Source: AGRICULTURAL RESEARCH SERVICE submitted to NRP
PERSISTENCE AND MOBILITY OF ESTROGENS IN THE ENVIRONMENT
Sponsoring Institution
Agricultural Research Service/USDA
Project Status
ACTIVE
Funding Source
Reporting Frequency
Annual
Accession No.
0418620
Grant No.
(N/A)
Cumulative Award Amt.
(N/A)
Proposal No.
(N/A)
Multistate No.
(N/A)
Project Start Date
Dec 1, 2009
Project End Date
Nov 30, 2013
Grant Year
(N/A)
Program Code
[(N/A)]- (N/A)
Recipient Organization
AGRICULTURAL RESEARCH SERVICE
(N/A)
FARGO,ND 58102-2765
Performing Department
(N/A)
Non Technical Summary
(N/A)
Animal Health Component
60%
Research Effort Categories
Basic
40%
Applied
60%
Developmental
0%
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
7123310200050%
7123410200030%
7123510200020%
Goals / Objectives
All animals produce natural hormones in the healthy function and regulation of their endocrine system. When a hormone is eliminated from the body and gets into the environment, it can act upon other animals as an endocrine disrupting compound by binding to and activating receptors within hormone-responsive organs. In sensitive organisms this can occur at the parts per trillion level, and risks include sex reversals and cancer. The potential for livestock farms to serve as sources of hormones to the environment has been recognized for many years. To guide the objectives of this proposal, the following research questions (RQ) were formulated to evaluate the respective testable hypotheses (TH): RQ 1) Does dissolved organic carbon and particulates from lagoon waste or soil enhance the mobility of estrogens in mineral soil and thus increase the potential for off-site movement? TH 1) If the movement of estrogens is related to the presence of lagoon- or soil-derived dissolved organic carbon and particulates, then estrogen in the presence of high amounts of soil/lagoon dissolved organic carbon will increase their mobility compared to aqueous free estrogens. RQ 2) Does dissolved organic carbon and particulates of lagoon waste or soil offer estrogenic hormones protection from microbial degradation and increase their longevities in the soil or manure storage facilities? TH 2) If estrogenic hormones are bound to dissolved organic carbon or particulates and not easily accessible to microbial processes, then hormone in the presence of high amounts of dissolved organic carbon or particulates will increase persistence in the environment compared to free aqueous hormone. RQ 3) Do estrogen conjugates (i.e. polar metabolites) promote the mobility or persistence of estrogens in soil? TH 3) If conjugated hormones are more water soluble than their de-conjugated forms, then they are also more mobile in the soil and can potentially migrate to areas of reduced microbial degradation. RQ 4) Do estrogens and their conjugates from lagoon waste applied to fields move into groundwater and into surface waters? TH 4) If the mobility of estrogens in soil is dependant on hormone conjugation, the presence of dissolved organic carbon or particulates, and the low retention time in upper soil layers, then application of manures on tile drainage fields will increase the presence of hormone/hormone conjugates in ground and surface waters. To answer these research questions and test the hypotheses, the following experimental objectives were formed: Objective 1 ¿ Determine the sorption characteristics of estradiol, estradiol glucuronide and sulfate conjugates with particulates originating from natural organic matter from soil and from animal manure lagoon liquors (laboratory); Objective 2 ¿ Determine the degradation of the parent compounds estradiol, estradiol glucuronide and sulfate conjugates in the presence of these particulates and soil (laboratory); and Objective 3 ¿ Determine how land application strategies (surface applied vs. injection) for lagoon liquor influence the fate and transport of estradiol in a field setting.
Project Methods
Objective 1: Degradation of hormones is mediated primarily by biological activity and can lead to misinterpretation of observed physical/chemical soil absorption processes. In order to identify these processes experimentally, the experiments for this objective will be conducted under sterile conditions. Four hormone concentrations and nine time points will be used and sampled. Qualititative and quantitative assessment of hormone degradation and soil absorption will be made by chromatographic and spectrometric methods, and absorption curves and models can then be determined. Objective 2: High and low organic soils will be spiked with radioactive hormone conjugates with and without lagoon waste under aerobic/anaerobic and sterile/non-sterile conditions to measure biological degradation in soil. Mass balances, qualitative assessment of hormone fate, and separation of hormone compartments into the various soil fractions under these conditions will be determined. Objective 3: Well-defined field-scale Discovery Farms will be used to measure the transport of hormones when injected into soil and followed by uncontrolled and controlled drainage (rainfall). Both well water and soil extracts will be analyzed for hormone content across two growing seasons.

Progress 10/01/12 to 09/30/13

Outputs
Progress Report Objectives (from AD-416): All animals produce natural hormones in the healthy function and regulation of their endocrine system. When a hormone is eliminated from the body and gets into the environment, it can act upon other animals as an endocrine disrupting compound by binding to and activating receptors within hormone-responsive organs. In sensitive organisms this can occur at the parts per trillion level, and risks include sex reversals and cancer. The potential for livestock farms to serve as sources of hormones to the environment has been recognized for many years. To guide the objectives of this proposal, the following research questions (RQ) were formulated to evaluate the respective testable hypotheses (TH): RQ 1) Does dissolved organic carbon and particulates from lagoon waste or soil enhance the mobility of estrogens in mineral soil and thus increase the potential for off-site movement? TH 1) If the movement of estrogens is related to the presence of lagoon- or soil-derived dissolved organic carbon and particulates, then estrogen in the presence of high amounts of soil/lagoon dissolved organic carbon will increase their mobility compared to aqueous free estrogens. RQ 2) Does dissolved organic carbon and particulates of lagoon waste or soil offer estrogenic hormones protection from microbial degradation and increase their longevities in the soil or manure storage facilities? TH 2) If estrogenic hormones are bound to dissolved organic carbon or particulates and not easily accessible to microbial processes, then hormone in the presence of high amounts of dissolved organic carbon or particulates will increase persistence in the environment compared to free aqueous hormone. RQ 3) Do estrogen conjugates (i.e. polar metabolites) promote the mobility or persistence of estrogens in soil? TH 3) If conjugated hormones are more water soluble than their de- conjugated forms, then they are also more mobile in the soil and can potentially migrate to areas of reduced microbial degradation. RQ 4) Do estrogens and their conjugates from lagoon waste applied to fields move into groundwater and into surface waters? TH 4) If the mobility of estrogens in soil is dependant on hormone conjugation, the presence of dissolved organic carbon or particulates, and the low retention time in upper soil layers, then application of manures on tile drainage fields will increase the presence of hormone/ hormone conjugates in ground and surface waters. To answer these research questions and test the hypotheses, the following experimental objectives were formed: Objective 1 � Determine the sorption characteristics of estradiol, estradiol glucuronide and sulfate conjugates with particulates originating from natural organic matter from soil and from animal manure lagoon liquors (laboratory); Objective 2 � Determine the degradation of the parent compounds estradiol, estradiol glucuronide and sulfate conjugates in the presence of these particulates and soil (laboratory); and Objective 3 � Determine how land application strategies (surface applied vs. injection) for lagoon liquor influence the fate and transport of estradiol in a field setting. Approach (from AD-416): Objective 1: Degradation of hormones is mediated primarily by biological activity and can lead to misinterpretation of observed physical/chemical soil absorption processes. In order to identify these processes experimentally, the experiments for this objective will be conducted under sterile conditions. Four hormone concentrations and nine time points will be used and sampled. Qualititative and quantitative assessment of hormone degradation and soil absorption will be made by chromatographic and spectrometric methods, and absorption curves and models can then be determined. Objective 2: High and low organic soils will be spiked with radioactive hormone conjugates with and without lagoon waste under aerobic/anaerobic and sterile/non-sterile conditions to measure biological degradation in soil. Mass balances, qualitative assessment of hormone fate, and separation of hormone compartments into the various soil fractions under these conditions will be determined. Objective 3: Well-defined field-scale Discovery Farms will be used to measure the transport of hormones when injected into soil and followed by uncontrolled and controlled drainage (rainfall). Both well water and soil extracts will be analyzed for hormone content across two growing seasons.

Impacts
(N/A)

Publications


    Progress 10/01/11 to 09/30/12

    Outputs
    Progress Report Objectives (from AD-416): All animals produce natural hormones in the healthy function and regulation of their endocrine system. When a hormone is eliminated from the body and gets into the environment, it can act upon other animals as an endocrine disrupting compound by binding to and activating receptors within hormone-responsive organs. In sensitive organisms this can occur at the parts per trillion level, and risks include sex reversals and cancer. The potential for livestock farms to serve as sources of hormones to the environment has been recognized for many years. To guide the objectives of this proposal, the following research questions (RQ) were formulated to evaluate the respective testable hypotheses (TH): RQ 1) Does dissolved organic carbon and particulates from lagoon waste or soil enhance the mobility of estrogens in mineral soil and thus increase the potential for off-site movement? TH 1) If the movement of estrogens is related to the presence of lagoon- or soil-derived dissolved organic carbon and particulates, then estrogen in the presence of high amounts of soil/lagoon dissolved organic carbon will increase their mobility compared to aqueous free estrogens. RQ 2) Does dissolved organic carbon and particulates of lagoon waste or soil offer estrogenic hormones protection from microbial degradation and increase their longevities in the soil or manure storage facilities? TH 2) If estrogenic hormones are bound to dissolved organic carbon or particulates and not easily accessible to microbial processes, then hormone in the presence of high amounts of dissolved organic carbon or particulates will increase persistence in the environment compared to free aqueous hormone. RQ 3) Do estrogen conjugates (i.e. polar metabolites) promote the mobility or persistence of estrogens in soil? TH 3) If conjugated hormones are more water soluble than their de- conjugated forms, then they are also more mobile in the soil and can potentially migrate to areas of reduced microbial degradation. RQ 4) Do estrogens and their conjugates from lagoon waste applied to fields move into groundwater and into surface waters? TH 4) If the mobility of estrogens in soil is dependant on hormone conjugation, the presence of dissolved organic carbon or particulates, and the low retention time in upper soil layers, then application of manures on tile drainage fields will increase the presence of hormone/hormone conjugates in ground and surface waters. To answer these research questions and test the hypotheses, the following experimental objectives were formed: Objective 1 � Determine the sorption characteristics of estradiol, estradiol glucuronide and sulfate conjugates with particulates originating from natural organic matter from soil and from animal manure lagoon liquors (laboratory); Objective 2 � Determine the degradation of the parent compounds estradiol, estradiol glucuronide and sulfate conjugates in the presence of these particulates and soil (laboratory); and Objective 3 � Determine how land application strategies (surface applied vs. injection) for lagoon liquor influence the fate and transport of estradiol in a field setting. Approach (from AD-416): Objective 1: Degradation of hormones is mediated primarily by biological activity and can lead to misinterpretation of observed physical/chemical soil absorption processes. In order to identify these processes experimentally, the experiments for this objective will be conducted under sterile conditions. Four hormone concentrations and nine time points will be used and sampled. Qualititative and quantitative assessment of hormone degradation and soil absorption will be made by chromatographic and spectrometric methods, and absorption curves and models can then be determined. Objective 2: High and low organic soils will be spiked with radioactive hormone conjugates with and without lagoon waste under aerobic/anaerobic and sterile/non-sterile conditions to measure biological degradation in soil. Mass balances, qualitative assessment of hormone fate, and separation of hormone compartments into the various soil fractions under these conditions will be determined. Objective 3: Well-defined field-scale Discovery Farms will be used to measure the transport of hormones when injected into soil and followed by uncontrolled and controlled drainage (rainfall). Both well water and soil extracts will be analyzed for hormone content across two growing seasons. Animal manures have been hypothesized to be important sources of environmental estrogens, considered by some to be endocrine disrupting compounds. An ultrafiltration method was therefore developed that allowed the separation of freely soluble estrogens in water and estrogens bound to sludge. Free and bound estrogens were evaluated for their ability to interact with the estrogen receptor. We found that although the majority of estradiol in a soil:water mixture is rapidly partitioned into soil, a significant portion of the estradiol is associated with soil colloids. Association of estrogens with colloids provides a mechanism to explain the long-range transport of estradiol in soils. Furthermore, we learned that estradiol:colloid particles were capable of interacting with the estrogen receptor and eliciting a biological response. These data suggest a mechanism of how estradiol can be transported from manures to soil and surface waters. ADODR monitoring activities include meetings, phone calls, e-mails, conference calls, and site visits.

    Impacts
    (N/A)

    Publications


      Progress 10/01/10 to 09/30/11

      Outputs
      Progress Report Objectives (from AD-416) All animals produce natural hormones in the healthy function and regulation of their endocrine system. When a hormone is eliminated from the body and gets into the environment, it can act upon other animals as an endocrine disrupting compound by binding to and activating receptors within hormone-responsive organs. In sensitive organisms this can occur at the parts per trillion level, and risks include sex reversals and cancer. The potential for livestock farms to serve as sources of hormones to the environment has been recognized for many years. To guide the objectives of this proposal, the following research questions (RQ) were formulated to evaluate the respective testable hypotheses (TH): RQ 1) Does dissolved organic carbon and particulates from lagoon waste or soil enhance the mobility of estrogens in mineral soil and thus increase the potential for off-site movement? TH 1) If the movement of estrogens is related to the presence of lagoon- or soil-derived dissolved organic carbon and particulates, then estrogen in the presence of high amounts of soil/lagoon dissolved organic carbon will increase their mobility compared to aqueous free estrogens. RQ 2) Does dissolved organic carbon and particulates of lagoon waste or soil offer estrogenic hormones protection from microbial degradation and increase their longevities in the soil or manure storage facilities? TH 2) If estrogenic hormones are bound to dissolved organic carbon or particulates and not easily accessible to microbial processes, then hormone in the presence of high amounts of dissolved organic carbon or particulates will increase persistence in the environment compared to free aqueous hormone. RQ 3) Do estrogen conjugates (i.e. polar metabolites) promote the mobility or persistence of estrogens in soil? TH 3) If conjugated hormones are more water soluble than their de- conjugated forms, then they are also more mobile in the soil and can potentially migrate to areas of reduced microbial degradation. RQ 4) Do estrogens and their conjugates from lagoon waste applied to fields move into groundwater and into surface waters? TH 4) If the mobility of estrogens in soil is dependant on hormone conjugation, the presence of dissolved organic carbon or particulates, and the low retention time in upper soil layers, then application of manures on tile drainage fields will increase the presence of hormone/hormone conjugates in ground and surface waters. To answer these research questions and test the hypotheses, the following experimental objectives were formed: Objective 1 � Determine the sorption characteristics of estradiol, estradiol glucuronide and sulfate conjugates with particulates originating from natural organic matter from soil and from animal manure lagoon liquors (laboratory); Objective 2 � Determine the degradation of the parent compounds estradiol, estradiol glucuronide and sulfate conjugates in the presence of these particulates and soil (laboratory); and Objective 3 � Determine how land application strategies (surface applied vs. injection) for lagoon liquor influence the fate and transport of estradiol in a field setting. Approach (from AD-416) Objective 1: Degradation of hormones is mediated primarily by biological activity and can lead to misinterpretation of observed physical/chemical soil absorption processes. In order to identify these processes experimentally, the experiments for this objective will be conducted under sterile conditions. Four hormone concentrations and nine time points will be used and sampled. Qualititative and quantitative assessment of hormone degradation and soil absorption will be made by chromatographic and spectrometric methods, and absorption curves and models can then be determined. Objective 2: High and low organic soils will be spiked with radioactive hormone conjugates with and without lagoon waste under aerobic/anaerobic and sterile/non-sterile conditions to measure biological degradation in soil. Mass balances, qualitative assessment of hormone fate, and separation of hormone compartments into the various soil fractions under these conditions will be determined. Objective 3: Well-defined field-scale Discovery Farms will be used to measure the transport of hormones when injected into soil and followed by uncontrolled and controlled drainage (rainfall). Both well water and soil extracts will be analyzed for hormone content across two growing seasons. Estrogens are potent agonists of the estrogen receptors, and when exposed exogenously can alter an organism�s normal hormone balance. This can lead to reproductive abnormalities, such as feminization of male organisms. A major source of estrogens into the environment is from animal waste, particularly in the microenvironment surrounding concentrated animal feeding operations. However, despite the consistent detection of hormones in the environment, our previous laboratory data suggested that estrogens should not be mobile in the environment, and that movement into groundwater must be governed by more than vertical transport in soil by rainfall. Therefore, mechanisms need to be discovered on how estrogens enter and persist in the environment. Last year we discovered two such mechanisms, and this year have continued investigations. 1. Flushed swine manure wastewaters are composed of two compartments, i. e. the dissolved aqueous compartment and the particulate compartment. The particulate compartment was discovered to be composed of a sedimentary (sludge) and suspended fraction (colloidal). This colloidal fraction has significant potential for long-range transport, but it is not known if the colloidal-bound estrogens are still biologically active. We developed a method to isolate the colloidal fraction by ultrafiltration, and to quantitate the bound estrogen by radiochemical means. An assay was then developed that could assess the biological activity. Only preliminary results on real-world samples have been generated, however, it is hoped that results of these assays will determine whether these mobile, estrogen-bound colloids are biologically active and/or environmentally stable. 2. Last year it was shown that water-soluble conjugates of estrogens have significant potential to be transported in runoff to contaminate surface and groundwater. This year our investigations demonstrated that the various water-soluble conjugates can be degraded in the environment, but at different rates and to different endpoints. The degradation of some estrogen conjugates yielded metabolites that were not biologically active compounds, while others were degraded back to biologically active parent estrogen. The observed results were fitted into a robust model so that predictions on estrogen fate and transport could be made based on soil type. These results are very significant in understanding the fate and transport behavior of manure-borne estrogens, and to devise manure management methods that reduce their environmental release.

      Impacts
      (N/A)

      Publications


        Progress 10/01/09 to 09/30/10

        Outputs
        Progress Report Objectives (from AD-416) All animals produce natural hormones in the healthy function and regulation of their endocrine system. When a hormone is eliminated from the body and gets into the environment, it can act upon other animals as an endocrine disrupting compound by binding to and activating receptors within hormone-responsive organs. In sensitive organisms this can occur at the parts per trillion level, and risks include sex reversals and cancer. The potential for livestock farms to serve as sources of hormones to the environment has been recognized for many years. To guide the objectives of this proposal, the following research questions (RQ) were formulated to evaluate the respective testable hypotheses (TH): RQ 1) Does dissolved organic carbon and particulates from lagoon waste or soil enhance the mobility of estrogens in mineral soil and thus increase the potential for off-site movement? TH 1) If the movement of estrogens is related to the presence of lagoon- or soil-derived dissolved organic carbon and particulates, then estrogen in the presence of high amounts of soil/lagoon dissolved organic carbon will increase their mobility compared to aqueous free estrogens. RQ 2) Does dissolved organic carbon and particulates of lagoon waste or soil offer estrogenic hormones protection from microbial degradation and increase their longevities in the soil or manure storage facilities? TH 2) If estrogenic hormones are bound to dissolved organic carbon or particulates and not easily accessible to microbial processes, then hormone in the presence of high amounts of dissolved organic carbon or particulates will increase persistence in the environment compared to free aqueous hormone. RQ 3) Do estrogen conjugates (i.e. polar metabolites) promote the mobility or persistence of estrogens in soil? TH 3) If conjugated hormones are more water soluble than their de- conjugated forms, then they are also more mobile in the soil and can potentially migrate to areas of reduced microbial degradation. RQ 4) Do estrogens and their conjugates from lagoon waste applied to fields move into groundwater and into surface waters? TH 4) If the mobility of estrogens in soil is dependant on hormone conjugation, the presence of dissolved organic carbon or particulates, and the low retention time in upper soil layers, then application of manures on tile drainage fields will increase the presence of hormone/hormone conjugates in ground and surface waters. To answer these research questions and test the hypotheses, the following experimental objectives were formed: Objective 1 � Determine the sorption characteristics of estradiol, estradiol glucuronide and sulfate conjugates with particulates originating from natural organic matter from soil and from animal manure lagoon liquors (laboratory); Objective 2 � Determine the degradation of the parent compounds estradiol, estradiol glucuronide and sulfate conjugates in the presence of these particulates and soil (laboratory); and Objective 3 � Determine how land application strategies (surface applied vs. injection) for lagoon liquor influence the fate and transport of estradiol in a field setting. Approach (from AD-416) Objective 1: Degradation of hormones is mediated primarily by biological activity and can lead to misinterpretation of observed physical/chemical soil absorption processes. In order to identify these processes experimentally, the experiments for this objective will be conducted under sterile conditions. Four hormone concentrations and nine time points will be used and sampled. Qualititative and quantitative assessment of hormone degradation and soil absorption will be made by chromatographic and spectrometric methods, and absorption curves and models can then be determined. Objective 2: High and low organic soils will be spiked with radioactive hormone conjugates with and without lagoon waste under aerobic/anaerobic and sterile/non-sterile conditions to measure biological degradation in soil. Mass balances, qualitative assessment of hormone fate, and separation of hormone compartments into the various soil fractions under these conditions will be determined. Objective 3: Well-defined field-scale Discovery Farms will be used to measure the transport of hormones when injected into soil and followed by uncontrolled and controlled drainage (rainfall). Both well water and soil extracts will be analyzed for hormone content across two growing seasons. Steroid hormones are potent agonists of estrogen and androgen receptors, and when exposed exogenously can alter an organism�s normal hormone balance. This can lead to reproductive abnormalities, such as feminization of male organisms or vice versa. A major source of the introduction of steroid hormones into the environment is from animal waste, especially from concentrated animal feeding operations. Despite the constant detection of hormones in the environment, our previous laboratory data suggested that these hormones should not be mobile in the environment, and that movement into groundwater must be governed by more than simple rainfall transport from upper soil layers to lower. Therefore, mechanisms need to be discerned as to how hormones enter and persist in the environment. We have discovered two mechanisms that may help to explain hormone transport. 1. Flushed swine manure wastewaters are composed of two compartments, i. e. the dissolved aqueous compartment and the particulate compartment. We developed a method to quantify the particulate compartment based on selective filtration. We then conducted studies with radiolabeled estradiol (the principle female steroid hormone) spiked into flushed swine manure wastewater to measure the amount of the hormone in each of the two compartments. The amount present in the particulate-bound (colloidal) compartment was considered environmentally mobile. Upwards of 20% of the applied estradiol dose was associated with colloid particles. Results have provided a putative mechanism of for the introduction of this endocrine disruptor into the environment. A question to be addressed in the future is whether these mobile, estradiol-ladened colloid particles ever release the estradiol, or if the estradiol-colloid complex is biologically active. 2. Since steroid hormones are excreted to a large extent as water- soluble conjugates of sugar and acid molecules, this has been hypothesized as the means by which these hormones move in the environment. We also conducted laboratory soil/water batch studies to determine contribution of conjugates in the transport of steroid hormones. Preliminary data showed that a window exists for estradiol sulfate, an endogenous urinary metabolite of estradiol, to move through the environment before soil bacteria degrade it. However, degradation did not result in release of parent compound over the 2 week length of the study. Results indicate that whereas parent compound is poorly transported in soil/water systems, a mechanism of conjugate transport has been discovered which may explain the long-range transport of these endocrine disrupting compounds in the environment, although, under the conditions studied, does not explain how the potent parent compound itself is frequently detected in the environment. These results are very significant to understand the fate and transport behavior of these compounds, and provide the basis needed to devise means to reduce their environmental release.

        Impacts
        (N/A)

        Publications