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  • 1
    Keywords: Forschungsbericht ; Wasseraufbereitungsanlage
    Type of Medium: Online Resource
    Pages: 1 Online-Ressource (51 Seiten, 2,07 MB) , Illustrationen, Diagramme
    Language: German
    Note: Unterschiede zwischen dem gedruckten Dokument und der elektronischen Ressource können nicht ausgeschlossen werden
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  • 2
    Keywords: Hochschulschrift
    Type of Medium: Online Resource
    Pages: Online-Ressource (IX, 99 Bl) , Ill., graph. Darst , 30 cm
    Edition: 2011 Online-Ressource [Online-Ausg.]
    DDC: 570
    Language: English
    Note: Enth. 4 Sonderabdr. aus verschiedenen Zeitschr , Kiel, Univ., Diss., 2011 , Online-Ausg.: , [Online-Ausg.]
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  • 3
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    Elsevier
    In:  Comparative Biochemistry and Physiology Part C: Toxicology and Pharmacology, 157 (4). pp. 352-360.
    Publication Date: 2020-08-04
    Description: Pike-perch Sander lucioperca is currently considered as one of the most promising candidates for production in freshwater recirculation aquaculture systems (RAS). Here, due to the lack of studies on nitrite (NO(2)(-)) toxicity in pike-perch, a flow-through exposure at 0, 0.44, 0.88, 1.75, 3.5, 7, 14 and 28 mg/L NO(2)(-)-N was carried out to determine the acute and chronic toxicity over a period of 32 days. In juvenile pike-perch, 120 h LC(50) was 6.1mg/L NO(2)(-)-N and at ≥14 mg/L NO(2)(-)-N all fish had died within 24 h. Chronic exposure revealed a significant build up of NO(2)(-) in the plasma as well as in the muscles at ≥0.44 mg/L NO(2)(-)-N peaking in fish exposed to the highest concentration of 3.5 mg/L NO(2)(-)-N after 32 days. Still, due to high individual variation methemoglobin (MetHb) was only significantly increased (p〈0.01) at 3.5 mg/L NO(2)(-)-N. No adverse effects on red blood cells (RBC) and hematocrit were observed in any of the treatments. In a second experiment, compensation of NO(2)(-) toxicity at increasing chloride concentrations (40 (freshwater), 65, 90, 140, 240, 440 mg/L Cl(-)) was observed at a constant exposure of 10 mg/L NO(2)(-)-N for 42 days. At ≥240 mg/L Cl(-), NO(2)(-) build-up in blood plasma and muscle was completely inhibited. At lower Cl(-) concentrations (≤140 mg/L), NO(2)(-) was significantly increased in plasma, but only insignificantly elevated in muscle due to high individual variation. MetHb was increased significantly difference only at 40 mg/L Cl(-) (freshwater control) compared to the control. Again, high individual variations were observed. As a conclusion, S. lucioperca is moderately sensitive towards NO(2)(-) and acceptable levels in RAS should hence not exceed 1.75 mg/L NO(2)(-)-N to avoid MetHb formation. However, based on the 120 h LC(50) and a factor of 0.01 according to Sprague (1971), a NO(2)(-) concentration of ≤0.061 mg/L NO(2)(-)-N is considered as "safe." Thereby, no NO(2)(-) should accumulate in the plasma or muscle tissue during chronic exposure. For 10 mg/L NO(2)(-)-N, ≥240 mg/L chloride compensates for NO(2)(-) uptake in plasma and muscle.
    Type: Article , PeerReviewed
    Format: text
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  • 4
    Publication Date: 2017-12-12
    Description: Ozone is frequently used for water treatment and disinfection in recirculating aquaculture systems. However, due to the fragmentary data on chronic toxicity of ozone produced oxidants (OPO) and its safe concentrations, the daily application of ozone in aquaculture is challenging. To evaluate the chronic effects of sublethal OPO concentrations, juvenile turbot (Psetta maxima, L.) were exposed to OPO concentrations of 0.06, 0.10 and 0.15mg/l for 21 days. Gills were analysed for histopathological alterations and mRNA expression of heat shock protein 70 (hsp70), hsp90 as well as glutathione-S-transferase (gst) were determined in the gills and the liver after 1d, 7d and 21d. Histopathologic findings confirmed adverse effects at 0.10-0.15mg/l, but these (necrosis, lamellar clubbing, hypertrophy, hyperplasia) could only be observed after an extended exposure (mostly 21d), and were considered as irreversible tissue damage. Hsp70 expression in the gills was only significantly increased at the highest OPO concentration (0.15mg/l) on 1d and 7d, and returned to basic levels until day 21. Hsp90 mRNA was already increased at 0.10mg/l after 1 and 7 days of exposure, and again was comparable to the control group on day 21. In contrast, elevated gst mRNA expression was only observed on day 7 at 0.10mg and 0.15mg/l. Although similar trends were observed in the liver for all markers, differences were only significant in exceptional cases due to the high individual variation observed. Thus, mRNA expression in the gills rather than in the liver is recommended as a marker to characterize OPO-induced oxidative stress in turbot. It has to be noted that mRNA expression returned to basic levels on day 21 regardless the actual OPO concentration, suggesting a collapse of adaptive mechanisms as a possible explanation for the observed tissue damage.
    Type: Article , PeerReviewed
    Format: text
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  • 5
    Publication Date: 2017-12-12
    Description: Ozone is a powerful oxidizing agent and is widely used for disinfection and improvement of water quality in aquaculture plants. However, the generation of ozone-produced oxidants (OPO) during ozonation of seawater may lead to toxicity impacts. To determine adverse effects of continuous, sublethal OPO concentrations, juvenile turbot (Psetta maxima, L.) were exposed to three different OPO concentrations (0.06, 0.10 and 0.15 mg/l) for up to 21 days. Fish were sampled after 1, 7 and 21 days of exposure to cover short-term, intermediate and long-term OPO effects. Gills were analyzed for morphological alterations, hemoglobin and hematocrit were quantified to assess loss in gill functionality. Plasma cortisol was measured as physiologic stress marker. Gill histology revealed significant histopathological alterations with increasing OPO concentration and prolonged times of exposure. However, hemoglobin concentrations were only elevated during short-term exposure at the highest OPO concentration. Hematocrit values did not show any differences between OPO-exposed specimens and the control group. At 0.15 mg/l, plasma cortisol was elevated after 24 h. The results demonstrate that sublethal OPO concentrations of 0.10 and 0.15 mg/l cause histological and physiological alterations in juvenile turbot, characterising ozone-produced oxidants as substantial stressor in recirculation systems. At an OPO concentration of 0.06 mg/l, just slight alterations in the tested parameters were observed suggesting concentrations of ≤ 0.06 mg/l as acceptable OPO levels for the rearing of juvenile turbot.
    Type: Article , PeerReviewed
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  • 6
    Publication Date: 2019-09-23
    Description: The chronic effect of nitrate on the production performance and health of marine cultured fish species is still unknown. Thus, the aim of the present research was to evaluate the chronic effect of nitrate on production parameters and health status of turbot (Psetta maxima). Juvenile turbot were exposed to 0 mg/L NO3-N (control C), 125 mg/L NO3-N (low nitrate LN), 250 mg/L NO3-N (medium nitrate MN) and 500 mg/L NO3-N (high nitrate HN) for 6 weeks in small-scaled recirculating aquaculture systems (RAS). After 42 d, biomass yield, length, weight and specific growth rate (SGR) were significantly (p 〈 0.05) lower for LN, MN and HN compared to C. Mortality, food conversion ratio (FCR), condition factor (CF) and splenic index (SI) did not differ significantly (p 〉 0.05) between C and LN but were significantly (p 〈 0.05) higher in the MN and HN groups. Hepatosomatic index (HSI), total hemoglobin (Hb) and methemoglobin (MetHb) did not show significant differences (p 〉 0.05) between treatments. Thus, nitrate negatively influences the production performance of turbot, even at low concentrations and nitrate management is therefore a key-factor in turbot RAS production. (C) 2011 Elsevier B.V. All rights reserved.
    Type: Article , PeerReviewed
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  • 7
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    In:  (PhD/ Doctoral thesis), Christian-Albrechts-Universität, Kiel, Germany, 99 pp
    Publication Date: 2012-07-06
    Description: The aim of the present thesis was to assess the potential and limitations of ozonation in marine recirculating aquaculture systems (RAS) while particularly focussing on the toxicity, formation and removal of ozone-produced oxidants (OPO) in order to develop guidelines and thresholds for a reasonable and safe ozone application. In the first two chapters the toxicity of OPO was investigated for Pacific white shrimp (Litopenaeus vannamei) and turbot (Psetta maxima) and maximum safe exposure levels were determined for both species. Despite their strong differences in biology, both investigated species possess a similar sensitivity towards OPO. Results demonstrate that OPO concentrations ≥ 0.10 mg/l cause adverse effects in both species. An OPO concentration of 0.06 mg/l was determined as the maximum safe exposure level for rearing juvenile L. vannamei and P. maxima. Furthermore, we proved this safe level to be sufficient to control and reduce bacterial biomass in the recirculating process water. To improve the control of toxic OPO, the removal performance of activated carbon filtration was tested for different oxidant species (free bromine, bromamines, free chlorine and chloramines). Results proved activated carbon filtration to be very efficient in removing the dominating oxidant species free bromine and bromamines formed during the ozonation of natural and most artificial seawaters. In contrast, removability of chloramines, sometimes present in ozonated bromide-free artificial seawater, was shown to be significantly lower. Finally the suitability of ozone for water quality improvement was evaluated by investigating the ozone-based removal of nitrite, ammonia, yellow substances and total bacterial biomass with regard to feasibility, efficiency as well as safety for the cultivated organisms. Results demonstrate that ozone can be efficiently utilized to simultaneously remove nitrite and yellow substances from process water in RAS without risking the formation of toxic OPO concentrations. Although ammonia oxidation in seawater by ozonation is independent from pH and enables almost the complete removal of ammonia-nitrogen from the aquaculture system with nitrogen gas as the primary end product, it presupposes an initial accumulation of OPO to highly toxic amounts, restricting a safe application in aquaculture.
    Type: Thesis , NonPeerReviewed
    Format: text
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  • 8
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    In:  [Talk] In: 61. Öffentliche Hochschultagung der A+E-Fakultät der CAU, 03.02.2011, Kiel, Germany .
    Publication Date: 2012-02-23
    Type: Conference or Workshop Item , NonPeerReviewed
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  • 9
    Publication Date: 2012-02-23
    Type: Conference or Workshop Item , NonPeerReviewed
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  • 10
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    European Aquaculture Society
    In:  Special publication / European Aquaculture Society, 2010 . pp. 1204-1205.
    Publication Date: 2012-02-23
    Type: Article , NonPeerReviewed
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