where k (M− 2 s− 1) can be determined from the
in the pH range 2 to 5, from 5 to 40 °C and 0.01 to 1 M.The effect of pH and ionic strength on the reaction suggest that the rates are due to
where H2A = H2CrO4, HA = HCrO4, H2B = H2SO3 and HB = HSO3. The overall rate expression over the investigated pH range can be determined from
k=kH2A–H2B(αH2A)(αH2B)2+kHA–H2B(αHA)(αH2B)2+kH2A–HB(αH2A)(αHB)2
with kH2A−H2B = 5.0 × 107, kHA–H2B = 1.5 × 106 and kH2A–HB = 6.7 × 107.Fe(III) in the range 1.5 to 20 μM exerts a small catalytic effect on the reaction and significantly lowers the initial concentration of Cr(VI) compared to the nominal value. Contrary to Fe(III), formaldehyde (20 to 200 μM) reacts with S(IV) to form the hydroxymethanesulfonate adduct (CH2OHSO3), which does not react with Cr(VI). Major cations Mg2+ and some minor elements such as Ba2+ and Cu2+ did not affect the rates. The application of this rate law to environmental conditions suggest that this reaction may have a role in acidic solutions (aerosols and fog droplets). This reaction becomes more important in the presence of high Fe(III) and low HMS concentrations, contributing to affect the atmospheric transport of chromium species and the distribution of redox species of chromium, which reach surface water from atmospheric depositions.  相似文献   

13.
The Biology of Upogebia pusilla (PETAGNA) (Decapoda, Thalassinidea)     
Peter C.  Dworschak 《Marine Ecology》1987,8(4):337-358
Abstract. The distribution of the thalassinidean shrimp Upogebia pusilla was studied at four sites in the North Adriatic Sea: 1) a tidal flat in the lagoon of Grado, 2) a tidal flat at Lido di Staranzano near the mouth of the Isonzo, 3) a mud flat seawards of a salt marsh in a protected bay north of Rovinj, and 4) a sublittoral station in 6m depth near Aurisina. Information on grain size distribution, organic content, amount of debris, redox profiles and pH of sediment as well as temperature and salinity is given. Density, as determined by hole counts and a hole: burrow relationship derived from resin casting, generally increased with increasing water depth in the intertidal. The upper limits ranged between +10cm (Rovinj) and -20cm (Grado); densities between mean water and low water level varied strongly due to microtopography and macrophyte cover. Maximum densities in the intertidal ranged from 189 (Grado) to 2420 (Rovinj, juveniles) animals m2. Shrimp density at the sublittoral station ranged between 80 and 230 m"2. The zonation of the Upogebiidae and Callianassidae with respect to environmental parameters is discussed.  相似文献   

14.
Pleistocene Ross seal (ommatophoca Rossi) from New Zealand (note)     
Judith E. King 《新西兰海洋与淡水研究杂志》2013,47(4):391-397
A fossil seal jaw from the Early Pleistocene (Wanganui Series; Hautawan Stage) of Napier, New Zealand, is identified as that of an Ommatophoca rossi juvenile of less than 1.8 m body length.  相似文献   

15.
The Biology of Upogebia pusilla (PETAGNA) (Decapoda, Thalassinidea)     
Peter C.  Dworschak 《Marine Ecology》1988,9(1):51-77
Abstract. Populations of the thalassinidean shrimp Upogebia pusilla were studied on tidal flats in the Northern Adriatic Sea. Biometric analysis showed a sexual dimorphism, especially in propodus size. Size frequency distributions revealed the presence of large animals during all seasons; recruitment by juveniles occurred in autumn. Moult intervals and moult increments were determined in the laboratory and used to generate growth curves which were compared with those calculated from size frequency distributions. The life span of U, pusilla is over 5 years. Ovigerous females occurred between March and September. Egg numbers were high in spring, lower in summer and increased with body size. The incubation time of embryos was 35 days; a female produces an estimated number of three egg batches during the breeding season. A total annual production of 994 kJ was estimated for a theoretical population of 100 animals; 13.5 % is spent for somatic growth, 31 % for egg production of females, and 55.2% is lost as exuviae. The population structures, growth and breeding patterns, as well as embryonic and larval development within the Upogebiidae and Callianassidae are discussed.  相似文献   

16.
17.
18.
Leathery turtle (reptilia: Chelonia) in Foveaux Strait (note)     
D. Eggleston 《新西兰海洋与淡水研究杂志》2013,47(3-4):522-523
Further records of the leathery turtle, Dermochelys coriacea (Linnaeus), augment earlier records and perhaps indicate that this species may be a regular visitor.  相似文献   

19.
Juvenile form of the New Zealand turbot Colistium nudipinnis (Waite) (Pisces: Heterosomata: Rhombosoleinae) (note)     
J. A. Colman 《新西兰海洋与淡水研究杂志》2013,47(4):575-579
A juvenile (26 mm) specimen of the New Zealand turbot Colistium nudipinnis (Waite) is figured and described. Differences between the juvenile and adult forms, and characters distinguishing juvenile C. nudipinnis from the young of other New Zealand species of flatfish, are noted.  相似文献   

20.
波令-阿勒罗德间冰期时期西南印度夏季季风降雨的变化性     
Ashish Sinha  徐明芝 《海洋地质前沿》2006,22(5):15-17
北方春季时期印度次大陆和西藏高原的差异性增热吸引了印度洋的潮湿空气穿越印度大陆,产生了世界上最显著的西南印度夏季季风(ISM)体系(Webster,1987)。世界上大约25%的人口受到这种季节降雨的影响。20世纪60年代末期,印度约150万人死于连续3年的季风失常(重大灾害数据库,2005)  相似文献   

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1.
渤海裸甲藻和链状亚历山大藻的麻痹性贝毒毒素分析   总被引:1,自引:0,他引:1  
目的:分析渤海裸甲藻(Gymnodinium sp.)和链状亚历山大藻(Alexandrium catenella)的麻痹性贝毒毒素,为渤海天津海域的赤潮研究积累基础数据。方法:通过实验室培养裸甲藻和链状亚历山大藻,选取对数生长期、平台生长期的裸甲藻以及平台生长期的链状亚历山大藻,利用高效液相色谱法(HPLC)对这两种微藻进行麻痹性贝毒(PSP)毒素分析。结果:裸甲藻细胞内不含有麻痹性贝毒(PSP);链状亚历山大藻细胞内含有C毒素和GTX1-4毒素,该微藻每个细胞毒素含量约为10.81 fmol/cell。结论:裸甲藻细胞内虽不含有麻痹性贝毒(PSP),但不能排除其含有其它毒素的可能。链状亚历山大藻细胞内含有麻痹性贝毒(PSP),属于有毒微藻,需要对其进行密切监测。  相似文献   

2.
福建漳州海域麻痹性贝毒的污染状况调查   总被引:3,自引:0,他引:3  
王雪虹  宋振荣 《台湾海峡》2006,25(4):478-483
本文通过对漳州海域的养殖区栉孔扇贝扣僧帽牡蛎为期1a的麻痹性毒素(PSP)污染状况的调查分析,以了解贝类海产品的安全性.贝毒测定按照AOAC小白鼠法进行,利用高效液相色谱(HPLC)进行贝毒成分分析.结果表明:漳州海域的栉孔扇贝为该海域轻微PSP染毒贝类,含量为1.83~3.23MU/g;漳浦古雷和东山铜陵的栉孔扇贝样品检出率分别为66.7%和16.7%.高效液相色谱分析表明,样品中PSP成分为B1、GTX1/4、GTX2/3及STX和C毒素.漳州海域贝类PSP含量很低,未超出安全食用标准;但毒素分布存在季节差异,春季检出率较高.因此有针对性的加强贝毒监测非常必要.  相似文献   

3.
麻痹性贝毒 (ParalyticShellfishPoisoning ,PSP)毒素由石房蛤毒素 (saxitoxin ,STX)及其衍生物组成 ,目前已发现 2 0余种 ,在赤潮研究、分子生物学和神经生物学基础研究、医药、军事防化等方面都有应用潜力 [其结构、类型和应用见本集刊王云峰等 (2 0 0 3 )“麻痹性贝毒毒素的  相似文献   

4.
麻痹性贝毒 (ParalyticShellfishPoisoning ,PSP)毒素由石房蛤毒素 (saxitoxin ,STX)及其衍生物组成 ,目前已发现 2 0余种 ,在赤潮研究、分子生物学和神经生物学基础研究、医药、军事防化等方面均有应用潜力。由于PSP毒素的稀有来源和国际社会对STX交易的禁止 ,限制了国内PSP毒  相似文献   

5.
栉孔扇贝体内麻痹性贝毒的累积与排出过程研究   总被引:9,自引:1,他引:9       下载免费PDF全文
通过室内摄食实验,研究了栉孔扇贝(Chlamys farreri)对麻痹性贝毒(PSP)产毒藻的敏感性及其累积和排出毒素的特征.有毒微小亚历山大藻(Alexandrium minutum)在短时间内可对栉孔扇贝的摄食有一定的抑制作用,且投喂毒藻的浓度越大,对摄食作用的抑制越明显.栉孔扇贝对PSP贝毒的累积能力很强,实验中,48 h后内脏累积毒素就高达5000μg STXeq100g-1,但其毒素排出速率较慢,在24d解毒阶段后内脏中的毒素还没有下降至国际贝毒食用安全标准水平的80μg STXeq 100g-1.各毒素组成比在整个累积与排除过程中有较大变化,GTX1,GTX4在累积阶段比例下降,同时GTX2,GTX3比例上升;内脏中GTX2:GTX3的比值逐渐增加.毒藻中PSP贝毒毒素组成和贝体中PSP贝毒毒素组成之间的主要差别是GTX4含量的减少和GTX1含量的升高;而扇贝粪便中的毒素组成却与对数生长期的毒藻极为接近.  相似文献   

6.
麻痹性贝毒PSP在紫贻贝体内的累积、转化与排出   总被引:13,自引:2,他引:13  
于1998年9月在青岛鲁迅公园附近礁石区采集紫贻贝(Mytilus edulis),采用实验室培养的方法,初步研究了塔玛亚历山大藻(Alexandrium tamarense,ATHK)产生的麻痹性贝毒(Paralytic Shellfish Poison,PSP)在其体内累积、转化与排出的规律。结果表明,在累积实验阶段,紫贻贝内脏的和肌肉中的PSP毒素含量均随实验时间的延长而逐渐增加,累积实验结束时,平均每只贝体内的PSP毒素含量为13.40nmol,毒性水平为12.24ugSTXEq/100g,紫贻贝内脏中的毒素含量远远高于肌肉,内脏中PSP毒素占贝体内PSP毒素总量的97.5%。在8天的排出实验阶段,贝体内的PSP毒素总量呈下降趋势,实验结束时,PSP毒素共排除了约50%,每天排除率约为9%。  相似文献   

7.
通过检测深圳沿岸海域7种贝类的重金属、麻痹性贝毒(PSP)和腹泻性贝毒(DSP)含量,了解其食用安全性.严格按照国家标准进行检测,采用SPSS 20.0对数据进行Kruskal-Wallis H检验和方差分析.结果表明:各种重金属和贝类毒素在样品中均有检出,汞污染状况良好;铜含量范围为0.52~109.65 mg/kg,超标率为13.67%;铅含量范围为0.01~3.60 mg/kg,超标率为68.35%;镉含量范围为0.015~7.807 mg/kg,超标率为53.96%.PSP和DSP检出率为100%,PSP含量范围为0.30~34.23 ug/100 g;DSP含量范围为1.88~38.41 ug/100 g.总体看来,样品铅、镉超标严重,不同种类贝类重金属含量具有差异且贝类毒素检出率较高,应引起有关部门的重视,加强该海域监测工作.  相似文献   

8.
2004年~2005年在长江口及邻近海域曾发生有毒赤潮13起,约占赤潮总数的15%,引发赤潮的有毒赤潮生物包括链状亚历山大藻(Alexandrium catenella)、红色裸甲藻(Gymnodinium sanguineum)、米氏凯伦藻(Karenia mikimotoi)和环状异甲藻(Heterocapsa circularisquama),其中曾造成严重危害的有米氏凯伦藻和环状异甲藻。通过连续2年的四季本底调查结果表明,该海域存在多种有毒藻类,主要包括产麻痹性贝毒(PSP)的链状亚历山大藻、塔玛亚历山大藻(Alexandrium tamarense),产腹泻性贝毒(DSP)的具尾鳍藻(Dinophysis caudata)、倒卵形鳍藻(Dinophysis fortii);产记忆缺失性贝毒(ASP)的尖刺拟菱形藻(Pseudo-Nitzschia pungens)、多列拟菱形藻(Pseudo-Nitzschia multiseries)和多纹拟菱形藻(Pseudo-Nitzschia multistriata);其它有毒有害藻类包括红色裸甲藻、环状异甲藻、米氏凯伦藻等。有毒藻类种类5、6月份较多,产腹泻性贝毒(DSP)和产记忆缺失性贝毒(ASP)的有毒藻类常年均在该海域出现,这些有毒有害藻类多数密度并不高。与有毒藻类监测同步开展了赤潮毒素检测,长江口贝类赤潮毒素检出时段主要集中在5~6和8~9月份,PSP和DSP检出率分别在5%和12%左右,敏感种类为养殖的紫贻贝,未检出记忆缺失性贝毒。针对目前赤潮的危害中由有毒藻类和赤潮毒素造成的危害较大,建议在长江口贝类养殖海域开展的有毒藻类监测计划,以确保贝类水产品食用安全。  相似文献   

9.
根据2009-04—2010-02隔月6个航次桑沟湾9个调查站位贝类养殖区有机氯(OCPs)、有机磷(OPPs)农药残留和麻痹性贝毒(PSP)的调查资料,分析了它们在该海域海水中、表层沉积物中和主要贝类(栉孔扇贝、太平洋牡蛎和菲律滨蛤仔)体内的含量水平,就农药残留及贝毒污染对海洋环境质量的影响进行综合评价和类别划分,并对主要食用贝类中农药残留和贝毒的暴露水平进行健康风险评估。结果表明,桑沟湾贝类养殖区海水质量、沉积物质量和养殖贝类质量水平范围为1~2级,平均分别为2级、1级和1级,养殖生态环境综合质量水平为2级;总体上,该海域海洋环境综合质量处于良好水平,贝类产区生态环境质量为1类区(清洁区)。即该海域农药残留及贝毒污染对海洋环境质量影响较小或无明显影响。另外,针对食用桑沟湾贝类水产品的消费人群进行了农药残留及贝毒污染的健康风险评估,结果表明调查人群食用贝类中OCPs中的HCHs和DDTs、OPPs中的马拉硫磷和甲基对硫磷、PSP的日摄入量分别为0.75,2.11,0.19,0.09和1.22μg/(人·d),其摄入量低于ADI的推荐限值,因此桑沟湾主要食用贝类中农药残留及贝毒污染的健康风险处于安全范围。  相似文献   

10.
欧洲某些鞭毛藻对海洋生物的毒害,大致可分为由金黄曲沟藻(Gyrodinium aurcolum)引起的天然或养殖的海洋生物的毙死;由渐尖鳍藻(Dinophysis acuminata)引起的贻贝毒化和由塔马拉膝沟藻(Gonyaulax tamarensis)的游动细胞和休眠胞囊引起的麻痹性贝毒(PSP)和下痢性贝毒(DSP)。  相似文献   

11.
Alterations to nomenclature for two common intertidal New Zealand ‘top shells’ necessitated by re‐examination of type material have been confused by ambiguities in the way the alterations were first presented. We draw attention to recent misinterpretations and clarify the nomenclature. Condensed synonymies that indicate names used for each species during the interregnum are given, allowing papers dealing with these trochids to be read without uncertainty as to which species were really meant by the authors.  相似文献   

12.
The rates of the reduction of Cr(VI) with S(IV) were measured in deaerated NaCl solution as a function of pH, temperature and ionic strength. The rates of the reaction were found to be first order with respect to Cr(VI) and second order with respect to S(IV), in agreement with previous results obtained at concentrations two order higher than the present study. The reaction also showed a first-order dependence of the rates on the concentration of the proton and a small influence of temperature with an apparent energy of activation ΔHapp of 22.8 ± 3.4 kJ/mol. The rates were independent of ionic strength from 0.01 to 1 M. The rate of Cr(VI) reduction is described by the general expression
−d[Cr(VI)]/dt=k[Cr(VI)][S(IV)]2
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