ONLINE APPENDIX A. Precipitation and demographic information during the studies Annual precipitation (mm) recorded near each field site, classifying annual period as wet, normal or dry, according to the 75th and 25th percentiles of the last 30 years of precipitation. Deterministic population growth rate (λ) ± 95% C. I. (999 iterations from jackknife) ≥ 1 implies demographic viability, and < 1 indicates demographic decline. Period Cryptantha flava – Utah Carrichtera annua – Israel Precipitation Type λ Precipitation Type λ 1997-1998 491.744 Wet 0.94 ± 0.009 - - - 1998-1999 466.852 Wet 0.97 ± 0.011 - - - 1999-2000 382.778 Normal 0.96 ± 0.009 - - - 2000-2001 348.742 Normal 0.67 ± 0.002 - - - 2001-2002 174.24 Dry - - - 2002-2003 236.98 Dry 351.80 Wet 2.32 ± 0.008 2003-2004 252.984 Dry 0.93 ± 0.012 234.80 Normal 0.47 ± 0.001 2004-2005 533.65 Wet 0.97 ± 0.008 377.30 Wet 1.64 ± 0.005 2005-2006 382.78 Normal 0.73 ± 0.006 195.60 Dry 0.43 ± 0.002 2006-2007 313.94 Normal 0.71 ± 0.006 259.90 Normal 0.79 ± 0.002 319.28 Normal 181.20 Dry 0.450 ± 0.001 275.08 Dry 113.80 Dry 12.42 ± 0.070 2009-2010 321.56 Normal 0.84 ± 0.006 - - - 2010-2011 328.01 Normal 0.98 ± 0.008 - - - 75th percentile 391.22 2007-2008 2008-2009 0.59 ± 0.002 1.00 ± 0.006 1.18 ± 0.005 321.31 § Last 30-year average 350.75 25th percentile 295.21 264.43 212.46 2002 census was not carried out and the population growth rate (λ) represents the 2001-2003 population dynamics. ONLINE APPENDIX B. Details of the IPMs and PMMs used in this study Integral Projection Model (IPM) for Cryptantha flava An IPM describes the dynamics of a population by linking size distribution of individuals at time t , n(x, t) to their size distribution the next period t + 1, n(y, t + 1). This is accomplished by explicitly incorporating underlying demographic processes, the vital rates. This linkage is based on the contribution of established individuals, described by a kernel p(x,y), and their offspring, described by a kernel f(x,y). π π(π¦, π‘ + 1) = ∫πΌ [π(π₯, π¦) + π(π₯, π¦)] β π(π₯, π‘) β ππ₯ Both demographic processes are integrated for the range of sizes observed in the field: α = 1 rosette to ω = 60 rosettes. Although individuals larger than 60 rosettes exist in the field, their frequency is low (0.6%) and we did not include them in the output shown here, though their effects on the population were accounted for because we included all individuals, regardless of size, in our vital rate function parameterization (below). To parameterize the vital rate functions that integrate the IPM, we used data for each annual period. Each IPM included six vital rates (see Figure 3 and Online Appendix C). The first two define the kernel p: survival during the annual period t to t+1 (σ), and change in individual size from t to t+1 (γ) together with its associated variance. The remaining four vital rates define the kernel f: probability of flowering in year t (φ), number of flowering rosettes produced per individual that year (χ), probability of seedling establishment (ε), and size distribution of seedlings at the end of the annual period, in t+1 (ϑ) (Figure 3). Seedling establishment rates ε also include seed production per flowering rosette and seed germination, and here we treat them as a black box since we did not measure them separately in the field. Survival (σ) and flowering probabilities (φ) were modeled using logistic regressions. The size distribution of seedlings (ϑ) was modeled with a negative Poisson regression. The vital rates γ and χ were analyzed using linear regressions. For each vital rate parameterization, we used linear, quadratic and cubic functions and retained the one that resulted in the lowest Akaike Index Criterion score. π(π₯, π¦) = π(π₯) β πΎ(π₯, π¦) π(π₯, π¦) = π(π₯) β π(π₯) β π β π(π¦) In order to calculate the population growth rates and elasticities involved in our predicting scenarios (See Projecting demographic effects of changes in precipitation section) on this demographic model, one needs to first discretize the IPMs. This means that the kernel k of each IPM is converted (discretized) into a projection matrix K of large dimensions by imposing a mesh onto k [1-3]. Because mesh size can affect model output [4], we discretized each of our IPM kernels with 29 x 29, 59 x 59 and 119 x 119 mesh points over the state variable size, resulting in discrete categories in increments of 2, 1 and 0.66 rosettes, respectively. Since the calculated values of λ, stable stage distribution and relative reproductive output stayed fairly constant regardless of mesh size (not shown), we opted for the 59 × 59 mesh. This mesh size choice also allowed for a straightforward interpretation because each mesh point corresponds to a one-rosette change in individual size. Periodic Matrix Model (PPM) for Carrichtera annua We described the life cycle of Carrichtera with a PMM of three seasons within the annual period: dormant (k = 1 in figure 3.b), post-dormant (k = 2) and pre-dormant (k = 3) seasons. The population dynamics of season i are represented by a periodic matrix Bk which, similarly to an IPM, projects the population vector n from the beginning to the end of season k. Bk projects the population back to the beginning of the dormant season. Stages π©1 = ππππππππ π·ππππππ‘ π πππ πΊπππππππππ π πππ πΏπΊπππ 0 Stages π©2 = π ππππππ’ππ‘ππ£π π·ππππππ‘ π πππ ππππππππ π 0 Stages π©3 = πΊπππππππππ π πππ π·ππππππ‘ π πππ π·ππππππ‘ π πππ 0 πΏπ΅πππ1 π·ππππππ‘ π πππ 0 πΏπ΅πππ2 π ππππππ’ππ‘ππ£π ππΊπππ ππ΅πππ π·ππππππ‘ π πππ ππΊπππ πΏπ΅πππ3 Note that the season length need not be the same for each Bk, and that the stage type need not be the same from one season to the next [1]. In order to parameterize the Bk seasonal matrices, we used data for each annual period. Vital rates were estimated from mean field values. Seedling survival (σ) was directly estimated from permanent quadrat censuses. The remaining vital rates were calculated using the following approximations. First, we calculated per capita fecundity (ψ, the summation of column 1 in B3) from individual biomass records and the regression between seed number and reproductive individual biomass (F1,26 = 725.8, P < 0.001, R² = 0.97). As an estimate for the missing biomass record of 2005, we used the average biomass of all other sampling years. Second, we used the aforementioned seed bank experiment to determine (i) the percentage of non-dormant seeds by dividing the number of seeds germinating the first annual period by the total number of seeds germinating over all three annual periods, (ii) the proportion of dormant seeds by dividing the number of seeds germinating in the second and third annual periods by the total number of seeds germinating, (iii) the proportion of dormant seeds that became germinable after one annual period by dividing the number of seeds germinating in second annual period by the total number of dormant seeds, and (iv) the proportion of dormant seeds that remain dormant for more than one annual period by dividing the number of seeds germinating in the third annual period by the total number of dormant seeds. Since these proportions were always measured under the same experimental conditions, we took the mean proportions over all sampling annual periods as constant values for estimates of seed bank processes (online appendix A). Proportions (i) and (ii) were used to split the per capita fecundity into contribution to germinable seeds (ψGerm) and contribution to dormant seeds (ψBank). Proportion (iii) was used as an estimate for the transition from dormant to germinable seeds (εGerm). Proportions (iv) were used as estimates for the stasis of dormant seeds for each season (δBank1, δBank2, and δBank3). Germination (δGerm) was estimated as the ratio between number of seedlings and germinable seeds. Strictly speaking, δGerm is a combination of germination, seed mortality, and seed dispersal. Because we did not measure these processes separately, they are treated in the vital rate δGerm as a black box, although we must note that seed dispersal is negligible in this system [5] while granivores are known to consume large fractions of the total seed crop produced in deserts [6]. In our model, we assumed that germinable seeds that did not germinate after the dormant season were lost from the population. Likewise, we assumed that seed bank seeds can only become germinable seeds right before the dormant season (note that for B1 and B2, only the main diagonal elements ≠ 0). Back-multiplying all seasonal matrices Bk in the same annual period, from May of year t to May of year t + 1, results in the A matrix, which describes the annual population dynamics such that π(π‘ + 1) = π©3 β π©2 β π©1 β π(π‘) = π¨ β π(π‘) where n(t) describes the number of individuals at the beginning of the annual cycle. The matrix elements of A are consequently a function of the season-specific vital rates: Stages π¨ = π©3 β π©2 β π©1 = π ππππππ’ππ‘ππ£π π·ππππππ‘ π πππ π ππππππ’ππ‘ππ£π πΏπΊπππ β π β ππΊπππ πΏπΊπππ β π β ππ΅πππ1 π·ππππππ‘ π πππ ππ΅πππ1 β ππ΅πππ2 β ππΊπππ πΏπ΅πππ1 β πΏπ΅πππ2 β πΏπ΅πππ3 ONLINE APPENDIX C. Vital rate parameters The following tables contain the vital rates used to parameterize the stochastic integral projection model of Cryptantha flava and the stochastic periodic matrix model of Carrichtera annua. Cryptantha flava: Period Survival Change in individual size σ γ Variation of change in individual size Δγ a b1(σ) b2(σ)2 b3(σ)3 a b1(γ) b2(γ)2 b3(γ)3 a b1(Δγ) b2(Δγ)2 b3(Δγ)3 1997-1998 0.00 0.39 -0.02 0.00 2.74 0.72 0.00 0.00 1.38 0.32 0.00 0.00 1998-1999 0.08 0.07 0.00 0.00 2.47 0.52 0.00 0.00 0.82 0.22 0.00 0.00 1999-2000 0.22 0.29 0.00 0.00 3.31 0.84 0.02 0.00 1.77 0.37 0.00 0.00 2000-2001 -0.93 0.37 -0.02 0.00 3.94 0.77 0.00 0.00 2.27 0.24 0.00 0.00 2001-2003 -1.18 0.18 -0.01 0.00 6.76 0.82 0.00 0.00 6.19 -0.37 0.03 0.00 2003-2004 -0.92 0.35 -0.01 0.00 2.80 1.56 -0.01 0.00 2.40 0.39 0.00 0.00 2004-2005 -0.24 0.29 -0.01 0.00 6.09 0.36 0.02 0.00 4.45 -0.08 0.01 0.00 2005-2006 -0.71 0.26 -0.01 0.00 2.19 0.67 0.00 0.00 2.71 0.02 0.01 0.00 2006-2007 -0.29 0.02 0.00 0.00 3.28 0.15 0.05 0.00 2.06 0.34 0.00 0.00 2007-2008 -0.90 0.33 -0.01 0.00 1.52 1.32 -0.03 0.00 1.73 0.21 0.00 0.00 2008-2009 -0.59 0.51 -0.03 0.00 4.74 0.86 0.00 0.00 3.32 0.15 0.00 0.00 2009-2010 0.31 -0.09 0.01 0.00 3.73 0.94 0.00 0.00 -0.19 0.80 -0.01 0.00 2010-2011 0.27 0.13 0.00 0.00 6.17 0.71 0.00 0.00 3.78 0.28 0.00 0.00 Cryptantha flava (cont’d): Period Flowering probability Recruitment Ο χ Establishment probability ε a b1(Ο) b2(Ο)2 b3(Ο)3 a b1(χ) b2(χ)2 b3(χ)3 1997-1998 -5.37 0.98 -0.05 0.00 0.53 0.09 0.00 0.00 1998-1999 -3.29 0.71 -0.03 0.00 0.16 0.15 0.00 1999-2000 -4.29 0.65 -0.03 0.00 0.48 0.04 2000-2001 -4.14 0.94 -0.06 0.00 0.15 2001-2003 -7.03 2.43 -0.24 0.01 2003-2004 -2.40 0.02 0.00 2004-2005 -4.74 0.92 2005-2006 -5.05 2006-2007 Size distribution of recruits ϑ b2(ϑ)2 b3(ϑ)3 a b1(ϑ) 0.04 31.07 -49.92 26.15 -4.25 0.00 0.14 9.19 -6.27 2.02 -0.23 0.00 0.00 0.28 5.69 -1.75 0.00 0.00 0.15 0.00 0.00 0.04 3.72 -0.86 0.00 0.00 -0.38 0.17 0.00 0.00 0.02 2.75 -0.66 0.00 0.00 0.00 0.80 -0.01 0.00 0.00 0.88 5.42 -2.14 0.00 0.00 -0.06 0.00 0.65 0.05 0.00 0.00 0.04 39.13 -61.97 30.75 -4.77 0.93 -0.03 0.00 0.66 0.07 0.00 0.00 0.07 7.22 -3.11 0.00 0.00 -4.82 0.70 -0.02 0.00 0.28 0.04 0.00 0.00 0.49 7.55 -3.12 0.00 0.00 2007-2008 -6.26 1.52 -0.11 0.00 -0.36 0.10 0.00 0.00 0.31 9.33 -8.85 3.10 -0.36 2008-2009 -3.19 0.25 0.00 0.00 -0.30 0.10 0.00 0.00 0.40 9.56 -9.50 3.59 -0.43 2009-2010 -9.01 2.28 -0.18 0.00 -0.71 0.22 -0.01 0.00 0.10 -19.63 33.83 -11.56 0.00 2010-2011 -5.16 1.06 -0.05 0.00 -0.06 0.09 0.00 0.00 0.18 6.04 0.00 0.00 -2.74 a and bi represent the intercept and slopes, respectively, of the polynomic functions that parameterize the integral projection models. Carrichtera annua: Germinable Period seed survival Germinable Juvenile seed persurvival capita Seedbank stasis Seed per- Seed capita emergence contribution from production to seedbank seedbank δGerm σ ψGerm δBank1 δBank2 δBank3 ψBank εGerm 2002-2003 0.10 0.82 24.21 1.00 1.00 0.38 14.45 0.62 2003-2004 0.03 0.70 4.68 1.00 1.00 0.38 2.80 0.62 2004-2005 0.10 0.67 21.91 1.00 1.00 0.38 13.08 0.62 2005-2006 0.02 0.38 6.63 1.00 1.00 0.38 3.96 0.62 2006-2007 0.05 0.89 10.89 1.00 1.00 0.38 6.50 0.62 2007-2008 0.04 0.40 4.86 1.00 1.00 0.38 2.90 0.62 2008-2009 0.13 0.89 86.51 1.00 1.00 0.38 51.64 0.62 Each vital rate is described in the context of the life cycles of Cryptantha and Carrichtera in figure 3 of the manuscript. ONLINE APPENDIX D. Present, back-projected and projected precipitation Annual precipitation (from May of year t to April of year t+1) recorded by the closest permanent weather stations to both field sites, and back-projected by the super-high resolution climate change model used in this manuscript [7]. Cryptantha flava - Utah Carrichtera annua - Israel Permanent Permanent station (current) Backprojected station (current) Backprojected Maximum 533.65 354.12 456.04 430.62 75th percentile 399.35 305.93 321.31 262.04 Average 352.61 267.67 264.43 238.09 25th percentile 288.16 234.27 212.46 204.38 Minimum 174.24 168.64 113.80 119.85 1979-1980 - 308.11 456.04 265.13 1980-1981 - 246.31 243.45 237.20 1981-1982 280.92 298.19 196.32 245.60 1982-1983 318.52 256.54 338.37 239.57 1983-1984 477.27 234.52 140.51 187.99 1984-1985 346.71 214.01 259.98 140.86 1985-1986 501.90 239.74 211.79 261.01 1986-1987 332.74 294.70 304.50 214.78 1987-1988 309.12 354.12 315.05 296.81 1988-1989 210.82 241.96 235.92 248.28 1989-1990 290.58 337.68 259.17 205.46 1990-1991 375.67 345.40 337.14 299.88 1991-1992 239.27 212.55 446.06 234.23 1992-1993 392.18 305.21 265.13 311.13 1993-1994 368.81 233.54 228.23 201.13 1994-1995 420.88 168.64 358.50 215.11 1995-1996 388.37 312.76 214.48 218.90 1996-1997 440.18 332.58 232.08 223.91 1997-1998 491.74 260.42 244.11 178.06 1998-1999 466.85 234.63 127.34 119.85 1999-2000 382.78 284.01 173.08 430.62 2000-2001 348.74 275.93 307.93 303.18 2001-2002 174.24 217.62 323.40 176.12 2002-2003 236.98 214.83 351.80 259.39 2003-2004 252.98 - 234.80 - 2004-2005 533.65 - 377.30 - 2005-2006 382.78 - 195.60 - 2006-2007 313.94 - 259.90 - 2007-2008 319.28 - 181.20 - 2008-2009 275.08 - 113.80 - 2009-2010 321.56 - - - 2010-2011 328.01 - - - Annual precipitation projected by the super-high resolution climate change model used [7]. Cryptantha flava - Utah Carrichtera annua - Israel Projected Projected Maximum 491.83 318.84 75th percentile 349.26 251.38 Average 305.10 195.47 25th percentile 248.76 160.19 Minimum 195.08 84.62 2075-2076 268.74 174.99 2076-2077 248.82 186.35 2077-2078 491.83 206.95 2078-2079 282.37 182.93 2079-2080 291.82 212.74 2080-2081 238.27 250.65 2081-2082 471.35 268.89 2082-2083 280.15 106.76 2083-2084 224.10 265.66 2084-2085 459.83 105.15 2085-2086 276.46 204.49 2086-2087 230.24 179.90 2087-2088 269.81 204.73 2088-2089 352.44 292.48 2089-2090 323.85 318.84 2090-2091 269.12 253.59 2091-2092 282.57 115.81 2092-2093 248.57 198.80 2093-2094 399.56 279.52 2094-2095 195.08 102.72 2095-2096 262.79 108.59 2096-2097 348.20 188.34 2097-2098 378.82 197.88 2098-2099 227.72 84.62 References 1. Caswell, H. 2001 Matrix population models: construction, analysis, and interpretation, 2nd edn. Sunderland, MA, USA: Sinauer Associates. 2. 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