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971.
本项目组于1993年7月至8月,对青藏高原的地壳运动进行第1期监测,并用广播星历进行解算.1994年秋,又使用经武汉测绘科技大学改进到微机上的美国麻省理工学院研制的GAMIT精密定位软件和NGS(NationalGeodeticSurvey)精密星历,重新进行解算.解算结果表明,在400多公里范围内,观测两个时段平均基线的重复性达到几毫米的高精度,相对精度优于3.10×10(-8),与广播星历解相比,基线重复精度提高了5~12倍. 相似文献
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973.
黑龙江省东部饶河杂岩的就位时代与东北东部中生代构造演化 总被引:14,自引:22,他引:14
黑龙江省东部饶河杂岩由含放射虫深海沉积岩以及镁铁质的熔岩和侵入岩组成,并被视为大洋壳的残片。该杂岩被晚期蛤蚂河和太平村花岗岩侵入。锆石U-Pb年龄结果表明,上述两花岗岩岩体均形成于早白垩世,其中蛤蚂河岩体形成于131、124和~115Ma三个阶段,太平村岩体形成于111~114Ma左右。饶河杂岩中辉长岩的锆石U-Pb年龄为166±1Ma,深海沉积岩中最晚出现的放射虫的时代为160~150Ma,显示饶河杂岩的就位应发生在150~131Ma的晚侏罗世—早白垩世,古地磁资料显示本区自晚三叠世—侏罗纪有明显的从低纬度向高纬度的北移现象:从而表明在晚侏罗世—早白垩世及以前该区存在太平洋板块的俯冲-走滑作用。岩石学研究显示,两花岗岩岩体中均存在岩浆结晶成因的堇青石,并具有过铝质花岗岩的特点,为典型的来源于沉积岩部分熔融形成的S型花岗岩。Hf同位素测定发现,这些花岗岩中的锆石具有较高的~(176) Hf/~(177)Hf同位素比值和较正的ε_(Hf)(t)值,以长英质地壳为源岩的Hf同位素模式年龄为500~780Ma,说明其源岩应为新元古代—显生宙新增生的地壳物质,从而反映在晚侏罗世—早白垩世以前本区曾发生过显著的地壳抬升与风化剥蚀。 相似文献
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976.
Correlation, multiple regression, and path analyses were used to investigate the relationships between body weight and three other morphological traits in juvenile Japanese sea cucumbers Apostichopus japonicus. We measured live body weight(BW), body length(BL), numbers of papillae(NP), and numbers of tube feet(NF) at 60, 80, 100, and 130 days post-hatching(dph). We calculated path correlation coe cients, correlation indices( R~2), and coe cients of determination with BW as the dependent variable and the other morphological traits as independent variables. The coe cient of variation for BW was high across all age groups, and all measured morphological traits were significantly correlated( P 0.01). BL had the greatest direct ef fect on BW across all age groups(60 dph, 0.526; 80 dph, 0.404; 100 dph, 0.620;and 130 dph, 0.681), while NF had the greatest indirect ef fect on BW across all age groups(60 dph, 0.528;80 dph, 0.452; 100 dph, 0.666; and 130 dph, 0.603). Regression analyses between morphological traits and BW indicated that R 2 was greater than 0.85 only in the 100-dph specimens. The indirect ef fects of the other measured morphological traits on BW were age-dependent. The optimal regression equations,as determined with stepwise regression, were, for 60-dph specimens: BW_(60)=10~((-3.04+0.092 BL+0.014 NP+0.014 NF))( R~2 =0.632); for 80-dph specimens: BW _(80)=10~((-3.035+0.056 BL+0.017 NP+0.02 NF))( R~2 =0.686); for 100-dph specimens:BW_(100) =10~((-3.742+0.069 BL+0. 633*l g( NP)+0. 464*l g( NF)))( R~2 =0.893); and for 130-dph specimens: BW_(130)=10~((-2.472+0.065 BL+0.012 NP))( R~2 =0.774). Our work clarified the correlation between various morphological traits and body weight of a commercially-important sea cucumber species( A. japonicus). Our predictive models for body weight might be useful for the aquaculture and selective breeding of A. japonicus. These models might also provide theoretical support for the indirect selection of traits that are di cult to select directly. 相似文献
977.
978.
Wang?XiulinEmail author Shan?Baotian GE?Ming Zhang?Lei Zhu?Chenjian Han?Xiurong 《中国海洋大学学报(英文版)》2002,1(1):71-79
The growth of Chlorella marine, Nannochloris oculate, Pyramimonaos sp., Platymonas subcordiformis and Phaeodactylum tricornutum exposed to chlorobenzene, 1,2-dichlorobenzene, 1,2,3,4-tetrachlorobenzene and pentachlorobenzene was tested. The Boltzman
equation was used to describe organism growth. The time course for uptake of hydrophobic organic chemicals (HOCs) by aquatic
organisms was expressed by incorporating growth and, if desired, the effect of metabolism into the HOC bioconcentration process.
The probability of any given concentration of HOCs in the organisms causing a specified toxic endpoint was expressed with
a modified Weibull distribution function. The combined bioconcentration and probability equations were tested with data for
time course of incubation of algae exposed to chlorinated benzenes (CBs). A set of parameters, including the uptake rate constant
k
1, the elimination rate constant k
2 and thereafter the bioconcentration factor on a dry weight basis, BCF
D, the critical HOC concentration in the organism resulting in a specified toxic endpoint, C
A
*
, and the spread factor, S, could be obtained by fitting only experimental data for percent growth inhibition(%)-time-CB exposure concentration. The
average coefficients of variation within CBs were 15.2% for BCF
D, 21.0% for k
1, 18.3% for k
2, 8.1% for C
A
*
and 9.7% for S. The variability in toxicity (such as EC10, EC50, EC90) derived from the model equations agreed well with those experimentally observed. 相似文献
979.
980.