ABSTRACT
This study evaluated the toxicity and cellular stresses of ciprofloxacin (CIP) and its co-metabolic removal in a freshwater microalga Chlamydomonas mexicana. The toxicological effects of CIP on C. mexicana were assessed by studying the growth and biochemical characteristics of the microalga including total chlorophyll, carotenoid content, malondialdehyde (MDA) and superoxide dismutase (SOD) activity. The calculated effective concentration (EC50) of CIP on C. mexicana was 65±4mgL-1 at 96h. The growth of C. mexicana was significantly inhibited at increased concentrations of CIP, showing 36±1, 75±3. and 88±3% inhibition at 40, 60 and 100mgL-1 CIP, respectively, compared to the control after 11days of cultivation. The total chlorophyll, carotenoid, MDA and SOD activity were significantly increased as a result of relatively high concentrations of CIP stress. C. mexicana showed 13±1% removal of CIP (2mgL-1) after 11days of cultivation; however, the addition of an electron donor (sodium acetate, 4gL-1) highly enhanced the removal of CIP (2mgL-1) by>3-fold after 11days. Kinetic studies showed that removal of CIP followed a first-order model (R2 0.94-0.97) with the apparent rate constants (k) ranging from 0.0121 to 0.079 d-1.
Subject(s)
Chlamydomonas/metabolism , Chlorophyta/metabolism , Ciprofloxacin/toxicity , Fresh Water/chemistry , Sodium Acetate/metabolism , Water Pollutants, Chemical/toxicity , Biodegradation, Environmental , Chlamydomonas/drug effects , Ciprofloxacin/metabolism , Electron Transport , Kinetics , Water Pollutants, Chemical/metabolismABSTRACT
This study evaluated the toxicity and cellular stresses of carbamazepine (CBZ) on Chlamydomonas mexicana and Scenedesmus obliquus, and its biodegradation by both microalgal species. The growth of both microalgal species decreased with increase of CBZ concentration. The growth of S. obliquus was significantly inhibited (97%) at 200 mg CBZ L(-1), as compared to the control after 10days; whereas, C. mexicana showed 30% inhibition at the same experimental conditions. Biochemical characteristics including total chlorophyll, carotenoid contents and enzyme activities (SOD and CAT) for both species were affected by CBZ at relatively high concentration. C. mexicana and S. obliquus could achieve a maximum of 35% and 28% biodegradation of CBZ, respectively. Two metabolites (10,11-dihydro-10,11-expoxycarbamazepine and n-hydroxy-CBZ) were identified by UPLC-MS, as a result of CBZ biodegradation by C. mexicana. This study demonstrated that C. mexicana was more tolerant to CBZ and could be used for treatment of CBZ contaminated wastewater.
Subject(s)
Carbamazepine/metabolism , Chlamydomonas/metabolism , Microalgae/metabolism , Scenedesmus/metabolism , Water Pollutants, Chemical/metabolism , Biodegradation, Environmental , Carbamazepine/pharmacokinetics , Carbamazepine/toxicity , Carotenoids/metabolism , Catalase/metabolism , Chlamydomonas/drug effects , Chlamydomonas/growth & development , Chlorophyll/metabolism , Fresh Water , Microalgae/drug effects , Scenedesmus/drug effects , Scenedesmus/growth & development , Species Specificity , Superoxide Dismutase/metabolism , Wastewater/chemistry , Water Pollutants, Chemical/pharmacokinetics , Water Pollutants, Chemical/toxicityABSTRACT
The use of artificial tissues in regenerative medicine is limited due to hypoxia. As a strategy to overcome this drawback, we have shown that photosynthetic biomaterials can produce and provide oxygen independently of blood perfusion by generating chimeric animal-plant tissues during dermal regeneration. In this work, we demonstrate the safety and efficacy of photosynthetic biomaterials in vivo after engraftment in a fully immunocompetent mouse skin defect model. Further, we show that it is also possible to genetically engineer such photosynthetic scaffolds to deliver other key molecules in addition to oxygen. As a proof-of-concept, biomaterials were loaded with gene modified microalgae expressing the angiogenic recombinant protein VEGF. Survival of the algae, growth factor delivery and regenerative potential were evaluated in vitro and in vivo. This work proposes the use of photosynthetic gene therapy in regenerative medicine and provides scientific evidence for the use of engineered microalgae as an alternative to deliver recombinant molecules for gene therapy.
Subject(s)
Autotrophic Processes , Genetic Therapy , Photosynthesis , Regeneration , Tissue Engineering/methods , Animals , Autotrophic Processes/drug effects , Biocompatible Materials/pharmacology , Chlamydomonas/drug effects , Chlamydomonas/physiology , Dermis/drug effects , Female , Human Umbilical Vein Endothelial Cells/drug effects , Implants, Experimental , Inflammation/pathology , Mice , Microalgae/drug effects , Microalgae/physiology , Neovascularization, Physiologic/drug effects , Oxygen/pharmacology , Photosynthesis/drug effects , Recombinant Proteins/pharmacology , Regeneration/drug effects , Tissue Scaffolds/chemistry , Vascular Endothelial Growth Factor A/pharmacology , ZebrafishABSTRACT
The effect of insecticides (acephate and imidacloprid) on a freshwater microalga Chlamydomonas mexicana was investigated with respect to photosynthetic pigments, carbohydrate and protein contents, fatty acids composition and induction of stress indicators including proline, superoxide dismutase (SOD) and catalase (CAT). C. mexicana was cultivated with 1, 5, 10, 15, 20 and 25 mg L(-1) of acephate and imidacloprid. The microalga growth increased with increasing concentrations of both insecticides up to 15 mg L(-1), beyond which the growth declined compared to control condition (without insecticides). C. mexicana cultivated with 15 mg L(-1) of both insecticides for 12 days was used for further analysis. The accumulation of photosynthetic pigments (chlorophyll and carotenoids), carbohydrates and protein was decreased in the presence of both insecticides. Acephate and imidacloprid induced the activities of superoxide dismutase (SOD) and catalase (CAT) and increased the concentration of proline in the microalga, which play a defensive role against various environmental stresses. Fatty acid analysis revealed that the fraction of polyunsaturated fatty acids decreased on exposure to both insecticides. C. mexicana also promoted 25 and 21% removal of acephate and imidacloprid, respectively. The biochemical changes in C. mexicana on exposure to acephate and imidacloprid indicate that the microalga undergoes an adaptive change in response to the insecticide-induced oxidative stress.
Subject(s)
Chlamydomonas/drug effects , Insecticides/toxicity , Microalgae/drug effects , Carotenoids/metabolism , Catalase/metabolism , Chlamydomonas/genetics , Chlamydomonas/growth & development , Chlamydomonas/metabolism , Chlorophyll/metabolism , Fatty Acids/metabolism , Fresh Water/analysis , Imidazoles/toxicity , Microalgae/growth & development , Microalgae/metabolism , Neonicotinoids , Nitro Compounds/toxicity , Proline/metabolism , Superoxide Dismutase/genetics , Superoxide Dismutase/metabolismABSTRACT
This study evaluated the toxicity of herbicide atrazine, along with its bioaccumulation and biodegradation in the green microalga Chlamydomonas mexicana. At low concentration (10 µg L(-1)), atrazine had no profound effect on the microalga, while higher concentrations (25, 50, and 100 µg L(-1)) imposed toxicity, leading to inhibition of cell growth and chlorophyll a accumulation by 22 %, 33 %, and 36 %, and 13 %, 24 %, and 27 %, respectively. Atrazine 96-h EC50 for C. mexicana was estimated to be 33 µg L(-1). Microalga showed a capability to accumulate atrazine in the cell and to biodegrade the cell-accumulated atrazine resulting in 14-36 % atrazine degradation at 10-100 µg L(-1). Increasing atrazine concentration decreased the total fatty acids (from 102 to 75 mg g(-1)) and increased the unsaturated fatty acid content in the microalga. Carbohydrate content increased gradually with the increase in atrazine concentration up to 15 %. This study shows that C. mexicana has the capability to degrade atrazine and can be employed for the remediation of atrazine-contaminated streams.