水产科学
水產科學
수산과학
FISHERIES SCIENCE
2013年
9期
524-530
,共7页
王吉桥%张凯%袁成玉%姜玉声%张剑诚%宫德龙%曹旭鹏
王吉橋%張凱%袁成玉%薑玉聲%張劍誠%宮德龍%曹旭鵬
왕길교%장개%원성옥%강옥성%장검성%궁덕룡%조욱붕
仿刺参%附着基%生长%藻类%微生态制剂
倣刺參%附著基%生長%藻類%微生態製劑
방자삼%부착기%생장%조류%미생태제제
sea cucumber (A postichopus japonicus)%attachment%growth%alga%probiotics
在水温11.2~21.0℃下,将初始体质量为(1.00±0.05)g的仿刺参,随机放入容水为50 L (50 cm ×40 cm ×30 cm )的18个塑料水槽中,每槽20头,分为6组,每组3个重复,饲养80 d。A组水槽中只添加等比例混合的小球藻、筒柱藻和角毛藻;B组只添加微生态制剂(主要为光合细菌、乳酸菌和酵母菌),菌或藻细胞密度为2.22×108个/水槽;C、D和E组添加藻类和微生态制剂比例分别为1∶1、2∶1和1∶2,密度与A组相同;K组为对照组,不添加藻类和微生态制剂。试验结果表明,只添加藻类混合液的A组仿刺参的特殊质量增加率最高(0.16%/d ),E组次之,只添加微生态制剂的B组最低(-0.37%/d),A组和E组与B组间差异极显著(P<0.01)。A组水体中氨氮和活性磷含量较高,仿刺参体腔液中酸性磷酸酶和过氧化氢酶的活性最低,肠道内弧菌数最少。B组水槽中亚硝酸氮浓度始终很高,仿刺参体腔液中酸性磷酸酶和过氧化氢酶的活性增高,肠道内弧菌数增加。添加不同数量藻类和微生态制剂水槽中仿刺参肠道胃蛋白酶、淀粉酶和脂肪酶的活性不同,但与生长之间的相关性不明显。
在水溫11.2~21.0℃下,將初始體質量為(1.00±0.05)g的倣刺參,隨機放入容水為50 L (50 cm ×40 cm ×30 cm )的18箇塑料水槽中,每槽20頭,分為6組,每組3箇重複,飼養80 d。A組水槽中隻添加等比例混閤的小毬藻、筒柱藻和角毛藻;B組隻添加微生態製劑(主要為光閤細菌、乳痠菌和酵母菌),菌或藻細胞密度為2.22×108箇/水槽;C、D和E組添加藻類和微生態製劑比例分彆為1∶1、2∶1和1∶2,密度與A組相同;K組為對照組,不添加藻類和微生態製劑。試驗結果錶明,隻添加藻類混閤液的A組倣刺參的特殊質量增加率最高(0.16%/d ),E組次之,隻添加微生態製劑的B組最低(-0.37%/d),A組和E組與B組間差異極顯著(P<0.01)。A組水體中氨氮和活性燐含量較高,倣刺參體腔液中痠性燐痠酶和過氧化氫酶的活性最低,腸道內弧菌數最少。B組水槽中亞硝痠氮濃度始終很高,倣刺參體腔液中痠性燐痠酶和過氧化氫酶的活性增高,腸道內弧菌數增加。添加不同數量藻類和微生態製劑水槽中倣刺參腸道胃蛋白酶、澱粉酶和脂肪酶的活性不同,但與生長之間的相關性不明顯。
재수온11.2~21.0℃하,장초시체질량위(1.00±0.05)g적방자삼,수궤방입용수위50 L (50 cm ×40 cm ×30 cm )적18개소료수조중,매조20두,분위6조,매조3개중복,사양80 d。A조수조중지첨가등비례혼합적소구조、통주조화각모조;B조지첨가미생태제제(주요위광합세균、유산균화효모균),균혹조세포밀도위2.22×108개/수조;C、D화E조첨가조류화미생태제제비례분별위1∶1、2∶1화1∶2,밀도여A조상동;K조위대조조,불첨가조류화미생태제제。시험결과표명,지첨가조류혼합액적A조방자삼적특수질량증가솔최고(0.16%/d ),E조차지,지첨가미생태제제적B조최저(-0.37%/d),A조화E조여B조간차이겁현저(P<0.01)。A조수체중안담화활성린함량교고,방자삼체강액중산성린산매화과양화경매적활성최저,장도내호균수최소。B조수조중아초산담농도시종흔고,방자삼체강액중산성린산매화과양화경매적활성증고,장도내호균수증가。첨가불동수량조류화미생태제제수조중방자삼장도위단백매、정분매화지방매적활성불동,단여생장지간적상관성불명현。
The juvenile sea cucumber (Apostichopus japonicus Selenka) with initial body weight of (1 .00 ± 0 .05) g were reared in 18 plastic tanks supplemented with various ratios of microalgae to probiotics at a rate of 20 individuals per tank with triplication at water temperature of 11 .2~21 .0 ℃ for 80 days .During the culture period ,only alga mixture of Chlorella sp , Cylindrotheca sp and Chaetoceros sp at a same proportion was added to the tanks (Group A ) at a density of 2 .22 × 108 cells per tank ;only probiotics containing photosynthetic bacteria ,lactic bacteria ,and yeasts were added to the tanks at a density of 2 .22 × 108 individuals per tank (Group B);in the tanks (Group C) the algae and probiotics were supplemented at a ratio of 1∶1 ,that is ,1 .11 × 108 individuals per tank each ;the tanks in Group D and Group E were supplemented with alga mixture and probiotics at a ratio of 2∶1 ,and 1∶2 ;no any addition was in the tanks as a control group (Group K) .The results showed that the sea cucumber in Group A had the maximal specific growth rate (0 .16% /d) ,followed by the animals in Group E ,and the minimum in Group B (-0 .37% /d) ,with very significant difference between Group A and Group B ,and between Group E and Group B (P <0 .01) .The higher ammonia and active phosphorus levels in the water ,lower activities of acid phosphatase (ACP) and catase (CA T ) in the coelomic fluids and the least amount of V ibrio sp in the intestines were observed in the sea cucumber in Group B ,in which there were higher nitrite levels , higher activities of ACP and CAT in the coelomic fluids and more amount of Vibrio sp in the intestines . There was no significant relationship between activities of the digestive enzymes in the intestines and the growth in the sea cucumber in the experiment .The ecological functions and supplemental pattern (optimal ratio and time) of the microalgae and probiotics are discussed in the sea cucumber culture ponds in detail .