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WSP00036
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Last modified
1/26/2010 12:12:28 PM
Creation date
10/11/2006 9:29:26 PM
Metadata
Fields
Template:
Water Supply Protection
File Number
8200.750
Description
San Juan River General
State
CO
Basin
San Juan/Dolores
Water Division
7
Date
3/1/1975
Author
BOR
Title
San Juan Ecology Project - Interim Progress Report - March 1975
Water Supply Pro - Doc Type
Report/Study
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<br />4.7.1 Introduction <br /> <br />4.7 SMALL MAMMALS (Drs. Albert Spencer & Harold Steinhoff, Roger Sle per) <br /> <br />I <br /> <br />Small mammals of the forest are seldom seen by the <br />casual visitor so their importance in forest ecosystems <br />is easily overlooked. Their biomass often exceeds <br />that of the larger more obvious mammals. Add to this <br />the faster energy turnover rate characteristic of <br />smaller animals and the consumption of plants by small <br />mammals may greatly exceed consumption by larger ones. ~ <br />The result is competition with larger game and domes- <br />tic mammals of direct importance to man. Also, small <br />mammals girdle tree seedlings a~d eat tree seeds, thus <br />interfering with reforestation. This is particularly <br />a problem in the San Juans where spruce must be clear- <br />cut to reduce wind throw and resultant natural regener- <br />ation is poor. Forest officers routinely check small <br />mammal populations before reseeding cut-over areas, <br />and spend extra effort on control if populations above <br />about 6 per hundred trap nights. <br /> <br />Thus effects of varying snowfall on small mammal popu- <br />lations is of interest to resource managers of the <br />San Juans regardless of the question of cloud seeding. <br />If increased snow hurts small mammal populations, <br />Project Skywater is of economic aid to the timber <br />industry. Of course, the inverse 'lso is true. <br /> <br />The objective of the small mammal project is to <br />investigate effects of varying snowfall on aspects <br />of the population dynamics which, ~e1ate to size of <br />small mammal 'populations. These aspects may show <br />responses which demonstrate not only changes in small <br />mammal populations, but the more basic reasons for <br />those changes. Small mammal populations fluctuate <br />~onsiderab1y, but there are ~nvironmenta1 reasons for <br />these variations. If snow is related (or is not <br />related) to the fluctuations, we expect to find this <br />out. The six Jobs in this project are aimed at <br />sensitive and investigable points of small mammal <br />popu~ation dynamics. <br /> <br />4.7.2. Job 1. Litter Size and Survival <br />(Roger Sleeper) <br /> <br />- Objective <br /> <br />To relate snowfall to the timing and survival of <br />litters of small mammals. <br /> <br />- Procedures <br /> <br />Weekly examination of the 196 nest boxes provided in- <br />formation on litter survival. Young were marked with <br />ear tags when about 2 weeks old. Nursing young were <br />aged to the nearest week. Live trapping with Sherman <br />live traps provided information on winter survival. <br /> <br />- Findings <br /> <br />The size of the deer mouse (Peromyscus maniculatus) <br />population was very small in the summer of 1973, and <br />thus there were very few observations of deer mice in <br />the nest boxes on the study area. There was only one <br />litter of young found in a nest box during 1973, so it <br />was not possible to compare litter survival for the 3 <br />years. Discussion of litter survival for' 1971 and <br />1972 appears in the previous annual report (Teller, <br />Ives, and Steinhoff, 1973). <br /> <br />Over-winter survival was very low during the winter of <br />1972-73. Only one deer mouae was captured during the <br />first live-trapping period in June, 1973, and this <br />animal was not previously marked. None of the 108 <br /> <br />de~r mice marked in the summ r of 1972 were recaptured <br />in_ 1973. The mortality duri g the winter of 1972-73 <br />was so high. there was a ver small probability of any <br />deer mouse surviving. In 19 2, seven deer mice recap- <br />tured from those marked in 1 71 were all born prior to <br />mip-Ju1y, 1971. This indica ed that there was either <br />preferential survival for 01 er animals or that <br />younger animals had a greate tendency to disperse <br />from the area. Due to the h gh mortality in the win- <br />ter of 19.72-73, no more info 'mation was obtained in <br />1973 to determine which of t ese two mechanisms might <br />be- operating. <br /> <br />There were some data availab <br />of litter production for the <br />consist of estimates of the <br />and dates when females were <br />ing. The information on lac <br />not as good as the data on p <br />some subjectivity is involve <br />and late in lactation period <br />ulied to compare the breedins <br />on birth dates of litters wa <br /> <br />The data on birth dates of <br />indicates breeding commenced <br />1971 and 1972, but breeding <br />The majority of litters were <br />yeara. No information was <br /> <br />Table 1. Number of litters <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />e to compare the timing <br />3 years. These data <br />irth dates of litters, <br />ound pregnant or lac tat- <br />ation and pregnancies is <br />rturition dates, because <br />during early pregnancies <br />Thia information was <br />seasons, because data <br />not obtained in 1973. <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />tters (Table 1) <br />about the same time in <br />nded earlier in 1972. <br />produced in July both <br />ai1ab1e for 1973. <br /> <br />I <br /> <br />om each week. <br /> <br />I <br /> <br /> June Ju1 Auaust ~ <br /> Week <br />Year .! 2 3 4 1 ; 3 4 1 2 3 4 1 <br />1971 "2 I "2 "2 I "3 "2 "3 "2 <br />1972 2 2 2 2 2 1 2 <br />1973 1 <br /> <br />Observations of pregnant fe .ales are presented in <br />Table 2. The number of pre nant females is related <br />to population size, so the elative distribution of <br />pregnancies over the summer was used_ to compare <br />trends in timing of breedin Observations were not <br />begun until July in 1971. regnant deer mice were <br />found early in June, but no late in the summer <br />during 1972. In 1973, bree ing apparently began <br />later and ended later, beca se the pregnancies are <br />distributed more toward the end of the summer. <br />Breeding in 1971 also conti ued longer than in 1972, <br />but not as long as in 1973. <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />Table 2. Percent of female observed pregnant each <br />week of each year <br /> <br />I <br /> <br /> June Ju1 August ~ <br /> Week <br />Year .! 2 1 i 1 1- 4 .! 2 3 4 1 <br />1971 "8 i'l i'l25 "8 i'l <br />1972 2 28 1 7 19 19 6 <br />1973 10 10 10 30 40 <br /> <br />The deer mouse breeding sea on began earlier in 1972 <br />than in 1973. The delay in 1973 was probably due to <br />the prolonged snowpack. Hi ckley (1966) found that <br />extracts from ge~inating s eds enhanced testes <br />development in montane vole (Microtus montanus). <br />The snowpack may have restr cted deer mouse breeding <br />because of the delay in ini iation of plant growth. <br />The breeding season was shi ted more towards the end <br />of the summer in 1973 than n 1971 or 1972. The 1972 <br /> <br />35 <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br />
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