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An approach
for mapping the vulnerability of
European Union soils
to antibiotic contamination

 De la Torre, A; Iglesias, I; Carballo, M; Muñoz, M
torre@inia.es        CISA-INIA
Worldwide, antibiotics are widely
prescribed to treat bacterial infections in human and
animals.
Their use show many
advantages among which
the most important are:




 They are compounds commonly used.
 Many of them show a high stability in the environment.
 They are biologically very potent and able to trigger
responses at very low doses.
They are active against highly conserved biological
pathways. They can therefore act on different living
organisms.
Veterinary antimicrobials
are widely used as
therapeutics in intensive
farming, at both the
prestarter (weaning) and
fattening (first month)
stages.
Antibiotics pose specific risks for the environment, since they
are particularly designed to kill or inhibit microorganisms:

                  Adverse effects on living organisms



                      Antibiotic residual in the food chain



                             Antibiotic residual in wildlife


                                        Microbial resistence
TWO MAIN ACTIONS ARE BEING PROMOTED BY I.O.

                               European Medicines Agency
                               requires the ecotoxicological
                               assessment of antimicrobials
                               before marketing authorization


Many international organisms
such as OIE and WHO have
alerted about the appearance of
antimicrobial resistance. They
have argued
that environmental surveillance of
antimicrobial presence and
resistance should also be
mandated.
Environmental Surveillance
         of antimicrobial presence and resistance




                        ¿?
The objective of the present work is to develop a soil
vulnerability map to antibiotic contamination.

• It would allow to identify areas at high risk for antibiotic
contamination.
• It may help to allocate surveillan efforts in future researches.
METHODOLOGY: Spatial RISK ANALYSIS conducted in a GIS
 environment.

1. RELEASE        LIVESTOCK DENSITY                                                       Values from 0 to 1 as function of density




                                                                                                                                                          MCD = Release x Exposure x Consequence
                                                                                                                                                          MCD = Release x Exposure x Consequence
2. EXPOSURE                                            ANTIBIOTIC CONTAMINATION IN SOIL = (B+P)/2



                   BINDING POTENTIAL (B)*                                                  PERSISTENCE POTENTIAL (P)*

                   BINDING                              Adsorption value (Koc)**           PERSISTENCE                       Degradation value (DT50)**
                   VALUE                                                                   VALUE
                                                        1    2     3     4     5                                             1    2     3     4     5
                     Soil organic carbon content




                                                                                               Mean annual temperature
                                                   1                                                                     1


                                                   2                                                                     2


                                                   3                                                                     3


                                                   4                                                                     4


                                                   5                                                                     5




3. CONSEQUENCE   SOIL USE                                     Agricultural and Pasture land use assumes value of 1 (Other soil types=0)
The study area comprised the European Union countries
where the required geo-referenced data at 10 km resolution
were available on a continuous scale for statistical analyses.
1. RELEASE




                 2. EXPOSURE




3. CONSEQUENCE
PERSISTENCE: Persistence is the opposite to degradation or the break down as a
                result of microbiological reactions in soils.


ADSORPTION: Adsorption describes the attraction between a chemical and soil.
Boxall el at., 2010


                                         NON PERSISTENT     SLIGHTLY PERSISTENT   MODERATELY PERSISTENT    PERSISTENT
                                            DT50<5d              DT50 5-21d            DT50 22-60 d         DT50 >60 d

                                                             INCREASING PERSISTENCE

    VERY LOW                             Sulfamethazine
     Koc < 15



       LOW                               Sulfadimethoxine     Metronidazole            Chlordufon
     Koc 15-74                                                                         Florfenicol
                 DECREASING ADSORPTION
                 DECREASING ADSORPTION



MODERATE                                                        Olaquindox               Ceftiofur
Koc 75-499




     HIGH                                                        Tylosin                                   Eprinomectin
  Koc 500-4000                                                  Emamectin                                   Diclazuril
                                                                                                           Oxfendazole


    VERY HIGH                                                                          Deltamethrin        Albendazole
    Koc >4000                                                                                              Cypermethrin
                                                                                                           Danofloxacin
                                                                                                            Doramectin
                                                                                                           Erythromycin
                                                                                                            Ivermectin
                                                                                                            Moxidectin
                                                                                                          Oxytetracycline
                                                                                                            Selamectin
                                                                                                           Sarafloxacin
FLUORO & QUINOLONES

     TETRACYCLINES

     SULPHONAMIDES




                  0


                      50


                           100


                                     150


                                            200


                                                    250


                                                              300


                                                                    350


                                                                           400
                                 Soil concentration (µg/kg)




                                                          TETRACICLINAS (1.183 Tn)

                                                          SULFONAMIDAS+TRIMETOPRIMAS (428 Tn)

                                                          β LACTÁMICOS+CEFALOSPORINAS (273 Tn)

                                                          MACRÓLIDOS+LINCOSAMIDAS (197 Tn)

                                                          AMINOGLICÓSIDOS (121 Tn)

                                                          FLUORO + QUINOLONAS (29 Tn)

                                                          ANFENICOLES (6 Tn)

                                                          OTROS (109 Tn)
CONCLUSIONS
The inclusion of fluoroquinolones and tetracyclines
  in the surveillance plans should be deeper
  considered.

To know the geographical variability of potential
  antibiotic accumulation on soil is very useful for
  deciding how to allocate limited resources
  among national environmental surveillance
  programs of antibiotics.
THANKS FOR YOUR ATTENTION!!!

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An Approach for Mapping the Vulnerability of European Union Soils to Antibiotic Contamination

  • 1. An approach for mapping the vulnerability of European Union soils to antibiotic contamination De la Torre, A; Iglesias, I; Carballo, M; Muñoz, M torre@inia.es CISA-INIA
  • 2. Worldwide, antibiotics are widely prescribed to treat bacterial infections in human and animals.
  • 3. Their use show many advantages among which the most important are: They are compounds commonly used. Many of them show a high stability in the environment. They are biologically very potent and able to trigger responses at very low doses. They are active against highly conserved biological pathways. They can therefore act on different living organisms.
  • 4. Veterinary antimicrobials are widely used as therapeutics in intensive farming, at both the prestarter (weaning) and fattening (first month) stages.
  • 5. Antibiotics pose specific risks for the environment, since they are particularly designed to kill or inhibit microorganisms: Adverse effects on living organisms Antibiotic residual in the food chain Antibiotic residual in wildlife Microbial resistence
  • 6. TWO MAIN ACTIONS ARE BEING PROMOTED BY I.O. European Medicines Agency requires the ecotoxicological assessment of antimicrobials before marketing authorization Many international organisms such as OIE and WHO have alerted about the appearance of antimicrobial resistance. They have argued that environmental surveillance of antimicrobial presence and resistance should also be mandated.
  • 7. Environmental Surveillance of antimicrobial presence and resistance ¿? The objective of the present work is to develop a soil vulnerability map to antibiotic contamination. • It would allow to identify areas at high risk for antibiotic contamination. • It may help to allocate surveillan efforts in future researches.
  • 8. METHODOLOGY: Spatial RISK ANALYSIS conducted in a GIS environment. 1. RELEASE LIVESTOCK DENSITY Values from 0 to 1 as function of density MCD = Release x Exposure x Consequence MCD = Release x Exposure x Consequence 2. EXPOSURE ANTIBIOTIC CONTAMINATION IN SOIL = (B+P)/2 BINDING POTENTIAL (B)* PERSISTENCE POTENTIAL (P)* BINDING Adsorption value (Koc)** PERSISTENCE Degradation value (DT50)** VALUE VALUE 1 2 3 4 5 1 2 3 4 5 Soil organic carbon content Mean annual temperature 1 1 2 2 3 3 4 4 5 5 3. CONSEQUENCE SOIL USE Agricultural and Pasture land use assumes value of 1 (Other soil types=0)
  • 9. The study area comprised the European Union countries where the required geo-referenced data at 10 km resolution were available on a continuous scale for statistical analyses.
  • 10. 1. RELEASE 2. EXPOSURE 3. CONSEQUENCE
  • 11. PERSISTENCE: Persistence is the opposite to degradation or the break down as a result of microbiological reactions in soils. ADSORPTION: Adsorption describes the attraction between a chemical and soil.
  • 12.
  • 13. Boxall el at., 2010 NON PERSISTENT SLIGHTLY PERSISTENT MODERATELY PERSISTENT PERSISTENT DT50<5d DT50 5-21d DT50 22-60 d DT50 >60 d INCREASING PERSISTENCE VERY LOW Sulfamethazine Koc < 15 LOW Sulfadimethoxine Metronidazole Chlordufon Koc 15-74 Florfenicol DECREASING ADSORPTION DECREASING ADSORPTION MODERATE Olaquindox Ceftiofur Koc 75-499 HIGH Tylosin Eprinomectin Koc 500-4000 Emamectin Diclazuril Oxfendazole VERY HIGH Deltamethrin Albendazole Koc >4000 Cypermethrin Danofloxacin Doramectin Erythromycin Ivermectin Moxidectin Oxytetracycline Selamectin Sarafloxacin
  • 14.
  • 15.
  • 16. FLUORO & QUINOLONES TETRACYCLINES SULPHONAMIDES 0 50 100 150 200 250 300 350 400 Soil concentration (µg/kg) TETRACICLINAS (1.183 Tn) SULFONAMIDAS+TRIMETOPRIMAS (428 Tn) β LACTÁMICOS+CEFALOSPORINAS (273 Tn) MACRÓLIDOS+LINCOSAMIDAS (197 Tn) AMINOGLICÓSIDOS (121 Tn) FLUORO + QUINOLONAS (29 Tn) ANFENICOLES (6 Tn) OTROS (109 Tn)
  • 17. CONCLUSIONS The inclusion of fluoroquinolones and tetracyclines in the surveillance plans should be deeper considered. To know the geographical variability of potential antibiotic accumulation on soil is very useful for deciding how to allocate limited resources among national environmental surveillance programs of antibiotics.
  • 18. THANKS FOR YOUR ATTENTION!!!