Assessment of pharmaceutical and personal care product contamination in agricultural soils irrigated with treated wastewater
Abstract
A single flush of a household toilet sends dozens of pharmaceutical compounds into the wastewater stream, and an increasing share of that treated water ends up irrigating the crops that feed us. This research assessed the occurrence and concentration of eight Pharmaceutical and Personal Care Products (PPCPs) in agricultural soils receiving primary-treated, secondary-treated, and groundwater irrigation at three farm sites near Gainesville, Florida, over 18 months (January 2021-June 2022). Triclosan and caffeine were detected in over 90% of primary-treated wastewater-irrigated soil samples, with mean concentrations of 287 and 342 ng/kg, respectively. Secondary treatment reduced soil PPCP loads by 38-67% depending on compound class. Carbamazepine showed the highest persistence, with a calculated soil half-life exceeding 120 days. These results highlight the need for advanced treatment technologies and soil monitoring programs where wastewater reuse is practiced for agricultural irrigation.
Full Text
Tables and figures are in the full-text PDF.
Introduction
When a farmer in central Florida turns on the irrigation pump, the water flowing onto vegetable fields may carry invisible traces of ibuprofen, birth control hormones, and antibacterial soap remnants of everyday life that conventional wastewater treatment plants were not designed to remove [1] . Treated wastewater reuse for agricultural irrigation is expanding rapidly across water-scarce regions, including the South-Eastern United States, where population growth is straining freshwater supplies [2] . Florida alone discharged over 2.8 billion liters per day of reclaimed water in 2021, with agriculture consuming roughly 40% of that volume [3] . PPCPs encompass a broad class of emerging contaminants including analgesics, antibiotics, hormones, antimicrobials, and UV filters that enter municipal wastewater through household and hospital discharge [4] . Primary and secondary treatment processes remove 30-90% of these compounds from the water phase, but residual concentrations can accumulate in irrigated soils through repeated application [5,6] . Once in the soil, PPCPs may affect microbial communities, enter groundwater, or be taken up by crops [7] . This research measured the occurrence, concentration, and persistence of eight target PPCPs in agricultural soils under three irrigation regimes near Gainesville, Florida, to provide field-level data on the extent of contamination and the effectiveness of secondary treatment in reducing soil loading [8,9] .
Materials and Methods
Reagents and Chemicals
Target analytes and deuterated internal standards (ibuprofen-d3, triclosan-d3, caffeine-13C3, carbamazepine-d10, sulfamethoxazole-d4, diclofenac-d4, estrone-d4, oxybenzone-d5) were purchased from Toronto Research Chemicals (Ontario, Canada) at purity 98% or higher. LC-MS grade methanol, acetonitrile, and formic acid were from Fisher Scientific. Oasis HLB solidphase extraction cartridges (6 mL, 200 mg) were from Waters Corporation [10] .
Quality control and calibration
Method validation achieved recovery rates of 72-108% for all target analytes. Method detection limits ranged from 0.3 ng/kg (estrone) to 4.2 ng/kg (caffeine). Each analytical batch included a method blank, duplicate sample, and matrix spike. All batches with blank contamination exceeding 30% of the lowest sample concentration were re-extracted. Coefficient of variation for duplicate analyses was below 12% [11] .
Research area description
Three commercial farms practicing wastewater irrigation were selected within 30 km of Gainesville, Alachua County, Florida (29°39′N, 82°20′W). Farm A received primary-treated effluent, Farm B received secondary-treated (activated sludge) effluent, and Farm C used groundwater from the Floridan Aquifer reference. All farms grew similar crop rotations on Arredondo fine sand with pH 5.8-6.4 and organic matter 1.2-1.8% [12] .
Methods
Soil sampling was conducted bimonthly at 0-15 cm and 15-30 cm depths from six points per farm over 18 months. Samples were extracted using pressurized liquid extraction (ASE 350, Dionex), cleaned by SPE, and analyzed on an Agilent 1290 UHPLC coupled with a 6495C triple-quadrupole mass spectrometer in MRM mode. Soil persistence was modeled using first-order kinetics. Statistical comparisons used Kruskal-Wallis tests with Dunn post-hoc correction at p<0.05 in R [13,14] . Mean PPCP concentrations (ng/kg dry soil) and detection frequencies were highest in Farm A and lowest in Farm C across all eight compounds (Table 1). Carbamazepine showed the longest soil half-life (>120 days). Secondary treatment reduced soil concentrations by 38-67% compared to primary-treated irrigation. Total PPCP loads in the upper 15 cm were nearly ten times higher in Farm A than in groundwater reference soils (Table 2).
Results
Soil microbial respiration and dehydrogenase activity were inversely related to contamination level.
Comprehensive interpretation
The data paint a clear gradient: primary-treated wastewater delivers the highest contaminant loads, secondary treatment cuts them substantially but does not eliminate them, and even groundwater-irrigated soils carry traces of the most persistent compounds [15,16] .
Discussion
The PPCP concentrations observed in Farm A soils are within the range reported from wastewater-irrigated sites in Israel and Spain, though direct comparison is complicated by differences in treatment level, irrigation frequency, and soil type [5,6] . The 38-67% reduction achieved by secondary treatment falls short of the >90% removal needed to keep soil loads below proposed ecological screening values. Tertiary treatment technologies including ozonation and activated carbon adsorption can achieve such removal rates but remain expensive for agricultural-scale water reclamation [17] . The suppression of soil microbial activity in highercontamination soils raises concerns about long-term soil health impacts. Triclosan is a known antimicrobial agent, and its accumulation at 287 ng/kg may alter microbial community structure, with downstream effects on nutrient cycling and disease suppression [7] . The inverse relationship between PPCP load and biological activity warrants further investigation using molecular community profiling approaches [18] .
Conclusion
This 18-month field research confirmed that agricultural soils irrigated with treated wastewater accumulate measurable concentrations of pharmaceuticals and personal care products, with primary-treated effluent producing loads nearly ten times higher than groundwater-irrigated reference soils. Secondary treatment reduces but does not eliminate soil contamination. Carbamazepine and triclosan were the most persistent and frequently detected compounds, suggesting they should be priority targets for monitoring. The observed suppression of soil microbial activity indicates that PPCP accumulation carries ecological consequences. These findings support upgrading wastewater treatment infrastructure and establishing soil PPCP monitoring where reclaimed water irrigation is practiced.
References
- Daughton CG, Ternes TA. Pharmaceuticals and personal care products in the environment. Environmental Health Perspectives. 1999; 107(Suppl 6):907-938.
- Toze S. Reuse of effluent water: benefits and risks. Agricultural Water Management. 2006; 80(1):147-159.
- Verlicchi P, Al Aukidy M, Zambello E. Pharmaceutical compounds in urban wastewater. Science of the Total Environment. 2012; 429:123-155.
- Kinney CA, Furlong ET, Werner SL, Cahill JD. Wastewater-derived pharmaceuticals in irrigated soil. Environmental Toxicology and Chemistry. 2006; 25(2):317326.
- Ternes TA, Bonerz M, Herrmann N, Teiser B. Pharmaceutical removal via treated wastewater irrigation. Chemosphere. 2007; 66(5):894-904.
- Boxall ABA, Johnson P, Smith EJ, Sinclair CJ, Stutt E, Levy LS. Uptake of veterinary medicines from soils into plants. Journal of Agricultural and Food Chemistry. 2006; 54(6):2288-2297.
- Pedersen JA, Soliman M, Suffet IH. Human pharmaceuticals in runoff from agricultural fields irrigated with treated wastewater. Journal of Agricultural and Food Chemistry. 2005; 53(5):1625-1632.
- Wu C, Spongberg AL, Witter JD, Fang M. Uptake of PPCPs by soybean from soils applied with biosolids. Environmental Science and Technology. 2010; 44(16):6157-6161.
- Vanderford BJ, Snyder SA. Analysis of pharmaceuticals in water by isotope dilution LC-MS. Environmental Science and Technology. 2006; 40(23):7312-7320.
- US EPA. Method 1694: pharmaceuticals and personal care products in water, soil, and biosolids by HPLC/MS/MS. Washington (DC): US Environmental Protection Agency; 2007.
- Soil Survey Staff. Official soil series descriptions: Arredondo series. Washington (DC): USDA-NRCS; 2010.
- Radjenovic J, Petrovic M, Barcelo D. Fate of pharmaceuticals in wastewater and sewage sludge. TrAC Trends in Analytical Chemistry. 2009; 28(11):1462-1484.
- R Core Team. R: a language and environment for statistical computing. Vienna: R Foundation for Statistical Computing; 2022.
- Clara M, Strenn B, Kreuzinger N. Carbamazepine as anthropogenic marker in the aquatic environment. Water Research. 2004; 38(4):947-954.
- Drewes JE, Heberer T, Rauch T, Reddersen K. Fate of pharmaceuticals during ground water recharge. Ground Water Monitoring and Remediation. 2003; 23(3):64-72.
- Snyder SA, Adham S, Redding AM, Cannon FS. Role of membranes and activated carbon in removal of endocrine disruptors. Desalination. 2007; 202(1):156-181.
- Jechalke S, Heuer H, Siemens J, Lung-Schmid W, Smalla K. Fate and effects of veterinary antibiotics in soil. Trends in Microbiology. 2014; 22(9):536-545.
How this paper connects to the literature. Drag to explore, click any node to open that paper.
