贵州黔灵山公园半野生的猕猴的种群动态

科学分析动物种群增长动态,合理确定环境容量是管控城市半野生动物种群激增危害的根本途径。本文对贵州贵阳黔灵山公园半野生猕猴种群特征、种群增长、环境容纳量以及猴群对公园的危害进行了研究分析。结果表明：（1）较之野生种群,园内栖息种群密度高、猴群大。现有8个稳定猴群共计1067只[最小群：47只;最大群：226只,平均：（133±67）只],总体雌雄性比为1.33;全区种群密度约达251只/km²,但猴群主要栖息于游道及其周边,导致主分布区密度高达 2134只/km2;（2）种群增长迅速、繁殖力旺盛。自1992年以来,种群呈指数型增长（年均增长率为8.08%,增长函数为y=30.6789*exp[(x-1987)/8.7894+ 64.0193),当前种群总体年龄结构为成年猴>青年猴>幼年猴,虽青幼个体数量较成年个体少,但成年雌雄性比达到1.50,性成熟个体较多,有效种群数大,仍保持旺盛的繁殖力;（3）种群Logistic增长曲线（y=792/(1+2.8495E+183*exp-0.2104x）表明园内环境容量（K值）为792只,与该区猕猴伤人事件频率曲线进入高位平台期所对应的种群数量接近。文中还对猴群栖息对当地植物多样性造成的影响进行了调查。调查监测表明,种群过大且集中栖息导致公园内生物多样性破坏、人猴冲突、公共健康隐患等一系列问题产生,建议应通过节育、分流等相关措施,将种群数量控制在K/2即400只左右为宜。本文可为黔灵山公园猕猴保护管理及其他城市野生动物管理提供参考。     

小麦各生育期的两种麦蚜种群动态研究

高、中氮肥条件下二叉蚜的种群曲线为"J"形和"S"形、其数学模型依次为y＝35.7446e~0.1072x和y=;高、中氮肥条件下长管蚜的种群曲线均为"凸"形,5月3日即灌浆期前的种群数学模型依次为y＝16.6515e~0.199x和=18.752e~0.201x,5月3日后种群数学模型依次为y＝1156432e~-0.1977x和y＝6545903ee~－0.2233x其结果可为两种麦蚜的预测预报提供科学依据。     

棉田绿盲蝽种群密度的调查方法

本文比较研究了棉田绿盲蝽Apolygus lucorum(Meyer-Dür)种群的调查方法。全株调查法中,目测法调查到的绿盲蝽种群密度最高,显著高于扫网法和盆拍法。局部调查法发现,蕾上的绿盲蝽种群数量显著高于叶片和花上;蕾上种群数量与整株密度之间呈显著正相关关系(y=1.18 x+3.69)。间接调查法表明:在苗期和蕾期,叶片受害等级和绿盲蝽种群密度之间呈显著正相关关系(苗期:y=25.28 x+8.20;蕾期:y=43.99 x+27.58)。     

Sampling techniques for estimating the population density of Apolygus lucorum in cotton fields

本文比较研究了棉田绿盲蝽Apolygus lucorum(Meyer-Dür)种群的调查方法.全株调查法中,目测法调查到的绿盲蝽种群密度最高,显著高于扫网法和盆拍法.局部调查法发现,蕾上的绿盲蝽种群数量显著高于叶片和花上;蕾上种群数量与整株密度之间呈显著正相关关系(y=1.18x+3.69).间接调查法表明:在苗期和蕾期,叶片受害等级和绿盲蝽种群密度之间呈显著正相关关系(苗期:y=25.28x+8.20;蕾期:y=43.99x+27.58).     

海南南湾猕猴种群增长的研究

对海南南湾猕猴１９６５～１９９４年间的种群动态和雌性猴生命表的研究表明,该种群年均增长率为９．７％,１９８７年后种群增长率和繁殖率有所下降,猴群中非成年猴比例已不足５０％。半驯化雌性猴的逐年存活率到１７岁仍达０．５８,通过对存活曲线和寿命期望曲线的分析,南湾雌猴寿命可达３３～３８岁。婴猴死亡率较低、成年猴死亡率较高,存活曲线属Ⅰ形即凸形。研究表明静态生命表编制方法不适于灵长类,在建立标准化存活曲线时应考虑种群综合死亡系数。猕猴通过存活率、繁殖率、群体结构变化等社群调节机制达到种群平衡。对南湾猕猴近年内每年可捕捉利用１００～１５０只左右,１０岁以上的猴应占５０％以上,在不影响种群遗传多样性水平上,可适当多捕一些成年雄猴。     

维生素B12对萼花臂尾轮虫种群的影响

温度为15℃时,添加20,40,80和100μg/mL维生素B12后,萼花臂尾轮虫(Brachionuscalyciflorus)种群密度随时间增加而增长,其回归方程依次为:y=e(0.1757+0.2974x),y=4.6765x1.2079,y=7.7798x1.0175和y=e(0.6117+0.3469x),密度显著高于对照组(t=4.56,8.15,8.53和9.86;P1.4366,y=7.7461x1.6533,y=6.3611x1.7790和y=9.064x1.6872,对照为y=7.5902x1.50192。各添加组的密度均显著高于对照组(t值分别为16.12,10.17,5.83和5.86;P(0.1376+0.4395x),y=e(0.2032+0.4856x),y=3.4615x1.9522和y=e(0.0220+0.48074x)。对照组除了和20ng/mL组间没有统计差异外(t=0.34,P>0.05),其他各实验组密度显著高出对照组(t值分别为3.66,10.23和2.13)。最高混交率分别为18.18%,7.60%,18.18%和16.67%,对照为66.70%。最大卵雌比依次为0.70,1.90,0.91,1.09,对照组为0.95。       

松树内含物与松墨天牛种群数量的关系

对不同林分松墨天牛种群密度进行解剖调查,黑松为32.63头/株,马尾松为16.69头/株,湿地松为12.44头/株,黑松与湿地松之间差异显著;对黑松、马尾松、湿地松枝条及韧皮部中蛋白质、可溶性糖、水分、N、P、K、S、Cl、Ca、Mg、Cu、Zn、Fe、Mn、16种游离氨基酸和16种水解氨基酸进行测定,并与黑松、马尾松、湿地松上的松墨天牛种群数量(y)之间关系进行数学分析。蛋白质(x1)、可溶性糖(x2)与y的关系为y=-44.07-1.5601x1+6.9355x2,复相关系数为0.8374*;游离氨基酸与y的关系为y=63.24-1.1775x5-0.0680x11+0.1665x12-0.1257x15,复相关系数为0.9999**。x5为甘氨酸、x11为酪氨酸、x12为苯丙氨酸、x15为脯氨酸;水解氨基酸与y的关系为y=37.59-0.1146x10-0.5741x11+0.0112x15+0.1468x16,复相关系数R为0.9955**,x11为酪氨酸、x15为脯氨酸、x16为精氨酸、x10为亮氨酸;矿质元素与y的关系为y=-67.94+409.4696x3+37.4746x6-1004.4480x7+4.2958x8,复相关系数R为0.9826*,x3为K、x6为Ca、x7为Mg、x8为Cu。综合分析14种入选的内含物与y的关系为y=19.94+0.0114x2+0.0457x4-0.5317x5+62.5214x9,复相关系数R为0.9966**,x2为水解酪氨酸、x4为水解脯氨酸、x5为游离酪氨酸、x9为K,综合分析表明水解和游离的酪氨酸、水解脯氨酸和K的含量对松墨天牛种群有重要影响。     

广西龙虎山猕猴种群生态特征

１９８８～１９９５年,采用定点观察法和绝对计数与相对计数结合法对龙虎山猕猴种群生态作了调查研究。１９９０年核心区有猕猴１４群,５００只左右,猴群密度１．６群／ｋｍ２,种群密度５５．６只／ｋｍ２．猴群大小平均３３．８±２３．１（ｎ＝６）只。一般每隔４～５年分群一次,猴群群体年均增长率１４．８％,种群年均增长率为９．７％。猴群中成年猴性比为７．６±６．５（ｎ＝１２）,１～３岁组的性比为０．７４±０．６１（ｎ＝４）,群内未成年猴比例为６７．７±３．１％（ｎ＝１２）。发情交配期最早１１月１２日,最晚次年１月２０日,高峰期１２月上旬,持续３个月．产仔期最早４月１日,最晚８月１４日,高峰期５月上旬,持续时间４个半月．繁殖率４５．５％～１００％,平均７５．４±１３．２％（ｎ＝２１）。新生猴死亡率较低,新生猴性比（雌：雄）平均０．７４±０．３４（ｎ＝５）。     

树木生长势与松墨天牛种群密度及松材线虫发病程度关系

对不同生长势林区内的松墨天牛种群密度和松材线虫发病程度的研究表明,树木生长势（x）分别与松墨天牛种群密度（y）、松材线虫发病程度（z）呈负相关,其线性回归方程分别为：y=1793.771-16404.47x;z=31.80989-241.9274x,相关系数分别为r=-0.8319和r=-0.8770。而松墨天牛种群密度（y）与松材线虫发病程度（z）呈正相关,其线性回归方程为：y＝－407.0611＋70.51478z;相关系数为r=0.9864。     

风雨强度指数及其在棉铃虫种群数量变动分析中的应用

长期以来,风雨强度仅是个模糊概念。作者通过棉铃虫自然种群生命表的研究实践,认识到风雨的冲刮作用实质为两因子的迭加效应。提出了风雨强度的数学表示式I=RW,并应用于棉铃虫种群数量变动分析与预测预报中,得出风雨强度(x)与其所致的消亡率(y)的关系式为:二代卵y′=-2.0996+0.3704x,三代卵y′=-1.044+0.354x,四代卵y′=-2.6252+0.4506x,二代一龄虫y′=-0.5816+0.1996x,三代一龄虫y′=-0.0486+0.1329x,四代一龄虫y′=-0.2025+0.184x。     

Population ecology of rhesus monkeys (Macaca mulatta) at Nanwan Nature Reserve,Hainan, China

Rhesus monkeys (Macaca mulatta) at the Nanwan peninsula of Hainan Island, China, have been observed in the field for 25 years, and have been studied intensively for eight years, beginning in 1981. There were about 115 monkeys in 5 natural groups when the Nanwan Reserve was founded in 1965. From 1965 to 1984, the number of groups increased from 5 to 19, and the total population increased from 115 to 930 individuals, an annual population increase of 12.7%. From 1984 to 1987, the population continued a slower rate of increase (8.9%) to approximately 1200 monkeys in 20 groups. The home ranges of each monkey group at Nanwan varied from 0.16 to 0.72 km², with a mean and standard deviation of 0.37 ± 0.18. The size of the home range of the rhesus was affected by the quality of vegetation and rhesus population density. The average birth rate per year was 77.8 ± 13.9%, varying from 53.8% to 100% since 1978. From 1978, the birth rates of two food provisioned groups were higher in alternate years (x? = 91.7%) and lower in intervening years (x? = 68.8%; P = <0.01). A minority (26.5%) of females have given birth at 4 years of age, most at 5 years. The sex ratio of newborns in any one year varied from 0.3 to 3.5 males to females, with a mean and standard error of 1.09 ± 0.37 males to females.     

Management of individual body weight growth of infant squirrel monkey (Saimiri sciureus) in indoor breeding colony

We biometrically analyzed the body weight growth data of new-born squirrel monkeys, obtained during the nursing period from 0 to 12 weeks of age. Body weight (y in grams) could be expressed as a function of birth weight (a in grams) and age (x in weeks) by the following equation: y = a + b x, where b indicates growth rate. This equation corresponded significantly with actual growth curves (R2 = 0.96). The frequency distribution of b values was demonstrated to be abnormal distribution. This value was used to judge whether the body weight growth of each monkey was normal or abnormal. The lower control limit (LCL) was calculated by using a linear equation with the b value of 9.07 (M-1.25 x S.D.) and each birth weight. For the monkeys whose body weight was above the LCL during the first three weeks after birth, it was determined whether the frequency of weighings could be reduced from 13 to 7. Using the same animals, no significant difference was detected between the b value estimated from 13 measurements and that estimated from 7 measurements. Thus, from the standpoint of management's policy to save labor, the frequency of weighings could be reduced. A new daily routine has been established in our primate center to save labor by reducing the number of body weighings of the many infant monkeys. In the new program, newborn monkeys whose body weight is above the LCL are weighed only 7 times during the nursing period of 12 weeks, while those whose weight is below the LCL are weighed 8 to 13 times.     

裂叶沙参个体生长动态研究（1）：一个生长季地上部分的生长

在不同生境条件下的固定样地内,观察分析了裂叶沙参种群的地上部分在一个生长季的生长过程和物侯特点。生长于灌木群落下,裂叶沙参地上部分生物量生长（ｙ,ｇ）与时间（ｘ、ｄ）的关系可以用公式：ｙ＝０．２８７２－０．０１８７ｘ＋０．０００９ｘ＾２表示;地上各器官茎、叶、花枝、花芽、花和果的生物量（ｙ,克）与生长时间（ｘ,天）的关系可以用公式：ｙ＝ｂ０＋ｂ１ｘ＋ｂ２ｘ＾２表示。从４月１０日到８月１５日的速生期     

Specific metabolic rate, longevity and "Rubner constant" for birds

An assumption was made that age constituent alpha x(beta) of mortality of individuals in a population in Weibull equation mx = m0 + alpha x(beta) (Ricklefs, 2000) reflects change of specific metabolic rate of one individual with age. Based upon that hypothesis a formula was proposed for relationship of specific metabolic rate of an adult individual after cessation of growth, when mass W is attained, and age t: q(t) = q0(1-omega(beta) + 1t(beta)) where q0 = aW(-b) is value q(t) at the moment of growth cessation and omega = alpha(1/(beta + 1)) is "ageing rate", determined and estimated by R. Ricklefs. Maximum longevity of an individual was determined as [equation: see text], where qcrit is specific metabolic rate at the age tmax. Parameter beta and relationships omega(W) and (qcrit/q0)(W) were approximated for birds from data of Ricklefs. Statistical comparison of results of calculations of tmax was carried out on the basis of the above formula and other known formulas for groups of Passeriformes and non-Passeriformes. Rubner constant [equation: see text] was calculated assuming that body mass of an adult individual (W) is attained in the first year of life (tA = 0). Average values of 602.4 +/- 2.5 kcal g(-1) (n = 83) for non-Passeriformes and 963 +/- 6.3 kcal g(-1) (n = 41) for Passeriformes were obtained.     

扁禾旱 蔗草的生物学特性及防治研究

 研究表明,扁秆藨草生育节律明显,有性繁殖对季节要求严,无性繁殖对季节要求宽,在“半遮光”条件下不能抽穗结实,无性繁殖受到抑制。扁秆藨草的阶段发育与叶龄相关显著,用主茎叶龄预测再生苗的线性回归方程式：Ŷa=-36.74+6.24x(1983)和Ya=-32.42+6.28x(1984年);预测块茎发生量的线性回归方程式：Ŷt= -67.97+10.12x(1983年)和Yt=-33.91+80.4x(1984年)。机械和人工除草可抑制块茎的形成和阻止抽穗结实,但能促进再生苗的蔓延。大田防治必须在扁秆藨草块茎形成之前用药,并做到株株受药,才能起到“斩草除根”的作用。扁秆藨草的发生分布与耕作栽培制度关系密切,实生苗萌发迟而集中,再生苗萌发早而分散,是防除的主要对象。实验表明,只有运用农业、生物、化学等综合防治手段,才能有效地控制扁秆藨草的为害。     

大型溞生长、生殖和种群增长的研究

年龄6±6小时的纯系大型溞培养在25±1℃静置换水条件下,饲以斜生栅藻,其平均寿命为68.40±9.82天。龄期(x)和年龄(t,天)之间呈曲线迴归关系:t=-2.245+1.510x+0.035x2(r=0.99,p3.86-0.131t)(式中Y为累计生殖量个数,t为天数)。       

桃小食心虫在不同温度下的实验种群生命表

为探索温度对桃小食心虫Carposina sasakii生长发育和繁殖的影响,在室内17, 20, 23, 26, 29和32(±1) ℃,80%±7% RH和15L: 9D条件下,测定了桃小食心虫各发育阶段的历期、存活率和/或产卵量, 组建了桃小食心虫的实验种群生命表.结果表明, 桃小食心虫各虫态的发育历期随温度的升高而缩短; 初孵幼虫的蛀果率随温度升高而提高,幼虫脱果率与温度之间呈抛物线关系：y=-0.5638x²+27.882x-269.18 (R²=0.9801,P＜0.01);结茧率和羽化率在17～29℃间无明显变化,但在32℃时则明显降低;雌蛾的产卵量和寿命随温度的升高而降低,23℃时雌蛾交配率最高.生命表分析表明,种群趋势指数在17～29℃间均大于1,26℃时内禀增长率最高;世代存活率与温度的关系可用S=-0.073x³+4.626x²-92.019x+596.57（R²=0.9832）表示; 内禀增长率与温度之间的关系可用r_m=-0.0008x²+0.0409x-0.4438（R²=0.9851）描述。 据此得出,23～26℃是最适宜桃小食心虫生长发育和繁殖的温度范围。     

李肖叶甲成虫数量及三维空间格局动态

对合肥地区李肖叶甲成虫数量动态及三维空间格局进行研究,结果表明该成虫5月下旬初见,6月4日至7月16日为发生高峰期,9月上旬仍有零星虫口。6月4日至9月10日种群增长模型为y=1692.2258e-0.0545t,6月4日至8月27日树冠上部部位增长模型为y=205.60e-0.0523t,树冠西部部位的增长模型为y=257.13e-0.0505t。样地中的李肖叶甲5月21日至8月13日半变异函数方程是y=0.0709x3-10.479x2+391.67x-300.71、y=-0.0122x3+1.1201x2-19.781x+317.84、y=-0.0013x3+0.1613x2-4.4862x+67.363、y=-0.0016x3+0.9177x2-11.495x+551.94、y=-0.0029x3+0.3034x2-7.5906x+103.37和y=-0.0002x3+0.0172x2-0.4975x+13.691,变程在20.3938—65.0289之间,均为聚集格局,聚集强度指标表明也均为聚集格局;树冠东、西、南、北方位的水平分布5月21日至8月13日的C值均大于1,I值均大于0,CA值均大于0,Iw值均大于1,为聚集格局;树冠上、中、下方位的垂直分布6月4日至8月13日的C值均大于1,I值均大于0,CA值均大于0,Iw值均大于1,为聚集格局;5月21日至8月13日的树冠东、南、西、北、上、中、下部位的C值均大于1,I值均大于0,CA值均大于0,Iw值均大于1,三维分布均为聚集格局。用Iwao公式计算的结果与聚集强度指标分析的结果一致。6月4日—8月13日林间李肖叶甲的种群聚集均数λ值均大于2,聚集是李肖叶甲本身的行为所致。     

Relationships Between Population Growth and Population Density in Monocultures of Larix leptolepis

One year-old Japanese larch (Larix leptolepis) seedlings were planted in a nursery from 1984 to 1986 at four density levels with four replicates in order to investigate the relationships between plant growth and density of survivors. As the results shown, self-thinning occurred severely in populations growing at high densities. The rate of the self-thinning followed a trajectory defined by the 3/2 power law. The relationship between mean dry weight per tree and population density at a given stage of growth followed the reciprocal equation and power equation at early experimental stages, but changed gradually to follow the 3/2 power law as plants grew further. Shch a change was mainly caused by the constant basal area per ms and decreased growth of tree height along a gradient of the density. The relationship between tree height (h) and density (p) also be discussed and in the 3/2 power law system it could be described by an equation consisting of h=αp（-1/2） where α is a constant.