甘肃草原鼠害区划及高原鼠兔的精确性可持续控制技术研究
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摘要
(1)甘肃草原啮齿类动物区系由68种组成,占全省啮齿动物总种数的75.6%,其中,大多数种的种群密度不超过经济损害水平,有一定的生态学价值;约有18~26种的种群密度在多数地区几乎经常维持在经济损害水平以上,是不同草原类型的优势种害鼠。
     (2)以草原分布的规律性、草原害鼠区系组成、草原害鼠对不同草原的适宜性及草原鼠害的普遍性、长期性和严重性为草原鼠害区划基础,坚持历史发展、生态适应和生产实践三项基本原则,先按草原啮齿动物区系组成、地带性生物气候和地带性植被等项标准将甘肃草原鼠害划分为5个草原鼠害区,再按具有一定优势的地带性草原类型,具有代表性鼠类分布型和优势种害鼠等标准,将甘肃草原鼠害划分为13个草原鼠害亚区。
     (3)经实地抽样调查,高原鼠兔种群数量与其危害所造成草原牧草减产量(地上植物)及经济损失量呈正相关关系,相关系数为:r =0.9765;高原鼠兔的有效洞口数(X)与牧草减产量(M)的线性回归方程为:M = -16.9603 + 0.9180X ;在1330hm~2范围内进行大面积防治,核算单位面积防治成本为25.05元/hm2;通过计算,确认在2008年4月份肃南县大岔乡的高寒草甸和高寒草原上高原鼠兔的经济损害水平是130(个)有效洞口/hm~2,对应的经济允许损失率为7.5%;提出了不同经济允许损失率对应的理论防治指标。
     (4)对杀鼠剂、杀鼠剂浓度、毒饵投放量和饵料种类的L_9(3~4)试验结果表明:
     ①前3个因子差异极显著,且各因子对灭洞率影响的主、次不同,表现为杀鼠剂﹥杀鼠剂浓度﹥毒饵投放量﹥饵料种类;
     ②由于各水平间存在不同程度的差异显著性,因而对灭洞率亦有不同程度的影响,其中:D型肉毒梭菌生物毒素的平均灭洞率为82.6%,C型肉毒梭菌生物毒素灭洞率为75.0%,敌鼠钠盐为68.9%;3种用药浓度对应的平均灭洞率在69.0~82.4%之间;3种投饵量对应的平均灭洞率为69.4%、80.8%和76.2%;3种饵料对应的平均灭洞率是75.3%、72.7%和78.4%;
     ③最优组合是A_2B_3C_2D_3,即,用0.15%的D型肉毒梭菌生物毒素,以小麦作饵料,每个有效洞口投25粒毒饵有最佳的防治效果。
     (5)对大隆的使用浓度、投饵量和饵料种类的L_9(3~4)试验结果表明:
     ①试验重复间、各因子间及不同因子各水平间的差异均不显著,所有处理组合的平均灭洞率差别也不大,在81.6%~86.8%之间;
     ②从R值及各因子的不同水平与灭洞率关系示意图可直观看出最优组合是A2B1C1,也就是用0.01%的大隆,以青稞作饵料,每个有效洞口投5g毒饵应当有最佳灭效。这个组合同样在已经做过试验的9个组合中没有出现,但是它应该比从9个组合中直接找出的最好组合A_1B_1C_1更好;
     (6)对溴敌隆的使用浓度、投饵量和饵料种类的L_9(3~4)试验结果表明:
     ①试验重复间、各因子间及不同因子各水平间都有不同程度的差异显著性,因此,灭洞效果也不一样。3个用药浓度(0.005%、0.010%和0.015%)对应的灭洞率依次是:72.6%、85.3%和80.4%;3个投饵量(1g、2g和3g)对应的灭洞率是:80.6%、75.7%和82.1%;3个饵料种类(青稞、燕麦和小麦)对应的灭洞率依次是76.7%、80.6%和81.3%。
     ②A_2B_3C_3是最优组合,也就是用0.01%溴敌隆,以小麦作饵料,每个有效洞口投3g毒饵是最佳组合。
(1) The grassland rodent faunal composition of Gansu province was composed of sixty-eight species, accounting for 75.6% of total rodent species of the province, thereinto, most species had determinate ecological value and their population densities were below than EIL. There were about 18~26 species whose population densities maintained above EIL regular in many regions, and they were dominant rodent species of different steppes.
     (2) Used the disciplinarian of grassland distribution, grassland rodent faunal composition, adaption of grassland rodent to different steppes and universality, protracted, ponderance of grassland rodent pest as the fundamental of grassland rodent pest division, followed history development, zoology adaptability and production practice principle, firstly, the grassland rodent pests of Gansu province were compartmentalized five regions according to indicators of grassland rodent faunal composition, zonation biology climate, zonation vegetation and then thirteen subregions according to indicators of preponderant zonation grassland type, representative rodent distribution and dominant rodent species.
     (3) A sampling survey had been conducted and the result showed that there was a positive correlation between plateau pika population quantity and plants loss and economy loss which were caused by plateau pika, and the correlation coefficient was 0.9765. The linear regression equation between active burrows(X) of plateau pika and plants loss (M) was M = -16.9603 + 0.9180X. The large area control had been carried out in 1330 hm2 scope and unit area control cost was 25.05 yuan/hm2. Based on calculation, the EIL of plateau pika of alpine meadow and steppe was 130 active burrows per hectare in Dacha township, Sunan country in April, 2008, and the corresponding ratio of economic allowed loss was 7.5%. The theoretical control indexs were put forward on different economic allowed loss rates.
     (4) The results of orthogonal test L_9(3~4) for rodenticide, rodenticide concentration, bait collecting volume and bait species showed as follows:
     ①The first three factors had extremely significantly difference, and different factors had different primary-secondary effects to the eliminating mousehole rate, showed as rodenticide﹥rodenticide concentration﹥bait collecting volume﹥bait species.
     ②Because of the different degree significantly between different levels, the eliminating mousehole rate was also influenced with different degree. Thereinto, the average eliminating mousehole rate of Botulin type D was 82.6%, the Botulin type C was 75.0%, the Null was 68.9%. The average eliminating mousehole rate of three rodenticide concentrations between 69.0 and 82.4%. That of three bait collecting volumes were 69.4%, 80.8% and 76.2%, respectively. And that of three baits were 75.3%, 72.7% and 78.4%, respectively.
     ③The optimal combination was A_2B_3C_2D_3, namely, with 0.15% Botulin type D, used wheat as bait, threw 25 grain poison baits every active burrow would have the best control efficiency.
     (5) The results of orthogonal test L_9(3~4) for concentration, bait collecting volume and bait species of Talon showed as follows:
     ①There was no significant difference between test replication, factors and levels of different factors. The average eliminating mousehole rates of all treatment combinations also had little difference, between 81.6% and 86.8%.
     ②The R value and schematic diagram of relationship between control effect and different factors on different levels showed that the optimal combination was A2B1C1, namely, with 0.01% Talon, used highland barley as bait, threw 5 grams poison bait every active burrow would have the best control efficiency. This combination had not appeared in the nine experimental combinations, but it should be better than A_1B_1C_1 which was the best combination of nine.
     (6) The results of orthogonal test L_9(3~4) for concentration, bait collecting volume and bait species of Bromadiolone showed as follows:
     ①There was different degree significant difference between test replication, factors and levels of different factors, therefore, the eliminating mousehole rate was also dissimilar. The eliminating mousehole rate of three rodenticide concentrations (0.005%, 0.010%, 0.015%) were 72.6%, 85.3% and 80.4%, respectively. That of three bait amounts(1g, 2g,3g) were 80.6%, 75.7% and 82.1%, respectively. And that of three baits (highland barley, oat, wheat) were 76.7%, 80.6% and 81.3%, respectively.
     ②The optimal combination was A_2B_3C_3, namely, with 0.01% Bromadiolone, used wheat as bait, threw 3 grams poison bait every active burrow would have the best control efficiency.
引文
[1] Candolle, A.P. Geographic botanigue. In: Dictionaire des sciences naturelles[C]. Strasboarg and paris.1820:18.
    [2] Wallace, A.R. The geographical distribution of animals[M]. London: Mac Millan and Co, 1876, 1~2.
    [3] Darlington, P.J. Darwin and zoogeography [J]. Proc Amer Phil Soc, 1959, 103:307-319.
    [4] Darlington, P.J. Biogeography of the Southern end of the World [M]. Cambridge: Harvard University Press, 1965: 28-30.
    [5] Simpson, G. G. Species density of North American mammals [J]. Syst.Zool, 1964, 13:51-57.
    [6] Croizat, L. Space time and form, The biological synthesis [M].Published by the author, Caracas, 1964.
    [7]张荣祖.中国动物地理[M].北京:科学出版社, 2004: 411-414.
    [8]王祖望,张知彬.二十年来我国兽类学研究的进展与展望: II·形态分类、动物地理、古兽类学[J].兽类学报,2001,21(4):241-250.
    [9]游群.我国啮齿动物种群生态学研究进展[J].陕西林业科技,2004(1):26-30.
    [10]张君,胡锦矗.行为生态学在中国的研究与进展[J].西华师范大学学报(自然科学版), 2003,24(3):325-329.
    [11]王廷正.陕西省啮齿动物区系与区划[J].兽类学报,1990,10(2):128-136.
    [12]秦长育.宁夏啮齿动物区系及动物地理区划[J].兽类学报,1991,11(2):143-151.
    [13]武晓东,傅和平,庄光辉,等.内蒙古阿拉善荒漠区啮齿动物区系调查[J].内蒙古农业大学学报, 2000,21(4): 36-39.
    [14]付和平,郭志成,董清,等.内蒙古阿拉善右旗、额济纳旗啮齿动物区系[J].内蒙古草业, 2003,15(3):5-7.
    [15]董清,付和平,斯琴高娃,等.内蒙古阿拉善左旗啮齿动物区系[J]. 2004, 16(1):38-39.
    [16]侯兰新,马良贤.新疆东部啮齿动物的分类和分布[J].干旱区研究,1998,15(3):44-47.
    [17]张荣祖,王宗炜.青海甘肃兽类调查报告[M].北京:科学出版社,1964.
    [18]张荣祖.青甘地区哺乳动物地理区划问题[J].动物学报, 1964,16(2):315-321.
    [19]陈钧,伊佩衡.兰州盆地子午沙鼠(Meriones meridianus)对水土保持影响的初步观察[J].动物学杂志,1959,(7):281-291.
    [20]陈钧,杨若莉.达乌尔黄鼠和长爪沙鼠在河西分布的初步调查[J].动物学杂志, 1980 (4):30.
    [21]陈鉴朝.天祝县喜马拉雅旱獭(Marmota himalayana)[J].动物学杂志,1980(4):30.
    [22]王定国.甘肃河西走廊啮齿动物[J].兽类学报,1984,4(4):320-325.
    [23]梁俊勋,张军.黄土高原东北缘的鼠类及其区划研究[J].兽类学报,1985,5(4):299-309.
    [24]陈敬先.陇东地区啮齿动物调查报告[J].动物学杂志,1986(5):16-18.
    [25]王定国.额济纳旗和马鬃山北部边境地区啮齿动物调查[J].动物学杂志, 1988,23(6): 21-23.
    [26]李锡璋.甘肃省陇南、甘南地区啮齿类区系及分布[J].动物学杂志,1991,26(4):15-18.
    [27]谷景和,高行宜.新疆东昆仑-阿尔金山的动物区系与动物地理区划[J].新疆动物研究, 1991(1):30-43.
    [28]孙庆.阿拉善地区啮齿动物区系组成与地理分布[J].动物学杂志,1997,32(3):49-50.
    [29]尉剑,张和平,胡江林.张掖地区草原啮齿动物种类组成与群落结构研究[J].草业科学, 1999,16(6):26-31.
    [30]刘荣堂,黄淑娟,李海霞.改造鼠荒地,改善草原生态环境[J].草原与草坪,2000(4):15-19.
    [31]宋延龄,李俊生,曾治高,等.甘肃河西走廊不同生境中鼠类群落结构初步研究[J].生物多样性,2002,10(4):386-392.
    [32]郑涛,张迎梅.甘肃省啮齿动物区系及地理区划的研究[J].兽类学报,1990,10(2):137-144.
    [33]王香亭,陈鉴潮,宋志明,等.甘肃脊椎动物志[M].兰州:甘肃科学技术出版社,1991.
    [34]谭邦杰.哺乳动物分类名录[M].北京:中国医药科技出版社,1992:165-310.
    [35]黄文几,陈延熹,温业新.中国啮齿类[M].上海:复旦大学出版社,1995.
    [36]王应祥.中国哺乳动物地理分布物种和亚种大全[M].北京:中国林业出版社,2003.
    [37]花立民,黄倩,曹慧.甘肃啮齿动物区系组成研究[J].草原与草坪,2008(2):46-51.
    [38] Stern, V. M. et al. The integration of chemical and biological control of the spotted aphid[J]. Hilgarolia, 1959, 29(2): 81-101.
    [39]宋凯,刘荣堂,陈永国,等.草原啮齿动物学[M].第二版.北京:中国农业出版社, 1999:195.
    [40] Mumford, J. D. et al. Economics of decision making inpest management. Ann. Rev. Entomol., 1984, 29:157-174.
    [41] Hall, D.C. et al. On the timing and application of pesticides[J]. Agric. Econ.1973, 55(2): 198-201.
    [42] Onstad, D.W. Calculation of economic-injury levels and economic thresholds for pest management [J]. Econ.Entomol. 1987, 80: 297-303.
    [43] Hutchins, S.H.et al.Injury equivalency as a basis for developing multiple species economic injury levels [J]. Econ.Entomol. 1988, 81 (1): 1-8.
    [44] Flint, M. L. et al. Introduction to integrated Pest Managent [M]. New York: Plenum Press. 1981.
    [45] Peterson, R.K.D., Hunt, T.E., The Probabilistic Economic Injury Level: Incorporating Uncertainty into Pest Management Decision-Making [J]. Journal of Economic Entomology,1996, 18:536-542.
    [46]盛承发.害虫经济阈值的研究进展[J].昆虫学报,1989,32(4):492-499.
    [47]何东进,洪伟.害虫防治经济阈值研究进展[J].福建林业科技,1998,25(4):7-12.
    [48]盛承发.华北棉区第二代棉铃虫的经济阈值[J].昆虫学报,1985,28(4):382-389.
    [49]盛承发.华北棉区第三代棉铃虫的经济阈值[J].昆虫学报,1988,31(1):37-41.
    [50]高宗仁,赵洪义,秦田丰,等.河南棉铃虫再猖撅的生态学特点及经济闽值研究[J].棉花学报,1994,6(1):57-60.
    [51]盛承发,杨辅安.棉铃虫经济阈值研究中的几个问题[J].生态学报, 1999,19(5):720-723.
    [52]郭明,万传星,王小英,等.棉蚜危害损失和经济阈值的研究现状[J].塔里木农垦大学学报,2000,12(1):51-56.
    [53]严英俊,尤民生,吴中孚.褐稻虱危害水稻经济阈值的研究[J].华南农业大学学报,1992, 13(2): 40-46.
    [54]蒋杰贤,陈永年,潘桐.稻纵卷叶螟与褐稻虱混合种群经济阈值的研究[J].湖南农学院学报,1994,20(4):358-362.
    [55]叶正襄,秦厚国,李华.水稻苗期稻茎毛眼水蝇经济阈值的研究[J].植物保护,1996,22 (3):13-15.
    [56]秦厚国,叶正襄,李华,等.水稻孕穗期稻茎毛眼水蝇经济阈值的研究[J].植物保护, 1997, 23(6):12-15.
    [57]李茂胜,李起林,严叔平,等.水稻对稻瘿蚊为害补偿力及经济阈值研究[J].华东昆虫学报, 2000,9(1): 89-95.
    [58]朱文达.稗对水稻生长和产量性状的影响及其经济阈值[J].植物保护学报,2005,32 (1): 81-86.
    [59]由振国.春小麦田野燕麦的经济阈值及防除策略[J].农业技术经济,1986,(1):86-97.
    [60]付迎春,胡凡,朴英,等.麦田阔叶杂草经济阈值及防除研究[J].植物保护学报,1998,25 (2):175-180.
    [61]于金凤,王金信,陈茂学,等.麦田混生杂草生态经济阈值的研究[J].植物保护,2002,28 (5): 13-15.
    [62]白莉,郑王义,任东植,等.麦长管蚜为害损失估计及防治阈值研究[J].山西农业科学2006,34(1):61-64.
    [63]王风延,刘俊臣,李瑞花,等.小麦丛矮病发生程度与经济阈值分析[J].植保技术与推广, 1998,18(3):18-19.
    [64]杨先法.小麦黄矮病经济阈值的研究[J].天津农业科学,2007,13(2):57-58.
    [65]邝幸泉,毕成鹏.亚洲玉米螟多元动态经济阈值模拟模型[J].应用生态学报,1992,3(3): 247-252.
    [66]文丽萍,王振营.亚洲玉米螟对玉米危害损失估计及经济阈值研究[J].中国农业科学,1992,25(1):44-49.
    [67]陆温,张永强,黄崇科.玉米铁甲虫的防治指标研究[J].广西农业生物科学,2003,22(1): 29-31.
    [68]杨振宇,江小蕾.高原鼠兔对草地植被的危害及防治阈值研究[J].草业科学,2002,19 (4) :63-65.
    [69]余晓华,刘荣堂.高原鼢鼠的经济损害和经济阈值研究[J].草原与草坪,2002(3):36-37.
    [70]韩崇选,陈孝达,胡忠朗,等.甘肃酚鼠对油松危害动态经济阈值研究[J].西北林学院学报,1994,9(3):45-52.
    [71]杨学军,韩崇选,王明春,等.油松种子园甘肃鼢鼠防治试验研究[J].陕西林业科技, 2004,3(2):14-17.
    [72]付文斌,汪有奎,孙小霞,等.云杉幼林地中华鼢鼠防治阈值研究[J].北华大学学报(自然科学版),2000,1(5):439-442.
    [73]董百赟,张三亮.人工油松林地中华鼢鼠防治指标研究[J].甘肃农业大学学报,2004,39 (5):559-561.
    [74] Szatmari S., et al. Lepidoptera living on raspberry in North Hungary, Integrated plant protection in orchards, soft fruits [J]. Bulletin OILB SROP, 1998, 21(10):35-38.
    [75] Ukey S.P., Naitam N., Patil M.J., Determination of economic threshold level of mites on chilli crop[J]. Journal of Soils and Crops, 1999, 9(2):268-270.
    [76] Bharpoda T.M., Evaluation of economic threshold levels for Helicoverpa armigera on 'H 6'cotton (Gossypium hirsutum) in central Gujarat region [J]. Indian Journal of AgriculturalSciences, 1999, 69(4):304-305.
    [77] Ulu O., and Onucar A., Investigations on the economic threshold of rose leaf roller, Archips rosanus (L.)(Lepidoptera: Tortricidae) [J]. Bitki Koruma Bulteni, 1999, 39:3-4,103-114.
    [78] Jai Singh., Economic threshold for spotted bollworms, Earias spp. in cotton, Gossypium arboreum L [J]. Journal of Insect Science, 1998, 11(1):66-68.
    [79] Muhammad Afzal., et. al., Evaluation and demonstration of economic threshold level (ETL) for chemical control of rice stem borers, Scirpophaga incertulus Wlk. and S. innotata Wlk [J]. International Journal of Agriculture and Biology.2002, 4(3): 323-325.
    [80] Brown J.R., Herrick J., Managing low output agro-ecosystems sustainably: the importance of ecological thresholds Proceedings of the third International Conference on Forest Vegetation Management [J]. Canadian Journal of Forest Research, 1999, 29(7):1112-1119.
    [81] Larsson H, Water distribution, grazing intensity and alterations in vegetation around different water points in Ombuga Grassland Northern Namibia [M]. Minor Field Studies International Office, Swedish University of Agricultural Sciences, 2003, 225:54.
    [82]白全江,程玉臣,赵存才.春小麦田菜和野燕麦生态经济阈值模型的初步研究[J].华北农学报,2000,15(4): 93-98.
    [83]张宏利,韩崇选,杨学军,等.鼠害防治方法研究进展[J].陕西林业科技, 2004 (1):41-47.
    [84]韩熹莱.农药概论[M].北京:北京农业大学出版社,1995,251-254.
    [85]戴忠平,施大钊.驱鼠剂的研究现状及展望[J].植物保护, 2004,30,(5):11-14.
    [86]王明春,韩崇选,杨学军,等.克鼠星1号防治甘肃鼢鼠研究[J].西北林学院学报,1999,14 (2):51-56.
    [87]李富华,张厘,王云济.昆明市家鼠对杀鼠灵的抗药性测定[J].中华卫生杀虫药械,2003, 9(4):31-32.
    [88]邹添明,张春明,黄福涛,等.惠州市家栖鼠对第一代抗凝血杀鼠剂抗药性研究[J].热带医学杂志,2005,5(5):663-665.
    [89]刘晓倩,史森,张莹,等.长春市两个地区褐家鼠对杀鼠灵的抗药性实验研究[J].中国地方病防治杂志,2007,22(2):102-103.
    [90]张世炎,胡杰,梁练,等.湛江地区黄胸鼠和褐家鼠对抗凝血剂的抗药性[J].中国媒介生物学及控制杂志,2002,13(1):66-68.
    [91]崔生发.在不同生境中C型肉毒梭菌毒素杀鼠剂的杀鼠效果试验研究[A].中国有害生物综合治理论文集[C].北京:中国农业科技出版社,1996.
    [92]张绪校,杨廷勇,郭时友,等. D型肉毒毒素灭高原鼠兔试验[J].草业科学,2007,24(2): 56-58.
    [93]席国兴,朱红良,钟海琼. 2005-2006年青海省平安县保护性灭獭结果分析[J].中国媒介生物学及控制杂志,2007,18(4):346.
    [94]谢俭波,李长升,王永利.四种熏蒸剂杀虫灭鼠效果评价[J].医学动物防制, 2003,19(3): 157-160.
    [95]杨学军,王显车,吴凤霞,等.多效抗旱驱鼠剂(RPA)的研制与应用[J].西北农林科技大学学报(自然科学版),2004,32(4):37-40.
    [96]庄凯勋,贾培峰,初德志,等.应用植物不育剂控制林木鼠害新技术应用[J].中国森林病虫,2000(增刊):34-37.
    [97]王酉之,马林,陈东平,等.化学不育剂—环丙醇类衍生物控制鼠害:Ⅲ灭鼠现场试验[J].四川动物,2003,22(4):215-217.
    [98]马有忠,刘勋才,刘芝玲.不同投饵方法防治中华鼢鼠技术[J].森林保护,2007(3):30-31.
    [99]刘发央,刘荣堂.高原鼠兔(Ochotona curzoniae)的研究现状及最新进展[J].甘肃科技, 2002,18(3):30-31.
    [100]赵同标,赵新全,常智杰,等.常氧下高原鼠兔HIF-1αmRNA的表达[J].动物学研究, 2004,25(2):132-136.
    [101]杨洁,赵新全,郭松长,等.高原鼠兔ob基因的组织表达特征[J].兽类学报,2007,27(1): 33-38.
    [102]陈婷方,白振忠,侯冰,等.青藏高原高原鼠兔肌红蛋白(MGB)基因编码区的克隆与分析[J].高原医学杂志,2005,15(4):4-7.
    [103]尚爱加,陈婷方,周定标,等.青藏高原高原鼠兔Na+,K+-ATP酶β2亚基基因编码区的克隆与分析[J].生物技术通讯,2007,18(4):553-556.
    [104]王淯,王小明,王正寰,等.高原鼠兔生境选择的初步研究[J].四川大学学报,2004,41 (4):1041-1045.
    [105]赵廷贵,潘桂兰,骆海强.高原鼠兔对燕麦等三种饵料适口性及采食量的对比试验[J].青海草业,2002,11(3):8-12.
    [106]马静,范薇,张雁,等.高原鼠兔昼夜摄食量和饮水量的观察[J].青海畜牧兽医杂志, 2005,35(5):17-18.
    [107]殷宝法,王金龙,魏万红,等.高寒草甸生态系统中高原鼠兔的繁殖特征[J].兽类学报, 2004,24(3):222-228.
    [108]张毓,刘伟,王学英.高原鼠兔贮草行为初探[J].动物学研究,2005,26(5):479-483.
    [109]张堰铭,张知彬,魏万红,等.高原鼠兔领域行为时间分配格局及其对风险环境适应的探讨[J].兽类学报,2005,25(4): 333-338.
    [110]王金龙,魏万红,张堰铭,等.高原鼠兔种群的性比[J].兽类学报,2004,24(2):177-181.
    [111]严作良,周立,孙英,等.江河源区高寒草地高原鼠兔种群动态模式初步研究[J].四川草原,2005(5):17-19.
    [112]马隆喜,江小雷,张卫国.高原鼠兔行为格局对种群密度的响应[J].草业科学,2007,24 (9):79-82.
    [113]周乐,杨生妹,于智勇,等.高原鼠兔四个地理种群的遗传多样性与遗传分化[J].兽类学报,2007,27(3):221-228.
    [114]曲家鹏,李克欣,杨敏,等.高原鼠兔家群空间领域的季节性动态格局[J].兽类学报, 2007,27(3):215-22.
    [115]盖钧镒.试验统计方法[M].北京:中国农业出版社,2000:285-290.

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