Fate and Transport of Hormones & Antimicrobials

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Fate and Transport of Hormones & Antimicrobials Linda S. Lee Purdue University Dept. of Agronomy April 25, 2008 1 Basic Properties & Source Concentrations Fate Processes Transport Processes 2 Hormones: Natural & Synthetic Estrogens & Androgens 17β-estradiol testosterone 17β-trenbolone 3 Hormones are weakly polar compounds that do not exhibit a charge (0) in the environment 1

Antimicrobials (antibiotics and antiparasitics) range in size and polarity, and their behavior in soil and water is depend on acidity (ph). General Tetracycline Structure 100 80 Charge Characteristics Change with ph Percent 60 40 20 Antibiotics can exhibit a positive charge (+), a negative charge (-), both charges (+ -) at the same time, or no charge (neutral) depending on ph (a measure of acidity). 4 0 3 5 7 ph Large portions of antibiotics are not adsorbed or degraded by the animal, thus excreted in feces and urine Antibiotic excreted Tetracyclines 75 80 % mg/kg or mg/l (in near fresh manure) <1 to 200 beef, swine, poultry Monensin 50 90 % 1 to 5 cattle Tylosin 50 90 % 3 to 8 swine Natural hormones are also excreted in feces and urine 5 Manure is land-applied based on N needs Swine manure: 65,000 to 130,000 lbs/ha ~1 to 3 % mass relative to soil in a hectare 6 Municipal biosolids, which are also land applied, contain antimicrobials and hormones as well as other personal care products 2

Multiple Fate & Transport Processes Photocomposition Winds Tile Drain Plant Uptake Volatilization Leaching Sorption Degradation Surface Runoff Water Table 7 Sorption The affinity of compounds such as hormones and antimicrobials for soil particles. -o+ -o+ -o+ -o+- - Soil -o+- -+ o - 8 -o+ Soil Solution -o+- -o+ - Higher sorption means less is in the water. Sorption varies substantially for different antimicrobials, but variation is small for different hormones. The soil property that controls sorption also varies between hormones and antimicrobials. The affinity of hormones for soil is primarily controlled by the organic matter in soil. Concentration in Soil Soil-water Distribution Coefficient: K d = Concentration in Water K d Increasing Sorption 9 Percent Organic Matter Increasing Hormone sorption increases with increasing soil organic matter content. 3

Sorption is ph-dependent for almost all antimicrobials 10000000 Tetracyclines 10000 Monensin 1000000 Sorption Magnitude 100000 1000 10000 1000 100 3 4 5 6 7 8 4 5 6 7 8 ph ph ph +00 +- 0 +-- 0 - Sorption correlates well to Soil Cation Exchange Capacity from clay & organic matter Sorption correlates well to Soil Organic Carbon The soil property of greatest importance in estimating affinity to soil depends on the type of antibiotic 10 Antimicrobials and hormone ( ) distribution in holding ponds of manure flushed out of animal housing units Lagoon Effluent 0.04 mg/l (ppm) Lagoon Solids 2.0 mg/kg (ppm) 11 Typically much more antimicrobial or hormone is associated with the solids compared to the liquid Microbial Degradation Half lives (t ½ ): time for 50% loss of target compound t ½ ranges from a few days to over one year Low Oxygen High Oxygen (anaerobic) decreasing t½ (aerobic) Manure Pit Agriculture Field Conditions that favor activity of aerobic bacteria tends to reduce antimicrobial & hormone persistence 12 Preferred Temperature: 20 C to 37 C Preferred Moisture: not flooded; not dry Preferred ph range: 6 to 8 Soil only Manure + Soil 4

Degradation = complete mineralization only that the parent antibiotic is changed Tylosin A CHO OCH 3 Tylosin B Degradation of antibiotic may not equate to loss of antibiotic activity 13 Degradation May Be Reversible (Form in beef implant) (Most active form) (Primary form in manure) Reversible degradation within soil (likely small) and within unintended receptor such as fish 14 Abiotic Degradation (not dependent on bacteria) Factoryfarm.org Nitrates can enhance antibiotic photolysis in water. Dissolved humic materials can enhance or hinder antibiotic photolysis Soil surfaces can enhance transformation of antibiotics and hormones, but microbial processes dominate 15 5

Plant Uptake of Antimicrobials Yes, for some antibiotics and some plant species. HOWEVER Estimated potential daily intake for a human consuming these plants is in the order of a few µg/day - not an amount expected to pose a threat to human health 16 Noteworthy Humans take antibiotics at the 50,000 to 500,000 μg/day level. Streptomycin and oxytetracycline are approved for use in many food crops including several fruits, potatoes, and celery. Antimicrobial & Hormone Transport through Soil with Infiltrating Water: Leaching Leaching is generally inversely proportional to sorption The higher affinity an antimicrobial or hormone has for the soil, the slower it will leach The more resistant an antibiotic or hormone is to degradation, the more time it has to leach Antimicrobials and hormones sorbed to mobile clay colloids or dissolved organic matter will move faster than expected 17 Transport with Overland Flow: Run-Off Rainfall rate > infiltration rate Saturated soils can not hold additional water What moves with water run-off? Hormone-laden soil Hormone-laden manure Antibiotic-laden soil Antibiotic-laden manure Antibiotic-resistant bacteria Run-off is considered to contribute more to inputs from manure and antibiotics to streams than leaching 18 6

Tile Drainage and Facilitated Transport Midwest soils are typically fertile, but poorly drained To enhance productivity, drainage is facilitated by an artificial subsurface drain network placed 1 m below the soil surface Excess soil water (and associated constituents) is rapidly moved to surface waterways Preferential flow paths to tiles develop over time reducing the effect of soil attenuation on transport Relative contribution not well known yet 19 Concentrations decrease over time while in storage and once land applied: (degradation & dilution) Oxytetracycline from Calves (fed 60,000 ppb in milk) Fresh manure 872 ppb Bedding 367 ppb Aged manure (1 mo) 19 ppb Aged manure (4 mo) 2.1 ppb Soil 0.006 ppb Tile Drain Water Not detected Current issues of greater focus: Transfer & growth of antibiotic resistant bacteria Hormones 20 ( Example from study by De Liguoro et al. 2003) Potential Impact of Antimicrobials versus Hormones Antimicrobials Low concentrations not likely to affect humans. Too low to induce antibiotic resistance in native bacteria Bluegreen algae impacted in the ppb range - food chain implications?? Kolpin et al. 2002 Hormones at low part per trillion (10 to 100 ppt) in waterways can adversely affect the reproductive biology of aquatic species (sex and diversity in fish) and possibly other wildlife. 21 And then what about mixtures???? 7

22 Summary: General Rules of Thumb Major transport processes of manure-borne constituents includes leaching, run off, and tile drainage. Antimicrobial sorption to soils increases ( ) with soil ph, % clay and % organic matter (OM). Hormone sorption to soils increases ( ) with %OM. Antimicrobials & hormones generally degrade faster in moist aerobic soil environments reducing their persistence. Antimicrobial concentrations in plants are several orders of magnitude lower than what we take orally. Antibiotic-resistant bacteria are a currently a greater concern than antibiotic concentrations in the environment. Very low hormones concentrations are still of concern and can negatively impact aquatic species. 8