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Last modified
7/28/2009 2:27:42 PM
Creation date
10/1/2006 2:12:32 PM
Metadata
Fields
Template:
Weather Modification
Applicant
Western Weather Consultants
Project Name
Vail Pass
Date
11/1/1984
Weather Modification - Doc Type
Application
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<br />E\~(..LUATlO:; <br /> <br />(I,' ECOi.()(:lCAL EFFECT~ OF <br />;:Oor.,11J ".:... ~']~i:1l/ .arw <br /> <br />ABSTRACT <br /> <br />the possible effects of silv~r iodide seeding agent <br />accumulation in surface soils of the San Juan area <br />were investigated by use of l~~aratory studies in- <br />volving Arthrabacter - silver interactions, treatment <br />of soils with varied forms and l~vels of silver, by <br />examination of silver gradients surrounding seeding <br />generator sites, and by use of treatment p:o~s in <br />spruce, aspen, and subalpine meadow commun1tles <br />located in the San Juan sno~ augmentation area. Lab- <br />oratory st~dies have shown that on a short-term basis," <br />silver iodide or seeding generator burn mixtures at <br />hiRher than field concentration show only slight <br />effects on microbial groY!h or enzyme function, while <br />free silver ions, even at part-per-billion levels, <br />can cause ~rked changes in microbial activities. <br />These effects were lessened in the presence of soil or <br />complexing ions. However, ~nder field conditions on <br />a 3 year basis, silver iodlde appears to have a great- <br />er potential for altering soil decomposer functions <br />than silver from silver ion. The presence of silver <br />from silver iodide - sodium iodide complexes, again at <br />higher than backgro~,d levels, in the San Juan target <br />area led to a gradual increase in soil organic matter <br />content in 5p~uce and aspen su~face soils. No such <br />increase was observed in the subalpine meadoy plot. <br />Silver from silver nitrate tended to concentrate more <br />in upper plant portions than silver from silver iodide, <br />although silver from silver iodide was more closely <br />associated vith the plant roots. These effects were <br />only observed using silver levels 10-100X expected <br />field acc~ulation levels. Based on the available <br />literature and experiments carried out to date, the <br />accumulation of silver iodide seeding agent does not <br />~ppear to present an ecological threat, although con- <br />tinual monitoring of test systems should be carried <br />out to extend the time period over ~hich this conclu- <br />sion can be tested. <br /> <br />OBJECTIVES AND HYPOTHESES <br /> <br />1. <br /> <br />To monitor soil microbial activities in the San <br />Juan area, to determine if possible silver accre- <br />tion is influencing soil microb1al processes. <br />To analyze treatment plot soils to WhlCh varlOUS <br />silver additons have been made tn aspen, spruce, <br />and grass communities. <br />To measure microbial responses to silver gradients <br />present in the vicinity of the Pagosa ~prlngs gen- <br />erator site No. 25, and the Emerald Mountain SIte. <br />To determine the existence ot possible sub-lethal <br />eftects ot varled SILver LeveLS ana IUlllll:> UII <br />microbial processes, includ~ng ettects on m~crobl- <br />al viability and capabilities to transtorm SUb <br />strates requirlng enzymatlc aaaptatlon and enetgy- <br />p'roduction processes. <br />To determine if soil microbes are capable of <br />transforming silver present as silver 10dide to <br />additional sil~er forms, and to determine physio <br />"logical mechanisms which may result in silver <br />trans format 10ns. <br />To determine if assay procedures for varied silver <br />forms in soil c~n be developed. <br /> <br />2. <br /> <br />3. <br /> <br />4. <br /> <br />5. <br /> <br />6. <br /> <br />These objectives have <br />hypotheses: <br /> <br />.....Hypothesis 1. <br /> <br />been surr~rized in a series of <br /> <br />Accumulation of" silver iodide Trcm <br />~eather modification ~ill result in no <br />overt toxicity effects, but may resul. <br />in a slight delay in biological <br />pro.cesses. <br /> <br />~:LVE~ !GDID~ SEEDI~G <br /> <br />AGE~T1-/ <br /> <br />:-:ich,~" r(: <br /> <br />SL.~:C : <br /> <br />Hypothesis II. Laboratory studies can give an indica- <br />tion of the degree oi possible dimin- <br />uatien of microbial activity ~hich <br />might result fro~ silver accu~ulation. <br />:Hypothesis III. Soil bacteria tan cause a ch~nge ir. <br />silver iodide to fo~s more c~sily <br />taken up by plants. This modification <br />of silver form may ~ake it necessary <br />to carry out experi~ents under field- <br />related conditions as m~ch as possible. <br /> <br />-A,,~IY';5 .s~ct;onj C>":'i1l~-! <br />, <br />L <br /> <br />SU:1X..o\RY <br /> <br />Based on work carried out on the possible ecological <br />effects of silver iodide seeding agent accumulation in <br />soils of the San Juan area, the followi~g conclusions <br />c~n be drawn: <br /> <br />, , <br />1. "The accumulation of silver iodide nu"cleatin~ agent:- <br />presents D~overt.danRer to h~ans; plants or ani- <br />mals, based on available literature and work car- <br />rleo Cut under this studv for a 3 vear oeriod. <br />2. Silver io~ con C3use decreased ~ro~ih and enz'~e <br />induction in a soil Arthrobacter species at l-lQ <br />ppb free silver ion. The effect observed is depen- <br />dent on other anions and cations present. Soil <br />decreases the activity of free silver ions. <br />3. Silver from silver iodide or burn mixtures does <br />not show such ettects on m1croDlal growtn or en- <br />zymatic actlvlty. Generally 10-10U ppm at Ag! <br />torm silver is required to observe effects on <br />growth, v1ablllCY. and enzyme inductlon. <br />4. tree silver lon tram silver iodide dissociation at <br />5-6 ppb can ca~se'observable effects"on micro_ <br />organisms. To achieve this silver level <br />100-200 ppm of silver as silver iodide are re- <br />quired. <br />5. Microorganisms can cause reduction of free sil~er <br />10n or silver iodide to metallic silver. Amine- <br />type materials may be responsible for this reduc- <br />tion. <br />6. Silver iodide added at 1000 ppm shows no immediate <br />effects on soil respiration processes. <br />7. Attempts to establish respiration in~ices for test <br />soils across the impact area were not successful <br />due to short-term variability of soil. moisture and <br />temperature. <br />8. Silver accumulation in the vicinity of tvO seeding <br />generator sites did not cause decreases in nlcro- <br />bial respiration. Silver tended to accumulate and <br />~em3in in the surface solI zone 1n spIte ot ~x- <br />tended water percolation through the zone. <br />9. A subalpine meadow test plot install~d for 3 years <br />using silver iodide and" slIver nitrate at I, lU, <br />100 ppm surtace 5011 levels did not shov changes <br />in decomposer functions ~hich could'be related to <br />this treatment. . <br />10. Silver from silver iodide moved to upper plant por- <br />tions"to a lesser extent than silver frOm silver <br />nitrate. <br />11. Silver from silver iodide was more closely associ- <br />ated with plant roots than silver from silver ion. <br />12. After 3 years, silver from these tvo differing <br />original forms have not equilibrated to forms <br />which will give similar activities. <br />13. In spruce and aspen plots. imposition with silver <br />iodide tends to be related to increased organic <br />matter retention in the test systems. No such <br />relationships ~ere observed with equivalent treat- <br />ments using silver from silver nitrate (silver <br />ion). <br /> <br />!' ~ Steinhoff, H'~.I and J.D. rves (Eds). 1976. Ecolo~ical impacts of s~owpack <br />!1e~ntains, Colorado. San Juan Ec:olC'~y Projec:t, Final Report. Colorado State <br />II Present address: Dept. of Microbi01o~y. Colorado State Vniv., ~t. Colltns, Co. <br /> <br />augmentation <br />Univ. Pub!., <br />80523. . <br /> <br />in the San Juan <br />fort Collins. <br /> <br />us <br />
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