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Indicators of environmental pressure in artificial and natural habitats: Analysis of fluctuating asymmetry in otoliths from Cynoglossus joyneri

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Abstract

Since the 20th century, as research on the fluctuating asymmetry (FA) of otoliths in sedentary fish has deepened in a gradual way, many scholars have focused on exploring the ability of their otolith FA to indicate different environmental pressures. In this study, a typical benthic fish – Cynoglossus joyneri from three artificial habitats (artificial reef area (ARA), oyster reef area (ORA) and kelp cultivation area (NCA)) and a natural habitat (natural area (NA)) of Haizhou Bay (Lianyungang, Jiangsu Province, China) was selected as the research object, of which four otolith characters (length, width, perimeter, and area) were used to detect FA based on the squared coefficient of asymmetry variation (CV2a). The results showed that the CV2a of otolith in C. joyneri tended to decrease as their body length increased. In terms of indicating environmental pressure, the CV2a of otolith length in NA was significantly higher than those in the other area (P<0.05); the CV2a of otolith width in NA was significantly higher than those in ARA and ORA (P<0.05), and those in NCA were significantly higher than those in ORA (P<0.05); and the CV2a of otolith area in NA was significantly higher than those in ARA (P<0.05), and those in NCA were significantly higher than those in ORA (P<0.05). Generally, the otolith FA of C. joyneri in artificial habitats has lower CV2a than that in natural habitats, indicating that the environmental pressure in artificial habitats is lower than that in natural habitats. We believe that C. joyneri can serve as an indicator species for environmental pressure between different habitats, which could be considered as a groundbreaking milestone in the study of otolith FA in fish. The findings not only advance the ability to assess environmental pressure in sedentary fish, which provide new insights into evaluating environmental pressure in artificial and natural habitats.

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Asymmetry was calculated for the otolith length, width, and thickness of two pelagic fi sh species, Sardinella sin-densis (Clupeidae) and Sillago sihama (Sillaginidae). The results showed that the level of asymmetry of the otolith width was the highest among the two asymmetry values obtained for the otolith of S. sindensis. For S. sihama, otolith thickness showed the highest value among the three otolith measurements. The asymmetry value was zero for the otolith thickness in S. sindensis. The lowest and highest values of asymmetry for the three otolith measurements are recorded in the following fi sh size classes of S. sindensis: for otolith length, 9.0-9.9 mm and 14.0-14.9 mm respec-tively; for otolith width, 9.0-9.9 mm, 14.0-14.9 mm respectively. In S. sihama, for otolith length, 19.0-20.9 mm. and 21.0-22.9 mm. respectively, for otolith width, 15.0-16.9 mm and 25.0-26.9 mm respectively; for otolith thickness, 17.0-18.9 mm and 19.0-20.9 mm respectively. The possible cause of asymmetry in these two species has been dis-cussed in relation to different pollutants and their presence in the area. The trend of an increase in the asymmetry value with the fi sh length was noticed in the width of the otolith of the two species studied. ASIMMETRIA FLUTTUANTE IN LUNGHEZZA, LARGHEZZA E SPESSORE DI OTOLITE IN DUE SPECIE DI PESCI PELAGICI DEL GOLFO PERSICO, VICINO A BANDAR ABBAS SINTESI L'asimmetria è stata calcolata per lunghezza, larghezza e spessore degli otoliti di due specie di pesci pelagici, Sardi-nella sindensis (Clupeidae) e Sillago sihama (Sillaginidae). I risultati hanno evidenziato che per l'otolite di S. sindensis, l'asimmetria era presente per due parametri, e il livello di asimmetria è risultato massimo per la larghezza dell'otolite. Per S. sihama, il valore più alto di assimetria si è registrato per lo spessore dell'otolite. Per S. sindensis invece, il valore dell'asimmetria per lo spessore degli otoliti era pari a zero. Sempre per S. sindensis, i valori minimo e massimo di asim-metria si sono registrati nelle seguenti classi di grandezza: per la lunghezza degli otoliti pari a 9,0-9,9 mm e 14,0-14,9 mm rispettivamente, e per la larghezza degli otoliti pari a 9,0-9,9 mm e 14,0-14,9 mm rispettivamente. Per S. sihama, i valori minimo e massimo di asimmetria si sono registrati per la lunghezza degli otoliti pari a 19,0-20,9 mm e 21,0-22,9 mm rispettivamente, per la larghezza degli otoliti pari a 15,0-16,9 mm e 25,0-26,9 mm rispettivamente, nonché per lo spessore degli otoliti pari a 17,0-18,9 mm e 19,0-20,9 mm rispettivamente. La possibile causa di asimmetria in queste due specie è stata messa in relazione a diverse sostanze inquinanti e alla loro presenza nella zona. Per entrambe le spe-cie, gli autori hanno registrato una tendenza all'aumento del valore di asimmetria in relazione alla lunghezza del pesce.
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Published on-line: 17 December 2013 Asimetría de la masa de los otolitos del mugílido Liza klunzingeri (Day, 1888), capturados en el Golfo Pérsico junto a Bandar Abbas Se calculó la asimetría de masa, x, como la diferencia entre la masa de otolidos pareados a izquierda y derecha, dividida por la masa media. Se estudió la asimetría del otolito sacular de Liza klunzingeri. Como en otras especies de peces simétricos, el valor absoluto de x no dependió de la longitud del pez ni del ratio de cre-cimiento del otolito. El valor medio de x estuvo entre -0,2 y +0,2. Abstract The otolith mass asymmetry, x, was calculated as the difference between the mass of the right and left paired otoliths divided by av-erage otolith mass. Saccular otolith mass asymmetry was studied in the mugilid fish Liza klunzingeri. As in the case of other symmet-rical fish species, the absolute value of x in L. klunzingeri does not depend on fish length and otolith growth rate. The mean value of x was between -0.2 and +0.2.
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Fluctuating asymmetry (FA) is assumed to reflect the developmental instability caused by environmental or genetic stress. Fish otoliths represent a very good tool for investigating the consequence of different effects on FA. Otolith FA analysis, coupled with genetic analysis, has been undertaken on two common West African estuarine species, Ethmalosa fimbriata (EFI) and Sarotherodon melanotheron (SME), in two neighbouring estuaries, in order to highlight the impact of salinity on developmental stability. The Gambia estuary has a normal functioning and the Saloum estuary is inverse (saltier waters in the upper river), reaching extremely high salinities (>100 psu) and constituting severe environmental stress. Five sub-populations of EFI and six of SME were studied along a salinity gradient. The differences between right and left otoliths were estimated with image processing by measuring five dimensions (area, perimeter, diameter, rostrum and posterior radii). Analyses of genetic differentiation at three EPIC and one anonymous nuclear gene loci for EFI and six polymorphic enzymatic loci for SME were carried out to measure the level of heterozygosity. Absolute FA in all otolith traits examined was unaffected by gender but increased significantly with fish size. Size-corrected absolute FA did not show any significant difference among sites differing largely in salinity, although a higher asymmetry in otolith area was recorded in the saltiest site. These findings suggest that otolith asymmetry is a poor indicator of osmotic stress. The individual heterozygosity level did not seem to have an effect on otolith FA for either species, even though a slight correlation appeared with otolith area or perimeter. Otolith FA cannot be considered to be a useful indicator for estimating changes linked with environmental or genetic stress in these estuaries.
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The current study aims to calculate and assess the asymmetry of the two goatfish species, Yellowstripe goatfish Mulloidichthys flavolineatus (Lacepède 1801) and Red Sea goatfish, Parupeneus forsskali (Fourmanoir & Guézé 1976) collected from Hurghada fishing harbour, Egypt. The asymmetry valuation for M. flavolineatus and P. forsskali is imperative to demonstrate the impact of asymmetry on the larvae settlement in this vital fishing ground. Asymmetry was calculated for the saccular otolith (Sagittae) biometry, namely length, width, and mass. The results showed that the otolith height had a lower asymmetry value than the otolith length for the two goatfish species inspected. No relationship between the asymmetry value of otolith length and width and total fish length was observed. Both goatfish species' calculated otolith mass asymmetry was higher than that of many teleost fish species.
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The problem of testing smooth components of an extended generalized additive model for equality to zero is considered. Confidence intervals for such components exhibit good across-the-function coverage probabilities if based on the approximate result, where f is the vector of evaluated values for the smooth component of interest and V f is the covariance matrix for f according to the Bayesian view of the smoothing process. Based on this result, a Wald-type test of f=0 is proposed. It is shown that care must be taken in selecting the rank used in the test statistic. The method complements previous work by extending applicability beyond the Gaussian case, while considering tests of zero effect rather than testing the parametric hypothesis given by the null space of the component's smoothing penalty. The proposed p-values are routine and efficient to compute from a fitted model, without requiring extra model fits or null distribution simulation.
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Data
Fluctuating asymmetry was described for the otolith width and length of adult teleost Beryx splendens. The results showed that the level of asymmetry of the otolith width was the highest among the two asymmetry values obtained for the otolith of B. splendens. For the otolith width character, the results showed that the level of asymmetry at its highest value in fish ranging in length be-tween 191–200 mm and in its lowest value in fish ranging in length between 121–180 mm. For the otolith length, the highest value of asymmetry is noticed in fish ranging in length between 231–244 mm and the lowest value in fish within the length of 121–190 mm. The possible cause of the asymmetry in this species has been discussed in relation to different pollutants and their pres-ence in the area. No trend of increase in the asymmetry values with the fish length was noticed for the otolith width, but there is a weak trend of increase with the fish length in case of otolith length character.
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One of the more difficult tasks in evaluating the possible deleterious effects of multiple toxicants on natural communities is in defining subtle sublethal effects before the onset of chronic morbidity. We reason that before detectable changes in either species diversity or species abundance occur subtle changes must take place in a number of important processes, ranging from molecular to behavioral changes. Unfortunately, changes in these parameters have proven most difficult to detect with current methodology. We, therefore, have been examining the possible use of fluctuating asymmetry as a possible measure of environmental stress. Fluctuating asymmetry is simply the random deviation from perfect symmetry of any bilateral anatomical character. It is, therefore, a nonspecific measure of developmental perturbation. Using asymmetry analysis on three species of marine teleost-barred sand bass, Paralabrax Ilebulifer; grunion, Leureslhes lenuis; and barred surfperch, AlIlphistichus argellteus-from southern California and B
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The correlations between the fluctuating asymmetries of different characters were investigated in three species (chaetae and wings of Drosophila melanogaster, cheek teeth of Peromyscus leucopus, and cheek teeth of the fossil horse Griphippus gratus). A mean correlation of 0 was found for the two former species, but a mean positive correlation of +0.046 was found for the horse. Reasons are given why this exception may be only apparent. The intensities of some morphological differences in Drosophila have a general component even though they may be bilaterally independent. The lack of variation for a general buffering capacity against minor developmental accidents was not expected. This and related matters are discussed.
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A dimensionless measure of otolith mass asymmetry, χ, was calculated as the difference between the masses of the right and left paired otoliths divided by average otolith mass. Saccular otolith mass asymmetry was studied in eight flatfish species (110 otolith pairs) and compared with data from a previously published study on roundfishes. As in the case of symmetrical fishes, the absolute value of χin flatfishes does not depend on fish length and otolith growth rate, although otolith mass and the absolute value of otolith mass difference are correlated with fish length. The values of χwere between −0·2 and +0·2 in 96·4% of flatfishes studied. The mean ±s.e. value of χin flatfishes was significantly larger than in standard bilaterally symmetrical marine fishes (‘roundfishes’), respectively 0·070 ± 0·006 and 0·040 ± 0·006. The most prominent distinction is the existence of downside prevalence of saccular otolith mass in flatfishes, which contrasts with no right–left prevalence in roundfishes found in a previous study. In the right-eyed flatfishes (Soleidae), the left saccular otoliths are heavier than the right otoliths. In the left-eyed flatfishes (Bothidae and Citharidae), the right saccular otoliths are heavier than the left otoliths. Not all flatfishes, however, fit in this design: 11·8% of flatfishes studied had the heavier saccular otoliths in the upside labyrinth and 5·4% of flatfishes had no otolith mass asymmetry (within the accuracy of the analysis). At the same time, the more mobile flatfishes (bothids and citharids) have more symmetrical and, hence, more precisely organized saccular otolith organs than the bottom-associated flatfishes (soleids). It is possible to assume that the value of the otolith asymmetry is not only correlated with flatfish placement in a particular family, or position of eyes, but also may correlate with general aspects of their ecology. Mathematical modelling indicated that for most flatfishes one-side saccular prevalence had no substantial significance for sound processing. On the other hand, calculations showed that 49% of flatfishes (but only 14·5% of roundfishes) have |χ| which exceed the critical level and, in principle, could sense the difference between the static displacement of the large and small paired otoliths. At that, the number of the soleids that could sense this difference is greater than the number of the bothids and citharids, 84 and 27%, respectively.
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Fluctuating asymmetry (FA), which has been examined in a variety of plants and animals, is widely promoted as a useful bioindicator of exogenous stressors in habitats, whether of natural or anthropogenic origin. Wildlife managers and researchers often use a specific group of organisms as an indicator of the health of a given habitat. The purpose of this review is to demonstrate that FA can be an effective fish biomonitoring tool by presenting a vote counting meta-analysis of 81 fish FA studies published between 1966 and the first half of 2009. The vote counts were analyzed with the G test for independence to determine whether the probability of observing significant morphological asymmetry is determined by character type, exogenous stressor type, or fish order. The information obtained from these papers and their analysis is then used to outline areas in which FA studies can be improved: (1) carefully considering character choice; (2) distinguishing between asymmetry types; (3) determining the level of measurement error in between-sides character variation; (4) determining baseline FA levels in populations; (5) increasing the number of laboratory studies which corroborate field observations of FA; (6) conducting true replications of studies to validate previous findings. Only with more critical experimental design and data analysis can FA be used as a powerful tool for assessing environmental degradation. KeywordsFluctuating asymmetry–Fishes–Environmental stress–Sub-lethal stress–Exogenous stress
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Habitatrestoration encompasses a broad range of activities, emphasizing very different issues, goals, and approaches depending on the operational definition of ‘restoration’. This is particularly true for many shellfish (molluscan) dominated systems (e.g. oyster reefs, mussel beds, vermetid gastropod reefs). In contrast to other well-studied biogenic habitats, such as seagrasses, mangroves, or salt marshes, bivalves are directly consumed as a resource. Hence resource extraction has direct consequences for habitat health. Restoration objectives have typically included reduction of public health risks through improved water quality to increase harvest. Restoration or enhancement of populations of commercially exploited shellfish depressed by overharvesting and/or reduced environmental quality remains the principal motivation behind most shellfish ‘restoration’ efforts. Direct and indirect ecosystem services (e.g. filtering capacity, benthic–pelagic coupling, nutrient dynamics, sediment stabilization, provision of habitat, etc.) derived from oyster habitat have been largely ignored or underestimated. Only recently, the restoration of lost ecological function associated with shellfish communities has been included in our discussions and related research examining habitat development and function through a scientific approach. The former area has been reviewed extensively and will not be our focus here. In this review, we examine some of the restoration efforts made in the name of fisheries enhancement, address their effectiveness, and discuss some of the issues associated with realizing the broader goal of ecological restoration. We note the importance of linking success criteria to specific goals and make the case for a greater need in clarifying the ecological functions of shellfish and shellfish habitats. We recognize the limitations of existing datasets and summarize ongoing attempts to address oyster habitat restoration throughout the broad geographic distribution of the American oyster, Crassostrea virginica (Gmelin). In many ways this topic parallels the ongoing debate over ‘attraction versus production’ associated with artificial reef management. We consider how local conditions (e.g. tidal range, bottom topography, turbidity, salinity) and resulting habitat traits affect restoration strategies. We also discuss the underappreciated value of shellfish populations from those areas designated as closed to harvesting due to their intrinsic worth as habitat/larval reserves. The necessity of ecosystem (adaptive) management strategies emerges from this discussion. Finally, this overview supports our contention that shellfish habitat should be included in discussions of ‘essential fish habitats’ (or EFH).
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Generalized additive models: an introduction with R
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Evaluation of the prediction effect of two GAMs on the distribution of Cynoglossus joyneri in the Haizhou Bay
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Bilateral asymmetry in size of otolith of Otolithes ruber (Bloch and Schneider, 1801) collected from the marine waters of Iraq
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