journals.plos.org/plosone/s/submission-guidelines#loc-laboratory-protocols. Additionally, PLOS ONE offers an option for publishing peer-reviewed Lab Protocol articles, which describe protocols hosted on protocols.io. Read more information on sharing protocols at https://plos.org/protocols?utm_medium=editorial-email&utm_source=authorletters&utm_campaign=protocols.

We look forward to receiving your revised manuscript.

Kind regards,

Elingarami Sauli, PhD

Academic Editor

PLOS ONE

Journal Requirements:

  • When submitting your revision, we need you to address these additional requirements.
  • Please ensure that your manuscript meets PLOS ONE's style requirements, including those for file naming. The PLOS ONE style templates can be found at 

    https://journals.plos.org/plosone/s/file?id=wjVg/PLOSOne%5fformatting%5fsample%5fmain%5fbody.pdf and 

    https://journals.plos.org/plosone/s/file?id=ba62/PLOSOne_formatting_sample_title_authors_affiliations.pdf

    • 2. Please provide additional details regarding participant consent. In the ethics statement in the Methods and online submission information, please ensure that you have specified (1) whether consent was informed and (2) what type you obtained (for instance, written or verbal, and if verbal, how it was documented and witnessed). If your study included minors, state whether you obtained consent from parents or guardians. If the need for consent was waived by the ethics committee, please include this information.
    • 3. If you are reporting a retrospective study of medical records or archived samples, please ensure that you have discussed whether all data were fully anonymized before you accessed them and/or whether the IRB or ethics committee waived the requirement for informed consent. If patients provided informed written consent to have data from their medical records used in research, please include this information.
    • 4. Thank you for stating in your Funding Statement: 

    This work was supported by cooperative agreement 58-8040-8-018 between the US Department of Agriculture Agricultural Research Service and Virginia Tech, and by cooperative agreement 58-8040-8-021 between the U.S. Department of Agriculture Agricultural Research Service and Johns Hopkins University. Sara Lupolt was supported by a dissertation grant from the Johns Hopkins 21st Century Cities Initiative; a pilot award from the Johns Hopkins Education and Research Center for Occupational Safety and Health, supported by the National Institute for Occupational Safety and Health and the US Department of Agriculture Northeast Sustainable Agriculture Research and Education Program (GNE 19-209); and a Johns Hopkins Center for a Livable Future-Lerner Fellowship. Because this was a cooperative agreement, three USDA staff members (Naomi Fukagawa, Carrie Green, and Tiabao Yang) were involved in helping design, conduct, and co-author the study. Other funders had no role in preparing, reviewing, or editing the manuscript. Support for statistical consulting was made possible by The Johns Hopkins Institute for Clinical and Translational Research, funded in part by [Grant Number UL1 TR003098] the National Center for Advancing Translational Sciences, a component of the National Institutes of Health (NIH) and the NIH Roadmap for Medical Research.

    Please provide an amended statement that declares all the funding or sources of support (whether external or internal to your organization) received during this study, as detailed online in our guide for authors at http://journals.plos.org/plosone/s/submit-now.  Please also include the statement "There was no additional external funding received for this study." in your updated Funding Statement. 

    Please include your amended Funding Statement within your cover letter. We will change the online submission form on your behalf.

    5. Please include captions for your Supporting Information files at the end of your manuscript, and update any in-text citations to match accordingly. Please see our Supporting Information guidelines for more information: http://journals.plos.org/plosone/s/supporting-information. 

    [Note: HTML markup is below. Please do not edit.]

    Reviewers' comments:

    Reviewer's Responses to Questions

    Comments to the Author

    1. Is the manuscript technically sound, and do the data support the conclusions?

    The manuscript must describe a technically sound piece of scientific research with data that supports the conclusions. Experiments must have been conducted rigorously, with appropriate controls, replication, and sample sizes. The conclusions must be drawn appropriately based on the data presented.

    Reviewer #1: Yes

    Reviewer #2: Yes

    Reviewer #3: Yes

    Reviewer #4: No

    Reviewer #5: Yes

    Reviewer #6: Yes

    ***

    2. Has the statistical analysis been performed appropriately and rigorously?

    Reviewer #1: Yes

    Reviewer #2: Yes

    Reviewer #3: Yes

    Reviewer #4: No

    Reviewer #5: No

    Reviewer #6: Yes

    ***

    3. Have the authors made all data underlying the findings in their manuscript fully available?

    The http://www.plosone.org/static/policies.action#sharing requires authors to make all data underlying the findings described in their manuscript fully available without restriction, with rare exception (please refer to the Data Availability Statement in the manuscript PDF file). The data should be provided as part of the manuscript or its supporting information, or deposited to a public repository. For example, in addition to summary statistics, the data points behind means, medians and variance measures should be available. If there are restrictions on publicly sharing data—e.g. participant privacy or use of data from a third party—those must be specified.

    Reviewer #1: No

    Reviewer #2: Yes

    Reviewer #3: Yes

    Reviewer #4: Yes

    Reviewer #5: Yes

    Reviewer #6: Yes

    ***

    4. Is the manuscript presented in an intelligible fashion and written in standard English?

    PLOS ONE does not copyedit accepted manuscripts, so the language in submitted articles must be clear, correct, and unambiguous. Any typographical or grammatical errors should be corrected at revision, so please note any specific errors here.

    Reviewer #1: No

    Reviewer #2: Yes

    Reviewer #3: Yes

    Reviewer #4: Yes

    Reviewer #5: Yes

    Reviewer #6: Yes

    ***

    5. Review Comments to the Author

    Please use the space provided to explain your answers to the questions above. You may also include additional comments for the author, including concerns about dual publication, research ethics, or publication ethics. (Please upload your review as an attachment if it exceeds 20,000 characters)

    Reviewer #1: General comment:

    The pilot study discussed in this paper examines the nutritional elements, non-essential metals, and health-relevant nutrients in Darkibor kale grown in urban and rural settings. Despite its small sample size, the research reveals significant differences in kale composition between these two environments, which has important implications for the future of kale farming and nutrition.

    Specific comments:

  • The paper effectively underscores the significance of kale as a nutrient-dense vegetable and its potential role in addressing the challenges posed by the climate crisis. This context is essential for understanding the importance of the study. What are the specific nutritional elements and non-essential metals that were found to exhibit differences between urban and rural-grown Darkibor kale in the study?
  • The study's limitations in terms of sample size are acknowledged, but it does a commendable job in highlighting potentially meaningful differences in kale composition between urban and rural farms. However, more details about the sample size and methodology would be beneficial for readers to gauge the study's reliability.
  • It's noteworthy that the research identifies higher concentrations of elements in kale from urban farms and elevated levels of carotenoids and vitamins in kale from rural farms. This specific insight adds value to our understanding of kale quality and can guide both urban and rural farming practices. The mention of variance within and between farm settings is an interesting observation that could lead to further research. Can you elaborate on the potential reasons behind the variations in kale composition between urban and rural farming environments, and how might these findings impact farming practices?
  • This paper sheds light on the nutritional composition of Darkibor kale grown in urban and rural settings, highlighting distinctions between the two. Despite the small sample size, the study presents valuable insights into kale quality and the factors contributing to these differences. Considering the importance of kale in addressing the climate crisis and food security, what future research or actions do you believe are necessary based on the insights gained from this pilot study?
  • Constructive feedback:

    The paper could be strengthened by providing a more comprehensive explanation of the methodology employed in the study. Additionally, including data on the actual concentrations of the identified elements and nutrients would help readers better grasp the significance of the findings.

    While the study rightly mentions that concentrations of metals remained below public health guidelines, it would be beneficial to explicitly state the actual concentrations and compare them to those guidelines for clarity.

    Summary:

    The significance of kale as a climate-resilient crop is well articulated, and the study motivates further investigation in this area, which is crucial given the increasing popularity of this nutrient-dense vegetable. However, to improve its impact, the paper should provide more detailed information on the methodology and specific concentration levels of elements and nutrients.

    Reviewer #2: The manuscript entitled "Nutrients and Non-Essential Metals in Darkibor Kale Grown at Urban and Rural Farms: A Pilot Study" has been reviewed. The manuscript is well written; however, before the final acceptance authors should execute the following minor corrections:

  • The abstract is too much descriptive. Please add some statistical findings.
  • Line 124, "Between 27-29 August" please mention the year.
  • Line 132, "Supporting" should be "supporting".
  • Reviewer #3: This study explored potential differences in nutritional elements, non-essential metals, and certain health-relevant nutrients in Darkibor kale grown at urban versus rural farms. The objectives are clear. The selection of farms for planting and survey are good representatives. The sample harvesting and processing, the analyses of different parameters are well-described. The results collected are meaningful. Although there are constraints such as small sample sizes, which precluded statistical significance for some analyses, this study identified non-significant but potentially meaningful differences in in concentrations of several components between urban and rural kale samples. The paper is well-written. It can be accepted for publication in "PLOS ONE": after making the following revision:

  • Line 48: "According to ...".
  • Line 126: "All plants were grown in open air, ..." Is it possible to provide the growth conditions of different farm?
  • Table 2: It would be better to include standard errors and statistical analysis for the means.
  • Lines 419 - 421: "...contrast, with the exception of manganese and potassium, mean concentrations of nutritional elements were higher in urban field samples by as much as 413% for iron. Why? Was the lower iron concentration of kale from the rural resulting from iron deficiency?
  • Lines 468 – 471 "Similarly, concentrations of elements and metals in some cases positively correlated with one another, e.g., iron with copper, magnesium, arsenic, chromium, uranium, and vanadium (P<0.05). Potassium was positively correlated with carotenoids and vitamins, while lead and zinc were inversely correlated with most carotenoids and vitamins (P<0.05)." Why?
  • Lines 470-471: "Potassium was positively correlated with carotenoids and vitamins, while lead and zinc were inversely correlated with most carotenoids and vitamins (P<0.05). Why? Any explanation with references to support?
  • Lines 635-639: "By contrast, concentrations of lead and zinc were negatively correlated with concentrations of carotenoids and vitamins. Since urban farms were generally significantly lower in carotenoids and vitamins and higher in elements compared to rural farms, urbanicity—and the associated properties of urban and rural soils explained above—could be the confounders that explain these differences." From Table 2, kale grown in urban farm had much higher Zinc that rural farm. Why urban farms were generally significantly lower in carotenoids and vitamins? Were the lead and zinc concentrations in urban farm soil too high, which resulted in the reductions of carotenoids and vitamins?
  • Reviewer #4: PONE-D-23-29655-Nutrients and Non-Essential Metals in Darkibor Kale Grown at Urban and Rural Farms: A Pilot Study

    The words "Pilot study" may not be relevant in the publications.

    Abstract

    Lines 32-34 "In this pilot study we explored potential differences in nutritional elements, non-essential metals, and select health-relevant nutrients in Darkibor kale grown at urban versus rural farms"

    What is the meaning of "pilot study" in this context?

    What do authors mean by "Darkibor kale"- I guess Darkibor is a local name.

    Lines 35-37 "Although small sample sizes precluded statistical significance for some analyses, we identified non-significant but potentially meaningful differences in concentrations of several components between urban and rural kale samples"

    Clarify the meaning of "small sample sizes precluded statistical significance for some analyses'

    The statements like "we identified non-significant but potentially meaningful differences..." This is quite confusing. Please present direct and explicit information, and given that this is an abstract, then should use catchy statements.

    Lines 38-41 "Some urban-rural differences were more pronounced than those identified in prior research, although for some elements, variance within urban and rural farms was greater than variance between urban and rural farms"

    Please rephrase the statement. See the bolded section.

    Line 45: Introduction

    This section was fairly well written though there were no compelling reasons to warrant research in Urban and Rural set up. For instance, are there more fumes as a result of vehicles and hence more heavy metal in urban areas? Let the background show previous work be reviewed showing the critical dissimilarities and find the gap that this work intended to fill. Please also clearly show the objective(s) of study and hypothesis/hypotheses (these should come out at the end of the section).

    Line 102: Materials and Methods

    This section is quite mixed up and quite confusing. This was supposed to be experimental research. Whereas in rural areas there were four (4) experimental farms, there were only two experimental farms in the rural area. Why this differences? My guess would be that the farms formed part of replications.

    The experimental design is not shown but even more fundamental is that the replication does not comes out. For the rural areas, we assume that the four farms represent 4 replicates; which make lots of sense. However, the same cannot be said about the urban area. The two farms cannot be considered as a sufficient replication as this is not analysable.

    The authors did not take initial soil samples before the start of the experiments. In that case it is not possible to speculate the possible causes in differences in kales grown in the urban areas compared to rural areas.

    Line 103 Farm selection

    It is not clear why this is being reported in the manuscript. I fully acknowledge the effort made in the identification of the farms, but the information is not necessary for the purposes of this manuscript. The authors can explain how the population in the rural and urban affect the mineral elements in the soil and hence uptake by the plant varieties.

    Line 114 Kale seedling and planting

    This subtitle is confusing – unless there were two sets where there was direct planting and transplanting of the seedlings. Can the authors clarify this?

    Line 117 There is need to clarify the statement "The seeds were sown in seedling starting trays filled with Fafard growing mix" – see the bolded words

    Lines 125-126 "in configurations most suitable for the location, e.g., 1x24, 2x12, 3x8 or 4x6" – the authors need to clarify the spacing as shown in bold above. What these spacing/numbers stand for?

    Line 130 Surveys on farm history and growing practices

    This section may not be relevant unless during the process (survey), soil samples were picked and analysis made to check the chemical composition (including essential elements, beneficial elements, non-essential or toxic heavy metals and pesticides). Otherwise the way the section is presented, I do not find its relevance, but the authors can explain.

    Line 161 "Kale sample processing and storage"

    The authors need to justify the relevance of this section. Is it important that the vegetables be transported in refrigerated form yet tissue analysis (usual procedures) require heating at very high temperatures?

    Line 180: Nutrient and non-essential metals analyses

    In this section, there is need to clearly break down the methods- they cannot be lumped together- e.g. the methods for extraction of heavy metals is quite different compared for instance with the other essential elements. Method for P is totally different from say Ca and so they should be done as subsections. Then the vitamins and carotenoids are also determined using different protocols.

    Still under this section, please explain the need for the vegetables being carried in ice box or freezer.

    But looking at section starting from line 197- "analytical methods", then you will notice that there is no need for section on "Nutrient and non-essential metals analyses" above since section starting from line 197 is more comprehensive. Maybe have section as "Determination of minerals and vitamins in vegetables" to replace "analytical methods" and do away with "Nutrient and non-essential metals analyses"

    However section in lines 209-213 need more elaboration – the analysis part of the metals is clear but the extraction methods not mentioned. A brief mention of the methods with citation of authors that the methods are adapted from can be quite useful.

    Line 241: Data reporting and analyses

    The contents should have been better be placed under "Results" section starting from section 286.

    Why report in ppb instead of ppm? No wonder the metals were below the detectable limit leading to erroneous conclusion that the vegetables are safe (irrespective of whether cultivated in the urban or rural area (see abstract; line 41).

    Line 255- there is a formula for conversion from fresh weight to dry weight- why not just dry the vegetables at a prescribed temperature till the weight is stable?

    Line 286 Results

    Line 287 Kale yields

    In this section, reference is made of field samples and market samples – from materials and method section, such categorization was not evident. Can this be elaborated?

    Table 1; These are raw data that have not been analysed and hence there is no point of presenting in this section.

    Line 301: Farm history and growing practices

    The section does fit under results – moreover, this would only be important if that history led to differences in factors like pH, organic carbon and nutrients as these would affect the availability of these elements to the crop. Can the authors explain the relevance of this section as far as the presentation of the results are concerned

    Line 338; Kale sample processing and storage

    This section does not belong to the "results" section. Is there any reason as to why this section is presented under "results" section?

    Line 348: Analytical quality control

    The authors present quite interesting results on different types of carotenoids. Unfortunately such differentiations/distinctions were not presented under "materials and methods' section.

    Table 2: the heavy and essential elements are reported in terms of mg/100mg fresh weights. It is not common to report metal concentrations in fresh weights, instead dry weight is used. Any reasons for this exception?

    And for the case when the concentration is in ppm fresh weight – why not mg/kg since we are dealing with solid particles and not liquid?

    Note that here the reporting is in ppm yet in the materials and method the authors always made reference of ppb.

    There is a column for "current mean- Urban" and "current mean, rural" – were these results analysed? Please use t-test to compare the two. But since the mean for urban had can only two replications, is it possible to have calculation using two replications?

    In the figures, the symbols U1, U2, R1, R2, R3 and R4 are used yet there was no mention of these under "materials and method" section. It would have been polite for the authors to have figure captions where all these could be explained. Otherwise the way they are, it is not possible to interpret.

    It is quite interesting that almost all the results show p-values more than 0.05 hence not significant. Is there possible reason? Could it be that calculation was not well done?

    Discussion

    Since the methodology needs serious reworking (a lot need to be cut out – especially the survey part and only remain with experimental components). And once the result section is more comprehensive and clear (cut out on survey and reduce the subsections under results; same with discussion). Once there is that kindly harmony, it is too premature to take a look at the discussion.

    Reviewer #5: The material and method section is too narrative, and contains a lot of redundant information. It should be more concise and clear. E.g. Line 135 Redundant information. Line 162 the same.

    Why authors choose different digestion methods for essential vs trace elements analysis?

    Lines 516-519 already mentioned, not part of the discussion

    Reviewer #6: In the manuscript entitled "Nutrients and Non-Essential Metals in Darkibor Kale Grown at Urban and Rural Farms: A Pilot Study", the authors studied a pilot plant to explore potential differences in nutritional elements, non-essential elements, and some health-relevant nutrients in kale grown at urban versus rural farms. The manuscript is very relevant and interesting. However, the authors need to clarify some parts before publication on Plos one.

    The following are my comments and suggestions:

    General comments:

    The authors need to revise all the units and the effective numbers in the whole manuscript.

    Abstract:

    The abstract needs to contain all parts of the manuscript. So the authors need to improve this topic, including parts of the methodology. The authors need to insert some results (numbers) , for example, when the authors said "Concentrations of elements were generally higher in kale from urban farms", how much higher? A conclusion sentence about their work is necessary too.

    Introduction:

    The introduction is interesting and contextualizes the environmental problem for the reader. However, the authors should insert more recent references in the Introduction and it´s essential to describe the potentially toxic metal levels allowed in the national and international legislation. Also, when the authors said on page 4 lines 83-84"concentrations of essential and non essential (arsenic (As), barium (Ba), cadmium (Cd), chromium (Cr), lead (Pb)) metals in.." trivalente chromium is essential for the human being. The authors need to research more specific references about it. Please, pay attential to this part including about chemistry speciation.

    Page 5: "Building upon the existing body of evidence.." The authors need to write more about the aim of the work. They determined a lot of importance parameters obtaining different kind of results, but what is the main question to be answered?

    Materials and methods:

    Page 06: The authors need to standardize the date. Sometimes the authors write day, month and year and other times no.

    Page 10: The authors need to explain more about the digestion process, including more information as the weight of the samples, temperature, final volume, acid concentration, etc.

    Page 10: The authors need to write more about organic and inorganic determination as lines of emissions, analytical concentration curve, detection and quantification limits. The authors need to mention the replicates here too.

    Page 12, line 255: The authors need to include the reference for this equation.

    Results and discussion

    In general, the authors need to discuss more the results comparing with the literature. The authors need to explore further the parts containing discussion and results, for example, in the topic "Correlations among analytes", the authors said "We also observed some statistically significant relationships among analyte concentrations and other properties of the kale samples.", the authors need to discuss and to say more specifically about all the parameters studied. In the sentence, "Similarly, concentrations of elements and metals were in some cases correlated with one another. ", the authors need to specify the elements here. What´s the diference between metals and elements?

    ***

    6. PLOS authors have the option to publish the peer review history of their article (https://journals.plos.org/plosone/s/editorial-and-peer-review-process#loc-peer-review-history). If published, this will include your full peer review and any attached files.

    If you choose "no", your identity will remain anonymous but your review may still be made public.

    Do you want your identity to be public for this peer review? For information about this choice, including consent withdrawal, please see our https://www.plos.org/privacy-policy.

    Reviewer #1: Yes: Wiktor Halecki

    Reviewer #2: Yes: Tapos Kormoker

    Reviewer #3: No

    Reviewer #4: Yes: Joseph Gweyi-Onyango

    Reviewer #5: No

    Reviewer #6: No

    ***

    [NOTE: If reviewer comments were submitted as an attachment file, they will be attached to this email and accessible via the submission site. Please log into your account, locate the manuscript record, and check for the action link "View Attachments". If this link does not appear, there are no attachment files.]

    While revising your submission, please upload your figure files to the Preflight Analysis and Conversion Engine (PACE) digital diagnostic tool, https://pacev2.apexcovantage.com/. PACE helps ensure that figures meet PLOS requirements. To use PACE, you must first register as a user. Registration is free. Then, login and navigate to the UPLOAD tab, where you will find detailed instructions on how to use the tool. If you encounter any issues or have any questions when using PACE, please email PLOS at figures@plos.org. Please note that Supporting Information files do not need this step.

    Attachment

    Submitted filename: PONE-D-23-29655-Nutrients and Non-Essential Metals in Darkibor Kale Grown at Urban and Rural Farms.pdf

    Author response to Decision Letter 0

    11 Dec 2023

    Please refer to the attached PDF for responses to reviewer comments.

    Attachment

    Submitted filename: Response to Reviewers.pdf

    Decision Letter 1

    Sauli Elingarami Academic Editor

    20 Dec 2023

    Nutrients and Non-Essential Metals in Darkibor Kale Grown at Urban and Rural Farms: A Pilot Study

    PONE-D-23-29655R1

    Dear Dr. Keeve. E. Nachman,

    We're pleased to inform you that your manuscript has been judged scientifically suitable for publication and will be formally accepted for publication once it meets all outstanding technical requirements.

    Within one week, you'll receive an e-mail detailing the required amendments. When these have been addressed, you'll receive a formal acceptance letter and your manuscript will be scheduled for publication.

    An invoice for payment will follow shortly after the formal acceptance. To ensure an efficient process, please log into Editorial Manager at http://www.editorialmanager.com/pone/, click the 'Update My Information' link at the top of the page, and double check that your user information is up-to-date. If you have any billing related questions, please contact our Author Billing department directly at authorbilling@plos.org.

    If your institution or institutions have a press office, please notify them about your upcoming paper to help maximize its impact. If they'll be preparing press materials, please inform our press team as soon as possible -- no later than 48 hours after receiving the formal acceptance. Your manuscript will remain under strict press embargo until 2 pm Eastern Time on the date of publication. For more information, please contact onepress@plos.org.

    Kind regards,

    Elingarami Sauli, PhD

    Academic Editor

    PLOS ONE

    Additional Editor Comments (optional):

    Reviewers' comments:

    Reviewer's Responses to Questions

    Comments to the Author

    1. If the authors have adequately addressed your comments raised in a previous round of review and you feel that this manuscript is now acceptable for publication, you may indicate that here to bypass the "Comments to the Author" section, enter your conflict of interest statement in the "Confidential to Editor" section, and submit your "Accept" recommendation.

    Reviewer #3: All comments have been addressed

    Reviewer #7: All comments have been addressed

    ***

    2. Is the manuscript technically sound, and do the data support the conclusions?

    The manuscript must describe a technically sound piece of scientific research with data that supports the conclusions. Experiments must have been conducted rigorously, with appropriate controls, replication, and sample sizes. The conclusions must be drawn appropriately based on the data presented.

    Reviewer #3: Yes

    Reviewer #7: Yes

    ***

    3. Has the statistical analysis been performed appropriately and rigorously?

    Reviewer #3: Yes

    Reviewer #7: Yes

    ***

    4. Have the authors made all data underlying the findings in their manuscript fully available?

    The http://www.plosone.org/static/policies.action#sharing requires authors to make all data underlying the findings described in their manuscript fully available without restriction, with rare exception (please refer to the Data Availability Statement in the manuscript PDF file). The data should be provided as part of the manuscript or its supporting information, or deposited to a public repository. For example, in addition to summary statistics, the data points behind means, medians and variance measures should be available. If there are restrictions on publicly sharing data—e.g. participant privacy or use of data from a third party—those must be specified.

    Reviewer #3: Yes

    Reviewer #7: Yes

    ***

    5. Is the manuscript presented in an intelligible fashion and written in standard English?

    PLOS ONE does not copyedit accepted manuscripts, so the language in submitted articles must be clear, correct, and unambiguous. Any typographical or grammatical errors should be corrected at revision, so please note any specific errors here.

    Reviewer #3: Yes

    Reviewer #7: (No Response)

    ***

    6. Review Comments to the Author

    Please use the space provided to explain your answers to the questions above. You may also include additional comments for the author, including concerns about dual publication, research ethics, or publication ethics. (Please upload your review as an attachment if it exceeds 20,000 characters)

    Reviewer #3: The authors have addressed all of my concerns with the original manuscript. The revised manuscript can be now accepted for publication.

    Reviewer #7: Authors have addressed all the comments and suggestions of all reviewers and have done good efforts for improving the manuscript. Therefore, I consider that it is now I consider that their R1 version of the manuscript may be accepted for publication.

    ***

    7. PLOS authors have the option to publish the peer review history of their article (https://journals.plos.org/plosone/s/editorial-and-peer-review-process#loc-peer-review-history). If published, this will include your full peer review and any attached files.

    If you choose "no", your identity will remain anonymous but your review may still be made public.

    Do you want your identity to be public for this peer review? For information about this choice, including consent withdrawal, please see our https://www.plos.org/privacy-policy.

    Reviewer #3: No

    Reviewer #7: No

    ***

    Acceptance letter

    Sauli Elingarami Academic Editor

    2 Apr 2024

    PONE-D-23-29655R1

    PLOS ONE

    Dear Dr. Nachman,

    I'm pleased to inform you that your manuscript has been deemed suitable for publication in PLOS ONE. Congratulations! Your manuscript is now being handed over to our production team.

    At this stage, our production department will prepare your paper for publication. This includes ensuring the following:

    * All references, tables, and figures are properly cited

    * All relevant supporting information is included in the manuscript submission,

    * There are no issues that prevent the paper from being properly typeset

    If revisions are needed, the production department will contact you directly to resolve them. If no revisions are needed, you will receive an email when the publication date has been set. At this time, we do not offer pre-publication proofs to authors during production of the accepted work. Please keep in mind that we are working through a large volume of accepted articles, so please give us a few weeks to review your paper and let you know the next and final steps.

    Lastly, if your institution or institutions have a press office, please let them know about your upcoming paper now to help maximize its impact. If they'll be preparing press materials, please inform our press team within the next 48 hours. Your manuscript will remain under strict press embargo until 2 pm Eastern Time on the date of publication. For more information, please contact onepress@plos.org.

    If we can help with anything else, please email us at customercare@plos.org.

    Thank you for submitting your work to PLOS ONE and supporting open access.

    Kind regards,

    PLOS ONE Editorial Office Staff

    on behalf of

    Dr. Elingarami Sauli

    Academic Editor

    PLOS ONE

    The authors thank the Maryland farmers who participated in the study; Johns Hopkins Center for a Livable Future's research assistants Trent Dilka, Andrea Chiger, and Ruth Young for assistance with fieldwork and other support; Nancy Pennington, who did protocol and instrument training and assisted with distributions of samples and controls to labs; Ryan McGinty, who also assisted with distribution of samples and controls, and ran the moisture and vitamin C analyses; and Kit Carson at the Johns Hopkins Institute for Clinical and Translational Research, who provided guidance on statistical methods.

    Footnotes 1 The authors have declared that no competing interests exist. References Šamec D, Urlić B, Salopek-Sondi B. Kale (Brassica oleracea var. acephala) as a superfood: Review of the scientific evidence behind the statement. Critical Reviews in Food Science and Nutrition. Taylor and Francis Inc.; (2019). pp. 2411–2422. doi: 10.1080/10408398.2018.1454400, 29557674 2 U.S. Department of Agriculture Agricultural Research Service. Kale, raw. In: Fooddata Central [Internet]. 2019 [cited 21 Jul 2023]. https://fdc.nal.usda.gov/fdc-app.html#/food-details/323505/nutrients 3 United States Food and Drug Administration. Daily Value and Percent Daily Value: Changes on the New Nutrition and Supplement Facts Labels. 2020 Mar. Available: Food and Drug Administration of the United States of America 4 Björkman M, Klingen I, Birch ANE, Bones AM, Bruce TJA, Johansen TJ, et al. Phytochemicals of Brassicaceae in plant protection and human health—Influences of climate, environment and agronomic practice. Phytochemistry. (2011). pp. 538–556. doi: 10.1016/j.phytochem.2011.01.014, 21315385 5 Harvard T. H. Chan School of Public Health. Kale. In: The Nutrition Source [Internet]. 2022 [cited 19 Jan 2022]. https://www.hsph.harvard.edu/nutritionsource/food-features/kale/ 6 U.S. Department of Agriculture Economic Research Service. Vegetables and Pulses Yearbook Tables. 30 Jul 2021 [cited 19 Jan 2022]. https://www.ers.usda.gov/data-products/vegetables-and-pulses-data/vegetables-and-pulses-yearbook-tables/ 7 Kāle M, Agbozo E. Healthy Food Depiction on Social Media: The Case of Kale on Twitter. CEUR Workshop Proceedings. Vol. 2865. CEUR-WS.; 2020. 8 Kerry Staight. Kale suppliers say rapid rise of vegetable's popularity is leading to worldwide shortage. ABC News. 18 Jul 2014. https://www.abc.net.au/news/2014-07-19/rapid-rise-of-kale-catches-seed-suppliers-out/5608948. Accessed 19 Jan 2022. 9 Industry Reseach. Global and United States Kale Chips Market Insights, Forecast to 2027. 22 Jul 2021 [cited 19 Jan 2022]. https://www.industryresearch.biz/global-and-united-states-kale-chips-market-18787672 Santo RE, Lupolt SN, Kim BF, Burrows RA, Evans E, Evenson B, et al. Characteristics and growing practices of Baltimore City farms and gardens. Urban For Urban Green. (2021). doi: 10.1016/j.ufug.2021.127357 Cartea ME, Picoaga A, Soengas P, Ordás A. Morphological characterization of kale populations from northwestern Spain. Euphytica. (2003); 129: 25–32. doi: 10.1023/A:1021576005211 Becerra-Moreno A, Alanís-Garza PA, Mora-Nieves JL, Mora-Mora JP, Jacobo-Velázquez DA. Kale: An excellent source of vitamin C, pro-vitamin A, lutein and glucosinolates. CYTA—Journal of Food. (2014); 12: 298–303. doi: 10.1080/19476337.2013.850743 Thavarajah D, Thavarajah P, Abare A, Basnagala S, Lacher C, Smith P, et al. Mineral micronutrient and prebiotic carbohydrate profiles of USA-grown kale (Brassica oleracea L. var. acephala). Journal of Food Composition and Analysis. (2016); 52: 9–15. doi: 10.1016/j.jfca.2016.07.003 Waterland NL, Moon Y, Tou JC, Kim MJ, Pena-Yewtukhiw EM, Park S. Mineral content differs among microgreen, baby leaf, and adult stages in three cultivars of Kale. HortScience. (2017); 52: 566–571. doi: 10.21273/HORTSCI11499-16 Mercadante AZ, Rodriguez-Amaya DB. Carotenoid Composition of a Leafy Vegetable in Relation to Some Agricultural Variables. J Agric Food Chem. (1991); 39: 1094–1097. doi: 10.1021/jf00006a018 Thavarajah D, Siva N, Johnson N, McGee R, Thavarajah P. Effect of cover crops on the yield and nutrient concentration of organic kale (Brassica oleracea L. var. acephala). Sci Rep. (2019); 9. doi: 10.1038/s41598-019-46847-9, 31316128 Zafar S, Farooq S, Qazi HA, Jaweed TH, Kadam AK, Lone FA. Evaluation of nutrient status of kale and spinach as affected by sewage sludge and mineral fertilizers. J Plant Nutr. (2020); 43: 2633–2644. doi: 10.1080/01904167.2020.1783306 Kopsell DA, Kopsell DE, Curran-Celentano J. Carotenoid pigments in kale are influenced by nitrogen concentration and form. J Sci Food Agric. (2007); 87: 900–907. doi: 10.1002/jsfa.2807 Pathirana I, Thavarajah P, Siva N, Wickramasinghe ANK, Smith P, Thavarajah D. Moisture deficit effects on kale (Brassica oleracea L. var. acephala) biomass, mineral, and low molecular weight carbohydrate concentrations. Sci Hortic. (2017); 226: 216–222. doi: 10.1016/j.scienta.2017.08.050 Ljubej V, Karalija E, Salopek-sondi B, Šamec D. Effects of short-term exposure to low temperatures on proline, pigments, and phytochemicals level in kale (Brassica oleracea var. acephala). Horticulturae. (2021); 7. doi: 10.3390/horticulturae7100341 Fadigas JC, dos Santos AMP, de Jesus RM, Lima DC, Fragoso WD, David JM, et al. Use of multivariate analysis techniques for the characterization of analytical results for the determination of the mineral composition of kale. Microchemical Journal. (2010); 96: 352–356. doi: 10.1016/j.microc.2010.06.006 Acikgoz FE. Mineral, vitamin C and crude protein contents in kale (Brassica oleraceae var. acephala) at different harvesting stages. Afr J Biotechnol. (2011); 10: 17170–17174. Lefsrud M, Kopsell D, Wenzel A, Sheehan J. Changes in kale (Brassica oleracea L. var. acephala) carotenoid and chlorophyll pigment concentrations during leaf ontogeny. Sci Hortic. (2007); 112: 136–141. doi: 10.1016/j.scienta.2006.12.026 Westwood CT, Cutts MK, Russell RJ, O'Brien KM. Effect of timing of harvest on nutritive value of four cultivars of kale (Brassica oleracea L. var. acephala). Proceedings of the New Zealand Grassland Association. (2014); 76: 135–140. doi: 10.33584/jnzg.2014.76.2970 Oliveira SM, Ramos IN, Brandão TRS, Silva CLM. Effect of Air-Drying Temperature on the Quality and Bioactive Characteristics of Dried Galega Kale (Brassica oleraceaL. var. Acephala). J Food Process Preserv. (2015); 39: 2485–2496. doi: 10.1111/jfpp.12498 Korus A.Effect of the cultivar and harvest date of kale (Brassica oleracea L. var. acephala) on crop yield and plant morphological features. Vegetable Crops Research Bulletin. (2010); 73: 55–65. Yesilonis ID, Pouyat R V., Neerchal NK. Spatial distribution of metals in soils in Baltimore, Maryland: Role of native parent material, proximity to major roads, housing age and screening guidelines. Environmental Pollution. (2008); 156. doi: 10.1016/j.envpol.2008.06.010, 18656291 Mielke HW, Laidlaw MAS, Gonzales CR. Estimation of leaded (Pb) gasoline's continuing material and health impacts on 90 US urbanized areas. Environment International. (2011). doi: 10.1016/j.envint.2010.08.006, 20825992 Mielke H W, Anderson J C, Berry K J, Mielke P W, Chaney R L, Leech M. Lead concentrations in inner city soils as a factor in the child lead problem. Am J Public Health. (1983); 73. doi: 10.2105/ajph.73.12.1366, 6638229 Harvey PJ, Rouillon M, Dong C, Ettler V, Handley HK, Taylor MP, et al. Geochemical sources, forms and phases of soil contamination in an industrial city. Science of the Total Environment. (2017);584–585. doi: 10.1016/j.scitotenv.2017.01.053, 28129903 Clark HF, Hausladen DM, Brabander DJ. Urban gardens: Lead exposure, recontamination mechanisms, and implications for remediation design. Environ Res. (2008); 107. doi: 10.1016/j.envres.2008.03.003, 18456252 Nicklow CW, Comas Haezebrouck PH, Feder WA. Influence of varying soil lead levels on lead uptake of leafy and root vegetables. Journal of the American Society for Horticultural Science. (1983); 108. doi: 10.21273/jashs.108.2.193 Ozdener Y, Aydin B, Fatma Aygün S, Yürekli F. Effect of hexavalent chromium on the growth and physiological and biochemical parameters on Brassica oleracea L. var. acephala DC. Acta Biol Hung. (2011); 62. doi: 10.1556/ABiol.62.2011.4.11, 22119874 Marschner H., Uptake, distribution, and binding of cadmium and nickel in different plant species. J Plant Nutr. (1995); 18. doi: 10.1080/01904169509365094 Lupolt SN, Santo RE, Kim BF, Green C, Codling E, Rule AM, et al. The Safe Urban Harvests study: A community-driven cross-sectional assessment of metals in soil, irrigation water, and produce from urban farms and gardens in Baltimore, MD. Environ Health Perspect. (2021). Kohrman H, Chamberlain CP. Heavy metals in produce from urban farms in the San Francisco Bay Area. Food Addit Contam Part B Surveill. (2014); 7: 127–134. doi: 10.1080/19393210.2013.859740, 24914598 Chollet AL, Brock JW. Evaluation of Lead Content of Kale (Brassica oleraceae) Commercially–Available in Buncombe County, North Carolina. J N C Acad Sci. (2008); 124: 23–25. U.S. Food and Drug Administration. Total Diet Study. 3 Jun 2021 [cited 19 Jan 2022]. https://www.fda.gov/food/science-research-food/total-diet-study Johns Hopkins Center for a Livable Future. Maryland Food System Map. 2021. https://gis.mdfoodsystemmap.org/map/#x=-8600388.674532637&y=4687424.322558925&z=7&ll=2,3,94 Phillips KM, Tarrago-Trani MT, McGinty RC, Rasor AS, Haytowitz DB, Pehrsson PR. Seasonal variability of the vitamin C content of fresh fruits and vegetables in a local retail market. J Sci Food Agric. (2018); 98: 4191–4204. doi: 10.1002/jsfa.8941, 29406576 Haytowitz DB, Pehrsson PR. USDA's National Food and Nutrient Analysis Program (NFNAP) produces high-quality data for USDA food composition databases: Two decades of collaboration. Food Chem. (2018); 238: 134–138. doi: 10.1016/j.foodchem.2016.11.082, 28867083 U.S. Department of Agriculture Agricultural Research Service. FoodData Central. 2019 [cited 19 Jan 2022]. https://fdc.nal.usda.gov/ United States Environmental Protection Agency. Specifications and Guidance for Contaminant-Free Sample Containers. 1992. https://cms-resources.environmentalexpress.com/ee/d/EPA%20Specifications%20and%20Guidance%20for%20Contaminant%20Free%20Sample%20Containers.PDF Phillips KM, Council-Troche M, McGinty RC, Rasor AS, Tarrago-Trani MT. Stability of vitamin C in fruit and vegetable homogenates stored at different temperatures. Journal of Food Composition and Analysis. (2016); 45. doi: 10.1016/j.jfca.2015.09.008 Phillips KM, Tarragó-Trani MT, Gebhardt SE, Exler J, Patterson KY, Haytowitz DB, et al. Stability of vitamin C in frozen raw fruit and vegetable homogenates. Journal of Food Composition and Analysis. (2010); 23. doi: 10.1016/j.jfca.2009.08.018 Association of Official Analytical Chemists International. Official Method 934.01. 15th edition. Official Methods of Analysis. 15th edition. 2003. Tarrago-Trani MT, Phillips KM, Cotty M. Matrix-specific method validation for quantitative analysis of vitamin C in diverse foods. Journal of Food Composition and Analysis. (2012); 26: 12–25. doi: 10.1016/J.JFCA.2012.03.004 Craft NE. Chromatographic Techniques for Carotenoid Separation. Current Protocols in Food Analytical Chemistry. (2001); 00: F2.3.1–F2.3.15. doi: 10.1002/0471142913.faf0203s00 Booth SL, Sadowski JA. Determination of phylloquinone in foods by high-performance liquid chromatography. Methods Enzymol. (1997); 282: 446–456. doi: 10.1016/s0076-6879(97)82128-3, 9330309 Association of Official Analytical Chemists International. Official Methods of Analysis, Method 984.27, 985.01, and 2011.14. Gaithersburg, MD, USA; Association of Official Analytical Chemists International. Official Methods of Analysis, Method 2011.19 and 993.14. Gaithersburg, MD, USA; Pacquette LH, Szabo A, Thompson JJ. Simultaneous determination of chromium, selenium, and molybdenum in nutritional products by inductively coupled plasma/mass spectrometry: Single-laboratory validation. J AOAC Int. (2011); 94. doi: 10.1093/jaoac/94.4.1240, 21919358 National Institute of Standards and Technology. Standard Reference Materials. https://www.nist.gov/srm Finglas PM, van den Berg H, de Froidmont-Goertz I. The Certification of the Mass Fractions of Vitamins in Three Reference Materials: Margarine (CRM 122), Milk Powder (CRM 421) and Lyophilized Brussels Sprouts Powder (CRM 431). Luxembourg; 1997. Phillips KM, Patterson KY, Rasor AS, Exler J, Haytowitz DB, Holden JM, et al. Quality-control materials in the USDA National Food and Nutrient Analysis Program (NFNAP). Anal Bioanal Chem. (2006); 384: 1341–1355. doi: 10.1007/s00216-005-0294-0, 16501956 U.S. Environmental Protection Agency. Update for Chapter 9 of the Exposure Factors Handbook: Intake of Fruits and Vegetables. 2018. Galbraith S, Daniel JA, Vissel B. A study of clustered data and approaches to its analysis. Journal of Neuroscience. (2010); 30. doi: 10.1523/JNEUROSCI.0362-10.2010, 20702692 Organic Materials Review Institute. OMRI Search. 2021. https://www.omri.org/omri-search?page=1&query=&exactMatch=false Horwitz W, Albert R. The Horwitz ratio (HorRat): A useful index of method performance with respect to precision. J AOAC Int. (2006); 89. doi: 10.1093/jaoac/89.4.1095, 16915851 Food and Agriculture Organization of the United Nations, World Health Organization. Codex Alimentarius International Food Standards: General Standard for Contaminants and Toxins in Food and Feed (CXS 193–1995). 2019. United States Environmental Protection Agency. National Ambient Air Quality Standards (NAAQS) for PM. 2021 [cited 3 Nov 2021]. https://www.epa.gov/pm-pollution/national-ambient-air-quality-standards-naaqs-pm U.S. Department of Agriculture National Agricultural Statistics Service. 2021 Maryland Farms and Land in Farms Unchanged from Previous Year. 18 Feb 2022 [cited 7 Aug 2023]. https://www.nass.usda.gov/Statistics%5fby%5fState/Maryland/Publications/News%5fReleases/2022/2021-Maryland-Farms-and-Land-in-Farms.pdf Vodyanitskii YN. Organic matter of urban soils: A review. Eurasian Soil Science. (2015); 48. doi: 10.1134/S1064229315080116 Ramirez-Andreotta MD, Brusseau ML, Beamer P, Maier RM. Home gardening near a mining site in an arsenic-endemic region of Arizona: Assessing arsenic exposure dose and risk via ingestion of home garden vegetables, soils, and water. Science of the Total Environment. (2013);454–455. doi: 10.1016/j.scitotenv.2013.02.063, 23562690 Khan A, Khan S, Khan MA, Qamar Z, Waqas M. The uptake and bioaccumulation of heavy metals by food plants, their effects on plants nutrients, and associated health risk: a review. Environmental Science and Pollution Research. (2015); 22. doi: 10.1007/s11356-015-4881-0, 26194234

    By Brent F. Kim; Sara N. Lupolt; Raychel E. Santo; Grace Bachman; Xudong Zhu; Tianbao Yang; Naomi K. Fukagawa; Matthew L. Richardson; Carrie Green; Katherine M. Phillips and Keeve E. Nachman

    Reported by Author; Author; Author; Author; Author; Author; Author; Author; Author; Author; Author

    Titel:
    Nutrients and non-essential metals in darkibor kale grown at urban and rural farms: A pilot study
    Autor/in / Beteiligte Person: Kim, Brent F. ; Lupolt, Sara N. ; Santo, Raychel E. ; Bachman, Grace ; Zhu, Xudong ; Yang, Tianbao ; Fukagawa, Naomi K. ; Richardson, Matthew L. ; Green, Carrie ; Phillips, Katherine M. ; Nachman, Keeve E.
    Link:
    Zeitschrift: PLoS ONE, Jg. 19 (2024), Heft 4
    Veröffentlichung: Public Library of Science (PLoS), 2024
    Medientyp: academicJournal
    ISSN: 1932-6203 (print)
    Schlagwort:
    • Medicine
    • Science
    Sonstiges:
    • Nachgewiesen in: Directory of Open Access Journals
    • Sprachen: English
    • Collection: LCC:Medicine ; LCC:Science
    • Document Type: article
    • File Description: electronic resource
    • Language: English

    Klicken Sie ein Format an und speichern Sie dann die Daten oder geben Sie eine Empfänger-Adresse ein und lassen Sie sich per Email zusenden.

    oder
    oder

    Wählen Sie das für Sie passende Zitationsformat und kopieren Sie es dann in die Zwischenablage, lassen es sich per Mail zusenden oder speichern es als PDF-Datei.

    oder
    oder

    Bitte prüfen Sie, ob die Zitation formal korrekt ist, bevor Sie sie in einer Arbeit verwenden. Benutzen Sie gegebenenfalls den "Exportieren"-Dialog, wenn Sie ein Literaturverwaltungsprogramm verwenden und die Zitat-Angaben selbst formatieren wollen.

    xs 0 - 576
    sm 576 - 768
    md 768 - 992
    lg 992 - 1200
    xl 1200 - 1366
    xxl 1366 -