渔业科学进展
漁業科學進展
어업과학진전
MARINE FISHERIES RESEARCH
2015年
4期
44-50
,共7页
过锋%陈聚法%张艳%陈碧鹃
過鋒%陳聚法%張豔%陳碧鵑
과봉%진취법%장염%진벽견
营养盐%营养状况%有机污染状况%黄岛区近岸海域
營養鹽%營養狀況%有機汙染狀況%黃島區近岸海域
영양염%영양상황%유궤오염상황%황도구근안해역
Nutrients%Nutritional status%Organic pollution condition%Offshore area of Huangdao District
利用2008–2013年水质调查资料,分析了青岛市黄岛区南部海域营养盐分布与变化特征,并采用营养指数(E)法和有机污染综合指数(A)法对该海域海水的营养状况和有机污染状况进行了评价。结果显示,(1)2012–2013年调查期间,无机氮含量范围为20.82–197.62μg/L,活性磷酸盐为4.52–52.91μg/L,COD 为0.39–1.25 mg/L。除个别站点活性磷酸盐含量超标外,其余站点活性磷酸盐含量以及全部站点无机氮和 COD 含量均符合二类海水水质标准要求。(2)调查海域无机氮以春季最高(86.42μg/L),秋季次之,夏季最低(38.59μg/L);活性磷酸盐以秋季最高(18.68μg/L),春季次之,夏季最低(9.10μg/L);COD 以夏季最高(0.962 mg/L),秋季次之,春季最低(0.682 mg/L)。(3)调查海域无机氮和 COD 含量2008–2011年呈逐年降低的变化趋势,2012年又有所增高;活性磷酸盐含量2008–2010年呈逐年降低的变化趋势,2010–2012年呈逐年增高的变化趋势。研究表明,调查海域海水的营养水平较低,未达到富营养化水平,发生赤潮的可能性较小。调查海域水质状况良好,未受到有机污染。
利用2008–2013年水質調查資料,分析瞭青島市黃島區南部海域營養鹽分佈與變化特徵,併採用營養指數(E)法和有機汙染綜閤指數(A)法對該海域海水的營養狀況和有機汙染狀況進行瞭評價。結果顯示,(1)2012–2013年調查期間,無機氮含量範圍為20.82–197.62μg/L,活性燐痠鹽為4.52–52.91μg/L,COD 為0.39–1.25 mg/L。除箇彆站點活性燐痠鹽含量超標外,其餘站點活性燐痠鹽含量以及全部站點無機氮和 COD 含量均符閤二類海水水質標準要求。(2)調查海域無機氮以春季最高(86.42μg/L),鞦季次之,夏季最低(38.59μg/L);活性燐痠鹽以鞦季最高(18.68μg/L),春季次之,夏季最低(9.10μg/L);COD 以夏季最高(0.962 mg/L),鞦季次之,春季最低(0.682 mg/L)。(3)調查海域無機氮和 COD 含量2008–2011年呈逐年降低的變化趨勢,2012年又有所增高;活性燐痠鹽含量2008–2010年呈逐年降低的變化趨勢,2010–2012年呈逐年增高的變化趨勢。研究錶明,調查海域海水的營養水平較低,未達到富營養化水平,髮生赤潮的可能性較小。調查海域水質狀況良好,未受到有機汙染。
이용2008–2013년수질조사자료,분석료청도시황도구남부해역영양염분포여변화특정,병채용영양지수(E)법화유궤오염종합지수(A)법대해해역해수적영양상황화유궤오염상황진행료평개。결과현시,(1)2012–2013년조사기간,무궤담함량범위위20.82–197.62μg/L,활성린산염위4.52–52.91μg/L,COD 위0.39–1.25 mg/L。제개별참점활성린산염함량초표외,기여참점활성린산염함량이급전부참점무궤담화 COD 함량균부합이류해수수질표준요구。(2)조사해역무궤담이춘계최고(86.42μg/L),추계차지,하계최저(38.59μg/L);활성린산염이추계최고(18.68μg/L),춘계차지,하계최저(9.10μg/L);COD 이하계최고(0.962 mg/L),추계차지,춘계최저(0.682 mg/L)。(3)조사해역무궤담화 COD 함량2008–2011년정축년강저적변화추세,2012년우유소증고;활성린산염함량2008–2010년정축년강저적변화추세,2010–2012년정축년증고적변화추세。연구표명,조사해역해수적영양수평교저,미체도부영양화수평,발생적조적가능성교소。조사해역수질상황량호,미수도유궤오염。
The current study analyzed the distributional and variational feature of nutrients of seawater in the southern offshore area of Huangdao District based on the environmental data collected by surveys from 2008 to 2013. The methods of Eutrophication Index (E) and Organic Pollution Comprehensive Index (A) were used to assess nutritional status and organic pollution condition of seawater. Based on the surveys from 2012 to 2013, the concentrations of dissolved inorganic nitrogen(DIN), dissolved inorganic phosphate(DIP) and chemical oxygen demand (COD) varied within 20.82-197.62 μg/L, 4.52-52.91 μg/L and 0.39-1.25 mg/L, respectively. Except one station that the concentration of DIP was above the standard limit, all other concentration including DIP, DIN and COD met the second class of national standard. In three seasons, the highest concentration of DIN (86.42 μg/L) was in the spring, and the lowest (38.59 μg/L) was in the summer. The highest concentration of DIP (18.68 μg/L) was in the autumn, and the lowest (9.10 μg/L) was in the summer. The highest concentrations of COD (0.962 mg/L) was in the summer, and the lowest (0.682 mg/L) was in the spring. The concentrations of DIN and COD was gradually decreased from 2008 to 2011 and then was increased in 2012. The concentration of DIP was gradually decreased from 2008 to 2010 and then was gradually increased from 2010 to 2012. The seawater of the surveyed area was at oligotrophic level, showing the low possibility of red tide occurrence. The water quality in the surveyed area was good, indicating that seawater was not polluted by organic matters.