scholarly journals Pharmaceuticals and personal care products (PPCPs) and their sublethal and lethal effects in aquatic organisms

2020 ◽  
Author(s):  
Harveer S. Srain ◽  
Karen F Beazley ◽  
Tony R. Walker

Pharmaceutical and personal care products (PPCPs) include over-the-counter and prescription drugs, veterinary drugs, fragrances, and cosmetics. PPCPs have been detected in aquatic environments at low concentrations and are emerging as contaminants of concern. PPCPs are primarily released into aquatic environments via untreated sewage, wastewater treatment plants, landfill leachate and can affect aquatic life through persistence, bioaccumulation, and toxicity. However, there are limited reviews of lethal and sublethal effects of PPCP exposures on aquatic organisms. To understand PPCP toxicity on aquatic organisms, a literature review was conducted which identified aquatic organisms known to be affected by PPCPs; concentrations of PPCPs reported as producing sublethal and lethal effects in aquatic organisms; and research gaps on PPCP aquatic toxicity. Twelve PPCPs were selected from three seminal studies for review, including bisphenol A, carbamazepine, erythromycin, fluoxetine, linear alkylbenzene sulfonate, metoprolol, naproxen, nonylphenol, ofloxacin, sertraline, sulfamethoxazole, and triclosan. Many aquatic species were affected by PPCPs at sublethal and lethal exposures, including sublethal effects at environmentally relevant concentrations. Because lethal effects were seldom observed at environmentally relevant concentrations, many studies considered PPCPs non-toxic. Few studies have compared effects of PPCPs on the same organisms for identical exposure parameters (time and concentration), resulting in wide variation in reported toxicity levels with limited consensus in the academic literature. Consensus in lethal concentrations was reported for Daphnia magna with 48 h exposure for bisphenol A and triclosan and Vibrio fischeri with 15 min exposure to carbamazepine. Environmentally relevant sublethal concentrations were higher than water quality guidelines developed for Canada and predicted no-effect concentrations derived globally. Species sensitivity distributions for some PPCPs show that aquatic species are affected lethally at environmentally relevant concentrations. More studies on indirect, and long-term ecological effects along with testing chronic toxicity of PPCPs at environmentally relevant concentrations, is recommended. These will help guide future research to determine extent and magnitude of PPCP concentrations in aquatic environments and help inform management decisions to reduce sources of PPCPs into the environment. Future management requires effective monitoring strategies regarding use, disposal, occurrence, and impacts at different life cycle stages of PPCPs in the environment.

2016 ◽  
Vol 6 (1) ◽  
pp. 43-56 ◽  
Author(s):  
Zdena Křesinová ◽  
Klára Petrů ◽  
Ondřej Lhotský ◽  
Torgeir Rodsand ◽  
Tomáš Cajthaml

2021 ◽  
Author(s):  
Yizhou Tu ◽  
Huimin Wang ◽  
Pingping Yang ◽  
Guizhou Xu ◽  
Xuejiao Hu ◽  
...  

Pharmaceuticals and personal care products (PPCPs) are widely distributed in aquatic environments due to their large consumption and low biodegradability, causing ecological risks. In this study, porous thienyl cyclodextrin polymer...


2019 ◽  
Vol 5 (2) ◽  
pp. 209-223 ◽  
Author(s):  
Feijian Mao ◽  
Yiliang He ◽  
Karina Yew-Hoong Gin

Benzophenone-type ultraviolet filters (BP-type UV filters or BPs) are extensively used in a diverse array of personal care products (PCPs), including sunscreens and many cosmetics.


2018 ◽  
Vol 43 (1SI) ◽  
pp. 22 ◽  
Author(s):  
Fernando Fabriz Sodré ◽  
Priscila Mendonça Dutra ◽  
Viviane Portela Dos Santos

The present work intended to present a preliminary snapshot on the contamination of Brazilian surface waters by pharmaceuticals and personal care products. Data were collected elsewhere for Measured Environmental Concentrations (MEC) in surface waters and Predicted No-Effect Concentration (PNEC). Prioritization was based on risk assessment, where MEC/PNEC ratios higher than 1.0 indicate a positive risk, values below 0.1 indicate absence of risk and intermediate values, potential risk. Results revealed that hormones, antibiotics drugs and triclosan should be prioritized to subsidize the generation of water quality standards to protect aquatic life.


2021 ◽  
Vol 17 (40) ◽  
pp. 297
Author(s):  
Kouakou Kouamé ◽  
Etchian Assoi Olivier ◽  
Seka Yapoga Jean ◽  
Yapo Ossey Bernard

L’objet de cette étude est d’évaluer les risques environnementaux liés aux polluants émergents (parabènes, triclosan et triclocarban) par le calcul de l’indice de risque afin de prévenir des dangers liés à la contamination de certaines espèces aquatiques. En effet, les polluants émergents originaires des produits pharmaceutiques et des produits de soins personnels représentent un danger pour l’environnement. Le calcul de l’indice de risque des espèces aquatiques (bactéries, protozoaires, algues, crustacés, oursins, mollusques, poissons) exposées aux polluants émergents (parabènes, triclosan et triclocarban) a montré que celui-ci est proche de la valeur limite (1) dans certaines baies lagunaires Ebrié. Les baies d’Azito et de Banco, présentent des risques pour certaines espèces aquatiques. L’indice de risque obtenu par le quotient de concentration du polluant dans le milieu (PEC) et la concentration la plus faible pour laquelle on ne prévoit aucun effet sur l’environnement (PNEC), montre le risque du triclosan dans les algues au niveau de la baie d’Azito (IR= 1,71). Dans les baies d’Azito et du Banco, les algues, les crustacés, les oursins et les mollusques exposés au triclocarban sont montrés dangereux (IR> 1). L’exposition des espèces aquatiques aux polluants émergents (triclosan et triclocarban) est plus élevée dans la baie du Banco (1,71 à 29,5) que dans la baie d’Azito (1,01 à 6,93). Les espèces aquatiques telles que les algues, les oursins et les mollusques se sont montrées vulnérables au triclosan. The purpose of this study is to evaluate the environmental risks related to emerging pollutants (parabens, triclosan and triclocarban) by calculating the risk index in order to prevent the dangers related to the contamination of certain aquatic species. Indeed, the emerging pollutants originating from pharmaceutical products and personal care products represent a danger for the environment. The calculation of the risk index of aquatic species (bacteria, protozoa, algae, crustaceans, sea urchins, mollusks, fish) exposed to emerging pollutants (parabens, triclosan and triclocarban) has shown that it is close to the limit value (1) in some Ebrié lagoon bays The bays of Azito and Banco, present risks for some aquatic species. The risk index obtained by the quotient of the concentration of the pollutant in the environment (PEC) and the lowest concentration for which no effect on the environment is expected (PNEC), shows the risk of triclosan in algae in Azito bay (IR= 1.71). In Azito and Banco bays, algae, crustaceans, sea urchins and mollusks exposed to triclocarban are shown to be hazardous (IR> 1). Exposure of aquatic species to the emerging pollutants (triclosan and triclocarban) is higher in Banco Bay (1.71 to 29.5) than in Azito Bay (1.01 to 6.93). Aquatic species such as algae, sea urchins,and mollusks were found to be vulnerable to triclosan.


2021 ◽  
Vol 1 (01) ◽  
pp. 1-2
Author(s):  
MOHAMMED ABU-DIEYEH

Currently, the world environment is changing more rapidly than at any other time. These changes have immense effects on aquatic life forms, from microscopic plankton to large fish (1). Some of the relevant stressors, amongst many, are temperature, salinity, and water pH, all of which are variables that directly impact living organisms present in the concerned aquatic environments (2). Scientists have found a correlation with physiological, morphological, and molecular changes in living organisms due to environmental fluctuations. In any aquatic ecosystem, photosynthetic primary producers are the basis of other life forms, and it is now established that environmental change has many detrimental effects on these primary producers; thus aquatic ecosystems. For example, increasing temperatures can reduce the productivity, cell size, and overall growth of many aquatic organisms, also a significant cause for coral bleaching (3,4).


BMC Chemistry ◽  
2020 ◽  
Vol 14 (1) ◽  
Author(s):  
Adewumi Olufemi Oluwole ◽  
Elizabeth Oyinkansola Omotola ◽  
Olatunde Stephen Olatunji

Abstract The presence of emerging contaminants such as pharmaceutical and personal care products in many aqueous matrices have been reported. One of such matrix is streams of wastewater, including wastewater treatment plants inflows and outflows and wastewater flow by-passing wastewater treatment plants. Their persistence arises from their resistant to breakdown, hence they may remain in the environment over long time, with a potential to cause adverse effects including endocrine disruption, gene toxicity, the imposition of sex organs, antibiotic resistance and many others in some aquatic organisms exposed to arrays of residues of pharmaceutical and personal care products. Among the treatment techniques, advanced oxidation processes have been reported to be a better technique through which these PPCPs can be degraded in the WWTPs. Heterogeneous photocatalysis using various photocatalyst immobilized on solid support such as activated carbon, graphene and carbon nanotubes in AOPs have been shown to be a viable and efficient method of PPCPs degradation. This is because, the performance of most WWTPs is limited since they were not designed to degrade toxic and recalcitrant PPCPs. This review highlight the occurrence, concentration of PPCPs in wastewater and the removal efficiency of heterogeneous photocatalysis of TiO2 immobilized on solid supports.


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