中国农学通报
中國農學通報
중국농학통보
CHINESE AGRICULTURAL SCIENCE BULLETIN
2013年
11期
50-54
,共5页
谢文军%孙同秋%陈昕%宋颖
謝文軍%孫同鞦%陳昕%宋穎
사문군%손동추%진흔%송영
扇贝%海水水质%重金属%富集
扇貝%海水水質%重金屬%富集
선패%해수수질%중금속%부집
Argopectens irradias%sea water quality%heavy metal%bioconcentration
海水水质直接影响养殖业发展及海洋产品品质,受到越来越多关注。为了解扇贝养殖区域海水水质状况及对扇贝品质的影响,采用分期取样的方法,在莱州湾某扇贝养殖区采集表层海水样品,以非养殖区为对照,分析其pH、营养盐、COD、Cu及Zn含量;同时,采集扇贝幼体、成体,分析Cu、Zn在闭壳肌(贝柱)中蓄积。结果表明:研究区域海水中无机氮含量较高,接近0.30 mg/L,不同时间其含量和组成差异显著,10月海水中无机氮以硝态氮为主,含量极显著高于以氨态氮为主的6月(P<0.01)。不同时间,不同采样点海水中无机磷含量均小于0.02 mg/L,差异不显著。COD、Cu及Zn含量均为6月显著高于10月(P<0.05),未超出二类海水水质标准值。COD、Cu及Zn三者间呈极显著正相关(P<0.01),表明它们可能来自同一污染源。扇贝对Cu、Zn的富集能力较强,对Zn富集能力大于Cu。尽管扇贝闭壳肌中Cu、Zn含量在相关标准值之内,但Cu、Zn富集程度分别达到了1.06、0.821,所以,扇贝养殖过程中Cu、Zn等重金属在体内蓄积应引起更多关注。
海水水質直接影響養殖業髮展及海洋產品品質,受到越來越多關註。為瞭解扇貝養殖區域海水水質狀況及對扇貝品質的影響,採用分期取樣的方法,在萊州灣某扇貝養殖區採集錶層海水樣品,以非養殖區為對照,分析其pH、營養鹽、COD、Cu及Zn含量;同時,採集扇貝幼體、成體,分析Cu、Zn在閉殼肌(貝柱)中蓄積。結果錶明:研究區域海水中無機氮含量較高,接近0.30 mg/L,不同時間其含量和組成差異顯著,10月海水中無機氮以硝態氮為主,含量極顯著高于以氨態氮為主的6月(P<0.01)。不同時間,不同採樣點海水中無機燐含量均小于0.02 mg/L,差異不顯著。COD、Cu及Zn含量均為6月顯著高于10月(P<0.05),未超齣二類海水水質標準值。COD、Cu及Zn三者間呈極顯著正相關(P<0.01),錶明它們可能來自同一汙染源。扇貝對Cu、Zn的富集能力較彊,對Zn富集能力大于Cu。儘管扇貝閉殼肌中Cu、Zn含量在相關標準值之內,但Cu、Zn富集程度分彆達到瞭1.06、0.821,所以,扇貝養殖過程中Cu、Zn等重金屬在體內蓄積應引起更多關註。
해수수질직접영향양식업발전급해양산품품질,수도월래월다관주。위료해선패양식구역해수수질상황급대선패품질적영향,채용분기취양적방법,재래주만모선패양식구채집표층해수양품,이비양식구위대조,분석기pH、영양염、COD、Cu급Zn함량;동시,채집선패유체、성체,분석Cu、Zn재폐각기(패주)중축적。결과표명:연구구역해수중무궤담함량교고,접근0.30 mg/L,불동시간기함량화조성차이현저,10월해수중무궤담이초태담위주,함량겁현저고우이안태담위주적6월(P<0.01)。불동시간,불동채양점해수중무궤린함량균소우0.02 mg/L,차이불현저。COD、Cu급Zn함량균위6월현저고우10월(P<0.05),미초출이류해수수질표준치。COD、Cu급Zn삼자간정겁현저정상관(P<0.01),표명타문가능래자동일오염원。선패대Cu、Zn적부집능력교강,대Zn부집능력대우Cu。진관선패폐각기중Cu、Zn함량재상관표준치지내,단Cu、Zn부집정도분별체도료1.06、0.821,소이,선패양식과정중Cu、Zn등중금속재체내축적응인기경다관주。
Seawater quality can affect sea fishing and seafood quality, and thus has received more and more concerns. In order to know the seawater quality in Argopectens irradias fishing area and the influence of seawater on the quality of Argopectens irradias, the quality of surface seawater samples collected from an Argopectens irradias fishing area and un-fishing area in Laizhou Bay at different times was assessed, involved pH and nutrients, chemical oxygen demand (COD), Cu and Zn concentrations. Results showed that, in study area, the inorganic N concentration was high relatively, and approximately reached 0.30 mg/L. Nitrate-N was the main component of inorganic N of seawater in October, which was significantly higher than that in June in which the main inorganic N was ammonia-N (P<0.01). In different sampling sites, the inorganic P concentrations at different times were all less than 0.02 mg/L, and changed insignificantly. COD, Cu and Zn concentrations were all less than the value of the second grade seawater standard, and were significantly higher in October than that in June (P<0.05). The significant positive correlation among COD, Cu and Zn indicated that they probably came from the same polluted source (P<0.01). Argopectens irradias had high bioconcentration capability of Cu and Zn, and the capability of Zn was greater than that of Cu. Although the concentrations of Cu and Zn were both less than the associated standard values, the accumulation extents of Cu and Zn were 1.06 and 0.821, respectively. Therefore, heavy metals accumulation in Argopectens irradias should be aroused more concerns in future.