Growth response of Agropyron smithii individuals to increased summer water availability by John Joseph Newbauer A thesis submitted in partial fulfillment of the requirements for the degree of Master of Science in Biological Sciences Montana State University © Copyright by John Joseph Newbauer (1985) Abstract: Four irrigation treatments -- 0, 6, 12, and approximately 25 mm/week -- were applied to a homogeneous stand of Agropyron smithii to determine the response of individual plants to differences in water availability. Sigmoid growth curves were observed. From these and records of green leaf area, unit leaf rates for major growth stages were calculated. Across treatments these averaged. 78, 32, 4, and 7 mg dm^-2 day^-1 for early-rapid-growth, peak-of-green, early-quiescent-period and season's end, respectively. Aboveground production of individual plants read from growth curves averaged 156, 151, 150, and 307 mg in dry 1979 and 301, 209, 431, and 343 mg in wet 1978 in the 0, 6, 12, and 25 mm treatments respectively. Replacement of unit leaf rates with estimated photosynthetic rates suggested that belowgrowth. production was at least half and probably not much more than twice aboveground production. Production seems to be controlled both by water stress—-with slowing of growth at -5 bars and halting at -20 bars—-and by another seasonally correlated factor, perhaps daylength. GROWTH RESPONSE OF Agropyron smithii INDIVIDUALS TO INCREASED SUMMER WATER AVAILABILITY by JOHN JOSEPH N E WBAUER, III A thesis submitted in partial fulfillment of the requirements for the degree of Master of Science in Biological Sciences MONTANA STATE UNIVERSITY Bozeman, Montana March 1985 COPYRIGHT by John Joseph Newbauer , III 1985 All Rights Reserved ii APPROVAL of a thesis submitted by John Joseph Newb a u e r , III This thesis has been read by each member of the thesis committee and has been found to be satisfactory regarding content, English u s a g e , format, citations, bibliographic style, and consistency, and is ready for submission to the College of Graduate Studies. Date Chairperson, Graduate Commit tee Approved for the Major Department Head, MajorDepartment Approved for the College of Graduate Studies 3 Date ^ Graduate Dean ill STATEMENT OF PERMISSION TO USE In the presenting this thesis in partial fulfillment requirements University, I for a master's degree at Montana agree that the Library shall complete permission. provided acknowledgment of source is made. Permission reproduction for of this that extensive quotation the opinion of either, accurate from my major Any copying or use of material in this thesis for financial gain shall Signature or the proposed use of the be allowed without my written permission. Date Brief by the Director of Libraries material is for scholarly purp o s e s . the and thesis may be granted by professor, or in his absence, in it from this thesis are allowable without special quotations when, State make available to borrowers under rules of the L i b r a r y . of not iv VITA John Joseph N e w b a u e r , III was born November 10, 1943 in Washington, D .C . His father is John J . Newb a u e r , Jr. and his mother, Eleanor W . N e w b a u e r . Following graduation from Miller School of Albermarle, Miller School, Virginia, in 1963, he moved to W h i t e f ish, Montana, where he met and married his wife, Sydney L . Newbauer in January 19.65. He received a Bachelor of Science degree in Zoology from Montana State University in June 1973. He has worked as a Range Biologist for the Montana Department of Natural Resources and Conservation on the High Plains Experiment in Miles City, Montana since 1974. He began Graduate studies at Montana State University, in the Department of Biology, winter 1980. V ACKNOWLEDGMENTS Sincere appreciation is individuals who made this study thanks due to Dr. are guid a n c e , T. extended the possible. Weaver for many Particular providing field constructive criticism during the course of the investigations and editorial a i d . extended to to cooperation, Dr. J. Pickett Special thanks are also for his efforts and without which completion of this thesis would not have been poss i b l e . I also thank my continual encouragement wife, Sydney, for throughout the study. patience and vi ' V ' TABLE OF CONTENTS Page LIST OF T A B L E S ......................................... LIST OF F I G U R E S ............................... . . . vii viii A B S T R A C T ................................ -Ix INTRODUCTION........................................... ■ LITERATURE R E V I E W ..................................... I 2 \ Effects of water stress on plant performance. 2 ................................ 6 Site and plot d escription .................. Growth measurement and a n a l y s i s ................ Leaf weight and area determinations........... Water potential measurements .................. 6 7 9 IO MATERIALS AND METHODS RESULTS AND D I S C USSION ........... Aboveground growth rates ....................... Unit leaf ra t e s .................................. Estimation of p r o d u c t i o n ....................... Belowground production .................... Factors controlling production and g r o w t h . . . Growth response to water supplements . . . . . CONCLUSIONS 11 11 13 17 23 26 33 . . .......................... .............. 37 LITERATURE C I T E D ....................................... 39 vi i LIST OF TABLES Page Table I. Calculation of unit leaf r a t e .............. 16 Table 2. Unit leaf rates of Agropyron smithii Table 3. Calculation of seasonal production, a demonstration of methods ................ 19 Table 4. Production (mg/plant) of individuals of Agropyron smithii grown under four irrigation regimes ......................... 20 Belowground production (mg/plant) calculated using minimum or maximum estimates of photosynthetic r a t e s ......... 24 Belowground production (% of total) calculated using mimimum or maximum estimates of photosynthetic ra t e s ......... 25 Total aboveground yields, on culm length (mm) and biomass (mg) bases, of average Agropyron smithii plants from plots subjected to four water regimes. Each datum is reexpressed (in parentheses) as a percentage of the control. ................... ............. 34 Table 5 Table 6 Table 7 . . . . 14 viii LIST OF FIGURES Page Figure I. Figure 2. Figure 3. Cumulative growth, green leaf length, soil water status, and plant water status of Agropyron smith!! plants subjected to four water treatments in three years .............. 12 Relationships of growth rate to water availability for Agropyron smithii plants subjected to four water treatments for three y e a r s ......................... 28 The effect of water potential and season on unit leaf r a t e ............................ 31 ix ABSTRACT Four irrigation treatments — 0, 6, 12, and approximately 25 mm/week -- were applied to a homogeneous stand of Agropyron smithii to determine the response of individual plants to differences in water availability. Sigmoid growth curves were obse r v e d . From these and records of green leaf a r e a , unit leaf rates for major growth stages were calculated. Across treatments these averaged. 78, 32, 4, and 7 mg.dm .day for early-rapidgrowth, p eak-of-gre e n , earTy-quiescent-period and season's end, respectively. Aboveground production of individual plants read from growth curves averaged 156, 151, 15 0, and 307 mg in dry 1979 and 301, 209, 431, and 343 mg in wet 1978 in the 0, 6 , 12, and 25 mm treatments respectively. Replacement of unit leaf rates with estimated photosynthetic rates suggested that belowgrowth. production was at least, half and probably not much more than twice aboveground production. Production seems to be controlled both by water stress--with slowing, of growth at -5 bars and halting at -20 bars— and by another seasonally correlated factor, perhaps d a ylength. I INTRODUCTION Agropyron smith!! ranges from Alberta and British Columbia is south to Texas and Arizona (Hitchcock 1950) and 2 a dominant grass in 437,000 km of the North American Great Plains the (Kuchler 1964). northern and early pasture, importance central Great Plains and is h a y , and erosion control I the used for (USDA 1972). Its east of the Mississippi has been increased agricultural planting management It is a major range grass in (Hitchcock 1950). Interest In by its is therefore high. have examined the effects of water availability on performance of Agropyron smith!! because the might modify water availability by a variety of including cloud water pitting, by (Valentine seeding 1980). (Hess 1974) or water spr e a d i n g , Detailed manager processes reallocation or measurements of irrigation of Agropyron smithii growth allowed me to describe the seasonal pattern of above- and below-ground growth, the control of growth by water availability and perhaps photoperiod, the might growth responses to treatments bracketing be achieved by irrigation or cloud those or at least 25 mm per week. and that seeding: repeated supplementation of rainfall to 6 mm per week, mm per week, that 12 2 LITERATURE REVIEW: EFFECTS OF WATER STRESS ON PLANT PERFORMANCE The Great growth of native forage species Plains is often limited by lack in the of northern water. The growth process is the most sensitive of plant processes to moisture stress (Acevedo et al. Fischer and Hagan 1965). 1971; 1979; Haiao 1973; Among the first effects of plant water stress are reduction in shoot and leaf growth (Hsiao 1973). Brown (1977) and others have reported continuing decline in plant water potential substantial reduction in respiration that a causes a (Henckel carbon translocation (Hsiao 1973; Henckel 1964), 1964), cytokinin titer (I tai and Vaadia 1971), and an increase in' abscisic acid level When water (Ackerson 1980) . severe, proline accumulation occurs 1978) and CO^ assimilation stress (Haglund 1980; ceases (Hsiao becomes Stewart 1973). Senescence induced by drought may become visible at severe water stresses. severe stress, to If water is added to the after growth may r e s u m e , but it will never return the rates of unstressed plants Hsiao 1973; system (Noggle and Fritz 1976; Fischer and Hagan 1965; Acevedo et al. 1971). 3 Translocation of photosynthates continues under water stress (Wardlaw portions 1977). the plant The (roots for of 1974) and is primarily storage (Sosebee and moderate when leaf -- or Wiebe to 1971; recall conditions Moser organs resources i m p rove. During stress photosynthate accumulates in other portions of the accumulation short moisture water below-ground of resources in perennating and crowns) allows the plant growth to occurs, in plant -- a n d , growth may be more vigorous since for a time after a period of water deficiency than before (Boyer 1970) . Translocation to storage depots generally most active in the fall and these will be on the is drawn during either fall regrowth or in initiation of spring growth (Trlica 1977). Carbohydrate t reserves therefore show a significant decline during spring g r o w t h , with the extent and duration of the decline differing among species (Trlica 1977). Phleum prat e n s e , initiation found For example, using of stem elongation, and inflorescences carbohydrates; C Balasko and Smith (1973) at contained and at anthesis, transport relative report should found that at most of the these stems and roots contained The results of be observable as changes masses of plant parts. that, in flowering, 73% of the labeled soluble carbohydrates. such techniques mobile carbohydrates were primarily in roots and leaves; stems 14 Sims and Singh in a variety of grasslands, crown in the (1978a) biomass 4 decreased in the early season period of increased thereafter, and initial peaked after the growth, live shoot biomass p e a k e d . Generally, environmental moisture factor semi-arid regions sensitive to elongation but is the (Moore 1977). reductions in P than of shoots accumulation 1964). and of The leaf 1971) in The photosynthate produced initiation 2 ) increase in the dry elongation of internodes, carbohydrate reserves (Begg carbon is declines in a prioritized manner to I) and development of l e aves, in less Acevedo et al it is severely inhibited with continued (Boyer 1970). rates Photosynthesis is (Fischer and Hagan 1965; transferred dominant affecting photosynthetic initial water potential is stress allocation pattern weight and and 3) Wright changes phenological development and with root and rhizome with growth (Moser 1977). Any expected influence to competitive addition plant be delay the onset and reduce the intensity of among plants (Harper various environmental factors, and time of year may affect the growth juvenile size, to might stress that slows the growth rate plant is capable of exponential 1977). age rate. increases but as it matures the growth rate declines 1975). juvenile of In the The in (Leopold Dahl.and Hyder (1977) suggest that the end of the stage can only be defined,by the development of 5 spikelet buds and that the differentiation to reproductive status apex. is preceded by a rapid elongation of the shoot 6 MATERIALS AND METHODS Site and Plot homogeneous alluvial Description. stand The study of Agropyron smith!!, site the soil montmorillonitic• as The a Brollic texture is ® 3Ca horizon at 41 cm; through the horizon at horizon between 84 and 152 cm. 84 cm; a on an located fan of Kobar Silty Clay Loam soil. classified was The USDA/SCS camborthid a silty fine, clay loam loam through the and very fine sandy loam in the The site has a slope approximately 2% and a northerly a s p e c t . of It is located on the U .S . Livestock and Range Research Station, Miles City, Montana (latitude 4 6 ° 2 1 *15" N , detailed description of longitude 105°55'00"W). the study site and A the experimental plots is given by Weaver et al (1981). Water treatments control— no rainfall on four experimental plots augmentation throughout the were: study ^ wk — period; six millimeter— a minimum 6 of mm . guarantee; w e t — plots in which the soil moisture at 25 and 75 cm was maintained between O and -2 bars. stress condition 25 mm . wk could generally be The low water maintained with -I additions. Irrigations occurring between I May and I September are summarized in Figure 2 (p. 28). 7 Irrigation water was applied with sprinklers located approximately 50 applications minimize cm above were made ground between evaporation distribution. the and surface. 0300 and wind Water 0900 effects HDT on Irrigation was halted when winds to water exceeded _^ 13 cm . sec to avoid an irregular distribution pattern and unacceptable overspray. Drop by Mason sizes were determined using a method (1971). described Shallow rectangular pans approximately 31 x 61 cm with a layer of uncompacted flour on the bottom were e x p osed, seconds and determine at canopy height, the to sprinkling for dough balls produced were measured the drop size distribution and mean drop The sprinklers tested 10-20 (N=50) delivered drops in. the of 0.5 to 3.0 mm with a mean of 1.8+ 0.1 mm. to size. range These sizes are within the limits expected from summer rain showers in the northern Great Plains Growth Measurement and (Edmond H o l r o y d , 1978). Analysis. measured in three treatments wet) (control, Plant growth was six millimeter, in 1977 and in all four treatments in 1978-79. In each plot 20 individuals were marked approximately 0.75 a p a r t , in a line across the center of each plot. arid m Numbered metal reference tags were tied to the base of each plant. The growing leaves of Agropyron smithii were measured at weekly September intervals from of each y e a r . approximately I On the first sampling May to date I of 8 each year all except the lowermost leaf thereafter were measured; only the upper elongating leaves of the were m e a s u r e d . plant Measurements originated at the tip of the leaf and terminated at the ligule of the next leaf This method entire of me as ur emment included the growth leaf (blade and sheath) and therefore, above-ground nearest growth. significance x variance (ANOVA) was used to of differences 1200, The Rate 4 treatments 1978, 1979 data data sets used for the were from the control and transformation assumptions was (P>0.20) applied of A N O V A . normal distributions well Mensing examination wet of treatments, on the assumption that if met in the remaining plots. distributed test distributions normality criterion was met in these plots normally and 1979 on selected data sets (Os11e and the most diverse plots studied, be for The Kolmogorov-Smirnov goodness-of-fit distributions also test and 4 treatments x 12 dates in and 960 observations in 1977, normality 1975). the treatments. employed to assess deviations of from total Each cell contained 20 individuals for a total respectively: the among of 3 treatments x 13 dates in 1977, were used. was the the All measurements were made to of 15 dates in 1978, of 780, of I mm. Analysis matrices below. to The data were so better a would not logarithmic satisfy This yielded data sets (P <0.01, it that the fit Dixon and Massey 1969). 9 The transformation used was log (x+1) to eliminate zero values in the rate matrix. Leaf Weight and Area Determinations. collected Agropyron sections equivalent (i e , a phytomer). Leaves from randomly smithii plants were The units isolated included the sheath, of each leaf which cut away at the ligule of the leaf weight mg. The dry of each section was determined to the nearest 0.1 Leaves were below. then soaked in detergent facilitate unrolling the b lades, on clear laminating film. recorded Length, fully as developing, solution area, and condition of The condition fully developed and green, developed with brown tip > 5 mm but < 75% of leaf surace, or dead The damaged to blotted d r y , and mounted individually mounted leaves were recorded. was into to those used in growth determinations b l a d e , and associated stem (=Internode) was dissected total (leaf area reduced because of loss) (75% or more of the leaf surface brown). area of individual leaves was calculated using the method of trapezoidal area approximation (Beyer 1979), on a Tektronix 4051 minicomputer Tektronix 4956 digitizing to the nearest 0.01 mm closest I mm. 2 tablet. interfaced with a The areas were recorded and lengths were recorded to the 10 Water Potential M e asurements. Soil water potential ( 'f s ) was determined in the field using gypsum blocks (Taylor et al 1961) buried at three locations in each plot at depths of 10, mean 25, values mean and 75 cm. The blocks were read weekly for each depth were determined to and obtain a for each plot and depth at each measurement date. Plant water potential (j) ^ was measured with a Scholander-type pressure chamber (Scholander et al using procedures recommended by Ritchie and Hinkley (1978) except as noted b e l o w . Measurements were within one hour of sunrise, made 1965) weekly, on five plants selected from predetermined locations randomly placed within each of the treatments. treatment. The Dawn ^ presented are the means measurements were used for each because should be close to its maximum at that time (Slayter 1967; Ritchie and Hinkley 1978). dissecting scope, Plants were observed through a with magnification capabilities of 30x, within seconds of being c u t . sufficient point magnification for Generally, 7- IOx provided determination of the end Pressure was increased at less than I bar . sec until water was expressed from the cut e n d . -I 11 RESULTS AND DISCUSSION Above Ground Growth Rates. Agropyron smithil (Fig. with I) This In all treatments and plants show a sigmoidal growth growth pattern has been observed (e.g. Golubev 1971; Evans 1972; and Milthorpe and Moorby 1974) . each temperature) period) spring Erickson 1976; when become suitable. a r e a , and m u s t , therefore, rapid and leaf conditions index of begins when Canopy the rapid could be due to May or growth earlier. The quiescent phase (third of under Figure I suggests that begins by 15 exhaustion an conditions generation is rapid during this period but suddenly at its end. root photosynthetic capabilities conditions, (Sims and Singh 1978a; Hunt 1970). phase water, Since growth rate is the plant's photosynthetic growth is photosynthetic period indicates the season of optimum growing rapid most Growth (light, formation are adequate for high environmental in During the lag phase (first growth phase (second period) (Noggle and Fritz 1976). the a be determined by food reserves. rates prevailing by Larcher 1975; plant growth is limited by a small The curve and finally a quiescent or stationary plants initiated years an early season lag phase followed rapid growth p h a s e , phase. . water or ceases period) nutrients, f 12 180 ~0m m , 1977 Kw= 2 I mg/cm . K0 = 17 Sm m vcm - TREATMENT. YEAR Kw(WE)GHT CONSTANT) K0(AREA CONSTANT) "6 m m . 1977 Kw= 2 5 mg/cm . K0= I75m m z/cm I 20 PLANT LENGTH (CM) AG B PRESENT GREEN LEAF (cm) C MAXIMUM SOIL D DAWN PLANT ^ I--I V V 25mm, 1978 6 mm, 1978 Kw= 3 I mg/cm K0 = 19 6m m z/tm 8 0 r O m m , 1979 Kw= 2 Gmg/cm , Kq= I7 9 m m 2/cm MAY JUN J U L A U G Figure ^ o -°A ” A CUMULATIVE LEAF (cm) - -OA I 25mm. 1977 Kw =3 Smg/cm K0 = 19 9m m z/cm I. 6 mm, 1979 Kw= 2 8m g/cm K0 = 18 Smm2Zcm MAY JUN JU L AUG 12mm, 1979 Kw=2 SmgZcm K0 = 16 Amm2Zcm MAY JUN JUL AUG 25mm, 1979 Kw= 2 7 mgZcm K0 = 181 mm2/tm MAY JUN JU L AUG Cumulative growth (cm, solid line), green leaf length (cm, broken line), soil water status (A), and plant water status (B) of Agropyron smith!i plants subjected to four water t reatments (supplementation of natural rainfall to 0, 6 , 12, and 25 mm/week) in three years ( 1977-1979 ) . Growth and green leaf expanse expressed in mm (as measured) can be converted to weight or area by application of the constants provided (K^ and K ). The shading in bar 'A ' indicates the lowest soil water stress present in the upper 75 cm of the soil (clear = 0-5 negative bars, dots = 5-10 bars, hatching = 10-15 bars, and solid * 15+ bars. Shading in bar 'B 1 summarizes weekly measurements of dawn plant water potential (clear = 0-2 negative bars, dots - 2-10 bars, hatching - 10-20 bars, and solid - over 20 bars). Unit leaf rate calculations (Tables I and 2) are based on the leaf areas indicated by triangles on the green leaf curve and time periods between circles on the cumulative leaf c u r v e . 13 accumulation of m aterials), toxic substances increased photosynthesis, or to (inhibitors respiration diversion of or waste relative to photosynthate from vegetative growth to seed or storage reserves. Unit per Leaf Rates unit of green surface, calculated leaf by area. process calculations rate' doesn't unit Aboveground leaf production rate (ULR), dividing the rate of production by The necessary data appear in Fig. is preferred (mg.dm" 2 .day 1 ). demonstrated in Table I. with formulae over the once popular phrase 'net green I and the and The term 'unit leaf is sample rate is assimilation (NAR) because it clearly relates to leaf growth and suggest any relationship (Evans 1972 and Thomas 1980). to total production 14 Table I. Calculation of unit leaf rate. Unit leaf rate = rate of above ground production/per of photosynthetic area (= U L R ) . = ( W/ T) unit (1/A) where; T = a specified time period W = change in weight in mg during that time period = (change in leaf length read from Fig. I, upper c u r v e ) X ( K^, a weight conversion constant (mg/cm) reported in F i g . I ). 2 A = ' area in dm = (green length at the time considered from Fig. I , lower curve) X £Ka , an area conversion constant [mm /cm] reported in Fig. I) X (1/10 dm /mm ). Examples: Unit leaf rate for the early rapid growth phase of control 1977 is calculated as; ULR = 60 mg, = dm .da (570 mm - 3 60 mm) (0.21 mg/mm) (day 158 - day 144) X (300 mm) I. (1.75 m m ^ / m m ) (0.0001 dm^/mm^) Similarly unit leaf rate for the peak of green phase control 1977 is calculated as: ULR = 39 mg = (570 mm - 360 mm) (0.21 mg/mm) dm .da (day 158 - day 144) X (465 mm) I ____________ __ (1.75 m m 2 /mm) (0.0001 d 2 /mm2‘ ) of 15 At a given season ULR varies relatively little among treatments (Table early and the variation shows no consistent 2). Production averaged 78 mg.dm season, m g .dm -2 area, .day -I 32 these inconsistently -2 .day approximately and 7 mg.dm Because mg.dm -2 .day rates among -I at peak two weeks pattern day ^ in green past the area, peak 4 green -I . at the end of August (Table 2). differ relatively treatments, I little deduce and that the principal effect of irrigation has been on the area of the producing unit (leaf surface) rather than on its condition (photosynthetic capacity). Since ULR is primarily a function of (Potter and Jones 1977), photosynthetic photosynthesis I speculate that the maximum net rate of Agropyron smithii is equal to or greater than the ULR observed early in the log phase (78 -2 -I mg.dm .day ). Equality would occur if I) storage depot subsidies to shoot growth have ceased by the time the log phase of growth has b e g u n , 2 ) roots present in the early season support the sparse canopy adequately so there is no transport downward to support root growth, and 3 ) stem respiration is a constant proportion of total respiration. The (32 mg.dm decline in ULR later in the log phase of .day ) and the low production rate per unit of leaf surface observed late in the season (7 m g .dm probably understate these seasons. growth -2 .day the actual photosynthetic rates -I ), for The presumed understatement of production 16 Table 2. Unit Leaf Rates of Agropyron smith!i . - 2 , -I ULR (mg.diii .day aboveground) Early Rapid Growth Control 1977 1978 1979 6 mm 1977 1978 1979 12 mm 1977 1978 1979 At Peak Green After Peak Green At S e a s o n 's End 60 87 53 39 26 31 3 I I 7 3 13 69 106 64 43 29 40 9 2 4 8 5 6 —— —— 31 29 3 6 9 7 27* 24 28 5 4 3 6 6 78 32 4 7 8 2 I I H O 46 Wet 1977 1978 1979 Mean Standard Error 107 84 69 — Measurements not taken * Green material never p e a k e d , but continued to increase to the last measurement period in this year - 17 is due to increased allocation of photosynthate areas. Reallocation is probably the to storage major factor 6„ determining the declines recorded in the control, 12 mm plots where the canopy never c l o s e d . It is and likely that declines in wet plot ULR are due both to reallocation and to competition for light -- ie reduced photosynthesis -- after canopy c l o sure. The very lowest ULR (4 mg.dm —2 .day —1 ) was observed just after the end of the log phase when growth rates were low leaf areas and available water were but green Because unit it seems very unlikely that to rates speculate preceeding -2 lower that, photosynthetic mg.dm photosynthesis of leaf area should plunge at mid-season — rates .day -I should were, at a ) but leaf and, minimum, -2 at a m a x i m u m , .day -I ). roots. and Wiebe the and the not observed in above-ground 7 early production, c rowns, This is consistent with the report 1973) that, net between equal to I The excess photosynthesis appear as growth or storage in and — ra t e s , succeeding unit leaf rates (ie 32 season ULR (78 m g .dm predicted, unit per from high end-of-season rates despite rates and than high. in Agropyron smithii, rhizomes, (Sosebee almost all translocation during the quiescent phase is to the roots. Estimation of production. two methods methods The following paragraphs review for estimating aboveground production and for calculating total production. Table two 3 18 summarizes these methods and Table 4 compares the results of all methods. Leaf measurements made between mid-May and the end of August for permit us to calculate net aboveground any sub-period by either production of two unit of length (Ky , summarized in Second, production Fig. for Fig. Such estimates any very short period of course, Fig. are aboveground m g .dm I lower curve). the product of leaf Unit extension from the slope of the upper curve of Fig. and the weight of a unit of length I). in I) by the weight is the product of unit leaf rate (ULR, rate is, divided First, Table 4. rate (mm.day ^ , I) Fig. I). day ■*") and leaf surface (mm. leaf methods. can be estimated by multiplying the change plant length during any period (mm. per production (mg.mm Fig. I) by the green leaf area producing it (lower cu r v e , For longer periods, one can estimate total production by plotting instantaneous production, estimated in integrate this matter, under the c u r v e . over a series of periods and Identical estimates must result if same data base is u s e d . than Either estimate is more accurate those made by harvest methods because material before harvest the lost to either grazing or senescence is included (Sims and Singh 1975). the Aboveground production might occur before measurement season. We doubt that or post after season 19 Table 3. Calculation of seasonal demonstration of methods. production, a Method I, read it directly from production graphs of Figure I. Seasonal production = P (mg/plant/season) = change in leaf length (■»"»fllull-'“ initial' from I, upper curve) X K (a constant converting mm to mg, (presented) in FigurewI). Method 2, calculate it from graphs in Figure I. Instantaneous production (mg/plant/day) = ULR x green leaf area 2 ULR (mg/dm /day) is read from Table 2 or calculated from Fig. I by methods illustrated in (Table I). green leaf area = gregn leaf length (mm, from lower Fig. I) X K q (mm /mm, presented in Fig. I). Seasonal production = days instantaneous production curve, (mg/plant/da) x This was estimated by plotting instantaneous rates over time and integrating under the curve by cutting out the area and comparing its weight with weights of known areas. Three sets of rates were considered. If we assume ULR = those actually observed (Fig. I and Table I), production calculated from method I equals that calculated by method 2 . If we assume (see text) that the initial ULR persists until the peak of green leaf area and end-of-season ULR applies for the remaining time, the seasonal production by method 2 exceeds that calculated by method I significantly. Table 4 summarizes the differences in production for the rapid growth and quiescent periods; .we believe the unobserved production contributes to below ground growth Table 5. If we assume (see text) that the initial ULR persists until the peak of green leaf area and that ULR after that time is actually ten times end-of-season-ULR (approximately initial growth rates) production is further increased, but without violation of possible root growth rates. Table 4 Parame ter 3 Season Production (mg/plant) of^individuals of Agropyrbn smithii grown under four irrigation regimes. 2 Aboveground production P E ' Q T Minimum total production P E T Q Maximum Total producti o n P E Q T Treatment and year O mm 1977 1978 1979 76 78 70 44 202 74 19 16 12 139 301 156 76 78 70 55 523 100 31 16 34 162 61 20 76 78 70 55 523 100 312 160 343 443 761 513 6 mm 1977 1978 1979 86 88 67 53 112 46 49 9 38 188 209 151 86 88 67 62 351 81 49 30 38 197 469 186 80 88 67 62 351 81 485 301 380 633 740 528 12 mm 1977 1978 1979 94 71 302 53 35 26 431 150 1977 1978 1979 42 69 85 357 241 202 11 33 20 510 343 307 PO Wet — _ - O _ 94 71 621 73 142 1324 69 588 85 323 35 26 750 170 11 1477 33 690 29 437 94 71 621 73 350 260 1065 404 142 1324 588 69 85 323 HO 250 292 1576 907 700 Irrigation regimes were an unirrigated control (O mm), a plot guaranteed 6 mm per week (6 mm), a plot guaranteed 12 mm per week (12 ram), and a plot in which soil water potentials were maintained above -2 bars with irrigiations of 25 mm per week or more. Aboveground production was estimated by multiplying leaf length (mm) produced in the period by the weight per mm. Total production was estimated by integrating under a curve of leaf production rate created by multiplying observed green leaf areas by either a minimum or maximum estimate of the photosyynthetic rate. 3 Production was estimated for the period before measurements began in May (preseason = P ) for the period of exponential growth before the peak-of-green (E ), for the quiescent period after peak-of-green (Q) and for the total season (T). 21 production was significant because the soils dried and the plants turned observable brown as measurements production green were is Estimates (Fig. I )• plant Preseason material initiated. easily growth present Preseason estimated by was the are presentated in Table 4. when aboveground first Our method. data cannot provide the rate estimates needed for the second method. Belowground smithii production . must grasslands aboveground masses since occur in belowground (Weaver et al 1981). Agropyron masses exceed Consideration of the second method of estimating production outlined and the unit estimating leaf this rate discussion suggests belowground production: a above way one of should integrate across time the product of green leaf area (Fig. I, lower curve) and its production r a t e . production (ULR) the production calculated as For aboveground rate was the unit above. . For total leaf rate production a production rate including belowground transport is n eeded. Two possibilities, labeled maximal and minimal, are outlined and applied below. A estimate of total production was made by summing production in three subseasons 5 the preseason, the period after minimal before maximum green leaf a r e a , maximum green leaf area. assumed calculated to be entirely and the period Preseason production aboveground and is therefore as the product of aboveground growth (mm) and 22 weight per unit production area is (Fig. of length (K^=mg/mm). Early calculated as the integral of I) and green a maximal unit leaf rate calculated from the curves in Figure I. season (Table observed drop in ULR during the log growth due to increasing transport to belowground o r g a n s . leaf phase (Fig. I) and the ULR at results appear in Table 4. production is season's is Late production is calculated as the integral of area 2) This assumes that the season leaf green end. The Our minimal estimate of total- about 150% of measured aboveground suspect that the proceeding procedure we that production. While we underestimates following total procedure total production. production, believe will give us a maximal We assume, as above, the estimate that of preseason production is entirely aboveground (for lack of data to do otherwise) and therefore underestimate total production if actual carbon transport is downward and overestimate it if carbon transport calculation season maximal upward. We assume early season production estimate which for differs, then, only in on late the I) it is generally that most late season photosynthate is stored Wiebe 1973); that early correct. we estimated as ten times two reasons: again based ULR and actual green leaf, areas is production estimate of is Our season minimal believed (Sosebee and and 2) early season unit leaf rates are about 23 ten times late season unit photosynthetic rates leaf rates (Table 2) do not actually fall, so, 90% of photosynthate would be transported below g r o u n d . our estimate maximal bec a u s e , green leaf areas, if the We call while it is based on actual estimated photosynthetic rates may be high since water and nutrient resources per unit of leaf area are probably less available late in the summer than in the spring. Table 4 Maximal production estimates presented in are about 300% of aboveground production rates measured by method I. Belowground r h i zome , pr o d u c t i o n . and aboveground crown) production downward absence flows During calculated observed, the therefore ie an implies 8 estimate SE and production that there and will To the extent that be net log phase transport for is of an carbon minimal downward and maximal belowground production of 43 +6 SE % of is total is net Quiescent phase transport averages % of total net 92+1 both similar average production (Table 6). + total belowground production may actually be similarly estimates; (root, In the preseason our assumptions of root growth. negative. 19 from transport are u p w a r d , production is easily calculated by substracting presented in Table 5. no Belowground production! in SE % in the maximal latter seems more reasonable since 98, the roots are belowground in our 0, 96, 6mm, the minimal estimate. The 95, and 56% of 12mm, and wet 24 Table 5. Parameter Season I Belowground production (mg/plant) calculated using minimum or maximum estimates of p hotosynthetic rates. 2 Production, minimum P E T Q Production , maximum P E T Q .mg/plant1 Treatment and year 0 mm 1977 1978 1979 0 0 0 11 316 26 12 0 22 23 316 . 48 0 0 0 11 316 26 293 144 331 304 460 357 6 mm 1977 1978 1979 0 0 0 9 239 35 0 21 0 9 260 35 0 0 0 9 239 35 436 242 342 445 531 377 12 mm 1977 1978 1979 — 0 0 — 319 20 — 0 0 _ 319 20 0 0 319 20 315 234 634 254 1977 1978 1979 0 0 0 997 347 101 .0 0 9 967 347 130 0 0 0 997 347 101 99 1066 217 564 272 393 Wet Belowground production = total production (Table 4) minus above ground production (Table 4). Production was estimated for the period before measurements began in May (preseason = P), for the period of exponential growth before the peak-of-green (E)s for the quiescent period after peak-of-greenn (Q), and for the total season (T). Irrigation regernes were an unirrigated control (0 mm), a plot guaranteed 6 mm per week (6 mm), a plot guaranteed 12 mm per week (12 mm) and a plot in which soil water potentials were maintained above - 2 bars with irrigations of 25 mm per week or more. 25 Table 6. Belowground production using minimum or p h o t osynthetic r a t e s . Parameter Season I (% of total) calculated maximum estimates of Production , minimum P E T Q Production, maximum P E T Q % of Total2 Treatment and year 0 mm 1977 1978 1979 0 0 0 20 60 26 38 0 65 14 51 24 0 0 0 20 60 26 94 90 96 69 60 70 6 mm 1977 1978 1979 0 0 0 15 68 43 0 70 0 5 55 19 0 0 0 15 68 43 90 97 90 70 72 71 12 mm 1977 1978 1979 _ _ 0 0 51 27 0 0 43 12 0 0 51 27 90 90 60 63 1977 1978 1979 0 0 0 73 59 6 0 0 8 65 50 6 0 0 0 73 59 6 90 87 I 68 42 3 Wet . Belowground production = total production (Table 4) minus above ground production (Table 4). Belowground production is expressed as a percentage of total production reported in Table 4. Production was estimated for the period before measurements began in May (preseason = P), for the period of exponential growth before the peak-of-green (E), for the quiescent period after peak-of-green (Q), and for the total season (T). Irrigation regimes were an unirrigated control (0 mm), a plot guaranteed 6 mm per week (6 mm), a plot guaranteed 12 mm per week (12 mm) and a plot in which soil water potentials were maintained above - 2 bars with irrigations of 25 mm per week or more. 26 treatments across respectively season (minimal total one (Weaver.et calculates al 1981). Summing that between 3 3 + 6 SE estimate) and 64 + 3 SE % (maximal estimate) net production is deposited in the % of belowground compart m e n t . Factors controlling observations availability production support is one the major and growth. : Three that water conclusion d e t e r m i n a n t . of production. F i r s t , increased water availability slows the rate of loss of green leaf areas and results in maintenance of a larger photosynthetic surface in the rapid (Fig. growth phase I) which might function late or after occurring during the quiescent phase. leaf any rainstorms The amount of green material on the average plant peaked before the end of the rapid growth phase of growth and was maintained for two 1979, to three weeks before it began to and wet plots. dry small populations, less rapid in the 6 mm, The same is true in dry 1977 super-adequate water supplies, Even In the decline in green leaf material was most rapid in the dry plot and progressively mm, decline. due to heavy watering 12 when and resulted in no decline in the wet plot. in the wet summer of 1978 when declines were similar in the control, 6 mm, and 12 mm treatments, the drop was least in the wet treatment. Secondly, in relatively leaves began to die (Fig. I), dry years (1977 and 1979) and growth stopped earlier 27 in the (Fig. a dry control treatment 2). dual than in the wet treatment Extending the period in which growth occurs has positive effect -- f i r s t , productive period and s e c o n d , on the length of the on any returns on additions to photosynthetic surface due to increased production, to a 'compound interest e f f e c t * . treatme n t , In contrast to the ie wet the 6 mm and 12 mm treatments had little or no effect on the length of the active growth period (Fig. 2). I tentatively conclude that the 6 mm and 12 mm treatments produced little additional plant material despite the additional water available. Thirdly, in all seasons, growth rates declined with increasing plant water stress (Fig. 3). Maximum above­ ground growth occurred when plant water stresses were less than -5 bars and cessation of growth occurred water stresses higher near -20 bars. stresses (Fig. 3) was at plant The scatter associated with probably caused by small spurts of growth after rainstorms. While such growth would have occurred in nonrstress moments it would associated in our records with low plant water (indicative of high stresses) have been potentials read at the beginning and end of the measurement p e r i o d . While growth always ceased when water was exhausted, the fact that it always slowed markedly in mid-July, though factors, water was not perhaps season, limiting, suggests also limit growth. that even other, The reader 28 Figure 2 * t illers in m m / d a y . 29 6 m m , 1977 O m m 1 1977 I5 -D -D GROWTH RATE (mm/day) 5 6 mm, 1978 r 20 ----- a— Ieeeeeeeeej — — — -£2 MM ^ I I Kg » I 9 6 m m 2/m m 6 m m , 1979 20 Ar Al' j m g /m m K a = I SS m m 2Zmm „ _ - jm g /m m K a = I 7 9 m m 2/m m _D 5 E I MAY JUN JUL AUG _____ r i I i I I I I r MAY JUN JUL AUG 30 TREATMENT, YEAR 2 5 m m , 1977 A WATER ADDED (m m ) r a in □ ir r ig a tio n B SOIL WATER POTENTIAL (MPn) C PLANT WATER POTENTIAL (MPa) * L2 25 0 -i I j. .Lm HiiL I I 1 K w = O 3 5 m g /m m K a = I 9 9 m m z/m m WEIGHT CONSTANT (m g /m m ) AR E A CONSTANT (m m 2/m m ) I5 D GROWTH OF INITIAL PLA N TS (m m /da) GROWTH RATE (mm/day) 5 E. T ILLE R GROWTH (m m /d a ) -D ~ I 2 5 m m , 1978 r 20 ArIiL L I If kJ I B LI I I I I--H I-H Kw = O 2 2 m g/m m K a = I 5 5 m m 2/m m I I 2 5 m m . 1979 a r A F20 ; ,I B C 32 Kw = 0 2 5 m gg //m mm r 6 4 m m vm m D 5 E Figure 2. T “r— 7 AUG Continued. l—i Ik I I I I I............ =L-T= KZ Kw = 0 2 7 m g /rn m K a = I 81 m m vm m 31 PLANT WATER POTENTIAL CMPaD Figure 3. The effect of water potential and season on unit leaf r a t e . The dashed lines are hand fit- 32 should verify from Figure 2 that growth slowed in the wet plot in kept plant mid-July in all years despite moist water Comparison cessation a of potentials between the wet and control O soils and plots that -5 bars. shows that of growth is probably not due to achievement of maximum plant exhaustion of concurrently size, to nutrients, internal since in shading, 1978 in dry plots and in wet plots larger plants, it or to occurred (which, with had more internal shading and had consumed more nutrients). I hypothesize, above-ground g r o w t h , at mid-summer — therefore, that the potential and therefore production, perhaps due preparation for fall and winter. to for is reduced daylength-induced Three lines of evidence support the daylength-control speculation. First, above­ ground growth ceases when no other factor seems to limit it. Second, the fact that growth rates associated with a given water stress fall as the season progresses (Fig. suggests to that photosynthate is being diverted from storage 1970). (Trlica 1977, I Moser 1977, and Brown & Blaser photosynthetic capacity of healthy green leaves with Thirdly, variety Bouteloua comata, growth do not accept.the alternative hypothesis season. of range grasses, gracilis, all 3) that declines under experimental conditions including Andropogon Agropyron scoparius, a smithii, and I grew more rapidly under energetically Stipa equal 33 short night conditions than under long night conditions (Weaver and Forcella 1983). While the midsummer, capacity for growth was reduced drought-stressed plants apparently retain some capacity to respond to late summer showers. both in Plants dry control plots and 6 mm plots grew after 1977 and extension greater 1979 (Fig. rates throughout 170, mm from showers plots and 400 leaf percent than those of the control plots in respectively. late August 1977, Though mid- and early growth continued the summer in 12 mm and wet plots, no effects of summer showers could be detected. Late season growth in the wetter plots may have been masked by the irrigation state In the 6 217, early August 1977, 1979, responses 2). were 150, (PCO.Ol) July 1977, July at treatments, (e.g. or prevented by carbohydrate balance) a physiological induced by regular watering. Growth response increased with J^o water increasing extension availability. treatment culm was 107 %, the average 12 mm treatment culm in (100 %), the 6 mm while the average 25 mm treatment culm was 207 dry 1977 and 1979 and 135 % in wet Table 7). average When with % control water Leaf compared was 106 %, the s u pplements. I; / Statistical analysis — ANOVA after logarithmic transformation 1978 (Fig. -- of the growth data summarized in Figure 2 show that plants in the control, 6 mm, and 12 mm plots 34 Table 7. Total aboveground yields, on culm length (mm) and biomass (mg) b a s e s , of average Agropyron smith!! plants from plots subjected to four water r e g i m e s . Each datum is reexpressed (in parentheses) as a percentage of the co n t r o l . Treatments Control 6 mm 12 mm Wet Total length production (mm) ■ -•— 1977 606 (100%) 735 (111%) 1978 1245 (100%) 1340 (106%) 1365 1979 585 (100%) 600 (102%) 600 1455 (220%) (110%) 1680 (135%) (102%) 1140 (195%) 510 (367%) Total mass production (mg) 1977 139 (100%) 188 (135%) 1978 301 (100%) 209 (6 9%) 431 (143%) 343 (114%) 1979 156 (100%) 151 (97%) 150 (96%) 307 (197%) — — 35 grow less than those in the wet plots ( P < 0 .0001) years. in in all Plants from the control plots grew less than those the 6 mm and 12 mm treatments in all years Although growth rates were not different 12 mm treatments in wet 1978, (P<0.02). in the 6 mm and they did differ in dry 1979 (P<0.0001). When weights with leaf (K^) length is multiplied specific there is no clear pattern of yield increasing water availability Despite by increases leaf increase (Table 4 or Table in growth described a b o v e , we 7). cannot therefore confidently conclude that per-plant yields increased yields by 6 mm or 12 mm would increased i n c rease, irrigation however, (see b e l o w ) . if were regimes. plant Total densities Per-plant yield increases due to the wet treatment are obv i o u s . Tillers Although 1977, were present in every plot in it is assumed that since tillers appeared three treatments under study, present in the 12 mm plot. Tillers, defined as lateral vegetative shoots, and growing intravaginally growth while year. measurements were not taken in the 12 mm plot in remaining axil, every — less upward (Moser which than 1977 they were as used leaf Thomas was measured only in 1978 that seasonal pattern (Fig. of parent plants 2). the also here, are arising from a leaf within the and in sheath, 1980). and had Tiller 1979 a ie — similar Tiller growth declined more 36 r a p idly, however, in response to drought stress than did the growth of parent plants. The reader will note (Table 7) that production of the average due, but culm was less in 1979 than in 1977. in part, is to the fact that 1979 was drier than 1977, probably undoubtedly due are (discussed here) elsewhere) and population of ) increased with increasing competition, plant a product of individual population size and (to be expected (and observed) - that this paper 'water of res ponses discussed tO the increases in understates the in so doing will conclude — - due density densities especially in the wet plots. benefits of added water. \ to will realize that the effects reader supplement s omis sion also associated which were observed, The This may be 37 CONCLUSIONS The results discussed above suggest five major conclus i o n s : 1) The cumulative growth of individual plants (gm/plant) followed the usual sigmoidal c u r v e . 2) Green curve leaf which peaked area generally exhibited peaked about the time the and sometimes before significant a bellshaped aboveground plant mass or soil area was water stress developed. 3) Aboveground production largest early in the season, peak of green leaf a r e a , fell to a low soon after the and rose slightly in summer. The reserves from the previous season. leaf first per unit of leaf growth the late built ^ith The decline in unit must have been rates through the log growth phase to the post-peak- of-green-stage increasing was amounts belowground probably due to of photosyntate to storage. allocation root growth growth; observation that Seasonal changes and By growth analysis it is estimated that one to two thirds of net photosynthate is devoted belowground of this .55-95% is not inconsistent of the plant is with to the belowground. in allocation of photosynthate may be 38 triggered by exhaustion of water and/or changes in daylength. 4) On a plant length basis, 6-7% after mm/week) plant per-plant growth increased light shower treatments (guarantees, and 33-107% when soils were kept weight basis, however, of moist. aboveground 6-12 On yields a were significantly increased only by the wet treatment. 5) Yield per-plant effects effects that effects of water treatments are a product (discussed here) and (the subject of another study). water supplements ever reduced plant It is plant Until the density effects are multiplied in, conclude that the effects reported here magnitude of water treatment effects. ! of density doubtful densities. one can only understate the 39 LITERATURE CITED A c e v e d o , E ., T. C. Hsiao, and D. W . Henderson. 1971. Immediate and subsequent growth responses of maize leaves to changes in water status. Plant Physiol. 48:,6 31-636. Acevedo, E., 1979. osmotic field. E . F e t e t e s , T . C . Hsiao, and D. W . Henderson. Diurnal growth trends, water potential, and adjustment of maize and soughum leaves in the Plant Physiol. 64:476-480. Ackerson, R. C. 1980. Stomatal response of cotton to water stress and abscisic acid as affected by water stress history. Plant Physiol. 65:455-459. B a l a s k o , J . A. and D . Smith. 197^ Carbohydrates in grasses: V. Incorporation of C into plant parts and nonstructural carbohydrates of timothy (Phleum pratense L.) at three developmental stages. Crop S c i . 13:19-22. Begg, J. E. and M. J. Wright. 1964. Relative effectiveness of top and basal leaves for the growth of vegetative shoots and reed canary grass. Crop Sci. 4:607-609. Beyer, W. H. CRC Press, 1979. Fla. CRC Standard Mathematical T a b l e s . Boyer, J.S . 1970. Leaf enlargement and metabolic rates in corn, soybean, and sunflower at various leaf water potentials. Plant Physiol. 46:233-235. Brown, R .W. 1977. Water relations of range plants. Rangeland Plant Physiology (E. Sosebee ed.). Range Science Series No. 4. p. 98-140. Brown, R . H . arid R . E . B l a s e r . 1970. Soil moisture and temperature effects on growth and soluble carbohydrates of orchardgrass (Dactylis g l omerate) . Crop Sci. 10:213-216. 40 Charley, J . L . 1977. Mineral cycling In rangeland ecosystems. Rangeland Plant Physiology (R. E. Sosebee ed.). Range Science Series No. 4. p. 216256. Dahl, B . E. and D. N . Ryder. 1977. Developmental morphology and management implications. Rangeland Plant Physiology (E. Sosbee ed.). Range Science Series No. 4. p. 258-290. Dixon, W . J. and F . J. Massey. 1969. statistical analysis. McGraw-Hill: 322-324. Erickson, Rev. R . 0. 1976. Plant Physiol. Introduction to New York. pi Modeling of plant growth. 27:407-434. Ann. Evans, G. C. 1972. The quantitative analysis of plant growth. Studies in Ecology. Vol. I. University of Calif. Press. Fischer, R . A. and R . M . Hagan. 1965. relations, irrigation management and E x p l . Agric. 1:161-177. Plant water crop yield. Golubev, V. N. 1971. Growth of vegetative shoots in grasses and sedge under conditions of the southern Crimean Shore. S o v . J. Ecol. 2 (4):357-359. . Haglund, B. M. 1980. Proline and valine - cues which stimulate grasshopper herbivory during drought stress? Nature 288:697-698. Harper, J. L. 1977. Population Academic Press: New York. biology of p l ants. Henckel, P . A. 1964. Physiology of plants under drought. Ann. Rev. Plant Physiol. 15:363-386. Hess, W. 1974. Weather and climate modification. . Wiley and Sons, N.Y. 841 pgs. Hitchcock, A. S . and A. Chase. grasses of the United States. 200. p . 23"4l J. 1950. Manual of the U .S .D .A . Mi sc. Pub. Holroyd III, Edmund. 1978. Ph.D. m e terologist. USDI Bureau of Reclamation Division of Atmospheric Resources Research. Skywater Office, Montrose, Co l o r a d o . Hsiao, T . C . 1973. Plant response to water stress. Rev. Plant Physiol. 24:519-570. Ann. 41 Hunt, W. F. 1970. The influence of leaf death on the rate of accumulation of green herbage during pasture regrowth. Itai and Vaadia. 1971. Cytokinin activity in stressed s h o o t s . Plant P h y s i o l . 47:87-90. water- K u c h l e r , A. W. 1964. Potential natural vegetation of the conterminous United S t a t e s . A m e r . Geo. S o c . SpTcial P u b . 36. 154 p . and map. L a r cher , W. 1975. Physiological Sp r inger-Verlag: New Y o r k . p. 252. plant ecology. Leopold, A. C . 1975 . Aging, senescence, and turnover in plants. Bio. Science 25:659-662. Mason, B. Press: J. 1971. The physics of c l o u d s . O x f o r d . p. 602-603. Clarendon M i l t h o r p e , F . L . and J . M o o r b y . 1974. An introduction to crop ph y s i o l o g y . Cambridge University Press: New Y o r k . p . 202. Moore, R. T. 1977. Gas exchange and photosynthetic pathways in range plants. Rangeland Plant Physiology (E . Sosebee e d .). Range Science Series No. 4. p. 146. Moser, L . E . 1977. Carbohydrate translocation in range plants. Rangeland Plant Physiology (E . Sosebee ed.). Range Science Series No. 4. p. 4 8 - 7 1 . N o g g l e , G . R . and g. J . F i r t z . ph y s i o l o g y . Prentice-Hall: O s t l e , B . and R . M e n s i n g . 1975. Iowa State University Press: 490. 1976. Introductory plant New Jersey. Statistics in research. Ames, Iowa. p . 489- Potter, J . R . and J . W . J ones. 1977 . Leaf area partitioning as an important factor in growth. Plant Physiol. 59:10-14. Ritchie, G . A. and T . M . H i n c k l e y . 1978. The pressure chamber as an intrument for ecological research. Advances in Field Research. (J . Gragg, ed.). Academic Press: New Y o r k . p. 165-254. Scholander, P . F., H . T . H a m m e l , D . B r a d street, and E . A. Hemmingsen. 1965. Sap pressure in vascular p l a n t s . S c i . 148:339-346. 42 S i m s , P • L . . and J . S . Singh. 1978a. The structure and function of ten western North American grasslands. II. Intra-seasonal dynamics in primary producer compartments. J. Ecol. 66:547-572. Sims, P. L . and J. S . Singh. 1978b. The structure and function of ten western North American grasslands. IV. Compartmental Transfers and Energy Flow Within the Ecosystem. J. Ecol. 66:983-1009. Singh, J., W . Lauenroth and R . Steinhorst. 1975. Review and assessment of various techniques for estimating net aerial primary production in grasslands from harvest data. B o t . Review 41:181-232. Slay ter, R . 0. 1967. Press: New York. Plant-water r e l a tionhips♦ p. 366. Academic S o s ebee , R . E . and H . H . Wiebe. 1971. Effect of water stress and clipping on photosynthate translocation in two grasses. Agron. J. 63:14-17. Sosebee, R . E . and H. H. Wiebe. 1973. Effect of phonological development on radiophosphorous translocation from leaves in creasted wheatgrass. Oecologia 13:103-112. Stewart, C. R. 1978. Role of carbohydrates in proline accumulation in wilted barley leaves. Plant Physiol. 61:775-778. Taylor, S.., D . Evans, and W . Kemper. 1961. . Evaluating soil water. Ag. E x p t . Station Bull. 426. Utah State Univ., Logan. 67 pgs. Thomas, H . 1980. Terminology and definitions in studies of grassland plants. Grass arid Forage Sci. 35:13-23. Trlica, M. J. 1977. Distribution and utilization of carbohydrate reserves in range plants. Rangeland Plant Physiology (E. Sosebee ed.). Range Science Series No. 4. p. 74-96. U. S . Department of Agriculture, Agricultural Research Services. 1972. Grass varieties in the United States. U.S.D.A. Agricultural Handbook 170. U.S. Gov. Printing Office, Washington, D.C. p. 8-9. Valentine, J. 1980. Range development and improvements. Brigham Young Univ. Provo, Utah. 545 pgs. 43 Wardlaw, I. F. 1974. Phloem transport; physical, chemical or impossible. A n n u . Rev. Plant Physiol. 25:515-539. Weaver, T., J. B i r k b y , J . Welker, and J. N e w b a u e r . 1981. Short-term responses of an Agropyron smithii grassland to six water regimes. IN; G . Knutsen and R . Moy eds. State of Montana Act. activities in the High Plains Cooperative Program. 1975-1980. Helena, MT. 287 p g s . Weaver, T . and F . Forcella. 1983. Nyctoperiod (photoperiod) control of vegetative growth . of high plains grasses. p. 103-110. IN: L. Holman and G . Knutsen 198 eds. 1983 State of Montana activities in the High Plains Cooperative Program: 1981-1983. Mont. Dept. of Natural Resources and Conservation, Helena. 171 pgs. rt MONTANA STATE IJNIVFocttv i m n . WftlN '" N378 Nk22 Newbauer, j. j. cop.2 Growth response of Agropyron smithii N378 N422 cop. 2 C A V ^ O H D 40