
Citation: Djordje Vilimanovic, Gangadhar Andaluri, Robert Hannah, Rominder Suri, A. Ronald MacGillivray. Occurrence and aquatic toxicity of contaminants of emerging concern (CECs) in tributaries of an urbanized section of the Delaware River Watershed[J]. AIMS Environmental Science, 2020, 7(4): 302-319. doi: 10.3934/environsci.2020019
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Severe accidents of pressurized water reactors of nuclear power plants (NPPs) are accompanied by melting of the core and the formation of corium-a melt of a radioactive mixture of uranium oxide, zirconium, steel, products of the interaction of metals with an oxidizing environment, and other structural elements. The release of corium, under certain conditions, outside the reactor facility is considered as a possible scenario due to the large amount of stored energy and the presence of decay heat [1].
Currently, there are two options for localizing the core melt inside the containment during a severe accident at a NPP with light water reactors under pressure: in-vessel and out-of-vessel containment of the melt [2]. At the same time, the most acceptable method at the moment for managing the final stage of a severe accident with a core meltdown at NPPs with high-power reactors (over 1000 MW) is the concept of containing and cooling the corium outside the reactor vessel. This concept consists of installing a melt localization device (melt trap) in the sub-reactor space [3].
During its development, the concept of melt traps had moved from a simple pool filled with water to complex structures that combine many unique engineering solutions [4,5,6,7,8]. Currently, melt traps are known for light water reactors: evolutionary power reactor (EPR) [9], European Union advanced boiling water reactor (EU-ABWR) [10], economic simplified boiling water reactor (ESBWR) [11], European Union advanced power reactor (EU-APR) [12], water–water energetic reactor (WWER) [13], etc. One of the most technically feasible and often used melt traps is the crucible-type melt trap of the WWER reactor.
A crucible-type melt trap is a steel housing that forms a vessel in which a bath of corium melt coming from the core is formed. Cooling of the melt pool formed in the trap occurs by heat removal to the cooling water through the shell of the steel housing, as well as by water supplied directly to the surface of the melt after completion of gravitational inversion of the corium layers.
The main element of the gravitational inversion concept is sacrificial materials. The role of sacrificial materials is to dilute the heat-generating oxide part of the corium in order to create thermodynamic conditions for gravitational inversion of parts of the corium and reduce the high temperature [14].
Based on a set of experiments to justify the use of the first such trap at the Tianwan NPP, the use of ceramic materials as sacrificial materials was recommended. Experiments confirmed the eutectic nature of the phase diagrams formed by a multicomponent core melt with Al2O3 and Fe2O3. It was shown that the mutual dissolution of the sacrificial material and the melt occurs at a rate sufficient to implement the inversion of the oxide and metal layers in less than 1 hour. As a result, an oxide ceramic sacrificial material was synthesized, consisting of 67 wt.% Fe2O3 and 30 wt.% Al2O3 [15].
However, in the process of further research it was found that the selected materials have disadvantages, among which the following can be identified [16,17]:
- Heat removal from the corium by the bulk of sacrificial materials is not fully justified due to the low thermal conductivity of sacrificial materials (λ = 0.5 W/m·K);
- Release of oxygen during the decomposition of Fe2O3 will create a barrier gas-liquid layer that prevents heat and mass transfer.
Thus, the search for new sacrificial materials for melt traps is an urgent task. As an example, it is possible to note the latest experiments on the study of candidate oxide and concrete sacrificial materials [18,19].
To improve the efficiency of using sacrificial materials and eliminate the above-described disadvantages, it was decided to apply the previously conducted studies on the selection of material for a core catcher similar to the Tianwan NPP. Thus, in the original version, steel was considered as a sacrificial material, but the calculations and experimental studies performed showed that if only metal is used as a sacrificial material, then the thermal loads to the side cooling surfaces in the area where the oxide melt bath is located may exceed permissible values due to the limited depth and high-volume energy release densities [20]. Ultimately, experts concluded that the use of metal as SM is promising only in combination with an oxide sacrificial material.
Previously, in [21], to eliminate the above disadvantages, the authors proposed to consider a ceramic material made of aluminum oxide (Al2O3) with a lead layer (fluidized bed) as a sacrificial material. Computer simulation in the Ansys program showed that, due to the heat transfer from the corium to lead phase transitions, the growth rate of the average temperature of the corium decreases due to decay heat. At the same time, the interaction between lead and the sacrificial material leads to an increase in the intensity of heat exchange processes compared to the interaction between corium and the sacrificial material. This fact can lead to accelerated destruction of the sacrificial material and its further dissolution in the corium for the successful completion of gravitational inversion.
However, the disadvantage of the computer simulation is that it only takes into account the thermophysical interaction between the elements of the trap. Thus, the purpose of this study, in order to understand all aspects of such interaction, is to conduct physical simulation of the interaction between corium and ceramic material made of aluminum oxide and a lead layer under conditions of simulating decay heat in corium.
Experiments on the interaction between corium and sacrificial material were conducted in the Lava-B test-bench [22,23,24,25]. Figure 1 shows the physical form and layout of the Lava-B facility. The experimental facility includes two main functional blocks: an electric melting furnace (EMF) for preparing the corium and a melt receiver (MR), which houses an experimental section for modeling the studied processes.
Before the start of the experiment to obtain corium, an electric melting furnace (EMF) crucible with a total mass of 25.5 kg was loaded with the following composition: UO2: 16.5 kg; Zr: 7.5 kg; ZrO2: 1.5 kg [26]. To add a steel component to the corium and eliminate the negative effect of carbon on its composition, a steel element (brand 12Х18Н10Т: Х—chromium, Н—niccolum, Т—titanium) with a developed interaction surface weighing 4.5 kg was installed in the concrete trap. Disks and cylinders made of aluminum oxide (A12O3, purity 99 %) were installed in the internal cavity of the concrete trap. A general view of the core catcher with the studied samples is shown in Figure 2.
Figure 3 shows a diagram of the arrangement of thermocouples (tungsten–rhenium type with measurement error of 0–7%) in the core catcher with the dimensions of the concrete trap, blocks and cylinders made of A12O3, and a lead liner (dimensions in the figure are in mm.). The routing of the compensation wires of the thermocouples of the concrete trap from the platform to the MR cover is made inside pipes made of corrosion-resistant steel.
Next, the corium components were heated in an EMF crucible until a liquid state. The amount of integrated energy supplied to the EMF crucible was 367.4 MJ after 6960 s while the melt temperature, according to the infrared pyrometer readings, was about 2514 ℃. Then, the voltage on the EMF inductor was reduced to 0 V and the crucible plug was chipped in order to move the corium into the core catcher.
After the melt was drained into the trap, voltage was applied to the MR inductor to simulate the decay heat in the corium. The method for selecting the parameters of the induction system in the MR and the results of previously conducted calibration experiments are described in detail in [27].
The interaction between corium and studied materials with the simultaneous input of extra energy into the melt lasted for 2700 s. The experiment was stopped when most of the controlling thermocouples failed. After turning off the power, the experimental device was cooled due to heat leakage into the MR elements of the Lava-B bench.
The temperature of the experimental device (ED) during the experiment is shown in Figures 4 and 5. Figure 4 evidences that after the corium is moved into the trap, its active interaction with the sacrificial material begins, which is expressed by an increase in the temperature of the aluminum oxide blocks. At the same time, taking into account the reading of thermocouple T4, which is commensurate with the value of the melting point of aluminum oxide, it can be assumed that in the area where this thermocouple is located, melting of aluminum oxide occurred in the process of interaction with corium. Thermocouple T4 is located at the junction of areas with and without a lead layer. In the course of further research, the maximum erosion of aluminum oxide ceramics will occur and a sample for materials science research will be selected from this area.
At the same time, according to the results of the experiment, the readings of thermocouples installed in ceramic disks, not closed (thermocouple T13, Figure 5) and closed with the lead layer (thermocouple T11, Figure 5), differ significantly after the start of boiling and evaporation of lead. The rate of increase in temperature of the ceramic disk under the lead layer is lower. The boiling of the lead layer is also confirmed, as a later analysis showed, by the presence in the MR chamber and on the surface of the core catcher of particles of material with a diameter of 1–10 mm (Figure 6) after the experiment, visually identified as lead, presumably deposited during the condensation of metal vapors.
X-ray diffraction phase analysis was implemented to more accurately determine the composition of the material. Analysis of the diffraction pattern showed (Figure 7) that the main component of the phase composition is metallic lead. All the main intense peaks of the diffraction pattern correspond to this phase.
To obtain data on the interaction between corium and ceramic material (aluminum oxide), a diametrical section of the core catcher was made, which showed the presence of corium penetration beyond the original boundary of the side walls of the ceramic material to various depths (penetrating erosion). It was revealed that in the cross section of the trap, the depth of erosion of the side wall was maximum on the side containing lead, minimal on the side without a lead layer, and there was through erosion on the bottom disks and part of the concrete trap material in the entire section. For subsequent microstructural studies, it was necessary to obtain templates containing the pattern observed in the cross section. In this regard, it is supposed to make an additional diametrical cut in half of the trap and subsequent cutting of the plates.
From the quarters of the trap obtained after the additional cut, templates in the form of plane-parallel plates were cut along the entire height of the trap. Cutting a plate about 30 mm thick from a quarter of a trap containing lead was not successful, since during the cutting process the plate broke up into many fragments. From the part of the trap that did not contain lead, a more massive sample with a thickness of about 50 mm was cut out, located at the junction of both zones (without a layer of lead and with lead). By increasing the thickness of the template, it was possible to maintain its overall integrity. The cut plate contains a representative cross-sectional area of the trap with maximum sidewall erosion and metal accumulation detected (Figure 8).
As can be seen, on the cut-out plate there are areas of through erosion of the internal insert, local penetration of the melt into the gap between the internal and external liners, and partial local erosion of the material of the external ceramic liner.
The choice of area for studying changes in structure was determined by searching for a fragment containing all the characteristic signs of erosion of ceramic material, i.e., the presence of an area of erosion, the presence of changes in structure, and cracks in ceramic liners. For further materials science research, the workpiece was cut into three plates about 15 mm thick. The plate cutting diagram and sample markings are shown in Figure 9.
For materials science research, a thin section was made, including the area of maximum erosion of the ceramic material (Figure 10). The prepared section contains a close-to-diametrical cut of materials in the area of contact between the corium and the ceramic material.
Along with the obvious erosion boundary characterized by a sharp transition from the structure of the corium melt to the structure of the ceramic material, the area of influence of the melt on the ceramic material is also the area of visible preserved structure of the aluminum oxide material at different distances from the boundary with the melt. Indicators property degradation (mediated, secondary and indirect erosion) are signs of changes in the structure of a ceramic material, determined by optical macroanalysis, microstructural studies, and studies of strength properties.
The prepared section (see Figure 10a) contains an area of erosion of the ceramic material, areas of darkening of the structure (8), microcracks (5), macrocracks (6), and areas of corium penetration into the gap between the liners and into the macrocrack (3) in the ceramic material formed during the experiment. The structure of the corium and ceramic material also contains macrocracks (9), which were formed either during the processes of dismantling the trap and cutting out the workpieces or during the cooling of the assembly in the post-experimental period, at least after the melt solidified. A layer of solidified corium melt with a thickness of about 1 cm near the contact boundary with the ceramic material has a dense homogeneous structure (10), different from the structure of corium in the rest of the section (11), which is characterized by porosity and the presence of round metal inclusions.
In this study, we conducted an experiment to study the interaction of a candidate SM with corium under conditions as close as possible to the real processes of a severe light water reactor accident, i.e., using an aluminum oxide SM with a lead layer in the melt trap.
The experiment showed that during the interaction between corium with SM, melting and subsequent boiling of the lead component took place. These processes are confirmed by thermocouple readings and the presence of lead in the MR chamber and on the surface of the trap. In this case, when the boiling point of lead is reached, the rate of increase in the temperature of the ceramic material slows down over a certain time interval. This is most likely caused by phase transitions in the lead layer.
It was also found that the presence of lead increases the intensity of erosion of the oxide component of SM. Thus, the depth of side wall erosion turned out to be maximum on the side containing lead and minimal on the side without lead.
As a result of the destruction of the oxide part structure of the SM, its active introduction into the composition of the corium occurred. It was noticed that the layer of solidified corium melt near the contact boundary with the ceramic material had a dense homogeneous structure, different from the structure of the corium in the rest of the section, which was characterized by porosity and presence of round metal inclusions.
Thus, the experiment showed the perspective of the proposed combination of sacrificial materials for the melt trap. During future materials research, the processes of interaction between corium and the proposed SM will be studied in detail and conclusions will be drawn about the possibility of its use in melt traps of a light water reactor.
The authors declare they have not used Artificial Intelligence (AI) tools in the creation of this article.
This research was funded by the Ministry of Energy of the Republic of Kazakhstan (BR09158470).
The authors declare no conflict of interest.
[1] |
Fent K, Weston AA, Caminada D (2006) Ecotoxicology of human pharmaceuticals. Aquat Toxicol 76: 122-159. doi: 10.1016/j.aquatox.2005.09.009
![]() |
[2] |
Barceló D, Petrovic M (2007) Pharmaceuticals and personal care products (PPCPs) in the environment. Anal Bioanal Chem 387: 1141-1142. doi: 10.1007/s00216-006-1012-2
![]() |
[3] |
Kim JW, Jang HS, Kim JG, et al. (2009) Occurrence of Pharmaceutical and Personal Care Products (PPCPs) in Surface Water from Mankyung River, South Korea. J Heal Sci 55: 249-258. doi: 10.1248/jhs.55.249
![]() |
[4] |
Vidal-Dorsch DE, Bay SM, Maruya K, et al. (2012) Contaminants of emerging concern in municipal wastewater effluents and marine receiving water. Environ Toxicol Chem 31: 2674-2682. doi: 10.1002/etc.2004
![]() |
[5] |
Pal A, Gin KYH, Lin AYC, et al. (2010) Impacts of emerging organic contaminants on freshwater resources: Review of recent occurrences, sources, fate and effects. Sci Total Environ 408: 6062-6069. doi: 10.1016/j.scitotenv.2010.09.026
![]() |
[6] |
Blair BD, Crago JP, Hedman CJ, et al. (2013) Pharmaceuticals and personal care products found in the Great Lakes above concentrations of environmental concern. Chemosphere 93: 2116-2123. doi: 10.1016/j.chemosphere.2013.07.057
![]() |
[7] |
Fairbairn DJ, Karpuzcu ME, Arnold WA, et al. (2015) Sediment-water distribution of contaminants of emerging concern in a mixed use watershed. Sci Total Environ 505: 896-904. doi: 10.1016/j.scitotenv.2014.10.046
![]() |
[8] |
Paíga P, Santos LHMLM, Ramos S, et al. (2016) Presence of pharmaceuticals in the Lis river (Portugal): Sources, fate and seasonal variation. Sci Total Environ 573: 164-177. doi: 10.1016/j.scitotenv.2016.08.089
![]() |
[9] |
Andaluri G, Suri RPS, Graham K (2017) Steroid hormones in environmental matrices: extraction method comparison. Environ Monit Assess 189: 626. doi: 10.1007/s10661-017-6345-0
![]() |
[10] |
Andaluri G, Suri RPS, Kumar K (2012) Occurrence of estrogen hormones in biosolids, animal manure and mushroom compost. Environ Monit Assess 184: 1197-1205. doi: 10.1007/s10661-011-2032-8
![]() |
[11] |
Bean TG, Rattner BA, Lazarus RS, et al. (2018) Pharmaceuticals in water, fish and osprey nestlings in Delaware River and Bay. Environ Pollut 232: 533-545. doi: 10.1016/j.envpol.2017.09.083
![]() |
[12] |
Jones OAH, Voulvoulis N, Lester JN (2002) Aquatic environmental assessment of the top 25 English prescription pharmaceuticals. Water Res 36: 5013-5022. doi: 10.1016/S0043-1354(02)00227-0
![]() |
[13] | Carlsson C, Johansson AK, Alvan G, et al. (2006) Are pharmaceuticals potent environmental pollutants?. Part I: Environmental risk assessments of selected active pharmaceutical ingredients. Sci Total Environ 364: 67-87. |
[14] |
Sui Q, Huang J, Deng S, et al. (2010) Occurrence and removal of pharmaceuticals, caffeine and DEET in wastewater treatment plants of Beijing, China. Water Res 44: 417-426. doi: 10.1016/j.watres.2009.07.010
![]() |
[15] |
Hansen M, Krogh KA, Björklund E, et al. (2009) Environmental risk assessment of ionophores. TrAC - Trends Anal Chem 28: 534-542. doi: 10.1016/j.trac.2009.02.015
![]() |
[16] | EEA (2014) Chapter 6: Ecological Risk Assessment. Eur Environ Agency 4-7. |
[17] |
Higgins CP, Paesani ZJ, Chalew TEA, et al. (2009) Pharmaceuticals and Personal Care Products in the Environment BIOACCUMULATION OF TRICLOCARBAN IN LUMBRICULUS VARIEGATUS. Environ Toxicol 28: 2663-2670. doi: 10.1897/08-485.1
![]() |
[18] | DRBC (2019) State of the Basin. |
[19] | MacGillivray AR (2013) Contaminants of Emerging Concern In the Tidal Delaware River. |
[20] | USEPA (2007) Method 1694: Pharmaceuticals and Personal Care Products in Water, Soil, Sediment, and Biosolids by HPLC / MS / MS. |
[21] | CENSUS UBO (2010) U.S. Census Bureau, US Census Bureau 2010 Census, 2010. Available from: http://www.census.gov/2010census/. |
[22] |
Scheurer M, Michel A, Brauch HJ, et al. (2012) Occurrence and fate of the antidiabetic drug metformin and its metabolite guanylurea in the environment and during drinking water treatment. Water Res 46: 4790-4802. doi: 10.1016/j.watres.2012.06.019
![]() |
[23] |
Kosma CI, Lambropoulou DA, Albanis TA (2015) Comprehensive study of the antidiabetic drug metformin and its transformation product guanylurea in Greek wastewaters. Water Res 70: 436-448. doi: 10.1016/j.watres.2014.12.010
![]() |
[24] |
Niemuth NJ, Jordan R, Crago J, et al. (2015) Metformin exposure at environmentally relevant concentrations causes potential endocrine disruption in adult male fish. Environ Toxicol Chem 34: 291-296. doi: 10.1002/etc.2793
![]() |
[25] |
Karpuzcu ME, Fairbairn D, Arnold WA, et al. (2014) Identifying sources of emerging organic contaminants in a mixed use watershed using principal components analysis. Environ Sci Process Impacts 16: 2390-2399. doi: 10.1039/C4EM00324A
![]() |
[26] |
Trautwein C, Kümmerer K (2011) Incomplete aerobic degradation of the antidiabetic drug Metformin and identification of the bacterial dead-end transformation product Guanylurea. Chemosphere 85: 765-773. doi: 10.1016/j.chemosphere.2011.06.057
![]() |
[27] | Tamura I, Kagota KI, Yasuda Y, et al. (2013) Ecotoxicity and screening level ecotoxicological risk assessment of five antimicrobial agents: Triclosan, triclocarban, resorcinol, phenoxyethanol and p-thymol. J Appl Toxicol 33: 1222-1229. |
[28] | WET Center (2016) WET Center Pharmaceutical PNEC list. |
[29] |
Ferrari B, Mons R, Vollat B, et al. (2004) Environmental Risk Assessment of Six Human Pharmaceuticals: Are the Current Environmental Risk Assessment Procedures Sufficient for the Protection of the Aquatic Environment? Environ Toxicol Chem 23: 1344. doi: 10.1897/03-246
![]() |
[30] | Ferrari G, Junghans M, Korkaric M, et al. (2019) Antibiotikaresistenzbildung in der Umwelt. Herleitung von UQK für Antibiotika unter Berücksichtigung von Resistenzbildung. Aqua Gas 52-59. |
[31] |
Isidori M, Parrella A, Pistillo P, et al. (2009) Effects of ranitidine and its photoderivatives in the aquatic environment. Environ Int 35: 821-825. doi: 10.1016/j.envint.2008.12.002
![]() |
[32] |
Isidori M, Nardelli A, Pascarella L, et al. (2007) Toxic and genotoxic impact of fibrates and their photoproducts on non-target organisms. Environ Int 33: 635-641. doi: 10.1016/j.envint.2007.01.006
![]() |
[33] | US EPA (2014) Ecological Structure Activity Relationships (ECOSAR). |
[34] |
Deo RP (2014) Pharmaceuticals in the Surface Water of the USA: A Review. Curr Environ Heal reports 1: 113-122. doi: 10.1007/s40572-014-0015-y
![]() |
[35] |
Kim Y, Choi K, Jung J, et al. (2007) Aquatic toxicity of acetaminophen, carbamazepine, cimetidine, diltiazem and six major sulfonamides, and their potential ecological risks in Korea. Environ Int 33: 370-375. doi: 10.1016/j.envint.2006.11.017
![]() |
[36] |
Cunningham VL, Buzby M, Hutchinson T, et al. (2006) Effects of human pharmaceuticals on aquatic life: Next steps. Environ Sci Technol 40: 3456-3462. doi: 10.1021/es063017b
![]() |
[37] | ECHA (2008) Guidance on information requirements and chmical safety assessment. Chapter R.10: Characterisation of dose [concentration]-response for environment. Eur Chem Agency 1-65. |
[38] | Caldwell JC, Evans M V., Krishnan K (2012) Cutting edge PBPK models and analyses: Providing the basis for future modeling efforts and bridges to emerging toxicology paradigms. J Toxicol 2012: 1-10. |
[39] |
Heidler J, Sapkota A, Halden RU (2006) Partitioning, persistence, and accumulation in digested sludge of the topical antiseptic triclocarban during wastewater treatment. Environ Sci Technol 40: 3634-3639. doi: 10.1021/es052245n
![]() |
[40] |
Brausch JM, Rand GM (2011) A review of personal care products in the aquatic environment: Environmental concentrations and toxicity. Chemosphere 82: 1518-1532. doi: 10.1016/j.chemosphere.2010.11.018
![]() |
[41] |
DeLeo PC, Sedlak RI (2014) Comment on 'on the need and speed of regulating triclosan and triclocarban in the United States'. Environ Sci Technol 48: 11021-11022. doi: 10.1021/es503494j
![]() |
[42] | U.S. Food and Drug Administration (2016) Focus on Surfactants, FDA issues final rule on safety and effectiveness of antibacterial soaps, 2016. Available from: https://www.fda.gov/news-events/press-announcements/fda-issues-final-rule-safety-and-effectiveness-antibacterial-soaps. |
[43] | Halden RU (2020) Triclosan and Triclocarban: Exposures, Toxicity and Testing - Environmental Health Symposium, 2020. Available from: http://environmentalhealthsymposium.com/blog/2020/2/3/triclosan-and-triclocarbon-exposures-toxicity-and-testing. |
[44] |
Berninger JP, Du B, Connors KA, et al. (2011) Effects of the antihistamine diphenhydramine on selected aquatic organisms. Environ Toxicol Chem 30: 2065-2072. doi: 10.1002/etc.590
![]() |
[45] |
Ramirez AJ, Mottaleb MA, Brooks BW, et al. (2007) Analysis of pharmaceuticals in fish using liquid chromatography-tandem mass spectrometry. Anal Chem 79: 3155-3163. doi: 10.1021/ac062215i
![]() |
[46] |
Andreozzi R, Marotta R, Pinto G, et al. (2002) Carbamazepine in water: Persistence in the environment, ozonation treatment and preliminary assessment on algal toxicity. Water Res 36: 2869-2877. doi: 10.1016/S0043-1354(01)00500-0
![]() |
[47] |
Garber AJ, Duncan TG, Goodman AM, et al. (1997) Efficacy of metformin in type II diabetes: Results of a double-blind, placebo-controlled, dose-response trial. Am J Med 103: 491-497. doi: 10.1016/S0002-9343(97)00254-4
![]() |
[48] | Ecotox Centre Eawag-EPFL (2017) Proposals for Acute and Chronic Quality Standards | Oekotoxzentrum, 2017. Available from: http://www.ecotoxcentre.ch/expert-service/quality-standards/proposals-for-acute-and-chronic-quality-standards/. |
[49] |
Isidori M, Lavorgna M, Nardelli A, et al. (2005) Toxic and genotoxic evaluation of six antibiotics on non-target organisms. Sci Total Environ 346: 87-98. doi: 10.1016/j.scitotenv.2004.11.017
![]() |
[50] |
Danner MC, Robertson A, Behrends V, et al. (2019) Antibiotic pollution in surface fresh waters: Occurrence and effects. Sci Total Environ 664: 793-804. doi: 10.1016/j.scitotenv.2019.01.406
![]() |
[51] |
Luo Y, Guo W, Ngo HH, et al. (2014) A review on the occurrence of micropollutants in the aquatic environment and their fate and removal during wastewater treatment. Sci Total Environ 473-474: 619-641. doi: 10.1016/j.scitotenv.2013.12.065
![]() |
[52] |
Hirsch R, Ternes T, Haberer K, et al. (1999) Occurrence of antibiotics in the aquatic environment. Sci Total Environ 225: 109-118. doi: 10.1016/S0048-9697(98)00337-4
![]() |
[53] | US EPA (2004) Overview of the Ecological Risk Assessment Process in the Office of Pesticide Programs - Endangered and Threatened Species Effects Determinations. |
[54] | He W, Goodkind D, Kowal P (2016) An Aging World: 2015 International Population Reports. Aging (Albany NY) 165. |
[55] |
Nakashima M, Canda ER (2005) Positive dying and resiliency in later life: A qualitative study. J Aging Stud 19: 109-125. doi: 10.1016/j.jaging.2004.02.002
![]() |
[56] | OECD (2019) Pharmaceutical Residues in Freshwater - Hazards and Policy Responses |
[57] |
Christensen NS, Wood AW, Voisin N, et al. (2004) The effects of climate change on the hydrology and water resources of the Colorado River basin. Clim Change 62: 337-363. doi: 10.1023/B:CLIM.0000013684.13621.1f
![]() |
[58] | Pennsylvania Environmental Council (2020) Stormwater Resources for Philadelphia & Urban Centers, 2020. Available from: https://pecpa.org/stormwater-philadelphia-urban-centers/. |
[59] | Kricun A (2018) Using a Triple Bottom Line Approach To Reduce Combined Sewage Flooding and Provide Community Benefit in Camden City. |
[60] |
Jeffries KM, Brander SM, Britton MT, et al. (2015) Chronic exposures to low and high concentrations of ibuprofen elicit different gene response patterns in a euryhaline fish. Environ Sci Pollut Res 22: 17397-17413. doi: 10.1007/s11356-015-4227-y
![]() |
[61] | MedlinePlus (NIH) (2015) Diphenhydramine: MedlinePlus Drug Information, 2015. Available from: https://www.nlm.nih.gov/medlineplus/druginfo/meds/a682539.html. |
[62] | National Cancer Institute (2019) NCI Thesaurus, 2019. Available from: https://ncit.nci.nih.gov/ncitbrowser/ConceptReport.jsp?dictionary=NCI_Thesaurus&ns=ncit&code=C873. |
[63] | Cerner Multum I (2010) Thiabendazole Uses, Side Effects & Warnings - Drugs.com, 2010. Available from: https://www.drugs.com/mtm/thiabendazole.html. |
[64] |
Johnson AC, Keller V, Dumont E, et al. (2015) Assessing the concentrations and risks of toxicity from the antibiotics ciprofloxacin, sulfamethoxazole, trimethoprim and erythromycin in European rivers. Sci Total Environ 511: 747-755. doi: 10.1016/j.scitotenv.2014.12.055
![]() |
[65] |
Wright SW, Wrenn KD, Haynes ML (1999) Trimethoprim-sulfamethoxazole resistance among urinary coliform isolates. J Gen Intern Med 14: 606-609. doi: 10.1046/j.1525-1497.1999.10128.x
![]() |
[66] |
Heberer T (2002) Tracking persistent pharmaceutical residues from municipal sewage to drinking water. J Hydrol 266: 175-189. doi: 10.1016/S0022-1694(02)00165-8
![]() |
[67] | PWD (2011) Schuylkill | Philadelphia Water Department, 2011. Available from: http://www.phillywatersheds.org/your_watershed/schuylkill. |
[68] |
Sunger N, Teske SS, Nappier S, et al. (2012) Recreational use assessment of water-based activities, using time-lapse construction cameras. J Expo Sci Environ Epidemiol 22: 281-290. doi: 10.1038/jes.2012.4
![]() |
[69] |
Cunningham VL, Binks SP, Olson MJ (2009) Human health risk assessment from the presence of human pharmaceuticals in the aquatic environment. Regul Toxicol Pharmacol 53: 39-45. doi: 10.1016/j.yrtph.2008.10.006
![]() |
[70] |
Kostich MS, Lazorchak JM (2008) Risks to aquatic organisms posed by human pharmaceutical use. Sci Total Environ 389: 329-339. doi: 10.1016/j.scitotenv.2007.09.008
![]() |
[71] |
Kostich MS, Batt AL, Lazorchak JM (2014) Concentrations of prioritized pharmaceuticals in effluents from 50 large wastewater treatment plants in the US and implications for risk estimation. Environ Pollut 184: 354-359. doi: 10.1016/j.envpol.2013.09.013
![]() |
[72] |
Schwab BW, Hayes EP, Fiori JM, et al. (2005) Human pharmaceuticals in US surface waters: A human health risk assessment. Regul Toxicol Pharmacol 42: 296-312. doi: 10.1016/j.yrtph.2005.05.005
![]() |
[73] |
Collier AC (2007) Pharmaceutical contaminants in potable water: Potential concerns for pregnant women and children. Ecohealth 4: 164-171. doi: 10.1007/s10393-007-0105-5
![]() |
[74] |
Bruce GM, Pleus RC, Snyder SA (2010) Toxicological relevance of pharmaceuticals in drinking water. Environ Sci Technol 44: 5619-5626. doi: 10.1021/es1004895
![]() |
[75] |
Kumar A, Xagoraraki I (2010) Human health risk assessment of pharmaceuticals in water: An uncertainty analysis for meprobamate, carbamazepine, and phenytoin. Regul Toxicol Pharmacol 57: 146-156. doi: 10.1016/j.yrtph.2010.02.002
![]() |
[76] | Kumar A, Xagoraraki I (2010) Pharmaceuticals, personal care products and endocrine-disrupting chemicals in U.S. surface and finished drinking waters: A proposed ranking system. Sci Total Environ 408: 5972-5989. |
[77] |
Ottmar KJ, Colosi LM, Smith JA (2010) Development and application of a model to estimate wastewater treatment plant prescription pharmaceutical influent loadings and concentrations. Bull Environ Contam Toxicol 84: 507-512. doi: 10.1007/s00128-010-9990-3
![]() |
![]() |
![]() |
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