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Emerging Contaminants  in  Biosolids George O’Connor Soil and Water Science Department,  University of Florida 20 th  Annual Biosolids Management Conference September 9-11, 2007 Contributing author: Liz H. Snyder
Slide credit:  Adapted and extended by Daughton from:  Renewable Resources Journal , 2005, 23(4):6-23. Common Contaminant “Lingo” ,[object Object],[object Object],Chemical Group Grouping Method EDC   (Endocrine Disrupting Chemical) toxicological mode of action or endpoint PBT   (Persistent, Bioaccumulative Toxic) POP   (Persistent Organic Pollutant) environmental properties OWC   (Organic Wastewater Contaminant) location of occurrence PPCP  (Pharmaceuticals and Personal Care Product) type of intended usage Priority Pollutant regulation ECC  (Emerging Compound of Concern) novelty, fad, timeliness, or new concern Xenobiotics foreign versus endogenous HPV  (High Production Volume) chemical quantity (manufactured/imported in US  ≥1 million pounds/year) POHO   (Pollutant Of Human Origin) source or origin
Target Compounds for USGS National Reconnaissance of Emerging Contaminants in US  Streams   Extend list to biosolids? ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Emerging Contaminants in Biosolids ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
PPCPs  as “Emerging” Risks? It is reasonable to surmise that the occurrence of PPCPs in waters is not a new phenomenon.  It has only become more widely evident in the last decade because continually improving chemical analysis methodologies have lowered the limits of detection for a wide array of xenobiotics in environmental matrices.  There is no reason to believe that PPCPs have not existed in the environment for as long as they have been used commercially. Slide credit:  Adapted from Christian Daughton, PhD, Environmental Protection Agency
Einstein on: Environmental Monitoring “ Not everything that can be counted counts, and not everything that counts can be counted.“  (o ft attributed to Albert Einstein) corollary for environmental monitoring: Not everything that can be measured is worth measuring, and not everything worth measuring is measurable. Slide credit:  Adapted from Christian Daughton, PhD, Environmental Protection Agency
Predicting the fate of  emerging contaminants  – difficult, but  not  hopeless ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
[object Object],[object Object],[object Object],Objectives
 
Available:  http://www.epa.gov/nerlesd1/chemistry/pharma/image/drawing.pdf
Concentrated population Central wastewater treatment facility Sewage sludge Effluent Kill pathogens Remove solids Biosolids Landfill or incineration Land application Industry Pre-treatment
Metabolite Metabolite Contaminant Contaminant Contaminant Contaminant Metabolite + In biosolids and/or effluent WWTP
Contaminant Fate In WWTPs ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Some Organic Contaminants in Biosolids * Adapted from Xia, 2005; Kinney, 2006; Kester, 2005 Compound Concentration (mg kg -1 ) Log Kow Solubility (mg L -1 ) Vapor Pressure  (mmHg) Antimicrobial Compounds         triclosan 10.2 4.53 10   6.45 x 10 -7 Human Drugs         carbamazepine 0.07 2.45  17.7 1.84 x 10 -7 Fragrances         d-limonene 0.63 4.57  13.8  1.98 indole 19.6 2.14  3560  1.22 x 10 -2 Sex and Steroidal Hormones         3b-coprostanol 126  8.82  0.000203  5.47 x 10 -10 cholesterol 209 8.74  0.095  7.79 x 10 -10 Plasticizers         bis(2-ethylhexyl)phthalate 20 - 160 3.98 0.40   6.45 x 10 -6 diethylhexyl phthalate 10.5 7.88  0.27  1.42 x 10 -7 Polycyclic aromatic hydrocarbons          anthracene 0.14 4.5  0.0434  6.53 x 10 -6 phenanthrene 0.342 4.52 1.15  1.21 x 10 -4 Others         1,4-dichlorobenzene 5.3    3.52   79 1 phenol 2.1 - 54.7 1.5  82800  0.35 bisphenol A 4.70 3.32 120 3.91 x 10 -7 PCBs (Actual concentration – 95 th  %) Total toxic equivalent basis (TEQ)– 95 th  percentile 0.21 0.0000131   4.5 – > 8.0 0.000004 – 7.48   7.6 x 10 -10  – 0.08 Penta dibrominated diphenyl ethers PBDEs (Sum)   <0.008 – 4.89 5.74 – 8.27 0.01 - 0.13 2.12 x 10 -9  –  1.94 x 10 -3 Polychlorinated dibenzodioxins and Dibenzofurans (total TEQ) 0.0000333 6.8 0.0000193 7.4 x 10 -4
Attitudes Towards Emerging Contaminants in Biosolids ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
The “Correct” Attitude ,[object Object],[object Object],[object Object]
Principles of Organic Contaminant  Behavior in Biosolids-Amended Soils ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
 
Retention/Release/Partitioning
Retention/Release ,[object Object],[object Object],[object Object],[object Object],[object Object]
Partitioning, K ow ,[object Object],[object Object],[object Object],[object Object]
Degradation
Degradation ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Volatilization
Volatilization ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Photolysis
Photolysis ,[object Object],[object Object],[object Object],[object Object],[object Object]
Plant Uptake and Metabolism
Plant Uptake and Metabolism ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Leaching and Runoff
Leaching and Runoff ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
“ Hazardous Traits”  ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Applying Principles to Emerging Organics ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Transport Hydrus Chemflo 2000 Chemical Movement in Soils (CMIS) ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
QSAR Persistent, Bioaccumulative,  Toxin Profiler Ecological Structure Activity Relationships (ECOSAR) ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Fugacity Biosolids-Amended Soil: Level 4 (BASL 4) ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Inferences
Inferences Continued
[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],Knowns and Expectations
[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],Unknowns and Potential Surprises ?
Chemical Movement in Soils (CMIS) Exercise 1
logK oc  = 3.7  Half-life = 100 days logK oc  = 3.7  Half-life = 5 days
Chemical Movement in Soils (CMIS) Exercise 2
logK oc  = 3.1  Half-life = 30 days logK oc  = 1.8  Half-life = 60 days
Thumbs Up / Thumbs Down ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
 

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Emerging Contaminants in Biosolids and Soil

  • 1. Emerging Contaminants in Biosolids George O’Connor Soil and Water Science Department, University of Florida 20 th Annual Biosolids Management Conference September 9-11, 2007 Contributing author: Liz H. Snyder
  • 2.
  • 3.
  • 4.
  • 5. PPCPs as “Emerging” Risks? It is reasonable to surmise that the occurrence of PPCPs in waters is not a new phenomenon. It has only become more widely evident in the last decade because continually improving chemical analysis methodologies have lowered the limits of detection for a wide array of xenobiotics in environmental matrices. There is no reason to believe that PPCPs have not existed in the environment for as long as they have been used commercially. Slide credit: Adapted from Christian Daughton, PhD, Environmental Protection Agency
  • 6. Einstein on: Environmental Monitoring “ Not everything that can be counted counts, and not everything that counts can be counted.“ (o ft attributed to Albert Einstein) corollary for environmental monitoring: Not everything that can be measured is worth measuring, and not everything worth measuring is measurable. Slide credit: Adapted from Christian Daughton, PhD, Environmental Protection Agency
  • 7.
  • 8.
  • 9.  
  • 11. Concentrated population Central wastewater treatment facility Sewage sludge Effluent Kill pathogens Remove solids Biosolids Landfill or incineration Land application Industry Pre-treatment
  • 12. Metabolite Metabolite Contaminant Contaminant Contaminant Contaminant Metabolite + In biosolids and/or effluent WWTP
  • 13.
  • 14. Some Organic Contaminants in Biosolids * Adapted from Xia, 2005; Kinney, 2006; Kester, 2005 Compound Concentration (mg kg -1 ) Log Kow Solubility (mg L -1 ) Vapor Pressure (mmHg) Antimicrobial Compounds         triclosan 10.2 4.53 10   6.45 x 10 -7 Human Drugs         carbamazepine 0.07 2.45 17.7 1.84 x 10 -7 Fragrances         d-limonene 0.63 4.57 13.8 1.98 indole 19.6 2.14 3560 1.22 x 10 -2 Sex and Steroidal Hormones         3b-coprostanol 126 8.82 0.000203 5.47 x 10 -10 cholesterol 209 8.74 0.095 7.79 x 10 -10 Plasticizers         bis(2-ethylhexyl)phthalate 20 - 160 3.98 0.40   6.45 x 10 -6 diethylhexyl phthalate 10.5 7.88 0.27 1.42 x 10 -7 Polycyclic aromatic hydrocarbons         anthracene 0.14 4.5 0.0434 6.53 x 10 -6 phenanthrene 0.342 4.52 1.15 1.21 x 10 -4 Others         1,4-dichlorobenzene 5.3   3.52   79 1 phenol 2.1 - 54.7 1.5 82800 0.35 bisphenol A 4.70 3.32 120 3.91 x 10 -7 PCBs (Actual concentration – 95 th %) Total toxic equivalent basis (TEQ)– 95 th percentile 0.21 0.0000131   4.5 – > 8.0 0.000004 – 7.48   7.6 x 10 -10 – 0.08 Penta dibrominated diphenyl ethers PBDEs (Sum)   <0.008 – 4.89 5.74 – 8.27 0.01 - 0.13 2.12 x 10 -9 – 1.94 x 10 -3 Polychlorinated dibenzodioxins and Dibenzofurans (total TEQ) 0.0000333 6.8 0.0000193 7.4 x 10 -4
  • 15.
  • 16.
  • 17.
  • 18.  
  • 20.
  • 21.
  • 23.
  • 25.
  • 27.
  • 28. Plant Uptake and Metabolism
  • 29.
  • 31.
  • 32.
  • 33.
  • 34.
  • 35.
  • 36.
  • 39.
  • 40.
  • 41. Chemical Movement in Soils (CMIS) Exercise 1
  • 42. logK oc = 3.7 Half-life = 100 days logK oc = 3.7 Half-life = 5 days
  • 43. Chemical Movement in Soils (CMIS) Exercise 2
  • 44. logK oc = 3.1 Half-life = 30 days logK oc = 1.8 Half-life = 60 days
  • 45.
  • 46.  

Notes de l'éditeur

  1. HYDRUS: Hydrus 1D is free (public domain); all versions require understanding of soil properties, soil/solute reactions, and some soil physics; considers equilibrium and dynamic scenarios CHEMFLO: public domain; still requires some knowledge of parameters important to solute transport in soils; considers equilibrium and dynamic scenarios CMIS : public domain; requires minimal knowledge of soil chemistry and physics
  2. QSAR: quantitative structure-activity relationship, i.e. activity is a function of physicochemical properties and/or structural properties PBT Profiler and ECOSAR : requires working knowledge of basic organic chemistry concepts; both available via EPA website
  3. Requires basic understanding of soil chemistry and physics, as well as the concept of fugacity, i.e. the tendency of a substance to prefer one phase over another