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1.
环境污染能够影响养殖贝类的免疫能力,是导致贝类大规模死亡的重要原因之一.探讨了大连周边4个海区污染物对采集的菲律宾蛤仔(Ruditapes philippinarum)免疫毒性影响.结果发现:污染物浓度和种类对蛤仔的免疫和生理指标具有重要影响,在重金属和石油污染物浓度较低的皮口海区,血细胞总数、亮氨酸氨基肽酶活性和血淋巴溶菌酶活性均显著高于其它3个海区(P<0.05),而蛤仔的脂质氧化水平则较低;在重金属和石油污染物浓度较高的黑石礁海区,蛤仔血淋巴谷胱甘肽含量显著高于其它3个海区(P<0.05);在重金属浓度较高的庄河海区,蛤仔表现出较高的超氧化物歧化酶活性(P<0.05).  相似文献   

2.
菲律宾蛤仔大连群体不同世代的遗传多样性   总被引:1,自引:0,他引:1  
采用12对有效微卫星引物对大连群体菲律宾蛤仔连续4个选育世代(F1、F2、F3、F4)的144个个体进行了遗传多样性分析。结果表明:共获121个等位基因,每个位点的等位基因数在2-6个不等,其大小在101-273 bp之间;各个世代平均等位基因数在3.75-4.58,平均观测杂合度在0.3391-0.3860之间。从F-检验结果上看,所有世代内有2个位点遗传分化较弱,8个位点遗传分化中等,2个位点遗传分化较大;配对比较Fst值(0.05-0.15)表明4个世代群体间遗传分化程度中等。Fis值表明有2个世代位点杂合度处于过剩状态;但对连续4个世代而言,每个世代均表现出一定程度的杂合子缺失。随着世代连续选育的进行,Nei氏遗传相似性逐渐减小(0.8203-0.8107-0.8031);遗传距离逐渐增大(0.1918-0.2099-0.2129);不同世代群体间遗传相似性系数为0.7873-0.8685,遗传距离为0.141-0.2391。4个世代平均PIC值为0.5055,表明选育后代遗传多样性较好,还有较大的选育潜力,可以继续进行上选。  相似文献   

3.
The dinoflagellate Prorocentrum minimum is increasingly recognized as a harmful algal bloom (HAB) species that affects filter-feeding shellfish. An experiment was done to investigate possible interactions between parasitic diseases and exposure to P. minimum in Manila clams, Ruditapes philippinarum. Manila clams, with variable levels of infection with Perkinsus olseni, were exposed for three or six days to the benign phytoplankton species Chaetoceros neogracile or a mixed diet of C. neogracile and P. minimum. After three or six days of exposure, clams were assessed individually for condition index, parasite status, and plasma and hemocyte parameters (morphological and functional) using flow-cytometry. Histological evaluation was also performed on individual clams to assess prevalence and intensity of parasitic infection, as well as other pathological conditions.Prorocentrum minimum caused several changes in Manila clams, especially after six days of exposure, such as decreased hemocyte phagocytosis and size and clam condition index. Pathological conditions observed in Manila clams exposed to P. minimum were hemocyte infiltration in the intestine and gonad follicles, myopathy, and necrosis of the intestine epithelial cells. The parasite P. olseni alone had no significant effect on Manila clams, nor did it modulate the hemocyte variables in clams exposed to P. minimum; however, the parasite did affect the pathological status of Manila clams exposed to the P. minimum culture, by causing atrophy and degeneration of residual ova in the gonadal follicles and hyaline degeneration of the muscle fibers, indicating synergistic effects of both stressors on the host over a short period of time. Additionally, an in vitro experiment also demonstrated detrimental effects of P. minimum and exudates upon P. olseni cells, thus suggesting HAB antagonistic suppression of transmission and proliferation of the parasite in the natural environment over a longer period of time. The results of this experiment demonstrate the complexity of interactions between host, parasite, and HAB.  相似文献   

4.
虞志飞  闫喜武  张跃环  杨霏  杨凤  张国范 《生态学报》2012,32(15):4673-4681
为查明年龄结构对菲律宾蛤仔同一群体内遗传多样的影响,采用14个SSR分子标记对大连石河不同年龄段的野生蛤仔进行了检测。结果表明:不同年龄段(1龄-Age1、2龄-Age2、3龄-Age3)蛤仔均维持着较高的遗传多样性。根据POPGENE 1.31和SPSS16.0统计分析显示,位点Rp-11、Rp-12、Rp-19对3个年龄段蛤仔的等位基因数差异极显著(P<0.01);位点Rp-20、Rp-24、Rp-27、Rp-30对其差异显著(P<0.05);剩余7个位点表现为差异不显著(P>0.05)。在平均水平上,每位点等位基因数目Na为4.3095,有效等位基因数目Ne为2.3729,多态位点百分数P(%)为14。观察杂合度和期望杂合度都比较高,观察杂合度平均为Ho=0.2335,期望杂合度平均为He=0.5140。而且,Ne和He随年龄的变化表现出Age2>Age3>Age1的趋势。各年龄段蛤仔——Age1、Age2、Age3的平均观察杂合度(Ho)和平均期望杂合度(He)分别为0.2357、0.2546、0.2159和0.4951、0.5286、0.5184。Age2的遗传多样性指数高于Age1及Age3,遗传分化相对较低。其中,Age1与Age3蛤仔遗传距离最小,D为0.0195,即变异很小;而Age1与Age2遗传距离较大,D为0.0437,变化范围不大(0.0195—0.0437)。从遗传一致度的数值上看了3个年龄段蛤仔的遗传相似程度很大,平均为0.9655。Age1与Age3遗传相似程度高达0.9807,而Age1与Age2相似程度较小为0.9572。说明不同年龄段蛤仔相似程度非常高。根据不同年龄段蛤仔的遗传距离,采用UPGMA平均聚类方法对其进行聚类可知,Age3与Age1蛤仔间遗传距离较小,与Age2蛤仔差异较大。通过对等位基因频率进行卡方检验发现,随着年龄结构的变化,部分基因基因频率减小;同时随着年龄的增长,有部分等位基因得到了纯化。大连群体蛤仔总的遗传分化较低,其遗传分化指数Fst为0.0248(Fst<0.05),遗传分化系数为0.02,说明总的遗传变异中有2%来自于不同年龄段的蛤仔之间。遗传距离和遗传一致度均值分别为0.035和0.9655,基因流(Nm=9.8238)相对流畅,进一步表明年龄结构对蛤仔种群内遗传分化的影响较小。  相似文献   

5.
We evaluated the pathogenicity of Perkinsus olseni towards the Manila clam, Ruditapes philippinarum, by an experimental challenge. For production of prezoosporangia of P. olseni, we injected uninfected Manila clams with cells of a pure strain of P. olseni and reared them for 7 d. Prezoosporangia were isolated from the soft tissue of the injected clams after culturing in Ray’s fluid thioglycollate medium. Hatchery-reared, uninfected juvenile clams (3-10 mm shell length) were challenged by immersion in one of two concentrations of a prezoosporangial suspension of P. olseni for 6 d. The challenged clams had significantly higher mortality at both the concentrations than the unchallenged clams. The mortality due to infection dose-dependently began approximately 4 weeks and 7 weeks after challenge in the higher and lower concentrations, respectively. This is the first experimental evidence that P. olseni causes direct mortality in Manila clams. The lethal level of infection was estimated at approximately 107 pathogen cells/g soft tissue weight.  相似文献   

6.
European stocks of the Manila clam Ruditapes philippinarum are affected by the Brown Ring Disease (BRD), which is caused by Vibrio tapetis. BRD is characterized by an accumulation of a brown organic matrix on the inner face of the shell. Clams that recover from BRD develop a white mineralized layer covering the brown matrix. Stocks of clams that showed resistance to BRD development, as enhanced recovery, have been monitored since 2000. We have examined two selected stocks: a Low Susceptibility (LS) stock and a High Susceptibility stock (HS), over three generations. The LS stock showed less evidence of the BRD symptoms, and more evidence of total shell repair, both in the field and following experimental challenge with V. tapetis, indicating that some clams may be less vulnerable to a V. tapetis attack than others. The inner face of the valves of the LS and HS clams of the two last generations were analysed with scanning electron microscopy. Examination of shells from BRD-affected clams showed that during the repair process, calcium crystals were progressively laid down until the affected zone was entirely covered. By the end of the shell repair process, a final organic layer covered the calcium crystal mounds. This layer seemed essential in the recovery process. The results indicate that the shell repair capability of the clams is the principal mechanism implicated in the development of BRD resistance in the Manila clam stocks. However, this resistance did not increase with generation because the broodstock was maintained at a site where selection pressure was low, due to a low prevalence of V. tapetis.  相似文献   

7.
The periodicity of increment formation in the shell of the Manila clam Ruditapes philippinarum was investigated in the subtidal zone of the Auray River estuary (South Brittany, France). Calcein markings were performed at different periods between May and October 2007 using in situ benthic chambers tented by scuba divers. This study shows that shell microgrowth increments were well-defined and deposited with a tidal periodicity in the subtidal zone, providing the calendar base for high-resolution ecological studies and environmental reconstruction from these R. philippinarum shells. Endogenous rhythmicity in shell microgrowth increment formation and oxygen consumption was previously documented in this species from intertidal flats. Our study suggests that, in the subtidal zone, Manila clams' rhythmic activity may be controlled by such an endogenous process, synchronized by tidal cues. As in other bivalves, R. philippinarum is an osmoconformer euryhaline bivalve. The tidal rhythmicity of shell microgrowth increments in subtidal specimens of this species could be explained by a behavioral adaptation of valve closure at low tide to protect the clam from low salinities and/or to synchronize with food availability. Finally, large inter-individual variability in tidally associated growth rates and asynchronous growth breaks were observed, and could be due to genetic variability between individuals, asynchronous partial spawning events or predation.  相似文献   

8.
9.
The oyster ovarian parasite Marteilioides chungmuensis has been reported from Korea and Japan, damaging the oyster industries. Recently, Marteilioides-like organisms have been identified in other commercially important marine bivalves. In this study, we surveyed Marteilioides infection in the Manila clam Ruditapes philippinarum, Suminoe oyster Crassostrea ariakensis, and Pacific oyster Crassostrea gigas, using histology and Marteilioides-specific small subunit (SSU) rDNA PCR. The SSU rDNA sequence of M. chungmuensis (1716 bp) isolated from C. gigas in Tongyoung bay was 99.9% similar to that of M. chungmuensis reported in Japan. Inclusions of multi-nucleated bodies in the oocytes, typical of Marteilioides infection, were identified for the first time in Suminoe oysters. The SSU rDNA sequence of a Marteilioides-like organism isolated from Suminoe oysters was 99.9% similar to that of M. chungmuensis. Marteilioides sp. was also observed from 7 Manila clams of 1840 individuals examined, and the DNA sequences of which were 98.2% similar to the known sequence of M. chungmuensis. Unlike Marteilioides infection of Pacific oysters, no remarkable pathological symptoms, such as large multiple lumps on the mantle, were observed in infected Suminoe oysters or Manila clams. Distribution of the infected Manila clams, Suminoe oysters and Pacific oysters was limited to small bays on the south coast, suggesting that the southern coast is the enzootic area of Marteilioides infection.  相似文献   

10.
杨凤  曾超  王华  文永升  何阳阳  张瑜 《生态学报》2016,36(3):795-802
作为埋栖型滩涂贝类的典型代表种类,菲律宾蛤仔Ruditapes philippinarum具有很强的潜沙行为。为了进一步了解其生态行为学,在室内实验室条件下,模拟了常见环境因子温度、盐度、p H值以及流速和规格大小对蛤仔幼贝(6—12 mm)潜沙速度的影响。结果表明,温度10—30℃,盐度25—30,p H值在6.0—9.0范围内蛤仔幼贝均能100%潜沙;在试验观察的4—5 h内,盐度由30突变至10时没有蛤仔潜沙,突变至20时有20%—30%潜沙(20℃,庄河蛤仔)或100%潜沙(15℃,福建蛤仔);p H值由8.0突变至10.0时不能潜沙;以暂养海水的温度(15或20℃)、盐度(30)和p H值(8.0)为中心,随着各个指标向两侧突变潜沙时间延长;流速为3、4和5 cm/s时,随流速增大潜沙速度加快;在规格6、9 mm和12 mm的幼贝中,以12 mm潜沙速度最快。若以半数潜沙时间(ET_(50))为判定指标,则适宜潜沙温度为15—20℃,盐度为25—30,p H值为7—9(莆田蛤仔)和8.0(庄河蛤仔)。在适宜条件下,蛤仔幼贝1 min内开始潜沙,3 min内有半数潜沙,5 min便全部潜沙。研究发现环境突变对蛤仔潜沙有明显影响,在天然海区放养蛤仔时应该注意购买地和放养海区温度、盐度和p H值的差异,并且选取10 mm以上幼贝放养效果较好。所得结论对完善菲律宾蛤仔幼贝的行为学及其底播养殖技术提供了有意义的参考。  相似文献   

11.
To examine the pattern of phylogeography of Ruditapes philippinarum, a length of 644-bp gene fragment of the mtDNA COI was sequenced. A total of 170 individuals from 19 locations were analyzed yielding 74 haplotypes, most of which were unique. The levels of haplotype diversity and nucleotide diversity for the species ranged from 0.80 ± 0.16 (Notsuke Bay) to 1.00 ± 0.13 (Nanao Bay, Miyazu Bay, Dalian 1 and Ariake), and from 0.002 ± 0.001 (Notsuke Bay) to 0.011 ± 0.006 (Qingdao), respectively. Both the phylogenetic (NJ tree) and minimum spanning trees (MST) showed three significant genealogical clusters corresponding to sampling localities, a genetic differentiation speculated to be caused by the isolation of the marginal seas of the Northwestern Pacific during Pleistocene low sea-level stands. Both AMOVA and pairwise Fst analyses revealed significant genetic differentiation between the populations from Japan and China. The pattern of isolation by distance was also detected in this species (r = 0.50, P < 0.001). Both mismatch distribution analysis and the neutrality tests showed that R. philippinarum had undergone a recent population expansion. The estimate of population expansion time was about 425 kya-1580 kya.  相似文献   

12.
菲律宾蛤仔EST_SSR标记与生长性状的相关分析   总被引:1,自引:0,他引:1  
研究利用20个微卫星标记对菲律宾蛤仔斑马蛤F2代家系107个个体进行遗传多样性分析,并对标记位点与生长相关性状进行分析。在20个微卫星位点共检测到41个等位基因,各位点等位基因数为2—3个,等位基因片段大小为109—430 bp,平均等位基因数为2.05个。平均有效等位基因数为1.71个,观测杂合度平均值为0.504,期望杂合度的平均值为0.431,平均多态信息含量为0.324。经卡方检验,3个位点SSR11,SSR164和SSR213的基因型分布显著偏离了孟德尔定律(P0.01)。运用SPSS 20.0对20个微卫星位点与菲律宾蛤仔斑马蛤家系生长性状的相关性(壳长、壳宽、壳高和体重)进行连锁显著性检验。结果表明,SSR9位点与壳高存在显著的相关关系(P0.05),SSR135和SSR164位点与壳宽呈显著相关(P0.05),SSR142位点与体重呈显著性相关(P0.05)。研究结果可为菲律宾蛤仔的分子标记辅助选育提供参考。  相似文献   

13.
14.
菲律宾蛤仔EST-SSRs标记开发及不同地理群体遗传多样性   总被引:1,自引:0,他引:1  
利用13对微卫星引物对大连、莆田、青岛3个地理群体蛤仔遗传多样性进行了检测。结果表明:13个基因座共检测到154个等位基因,每个座位检测到的等位基因数在2-7个之间,平均有效等位基因数为2.7657;3个群体平均观测杂合度分别为0.4387、0.4194、0.2383,平均期望杂合度分别为0.6488、0.6484、0.5526;群体间的遗传多样性差异不显著(P>0.05)。NJ聚类结果显示大连和莆田群体的蛤仔亲缘关系较近,二者与青岛群体关系较远。3个群体均有不同程度的偏离Hardy-Weinberg平衡现象,表明各群体基因频率和基因型频率的稳定性相对较低。本研究所获得的微卫星标记的多态信息含量(PIC)>0.5,说明这些微卫星位点的多样性较高,可为下一步遗传图谱构建研究提供参考。  相似文献   

15.
The shell length, height, and width, live body weight, and edible tissue weight of Manila clam of 1, 2, and 3 years of age were measured, and their correlation coefficients were calculated. The shell morphological traits were used as independent variables, and live body weight or edible tissue weigh used as a dependent variable for calculating the path coefficients, correlation index and determination coefficients. The results showed that the correlation coefficients between each shell morphological trait and the live body weight or edible tissue weight were all highly significant (P < 0. 01). The shell height at 1-year old clams was highly correlated with the live body weight and edible tissue weight. The shell width of 2- to 3-year-old clams was strongly associated with the live body weight, while the shell length was closely linked to the edible tissue weight. The results of coefficients of determination for the morphological traits against weight traits agreed well with the results of path analysis. The correlation indices for all morphological traits against weight traits were approximately the same as determination coefficients regardless of clam age. The correlation indices (R2) of morphological traits against the live body weight of clams of all ages and edible tissue weight of 1-year-old clams were larger than 0.85, but R2 of morphological traits against the edible tissue weight of 2- and 3-year-old clams was smaller than 0.85, indicating that some other factors might be associated with the edible tissue weight of 2- and 3-year-old clams. Multiple regression equations were obtained to estimate shell length X1 (cm), shell height X2 (cm), shell width X3 (cm) against live body weight Y (g), edible tissue weight Z (g): for 1-year-old clams: Y = ?4.317 + 0.18X1 + 0.147X2, (X1 < 0.01, X2 < 0.01), Z = ?1.011 + 0.095X2, (X2 < 0.01); for 2-year-old clams: Y = ?15.119 + 0.249X1 + 0.176X2 + 0.688X3, (X1 < 0.01, X3 < 0.01), Z = ?4.248 + 0.198X1, (X1 < 0.05, X3 < 0.01); and for 3-year-old clams: Y = ?25.013 + 0.415X1 + 1.184X3, (X1 < 0.01, X3 < 0.01), Z = ?7.082 + 0.119X1 + 0.332X3, (X1 < 0.05, X3 < 0.01).  相似文献   

16.
Brown Ring Disease (BRD), which affects the Manila clam in Europe, is caused by the bacterium, Vibrio tapetis. BRD has been diagnosed in Ireland on only one occasion (1997) although the aetiological agent has recently been detected in apparently healthy Manila clams from a number of sites around the Irish coast. The present work investigated the susceptibilities to BRD of two stocks of Manila clams, one from Ireland and the second from Galicia, north-western Spain, where BRD has been reported on a number of occasions. Exposure of the clams was by addition of V. tapetis to the holding waters. Development of BRD was assessed by the appearance of brown ring signs on the host shells, by bacterial isolation and characterization, and by detection of the bacterium by PCR. The pathogen was recovered from infected individuals and confirmed as V. tapetis by biochemical tests and a slide agglutination test. Galician clams experienced significantly higher mortalities, BRD prevalences and V. tapetis levels than Irish clams. Background infection with V. tapetis in the control stocks prevented conclusions being drawn on comparative susceptibility of the two stocks. Irish clams were significantly affected by the experimental challenge, as demonstrated by the development of BRD and an increase in V. tapetis levels. Results illustrate the vulnerability of Irish clams to BRD and have implications for the movement and transfer of clam seed in Ireland.  相似文献   

17.
Although the Manila clam (Ruditapes philippinarum) culture grounds are occasionally located in Zostera japonica beds along the coasts of Korea, plant responses to the clamming activity have not been reported for this seagrass species. Intense Manila clam harvesting activity took place in the intertidal Z. japonica bed during April 2004. The Z. japonica bed at the study site has been monitored since January 2003. Thus, this study provided a unique opportunity to compare the structure of the Z. japonica population before and after the clamming activity, which was conducted for approximately 1 week in April 2004. All Z. japonica shoots were removed and buried in the sediment immediately after the clamming activity. However, a few shoots were found at the disturbed area in July 2004, 3 months after the clamming activity. By September 2004, 5 months after the disturbance, shoot density and biomass were almost recovered to the levels reported before the clamming activity. No Z. japonica seedlings were observed when the shoot density rapidly increased in August and September 2004, 4-5 months after the disturbance, because revegetation of the disturbed seagrass bed has occurred before the seed germination time which is typically winter or early spring in this area. Thus, the initial rapid revegetation of the disturbed area occurred via asexual reproduction through new shoot formation from the buried below-ground tissues. The reproductive shoot density and reproductive efforts of Z. japonica were significantly higher after the disturbance relative to the levels recorded before the disturbance, and the duration of the fertile period was approximately three times longer following the clamming activity. The belowground biomass after the disturbance was also significantly higher than that before the disturbance. These results suggest that Z. japonica allocated more energy to sexual reproduction, as well as the maintenance of belowground tissues, to persist their population under unstable environmental conditions.  相似文献   

18.
19.
Previous estimations of nutrient mineralization in the water column by infaunal bivalves might have been overestimated because of underestimation of the uptake process by microphytobenthos in the field. We conducted field surveys of environmental conditions and quantitative sampling of Ruditapes philippinarum in a shallow lagoon system (Hichirippu Lagoon, eastern Hokkaido, Japan) in August 2006. We recorded the spatial distribution pattern and the molar ratio of dissolved inorganic nutrients to determine the limiting nutrients for microphytobenthos, to evaluate the input and output of nutrients at the entrance of the lagoon station, and to estimate potential nutrient mineralization by R. philippinarum. Our aim was to reevaluate the nutrient mineralization process by infaunal bivalve species. In this study, the mean standing stock of microphytobenthos inhabiting surface sediment (5 mm thick) on the tidal flats was 100 times higher than that of phytoplankton (1 m depth). Low N/P and high Si/N ratios (mean = 2.6 and 17.6, respectively) near the entrance of the lagoon compared to those of microphytobenthos (N:P:Si = 10.1:1:18) clearly suggest N deficiency. The flux of NH4-N coming into the lagoon was 3.4 kmolN d− 1, and the flux out was − 3.7 kmolN d− 1. Thus, assuming that there would have been no phytoplankton and microphytobenthos uptake during the day, 0.3 kmolN d− 1 of NH4-N was produced within the lagoon. However, the NH4-N mineralization rate of the clams has been estimated to be approximately 7.7 ± 6.8 kmolN d− 1. Thus, 96% (7.4 kmolN d− 1, i.e., 7.7 kmolN d− 1 minus 0.3 kmolN d− 1) of the NH4-N mineralized by the clam was consumed by microphytobenthos. In contrast, if all the NH4-N inflow (3.1 kmolN d− 1) was consumed by the microalgae before outflow, 52% (4.0 kmolN d− 1, i.e., 7.7 kmolN d− 1 minus 3.7 kmolN d− 1) of the NH4-N mineralized by the clams should have been consumed by microphytobenthos. Microphytobenthos on the tidal flats (11.3 ± 11.8 kmolN) used all of the surplus nutrients (between 4.0 and 7.4 kmolN d− 1), and the temporal division rate [=(NH4-N uptake)/(standing stock of microphytobenthos)] of microphytobenthos would have to be between 0.35 and 0.65 d− 1. Residual NH4-N (0.3 - 3.7 kmolN d− 1) was the water-column source and accounted for 12-148% of NH4-N in the water column near the entrance of the lagoon (2.5 ± 1.4 kmolN) per day. This is the first field-based observation with a quantitative evaluation of nutrient mineralization by infaunal bivalves and nutrient uptake by microphytobenthos.  相似文献   

20.
Yang F  Yao T  Huo Z M  Zhang Y H  Yan X W  Zhang G F 《农业工程》2010,30(3):135-140
A study was conducted to investigate the impact of starvation on different sizes of Manila clam Ruditapes philippinarum (0.66 ± 0.11, 2.12 ± 0.38, and 11.65 ± 0.84 mm in shell length, respectively) in the summer of 2008. Different size clams were starved for 7, 15, 30, 45, and 60 d, respectively, and followed by refeeding for 30 d. During the study, the water temperature ranged 26.2–28.4 °C, salinity 22–24‰, and pH 7.80–8.12. Compensatory growth occurred in the smallest size-group after 7 and 15 d of starvation, respectively. The point-of-no-return (PNR50) was determined to be 18.7 d. However, no compensatory growth was noted in the medium size-group, and the PNR50 for this group was 25.2 d. The complete compensatory growth was observed for the largest size-group following food depravation for 7 and 30 d, respectively. In the same group, over-compensatory growth occurred 15 d post-starvation. The PNR50 for the largest size-group was 46.3 d. The survival rate of different groups decreased as the starvation time prolonged. To discuss the change in body biochemical composition of individuals in the process of starvation and refeeding, the biochemical composition of the largest group individuals at different stages was determined. There were no significant differences in moisture and ash concentrations of the largest size-group during starvation and refeeding (P > 0.05). The relative body protein content increased as the starvation period prolonged and the level returned to normal after refeeding. The lipid content of the clam at the end of starvation was significantly lower than the initial level (P < 0.05), and remained below the initial level at end of the refeeding period.  相似文献   

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